JPH0978070A - Method for recycling plastic and method for producing carbon material for producing carbon electrode - Google Patents
Method for recycling plastic and method for producing carbon material for producing carbon electrodeInfo
- Publication number
- JPH0978070A JPH0978070A JP23743695A JP23743695A JPH0978070A JP H0978070 A JPH0978070 A JP H0978070A JP 23743695 A JP23743695 A JP 23743695A JP 23743695 A JP23743695 A JP 23743695A JP H0978070 A JPH0978070 A JP H0978070A
- Authority
- JP
- Japan
- Prior art keywords
- decomposition
- residue
- plastic
- carbon
- thermal decomposition
- 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
Classifications
-
- 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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E60/00—Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
- Y02E60/30—Hydrogen technology
- Y02E60/50—Fuel cells
-
- 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
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/141—Feedstock
- Y02P20/143—Feedstock the feedstock being recycled material, e.g. plastics
-
- 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
- Coke Industry (AREA)
- Manufacture Of Porous Articles, And Recovery And Treatment Of Waste Products (AREA)
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
- Carbon And Carbon Compounds (AREA)
- Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
- Electrodes For Compound Or Non-Metal Manufacture (AREA)
- Inert Electrodes (AREA)
- Processing Of Solid Wastes (AREA)
- Processing And Handling Of Plastics And Other Materials For Molding In General (AREA)
Abstract
(57)【要約】
【課題】 プラスチックの熱分解残渣を新たな用途に供
することができるプラスチックの再資源化方法を提供す
る。
【解決手段】 プラスチックを熱分解して分解生成物を
回収した後に残存する炭素質の固体分解残渣を700℃
以上で熱処理してコークス状炭素を得る。コークス状炭
素は分解生成物と混合し、成形、焼結を経て所望形状の
炭素電極を生成する。熱分解はアルカリ共存下で行い、
固体分解残渣の熱処理前に残渣の水洗を行う。
【効果】 プラスチックの分解残渣の電極製造用端素材
としての用途が見出され、廃プラスチックの処理が実用
化し易い。
(57) [Abstract] [PROBLEMS] To provide a method for recycling plastics, which allows the thermal decomposition residue of plastics to be used for a new purpose. SOLUTION: A carbonaceous solid decomposition residue remaining after thermally decomposing a plastic to recover a decomposition product is treated at 700 ° C.
The above is heat-treated to obtain coke-like carbon. The coke-like carbon is mixed with a decomposition product, and molded and sintered to form a carbon electrode having a desired shape. Pyrolysis is carried out in the presence of alkali,
The solid decomposition residue is washed with water before heat treatment. [Effect] Use of the decomposition residue of plastic as an end material for electrode production has been found, and treatment of waste plastic is easy to put into practical use.
Description
【0001】[0001]
【発明の属する技術分野】本発明は、産業廃棄物等に含
まれる廃プラスチック、特にポリ塩化ビニル樹脂を含む
廃プラスチックの処理・再資源化に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to the treatment and recycling of waste plastics contained in industrial wastes, especially waste plastics containing polyvinyl chloride resin.
【0002】[0002]
【従来の技術】近年、熱可塑性プラスチックを乾留熱分
解して燃料油として再利用する技術が開発され、多量に
発生する廃プラスチックのリサイクル方法として有望視
されている。廃プラスチックを熱分解した固形分解残渣
は埋立や道路舗装等に用いられる。2. Description of the Related Art In recent years, a technique has been developed in which a thermoplastic is pyrolyzed and pyrolyzed and reused as a fuel oil, and it is regarded as a promising method for recycling a large amount of waste plastic. The solid decomposition residue obtained by thermally decomposing waste plastic is used for landfills, road paving, etc.
