JP7326752B2 - Manufacturing method of recycled carbon fiber - Google Patents
Manufacturing method of recycled carbon fiber Download PDFInfo
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- JP7326752B2 JP7326752B2 JP2019009114A JP2019009114A JP7326752B2 JP 7326752 B2 JP7326752 B2 JP 7326752B2 JP 2019009114 A JP2019009114 A JP 2019009114A JP 2019009114 A JP2019009114 A JP 2019009114A JP 7326752 B2 JP7326752 B2 JP 7326752B2
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- 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
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- 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
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Description
本発明は、炭素繊維強化プラスチック(以下、CFRP:Carbon Fiber Reinforced Plastic、という)のマトリックス樹脂成分を熱分解して、CFRPから炭素繊維をリサイクルする製造方法に関する。 The present invention relates to a manufacturing method of thermally decomposing a matrix resin component of carbon fiber reinforced plastic (hereinafter referred to as CFRP ) to recycle carbon fiber from CFRP.
CFRPは、比強度や比弾性率といった力学的特性に優れていることから、航空・宇宙用途や、釣竿、ゴルフシャフト、テニスラケット等のスポーツ・レジャー用途、その他の用途において広く用いられているが、製造工程で発生する屑類や、不要になったものの廃棄処理が大きな問題であった。炭素繊維は不燃性であり、しかも、決して腐らないから、現状では埋立処理によるほかはないが、埋立処理による地下汚染の観点から少しでも廃棄を回避できれば環境負荷低減に大きく貢献できる。また、炭素繊維は、よく知られているように、ポリアクリロニトリル繊維等のプリカーサー繊維を1000~3000℃もの高温で焼成して得られるものであり、その製造に費消されるエネルギーは相当なものであるから、そのまま埋め立てて廃棄するのではなく、有効に再利用することが重要である。ところで、炭素繊維は不燃性であるが、マトリックス樹脂を形成している熱硬化性樹脂は燃えるので、CFRPを加熱炉に入れ、熱硬化性樹脂を燃やせば、炭素繊維を回収することはできる。 CFRP has excellent mechanical properties such as specific strength and specific modulus, so it is widely used in aerospace applications, sports and leisure applications such as fishing rods, golf shafts, tennis rackets, and other applications. , waste generated in the manufacturing process and disposal of unnecessary items have been a big problem. Carbon fiber is incombustible and never rots, so currently there is no alternative but to landfill it. However, from the viewpoint of underground pollution due to landfill processing, if disposal can be avoided even a little, it will greatly contribute to reducing the environmental load. In addition, as is well known, carbon fibers are obtained by firing precursor fibers such as polyacrylonitrile fibers at a high temperature of 1000 to 3000° C., and the energy consumed for their production is considerable. Therefore, it is important to recycle them effectively instead of throwing them in landfills. By the way, carbon fibers are non-flammable, but the thermosetting resin forming the matrix resin is combustible, so if CFRP is placed in a heating furnace and the thermosetting resin is burned, the carbon fibers can be recovered.
特許文献1(特表2016-521295号公報)では、CFRP中の熱硬化性樹脂を熱分解させた後、炭素繊維を取り出し切断してから再利用する方法が記載されている。 Patent Document 1 (Japanese Patent Application Laid-Open No. 2016-521295) describes a method of thermally decomposing a thermosetting resin in CFRP and then taking out and cutting carbon fibers for reuse.
特許文献2(特許第3180463)では、CFRPを任意の大きさになるまで破砕してからCFRP中の熱硬化性樹脂を熱分解させる方法が記載されている。 Patent Document 2 (Patent No. 3180463) describes a method of crushing CFRP to an arbitrary size and then thermally decomposing the thermosetting resin in the CFRP.
また、特許文献3(特開2013-147545号公報)では、熱分解炉に原料を自動で投入し、自動で製品を取り出す方法が記載されている。 Further, Patent Document 3 (Japanese Patent Application Laid-Open No. 2013-147545) describes a method of automatically charging raw materials into a pyrolysis furnace and automatically taking out products.
しかしながら、特許文献1の方法においては熱分解後の繊維を任意の繊維長に切断する工程が必要であるが、熱分解後の繊維は柔らかいため炭素繊維の切断が難しい。またCFRPは一般に複数の積層角度からなる層を含んでいるため、切断前に熱分解後の繊維を一方向に引きそろえる必要があり、作業効率が悪いものであった。 However, in the method of Patent Document 1, a step of cutting the pyrolyzed fibers into arbitrary fiber lengths is required, but the carbon fibers are difficult to cut because the pyrolyzed fibers are soft. In addition, since CFRP generally includes layers having multiple lamination angles, it is necessary to align the fibers after pyrolysis in one direction before cutting, resulting in poor work efficiency.
また、特許文献2の方法では破砕した材料をバッチで電気炉に投入しているため生産効率が悪く、生産コストを下げることができないものであった。 Further, in the method of Patent Document 2, since the crushed material is put into the electric furnace in batches, the production efficiency is poor and the production cost cannot be reduced.
さらに、特許文献3の方法では、連続製造を実現するために必要な熱分解炉の前後工程に関する記載がないものであった。 Furthermore, in the method of Patent Document 3, there is no description of the steps before and after the pyrolysis furnace, which are necessary for realizing continuous production.
またさらに、いずれの文献においても、収率を向上させるための技術、リサイクル炭素繊維分級体の長さをコントロールする技術、除粉に関する技術、作業環境を整えるための技術に関する記載がないものであった。 In addition, none of the documents describes a technique for improving the yield, a technique for controlling the length of the recycled carbon fiber classified material, a technique for powder removal, or a technique for preparing the work environment. Ta.
そこで本発明は、かかる従来技術の問題点に鑑み、廃CFRP製品やCFRP製品の製造時に発生する切屑等から、マトリックス樹脂成分を除去することによって、CFRPの再利用可能とするものである。具体的には、CFRP中の炭素繊維を高い収率で回収しリサイクルする工程において、製造工程間の搬送を自動化することを目的とする。 Therefore, in view of the problems of the prior art, the present invention enables CFRP to be reused by removing the matrix resin component from waste CFRP products and chips generated during the manufacture of CFRP products. Specifically, in the process of recovering and recycling carbon fibers in CFRP at a high yield, the object is to automate transportation between manufacturing processes.
