JP2001210160A - Device for recovering vinyl chloride resin from vinyl chlorine waste contained in plastic covered with scraps - Google Patents

Device for recovering vinyl chloride resin from vinyl chlorine waste contained in plastic covered with scraps

Info

Publication number
JP2001210160A
JP2001210160A JP2000018630A JP2000018630A JP2001210160A JP 2001210160 A JP2001210160 A JP 2001210160A JP 2000018630 A JP2000018630 A JP 2000018630A JP 2000018630 A JP2000018630 A JP 2000018630A JP 2001210160 A JP2001210160 A JP 2001210160A
Authority
JP
Japan
Prior art keywords
vinyl chloride
solvent
waste
tank
solution
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
JP2000018630A
Other languages
Japanese (ja)
Inventor
Tadayuki Uematsu
忠之 植松
Masatada Fukushima
正忠 福島
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.)
Japan Atomic Energy Agency
Original Assignee
Japan Atomic Energy Research Institute
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 Japan Atomic Energy Research Institute filed Critical Japan Atomic Energy Research Institute
Priority to JP2000018630A priority Critical patent/JP2001210160A/en
Publication of JP2001210160A publication Critical patent/JP2001210160A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • B29B17/02Separating plastics from other materials
    • 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
    • B29B17/02Separating plastics from other materials
    • B29B2017/0213Specific separating techniques
    • B29B2017/0293Dissolving the materials in gases or liquids
    • 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 provide a device to remove contaminants from plastic insulation refuse of the disassembled insulated wires recovered after used, by removing hazardous foreign matters, dissolving the refuse in a solvent and evaporating the solvent for recycling. SOLUTION: The device recovering vinyl chloride resin crushes the used wires, recovers vinyl chloride waste fro the crushed pieces as required, disolves the vinyl chloride waste in a solvent removes solid contents from the solution by using a separation device, and evaporates the solvent after separating the solid contents with an evaporator the evaporator has airtight evaporation chamber, and is featured in that it is divided into plural compartments from the bottom to a certain height. Thus, the solvent disolving vinyl chloride can be efficiently evaporated.

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】本発明は使用を終えたプラス
チック被覆電線を回収して解体し、解体したプラスチッ
ク電線の被覆廃材を先ず銅とプラスチック廃材とに一次
分離し、次いでプラスチック廃材を塩化ビニル廃材と他
の廃材とに分離し、分離した塩化ビニル廃材から塩化ビ
ニル樹脂を再利用または廃却処理可能とする電線被覆廃
材中に含まれる塩化ビニル廃材から塩化ビニル樹脂を回
収する装置に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention is to collect and disassemble used plastic-coated electric wires, disassemble them, firstly separate the waste plastics from the disassembled plastic electric wires into copper and plastic waste, and then convert the plastic waste to polyvinyl chloride waste. The present invention relates to an apparatus for recovering vinyl chloride resin from waste vinyl chloride contained in wire-covered waste, which can be reused or discarded from the separated vinyl chloride waste, which is separated into waste and other waste materials. .

【0002】[0002]

【従来の技術】電線、特に屋外に配線された電線は、そ
の安全性を考慮して、一定期間使用されると取り替えら
れる。取り替えられた廃電線は導体(主として銅)と被
覆廃材(主としてプラスチック)とに分離される。分離
された被覆廃材の内、石油系の材料からなる被覆廃材に
ついては燃料化して石油代替エネルギーとしての再利用
(リサイクル)の方法が開発されている。一方、塩化ビ
ニルを主体とした被覆廃材の再利用(リサイクル)は遅
れており、殆どが埋立処理されている。
2. Description of the Related Art Wires, particularly wires wired outdoors, are replaced after a certain period of use in consideration of their safety. The replaced waste wire is separated into a conductor (mainly copper) and a covering waste material (mainly plastic). Among the separated coated waste materials, a method of reusing (recycling) the coated waste materials made of petroleum-based materials as fuel instead of petroleum-based energy has been developed. On the other hand, the reuse (recycling) of coated waste materials mainly composed of vinyl chloride is delayed, and most of them are landfilled.