【0003】[0003]
【発明が解決しようとする課題】ところが、廃プラスチ
ックにポリ塩化ビニル樹脂等の含ハロゲンプラスチック
が含まれると、塩素ガス等のハロゲン化物が生じるの
で、これを捕捉するために廃プラスチックには水酸化ナ
トリウム等のアルカリが添加される。この結果、分解残
渣にはハロゲンを中和した塩と共に余剰のアルカリが含
まれることになるので、埋立等に分解残渣を使用するた
めには、環境汚染等を引き起こさないように分解残渣か
ら余剰アルカリを十分に除去する必要がある。しかし、
余剰アルカリの除去には手間やコストがかかるので、残
渣を埋め立て処理に用いるのは経済的に見合わない。し
かし、もし、残渣から経済的により価値の高い製品を生
成できる他の用途があれば、廃プラスチックの熱分解に
よる再資源化の実用化が促進される。従って、分解残渣
の新たな用途の開発が求められている。However, when halogen-containing plastic such as polyvinyl chloride resin is contained in the waste plastic, halides such as chlorine gas are generated. An alkali such as sodium is added. As a result, the decomposition residue contains excess alkali along with halogen-neutralized salt.Therefore, in order to use the decomposition residue for landfilling, etc. Need to be removed sufficiently. But,
Since it takes time and cost to remove excess alkali, it is not economically economical to use the residue for landfill treatment. However, if there are other uses that can produce economically more valuable products from the residue, the practical application of recycling of waste plastics by thermal decomposition will be promoted. Therefore, there is a demand for the development of new uses for decomposition residues.
【0004】本発明は、この様な従来技術の課題を解決
するためになされたもので、プラスチックの熱分解残渣
を新たな用途に供することができるプラスチックの再資
源化方法を提供することを目的とするものである。The present invention has been made in order to solve the problems of the prior art as described above, and an object thereof is to provide a method for recycling plastics, which enables the thermal decomposition residue of the plastics to be used for a new purpose. It is what
【0005】[0005]
【課題を解決するための手段】上記目的を達成するため
に、本発明者らは鋭意研究を重ねた結果、熱分解後に得
られる炭素質固体残渣を炭素電極の製造に使用できるこ
とを見いだし、本発明の再資源化方法を発明するに至っ
た。[Means for Solving the Problems] In order to achieve the above object, the inventors of the present invention have conducted extensive studies, and as a result, found that a carbonaceous solid residue obtained after thermal decomposition can be used for producing a carbon electrode. The inventors have invented a method for recycling the invention.
【0006】本発明のプラスチックの再資源化方法は、
プラスチックを熱分解して油状生成物と炭素質の固体分
解残渣とを得る熱分解工程と、該固体分解残渣を700
℃以上で加熱する熱処理工程と、該固体分解残渣と前記
油状生成物とを混合し残渣成形物を形成する成形工程
と、前記残渣成形物を焼結して炭素電極を生成する焼結
工程とを有するものである。The plastic recycling method of the present invention is
A thermal decomposition step of thermally decomposing the plastic to obtain an oily product and a carbonaceous solid decomposition residue;
A heat treatment step of heating at not less than 0 ° C., a molding step of mixing the solid decomposition residue with the oily product to form a residual molded article, and a sintering step of sintering the residual molded article to generate a carbon electrode. Is to have.
【0007】又、本発明の炭素電極製造用炭素材の製造
方法は、プラスチックを熱分解して分解生成物を回収し
た後に残存する炭素質の固体分解残渣を700℃以上で
熱処理するものである。In the method for producing a carbon material for producing a carbon electrode of the present invention, the carbonaceous solid decomposition residue remaining after the thermal decomposition of the plastic to recover the decomposition products is heat-treated at 700 ° C. or higher. .
【0008】上記において、プラスチックはアルカリ存
在下で熱分解され、上記熱処理工程前に、固体分解残渣
を水洗する水洗工程を有する。In the above, the plastic is thermally decomposed in the presence of an alkali, and before the heat treatment step, there is a water washing step of washing the solid decomposition residue with water.
【0009】[0009]
【発明の実施の形態】プラスチックを熱分解し燃料油を
熱分解生成物として得た後の固体分解残渣を700℃以
上で加熱することにより残渣はコークス状炭素となり、
コークス状炭素に燃料油を加えて成形、焼結、形状加工
することによって所望形状の炭素電極が生成する。BEST MODE FOR CARRYING OUT THE INVENTION By heating a solid decomposition residue obtained by thermally decomposing a plastic to obtain a fuel oil as a thermal decomposition product at 700 ° C. or higher, the residue becomes coke-like carbon,
By adding fuel oil to coke-like carbon, shaping, sintering, and shaping, a carbon electrode having a desired shape is produced.
【0010】以下、本発明をさらに詳細に説明する。Hereinafter, the present invention will be described in more detail.