上記課題を解決するために本発明は以下の手段を採用するものである。すなわち、
[1]炭素繊維及びマトリックス樹脂成分を含有する炭素繊維強化プラスチックからリサイクル炭素繊維を得るリサイクル炭素繊維の製造方法であって、以下の(a)から(g)に至る各工程間の搬送を自動化することを特徴とするリサイクル炭素繊維の製造方法。
(a)炭素繊維強化プラスチック廃材を破砕し所定の繊維長を有する炭素繊維強化プラスチック破砕片を作製する破砕処理工程
(b)前記炭素繊維強化プラスチック破砕片を風送式、ベルトコンベア式、バケットコンベア式いずれかの搬送方法でホッパーに送り貯蔵する搬送貯蔵工程
(c)前記炭素繊維強化プラスチック破砕片を前記ホッパーから除粉装置にスクリューフィーダー方式、ロータリーバルブ方式いずれかの方法で定量供給し、前記除粉装置にて前記炭素繊維強化プラスチック破砕片に含まれる粉体を除去し、炭素繊維強化プラスチック除粉片を生成する除粉処理工程
ここで、前記除粉処理工程において、前記ホッパーは攪拌羽と定量払い出し装置を具備し、前記除粉装置を構成する粉体吸引配管で詰まりを検出すると前記攪拌羽と前記定量払い出し装置の動作を停止し、前記炭素繊維強化プラスチック破砕片の前記除粉装置への供給を停止する
(d)前記炭素繊維強化プラスチック除粉片を熱分解炉に定量供給しながら加熱し、前記炭素繊維強化プラスチック除粉片に含まれる前記マトリックス樹脂成分を除去してリサイクル炭素繊維熱分解体を得る熱分解処理工程
(e)前記リサイクル炭素繊維熱分解体を冷却しながら次工程にベルトコンベア式、バケットコンベア式いずれかの方法で送る冷却搬送工程
(f)前記リサイクル炭素繊維熱分解体を分級してリサイクル炭素繊維分級体を得る分級処理工程
(g)前記リサイクル炭素繊維分級体から磁気力により金属粉を取り除く除鉄処理工程
[2]前記除粉処理工程において、前記炭素繊維強化プラスチック破砕片に含まれる5~30%の前記粉体を除去することを特徴とする[1]に記載のリサイクル炭素繊維の製造方法。
[3]前記除粉処理工程において、目開き500μm未満のスクリーンメッシュで前記粉体を除去することを特徴とする[2]に記載のリサイクル炭素繊維の製造方法。
[4]前記熱分解処理工程において、酸素濃度2~8%、加熱処理温度500~580℃、加熱処理時間10~40分とする乾留処理を実施し、下記式によりリサイクル炭素繊維中の前記マトリックス樹脂の残留量が7~17重量%である[1]~[3]のいずれかに記載のリサイクル炭素繊維の製造方法。
樹脂残留量(%)=((1-樹脂焼き飛ばし後重量/樹脂焼き飛ばし前重量)x100)
[5]前記分級処理工程において、前記リサイクル炭素繊維熱分解体の厚みに応じて、少なくとも3以上の分級厚み範囲にふるい分級し、前記分級厚み範囲の最大範囲と最小範囲に分級される前記リサイクル炭素繊維分級体を混合し、その後粉砕する[1]~[4]のいずれかに記載のリサイクル炭素繊維の製造方法。
[6]前記リサイクル炭素繊維分級体の厚み範囲の最小範囲が4μm≦厚み<300μm、最大範囲が1mm<厚みである[5]に記載のリサイクル炭素繊維の製造方法。
[7]前記リサイクル炭素繊維分級体の長さが1~20mmである[6]に記載のリサイクル炭素繊維の製造方法。
[8]前記リサイクル炭素繊維分級体の分級処理工程において分級装置内での滞留時間が1分以上2分以下である[1]~[7]のいずれかに記載のリサイクル炭素繊維の製造方法。
[9]前記除粉処理工程における除粉装置の除粉処理能力が、前記分級処理工程における分級装置の除粉処理能力よりも大きい、[1]~[8]のいずれかに記載のリサイクル炭素繊維に製造方法。
[10]各工程に微粉を吸引する吸引手段を更に設ける[1]~[9]のいずれかに記載のリサイクル炭素繊維の製造方法。
In order to solve the above problems, the present invention employs the following means. i.e.
[1] A method for producing recycled carbon fibers for obtaining recycled carbon fibers from carbon fiber reinforced plastics containing carbon fibers and matrix resin components, wherein transportation between the following steps (a) to (g) is automated. A method for producing recycled carbon fiber, characterized by:
(a) A crushing treatment step of crushing carbon fiber reinforced plastic waste to produce crushed carbon fiber reinforced plastic pieces having a predetermined fiber length (b) Pneumatic, belt conveyor, or bucket conveyor for the crushed carbon fiber reinforced plastic pieces (c) feeding the crushed pieces of carbon fiber reinforced plastic from the hopper to a powder removing device by a screw feeder method or a rotary valve method; A powder removal treatment step of removing powder contained in the crushed pieces of carbon fiber reinforced plastic with a powder removal device to generate powder removed pieces of carbon fiber reinforced plastic.
Here, in the powder removal treatment step, the hopper is equipped with a stirring blade and a fixed quantity dispensing device, and when clogging is detected in a powder suction pipe constituting the powder removing device, the stirring blade and the fixed quantity dispensing device are operated. stop and stop the supply of the carbon fiber reinforced plastic crushed pieces to the powder removing device
(d) Heating the carbon fiber reinforced plastic powder removing pieces while feeding them into a pyrolysis furnace to remove the matrix resin component contained in the carbon fiber reinforced plastic powder removing pieces to obtain recycled carbon fiber pyrolysates. Pyrolysis treatment step (e) cooling and transporting the recycled carbon fiber pyrolyzate to the next step by either belt conveyor or bucket conveyor while cooling (f) classifying the recycled carbon fiber pyrolyzate (g) an iron removal treatment step of removing metal powder from the recycled carbon fiber classified body by magnetic force [2] in the powder removal treatment step, in which the carbon fiber reinforced plastic crushed pieces are The method for producing recycled carbon fiber according to [1], wherein 5 to 30% of the powder contained is removed.
[3] The method for producing recycled carbon fibers according to [2], wherein in the powder removal treatment step, the powder is removed with a screen mesh having an opening of less than 500 μm.
[ 4 ] In the pyrolysis treatment step, a dry distillation treatment is performed with an oxygen concentration of 2 to 8%, a heat treatment temperature of 500 to 580 ° C., and a heat treatment time of 10 to 40 minutes. The method for producing recycled carbon fibers according to any one of [1] to [ 3 ], wherein the residual amount of resin is 7 to 17% by weight.
Residual amount of resin (%) = ((1-weight after resin is burned off/weight before resin is burned off) x 100)
[ 5 ] In the classification treatment step, the recycled carbon fiber pyrolyzate is sifted and classified into at least three or more classification thickness ranges according to the thickness of the recycled carbon fiber pyrolysate, and the recycled material is classified into the maximum range and the minimum range of the classification thickness range. The method for producing recycled carbon fibers according to any one of [1] to [ 4 ], wherein the carbon fiber classifier is mixed and then pulverized.
[ 6 ] The method for producing recycled carbon fibers according to [ 5 ], wherein the thickness range of the recycled carbon fiber classified body has a minimum range of 4 μm≦thickness<300 μm and a maximum range of 1 mm<thickness.
[ 7 ] The method for producing recycled carbon fibers according to [ 6 ], wherein the length of the recycled carbon fiber classified body is 1 to 20 mm.
[ 8 ] The method for producing recycled carbon fibers according to any one of [1] to [ 7 ], wherein the residence time in the classifier is 1 minute or more and 2 minutes or less in the classifying step of the recycled carbon fiber classified body.
[ 9 ] The recycled carbon according to any one of [1] to [ 8 ], wherein the powder removal capacity of the powder removal device in the powder removal process is greater than the powder removal capacity of the classifier in the classification process. Manufacturing method to fiber.
[1 0 ] The method for producing recycled carbon fibers according to any one of [1] to [ 9 ], further comprising suction means for sucking fine powder in each step.
この発明によれば、CFRP中から有用な炭素繊維を高い収率で回収し、リサイクル炭素繊維として利用することができる。さらに、その製造工程間の搬送を自動化することにより生産性が高いリサイクル炭素繊維の製造方法を提供することができる。 According to the present invention, useful carbon fibers can be recovered from CFRP at a high yield and used as recycled carbon fibers. Furthermore, by automating the transportation between the manufacturing processes, it is possible to provide a highly productive recycled carbon fiber manufacturing method.
以下に、本発明の実施の形態について順次説明する。本実施形態は本発明を実施する一例であって、本発明は本実施例形態に限定されるものではない。また、以下の説明において、CFRPはマトリックス樹脂の種類、炭素繊維の種類(例えば黒鉛繊維)を問わない。 Embodiments of the present invention will be sequentially described below. This embodiment is an example of implementing the present invention, and the present invention is not limited to this embodiment. In the following description, CFRP does not matter what kind of matrix resin and what kind of carbon fiber (for example, graphite fiber).