【0003】廃電線のリサイクルは先ず電線を導体
(銅)と被覆廃材(プラスチック)とに分離する。導体
と被覆廃材との分離は電線のサイズにより次の2つの方
法に分けられる。 (1)導体径が1.6mm以上の電線 回収された廃電線を一定の長さに切断し、ケーブルコア
まで解体後、該ケーブルコアを剥線機により導体から被
覆材を剥がして導体と被覆廃材とを分離する方法(以下
剥線法という)。 (2)導体径が1.6mm未満の電線 回収された廃電線を自動粉砕機に投入し、導体と被覆廃
材とを一緒に細かく切断、粉砕(ナゲット処理)し、粉
砕片を比重差によって導体と被覆廃材とに分離する方法
(以下ナゲット法という)。
In the recycling of waste electric wires, first, electric wires are separated into conductors (copper) and coated waste materials (plastic). Separation of the conductor and the coating waste material can be divided into the following two methods depending on the size of the electric wire. (1) Electric wire with a conductor diameter of 1.6 mm or more The collected waste electric wire is cut to a certain length, disassembled to a cable core, and the cable core is peeled off from the conductor by a stripping machine to cover the conductor. A method of separating waste materials (hereinafter referred to as stripping method). (2) Electric wire with a conductor diameter of less than 1.6 mm The collected waste electric wire is put into an automatic crusher, and the conductor and the coated waste material are finely cut together and crushed (nugget treatment). And a coating waste material (hereinafter referred to as a nugget method).

【0004】[0004]

【発明が解決しようとする課題】上記した導体サイズの
大きい電線については剥線法で導体と被覆材とに分離回
収するため、回収された被覆廃材に銅が付着しているこ
とは殆どなく、従って被覆廃材をそのまま再処理工程へ
と回すことができる。一方、通信線等細線からなる電線
は回収工程でポリエチレン被覆電線や塩化ビニル被覆電
線とに分別することなくそのまま切断、粉砕(ナゲット
処理)しているため、銅、ポリエチレン、塩化ビニル等
が混在している。
Since the above-mentioned electric wire having a large conductor size is separated and collected into a conductor and a coating material by a stripping method, copper is hardly adhered to the recovered coating waste material. Therefore, the coating waste material can be directly transferred to the reprocessing step. On the other hand, wires made of thin wires such as communication wires are cut and pulverized (nugget treatment) without being separated into polyethylene-coated wires or polyvinyl chloride-coated wires in the recovery process, so copper, polyethylene, vinyl chloride, etc. are mixed. ing.

【0005】ところで、近時、資源循環型社会の要求か
らマテリアルリサイクルの研究が進められ、電線被覆廃
材のリサイクルにもこのマテリアルリサイクルの適用が
検討されている。プラスチック被覆廃電線のナゲット廃
材には、前述したように銅、ポリエチレン、塩化ビニル
等が混在している。このように銅、ポリエチレン、塩化
ビニル等が混在しているナゲット廃材にマテリアルリサ
イクルを適用することはできないために、ナゲット廃材
を銅、ポリエチレン、塩化ビニル等、それぞれ単独成分
に分離、分別することが要求されてきている。このた
め、先ず、この粉砕片から水に浮遊するポリエチレン廃
材を分別し、残った銅と塩化ビニル廃材とを比重差分別
法により銅と被覆廃材(主として塩化ビニル)とに分離
している。分離された塩化ビニル廃材は再処理(脱塩
素、脱銅)して代替エネルギー(高炉用の原料)として
再利用するか、埋立廃棄処理される。しかしながら、塩
化ビニル廃材には塩化ビニルの可塑剤としてDOPが、
また熱安定剤として鉛が含まれているため、そのまま廃
棄すると土壌を汚染する懸念がある。
Recently, research on material recycling has been promoted in response to the demands of a resource-recycling society, and the application of this material recycling to the recycling of wire covering waste materials has been studied. Copper, polyethylene, vinyl chloride, and the like are mixed in the nugget waste material of the plastic-coated waste wire as described above. Since material recycling cannot be applied to nugget waste containing copper, polyethylene, vinyl chloride, etc., it is necessary to separate and separate nugget waste into individual components such as copper, polyethylene, vinyl chloride, etc. Is being requested. For this reason, first, polyethylene waste materials floating in water are separated from the crushed pieces, and the remaining copper and vinyl chloride waste materials are separated into copper and coated waste materials (mainly vinyl chloride) by a specific gravity difference method. The separated vinyl chloride waste is reprocessed (dechlorination, decopperization) and reused as alternative energy (raw material for blast furnaces), or landfill disposal. However, DOP is used as a plasticizer for vinyl chloride in vinyl chloride waste materials,
Also, since lead is contained as a heat stabilizer, there is a concern that soil will be contaminated if discarded as it is.