【0011】ポリ塩化ビニル(PVC)樹脂を加熱する
と、300℃付近で塩素元素の脱離が起こって塩化水素
が発生し、約400〜500℃で熱分解により油分(分
解の程度が低い場合には固形分も生じる)及びガス状分
解生成物が生成する。熱分解が終了した後には、固体の
分解残渣が残存する。ポリオレフィン系プラスチックや
他の樹脂においても概ね約400〜500℃で熱分解し
て油分が生成し、分解残渣が残存する。プラスチックの
熱分解で得られる油分は、炭素数が5〜22の脂肪酸、
パラフィンを含み、燃料油としての使用に適するもので
ある。熱分解前に予め300℃付近でプラスチックを加
熱することによって、プラスチックの脱塩素処理を行う
ことができる。When polyvinyl chloride (PVC) resin is heated, desorption of the chlorine element occurs at around 300 ° C. to generate hydrogen chloride, and at about 400 to 500 ° C., oil is decomposed by thermal decomposition (when the degree of decomposition is low, Also produces solids) and gaseous decomposition products are produced. After the thermal decomposition is completed, a solid decomposition residue remains. Polyolefin-based plastics and other resins are also thermally decomposed at about 400 to 500 ° C. to produce oil, and decomposition residues remain. The oil obtained by the thermal decomposition of plastic is a fatty acid having 5 to 22 carbon atoms,
It contains paraffin and is suitable for use as fuel oil. The plastic can be dechlorinated by heating the plastic in advance at around 300 ° C. before thermal decomposition.
【0012】ハロゲン化水素の捕捉及び有機塩素化合物
の生成防止のために、中和剤として塩基性金属水酸化物
が熱分解するプラスチックに添加される。塩基性金属水
酸化物としては、具体的には、水酸化ナトリウム、水酸
化カリウム、水酸化カルシウム、水酸化マグネシウム、
水酸化バリウム、水酸化リチウム等のアルカリが挙げら
れ、特に水酸化ナトリウム、水酸化カリウムのような強
アルカリが使用される。添加するアルカリの量は、モル
比に換算して、処理するプラスチックに含まれるハロゲ
ンの0.01倍から1.5倍の範囲に設定される。バッ
チ処理によってプラスチックを分解処理する場合に、プ
ラスチックが攪拌されないと、1〜1.5倍モルのアル
カリを添加する必要が生じ、予めプラスチックの脱塩素
処理を行うと、プラスチックに添加するアルカリの量を
当初の含有ハロゲンの0.5倍モル以下に抑えることが
できる。金属水酸化物の添加は、ポリエステル樹脂やエ
ポキシ樹脂のエーテル結合、エステル結合の分解を促進
して油化を促進する作用もある。又、プラスチックの熱
分解時にはPVC樹脂に通常含まれる可塑剤(フタル酸
ジエステル等)の無水物も生成するが、アルカリの添加
により無水物による配管等の閉塞が防止され、且つ、油
分の回収率が向上する。このような理由から廃プラスチ
ックの熱分解にはアルカリ添加が有効である。A basic metal hydroxide is added to the thermally decomposable plastic as a neutralizing agent in order to trap hydrogen halide and prevent the formation of organic chlorine compounds. As the basic metal hydroxide, specifically, sodium hydroxide, potassium hydroxide, calcium hydroxide, magnesium hydroxide,
Examples thereof include alkalis such as barium hydroxide and lithium hydroxide, and particularly strong alkalis such as sodium hydroxide and potassium hydroxide are used. The amount of alkali to be added is set in the range of 0.01 to 1.5 times the halogen contained in the plastic to be treated in terms of molar ratio. When decomposing plastics by batch processing, if the plastics are not agitated, it is necessary to add 1 to 1.5 times the molar amount of alkali, and if the plastics are dechlorinated beforehand, the amount of alkalis added to the plastics Can be suppressed to 0.5 times mol or less of the initially contained halogen. The addition of the metal hydroxide also has a function of promoting the decomposition of ether bonds and ester bonds of the polyester resin or the epoxy resin and promoting oil conversion. In addition, when the plastic is thermally decomposed, anhydrides of plasticizers (phthalic acid diester, etc.) usually contained in PVC resins are also generated, but addition of alkali prevents clogging of pipes and the like due to anhydrides, and oil recovery rate Is improved. For these reasons, alkali addition is effective for the thermal decomposition of waste plastic.