本リサイクル炭素繊維の製造方法のプロセスは、破砕したCFRP廃材から熱分解法を用いてリサイクル炭素繊維を取り出す製造方法で、図1に製造方法フローを示す。以下に工程毎の詳細を述べる。 The process of this recycled carbon fiber manufacturing method is a manufacturing method for extracting recycled carbon fibers from crushed CFRP waste material using a pyrolysis method, and the manufacturing method flow is shown in FIG. Details of each step are described below.
(a)破砕処理工程
図2に破砕処理工程の概略図を示す。原料であるCFRP廃材1は、まず一次破砕機2に投入され二軸方式の刃3で大まかに破砕された後、ベルトコンベヤ4によって二次破砕機5へと搬送される。 ベルトコンベヤ4にて搬送されたCFRP廃材1は二次破砕機5へと投入され、スクリーン6の網目以下の大きさになるまで固定刃7と回転刃8で破砕される。この時、CFRP破砕片9だけでなく、粉体10も発生する。その後、CFRP破砕片9と粉体10を次工程(矢印11方向)に搬送する。
(a) Crushing treatment process Fig. 2 shows a schematic diagram of the crushing treatment process. A CFRP waste material 1 as a raw material is first put into a primary crusher 2 and roughly crushed by a biaxial blade 3 , and then conveyed to a secondary crusher 5 by a belt conveyor 4 . The CFRP waste material 1 conveyed by the belt conveyor 4 is put into the secondary crusher 5 and crushed by the fixed blade 7 and the rotary blade 8 until the size becomes smaller than the mesh size of the screen 6 . At this time, not only CFRP fragments 9 but also powder 10 are generated. After that, the crushed CFRP pieces 9 and the powder 10 are conveyed to the next step (direction of arrow 11).
(b)搬送貯蔵工程、
図3に搬送貯蔵工程の概略図を示す。破砕されたCFRP破砕片9と粉体10は前工程(矢印11方向)から搬送され、ホッパー12に貯蔵される。搬送方法は風送式、ベルトコンベア式、バケットコンベア式等が挙げられる。設備費が安価である風送式を用いるのが好ましい。
(b) transportation and storage step;
FIG. 3 shows a schematic diagram of the transportation and storage process. The crushed CFRP pieces 9 and powder 10 are transported from the previous process (in the direction of arrow 11 ) and stored in a hopper 12 . Conveying methods include an air blowing method, a belt conveyor method, a bucket conveyor method, and the like. It is preferable to use the air blowing type, which has a low equipment cost.
(c)除粉処理工程
図3に除粉処理工程の概略図を示す。ホッパー12に貯蔵したCFRP破砕片9と粉体10を定量的に除粉装置14に搬送する(矢印13方向)。ここで除粉装置14は振動ふるい機が好ましい。その後除粉装置14でCFRP破砕片9と粉体10を分離し、CFRP除粉片15を次工程(矢印16方向)に送り、粉体10は別工程(矢印17方向)に送り回収して廃棄等を行う。
(c) Powder Removal Treatment Process FIG. 3 shows a schematic diagram of the powder removal treatment process. The crushed CFRP pieces 9 and the powder 10 stored in the hopper 12 are quantitatively conveyed to the powder removing device 14 (in the direction of arrow 13). Here, the powder removing device 14 is preferably a vibrating sieve. After that, the CFRP crushed pieces 9 and the powder 10 are separated by the powder removing device 14, the CFRP powder removed pieces 15 are sent to the next process (arrow 16 direction), and the powder 10 is sent to another process (arrow 17 direction) and collected. Discard, etc.
(d)熱分解処理工程
図4に熱分解処理工程の概略図を示す。CFRP除粉片15を熱分解炉ホッパー18に貯蔵した後、定量的に熱分解炉20に搬送する(矢印19方向)。CFRP除粉片15は熱分解炉20内で熱分解された後、リサイクル炭素繊維熱分解体22として排出される(矢印21方向)。また、熱分解によって発生したガスはガス処理装置23で適切に処理された後に大気に放出される。熱分解炉20の加熱方式は電気ヒーター、熱風等が挙げられる。本発明においては導電性のある炭素繊維を扱うため熱風方式が好ましい。
(d) Thermal decomposition process FIG. 4 shows a schematic diagram of the thermal decomposition process. After the CFRP powder removal pieces 15 are stored in the pyrolysis furnace hopper 18, they are quantitatively conveyed to the pyrolysis furnace 20 (arrow 19 direction). After the CFRP powder removing pieces 15 are thermally decomposed in the thermal decomposition furnace 20, they are discharged as recycled carbon fiber thermally decomposed bodies 22 (in the direction of arrow 21). Also, the gas generated by thermal decomposition is properly treated in the gas treatment device 23 and then released to the atmosphere. Heating methods of the pyrolysis furnace 20 include electric heaters, hot air, and the like. In the present invention, the hot air method is preferred because it handles conductive carbon fibers.
ここで、熱分解炉内での材料搬送方式として、ベルトコンベア式、バケットコンベア式、また、熱分解炉自身が回転するロータリーキルン式等がある。熱分解炉内は高温になっているため、設備寿命の観点からコンベアを使用しないロータリーキルン式が好ましい。 Here, as a method for conveying materials in the pyrolysis furnace, there are a belt conveyor type, a bucket conveyor type, a rotary kiln type in which the pyrolysis furnace itself rotates, and the like. Since the temperature inside the pyrolysis furnace is high, a rotary kiln type that does not use a conveyor is preferable from the viewpoint of equipment life.
(e)冷却搬送工程
図示していないが、冷却搬送工程は熱分解炉から排出したリサイクル炭素繊維熱分解体22を冷却しながら次工程に送る役割を持つ。搬送方式は特に限定は無く、熱分解直後の高温状態のリサイクル炭素繊維熱分解体22を搬送できるだけの耐熱性があればいい。また冷却方式として、風冷、自然冷却等がある。冷却設備が不要な自然冷却が好ましい。また、搬送方式をベルトコンベア式、バケットコンベア式等にして搬送中に自然冷却することも好ましい。
(e) Cooling and Conveying Process Although not shown, the cooling and conveying process has the role of cooling the recycled carbon fiber pyrolysates 22 discharged from the pyrolysis furnace and sending them to the next process. The transportation method is not particularly limited, and it is sufficient that it has heat resistance enough to transport the recycled carbon fiber thermally decomposed body 22 in a high temperature state immediately after thermal decomposition. Cooling methods include air cooling, natural cooling, and the like. Natural cooling, which does not require cooling equipment, is preferred. It is also preferable to use a belt conveyer system, a bucket conveyer system, or the like for the conveying method, and allow natural cooling during conveying.
(f)分級処理工程
図5に分級処理工程の概略図を示す。リサイクル炭素繊維熱分解体22は冷却搬送工程から分級装置25に通して(矢印24方向)、所定の厚みを有するリサイクル炭素繊維分級体に分級する。ここで分級装置は振動ふるい機が好ましい。振動ふるい機は段数とスクリーンメッシュを変えることにより所定の厚みのリサイクル炭素繊維分級体を得ることができる。図5にて2つのスクリーンメッシュで3種類の厚みのリサイクル炭素繊維分級体(26、27、28)に分級している様子を例示している。
(f) Classification Process FIG. 5 shows a schematic diagram of the classification process. The recycled carbon fiber thermally decomposed material 22 is passed through a classifier 25 (in the direction of arrow 24) from the cooling and conveying step to be classified into recycled carbon fiber classified bodies having a predetermined thickness. Here, the classifier is preferably a vibrating sieve. By changing the number of stages and the screen mesh of the vibrating sieve machine, it is possible to obtain a recycled carbon fiber classified body of a predetermined thickness. FIG. 5 illustrates how two screen meshes are used to classify recycled carbon fiber classified bodies (26, 27, 28) having three different thicknesses.
