JPH07178351A - Electrostatic sorting device for rubber and plastic waste - Google Patents

Electrostatic sorting device for rubber and plastic waste

Info

Publication number
JPH07178351A
JPH07178351A JP32552993A JP32552993A JPH07178351A JP H07178351 A JPH07178351 A JP H07178351A JP 32552993 A JP32552993 A JP 32552993A JP 32552993 A JP32552993 A JP 32552993A JP H07178351 A JPH07178351 A JP H07178351A
Authority
JP
Japan
Prior art keywords
rubber
plastic waste
waste
particles
electrode
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
JP32552993A
Other languages
Japanese (ja)
Inventor
Showa Miyauchi
将和 宮内
Norihiro Mori
範宏 森
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.)
DENSEN SOGO GIJUTSU CENTER
Original Assignee
DENSEN SOGO GIJUTSU CENTER
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 DENSEN SOGO GIJUTSU CENTER filed Critical DENSEN SOGO GIJUTSU CENTER
Priority to JP32552993A priority Critical patent/JPH07178351A/en
Publication of JPH07178351A publication Critical patent/JPH07178351A/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
    • Y02W30/52Mechanical 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
    • 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
    • Y02W30/82Recycling of waste of electrical or electronic equipment [WEEE]

Landscapes

  • Electrostatic Separation (AREA)
  • Processing And Handling Of Plastics And Other Materials For Molding In General (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)

Abstract

PURPOSE:To provide an inexpensive sorting device which is capable of accurately sorting the rubber and plastic waste generated at the time of production of electric wires and cables by kinds of materials and does not require a waste water treatment, etc. CONSTITUTION:An agitating machine 11 which is driven by a motor 10 and electrifies an insulating material by friction at the time of agitation is connected to a hopper 3 for supplying the crushed rubber and plastic waste 2. The end of the agitating machine 11 is connected through a small-diameter falling hole 12 to a dropping pipe 13. Parallel flat plate electrodes 14 applied with 21 DC high voltage are arranged to face each other in the intermediate part of the dropping pipe 13 so that the electrified waste particles receive the electrostatic force by the DC electric field generated between the parallel flat plate electrodes 14 during the course of dropping and are attracted and divided toward the electrode side of the polarity on the opposite side.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、電線・ケーブルの製造
時や使用後などに生じるゴム・プラスチック廃棄物を、
静電気を利用して、導電性材料と絶縁性材料とにあるい
は絶縁材料の種類別に選別する装置に関する。
[Field of Industrial Application] The present invention eliminates rubber / plastic waste generated during or after the production of electric wires / cables.
The present invention relates to an apparatus for selecting a conductive material and an insulating material or a type of insulating material by using static electricity.

【0002】[0002]

【従来の技術】近年電線・ケーブルの分野では、製造時
や使用後などに発生する大量の電線・ケーブル廃棄物を
破砕し、振動と風力を利用した比重選別法により銅を分
離回収し(ナゲットシステム)、銅を回収した残りを、
産業廃棄物として主に埋立て処理している。すなわち、
電線・ケーブルの廃棄物から銅を回収した残りには、少
量の銅の残留が認められたり導電性ポリエチレン(P
E)が混在する場合もあるが、ポリ塩化ビニル(PV
C)、ポリエチレン(PE)等の被覆材料がほとんどを
占め、これらを選別する有効な方法がないため、産業廃
棄物として埋立て処分されているのが現状であった。
2. Description of the Related Art In the field of electric wires and cables in recent years, a large amount of electric wire and cable waste generated during manufacturing or after use is crushed, and copper is separated and recovered by a specific gravity sorting method using vibration and wind force (nugget. System), the rest of the recovered copper,
It is mainly landfilled as industrial waste. That is,
A small amount of copper remains in the residual copper recovered from electric wire / cable waste, and conductive polyethylene (P
E) may be mixed, but polyvinyl chloride (PV
C), polyethylene (PE) and other coating materials occupy most of them, and since there is no effective method for selecting them, they are currently disposed of as landfill as industrial waste.