【0006】そこで、本発明者は塩化ビニル被覆廃材の
再利用につき鋭意研究を重ねた結果、塩化ビニル廃材に
含まれる他の成分や銅、並びに塩化ビニルに配合されて
いる添加剤(主として鉛化合物、炭酸カルシウム)を除
去し、高炉用原料としてリサイクル可能な、あるいは廃
棄処理しても公害問題を発生しない処理方法を完成し、
その処理を効率的に実施する装置の改良に成功したもの
である。
Accordingly, the present inventors have conducted intensive studies on the reuse of vinyl chloride-coated waste materials, and have found that other components contained in the vinyl chloride waste material, copper, and additives (mainly lead compounds) contained in the vinyl chloride. Calcium carbonate) has been removed, and a processing method that can be recycled as a raw material for blast furnaces or that does not cause pollution problems even when disposed of has been completed.
An apparatus that efficiently performs the processing has been successfully improved.

【0007】[0007]

【課題を解決するための手段】本発明は、プラスチック
被覆廃電線を粉砕し、必要により該粉砕片から塩化ビニ
ル廃材を選別し、該塩化ビニル廃材を溶媒で溶解し、該
溶液から固形分を固液分離装置で分離し、固形分を分離
した溶液を溶媒蒸発装置で前記溶媒を蒸発させ、塩化ビ
ニル樹脂を回収する装置において、前記溶媒蒸発装置は
気密にしうる蒸発槽を有し、該蒸発槽の少なくとも底は
複数の部屋に仕切られていることを特徴とするプラスチ
ック被覆電線廃材に含まれる塩化ビニル廃材から塩化ビ
ニルを回収する装置である。
SUMMARY OF THE INVENTION According to the present invention, a plastic-coated waste wire is crushed, if necessary, vinyl chloride waste material is selected from the crushed pieces, the vinyl chloride waste material is dissolved in a solvent, and solid content is removed from the solution. In a device for separating a solid content separated by a solid-liquid separator and evaporating the solvent with a solvent evaporator to recover a vinyl chloride resin, the solvent evaporator has an evaporation tank that can be airtight, At least the bottom of the tank is partitioned into a plurality of rooms, and is a device for recovering vinyl chloride from waste vinyl chloride contained in waste plastic-coated electric wires.

【0008】[0008]

【発明の実施の形態】以下本発明を詳細に説明する。本
発明は先ず、ナゲット廃材から比重差により銅を分離す
る。次いで、水中で塩化ビニル廃材とポリエチレン廃材
とに分離し、水に沈んだ塩化ビニル廃材と除去しきれて
いない銅を振動式湿式比重差分別装置により銅を分離除
去し、最後に塩化ビニル廃材から塩化ビニルに配合され
ている添加剤を除去し、銅や他のプラスチック廃材を含
まない塩化ビニル樹脂として回収するものである。な
お、導体径が1.6mm以上の電線廃材については、廃
材が塩化ビニル廃材として分別されているので、該廃材
を適当な大きさに粉砕し、塩化ビニルに配合されている
添加剤を本発明装置により除去し、塩化ビニル樹脂とし
て回収するものである。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below in detail. In the present invention, copper is first separated from waste nugget by a difference in specific gravity. Next, in the water, vinyl chloride waste material and polyethylene waste material are separated, and the polyvinyl chloride waste material submerged in the water and the copper that has not been completely removed are separated and removed by a vibration-type wet specific gravity discrimination device. The additives contained in the vinyl chloride are removed, and recovered as a vinyl chloride resin free of copper and other plastic waste materials. In addition, as for the electric wire waste material having a conductor diameter of 1.6 mm or more, since the waste material is classified as the vinyl chloride waste material, the waste material is pulverized to an appropriate size, and the additive compounded in the vinyl chloride is added to the present invention. It is removed by a device and recovered as a vinyl chloride resin.