(g)除鉄処理工程
図示していないが、リサイクル炭素繊維分級体が通る配管内に磁気力により金属粉を取り除く装置を設置することにより、処理中に発生した鉄粉を回収してリサイクル炭素繊維に金属粉が混入しないようにする。
(g) Iron removal treatment process Although not shown, by installing a device for removing metal powder by magnetic force in the piping through which the recycled carbon fiber classifier passes, the iron powder generated during the treatment is recovered and recycled carbon is removed. Make sure that the fibers are free of metal powder.
本発明では、除粉処理工程において、CFRP破砕片9に含まれる5~30%の粉体10を除去することが好ましく、より好ましくは7~28%、さらに好ましくは10~25%である。粉体の除去が5%未満だと粉体の除去が不十分であり、粉体爆発や粉体が熱分解炉の制御センサにつまる不良の原因になる。また粉体の除去が30%より大きいとロスが多くなり製造コストが増加する。 In the present invention, it is preferable to remove 5 to 30% of the powder 10 contained in the CFRP crushed pieces 9, more preferably 7 to 28%, and still more preferably 10 to 25% in the powder removal treatment step. If the removal of the powder is less than 5%, the removal of the powder is inadequate, which causes a powder explosion or a defect in which the control sensor of the pyrolysis furnace is clogged with the powder. Also, if the removal of powder is more than 30%, the loss increases and the manufacturing cost increases.
本発明において、粉体除去の割合を粉体除去率とし、粉体除去率(%)=(1-CFRP除粉片15重量/CFRP破砕片9重量x100)として計算している。 In the present invention, the ratio of powder removal is defined as the powder removal rate, which is calculated as follows: powder removal rate (%)=(1-15 weight of CFRP powder-removed pieces / 9 weights of CFRP crushed pieces x 100).
本発明によれば、ホッパーには攪拌羽と定量払い出し装置を具備していることが好ましい。図6に攪拌羽と定量払い出し装置を具備している除粉処理工程の概略図を示す。ホッパー12は攪拌羽30と定量払い出し装置31を備えている。CFRP破砕片9は硬くかつ先端が尖っているため、CFRP破砕片9同士がアーチ構造を形成し閉塞するいわゆるブリッジを発生させて、定量払い出し装置31からCFRP破砕片9を払い出すことができない。ブリッジを破壊する機構として、ホッパーを外側からたたくノッカー方式やCFRP破砕片9にエアを吹き付ける方式やホッパー内に設置した攪拌羽30でブリッジを破壊する方式がある。ノッカー方式、エア吹き付け方式では硬くかつ先端が尖っているCFRP破砕片9由来のブリッジを破壊することはできない。鋭意検討した結果、ホッパー内に設置した攪拌羽30でブリッジを破壊する方式が好適であることがわかった。攪拌羽30の設置位置、形状、個数に限定はなくブリッジの発生範囲を網羅していれば良い。 According to the invention, the hopper is preferably equipped with stirring blades and a metering device. FIG. 6 shows a schematic diagram of the powder removal treatment process equipped with a stirring blade and a fixed quantity dispensing device. The hopper 12 is provided with an agitating blade 30 and a metered dispensing device 31 . Since the CFRP crushed pieces 9 are hard and have sharp ends, the CFRP crushed pieces 9 form an arched structure to form a so-called bridge, which blocks the CFRP crushed pieces 9 , so that the fixed quantity dispensing device 31 cannot dispense the CFRP crushed pieces 9 . Mechanisms for destroying the bridges include a knocker system that hits the hopper from the outside, a system that blows air onto the crushed CFRP pieces 9, and a system that destroys the bridges with a stirring blade 30 installed in the hopper. The knocker method and the air blowing method cannot break the bridges derived from the CFRP fragments 9 that are hard and sharp. As a result of intensive investigation, it was found that a method of destroying the bridges with the stirring blades 30 installed in the hopper is suitable. The installation position, shape, and number of the stirring blades 30 are not limited as long as they cover the generation range of bridges.
また、攪拌羽30は回転方向が切り替えられる制御にすることが好ましい。攪拌羽30とホッパー13の隙間に粉体10が圧縮、蓄積されて最終的に攪拌羽30が回転できなくなる場合がある。鋭意検討した結果、回転方向を逆転させると粉体10の蓄積が容易に外れることがわかった。制御により安定的に生産を継続することができる。回転方向の切り替え機構として、規定時間ごとに方向を切り替える方法、攪拌羽30にかかる力を検出し一定力を超えると攪拌羽30の回転を逆転させる方法、ホッパー内の状態を映像で監視し異常を検知すると攪拌羽30の回転を逆転させる方法がある。特に、攪拌羽30にかかる力を検出し一定力を超えると攪拌羽30の回転を逆転させる方法が攪拌羽30の異常をすぐに検知することができ好適である。 Further, it is preferable that the stirring blade 30 is controlled so that the rotating direction can be switched. In some cases, the powder 10 is compressed and accumulated in the gap between the stirring blade 30 and the hopper 13 and eventually the stirring blade 30 cannot rotate. As a result of intensive investigation, it was found that the accumulation of the powder 10 is easily removed by reversing the direction of rotation. Production can be continued stably by control. As a rotation direction switching mechanism, a method of switching the direction at regular intervals, a method of detecting the force applied to the stirring blade 30 and reversing the rotation of the stirring blade 30 when it exceeds a certain force, a method of monitoring the state inside the hopper by video, and abnormalities There is a method of reversing the rotation of the stirring blade 30 when is detected. In particular, the method of detecting the force applied to the stirring blades 30 and reversing the rotation of the stirring blades 30 when the force exceeds a certain value is preferable because the abnormality of the stirring blades 30 can be immediately detected.
また、除粉装置14としては、所定のメッシュサイズを有するスクリーンメッシュを備えた振動ふるい機が例示できる。ここで、スクリーンメッシュのメッシュサイズとしては500μm未満であることが好ましい。より好ましくは400μm以下であり、さらに好ましくは300μm以下である。また、メッシュサイズは20μm以上が好ましい。より好ましくは100μm以上であり、さらに好ましくは200μm以上である。 Moreover, as the powder removing device 14, a vibrating sieve having a screen mesh having a predetermined mesh size can be exemplified. Here, the mesh size of the screen mesh is preferably less than 500 μm. It is more preferably 400 μm or less, still more preferably 300 μm or less. Moreover, the mesh size is preferably 20 μm or more. It is more preferably 100 µm or more, and still more preferably 200 µm or more.
スクリーンメッシュのメッシュサイズが500μm以上であると、ロスが多くなり製造コストが増加する。20μm未満だと粉体の除去が不十分であり、粉体爆発や粉体が熱分解炉の制御センサにつまる不良の原因になる。 If the mesh size of the screen mesh is 500 μm or more, loss increases and manufacturing costs increase. If the particle size is less than 20 μm, the removal of powder is insufficient, which may cause powder explosion or failure in which the control sensor of the pyrolysis furnace is clogged with powder.
