JPS63276509A - Method and appratus for regeneration of resin-metal composite material - Google Patents
Method and appratus for regeneration of resin-metal composite materialInfo
- Publication number
- JPS63276509A JPS63276509A JP62110708A JP11070887A JPS63276509A JP S63276509 A JPS63276509 A JP S63276509A JP 62110708 A JP62110708 A JP 62110708A JP 11070887 A JP11070887 A JP 11070887A JP S63276509 A JPS63276509 A JP S63276509A
- Authority
- JP
- Japan
- Prior art keywords
- resin
- separation
- metal
- composite material
- specific gravity
- 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
Links
- 230000008929 regeneration Effects 0.000 title claims abstract description 7
- 238000011069 regeneration method Methods 0.000 title claims abstract description 7
- 238000000034 method Methods 0.000 title claims description 26
- 239000002905 metal composite material Substances 0.000 title claims 3
- 229920005989 resin Polymers 0.000 claims abstract description 97
- 239000011347 resin Substances 0.000 claims abstract description 96
- 239000002245 particle Substances 0.000 claims abstract description 56
- 239000002131 composite material Substances 0.000 claims abstract description 46
- 239000000463 material Substances 0.000 claims abstract description 41
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 24
- 238000001816 cooling Methods 0.000 claims abstract description 20
- 239000007769 metal material Substances 0.000 claims abstract description 17
- 239000002699 waste material Substances 0.000 claims abstract description 15
- 238000000926 separation method Methods 0.000 claims description 57
- 230000005484 gravity Effects 0.000 claims description 42
- 239000007788 liquid Substances 0.000 claims description 32
- 229910052751 metal Inorganic materials 0.000 claims description 29
- 239000002184 metal Substances 0.000 claims description 28
- 238000001035 drying Methods 0.000 claims description 19
- 239000000203 mixture Substances 0.000 claims description 19
- 238000005406 washing Methods 0.000 claims description 16
- NTHWMYGWWRZVTN-UHFFFAOYSA-N sodium silicate Chemical compound [Na+].[Na+].[O-][Si]([O-])=O NTHWMYGWWRZVTN-UHFFFAOYSA-N 0.000 claims description 15
- 239000002612 dispersion medium Substances 0.000 claims description 14
- 235000019353 potassium silicate Nutrition 0.000 claims description 14
- 238000005520 cutting process Methods 0.000 claims description 12
- 239000002923 metal particle Substances 0.000 claims description 9
- 238000004064 recycling Methods 0.000 claims description 9
- 239000010419 fine particle Substances 0.000 claims description 6
- 238000012545 processing Methods 0.000 claims description 6
- 238000007885 magnetic separation Methods 0.000 claims description 5
- 238000007667 floating Methods 0.000 claims description 4
- 238000003672 processing method Methods 0.000 claims description 4
- 239000000805 composite resin Substances 0.000 claims description 3
- 239000000696 magnetic material Substances 0.000 claims description 3
- 230000000694 effects Effects 0.000 claims description 2
- 239000011802 pulverized particle Substances 0.000 claims 2
- 229910000831 Steel Inorganic materials 0.000 claims 1
- 239000000470 constituent Substances 0.000 claims 1
- 238000007599 discharging Methods 0.000 claims 1
- 238000012958 reprocessing Methods 0.000 claims 1
- 238000004062 sedimentation Methods 0.000 claims 1
- 238000007873 sieving Methods 0.000 claims 1
- 239000010959 steel Substances 0.000 claims 1
- 239000006148 magnetic separator Substances 0.000 abstract description 3
- 239000010935 stainless steel Substances 0.000 abstract description 2
- 229910001220 stainless steel Inorganic materials 0.000 abstract description 2
- 239000008188 pellet Substances 0.000 abstract 1
- 238000004140 cleaning Methods 0.000 description 14
- 239000002609 medium Substances 0.000 description 7
- 238000000465 moulding Methods 0.000 description 5
- 239000000843 powder Substances 0.000 description 5
- 238000011084 recovery Methods 0.000 description 5
- 239000011362 coarse particle Substances 0.000 description 4
- 229910000838 Al alloy Inorganic materials 0.000 description 3
- 229920000122 acrylonitrile butadiene styrene Polymers 0.000 description 3
- 239000000498 cooling water Substances 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 150000002739 metals Chemical class 0.000 description 3
- 239000011342 resin composition Substances 0.000 description 3
- 238000003756 stirring Methods 0.000 description 3
- 229910000640 Fe alloy Inorganic materials 0.000 description 2
- 238000013019 agitation Methods 0.000 description 2
- 238000007664 blowing Methods 0.000 description 2
- 238000011109 contamination Methods 0.000 description 2
- 239000011162 core material Substances 0.000 description 2
- 239000000428 dust Substances 0.000 description 2
- 238000000605 extraction Methods 0.000 description 2
- 238000010992 reflux Methods 0.000 description 2
- 239000003507 refrigerant Substances 0.000 description 2
- 238000003860 storage Methods 0.000 description 2
- 239000002344 surface layer Substances 0.000 description 2
- KZBUYRJDOAKODT-UHFFFAOYSA-N Chlorine Chemical compound ClCl KZBUYRJDOAKODT-UHFFFAOYSA-N 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- 239000004115 Sodium Silicate Substances 0.000 description 1
- BZHJMEDXRYGGRV-UHFFFAOYSA-N Vinyl chloride Chemical compound ClC=C BZHJMEDXRYGGRV-UHFFFAOYSA-N 0.000 description 1
- 239000004676 acrylonitrile butadiene styrene Substances 0.000 description 1
- 238000003287 bathing Methods 0.000 description 1
- 239000010786 composite waste Substances 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010949 copper Substances 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 230000018109 developmental process Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- NBVXSUQYWXRMNV-UHFFFAOYSA-N fluoromethane Chemical compound FC NBVXSUQYWXRMNV-UHFFFAOYSA-N 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000002844 melting Methods 0.000 description 1
- 230000008018 melting Effects 0.000 description 1
- 230000003472 neutralizing effect Effects 0.000 description 1
- 238000010979 pH adjustment Methods 0.000 description 1
- 230000002093 peripheral effect Effects 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 238000010298 pulverizing process Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000005057 refrigeration Methods 0.000 description 1
- 230000003014 reinforcing effect Effects 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 238000009958 sewing Methods 0.000 description 1
- 229910052911 sodium silicate Inorganic materials 0.000 description 1
- 239000011882 ultra-fine particle Substances 0.000 description 1
- 238000005303 weighing Methods 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/02—Separating plastics from other materials
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/04—Disintegrating plastics, e.g. by milling
- B29B17/0404—Disintegrating plastics, e.g. by milling to powder
- B29B17/0408—Disintegrating plastics, e.g. by milling to powder using cryogenic systems
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/04—Disintegrating plastics, e.g. by milling
- B29B17/0412—Disintegrating plastics, e.g. by milling to large particles, e.g. beads, granules, flakes, slices
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/02—Separating plastics from other materials
- B29B2017/0213—Specific separating techniques
- B29B2017/0217—Mechanical separating techniques; devices therefor
- B29B2017/0224—Screens, sieves
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/02—Separating plastics from other materials
- B29B2017/0213—Specific separating techniques
- B29B2017/0268—Separation of metals
- B29B2017/0272—Magnetic separation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29K—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES B29B, B29C OR B29D, RELATING TO MOULDING MATERIALS OR TO MATERIALS FOR MOULDS, REINFORCEMENTS, FILLERS OR PREFORMED PARTS, e.g. INSERTS
- B29K2705/00—Use of metals, their alloys or their compounds, for preformed parts, e.g. for inserts
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29K—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES B29B, B29C OR B29D, RELATING TO MOULDING MATERIALS OR TO MATERIALS FOR MOULDS, REINFORCEMENTS, FILLERS OR PREFORMED PARTS, e.g. INSERTS
- B29K2705/00—Use of metals, their alloys or their compounds, for preformed parts, e.g. for inserts
- B29K2705/08—Transition metals
- B29K2705/12—Iron
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/52—Mechanical processing of waste for the recovery of materials, e.g. crushing, shredding, separation or disassembly
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/62—Plastics recycling; Rubber recycling
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Mechanical Engineering (AREA)
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
- Processing Of Solid Wastes (AREA)
- Processing And Handling Of Plastics And Other Materials For Molding In General (AREA)
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は金属材と樹脂材とから成る複合材廃品を分離破
砕して両材料共に再利用可能に回収処理する方法並びに
その装置に関する。DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a method and an apparatus for separating and crushing a composite waste product made of a metal material and a resin material so that both materials can be reused.