【0009】図1は本発明の一実施形態を示すもので、
塩化ビニル廃材から塩化ビニルに配合される添加剤を除
去する工程を示すもので、1は溶解濾過槽で、該溶解濾
過槽1は上部が溶解槽2、下部が貯留槽3からなり、溶
解槽2には塩化ビニル廃材を投入する原料供給口4と塩
化ビニルを溶解する溶液を供給する溶剤供給管5、攪拌
装置6を備え、溶解槽2と貯留槽5との境には濾過手段
7(例えば所定の目開きの金網等)が設けられ、溶解濾
過槽1全体は図示しない加熱装置で加熱しうるように構
成されている。
FIG. 1 shows an embodiment of the present invention.
This shows the step of removing the additives mixed with vinyl chloride from the vinyl chloride waste material. Reference numeral 1 denotes a dissolving and filtering tank. The dissolving and filtering tank 1 includes a dissolving tank 2 at an upper part and a storage tank 3 at a lower part. 2 is provided with a raw material supply port 4 for charging waste vinyl chloride, a solvent supply pipe 5 for supplying a solution for dissolving vinyl chloride, and a stirrer 6, and a filtering means 7 (at the boundary between the dissolution tank 2 and the storage tank 5). For example, a wire mesh having a predetermined mesh is provided, and the entire dissolution filtration tank 1 is configured to be heated by a heating device (not shown).

【0010】溶解槽2の原料供給口4から投入される塩
化ビニル廃材と溶媒供給管5から注入される溶媒(例え
ばテトラヒドロフラン)とは攪拌装置6により混合され
て塩化ビニル廃材は溶解され、塩化ビニル廃材を溶解し
た溶液は濾過手段7により濾過されて貯留槽3に蓄積さ
れる。なお、図中配管8は溶液を溶解槽2に循環する管
路で、塩化ビニルの溶解度が薄い溶液は溶解槽2に戻さ
れて更に塩化ビニルを溶解し、濃度を上げるように構成
している。塩化ビニル廃材を溶解槽2で溶解することに
より、塩化ビニルは溶解して濾過手段7により濾過され
て貯留槽3に溜められる。溶媒に不溶な成分(塩化ビニ
ル廃材に混入している銅、ポリエチレン等)は濾過手段
7を通過できずに分離除去される。
The waste vinyl chloride material supplied from the raw material supply port 4 of the dissolving tank 2 and the solvent (eg, tetrahydrofuran) injected from the solvent supply pipe 5 are mixed by the stirrer 6 so that the waste vinyl chloride material is dissolved, and the vinyl chloride waste material is dissolved. The solution in which the waste material is dissolved is filtered by the filtering means 7 and accumulated in the storage tank 3. In the drawing, a pipe 8 is a conduit for circulating the solution to the dissolving tank 2, and a solution having a low solubility of vinyl chloride is returned to the dissolving tank 2 to further dissolve the vinyl chloride to increase the concentration. . By dissolving the vinyl chloride waste material in the dissolving tank 2, the vinyl chloride dissolves and is filtered by the filtering means 7 and stored in the storage tank 3. Components insoluble in the solvent (copper, polyethylene, etc. mixed in the waste vinyl chloride) cannot pass through the filtration means 7 and are separated and removed.

【0011】貯留槽3に溜められた溶液は遠心分離機か
らなる固液分離装置11に供給され、ここで溶液に含ま
れる(塩化ビニルの熱安定剤や充填剤として添加され
た)鉛、カルシウム等の固形分を除去する。固形分を除
去された溶液は気密にしうる溶媒蒸発槽22、加熱装置
23からなる溶媒蒸発装置21の溶媒蒸発槽22に供給
され、溶媒を蒸発除去し、塩化ビニル樹脂を回収する。
なお、図中29は溶媒の回収手段で、熱交換器24、タ
ンク25からなる。また、図中27は減圧ポンプ(真空
ポンプ)で、溶媒蒸発槽22内を該ポンプで減圧し、溶
媒を低い温度で蒸発させ、蒸発効率を向上させるもので
ある。
The solution stored in the storage tank 3 is supplied to a solid-liquid separation device 11 comprising a centrifugal separator, where the lead (calculated as a heat stabilizer for vinyl chloride and added as a filler) and calcium are added. And other solids. The solution from which the solid content has been removed is supplied to a solvent evaporating tank 22 of a solvent evaporating apparatus 21 including a solvent evaporating tank 22 and a heating device 23 which can be airtight, and the solvent is evaporated off to recover the vinyl chloride resin.
In the figure, reference numeral 29 denotes a solvent recovery means, which comprises a heat exchanger 24 and a tank 25. In the drawing, reference numeral 27 denotes a decompression pump (vacuum pump) which decompresses the inside of the solvent evaporation tank 22 by the pump to evaporate the solvent at a low temperature, thereby improving the evaporation efficiency.