【0013】プラスチックの熱分解後には固体分解残渣
が残り、ポリオレフィン系プラスチックの分解残渣はP
VC樹脂の場合に比べて生成量が少ないが、PVCが共
存すると、分解残渣の量は極度に増加する。このような
固体分解残渣は炭素質であり、アルカリ共存下で熱分解
を行うと、分解残渣には余剰のアルカリ及び塩化ナトリ
ウム等の中和塩が含まれる。After the thermal decomposition of the plastic, a solid decomposition residue remains, and the decomposition residue of the polyolefin plastic is P
Although the amount produced is smaller than in the case of VC resin, the amount of decomposition residue increases extremely when PVC coexists. Such a solid decomposition residue is carbonaceous, and when it is thermally decomposed in the presence of an alkali, the decomposition residue contains excess alkali and neutralized salts such as sodium chloride.
【0014】分解残渣は、分解時の反応条件によってそ
の状態が異なり、特に、PVCの分解残渣は、分解中に
アルカリが存在しない場合には、堅固な扱い難いものと
なるが、アルカリを添加した場合には、比較的粉砕し易
い残渣が得られる。更に、分解残渣が適量のアルカリ存
在下で強熱されると、固体残渣の表面の活性が向上す
る。The state of the decomposition residue varies depending on the reaction conditions at the time of decomposition. Particularly, the decomposition residue of PVC becomes solid and difficult to handle when no alkali is present during the decomposition, but alkali is added. In some cases, a residue that is relatively easy to grind is obtained. Furthermore, when the decomposition residue is ignited in the presence of an appropriate amount of alkali, the surface activity of the solid residue is improved.
【0015】分解残渣中に含まれる余剰アルカリ及び塩
は、水又は温水で洗浄することにより溶出、分離され
る。又、プラスチックには鉛等の金属成分を微量含有す
るものがあり、これに起因して分解残渣に含まれる金属
成分も水洗により除去される。Excess alkali and salt contained in the decomposition residue are eluted and separated by washing with water or warm water. Some plastics contain a trace amount of a metal component such as lead, and the metal component contained in the decomposition residue due to this is also removed by washing with water.
【0016】固体残渣を更に約700℃以上、好ましく
は1000℃前後で強熱すると、残渣はコークス状の炭
素分となる。コークス状の残渣は、表面の活性が高く、
又、粉砕し易く成形加工等を容易に施すことができ、炭
素電極の製造に利用するのに最適である。適切な加熱時
間はバッチの大きさに起因する熱伝達の相違等によって
左右されるが、1時間程度あるいはそれ以上の間加熱を
維持するのが効果的である。When the solid residue is further ignited at about 700 ° C. or higher, preferably around 1000 ° C., the residue becomes a coke-like carbon content. Coke-like residue has high surface activity,
Further, it is easy to crush and can be easily subjected to molding and the like, which is most suitable for use in the production of carbon electrodes. The appropriate heating time depends on the difference in heat transfer due to the size of the batch, but it is effective to maintain the heating for about 1 hour or longer.
【0017】コークス状の炭素分は、前述の熱分解で得
られたパラフィン成分を含有する油分を添加して棒状等
の所定形状に成形加工する。炭素分を成形加工した後
に、油分を成形物に浸透させてもよい。成形加工が行い
易いように、あるいは、得られる炭素電極の物性を適宜
調節するために、必要に応じて、コークス状炭素分に黒
鉛、ピッチ等を混合して用いてもよい。この後、成形物
を焼結炉で約1000〜1200℃の範囲で焼結して冷
却し、カッティング等によって焼結物の形状を整えるこ
とにより、棒状、板状等の炭素材が得られる。この炭素
材は人造黒鉛電極として使用することに適している。The coke-like carbon content is molded into a predetermined shape such as a rod shape by adding the oil content containing the paraffin component obtained by the above-mentioned thermal decomposition. After molding the carbon content, the oil content may be permeated into the molded product. If necessary, graphite, pitch or the like may be mixed with the coke-like carbon component so as to facilitate the molding process or to appropriately adjust the physical properties of the obtained carbon electrode. After that, the molded product is sintered in a sintering furnace at a temperature of about 1000 to 1200 ° C., cooled, and the shape of the sintered product is adjusted by cutting or the like to obtain a rod-shaped or plate-shaped carbon material. This carbon material is suitable for use as an artificial graphite electrode.
【0018】上述の製造過程を経て、固有抵抗値が1
0.0μΩm以下、曲げ強さが1275N/cm2 の棒状
黒鉛電極を得ることができる。板状電極の場合には、固
有抵抗値が11.0μΩm以下、曲げ強さが1765N
/cm2 のものを得ることができる(参照:JIS R
7201)。Through the above manufacturing process, the specific resistance value is 1
A rod-shaped graphite electrode having a bending strength of not more than 0.0 μΩm and a bending strength of 1275 N / cm 2 can be obtained. In the case of a plate electrode, the specific resistance value is 11.0 μΩm or less and the bending strength is 1765N.