近年自動車産業における金属と樹脂の複合材料の使用率
が高くなるに従い廃棄される複合材の量もまた著しく増
大し、その処理が社会問題化するほどに至っているが、
それらの再生処理は殆んど行われていない実状にある。In recent years, as the usage rate of composite materials of metal and resin has increased in the automobile industry, the amount of composite materials being discarded has also increased significantly, to the extent that its disposal has become a social issue.
In reality, these regeneration processes are hardly performed.
上記複合材を焼却処理により金属材を回収しようとする
場合にはPVc樹脂から発生する塩素ガスのために公害
対策設備等積々の障害を克服しなければならぬ。更に粉
砕による分離方法にしても経済性や分離性能の面でその
回収処理を困難にしている。従って廃棄複合材の回収率
の良い再生処理方法の開発が待望されている現状となっ
ている。When attempting to recover metal materials from the above-mentioned composite materials by incineration, it is necessary to overcome numerous obstacles such as pollution prevention equipment due to the chlorine gas generated from the PVc resin. Furthermore, even if a separation method using pulverization is used, recovery processing becomes difficult in terms of economy and separation performance. Therefore, the development of a recycling treatment method with a high recovery rate for waste composite materials is currently desired.
本発明の目的は金属材と樹脂材から成る一体化成形複合
材の廃材から個々の金属並びに樹脂材料を高収率を以っ
て再生可能に回収する再生処理方法並びにその装置を提
供しようとすることにある。An object of the present invention is to provide a recycling method and apparatus for recovering individual metals and resin materials with high yield from waste materials of integrally molded composite materials consisting of metal materials and resin materials. There is a particular thing.
上記回収処理方法は廃棄複合材料を予め所望の大いさに
細断し、更にこれを粉砕機にかけて細粒化し金属粒子群
と樹脂粒子群とが分離混在する混合生成物を得る場合に
前記細断した複合材料塊を前辺って樹脂材の脆化温度以
下に冷却して、樹脂材部分を金属材部分から剥離し易い
低温冷却状態に保持してこれを微粉化する点が重要とな
る。The above-mentioned recovery processing method involves shredding the waste composite material in advance to a desired size, and then crushing it into fine particles using a pulverizer to obtain a mixed product in which metal particles and resin particles are separated and mixed. It is important to cool the resulting composite material mass to a temperature below the embrittlement temperature of the resin material, maintain it at a low temperature in which the resin material part can easily separate from the metal material part, and then pulverize it.
前記複合材の金属部分が磁性金属例えば鉄合金の場合に
は回収再生すべき樹脂材料粒子群中の金属粉混入を最小
限に止めると同時に、回収金属部分の品質を高めるため
磁力選別手段を用いて磁性金属粒子群を分離回収するこ
とである。また複合材がアルミ合金等の非磁性金属から
成る場合に、上記粒状化生成混合物は特定の比重を有す
る液体を分散媒体として樹脂材および非磁性金属材の固
有の比重差を利用して各別に分離選別する手段が取られ
る。上記比重差利用の分離手段はまた複数種類の樹脂材
料からなる各組成樹脂材料粒子群に対しても適用しよう
とするものである。When the metal part of the composite material is a magnetic metal, such as an iron alloy, a magnetic separation means is used to minimize metal powder contamination in the resin material particle group to be recovered and recycled, and at the same time to improve the quality of the recovered metal part. The method is to separate and collect magnetic metal particles. In addition, when the composite material is made of a non-magnetic metal such as an aluminum alloy, the above-mentioned granulated mixture is separated by using a liquid having a specific specific gravity as a dispersion medium and utilizing the specific gravity difference between the resin material and the non-magnetic metal material. Separation and sorting measures are taken. The above-mentioned separation means using the difference in specific gravity is also intended to be applied to each composition resin material particle group consisting of a plurality of types of resin materials.
本発明に係る廃棄複合材の回収処理方法およびその装置
は下記工程および装置から成る。The waste composite material collection and treatment method and apparatus thereof according to the present invention consist of the following steps and apparatus.
該方法は廃棄処分になった金属材と樹脂材から成る複合
材を適宜の大いさに細断して塊状化し、これを低温冷却
装置において複合樹脂材の脆化温度例えば−40゛以下
に冷却して複合材中の付着樹脂部分を衝撃作用により金
属部分から剥離し易い状態に保持し、この脆化温度状態
にある複合材を衝撃湿粉砕機に投入して微粒化混合生成
物を得る。This method involves cutting a composite material made of discarded metal materials and resin materials into pieces of appropriate size and forming them into chunks, which are then cooled in a low-temperature cooling device to below the brittle temperature of the composite resin material, for example -40 degrees. The adhering resin portion in the composite material is maintained in a state where it is easily peeled off from the metal portion by impact action, and the composite material in the embrittlement temperature state is charged into an impact wet crusher to obtain an atomized mixed product.