【0003】ちなみに、電線・ケーブルの被覆材以外の
ゴム・プラスチック破砕物の選別には、風力選別や流動
層選別のような乾式の比重選別方法、または浮沈選別や
遠心力選別のような湿式の比重選別方法が使用されてい
るが、これらの方法のうちで乾式比重選別法を、前記し
た電線・ケーブルのゴム・プラスチック廃棄物の選別に
使用する場合には、比重別、重量別、サイズ別などの選
別には有効であるが、同形状のゴム・プラスチック破砕
物同士の選別精度を上げることが難しいという問題があ
った。また、湿式比重選別法のうちで浮沈選別法は、ポ
リオレフィン系プラスチックとそれ以外のプラスチック
とを選別する場合には有効であるが、選別に使用した廃
水の処理を必要とするという問題があり、さらにハイド
ロサイクロンによる遠心力選別法は、仕様、運転条件に
より適用範囲を広くとれる反面、装置が高価で廃水処理
を必要とするという問題があった。
By the way, in selecting rubber / plastic crushed materials other than electric wire / cable covering materials, dry specific gravity sorting methods such as wind power sorting or fluidized bed sorting, or wet type sorting such as floating / sink sorting or centrifugal sorting. Although specific gravity sorting methods are used, if the dry specific gravity sorting method is used to sort out the rubber / plastic waste of electric wires / cables described above, it is sorted by specific gravity, weight, and size. Although it is effective for sorting, etc., there is a problem that it is difficult to improve the sorting accuracy between crushed rubber / plastics having the same shape. Further, among the wet specific gravity sorting methods, the floating sedimentation sorting method is effective when sorting polyolefin-based plastics and other plastics, but there is a problem that the wastewater used for sorting is required to be treated. Further, the hydrocyclone centrifugal separation method has a wide range of application depending on specifications and operating conditions, but has a problem that the apparatus is expensive and requires wastewater treatment.

【0004】[0004]

【発明が解決しようとする課題】このように資源の再利
用や環境保全の観点から、電線・ケーブル被覆材の廃棄
物に限らず一般のゴム・プラスチック廃棄物の選別と回
収が求められているが、従来からのゴム・プラスチック
破砕物の選別技術は、環境に与える影響や種類別の選別
精度の点で未だ十分ではなかった。
Thus, from the viewpoint of resource reuse and environmental protection, it is required to select and recover not only electric wire / cable covering material waste but also general rubber / plastic waste. However, conventional techniques for selecting crushed rubber / plastic crushed materials have not been sufficient in terms of environmental impact and sorting accuracy by type.

【0005】本発明はこれらの問題を解決するためにな
されたもので、電線・ケーブルの製造時や使用後に生じ
るゴム・プラスチックを主とする廃棄物を、材料の種類
別に精度良く選別することができ、かつ廃水処理等を必
要としない安価な装置を提供することを目的とする。
The present invention has been made to solve these problems, and it is possible to accurately sort wastes mainly of rubber and plastic produced during or after the production of electric wires / cables by the type of material. It is an object of the present invention to provide an inexpensive device that can be processed and does not require wastewater treatment.

【0006】[0006]

【課題を解決するための手段】本発明のゴム・プラスチ
ック廃棄物の静電選別装置は、ゴム・プラスチック廃棄
物を供給する手段と、前記供給手段の供給口に接続され
た連続搬送手段と、前記ゴム・プラスチック廃棄物に電
荷を帯びさせる帯電手段と、前記搬送手段により搬送さ
れ前記帯電手段により帯電されたゴム・プラスチック廃
棄物を落下させる手段と、前記落下手段により落下しつ
つあるゴム・プラスチック廃棄物に対して、静電的な力
を加え、帯電の有無および電荷の種類に応じて落下方向
を変更させる手段と、前記静電気力印加手段の下方に並
置された複数の回収容器とを備えてなることを特徴とす
る。
An electrostatic separation apparatus for rubber / plastic waste according to the present invention comprises means for supplying rubber / plastic waste, and continuous conveying means connected to the supply port of the supplying means. A charging means for charging the rubber / plastic waste with an electric charge, a means for dropping the rubber / plastic waste carried by the carrying means and charged by the charging means, and a rubber / plastic falling by the dropping means A means for applying an electrostatic force to the waste to change the falling direction according to the presence or absence of electrification and the type of electric charge, and a plurality of recovery containers juxtaposed below the electrostatic force applying means. It is characterized by

【0007】本発明の選別対象とされるゴム・プラスチ
ック廃棄物としては、PE、ポリプロピレン、エチレン
−プロピレンコポリマー等の各種オレフィン系ポリマ
ー、PVC、ブチルゴム、スチレン−ブタジエンゴム等
の絶縁材料の混合物があげられる他、さらに導電性PE
等の導電性ゴム・プラスチックが混合されていても良
い。本発明においては、このようなゴム・プラスチック
廃棄物を、予め公知の破砕手段により粗粒状乃至粉末状
に破砕したものを使用する。
The rubber / plastic wastes to be sorted according to the present invention include various olefin polymers such as PE, polypropylene and ethylene-propylene copolymer, and a mixture of insulating materials such as PVC, butyl rubber and styrene-butadiene rubber. In addition, conductive PE
A conductive rubber or plastic such as the above may be mixed. In the present invention, such rubber / plastic waste is crushed in advance into a coarse grain or powder by a known crushing means.