本発明によれば、定量的にCFRP破砕片9と粉体10を除粉装置14に送ることが好ましい。定量的にCFRP破砕片9と粉体10を払い出すことができないと、CFRP破砕片9と粉体10の供給が過大になり除粉装置14での除粉処理が追いつかず粉体10が多く残る場合がある。また、CFRP破砕片9の排出が過少になると除粉処理量が少なくなり生産速度が低下する。 According to the invention, it is preferable to feed the CFRP fragments 9 and the powder 10 quantitatively to the powder removal device 14 . If the crushed CFRP pieces 9 and the powder 10 cannot be discharged quantitatively, the supply of the crushed CFRP pieces 9 and the powder 10 will be excessive, and the powder removal processing in the powder removal device 14 will not keep up, resulting in a large amount of the powder 10. may remain. Moreover, if the discharge of the CFRP crushed pieces 9 is too small, the amount of powder removal processing is reduced, and the production speed is lowered.
またCFRP破砕片9を払い出す方法としては、スクリューフィーダー方式(図7)、ロータリーバルブ方式(図8)等がある。方式については限定されないが、いずれの場合においてもスクリューフィーダーのケーシング33とスクリュー34、ロータリーバルブのケーシング35とローター36の隙間を3~30mmあけておくことが好ましい。隙間が3mm以下の場合、CFRP破砕片9や粉体10が隙間につまりスクリューもしくはローターが動かなくなる場合がある。隙間が30mmより大きいとCFRP破砕片9や粉体10の定量供給性が低下する。 Methods for discharging the CFRP crushed pieces 9 include a screw feeder method (FIG. 7), a rotary valve method (FIG. 8), and the like. Although the system is not limited, in any case, it is preferable to leave a gap of 3 to 30 mm between the screw feeder casing 33 and the screw 34 and the rotary valve casing 35 and rotor 36 . If the gap is 3 mm or less, the CFRP fragments 9 and the powder 10 may clog the gap and the screw or rotor may not move. If the gap is larger than 30 mm, the ability to feed the crushed CFRP pieces 9 and the powder 10 in a constant quantity decreases.
本発明によれば、除粉装置14の粉体吸引配管32につまりを検出すると攪拌羽30と定量払い出し装置31の動作が停止することが好ましい。粉体吸引配管32がつまると粉体10の吸引ができなくなるので、除粉能力が低下して粉体10の除去が不十分になる。そのような状態でCFRP破砕片9と粉体10の払い出しを継続すると、除粉が追いつかなくなり除粉装置がつまり生産できなくなる。 According to the present invention, it is preferable to stop the operation of the stirring blade 30 and the fixed quantity dispensing device 31 when clogging of the powder suction pipe 32 of the powder removing device 14 is detected. If the powder suction pipe 32 is clogged, the powder 10 cannot be sucked, so the powder removal capability is lowered and the removal of the powder 10 becomes insufficient. If the CFRP crushed pieces 9 and the powder 10 are continued to be discharged in such a state, the powder removal cannot catch up and the powder removal device becomes clogged, making production impossible.
また粉体吸引配管32のつまりを検出する方法として粉体吸引配管32の吸引圧力監視や粉体蓄積体積の映像監視、配管の重量監視などがある。監視システムの簡便性から吸引圧力監視が好ましい。 Methods for detecting clogging of the powder suction pipe 32 include suction pressure monitoring of the powder suction pipe 32, image monitoring of the powder accumulation volume, weight monitoring of the pipe, and the like. Aspiration pressure monitoring is preferred due to the simplicity of the monitoring system.
本発明では、熱分解処理工程において、酸素濃度は2~8%が好ましく、より好ましくは3~7%、さらに好ましくは4~6%が好ましい。酸素濃度が2%未満にするためには熱分解炉に不活性ガスを充填する必要があり、生産コストが増加する。酸素濃度が8%より大きいとCFRP除粉片15が熱分解炉内で発火する可能性がある。 In the present invention, the oxygen concentration in the pyrolysis treatment step is preferably 2-8%, more preferably 3-7%, and even more preferably 4-6%. In order to reduce the oxygen concentration to less than 2%, it is necessary to fill the pyrolysis furnace with an inert gas, which increases the production cost. If the oxygen concentration is higher than 8%, the CFRP powder removing piece 15 may ignite in the pyrolysis furnace.
また本発明において、低酸素雰囲気下にて500~580℃×10~40分の熱処理により乾留を実施する。プラスチック成分は、熱分解され、CO2 、CO、CH4などや、油状のベンゼン、トルエン、スチレンなどの分解物を排出し、分解残渣の炭化物が残される。加熱温度が500℃未満であると熱分解は起こるが、速度が遅く、処理に時間がかかる。また、580℃を超えると、熱分解炉の温度を保持するための消費エネルギーが多く好ましくない。熱処理は好ましくは505~575℃×12~35分、より好ましくは510~570℃×15~30分である。 In the present invention, dry distillation is carried out by heat treatment at 500 to 580° C. for 10 to 40 minutes in a low oxygen atmosphere. The plastic component is thermally decomposed to discharge decomposition products such as CO 2 , CO, CH 4 and oily benzene, toluene, styrene, etc., and carbonized decomposition residue remains. If the heating temperature is less than 500° C., thermal decomposition occurs, but the speed is slow and the treatment takes a long time. On the other hand, if the temperature exceeds 580° C., a large amount of energy is consumed to maintain the temperature of the pyrolysis furnace, which is not preferable. The heat treatment is preferably 505-575° C.×12-35 minutes, more preferably 510-570° C.×15-30 minutes.
また、熱分解後に含まれるリサイクル炭素繊維熱分解体22に含まれる樹脂残留量は、リサイクル炭素繊維対比7~17重量%まで熱分解を進めることが好ましい。より好ましくは8~16重量%の範囲、さらに好ましくは9~15重量%の範囲である。 Further, it is preferable to carry out thermal decomposition until the amount of residual resin contained in the recycled carbon fiber thermally decomposed material 22 contained after thermal decomposition is 7 to 17% by weight relative to the recycled carbon fiber. It is more preferably in the range of 8 to 16% by weight, still more preferably in the range of 9 to 15% by weight.
熱分解後の残留樹脂はリサイクル炭素繊維同士を互いに結着する、いわゆる接着剤の役目をしている。すなわち、リサイクル炭素繊維同士の結着の強さは、熱分解前のCFRP除粉片15における炭素繊維と熱硬化性樹脂とのそれよりも弱くなっており、樹脂残留量が7重量%未満ではリサイクル炭素繊維の形態保持力が低く、輸送中に綿状になったりする。一方、17重量%を超えると、結着力が低下しているとはいっても利用時におけるリサイクル炭素繊維の分離が難しくなり、リサイクル炭素繊維の他材料中における分散性が低下するようになる。 Residual resin after thermal decomposition serves as a so-called adhesive that binds recycled carbon fibers together. That is, the strength of binding between the recycled carbon fibers is weaker than that between the carbon fibers and the thermosetting resin in the CFRP powder removing piece 15 before pyrolysis. The shape retention of recycled carbon fiber is low, and it becomes fluffy during transportation. On the other hand, if it exceeds 17% by weight, it becomes difficult to separate the recycled carbon fibers at the time of use, even though the binding strength is reduced, and the dispersibility of the recycled carbon fibers in other materials is reduced.
本発明において、樹脂残留量は次の方法で測定している。5gのリサイクル炭素繊維を電気炉で600℃、3.5時間、窒素雰囲気下で樹脂を焼き飛ばした。その後、樹脂の焼き飛ばし前後の重量から樹脂残留量(%)=((1-樹脂焼き飛ばし後重量/樹脂焼き飛ばし前重量)x100)として計算している。 In the present invention, the residual resin amount is measured by the following method. 5 g of recycled carbon fiber was burned off in an electric furnace at 600° C. for 3.5 hours in a nitrogen atmosphere. After that, the resin residual amount (%) is calculated from the weight before and after the resin is burned off = ((1-weight after resin is burned off/weight before resin is burned off) x 100).