【0012】図2は溶媒蒸発槽22の断面図で、図示す
るように溶媒蒸発槽22の室内は底から所定の高さまで
仕切り板26にて複数の小部屋28に仕切られている。
仕切り板26には熱伝導性に優れた材料を選択する。仕
切り板26は溶媒蒸発槽22と一体に構成してもよく、
あるいは別に格子状に組み立てた部材を溶媒蒸発槽にセ
ットしてもよい。仕切り板の高さは一度に処理する溶液
の量にもよるが、仕切り板で仕切られる全ての部屋に溶
液が均一に入るように構成すれば、その高さは任意であ
る。
FIG. 2 is a cross-sectional view of the solvent evaporating tank 22. As shown, the interior of the solvent evaporating tank 22 is divided into a plurality of small chambers 28 by a partition plate 26 from a bottom to a predetermined height.
For the partition plate 26, a material having excellent heat conductivity is selected. The partition plate 26 may be formed integrally with the solvent evaporation tank 22,
Alternatively, a separately assembled member in a lattice shape may be set in the solvent evaporation tank. The height of the partition plate depends on the amount of the solution to be treated at a time, but the height is arbitrary as long as the solution is configured to uniformly enter all the rooms partitioned by the partition plate.

【0013】溶媒蒸発槽22に仕切り板26を設けて溶
媒蒸発槽内を複数の部屋28に仕切ることにより塩化ビ
ニル樹脂を含有する溶液から溶媒を効率よく蒸発させる
ことができ、塩化ビニル樹脂の回収作業がすこぶる改善
される。溶媒蒸発槽に仕切り板を設けず(従来の方法)
に溶液から溶媒を蒸発除去し塩化ビニル樹脂を回収しよ
うとすると、溶液を加熱する溶媒蒸発槽22の加熱面
(主として底側の壁面)から溶媒が蒸発するため、先ず
塩化ビニル樹脂は溶媒蒸発槽22の壁面から固化し始め
る。即ち、底の方の壁面部分(熱を伝える部分)から塩
化ビニル樹脂の膜ができ始める。加熱壁面に塩化ビニル
樹脂膜が生成すると塩化ビニル樹脂は熱伝導性が金属に
比べて劣るために溶媒蒸発槽22内の溶液に熱が伝わり
難くなり熱効率がすこぶる悪化する。
By providing a partition plate 26 in the solvent evaporation tank 22 and partitioning the inside of the solvent evaporation tank into a plurality of chambers 28, the solvent can be efficiently evaporated from the solution containing the vinyl chloride resin, and the vinyl chloride resin can be recovered. Work is greatly improved. No partition plate in the solvent evaporation tank (conventional method)
When the solvent is evaporated from the solution to recover the vinyl chloride resin, the solvent evaporates from the heating surface (mainly the bottom wall surface) of the solvent evaporation tank 22 for heating the solution. It begins to solidify from the 22 wall. That is, a vinyl chloride resin film starts to be formed from the bottom wall portion (portion transmitting heat). When a vinyl chloride resin film is formed on the heating wall surface, the heat conductivity of the vinyl chloride resin is inferior to that of the metal, so that heat is hardly transmitted to the solution in the solvent evaporating tank 22 and the thermal efficiency is greatly deteriorated.

【0014】また、溶液からの溶媒の蒸発と塩化ビニル
樹脂の固化は、熱が良く伝わる蒸発槽の壁の部分と溶液
の表面の部分から固化が始まって先ず膜状に固まり、次
いでこの膜が厚くなるように固化する。このため、未蒸
発の溶液は塩化ビニル樹脂の膜(固化した部分)に包ま
れた状態となり中心ほど溶媒の抜けが悪くなり、完全に
溶媒を除去することが極めて困難になる。そのため、あ
る程度溶媒を除去したのち、固形分(塩化ビニル樹脂)
を溶媒蒸発槽から取り出して細かく切断し、再度溶媒の
除去作業を行って溶媒を完全に除去する工程が付加され
ている。
The evaporation of the solvent from the solution and the solidification of the vinyl chloride resin begin with solidification from the wall of the evaporating tank where heat is well transmitted and the surface of the solution, and then solidify in the form of a film. Solidify to thicken. For this reason, the unevaporated solution is wrapped in a vinyl chloride resin film (solidified portion), so that the solvent is less likely to escape from the center, and it is extremely difficult to completely remove the solvent. Therefore, after removing the solvent to some extent, solid content (vinyl chloride resin)
Is removed from the solvent evaporation tank, cut into small pieces, and the solvent is removed again to completely remove the solvent.