/ Cm 2 can be obtained (reference: JIS R
7201).
【0019】図1はプラスチックの再資源化装置1を示
し、この装置を用いてプラスチックを熱分解し分解残渣
を電極製造用炭素材に調整することができる。FIG. 1 shows an apparatus 1 for recycling plastics. By using this apparatus, the plastics can be thermally decomposed and the decomposition residues can be adjusted to carbon materials for electrode production.
【0020】再資源化装置1の熱分解槽3には、配送管
5が接続され、添加剤槽7が弁9を介して取付られてい
る。添加剤槽7は、含ハロゲン樹脂を含有するプラスチ
ックを分解する際に発生するハロゲン化水素を捕捉中和
するための金属水酸化物を収容する。更に、水、触媒な
どを収容してもよい。熱分解槽3には、更に配送管11
が圧力制御弁13を介して接続され、配送管11は容器
15に連結されている。更に、配送管11には恒温部1
7、温度制御装置19が取り付けられている。温度制御
装置19は、恒温部17に所定温度の媒体を送り、恒温
部の温度を一定に維持する。媒体は、エア、水、液体化
合物等、通常使用されるものを用いることができる。A delivery pipe 5 is connected to the thermal decomposition tank 3 of the recycling apparatus 1, and an additive tank 7 is attached via a valve 9. The additive tank 7 contains a metal hydroxide for capturing and neutralizing hydrogen halide generated when the plastic containing the halogen-containing resin is decomposed. Further, water, a catalyst, etc. may be stored. In the thermal decomposition tank 3, a delivery pipe 11 is further provided.
Are connected via a pressure control valve 13, and the delivery pipe 11 is connected to a container 15. Further, the delivery pipe 11 has a constant temperature part 1
7. A temperature control device 19 is attached. The temperature control device 19 sends a medium having a predetermined temperature to the constant temperature part 17 to keep the temperature of the constant temperature part constant. As the medium, those commonly used such as air, water and liquid compounds can be used.
【0021】上記装置の配送管11には更にポンプ21
が設けられ、容器15に圧力制御弁23が取り付けられ
ている。これらは、熱分解を2工程に分けて行う際に使
用される。この場合、圧力制御弁13は開放し、容器1
5は、熱分解槽3と同様の操作が可能なように加熱手段
が備え付けられる。熱分解を複数工程に分けて行うの
は、より高品質な生成物を得るために有効である。A pump 21 is further provided in the delivery pipe 11 of the above apparatus.
Is provided, and the pressure control valve 23 is attached to the container 15. These are used when carrying out thermal decomposition in two steps. In this case, the pressure control valve 13 is opened and the container 1
5 is equipped with a heating means so that the same operation as the thermal decomposition tank 3 can be performed. Performing thermal decomposition in multiple steps is effective for obtaining a higher quality product.
【0022】熱分解槽3には、熱分解反応中のプラスチ
ックの攪拌及び反応後の残渣の掻き取り・破砕に使用さ
れる攪拌装置を設けてもよい。又、熱分解槽3の底部
に、槽内の内容物の排出を制御するための開閉シャッタ
ー内容物を分離するフィルターを設けることもできる。The thermal decomposition tank 3 may be provided with a stirring device used for stirring the plastic during the thermal decomposition reaction and scraping and crushing the residue after the reaction. Further, a filter for separating the contents of the opening / closing shutter for controlling the discharge of the contents in the tank can be provided at the bottom of the thermal decomposition tank 3.