【0008】また本発明において、前記したように破砕
されたゴム・プラスチック廃棄物に電荷を帯びさせる手
段としては、例えば針状電極とその他の電極との間に高
電圧を印加し、針状電極の先端部からコロナ放電を引起
こすことにより帯電させる手段や、高電圧を印加し、誘
電分極を利用して帯電させる方法や、あるいは絶縁材料
の混合物を撹拌し摩擦により帯電させる手段などが採ら
れる。
Further, in the present invention, as a means for charging the rubber / plastic waste crushed as described above with an electric charge, for example, a high voltage is applied between the needle electrode and the other electrode, and the needle electrode A method of charging by inducing a corona discharge from the tip of the, a method of applying a high voltage and using dielectric polarization, or a method of stirring a mixture of insulating materials and charging by friction is used. .

【0009】[0009]

【作用】本発明のゴム・プラスチック廃棄物の静電選別
装置によれば、予め公知の手段により粗粒状乃至粉末状
に破砕されたゴム・プラスチック廃棄物が、連続搬送手
段に供給され、その搬送過程であるいは搬送後に帯電手
段により、例えば材料の種類に応じて異なる符号の電荷
を帯びさせられた後、落下に向う。そして、落下過程に
おいて、これらの帯電したゴム・プラスチック廃棄物
に、帯電の有無や電荷の種類に応じて異なる静電的な力
が加えられ、落下方向が変えられる。その結果、帯電さ
れた電荷の種類ごとに異なる落下の道筋を経て、対応す
る回収容器内に到達し回収される。したがって、ゴム・
プラスチック廃棄物を構成材料の種類別に効率的に選別
することができ、かつ選別精度も向上させることができ
る。
According to the electrostatic separation apparatus for rubber / plastic waste of the present invention, the rubber / plastic waste, which has been crushed into coarse particles or powder by a known means, is supplied to the continuous conveying means and is conveyed. In the process or after being conveyed, the charging means gives a charge having a different sign depending on the type of material, for example, and then falls. Then, in the dropping process, different electrostatic forces are applied to these charged rubber / plastic wastes depending on the presence or absence of electrification and the type of electric charge, and the dropping direction is changed. As a result, the charged electric charge reaches the corresponding recovery container through a different drop path and is recovered. Therefore, rubber
The plastic waste can be efficiently sorted according to the type of the constituent material, and the sorting accuracy can be improved.

【0010】[0010]

【実施例】以下、本発明の実施例を図面に基いて説明す
る。図1は、本発明に係るゴム・プラスチック廃棄物の
静電選別装置の一実施例を概略的に示す構成図である。
Embodiments of the present invention will be described below with reference to the drawings. FIG. 1 is a schematic diagram showing an embodiment of an electrostatic sorting apparatus for rubber / plastic waste according to the present invention.