次いで上記微粒化された金属と樹脂から成る混合生成物
を磁力分離装置又は比重差分離装置に移送して金属粒子
群と樹脂粒子群に分離選別し、最終的に前記選別分離さ
れた各粒子群を個別的に設置された洗浄槽に移送されて
水洗され、乾燥装置に導びかれ乾燥後にて高品位の再生
樹脂材と金属材とが共に連続的に処理回収されるように
した方法及び装置となっている。廃棄複合材の金属が鉄
合金等の磁性材料を含む場合においては勿論磁力分離装
置を殊用するのが好ましい。Next, the mixed product consisting of the atomized metal and resin is transferred to a magnetic separation device or a specific gravity separation device to be separated and sorted into a metal particle group and a resin particle group, and finally each of the separated particle groups is separated. A method and apparatus in which high-grade recycled resin materials and metal materials are continuously processed and recovered after being transferred to a separately installed washing tank, washed with water, guided to a drying device, and dried. It becomes. Of course, when the metal of the waste composite material contains a magnetic material such as an iron alloy, it is preferable to use a magnetic separator.
また廃棄複合材中の金属がアルミ合金等の非磁性金属で
ある場合には樹脂の比重と非磁性金属の比重差を利用す
る比重差分離槽によって両者を分離抽出する。この比重
差分離槽は磁性金属を含む混合粒子群にも適用しうろこ
とはいうまでもない。If the metal in the waste composite material is a non-magnetic metal such as an aluminum alloy, both are separated and extracted using a specific gravity separation tank that utilizes the difference in specific gravity between the resin and the non-magnetic metal. It goes without saying that this specific gravity separation tank can also be applied to mixed particle groups containing magnetic metals.
更に廃棄複合材を構成する樹脂材が2種類以−ヒの異種
の組成樹脂を含む場合には、これら異種の組成樹脂材料
を各々別個に分離選別する方法も前述した比重差分離槽
を適用して遂行される。Furthermore, when the resin materials constituting the waste composite material include two or more different types of resin compositions, the above-described specific gravity separation tank can also be used to separately separate and sort these different types of resin compositions. will be carried out.
前記比重差分離法において、好ましくは水ガラス(珪酸
ソーダ)を分離分散媒体液即ち重液として使用し、該水
ガラス溶液の比重は異種組成樹脂材料の各比重値の中間
値に調整して設定される。In the specific gravity difference separation method, water glass (sodium silicate) is preferably used as a separation and dispersion medium liquid, that is, a heavy liquid, and the specific gravity of the water glass solution is adjusted and set to an intermediate value between the specific gravity values of the resin materials of different compositions. be done.
更に前記方法を実施する装置は金属材と樹脂材からなる
廃棄された複合材を所望の寸法サイズに細断すべき短尺
切断装置と、該短尺小塊化された複合材を含有樹脂材の
脆化温度以下に低温冷却するための脆化温度冷却装置と
、前記脆化温度状態において小塊化複合材を衝撃剥離す
るための衝撃形粉砕装置と、前記粉砕された微粒混合物
から金属及び樹脂材を分離選別するための分離選別装置
と、分離選別された各別個の金属粒子群および樹脂粒子
群を個別に洗浄する洗浄槽および水洗洗浄した各粒子群
を乾燥する乾燥設置を各々具備し、これら各装置間には
それぞれコンベア等の移送手段が設置されて、廃棄複合
材の短尺化切断から再生処理工程が連続的に、行なわれ
る連続的流れ方式による複合材再生処理装置となってい
る。前記金属と樹脂粒子混合物の分離選別装置は磁性金
属材の場合には特に磁力分離装置を採用するのが好しい
。Furthermore, the apparatus for carrying out the method includes a short cutting apparatus for cutting the discarded composite material made of metal material and resin material into desired size, and a short cutting device for cutting the waste composite material made of metal material and resin material into pieces, and a short cutting device for cutting the composite material into small pieces into short pieces. an embrittlement temperature cooling device for cooling to a temperature below the embrittlement temperature; an impact type crushing device for impact peeling the agglomerated composite material in the embrittlement temperature state; and a metal and resin material from the pulverized fine particle mixture. It is equipped with a separation and sorting device for separating and sorting, a washing tank for individually washing each separated metal particle group and resin particle group, and a drying installation for drying each particle group that has been washed with water. Transfer means such as conveyors are installed between each device, and the device is a composite material recycling device using a continuous flow system, in which the recycling process from cutting the waste composite material into short lengths is performed continuously. As the device for separating and sorting the metal and resin particle mixture, particularly in the case of magnetic metal materials, it is preferable to employ a magnetic separation device.
またアルミ合金等の非磁性金属を含む場合における分離
選別手段は特定の比重を有する媒体液を分散相とする比
重差分離装置によって達成される。Separation and sorting means when a non-magnetic metal such as an aluminum alloy is included is achieved by a specific gravity difference separation device using a medium liquid having a specific specific gravity as a dispersed phase.
前記比重差分離装置は複合材を構成する樹脂材が2種以
上の性質の異なる異種組成樹脂材から成る場合において
それらの分離選別装置として使用することができる。以
下図面に示す実施例に従って本発明を説明する。The specific gravity difference separation device can be used as a separating and sorting device when the resin materials constituting the composite material are composed of two or more different resin materials having different properties. The present invention will be described below according to embodiments shown in the drawings.
〔実施例〕
第1図は本発明に係る処理方法と装置の工程流れを概略
的に示す線図である。該線図は自動車ガラス窓シール用
のモール部品廃材を処理再生するための実施例として示
される。上記モール部品は不銹鋼を補強芯材として成形
され、これを取巻いてアクリルニトリルブタジェンスチ
レン(ABS)樹脂および塩化ビニール(P V C)
樹脂が適所に配置成形された長尺状のシール部品である
。該モール廃材は第1図左側に示す適宜の切断装置1に
より約5011の長さに細断される。細断小塊化された
複合材はコンベア2を経て投入ホッパ3内に貯溜される
。ホッパ3には調節可能な定量排出器4が付属し、常時
定量の小塊化複合材をホッパ移送フィーダ5側へ送り込
む。更に移送フィーダ5を経てマグネット式昇降コンベ
ア6により高所位置に揚上された複合材は計量回転弁8
を具備する重力式スライドシュート7を通って低温冷却
装置10に導入される。該冷却装置10は小塊化複合材
の樹脂部分を樹脂脆化温度約−40℃以下に冷却せしめ
るための装置であり、樹脂材料の低/IA脆弱化により
金属材に付着成形されていた樹脂材を衝撃剥離作用によ
り効果的に金属部分から分離することができる。低温冷
媒としてはフロンガスが採用される。冷却装置10は内
部雰囲気を常時−40℃以下に保持された大容量空間を
もつ冷却庫15を主体として設備される。計量回転弁8
を含む冷却庫15の全外周面には厚み約15(hmの断
熱材が被覆装された常温度状態にある複合材料塊は該コ
ンベアを通過する間に冷却庫内部の低温度雰囲気により
漸次冷却され、右Mの排出口において〜40゜ある。1
4は庫内部ファンである。冷却庫15内の天井壁には複
数個の冷却送風ユニット12が各別に設備され、該送風
ユニソ)12は配管を通して各冷凍機13に連結される
。冷凍機13はフロンガスを冷媒として作動する冷凍ユ
ニットで、符号Mは電動機である。符号16,16′、
17.+1+は冷凍機13の凝縮器の冷却水循環系を示
し、これらの配管は冷却塔19に付属するものとなって
いる。該冷却塔19の内部は浮子18により一定水位に
保持され、冷却水ポンプ17、共通送水管16を経て各
冷凍機13の凝縮器に冷却水を供給し、該凝縮器におい
て吸熱した高温水は戻り管16′を経て冷却塔19内上
部空間に噴射しファンにより放熱冷却される。上記移送
冷却シリンダ11は駆動モータ9により減速歯車段を介
して回転駆動される。[Example] FIG. 1 is a diagram schematically showing the process flow of the processing method and apparatus according to the present invention. The diagram is shown as an example for processing and recycling molding part waste material for automobile glass window seals. The above molding parts are molded using stainless steel as a reinforcing core material, which is surrounded by acrylonitrile butadiene styrene (ABS) resin and vinyl chloride (PVC).