本発明によれば、熱分解によって樹脂成分が分解されたリサイクル炭素繊維熱分解体22を分級装置25に投入し、所定厚みのリサイクル炭素繊維分級体を得ることができる。ここで分級装置は振動ふるい機が好ましい。振動ふるい機は段数とスクリーンメッシュを変えることにより所定厚みのリサイクル炭素繊維分級体を得ることができる。 According to the present invention, the recycled carbon fiber thermally decomposed body 22 in which the resin component is decomposed by thermal decomposition is put into the classifier 25, and a recycled carbon fiber classified body having a predetermined thickness can be obtained. Here, the classifier is preferably a vibrating sieve. By changing the number of stages and the screen mesh of the vibrating sieve machine, it is possible to obtain a recycled carbon fiber classified material of a predetermined thickness.
本発明においては、少なくとも3つ以上の厚みのリサイクル炭素繊維分級体にふるい分級することが好ましく、より好ましくは3~4つ、さらに好ましくは3つが好ましい。2つ以下の厚みのリサイクル炭素繊維分級体に分級した場合、任意の厚み範囲内に収まるリサイクル炭素繊維分級体を得ることができない。5つより多いと必要以上の厚み範囲に分級することになり、生産効率が悪くなる。 In the present invention, it is preferable to sieve and classify the recycled carbon fiber classified bodies having a thickness of at least 3 or more, more preferably 3 to 4, and still more preferably 3. When classified into recycled carbon fiber classified bodies having thicknesses of two or less, it is not possible to obtain recycled carbon fiber classified bodies that fall within an arbitrary thickness range. If there are more than 5, it will classify into the thickness range more than necessary, and production efficiency will worsen.
また、分級処理工程において、分級装置内での滞留時間が1分以上2分以下であることが好ましい。1分以上滞留することで、リサイクル炭素繊維熱分解体に十分に振動エネルギーが付与されるため、凝集したリサイクル炭素繊維熱分解体があっても、所定の厚みと長さを有するリサイクル炭素繊維分級体を得ることができ、収率を向上させることができる。一方、2分以下とすることで、分級体の過度な重なり合いを防止し、処理能力の低下を防ぐことができる。 Moreover, in the classification treatment step, the retention time in the classifier is preferably 1 minute or more and 2 minutes or less. By staying for one minute or more, sufficient vibration energy is imparted to the recycled carbon fiber pyrolyzate, so even if there is an aggregated recycled carbon fiber pyrolyzate, the recycled carbon fiber can be classified to have a predetermined thickness and length. body can be obtained and the yield can be improved. On the other hand, by setting the time to 2 minutes or less, it is possible to prevent excessive overlapping of the classified bodies and to prevent deterioration of the processing capacity.
本発明によれば、分級厚み範囲の最大範囲と最小範囲に分級されるリサイクル炭素繊維分級体を混合し、粉砕することが好ましい。分級厚みが小さいとリサイクル炭素繊維分級体が軽く、粉砕工程のフィーダーを通過することができない。そのため分級厚みが大きく重いリサイクル炭素繊維分級体と混ぜて粉砕することが好ましい。混合することにより最小の分級厚みの範囲に分級されるリサイクル炭素繊維の粉砕が可能になり、結果として導電性粉体を得ることができる。また、任意の厚み外のリサイクル炭素繊維を有効に活用することもできる。 According to the present invention, it is preferable to mix and pulverize the recycled carbon fiber classified bodies classified into the maximum range and the minimum range of the classification thickness range. If the classification thickness is small, the recycled carbon fiber classified body is too light to pass through the feeder in the pulverization process. Therefore, it is preferable to mix with a heavy recycled carbon fiber classified material having a large classification thickness and pulverize it. By mixing, it becomes possible to pulverize the recycled carbon fibers that are classified within the range of the minimum classification thickness, and as a result, conductive powder can be obtained. In addition, it is also possible to effectively utilize recycled carbon fibers outside the arbitrary thickness.
粉砕機はハンマーミル方式のミルド粉砕機であって、一定の大きさ以下のリサイクル炭素繊維へと加工される。ミルド粉砕機はハンマーミル、カッターミル、せん断破砕機等が用いることができ、品質が安定するハンマーミル式が好ましい。装置接触面の材質は、磨耗による異物混入が少ないステンレス鋼製を用いることが好ましい。 The pulverizer is a milled pulverizer of a hammer mill type, and is processed into recycled carbon fibers of a certain size or less. A hammer mill, a cutter mill, a shear crusher, or the like can be used as the mill pulverizer, and a hammer mill type is preferable because the quality is stable. As for the material of the device contact surface, it is preferable to use stainless steel, which is less susceptible to contamination due to wear.
リサイクル炭素繊維分級体の厚み範囲は厚み範囲の最小範囲が4μm≦厚み<300μm、最大範囲が1mm<厚みであることが好ましい。分級厚み範囲が300μm≦厚み≦1mmのリサイクル炭素繊維分級体はナイロン等の熱可塑性樹脂と混錬してペレットとして使用する。そのような用途において、分級厚みが300μm未満だとリサイクル炭素繊維分級体が軽くペレット設備のフィーダー通過性が悪くなる。また、分級厚みが1mmより大きいとペレット設備のフィーダーに詰まりフィーダーに負荷がかかりフィーダーが損傷する。また、分級厚み範囲が300μm≦厚み≦1mmのリサイクル炭素繊維分級体の用途はペレットに限定されず、不織布やマットに利用することもできる。 As for the thickness range of the recycled carbon fiber classified material, it is preferable that the minimum thickness range is 4 μm≦thickness<300 μm and the maximum range is 1 mm<thickness. Recycled carbon fiber classified bodies having a classification thickness range of 300 μm≦thickness≦1 mm are kneaded with a thermoplastic resin such as nylon and used as pellets. In such applications, if the classification thickness is less than 300 μm, the recycled carbon fiber classified material is light and poor in passage through the feeder of pellet equipment. Further, if the classification thickness is more than 1 mm, the feeder of the pellet equipment is clogged and the feeder is damaged. Further, the use of the recycled carbon fiber classified material having a classification thickness range of 300 μm≦thickness≦1 mm is not limited to pellets, but can also be used for non-woven fabrics and mats.
また、リサイクル炭素繊維分級体の長さが1~20mmであることが好ましい。リサイクル炭素繊維分級体の長さが1mm未満であると、繊維束が軽くペレット設備のフィーダー通過性が悪くなる。一方、リサイクル炭素繊維分級体の長さが20mmを超えると、ペレット設備のフィーダー通過性が悪くなる。長さが1~20mmの範囲にあるリサイクル炭素繊維分級体の用途はペレットに限定されず、不織布やマットに利用することもできる。 Moreover, it is preferable that the length of the recycled carbon fiber classified body is 1 to 20 mm. If the length of the recycled carbon fiber classified body is less than 1 mm, the fiber bundle is too light to pass through the feeder of pellet equipment. On the other hand, when the length of the recycled carbon fiber classified body exceeds 20 mm, the feeder passability of the pellet equipment is deteriorated. The use of the recycled carbon fiber classified material with a length of 1 to 20 mm is not limited to pellets, but can also be used for non-woven fabrics and mats.
本発明において、リサイクル炭素繊維分級体の模式図を図9に示す。リサイクル炭素繊維分級体の上面概略図37の繊維方向の長さをL、同図の繊維直交方向をWと定義している。繊維直角方向を中心に回転させた概略投影図38の最大厚みをtとし、これを分級体の厚みと定義している。厚みは任意に取り出した15個のリサイクル炭素繊維の厚み(t)をノギスで測定した平均値としている。 FIG. 9 shows a schematic diagram of a recycled carbon fiber classified body in the present invention. The length in the fiber direction in the schematic top view 37 of the recycled carbon fiber classified body is defined as L, and the fiber orthogonal direction in the figure is defined as W. The maximum thickness of the schematic projection 38 rotated around the direction perpendicular to the fiber is defined as t, which is defined as the thickness of the classifier. The thickness is the average value obtained by measuring the thickness (t) of 15 recycled carbon fibers arbitrarily taken out with a vernier caliper.