【0011】図1において符号1は、収容物に振動を与
えて一定量ずつ水平方向に搬送する振動搬送装置を示
し、その入口側端部には、電線・ケーブル廃棄物を破砕
し銅を分離回収した残りのゴム・プラスチック廃棄物2
を供給するホッパー3が接続されている。また、この振
動搬送装置1の出口側端部には、搬送されてきたゴム・
プラスチック廃棄物2をコロナ放電により帯電させるた
めの装置が配置されている。すなわち、この帯電装置
は、円筒状の電極面が振動搬送装置1の搬送路の延長線
上に位置するように配設された回転電極4と、その僅か
に上方に、先端部が回転電極4の電極面と対向するよう
に配置された針状電極5とから成り、回転電極4は接地
されている。そして、針状電極5と回転電極4との間に
直流高電圧を印加し、針状電極5の先端部でコロナ放電
を発生させるようになっている。さらに、このような帯
電装置の回転電極4電極面の下方(接線方向)には、複
数の回収容器6が並べて配置されており、さらに回転電
極4の下部には、その電極面に吸着されたまま移送され
るゴム・プラスチック廃棄物を掻き落とすためのブラシ
7が、接触配置されている。なお、図中符号8は、安全
確保のために帯電装置等を被包する絶縁カバーを示し、
9は装置を電気的に操作するための操作盤を示す。 こ
のように構成される静電選別装置においては、ホッパー
3から供給された粒子状などのゴム・プラスチック廃棄
物2が、振動搬送装置1により一定の速度で水平方向に
搬送された後、回転電極4の電極面を経て下方に落下す
る。ところが、この回転電極4と対向配置された針状電
極5の先端部ではコロナ放電が起こっているので、放電
の結果生じた高電圧側の極性と同じ極性の気体イオン
が、搬送されてきたゴム・プラスチック廃棄物2に付着
し、その結果ゴム・プラスチック廃棄物2は同じ極性に
帯電する。そして、このように帯電したゴム・プラスチ
ック廃棄物2が回転電極4の電極面に達すると、導電性
の粒子と絶縁性の粒子とではその後の落下挙動が異な
る。すなわち、導電性粒子では帯電された電荷が接地さ
れた回転電極4を伝って直ちに逃げてしまうため、回転
電極4の電極面上を早々に滑り落ちて、最も前方に配置
された回収容器6aの中に落下する。これに対して、絶
縁性の粒子では電荷が逃げることなく帯電したままであ
り、この電荷と回転電極4との間の静電気力により、回
転電極4の電極面に吸着される。そして、回転電極4の
回転にしたがって周方向に移送され、重力の方が静電気
力より大きくなった地点で下方に落下し、前記導電性粒
子の回収容器6aより後方に配置された回収容器6bの
中に落下する。さらに、ゴム・プラスチック廃棄物2粒
子が絶縁性で十分に小さい場合には、回転電極4の下部
でも静電気力の方が重力より大きくなるため、粒子は回
転電極4に吸着されたままで落下することがないが、こ
れは最終的にブラシ7により掻き落とされ、回収容器6
cの中に落下する。このようにして、ゴム・プラスチッ
ク廃棄物2の中の導電性粒子と絶縁性粒子とが、効率的
にかつ精度良く選別され回収される。なお、回収容器6
aと6cとの間にさらに回収小容器6bを配置すること
が好ましいが、その場合には、回収小容器6bの中に導
電性粒子と絶縁性粒子の両方が混じり合って落下するこ
とになり、ホッパー3に戻し再度選別することにより、
さらに選別精度を上げることができる。
In FIG. 1, reference numeral 1 denotes a vibrating and conveying device for vibrating a contained substance to convey it in a horizontal direction by a constant amount, and at the inlet end thereof, electric wire / cable waste is crushed to separate copper. Remaining collected rubber / plastic waste 2
Is connected to a hopper 3 for supplying. In addition, at the outlet side end of the vibration transfer device 1, the rubber
A device is arranged for charging the plastic waste 2 by corona discharge. That is, in this charging device, the rotating electrode 4 is arranged so that the cylindrical electrode surface is located on the extension line of the conveying path of the vibrating conveying device 1, and the tip portion of the rotating electrode 4 is slightly above the rotating electrode 4. The rotating electrode 4 is composed of a needle electrode 5 arranged so as to face the electrode surface, and the rotating electrode 4 is grounded. Then, a high DC voltage is applied between the needle-shaped electrode 5 and the rotating electrode 4 to generate corona discharge at the tip of the needle-shaped electrode 5. Further, a plurality of collection containers 6 are arranged side by side below the electrode surface (tangential direction) of the rotating electrode 4 of such a charging device, and further below the rotating electrode 4, the collecting container 6 is attracted to the electrode surface. A brush 7 for scraping off the rubber / plastic waste transferred as it is is arranged in contact therewith. In the figure, reference numeral 8 indicates an insulating cover for enclosing a charging device and the like for ensuring safety,
Reference numeral 9 indicates an operation panel for electrically operating the apparatus. In the electrostatic sorting device configured as described above, the rubber / plastic waste 2 in the form of particles supplied from the hopper 3 is horizontally transported at a constant speed by the vibration transport device 1, and then the rotating electrode is used. After passing through the electrode surface of No. 4, it falls downward. However, since corona discharge is occurring at the tip of the needle-like electrode 5 arranged opposite to the rotating electrode 4, gas ions having the same polarity as the polarity on the high voltage side generated as a result of the discharge have been conveyed. -It adheres to the plastic waste 2, and as a result, the rubber-plastic waste 2 is charged to the same polarity. When the charged rubber / plastic waste 2 reaches the electrode surface of the rotary electrode 4, the conductive particles and the insulating particles have different falling behaviors. That is, in the conductive particles, the charged electric charge travels through the grounded rotary electrode 4 and immediately escapes, so that the conductive particles quickly slide down on the electrode surface of the rotary electrode 4, and the recovery container 6a disposed at the foremost position. Fall inside. On the other hand, in the insulating particles, the electric charge does not escape and remains charged, and the electrostatic force between the electric charge and the rotating electrode 4 causes the particles to be attracted to the electrode surface of the rotating electrode 4. Then, as the rotating electrode 4 rotates, it is transferred in the circumferential direction, falls at a point where gravity becomes larger than the electrostatic force, and falls in the collecting container 6b arranged behind the conductive particle collecting container 6a. Fall inside. Furthermore, when the two particles of rubber / plastic waste are insulating and sufficiently small, the electrostatic force is larger than the gravity even at the lower part of the rotating electrode 4, so that the particles should fall while being attracted to the rotating electrode 4. However, this is finally scraped off by the brush 7 and the recovery container 6
It falls into c. In this way, the conductive particles and the insulating particles in the rubber / plastic waste 2 are efficiently and accurately sorted and collected. The collection container 6
It is preferable to further arrange the recovery small container 6b between a and 6c, but in that case, both the conductive particles and the insulating particles are mixed and fall into the recovery small container 6b. By returning to the hopper 3 and sorting again,
Further, the sorting accuracy can be improved.