It is a long sealing part that is molded with resin placed in the appropriate places. The molding waste material is shredded into lengths of about 5011 by a suitable cutting device 1 shown on the left side of FIG. The shredded composite material is stored in a charging hopper 3 via a conveyor 2. The hopper 3 is attached with an adjustable metering discharger 4, which constantly feeds a fixed amount of agglomerated composite material to the hopper transfer feeder 5 side. Furthermore, the composite material, which has passed through the transfer feeder 5 and is lifted to a high position by the magnetic lifting conveyor 6, is transferred to a metering rotary valve 8.
is introduced into the cryogenic cooling device 10 through a gravity-type slide chute 7 equipped with a. The cooling device 10 is a device for cooling the resin part of the agglomerated composite material to the resin embrittlement temperature of about -40°C or lower, and the resin that has been adhered and molded to the metal material due to the low/IA embrittlement of the resin material. The material can be effectively separated from the metal part by impact peeling action. Freon gas is used as the low-temperature refrigerant. The cooling device 10 is mainly equipped with a cooling store 15 having a large capacity space in which the internal atmosphere is always maintained at −40° C. or lower. Metering rotary valve 8
The entire outer circumferential surface of the cooling chamber 15 including and is ~40° at the right M outlet.1
4 is a fan inside the refrigerator. A plurality of cooling air blowing units 12 are individually installed on the ceiling wall of the refrigerator 15, and the air blowing units 12 are connected to each refrigerator 13 through piping. The refrigerator 13 is a refrigeration unit that operates using fluorocarbon gas as a refrigerant, and symbol M is an electric motor. Code 16, 16',
17. +1+ indicates a cooling water circulation system for the condenser of the refrigerator 13, and these pipes are attached to the cooling tower 19. The inside of the cooling tower 19 is maintained at a constant water level by a float 18, and cooling water is supplied to the condenser of each refrigerator 13 via a cooling water pump 17 and a common water pipe 16, and the high temperature water that has absorbed heat in the condenser is It is injected into the upper space of the cooling tower 19 through the return pipe 16' and is radiated and cooled by a fan. The transfer cooling cylinder 11 is rotationally driven by a drive motor 9 through a reduction gear stage.
計量回転弁8を通ってスライドシュート7の出口から定
量宛落下供給された小塊化複合材は冷却シリンダ11を
左から右へ漸次攪拌移送される間に低温雰囲気内に約2
0分乃至30分曝されその出口において樹脂材の脆化温
度−40’c以下に冷却される。次いで上記脆化温度以
下に冷却された小塊化複合材はハンマーミル等の衝撃形
粉砕装ff20に投入される。22は粉砕装置20の装
入口に設けたホッパで、21は計量回転弁である。単位
時間当り一定量宛送り込まれた小塊化複合材は回転ハン
マーにより粉砕され、約3〜10メソシユ範囲の粗粒以
下の微粒子粉末を含む粒状化混合生成物が得られる。The agglomerated composite material, which is supplied in a fixed amount from the exit of the slide chute 7 through the metering rotary valve 8, is gradually stirred and transferred from left to right through the cooling cylinder 11, while being transferred into a low-temperature atmosphere for about 2 hours.
The resin material is exposed for 0 to 30 minutes and cooled to below the embrittlement temperature of the resin material -40'C at the exit. Next, the agglomerated composite material cooled to below the embrittlement temperature is placed into an impact crushing device ff20 such as a hammer mill. 22 is a hopper provided at the charging port of the crushing device 20, and 21 is a metering rotary valve. The agglomerated composite material fed in a fixed amount per unit time is pulverized by a rotating hammer to obtain a granulated mixed product containing fine powder of coarse particles or less in the range of about 3 to 10 mesos.
次いで前記モール部品の如き不銹調芯材を含む金属材と
樹脂粒子とから成る混合生成物は分離コンベア31と振
動篩分機34からなる分#選別装置3oに導びかれ、金
属部分と樹脂部分が分離抽出される。Next, the mixed product consisting of a metal material containing a rust-proof core material such as the molding part and resin particles is led to a separating device 3o consisting of a separation conveyor 31 and a vibrating sieve 34, and is separated into metal parts and resin parts. are separated and extracted.
即ち上記分離コンベア31上に送り込まれた粉砕混合物
は該分離コンベアの走行通路上に配置された複数個の磁
力分離器32により不銹銅粒子部分が吸引除去されて、
その下方に配置した金属片回収箱33内に落下捕捉され
ると共に残余の樹脂粒子部分は振動篩分量34に送り出
されて、3メソシユ(約粒に分級選別される。通常10
%程度の粗粒樹脂部分は右側粗粒口36を経て粗粒樹脂
分離容器37に回収され、90%に達する大部分の細粒
子部分は左側細粒口35から取り出される。このように
して分離抽出された金属片部分は、再生原料として回収
され、また細粒樹脂部分は後述する水洗いによる洗浄装
置および乾燥装置においてそれぞれ洗浄され、乾燥され
て粒状再生品として処理回収される。細粒樹脂部分とし
て分離選別された微粉末を含む樹脂部分は更にサイクロ
ンユニットに移送され、超微粒子ダスト部分は粉末再生
品として回収され袋詰めされサイクロンユニットにおい
て捕捉された残余の約90%の比較的粒子サイズの粗い
細粒樹脂部分は前記の洗浄、乾燥処理工程を経て回収再
生品として袋詰めにされる。That is, the pulverized mixture fed onto the separation conveyor 31 has the non-rusting copper particles removed by suction by a plurality of magnetic separators 32 arranged on the running path of the separation conveyor.
The remaining resin particles fall into a metal piece collection box 33 placed below and are captured, and the remaining resin particles are sent to a vibrating sieve 34 where they are classified into 3 particles (usually 10 particles).