また、本発明において、除粉処理工程における除粉装置の除粉処理能力が、分級処理工程における分級装置の除粉処理能力よりも大きいことが好ましい。破砕処理工程から除粉処理工程の間で発生した破砕片に含まれる微粉を効率よく除去するために、除粉処理工程における除粉装置は、大型のスクリーンメッシュを用いて、振動を与える駆動モーターも高出力ものを用いることが好ましい。除粉処理工程で効率よく微粉を除去できれば、下流の各工程で微粉の影響を最小限とすることができる。特に分級処理工程における分級装置の除粉処理能力よりも大きな除粉処理能力を有すれば、分級処理工程における分級装置で微粉除去の手間が省け、各メッシュサイズに分級したリサイクル炭素繊維の回収率を高めることができる。 Further, in the present invention, it is preferable that the powder removal processing capacity of the powder removal device in the powder removal treatment step is greater than the powder removal processing capacity of the classification device in the classification treatment step. In order to efficiently remove the fine powder contained in the crushed pieces generated between the crushing process and the powder removal process, the powder removal device in the powder removal process uses a large screen mesh and a driving motor that gives vibration. It is also preferable to use a high-output one. If fine powder can be efficiently removed in the powder removal treatment process, the influence of fine powder can be minimized in each downstream process. In particular, if the powder removal processing capacity is greater than the powder removal processing capacity of the classifier in the classification process, the classification device in the classification process can save the trouble of removing fine powder, and the recovery rate of recycled carbon fibers classified into each mesh size. can increase
また、本発明において、各工程に微粉を吸引する吸引手段を更に設けることが好ましい。前述した除粉装置や分級装置以外の工程の搬送中等で発生する微粉をその都度吸引除去できるため、微粉に起因する装置の故障等が起こりにくくなったり、空気中に舞う微粉が極めて少なくなるため、作業者に優しい環境を提供することができる。微粉は大きさ1mm以下の目に見えないものが多く、作業者の肌に直接触れると、かゆくなったり、吸い込んでしまうと、健康被害におよぶ可能性がある。 Further, in the present invention, it is preferable to further provide suction means for sucking fine powder in each step. Since fine powder generated during transportation of processes other than the above-mentioned powder removal device and classifier can be sucked and removed each time, equipment failure due to fine powder is less likely to occur, and fine powder floating in the air is extremely small. , can provide a worker-friendly environment. Many of the fine powders are invisible with a size of 1 mm or less, and if they come into direct contact with the skin of workers, they may cause itching, and if they are inhaled, they may pose a health hazard.
次に、本発明を実施例によって説明するが、本発明はこれらの実施例に限定されるものではない。 EXAMPLES Next, the present invention will be described with reference to Examples, but the present invention is not limited to these Examples.
(実施例1)
東レ(株)製炭素繊維プリプレグ“トレカ(登録商標)プリプレグ”#3900―2Bを所定枚数積層した後、180℃で10時間硬化させた後に100mmx100mmx5mmのCFRP廃材を作製した。CFRP廃材を1軸の破砕機で破砕した後、8mmのスクリーンを通して所定の繊維長のCFRP破砕片を得た。その後、ホッパーにCFRP破砕片と粉体を貯蔵した後、エイクル(株)製ブリッジブレーカーをホッパー内で回転させながらロータリーバルブで400μmスクリーンメッシュを設置した(株)ダルトン製振動ふるい機(1003型)に定量供給した。この時100Aの粉体吸引配管を使用した。除粉前後の重量を測定し、粉体除去率を計算した。その結果、18%の粉体除去率であった。除粉後のCFRP除粉片をロータリーキルン方式の熱分解炉に投入して酸素濃度5%、熱処理温度520℃、加熱処理時間20分条件で熱分解を実施し、6時間継続して熱分解ができることを確認した。得られたリサイクル炭素繊維熱分解体の樹脂残留量は12%であった。リサイクル炭素繊維熱分解体を2つのスクリーンメッシュ(0.5mmと3mm)を取り付けた(株)ダルトン製振動ふるい機(1003型)で分級を行った。その後、φ20mmの円筒形で、中心間距離が30mmの磁力10000Gの磁石を4列に並べ、それらを4段重ねた除鉄処理装置((有)マグネットプラン製)を通して、除鉄を行うと長さ2mmの鉄片を4個回収することができた。得られたリサイクル炭素繊維厚みはシンワ測定(株)ノギス(品番19975)で測定した結果、120μmと0.6mmと1.4mmであった。最後に厚みが120μmと1.4mmのリサイクル炭素繊維分級体を混合させた後、ホソカワミクロン(株)製マイクロパルベライザ(AP-2DH)に通して粉砕した。
(Example 1)
After laminating a predetermined number of carbon fiber prepreg “Torayca (registered trademark) prepreg” #3900-2B manufactured by Toray Industries, Inc., and curing at 180° C. for 10 hours, a CFRP waste material of 100 mm×100 mm×5 mm was produced. After the CFRP waste material was crushed by a uniaxial crusher, it was passed through an 8 mm screen to obtain CFRP crushed pieces having a predetermined fiber length. After that, after storing the CFRP crushed pieces and powder in a hopper, a 400 μm screen mesh was installed with a rotary valve while rotating a bridge breaker manufactured by Ekele Co., Ltd. in the hopper. was metered to the At this time, a 100A powder suction pipe was used. The weight before and after powder removal was measured, and the powder removal rate was calculated. As a result, the powder removal rate was 18%. The powder-free CFRP pieces were put into a rotary kiln type pyrolysis furnace and thermally decomposed under the conditions of oxygen concentration of 5%, heat treatment temperature of 520 ° C., and heat treatment time of 20 minutes. Thermal decomposition continued for 6 hours. Confirmed that it can be done. The amount of residual resin in the obtained recycled carbon fiber pyrolyzate was 12%. The recycled carbon fiber pyrolyzate was classified with a vibrating sieve machine (1003 type) manufactured by Dalton Co., Ltd. equipped with two screen meshes (0.5 mm and 3 mm). After that, cylindrical magnets with a diameter of 20 mm and a magnetic force of 10,000 G with a center-to-center distance of 30 mm are arranged in four rows. Four pieces of iron with a thickness of 2 mm were recovered. The thickness of the obtained recycled carbon fiber was measured with a caliper (manufactured by Shinwa Measurement Co., Ltd., product number 19975) and found to be 120 μm, 0.6 mm and 1.4 mm. Finally, after mixing recycled carbon fiber classifiers having thicknesses of 120 μm and 1.4 mm, the mixture was pulverized through a Micro Pulverizer (AP-2DH) manufactured by Hosokawa Micron Corporation.
厚み0.6mmのリサイクル炭素繊維分級体は、コンパウンド化したリサイクル炭素繊維ペレットで平板を作成し、3点曲げ試験を行い、通常の炭素繊維カットファイバーを用いた成形品と同等の物性を得られることを確認した。 A recycled carbon fiber classifier with a thickness of 0.6 mm is obtained by making a flat plate from compounded recycled carbon fiber pellets, performing a three-point bending test, and obtaining the same physical properties as a molded product using ordinary carbon fiber cut fiber. It was confirmed.