【0012】次に、本発明の別の実施例について説明す
る。図2は、電線・ケーブルのゴム・プラスチック廃棄
物を、PVC、PEなど絶縁材料の種類別に選別する装
置の一例を示し、この装置においては、破砕された粒子
状などのゴム・プラスチック廃棄物2を供給するホッパ
ー3の供給口に、モーター10により駆動される撹拌機
11が接続されている。また、この撹拌機11の出口側
端部は、小径の落下孔12を経て落下管13に接続さ
れ、落下管13の中間部には、平行平板電極14が落下
路を挟んで対向配置されている。そして、これらの平板
電極14間には直流高電圧が印加され、電極間に一様な
直流電界が発生するようになっている。さらに落下管1
3の底部には、複数の回収容器6が隣接して並置されて
いる。
Next, another embodiment of the present invention will be described. FIG. 2 shows an example of an apparatus for sorting rubber / plastic waste of electric wires / cables according to the type of insulating material such as PVC or PE. In this apparatus, rubber / plastic waste 2 such as crushed particles is used. The stirrer 11 driven by the motor 10 is connected to the supply port of the hopper 3 for supplying. The end of the stirrer 11 on the outlet side is connected to a drop tube 13 through a drop hole 12 having a small diameter, and a parallel plate electrode 14 is disposed in the middle of the drop tube 13 so as to face each other across the drop path. There is. A high DC voltage is applied between the flat plate electrodes 14 so that a uniform DC electric field is generated between the electrodes. Further drop tube 1
At the bottom of 3, a plurality of recovery containers 6 are juxtaposed side by side.

【0013】このように構成される実施例の装置におい
ては、ホッパー3を経て撹拌機11に供給された粒子状
などのゴム・プラスチック廃棄物2が、撹拌機11内で
激しく撹拌され、相互の摩擦により絶縁材料の種類別に
異なる符号の電荷を帯びた後、小径落下孔12を通り一
定の速度で落下管13内を落下する。そして、このよう
に帯電したゴム・プラスチック廃棄物2粒子は、落下途
中で平行平板電極14間に生じた直流電界により静電気
力を受け、正に帯電した粒子は負電極側へ負に帯電した
粒子は正電極側へそれぞれ引寄せられ、各電極に近い位
置に配設された回収容器6の中に落下する。したがっ
て、例えばPVCとPEの混合物からなるゴム・プラス
チック廃棄物2を選別する場合には、正電極に近い回収
容器6dには摩擦により負に帯電したPVC粒子が、負
電極に近い回収容器6eには正に帯電したPE粒子がそ
れぞれ集まることになり、絶縁材料の種類に応じて精度
の高い選別がなされる。
In the apparatus of the embodiment thus configured, the rubber / plastic waste 2 in the form of particles, which is supplied to the stirrer 11 through the hopper 3, is vigorously stirred in the stirrer 11 to be mutually agitated. After being charged with an electric charge having a different sign depending on the type of the insulating material due to friction, it drops through the small diameter drop hole 12 and at a constant speed in the drop tube 13. Then, the two particles of the rubber / plastic waste thus charged are subjected to the electrostatic force by the DC electric field generated between the parallel plate electrodes 14 during the fall, and the positively charged particles are the particles negatively charged to the negative electrode side. Are attracted to the positive electrode side and fall into the recovery container 6 arranged at a position close to each electrode. Therefore, for example, when selecting the rubber / plastic waste 2 made of a mixture of PVC and PE, PVC particles negatively charged by friction are collected in the collection container 6d near the positive electrode and collected in the collection container 6e near the negative electrode. In this case, positively charged PE particles are collected respectively, and highly accurate sorting is performed according to the type of insulating material.