% of the coarse particles are collected into the coarse resin separation container 37 through the right coarse particle port 36, and most of the fine particle portions, which reach 90%, are taken out from the left fine particle port 35. The metal pieces separated and extracted in this way are recovered as recycled raw materials, and the fine resin particles are washed and dried in a water washing device and a drying device, which will be described later, and processed and recovered as granular recycled products. . The resin part containing fine powder separated and sorted as a fine resin part is further transferred to a cyclone unit, and the ultrafine particulate dust part is collected as a recycled powder product and packed in bags, which makes up about 90% of the residue captured in the cyclone unit. The fine resin particles with a coarse particle size are subjected to the above-mentioned washing and drying process and then packed into bags as recovered recycled products.
前述した樹脂粒子の再生回収処理は複合材を構成する樹
脂材が単一種類の樹脂組成分から成るものについて述べ
たが、前述したモール部品のようにABS樹脂とpvc
樹脂の2種の樹脂が部分的槽成として使用されている複
合材に対しては重液を分散媒液とする比重差分離装置を
用いて行なうことができる。第1図の下半部分に該装置
を示す。The above-mentioned recycling and recovery treatment of resin particles has been described for cases in which the resin material constituting the composite material consists of a single type of resin composition, but like the molding parts mentioned above, ABS resin and PVC
For composite materials in which two types of resins are used as a partial tank composition, a specific gravity separation device using a heavy liquid as a dispersion medium can be used. The device is shown in the lower half of FIG.
もし上記複合材を構成する樹脂材部分が異なる比重値を
有して部分的にそれぞれ成形されている場合に適用可能
となる。勿論この比重差利用の分離抽出方法は金属粒子
を包含する混合粒子群に適用可能なことはいうまでもな
い。説明を分り易くするため2種類の樹脂粒子混合物の
組成成分抽出について以下説明する。粉砕機20によっ
て剥離破砕された粒子混合物は空気ブロワ等の移送手段
を介して移送管39を通って分離槽41のためのサイク
ロン分離器42に達する。サイクロン分離器42におい
てサイクロン42で分離捕集しにくい超微粒子を含む微
粒部分はダストとして上方から分離排出してバッグフィ
ルターにて回収し、下方部分から粉粒を除去した粒子群
を分離槽41の攪拌貯溜室43に投下装入する。分離槽
41は稀釈水ガラスを重液として分散媒体相が形成され
、稀釈水ガラスの比重を上記2種の樹脂材料比重値の例
えば耐衝撃用ABSの比重を1.04、pvc樹脂の比
重を1.25とすればそれら中間0比重値の1.15に
調節設定される。This method can be applied if the resin material parts constituting the composite material are partially molded with different specific gravity values. Needless to say, this separation and extraction method using the difference in specific gravity can be applied to a mixed particle group including metal particles. In order to make the explanation easier to understand, extraction of the compositional components of the two types of resin particle mixture will be described below. The particle mixture exfoliated and crushed by the crusher 20 passes through a transfer pipe 39 via a transfer means such as an air blower and reaches a cyclone separator 42 for a separation tank 41 . In the cyclone separator 42 , the fine part containing ultrafine particles that are difficult to separate and collect in the cyclone 42 is separated and discharged as dust from above and collected by a bag filter. It is dropped and charged into the stirring storage chamber 43. In the separation tank 41, a dispersion medium phase is formed using diluted water glass as a heavy liquid. If it is set to 1.25, the specific gravity is adjusted to 1.15, which is the intermediate zero specific gravity value.
従って上記重液より比重の大なるpvc樹脂粒子は沈潜
して下部に浮遊沈降し、小なる比重値をもつABS樹脂
粒子は上部表層に浮上する。分散媒体中に均一に攪拌さ
れた粒子混合物は分離槽41の中間側壁部に開口する周
面開口を通って分離槽下方部に常時供給される。44は
分離槽41の側壁上部外周に設けた浮上粒子捕捉のため
の溢流樋であって、該溢流樋44に対面する分離槽側壁
上辺には一部を切込んだ溢流堰が形成されている。従っ
て軽比重の浮上樹脂粒子は溢流堰を越えて溢流樋44内
に流下する。更に該溢流樋44の底部に連結された流出
管を通って水切りスクリーンフィーダ47上に流下する
。該スクリーンフィーダ47は軽比重樹脂粒子を含んで
溢流流出した分散媒体液を水切り分離して該重液媒体を
循環槽100に戻して再使用を可能にすると共に上記重
液で濡れた粒子群を洗浄槽60に送り込んで水洗いし該
粒子群を再生利用可能にするものである。洗浄槽60は
水道管等の洗浄水源から導水管63を通して常時洗浄水
が供給され、スクリーンフィーダ47を経て投入された
被洗浄樹脂粒子群は電動機Mによる攪拌回転翼により攪
拌洗浄作用をうけ、次いで洗浄槽60の上部周壁に設け
た溢流堰(図示しない)を越えて溢れ出る。この溢流堰
は洗浄槽内水位を一定水位に保持する。Therefore, PVC resin particles having a higher specific gravity than the heavy liquid sink and float to the bottom, and ABS resin particles having a smaller specific gravity float to the upper surface layer. The particle mixture uniformly stirred in the dispersion medium is constantly supplied to the lower part of the separation tank 41 through a circumferential opening in the middle side wall of the separation tank 41. Reference numeral 44 denotes an overflow gutter for capturing floating particles provided on the outer periphery of the upper part of the side wall of the separation tank 41, and an overflow weir with a portion cut out is formed on the upper side of the side wall of the separation tank facing the overflow gutter 44. has been done. Therefore, the floating resin particles having a light specific gravity flow down into the overflow gutter 44 over the overflow weir. The water then flows down onto the drain screen feeder 47 through an outflow pipe connected to the bottom of the overflow gutter 44 . The screen feeder 47 drains and separates the overflowing dispersion medium containing light specific gravity resin particles, returns the heavy liquid medium to the circulation tank 100 to enable reuse, and collects particles wetted with the heavy liquid. The particles are sent to a cleaning tank 60 and washed with water, thereby making the particles recyclable. The cleaning tank 60 is constantly supplied with cleaning water from a cleaning water source such as a water pipe through a water conduit 63, and the group of resin particles to be cleaned fed through the screen feeder 47 is subjected to an agitation cleaning action by an agitation rotor driven by an electric motor M, and then The water overflows over an overflow weir (not shown) provided on the upper peripheral wall of the cleaning tank 60. This overflow weir maintains the water level in the cleaning tank at a constant level.