【0023】上記装置を用いて、例えば図2に示すフロ
ーに従って、プラスチックは処理される。まず、粉砕等
の前処理を適宜行った廃プラスチックAは、配送管5か
ら熱分解槽3へ供給され、金属水酸化物B等の添加剤が
添加剤槽7から樹脂に添加される。添加剤の量は弁9に
よって適宜調節される。廃プラスチックは、熱分解槽3
内で加熱され、熱分解(25)が行われ、気体状の分解生成
物で熱分解槽3が充満される。熱分解槽3内の圧力が所
定圧を越えると圧力制御弁13が開放されて気体状の分
解生成物が配送管11に放出されことによって反応系は
所定圧に規制される。従って、一定温度に熱分解槽3を
維持することにより、一定条件で反応が進行する。放出
された分解生成物は、恒温部17で冷却、凝縮されて、
容器15に燃料油等の液状の分解生成物Cとして蓄積さ
れる。Using the above apparatus, plastics are processed, for example, according to the flow shown in FIG. First, the waste plastic A that has been appropriately pretreated such as crushed is supplied from the delivery pipe 5 to the thermal decomposition tank 3, and an additive such as a metal hydroxide B is added to the resin from the additive tank 7. The amount of the additive is appropriately adjusted by the valve 9. Waste plastic is a thermal decomposition tank 3
It is heated inside to undergo thermal decomposition (25), and the thermal decomposition tank 3 is filled with gaseous decomposition products. When the pressure in the thermal decomposition tank 3 exceeds a predetermined pressure, the pressure control valve 13 is opened and a gaseous decomposition product is released to the delivery pipe 11, whereby the reaction system is regulated to a predetermined pressure. Therefore, by maintaining the thermal decomposition tank 3 at a constant temperature, the reaction proceeds under constant conditions. The released decomposition products are cooled and condensed in the constant temperature unit 17,
It is accumulated in the container 15 as a liquid decomposition product C such as fuel oil.
【0024】熱分解槽3内の分解残渣、余剰の金属水酸
化物及び塩の混合物Dには添加剤槽7から水Eが加えら
れ、洗浄される(27)。金属水酸化物及び塩を含んだ洗浄
液Fは洗浄後に分解残渣Gから分離除去される。熱分解
槽3内の分解残渣Gは更に700℃以上で加熱し(29)、
コークス状残渣Hが得られる。このコークス状残渣H
は、必要により更に金属成分を除去するために水E’で
洗浄し(27') 、洗浄液F’を除去して、コークス状炭素
H’が得られる。Water E is added from the additive tank 7 to the mixture D of the decomposition residue, excess metal hydroxide and salt in the thermal decomposition tank 3 to wash it (27). The cleaning liquid F containing the metal hydroxide and the salt is separated and removed from the decomposition residue G after cleaning. The decomposition residue G in the thermal decomposition tank 3 is further heated at 700 ° C. or higher (29),
A coke-like residue H is obtained. This coke residue H
Is washed with water E'to further remove metal components as needed (27 '), and the washing solution F'is removed to obtain coke-like carbon H'.
【0025】コークス状炭素H’は熱分解槽3から排出
され、適宜乾燥した後に黒鉛I及びピッチJを加え、分
解生成物Cを加えて十分混合する(29)。混合物は成形加
工機を用いて成形し(31)、焼結炉で1000〜1200
℃で焼結した(33)後、カッティング(35)によって所望形
状に整えることにより炭素棒あるいは炭素板Kが得られ
る。これを電極として使用する。The coke-like carbon H'is discharged from the thermal decomposition tank 3 and, after being appropriately dried, graphite I and pitch J are added, and decomposition product C is added and sufficiently mixed (29). The mixture is molded using a molding machine (31) and 1000-1200 in a sintering furnace.
After sintering (33) at 0 ° C., the carbon rod or carbon plate K is obtained by cutting (35) and shaping it into a desired shape. This is used as an electrode.
【0026】[0026]
【実施例】以下、実験例を参照して、本発明をさらに詳
細に説明する。尚、以下の例における単位「%」は、す
べて重量に基づいて示される。EXAMPLES The present invention will be described in more detail below with reference to experimental examples. The unit "%" in the following examples is all based on weight.
【0027】(実験例1)図1の装置を用い、ポリ塩化
ビニルを含む廃プラスチック50kgに水酸化ナトリウ
ム11kgを添加して、分解槽内で450℃に200分
間加熱した。廃プラスチックの熱分解によって生じたガ
スは凝縮器によって冷却され、30kgの液体が得られ
た。この液体はパラフィン成分を含有する油脂であっ
た。分解槽内には約20kgの黒色固形残渣が残った。(Experimental Example 1) Using the apparatus shown in FIG. 1, 11 kg of sodium hydroxide was added to 50 kg of waste plastic containing polyvinyl chloride, and heated at 450 ° C. for 200 minutes in a decomposition tank. The gas generated by the thermal decomposition of the waste plastic was cooled by the condenser and 30 kg of liquid was obtained. This liquid was a fat containing a paraffin component. About 20 kg of black solid residue remained in the decomposition tank.