【0014】次に、実施例の装置を用いてゴム・プラス
チック廃棄物の選別を行った具体的実験例を示す。
Next, a concrete experimental example in which rubber / plastic waste is sorted by using the apparatus of the embodiment will be shown.

【0015】まず、ゴム・プラスチック廃棄物の供試物
として、導電性PE粒子と絶縁性PE粒子との 50:50
(重量比)の混合物(実験例1)と、導電性PE粒子と
PVC粒子との 50:50の混合物(実験例2)、および導
電性PE粒子とPE粒子とPVC粒子との各 1/3重量ず
つの混合物(実験例3)を用意し、これらの供試物を図
1に示す装置のホッパーにそれぞれに供給した。そし
て、針状電極5に Kvの直流高電圧を印加して先端部
でコロナ放電を発生させ、高圧電極側受け皿(回収容器
6a)と中間の受け皿(回収容器6b)、および接地電
極側受け皿(回収容器6c)の各容器に回収された各粒
子の割合を測定した。
First, as a sample of rubber / plastic waste, 50:50 of conductive PE particles and insulating PE particles was used.
(Weight ratio) mixture (Experimental Example 1), conductive PE particles and PVC particles in a 50:50 mixture (Experimental Example 2), and conductive PE particles, PE particles and PVC particles each 1/3 A mixture of each weight (Experimental Example 3) was prepared, and these samples were supplied to the hopper of the apparatus shown in FIG. Then, a high DC voltage of Kv is applied to the needle-shaped electrode 5 to generate corona discharge at the tip, and the high-voltage electrode side receiving tray (collection container 6a), the intermediate receiving tray (recovery container 6b), and the ground electrode side receiving tray ( The proportion of each particle collected in each container of the collection container 6c) was measured.

【0016】測定結果を表1に示す。The measurement results are shown in Table 1.

【0017】[0017]

【表1】 表1から、供試物に含まれる導電性粒子と絶縁性粒子と
が高い精度で選別されていることがわかった。
[Table 1] From Table 1, it was found that the conductive particles and the insulating particles contained in the sample were sorted with high accuracy.

【0018】また、図2に示す装置をさらに簡易化した
図3に示す装置を使用し、PE粒子とPVC粒子を 50:
50の重量比で混合したものの選別を行った(実験例
4)。すなわち、この混合物をホッパー3に入れ、ホッ
パー3内で撹拌し相互の摩擦により帯電させた後、落下
速度緩和のために屈曲部を形成した細径のPVCパイプ
15を通過させ、緩慢な速度で落下させた。次いで、P
VCパイプ15の下方に配置された、50Kvの直流高電圧
が印加された平行平板電極14間を落下させ、正電極
(接地電極)および負電極(高圧電極)に近く配置され
た2つの回収容器6d、6eにそれぞれ回収した。そし
て、各容器に回収されたPE粒子とPVC粒子との割合
をそれぞれ測定した。
Further, using the apparatus shown in FIG. 3 which is a simplified version of the apparatus shown in FIG.
The mixture mixed at a weight ratio of 50 was selected (Experimental Example 4). That is, this mixture is put in the hopper 3, stirred in the hopper 3 and charged by mutual friction, and then passed through a small-diameter PVC pipe 15 having a bent portion to relax the falling speed, and at a slow speed. I dropped it. Then P
Two recovery containers placed below the VC pipe 15 and dropped between the parallel plate electrodes 14 to which a high DC voltage of 50 Kv is applied, and placed near the positive electrode (ground electrode) and the negative electrode (high voltage electrode). It collect | recovered to 6d and 6e, respectively. Then, the proportions of PE particles and PVC particles collected in each container were measured.

【0019】測定結果を表2に示す。The measurement results are shown in Table 2.

【0020】[0020]

【表2】 表2から、供試物に含まれるPE粒子とPVC粒子とが
高い精度で選別されていることがわかった。
[Table 2] From Table 2, it was found that PE particles and PVC particles contained in the sample were sorted with high accuracy.