上記洗浄槽60から溢流放出された洗浄された粒状樹脂
部分は溢流洗浄水に浮遊して放流管61を通って第2の
水切りスクリーンフィーダ65において洗浄水のみが落
下除外される。かくして水洗い処理を完了した樹脂粒子
群は投入コンベア66を経て乾燥装置70に移送される
。該乾燥装置70は水洗い処理後樹脂粒子を熱風等の加
熱乾燥により付着した水分を完全に除去して再生利用可
能な粒子群として回収するものであるから、従来慣用の
乾燥設備を適用しうる。従って第1図には乾燥装置70
の具体的構造は省略して図示しているが、この設備例に
おいては加熱蒸気によって乾燥室75の内部は所定の高
温雰囲気に保持されると共に水切りされた樹脂粒子群は
回転移送チューブ72内を通って排出ロア3に移送され
、清浄化された乾燥樹脂粒子は集収ホッパ74に貯溜さ
れる。集収ホッパ74に貯溜した樹脂粒は実際上は更に
空気移送用ブロワを介して大容量の製品ホッパ内に貯溜
され、付属の下部計量機により一定量毎に袋詰めミシン
掛けの後、再生粒状樹脂製品として出荷される。The washed granular resin parts overflowing from the washing tank 60 float in the overflowing washing water, pass through the discharge pipe 61, and fall into the second drain screen feeder 65 where only the washing water is removed. The resin particles that have been washed with water in this manner are transferred to the drying device 70 via the input conveyor 66. Since the drying device 70 completely removes attached moisture from the resin particles after washing with water by heating and drying them with hot air or the like, and recovers the resin particles as a recyclable particle group, conventional drying equipment can be used. Therefore, the drying device 70 is shown in FIG.
Although the specific structure is omitted in the drawing, in this equipment example, the interior of the drying chamber 75 is maintained at a predetermined high temperature atmosphere by heated steam, and the drained resin particles are transported inside the rotary transfer tube 72. The cleaned dry resin particles are transferred to the discharge lower 3 and stored in the collection hopper 74. The resin granules stored in the collection hopper 74 are actually further stored in a large-capacity product hopper via an air transfer blower, and after being packed into bags in fixed amounts using an attached lower weighing machine and run through a sewing machine, recycled granular resin is produced. Shipped as a product.
以上の説明は分離槽41の液面上層部に浮上した軽量樹
脂粒子の水洗い乾燥処理工程を説明したが、分離槽41
の底部に沈降堆積した比重の大なる異種樹脂粒子群に対
する洗浄・乾燥処理も前述のものと殆んど同様にして完
遂される。即ち分散媒体液である規定の水ガラス比重よ
り大なる異種の樹脂粒子群は時間と共に当然に分離槽4
1の底部に向って沈降堆積する。この比較的比重の大な
る樹脂粒子を分離槽底部からその外側上部に引出すため
に攪拌槽43の左側に落差タンク45が設置される。該
落差タンク45内に設けた浴出口46の高さ位置は分離
槽41の液面より低い位置に選定されている。従って分
離槽41内の分散媒体液は最底部流出開口からの落差管
47を通って、浴出口46からその水頭差に対応する流
速を以って常時噴水する。この浴出噴水流は分離槽41
の底部に沈積した比重大なる樹脂粒子を伴って落差タン
ク45内に常時放出される。The above explanation describes the process of washing and drying the lightweight resin particles floating on the upper part of the liquid surface of the separation tank 41.
The cleaning and drying treatment for the group of different types of resin particles having a large specific gravity that have settled and accumulated at the bottom of the container is completed in almost the same manner as described above. In other words, different kinds of resin particles having a specific gravity larger than the specified water glass, which is the dispersion medium liquid, naturally fall into the separation tank 4 over time.
It settles and accumulates toward the bottom of 1. A drop tank 45 is installed on the left side of the stirring tank 43 in order to draw out the resin particles having a relatively large specific gravity from the bottom of the separation tank to the upper part of the outside thereof. The height of the bath outlet 46 provided in the drop tank 45 is selected to be lower than the liquid level of the separation tank 41. Therefore, the dispersion medium liquid in the separation tank 41 passes through the drop pipe 47 from the bottom outflow opening and is constantly jetted from the bath outlet 46 at a flow rate corresponding to the water head difference. This bathing fountain flow is in the separation tank 41.
It is constantly discharged into the head tank 45 with resin particles of specific gravity deposited at the bottom of the tank.
この落差タンク45内へ樹脂粒子を伴って放出される分
散媒体流量は浴出口46の開口面積およびその高さ位置
を調節することにより調整可能にされている。落差タン
ク45に放出された高比重樹脂粒子を含む分散媒体液は
流出導管48を通って水切りスクリーンフィーダ49を
流下する間にその媒体液を水切りした後高比重樹脂粒子
用洗浄槽80に投入され、清水による洗浄作用を受ける
。次いで乾燥処理を受けて再生製品化されることは前述
した低比重樹脂粒子の場合と殆んど同じように遂行され
る。The flow rate of the dispersion medium discharged together with the resin particles into the drop tank 45 can be adjusted by adjusting the opening area of the bath outlet 46 and its height position. The dispersion medium liquid containing the high specific gravity resin particles discharged into the drop tank 45 is drained while flowing down the drain screen feeder 49 through the outflow conduit 48 and is then charged into the cleaning tank 80 for high specific gravity resin particles. , subjected to the cleaning action of fresh water. Subsequently, the drying process is carried out to produce a recycled product in almost the same manner as in the case of the low specific gravity resin particles described above.
従って洗浄槽80以降の処理工程は図示符号の説明だけ
に止める。81は洗浄樹脂粒子を含む洗浄水の設備90
へ送り込むための投入コンベアである。以上は本発明に
関連する粉砕微粒子群に対する比重差分離選別装置の基
本部分を構成している。次いで上記分離槽の付属的設備
について説明する。符号100は分離槽内分散媒体液即
ちこの場合水ガラス液を重液として使用するが、その水
ガラス液循環槽である。所望の規定比重値に設置された
水ガラス液が循環槽100内に満される。この水ガラス
液は水ガラス熔解槽110から移送ポンプ111により
供給される。レベルスイッチ10’7が循環槽100内
に設備され、規定水位以下になるとレベルスイッチIO
Tが作動し移送ポンプ111を始動し規定比重値に設定
された水ガラス液が自動的に補給される。また循環槽1
00の上部には還流溢流堰102゜103が設けられる
。これらの溢流堰102 、103は媒体重液用スクリ
ーンフィーダ49および47で水切りされた水ガラス液
媒体が還流管104 、105を経て流下し、この溢流
堰においてその表層部を流下する媒体液を循環槽100
内に溢流帰還せしめて再使用を計る。101は水ガラス
液循環ポンプで媒体液移送導管106を通して攪拌貯溜
槽43内に媒体液を連続的に供給するようにしている。Therefore, the processing steps after the cleaning tank 80 will be explained only by the reference numerals. 81 is a cleaning water equipment 90 containing cleaning resin particles.