【0015】本発明は、上述したように、溶媒蒸発槽2
2に仕切り板26を設けて、溶媒の蒸発除去を行うもの
である。仕切り板26を設けることにより溶液への熱の
伝達経路は溶媒蒸発槽22の壁面から仕切り板26に伝
わり、仕切り板から溶液に熱が伝わるために従来の壁面
のみから熱が伝わる状況からその熱伝達面積は格段に広
がり、かつ、塩化ビニル樹脂が固化して膜を作り熱伝導
度が悪くなっても各部屋28の容積はそれぞれ小さいの
で各部屋毎の溶媒の蒸発にはそれほど影響せず、従っ
て、溶媒の蒸発除去効率は格段に向上する。また、溶媒
を蒸発させた後の塩化ビニル樹脂の溶媒蒸発槽からの取
り出しは、蒸発処理の温度(約85°C)から取り出し
時温度(室温)へ低下するため塩化ビニル樹脂自身が熱
収縮し、塩化ビニル樹脂は部屋28単位の大きさで取り
出せるため、取り出し後の切断作業が不要となる等の付
随した効果もある。溶媒蒸発槽22で蒸発した溶媒は熱
交換器24により冷やされてタンク25に貯蔵され回収
される。回収された溶媒は再度塩化ビニル廃材の溶解に
使用することができる。
According to the present invention, as described above, the solvent evaporation tank 2
2, a partition plate 26 is provided to remove the solvent by evaporation. By providing the partition plate 26, the heat transmission path to the solution is transmitted from the wall surface of the solvent evaporation tank 22 to the partition plate 26, and the heat is transmitted from the partition plate to the solution. Even if the transmission area spreads remarkably, and the vinyl chloride resin solidifies to form a film and the thermal conductivity deteriorates, the volume of each room 28 is small, so that the evaporation of the solvent in each room is not so affected. Therefore, the efficiency of solvent removal by evaporation is significantly improved. In addition, when the vinyl chloride resin is removed from the solvent evaporation tank after the solvent is evaporated, the temperature of the evaporation process (about 85 ° C.) drops to the temperature at the time of removal (room temperature). In addition, since the vinyl chloride resin can be taken out in units of 28 units, there is an accompanying effect that the cutting work after taking out is unnecessary. The solvent evaporated in the solvent evaporation tank 22 is cooled by the heat exchanger 24 and stored in the tank 25 and collected. The recovered solvent can be used again for dissolving the vinyl chloride waste material.

【0016】[0016]

【実施例1】溶媒蒸発槽22に該溶媒蒸発槽壁面に接す
るように板厚3.5mmのステンレス板で作成した仕切
り板26(各部屋の大きさは5cm×5cm×8cm平
均)をセットした。この蒸発槽にテトラヒドロフランに
溶解した塩化ビニル廃材溶液から前工程で不純物を除去
した溶液を入れ、85°Cで減圧しつつ溶媒を除去し
た。その結果を図3に示す。図3から明らかなように5
時間後には約88%の溶媒が除去された。
Example 1 A partition plate 26 made of a 3.5 mm-thick stainless steel plate (the size of each room is 5 cm × 5 cm × 8 cm average) was set in the solvent evaporation tank 22 so as to be in contact with the wall surface of the solvent evaporation tank. . The solution obtained by removing the impurities in the previous step from the vinyl chloride waste material solution dissolved in tetrahydrofuran was put into this evaporating tank, and the solvent was removed while reducing the pressure at 85 ° C. The result is shown in FIG. As is apparent from FIG.
After time, about 88% of the solvent was removed.

【0017】[0017]

【比較例1】実施例1で使用した溶媒蒸発槽に間仕切り
板を設けることなく実施例1と同様の条件で溶液から溶
媒を除去する実験を行った。その結果を図3に併記し
た。図3から明らかなように5時間後の溶媒除去率は約
60%、8時間後でも約70%であり溶媒の除去効率が
上がらないことを示している。
Comparative Example 1 An experiment was conducted in which the solvent was removed from the solution under the same conditions as in Example 1 without providing a partition plate in the solvent evaporation tank used in Example 1. The results are also shown in FIG. As is clear from FIG. 3, the solvent removal rate after 5 hours is about 60%, and even after 8 hours, it is about 70%, indicating that the solvent removal efficiency does not increase.