【0021】[0021]

【発明の効果】以上説明したように本発明に係る装置に
よれば、電線・ケーブルの製造時などに生じるゴム・プ
ラスチック廃棄物が、導電性の有無や材料の種類別に効
率的にかつ精度良く選別されるので、資源の回収並びに
再利用を図ることができる。また、廃水処理を必要とし
ないなど、周囲環境に与える影響が小さい。
As described above, according to the device of the present invention, rubber / plastic waste produced during the production of electric wires / cables can be efficiently and accurately classified according to the presence or absence of conductivity and the type of material. Since they are selected, the resources can be collected and reused. In addition, it does not require wastewater treatment and has little impact on the surrounding environment.

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

【図1】本発明に係るゴム・プラスチック廃棄物の静電
選別装置の一実施例を概略的に示す構成図。
FIG. 1 is a configuration diagram schematically showing an embodiment of an electrostatic sorting apparatus for rubber / plastic waste according to the present invention.

【図2】本発明に係る静電選別装置の別の実施例を概略
的に示す構成図。
FIG. 2 is a configuration diagram schematically showing another embodiment of the electrostatic sorting device according to the present invention.

【図3】本発明の具体的実験例に使用する静電選別装置
を概略的に示す構成図。
FIG. 3 is a configuration diagram schematically showing an electrostatic sorting device used in a specific experimental example of the present invention.

【符号の説明】[Explanation of symbols]

1………振動搬送装置 2………ゴム・プラスチ
ック廃棄物 3………ホッパー 4………回転電極 5………針状電極 6………回収容器 7………ブラシ 8………絶縁カバー 9………操作盤 10………モーター 11………撹拌機 12………小径落下孔1 13………落下管 14………平行平板電極 15………細径PVCパイプ
1 ………… Vibration transfer device 2 ………… Rubber / plastic waste 3 ………… Hopper 4 ………… Rotating electrode 5 ………… Needle electrode 6 ………… Collection container 7 ………… Brush 8 ………… Insulation Cover 9 ………… Control panel 10 ………… Motor 11 ………… Stirrer 12 ………… Small diameter drop hole 1 13 ………… Drop tube 14 ………… Parallel plate electrode 15 ……… Small diameter PVC pipe

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 ゴム・プラスチック廃棄物を供給する手
段と、前記供給手段の供給口に接続された連続搬送手段
と、前記ゴム・プラスチック廃棄物に電荷を帯びさせる
帯電手段と、前記搬送手段により搬送され前記帯電手段
により帯電されたゴム・プラスチック廃棄物を落下させ
る手段と、前記落下手段により落下しつつあるゴム・プ
ラスチック廃棄物に対して、水平方向に静電的な力を加
え、帯電の有無および電荷の種類に応じて落下方向を変
更させる手段と、前記静電気力印加手段の下方に並置さ
れた複数の回収容器とを備えてなることを特徴とするゴ
ム・プラスチック廃棄物の静電選別装置。
1. A means for supplying a rubber / plastic waste, a continuous transfer means connected to a supply port of the supply means, a charging means for charging the rubber / plastic waste with an electric charge, and the transfer means. A means for dropping the rubber / plastic waste that is conveyed and charged by the charging means and a horizontal direction electrostatic force is applied to the rubber / plastic waste that is falling by the dropping means to charge the waste. Electrostatic sorting of rubber / plastic waste, characterized by comprising a means for changing the falling direction according to the presence or absence and the type of electric charge, and a plurality of collection containers juxtaposed below the electrostatic force applying means. apparatus.
【請求項2】 コロナ放電あるいは静電分極により、破
砕され粒状になったプラスチック廃棄物に帯電させ、導
電性粒子(金属、導電性ポリエチレンなど)と絶縁性粒
子に選別し、引き続いて、摩擦帯電により絶縁性粒子を
絶縁材料の種類別に選別する静電選別装置。
2. A crushed and granular plastic waste is charged by corona discharge or electrostatic polarization, and is separated into conductive particles (metal, conductive polyethylene, etc.) and insulating particles, and subsequently, triboelectric charging. An electrostatic sorting device that sorts insulating particles by type of insulating material.
JP32552993A 1993-12-24 1993-12-24 Electrostatic sorting device for rubber and plastic waste Pending JPH07178351A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP32552993A JPH07178351A (en) 1993-12-24 1993-12-24 Electrostatic sorting device for rubber and plastic waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP32552993A JPH07178351A (en) 1993-12-24 1993-12-24 Electrostatic sorting device for rubber and plastic waste

Publications (1)

Publication Number Publication Date
JPH07178351A true JPH07178351A (en) 1995-07-18