This is an input conveyor for sending the materials to the The above constitutes the basic part of a specific gravity separation and sorting apparatus for a group of pulverized fine particles related to the present invention. Next, the auxiliary equipment of the separation tank will be explained. Reference numeral 100 denotes a water glass liquid circulation tank in which a dispersion medium liquid in a separation tank, that is, a water glass liquid is used as a heavy liquid in this case. The circulation tank 100 is filled with water glass liquid set to a desired specified specific gravity value. This water glass liquid is supplied from a water glass melting tank 110 by a transfer pump 111. A level switch 10'7 is installed in the circulation tank 100, and when the water level falls below the specified level, the level switch IO
T is activated, the transfer pump 111 is started, and the water glass liquid set to the specified specific gravity value is automatically replenished. Also, circulation tank 1
At the top of 00, reflux overflow weirs 102 and 103 are provided. These overflow weirs 102 and 103 allow the water glass liquid medium drained by the heavy medium liquid screen feeders 49 and 47 to flow down through the reflux pipes 104 and 105, and the medium liquid flowing down the surface layer at these overflow weirs. circulation tank 100
The overflow will be returned to the tank for reuse. Reference numeral 101 denotes a water glass liquid circulation pump which continuously supplies the medium liquid into the stirring storage tank 43 through the medium liquid transfer conduit 106.
120は水切り槽で、各洗浄槽60 、80で洗浄処理
を連結される。洗浄処理後の処理水は外部に廃棄される
ことになるが、当然水ガラス成分を含むため、図示され
ないその後の工程処理においてpH調整槽に移送され、
中和溶液とされた後廃棄される。Reference numeral 120 denotes a draining tank, and the washing process is connected to each washing tank 60 and 80. The treated water after the cleaning process will be disposed of outside, but since it naturally contains water glass components, it will be transferred to a pH adjustment tank in the subsequent process treatment (not shown).
It is discarded after being made into a neutralizing solution.
本発明による再生製品は樹脂材及び金属材共に材料品質
の低下がなく、特に樹脂に関しては微粉の混入率が少な
く回収率も高く、直ちに再生品として使用可能となる特
徴を有する。また本発明に係る比重差利用による分離方
法は金属および樹脂のいずれに対しても適用可能である
からその適用範囲も広い。また大量生産に適する連続的
再生処理方式を可能とし、資源の再利用並びに公害防止
の一助となる。The recycled product according to the present invention has the characteristics that there is no deterioration in material quality for both resin materials and metal materials, and especially for resin, the contamination rate of fine powder is low and the recovery rate is high, so that it can be used immediately as a recycled product. Furthermore, the separation method using the difference in specific gravity according to the present invention can be applied to both metals and resins, and therefore has a wide range of application. It also enables a continuous recycling process suitable for mass production, helping to reuse resources and prevent pollution.
図面は本発明に係る処理方法をその工程流れに沿って図
解した説明図を示す。
1・・・切断機、 10・・・低温冷却装置
、20・・・衝撃形粉砕機、 30・・・分離選別装置
、34・・・振動篩分機、 40・・・比重差分離装
置、41 、49 、65 、85・・・水切りスクリ
ーンフィーダ、70 、80・・・乾燥設備。The drawings are explanatory diagrams illustrating the processing method according to the present invention along the process flow. DESCRIPTION OF SYMBOLS 1... Cutting machine, 10... Low-temperature cooling device, 20... Impact type crusher, 30... Separation sorting device, 34... Vibrating sieve machine, 40... Specific gravity difference separation device, 41 , 49 , 65 , 85 . . . draining screen feeder, 70 , 80 . . . drying equipment.
Claims (1)
断塊状化する工程と、前記塊状化複合材を該樹脂の脆化
温度以下に低温冷却せしめる冷却工程と、前記脆化温度
状態にある塊状複合材を衝撃粉砕作用により微粒混合物
に粉砕して金属材部分から樹脂材部分を剥離分離せしめ
る分離粉砕工程と、前記分離粉砕された複合材混合粒子
群を金属材と樹脂材とに分離する分離選別工程および前
記選別分離工程により抽出された金属材と樹脂材とをそ
れぞれ洗浄しかつ乾燥する洗浄・乾燥工程とから成る樹
脂、金属複合材の再生処理方法。 2、前記分離選別工程は粉砕粒子混合物を重液分散媒体
中に投入し、それら材料の比重による浮沈分離作用を利
用する比重差分離工程から成る特許請求の範囲第1項記
載の再生処理方法。 3、前記粉砕粒子混合物の分離選別工程は複合材の金属
部分が磁性材から成形される場合において、金属粒に対
して磁力吸引力利用の金属分離工程と樹脂粒に対して振
動篩分工程とから成る特許請求の範囲第1項記載の再生
処理方法。 4、前記複合材の組成樹脂部分が2種類以上の比重の異
なる樹脂材部分から成る場合において、前記金属粒子部
分を取り除いた樹脂粒子混合物に対する分離選別工程は
稀釈水ガラス液等を重液とする分散媒体中に前記樹脂粒
子混合物を投入攪拌してこれら樹脂材の比重差に基づく
浮沈作用により各組成材を各別に分離抽出するようにし
た特許請求の範囲第1項記載の再生処理方法。 5、樹脂と金属から成る廃棄複合材を適宜の大いさに細
断する切断装置と、該小塊化複合材を該樹脂材の脆化温
度以下に低温冷却する複合材冷却装置と、前記脆化温度
状態にある小塊化複合材を剥離分離するための衝撃形粉
砕装置と、該粉砕粒子混合物から樹脂部分と金属部分と
を各別に分離抽出するための混合物分離選別装置及び各
別個に選別抽出された金属粒子群と樹脂粒子群とをそれ
ぞれ洗浄しかつ乾燥する洗浄装置と乾燥設備とを具備す
ると共に前記各装置と設備間にはコンベア等の移送手段
を設けていることを特徴とする金属、樹脂複合材の再生
処理装置。 6、前記混合物分離選別装置は設定された所定の比重値
を有する重液分散媒体により満された比重差分離槽から
成り、該分離槽は前記衝撃形粉砕装置の排出口から移送
手段を介して粉砕生成物が供給されるように配置される
と共に前記分離槽上方に設けた溢流堰を介して軽量樹脂
材が浮上分離可能にされると共に分離槽底部に沈降した
比重値大なる材料を抽出するための溢流口が分離槽底部
開口に連通しかつ分離槽液面より低い位置に設置されて
いる特許請求の範囲第5項記載の再生処理装置。 7、前記複合材の金属部分が鋼材等の磁性材料から成る
場合において、前記分離選別装置は前記粉砕装置の排出
側に磁力分離装置を有する磁力分離コンベアが接続され
、更に該分離コンベアの送出側に金属粒子部分を除去し
た樹脂粒子部分を分級選別するための樹脂用振動篩分装
置が配置されている特許請求の範囲第5項記載の再生処
理装置。[Scope of Claims] 1. A process of cutting a waste composite material made of resin and metal into blocks of appropriate size, and a cooling process of cooling the agglomerated composite material at a low temperature below the embrittlement temperature of the resin; A separation and crushing step of crushing the bulk composite material in the embrittlement temperature state into a fine particle mixture by impact crushing action and peeling and separating the resin material portion from the metal material portion; A method for recycling resin and metal composite materials, comprising a separation and sorting step of separating the metal material and the resin material, and a washing and drying step of washing and drying the metal material and the resin material extracted in the sorting and separation step, respectively. 2. The regeneration processing method according to claim 1, wherein the separation and sorting step comprises a specific gravity difference separation step in which the pulverized particle mixture is introduced into a heavy liquid dispersion medium and a floatation and sedimentation separation effect based on the specific gravity of these materials is utilized. 3. In the case where the metal part of the composite material is formed from a magnetic material, the separation and sorting process of the pulverized particle mixture includes a metal separation process using magnetic attraction force for the metal particles and a vibrating sieving process for the resin particles. A reprocessing method according to claim 1, comprising: 4. Composition of the composite material When the resin part is composed of two or more types of resin parts with different specific gravity, the separation and sorting process for the resin particle mixture from which the metal particle part has been removed uses diluted water glass liquid etc. as a heavy liquid. 