【0028】上記黒色固形残渣に水100Lを加えて6
0分間煮沸した後に、水と固形残渣とを分離し、分離し
た水を分解槽から排出した。黒色固形残渣の重量は15
kg(乾燥重量換算)に減少した。分離した水には水酸
化ナトリウムが溶出していた。更に、黒色残渣をよく粉
砕して微粉化した後、1回につき15Lの純水を用いて
粉砕残渣を10回洗浄して残留金属成分及び塩類を除去
した。洗浄後の黒色残渣を1000℃で2時間加熱した
後冷却したところ、コークス状の炭素分14kgが得ら
れた。さらに、この一連の操作を繰り返して合計56k
gのコークス状の炭素分を得た。100 L of water was added to the above black solid residue to obtain 6
After boiling for 0 minutes, water and solid residue were separated, and the separated water was discharged from the decomposition tank. The weight of black solid residue is 15
It was reduced to kg (converted to dry weight). Sodium hydroxide was eluted in the separated water. Further, the black residue was well pulverized and pulverized, and then 15 L of pure water was used to wash the pulverized residue 10 times to remove residual metal components and salts. When the black residue after washing was heated at 1000 ° C. for 2 hours and then cooled, 14 kg of coke-like carbon was obtained. Furthermore, this series of operations is repeated for a total of 56k.
g of coke-like carbon was obtained.
【0029】上記炭素分に天然黒鉛4kg及びピッチ4
kgを添加し、更に、熱分解の際に得られた油脂16k
gを配合してよく混合し、成形加工機を用いて棒状に加
工した。この棒状成形物を焼結炉で1100℃に120
分間加熱して焼き固めた。これを切削加工して棒状電極
(呼び径=75mm、呼び長さ=1000mm)を形成し
た。4 kg of natural graphite and 4 pitches were added to the above carbon content.
16 kg of fats and oils obtained by pyrolysis
g was mixed and mixed well, and processed into a rod shape using a molding machine. This rod-shaped molded product is heated to 1100 ° C. for 120 hours in a sintering furnace.
Heat and bake for a minute. This was cut to form a rod-shaped electrode (nominal diameter = 75 mm, nominal length = 1000 mm).
【0030】ポリ塩化ビニルを含む別の廃プラスチック
を用いて上記と同じ操作を繰り返して得たコークス状の
炭素分を同様に天然黒鉛、ピッチ及び油脂と混合し、混
合物を板状に成形加工して焼結し、板状電極(長さ=2
50mm、幅=50mm、厚さ=20mm)を生成した。The coke-like carbon content obtained by repeating the same operation as above using another waste plastic containing polyvinyl chloride was similarly mixed with natural graphite, pitch and fat and oil, and the mixture was molded into a plate shape. And sinter the plate electrode (length = 2
50 mm, width = 50 mm, thickness = 20 mm).
【0031】上記棒状電極及び板状電極は、いずれも、
使用上有害な傷、ひび、割れは見られなかった。これら
の電極の固有抵抗及び曲げ強さを測定した。結果を表1
に示す。Both the rod-shaped electrode and the plate-shaped electrode are
No scratches, cracks, or cracks harmful to use were found. The specific resistance and bending strength of these electrodes were measured. Table 1 shows the results
Shown in
【0032】[0032]
【表1】 −−−−−−−−−−−−−−−−−−−−−−−−−−−−−− 固有抵抗 曲げ強さ 灰分 −−−−−−−−−−−−−−−−−−−−−−−−−−−−−− 棒状電極 9.0μΩm 1500N/m2 0.8% 板状電極 9.0μΩm 1900N/m2 0.15% −−−−−−−−−−−−−−−−−−−−−−−−−−−−−− 表1の結果はJIS R 7201に記載される基準に
適合するものであった。[Table 1] ------------------ Specific resistance, bending strength, ash content --------------- −−−−−−−−−−−−−−−−−−−− Rod electrode 9.0 μΩm 1500 N / m 2 0.8% Plate electrode 9.0 μΩm 1900 N / m 2 0.15% --- ---------------------------------------- The results in Table 1 were in conformity with the criteria described in JIS R7201.
【0033】(実験例2)図1の装置を用い、ポリ塩化
ビニルを含む廃プラスチック50kgに水酸化ナカリウ
ム15.4kgを添加して、分解槽内で450℃に20
0分間加熱した。廃プラスチックの熱分解によって生じ
たガスは凝縮器によって冷却され、30kgの液体が得
られた。この液体はパラフィン成分を含有する油脂であ
った。分解槽内には約25kgの黒色固形残渣が残っ
た。(Experimental Example 2) Using the apparatus shown in FIG. 1, 15.4 kg of sodium potassium hydroxide was added to 50 kg of waste plastic containing polyvinyl chloride, and the mixture was heated to 450.degree.