【0018】上記実施例では溶剤としてテトラヒドロフ
ランを用いたが、溶剤としてはこの外にジメチルスルホ
キシド、塩化エチレン、塩化メチレン、テトラリン等塩
化ビニル樹脂が溶解する溶剤であれば使用することがで
きる。また、溶剤を希釈する必要があるときは、希釈剤
としてアセトン、酢酸エチル、酢酸メチル、エチルアル
コール、メチルアルコール等を使用することができる。
また、濾過手段7としては、60〜325メッシュの金
網を用いるのが好ましいが、特に微細な粉砕片を除去す
るために目開きの細かい濾過材を使用することは濾過工
程の所要時間が長くなるため好ましくなく、濾過手段で
除去しきれなかった粉砕片は次工程の固液分離装置11
で分離することが可能なため作業効率を考慮した目開き
の濾過材を選定することが好ましい。
In the above embodiment, tetrahydrofuran was used as a solvent. However, any solvent may be used as long as a vinyl chloride resin such as dimethyl sulfoxide, ethylene chloride, methylene chloride, and tetralin can be dissolved therein. When it is necessary to dilute the solvent, acetone, ethyl acetate, methyl acetate, ethyl alcohol, methyl alcohol, or the like can be used as a diluent.
Further, as the filtering means 7, it is preferable to use a wire mesh of 60 to 325 mesh, but in particular, using a filtering material having a fine opening to remove fine crushed pieces increases the time required for the filtering step. Therefore, the pulverized pieces that cannot be removed by the filtration means are not preferable,
Therefore, it is preferable to select a filter material having openings in consideration of the working efficiency.

【0019】溶媒蒸発槽22内を仕切る間仕切り板26
としては熱伝導性に優れ、使用する溶剤で腐食しない材
料であればよく、その厚さは処理する溶液の量にもよる
が2〜5mm程度のものが好ましい。また、仕切る部屋
の形状は四角、六角、円等特に限定するものではなく、
製作するのに容易な形状を選定することができる。
A partition plate 26 for partitioning the inside of the solvent evaporation tank 22
Any material may be used as long as it has excellent thermal conductivity and does not corrode with the solvent used, and its thickness depends on the amount of the solution to be treated, but is preferably about 2 to 5 mm. Also, the shape of the room to be partitioned is not particularly limited, such as square, hexagon, circle, etc.
A shape that is easy to manufacture can be selected.

【0020】[0020]

【発明の効果】以上詳述したように、本発明の装置によ
れば、廃電線の被覆廃材から銅や他の廃材を含まず、ま
た、環境等に有害な塩化ビニルへの添加剤をも除去した
塩化ビニル樹脂を極めて効率よく回収できる。従って、
電線被覆廃材である塩化ビニルを脱塩素処理することで
高炉用の原料として再利用でき、或いはマテリアルリサ
イクルの適用が可能となり、また、埋立廃棄するに際し
ても土壌の汚染等を懸念することなく廃棄できる等優れ
た効果を有するものである。
As described above in detail, according to the apparatus of the present invention, copper and other waste materials are not contained in the waste wire coating waste material, and the additive to the vinyl chloride which is harmful to the environment and the like is also eliminated. The removed vinyl chloride resin can be recovered extremely efficiently. Therefore,
By dechlorinating vinyl chloride, which is a wire covering waste material, it can be reused as a raw material for blast furnaces, or material recycling can be applied.Furthermore, it is possible to dispose of landfill without worrying about soil contamination etc. It has excellent effects.

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

【図1】本発明の一実施形態を示す概略説明図である。FIG. 1 is a schematic explanatory view showing one embodiment of the present invention.

【図2】本発明で使用する蒸発槽の一実施形態を示す概
略説明図である。
FIG. 2 is a schematic explanatory view showing one embodiment of an evaporation tank used in the present invention.

【図3】本発明の効果を示すグラフである。FIG. 3 is a graph showing the effect of the present invention.