本発明の方法によって回収した炭素繊維は、粉砕し、ゴムや熱可塑性樹脂中に混入してその耐摩擦性を向上させたり、セメント、モルタル、コンクリートなどに混入してその力学的特性を向上させたりするのに使用することができる。 The carbon fibers recovered by the method of the present invention are pulverized and mixed into rubber or thermoplastic resins to improve their abrasion resistance, or mixed into cement, mortar, concrete, etc. to improve their mechanical properties. can be used to
1 CFRP廃材
2 一次破砕機
3 二軸方式の刃
4 ベルトコンベヤ
5 二次破砕機
6 スクリーン
7 固定刃
8 回転刃
9 CFRP破砕片
10 粉体
11 破砕処理工程から搬送貯蔵工程にCFRP破砕片と粉体が移動する方向
12 ホッパー
13 搬送貯蔵工程から除粉処理工程にCFRP破砕片と粉体が移動する方向
14 除粉装置
14a スクリーンメッシュ
15 CFRP除粉片
16 除粉処理工程から熱分解工程にCFRP除粉片が移動する方向
17 粉体が回収される方向
18 熱分解炉ホッパー
19 熱分解炉ホッパーから熱分解炉にCFRP除粉片が移動する方向
20 熱分解炉
21 熱分解炉内でCFRP除粉片が移動する方向
22 リサイクル炭素繊維熱分解体
23 ガス処理装置
24 冷却搬送工程から分級処理工程にCFRP熱分解体が移動する方向
25 分級装置
26 最大厚みを含むリサイクル炭素繊維熱分解体
27 最大および最小の厚みを含まないリサイクル炭素繊維熱分解体
28 最小厚みを含むリサイクル炭素繊維熱分解体
30 攪拌羽
31 定量払い出し装置
32 粉体吸引配管
33 スクリューフィーダーのケーシング
34 スクリューフィーダーのスクリュー
35 ロータリーバルブのケーシング
36 ロータリーバルブのローター
37 リサイクル炭素繊維の上面概略図
38 リサイクル炭素繊維を繊維方向を中心に回転させた概略投影図
1 CFRP waste material 2 Primary crusher 3 Biaxial blade 4 Belt conveyor 5 Secondary crusher 6 Screen 7 Fixed blade 8 Rotary blade 9 CFRP crushed pieces 10 Powder 11 CFRP crushed pieces and powder from the crushing process to the transportation and storage process The direction in which the body moves 12 Hopper 13 The direction in which crushed CFRP pieces and powder move from the transportation and storage process to the powder removal treatment process 14 Powder removal device 14 a Screen mesh 15 CFRP powder removal pieces 16 From the powder removal treatment process to the thermal decomposition process CFRP Direction 17 in which powder removing pieces move Direction 18 in which powder is collected Pyrolysis furnace hopper 19 Direction 20 in which CFRP powder removing pieces move from the pyrolysis furnace hopper to the pyrolysis furnace Pyrolysis furnace 21 CFRP is removed in the pyrolysis furnace Direction in which powder pieces move 22 Recycled carbon fiber pyrolyzate 23 Gas treatment device 24 Direction in which CFRP pyrolyzate moves from the cooling transportation process to the classification process 25 Classifier 26 Recycled carbon fiber pyrolyzate including maximum thickness 27 Maximum And recycled carbon fiber pyrolyzate 28 not including minimum thickness Recycled carbon fiber pyrolyzer 30 including minimum thickness Stirring blade 31 Fixed quantity dispensing device 32 Powder suction pipe 33 Screw feeder casing 34 Screw feeder screw 35 Rotary valve Casing 36 Rotary valve rotor 37 Schematic top view of recycled carbon fiber 38 Schematic projection view of recycled carbon fiber rotated around the fiber direction
Claims (10)
(a)炭素繊維強化プラスチック廃材を破砕し所定の繊維長を有する炭素繊維強化プラスチック破砕片を作製する破砕処理工程
(b)前記炭素繊維強化プラスチック破砕片を風送式、ベルトコンベア式、バケットコンベア式いずれかの搬送方法でホッパーに送り貯蔵する搬送貯蔵工程
(c)前記炭素繊維強化プラスチック破砕片を前記ホッパーから除粉装置にスクリューフィーダー方式、ロータリーバルブ方式いずれかの方法で定量供給し、前記除粉装置にて前記炭素繊維強化プラスチック破砕片に含まれる粉体を除去し、炭素繊維強化プラスチック除粉片を生成する除粉処理工程
ここで、前記除粉処理工程において、前記ホッパーは攪拌羽と定量払い出し装置を具備し、前記除粉装置を構成する粉体吸引配管で詰まりを検出すると前記攪拌羽と前記定量払い出し装置の動作を停止し、前記炭素繊維強化プラスチック破砕片の前記除粉装置への供給を停止する
(d)前記炭素繊維強化プラスチック除粉片を熱分解炉に定量供給しながら加熱し、前記炭素繊維強化プラスチック除粉片に含まれる前記マトリックス樹脂成分を除去してリサイクル炭素繊維熱分解体を得る熱分解処理工程
(e)前記リサイクル炭素繊維熱分解体を冷却しながら次工程にベルトコンベア式、バケットコンベア式いずれかの方法で送る冷却搬送工程
(f)前記リサイクル炭素繊維熱分解体を分級してリサイクル炭素繊維分級体を得る分級処理工程
(g)前記リサイクル炭素繊維分級体から磁気力により金属粉を取り除く除鉄処理工程 A method for producing recycled carbon fibers for obtaining recycled carbon fibers from carbon fiber reinforced plastic containing carbon fibers and matrix resin components, comprising automating transportation between the following steps (a) to (g). A method for producing recycled carbon fiber.
(a) A crushing treatment step of crushing carbon fiber reinforced plastic waste to produce crushed carbon fiber reinforced plastic pieces having a predetermined fiber length (b) Pneumatic, belt conveyor, or bucket conveyor for the crushed carbon fiber reinforced plastic pieces (c) feeding the crushed pieces of carbon fiber reinforced plastic from the hopper to a powder removing device by a screw feeder method or a rotary valve method; A powder removal treatment step of removing powder contained in the crushed pieces of carbon fiber reinforced plastic with a powder removal device to generate powder removed pieces of carbon fiber reinforced plastic.
Here, in the powder removal treatment step, the hopper is equipped with a stirring blade and a fixed quantity dispensing device, and when clogging is detected in a powder suction pipe constituting the powder removing device, the stirring blade and the fixed quantity dispensing device are operated. stop and stop the supply of the carbon fiber reinforced plastic crushed pieces to the powder removing device
(d) Heating the carbon fiber reinforced plastic powder removing pieces while feeding them into a pyrolysis furnace to remove the matrix resin component contained in the carbon fiber reinforced plastic powder removing pieces to obtain recycled carbon fiber pyrolysates. Pyrolysis treatment step (e) cooling and transporting the recycled carbon fiber pyrolyzate to the next step by either belt conveyor or bucket conveyor while cooling (f) classifying the recycled carbon fiber pyrolyzate (g) an iron removal treatment step of removing metal powder from the recycled carbon fiber classified body by magnetic force;
量が7~17重量%である請求項1~3のいずれかに記載のリサイクル炭素繊維の製造方法。
樹脂残留量(%)=((1-樹脂焼き飛ばし後重量/樹脂焼き飛ばし前重量)x100) In the pyrolysis treatment step, a dry distillation treatment is performed with an oxygen concentration of 2 to 8%, a heat treatment temperature of 500 to 580 ° C., and a heat treatment time of 10 to 40 minutes. station
The method for producing recycled carbon fibers according to any one of claims 1 to 3, wherein the amount is 7 to 17% by weight.
Residual amount of resin (%) = ((1-weight after resin is burned off/weight before resin is burned off) x 100)
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