Family

ID=18177898

Family Applications (1)

Application Number Title Priority Date Filing Date
JP32552993A Pending JPH07178351A (en) 1993-12-24 1993-12-24 Electrostatic sorting device for rubber and plastic waste

Country Status (1)

Country Link
JP (1) JPH07178351A (en)

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DE19522147A1 (en) * 1995-06-19 1997-01-02 Hamos Elektronik Gmbh Electrostatic sorter for comminuted particles of differing types, esp. plastics
WO2000027535A1 (en) * 1998-11-05 2000-05-18 Hitachi Zosen Corporation Triboelectrification device
WO2000027536A1 (en) * 1998-11-05 2000-05-18 Hitachi Zosen Corporation Selector
WO2000027534A1 (en) * 1998-11-05 2000-05-18 Hitachi Zosen Corporation Plastic separator
WO2000029119A1 (en) * 1998-11-18 2000-05-25 Hitachi Zosen Corporation Method of separating plastic
WO2000076669A1 (en) * 1999-06-11 2000-12-21 Hitachi Zosen Corporation Method and apparatus for separating plastic
WO2001052998A1 (en) * 2000-01-21 2001-07-26 The University Of Western Ontario Tribocharging and electrostatic separation of mixed electrically insulating particles
JP2002059082A (en) * 2000-08-17 2002-02-26 Mitsubishi Electric Corp Reusable plastic production method and apparatus
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JP2016533264A (en) * 2013-11-20 2016-10-27 コリア インスティチュート オブ ジオサイエンス アンド ミネラル リソースズ Friction-charged electrostatic sorting method for separation of ABS and PS waste plastic materials
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Cited By (20)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE19522147A1 (en) * 1995-06-19 1997-01-02 Hamos Elektronik Gmbh Electrostatic sorter for comminuted particles of differing types, esp. plastics
WO2000027535A1 (en) * 1998-11-05 2000-05-18 Hitachi Zosen Corporation Triboelectrification device
WO2000027536A1 (en) * 1998-11-05 2000-05-18 Hitachi Zosen Corporation Selector
WO2000027534A1 (en) * 1998-11-05 2000-05-18 Hitachi Zosen Corporation Plastic separator
WO2000029119A1 (en) * 1998-11-18 2000-05-25 Hitachi Zosen Corporation Method of separating plastic
US6415929B1 (en) * 1998-11-18 2002-07-09 Hitachi Zosen Corporation Method of separating plastic
WO2000076669A1 (en) * 1999-06-11 2000-12-21 Hitachi Zosen Corporation Method and apparatus for separating plastic
US6426474B1 (en) 1999-06-11 2002-07-30 Hitachi Zosen Corporation Method and apparatus for separating plastic
US6927354B1 (en) 2000-01-21 2005-08-09 The University Of Western Ontario Tribocharging and electrostatic separation of mixed electrically insulating particles
WO2001052998A1 (en) * 2000-01-21 2001-07-26 The University Of Western Ontario Tribocharging and electrostatic separation of mixed electrically insulating particles
JP2002059082A (en) * 2000-08-17 2002-02-26 Mitsubishi Electric Corp Reusable plastic production method and apparatus
KR100485814B1 (en) * 2002-07-11 2005-04-28 한국지질자원연구원 Arrangement of electrodes for electrostatic plastic particles separator
WO2005024854A1 (en) * 2003-09-09 2005-03-17 Korea Institute Of Geoscience And Mineral Resources Electrostatic separation system for removal of fine metal from plastic
JP2007504971A (en) * 2003-09-09 2007-03-08 コリア インスティチュート オブ ジオサイエンス アンド ミネラル リソースズ Electrostatic sorting system for plastic fine metal removal
JP2010119911A (en) * 2008-11-17 2010-06-03 Mitsubishi Electric Corp Electrostatic sorting method and electrostatic sorting apparatus
KR100916727B1 (en) * 2009-04-20 2009-09-14 류연진 Waste scrap recycling method and apparatus
JP2016533264A (en) * 2013-11-20 2016-10-27 コリア インスティチュート オブ ジオサイエンス アンド ミネラル リソースズ Friction-charged electrostatic sorting method for separation of ABS and PS waste plastic materials
CN109130004A (en) * 2018-08-07 2019-01-04 天津金派英克莱自行车股份有限公司 A kind of electric bicycle tire production technology
WO2023063454A1 (en) * 2021-10-15 2023-04-20 김현군 Conductive fine particle separation and sorting device
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