【符号の説明】[Explanation of symbols]

1 溶解濾過槽 2 溶解槽 3 貯留槽 7 濾過手段 11 固液分離装置 21 溶媒蒸発装置 22 溶媒蒸発槽 23 加熱手段 24 熱交換器 25 タンク 26 仕切り板 28 仕切られた部屋 29 溶媒の回収手段 DESCRIPTION OF SYMBOLS 1 Dissolution filtration tank 2 Dissolution tank 3 Storage tank 7 Filtration means 11 Solid-liquid separation device 21 Solvent evaporator 22 Solvent evaporation tank 23 Heating means 24 Heat exchanger 25 Tank 26 Partition plate 28 Partitioned room 29 Solvent recovery means

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 プラスチック被覆廃電線を粉砕し、必要
により該粉砕片から塩化ビニル廃材を選別し、該塩化ビ
ニル廃材を溶媒で溶解し、該溶液から固形分を固液分離
装置で分離し、固形分を分離した溶液を溶媒蒸発装置で
前記溶媒を蒸発させ、塩化ビニル樹脂を回収する装置に
おいて、前記溶媒蒸発装置は気密にしうる蒸発槽を有
し、該蒸発槽の底から所定の高さまでは複数の部屋に仕
切られていることを特徴とするプラスチック被覆電線廃
材に含まれる塩化ビニル廃材から塩化ビニル樹脂を回収
する装置。
1. A plastic-coated waste wire is crushed, if necessary, vinyl chloride waste material is selected from the crushed pieces, the vinyl chloride waste material is dissolved with a solvent, and a solid content is separated from the solution by a solid-liquid separator. In a device for recovering a vinyl chloride resin by evaporating the solvent with a solvent evaporating device from a solution from which a solid content is separated, the solvent evaporating device has an evaporating tank that can be airtight, and a predetermined height from the bottom of the evaporating tank. Is a device for recovering vinyl chloride resin from waste vinyl chloride contained in plastic-coated electric wire waste, which is divided into a plurality of rooms.
JP2000018630A 2000-01-27 2000-01-27 Device for recovering vinyl chloride resin from vinyl chlorine waste contained in plastic covered with scraps Pending JP2001210160A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000018630A JP2001210160A (en) 2000-01-27 2000-01-27 Device for recovering vinyl chloride resin from vinyl chlorine waste contained in plastic covered with scraps

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000018630A JP2001210160A (en) 2000-01-27 2000-01-27 Device for recovering vinyl chloride resin from vinyl chlorine waste contained in plastic covered with scraps

Publications (1)

Publication Number Publication Date
JP2001210160A true JP2001210160A (en) 2001-08-03

Family

ID=18545456

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000018630A Pending JP2001210160A (en) 2000-01-27 2000-01-27 Device for recovering vinyl chloride resin from vinyl chlorine waste contained in plastic covered with scraps

Country Status (1)

Country Link
JP (1) JP2001210160A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2007052936A1 (en) * 2005-11-07 2007-05-10 World Resources Co., Ltd A composition for dissolving electric wire covering
WO2007066533A1 (en) * 2005-12-05 2007-06-14 Orient Instrument Computer Co., Ltd. Method and facility for the treatment of scrap polyvinyl chloride resin
KR101110640B1 (en) 2011-10-18 2012-02-24 주식회사 제씨콤 Melting apparatus using reclaimed oil
FR3010083A1 (en) * 2013-09-03 2015-03-06 Solvay PROCESS FOR FILTERING A SOLUTION OF PLASTIC MATERIAL IN A SOLVENT
EP4067422A1 (en) * 2021-03-22 2022-10-05 Baerlocher GmbH Method for treating halogenated polymers

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2007052936A1 (en) * 2005-11-07 2007-05-10 World Resources Co., Ltd A composition for dissolving electric wire covering
WO2007066533A1 (en) * 2005-12-05 2007-06-14 Orient Instrument Computer Co., Ltd. Method and facility for the treatment of scrap polyvinyl chloride resin
KR101110640B1 (en) 2011-10-18 2012-02-24 주식회사 제씨콤 Melting apparatus using reclaimed oil
FR3010083A1 (en) * 2013-09-03 2015-03-06 Solvay PROCESS FOR FILTERING A SOLUTION OF PLASTIC MATERIAL IN A SOLVENT
EP4067422A1 (en) * 2021-03-22 2022-10-05 Baerlocher GmbH Method for treating halogenated polymers

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