2. The regeneration treatment method according to claim 1, wherein the resin particle mixture is introduced into a dispersion medium and stirred, and each constituent material is separately extracted by a floating action based on the difference in specific gravity of these resin materials. 5. A cutting device that shreds the waste composite material made of resin and metal into pieces of appropriate size; a composite material cooling device that cools the agglomerated composite material to a temperature below the brittle temperature of the resin material; an impact-type crushing device for peeling and separating the agglomerated composite material in a state of temperature, a mixture separation and sorting device for separately extracting a resin part and a metal part from the crushed particle mixture, and a separate sorting device for each separately. It is characterized by comprising a washing device and a drying device for washing and drying the extracted metal particle group and resin particle group, respectively, and a transfer means such as a conveyor is provided between each of the devices and the device. Recycling processing equipment for metal and resin composite materials. 6. The mixture separation and sorting device comprises a specific gravity difference separation tank filled with a heavy liquid dispersion medium having a predetermined specific gravity value, and the separation tank is connected to the discharge port of the impact type crushing device through a transfer means. The pulverized product is arranged so as to be supplied, and the lightweight resin material can be floated and separated via an overflow weir provided above the separation tank, and materials with a high specific gravity value that have settled at the bottom of the separation tank are extracted. 6. The regeneration processing apparatus according to claim 5, wherein the overflow port for discharging the water is connected to the bottom opening of the separation tank and is installed at a position lower than the liquid level of the separation tank. 7. In the case where the metal part of the composite material is made of a magnetic material such as steel, the separation and sorting device is connected to a magnetic separation conveyor having a magnetic separation device on the discharge side of the crushing device, and further on the delivery side of the separation conveyor. 6. The regeneration processing apparatus according to claim 5, further comprising a vibrating sieve for resin for classifying and sorting the resin particle portion from which the metal particle portion has been removed.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP62110708A JPS63276509A (en) | 1987-05-08 | 1987-05-08 | Method and appratus for regeneration of resin-metal composite material |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP62110708A JPS63276509A (en) | 1987-05-08 | 1987-05-08 | Method and appratus for regeneration of resin-metal composite material |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS63276509A true JPS63276509A (en) | 1988-11-14 |
Family
ID=14542447
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP62110708A Pending JPS63276509A (en) | 1987-05-08 | 1987-05-08 | Method and appratus for regeneration of resin-metal composite material |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS63276509A (en) |
Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH05147040A (en) * | 1991-12-02 | 1993-06-15 | Hitachi Ltd | Waste treatment apparatus |
JPH0847926A (en) * | 1995-07-12 | 1996-02-20 | Hitachi Ltd | Method for and apparatus of selection of plastics |
JPH0857853A (en) * | 1995-07-12 | 1996-03-05 | Hitachi Ltd | Disposer of waste matter and disposing method |
US5676318A (en) * | 1994-03-09 | 1997-10-14 | Nec Corporation | Method of recovering valuable substances from printed circuit board |
WO1998041374A1 (en) * | 1997-03-19 | 1998-09-24 | Hitachi, Ltd. | Disposal system for plastic |
JP2002361223A (en) * | 2001-06-07 | 2002-12-17 | Mitsubishi Heavy Ind Ltd | Apparatus and method for freezing waste |
US6588597B2 (en) | 1997-03-19 | 2003-07-08 | Hitachi, Ltd. | Disposal system for plastic |
US6660052B1 (en) | 1996-09-13 | 2003-12-09 | Nkk Corporation | Method for blowing synthetic resins as a fuel into a furnace |
JP2007260514A (en) * | 2006-03-27 | 2007-10-11 | Fujifilm Corp | Classification device and classification method |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS49112980A (en) * | 1973-02-28 | 1974-10-28 | ||
JPS5036466A (en) * | 1973-07-03 | 1975-04-05 | ||
JPS56106824A (en) * | 1979-09-10 | 1981-08-25 | Ford Motor Co | Method of regenerating plastic and metal from metallized plastic |
JPS5715530A (en) * | 1980-07-01 | 1982-01-26 | Ricoh Co Ltd | Power supply timer circuit |
-
1987
- 1987-05-08 JP JP62110708A patent/JPS63276509A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS49112980A (en) * | 1973-02-28 | 1974-10-28 | ||
JPS5036466A (en) * | 1973-07-03 | 1975-04-05 | ||
JPS56106824A (en) * | 1979-09-10 | 1981-08-25 | Ford Motor Co | Method of regenerating plastic and metal from metallized plastic |
JPS5715530A (en) * | 1980-07-01 | 1982-01-26 | Ricoh Co Ltd | Power supply timer circuit |
Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH05147040A (en) * | 1991-12-02 | 1993-06-15 | Hitachi Ltd | Waste treatment apparatus |
US5676318A (en) * | 1994-03-09 | 1997-10-14 | Nec Corporation | Method of recovering valuable substances from printed circuit board |
JPH0847926A (en) * | 1995-07-12 | 1996-02-20 | Hitachi Ltd | Method for and apparatus of selection of plastics |
JPH0857853A (en) * | 1995-07-12 | 1996-03-05 | Hitachi Ltd | Disposer of waste matter and disposing method |
US6660052B1 (en) | 1996-09-13 | 2003-12-09 | Nkk Corporation | Method for blowing synthetic resins as a fuel into a furnace |
WO1998041374A1 (en) * | 1997-03-19 | 1998-09-24 | Hitachi, Ltd. | Disposal system for plastic |
US6588597B2 (en) | 1997-03-19 | 2003-07-08 | Hitachi, Ltd. | Disposal system for plastic |
JP2002361223A (en) * | 2001-06-07 | 2002-12-17 | Mitsubishi Heavy Ind Ltd | Apparatus and method for freezing waste |
JP4658384B2 (en) * | 2001-06-07 | 2011-03-23 | 三菱重工業株式会社 | Waste refrigeration treatment apparatus and refrigeration treatment method |
JP2007260514A (en) * | 2006-03-27 | 2007-10-11 | Fujifilm Corp | Classification device and classification method |
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