Heat for 0 minutes. The gas generated by the thermal decomposition of the waste plastic was cooled by the condenser and 30 kg of liquid was obtained. This liquid was a fat containing a paraffin component. About 25 kg of black solid residue remained in the decomposition tank.
【0034】上記黒色固形残渣に水100Lを加えて6
0分間煮沸した後に、水と固形残渣とを分離し、分離し
た水を分解槽から排出した。黒色固形残渣の重量は15
kg(乾燥重量換算)に減少した。分離した水には水酸
化カリウムが溶出していた。更に、黒色残渣をよく粉砕
して微粉化した後、1回につき15Lの純水を用いて粉
砕残渣を10回洗浄して残留金属成分及び塩類を除去し
た。洗浄後の黒色残渣を1000℃で2時間加熱した後
冷却したところ、コークス状の炭素分14kgが得られ
た。さらに、この一連の操作を繰り返して合計56kg
のコークス状の炭素分を得た。100 L of water was added to the above black solid residue to obtain 6
After boiling for 0 minutes, water and solid residue were separated, and the separated water was discharged from the decomposition tank. The weight of black solid residue is 15
It was reduced to kg (converted to dry weight). Potassium hydroxide was eluted in the separated water. Further, the black residue was well pulverized and pulverized, and then 15 L of pure water was used to wash the pulverized residue 10 times to remove residual metal components and salts. When the black residue after washing was heated at 1000 ° C. for 2 hours and then cooled, 14 kg of coke-like carbon was obtained. Furthermore, repeating this series of operations, a total of 56 kg
Coke-like carbon content was obtained.
【0035】上記炭素分に熱分解で得られた油脂16k
gと天然黒鉛4kgとピッチ4kgとを配合してよく混
合し、成形加工機を用いて棒状に加工した。この棒状成
形物を焼結炉で1100℃に120分間加熱して焼き固
めた。これを切削加工して棒状電極(呼び径=75mm、
呼び長さ=1000mm)を形成した。Oil and fat 16k obtained by pyrolyzing the above carbon content
g, 4 kg of natural graphite and 4 kg of pitch were mixed and mixed well, and processed into a rod shape using a molding machine. This rod-shaped molded product was heated to 1100 ° C. for 120 minutes in a sintering furnace to be baked and solidified. By cutting this, a rod-shaped electrode (nominal diameter = 75 mm,
Nominal length = 1000 mm) was formed.
【0036】ポリ塩化ビニルを含む別の廃プラスチック
を用いて上記と同じ操作を繰り返して得たコークス状の
炭素分を同様に油脂と混合し、混合物から成形・焼結工
程を経て、板状電極(長さ=250mm、幅=50mm、厚
さ=20mm)を同様に形成した。Coke-like carbon content obtained by repeating the same operation as above using another waste plastic containing polyvinyl chloride is similarly mixed with fat and oil, and the mixture is subjected to a forming / sintering step to obtain a plate-like electrode. (Length = 250 mm, width = 50 mm, thickness = 20 mm) were similarly formed.
【0037】上記棒状電極及び板状電極は、いずれも、
使用上有害な傷、ひび、割れは見られなかった。これら
の電極の固有抵抗及び曲げ強さを測定した。結果を表2
に示す。Both the rod-shaped electrode and the plate-shaped electrode are
No scratches, cracks, or cracks harmful to use were found. The specific resistance and bending strength of these electrodes were measured. Table 2 shows the results
Shown in
【0038】[0038]
【表2】 −−−−−−−−−−−−−−−−−−−−−−−−−−−−−− 固有抵抗 曲げ強さ 灰分 −−−−−−−−−−−−−−−−−−−−−−−−−−−−−− 棒状電極 9.0μΩm 1500N/m2 0.9% 板状電極 9.0μΩm 1900N/m2 0.15% −−−−−−−−−−−−−−−−−−−−−−−−−−−−−− 表2の結果はJIS R 7201に記載される基準に
適合するものであった。[Table 2] ------------------ Specific resistance Bending strength Ash ---------- −−−−−−−−−−−−−−−−−−−− Rod electrode 9.0 μΩm 1500 N / m 2 0.9% Plate electrode 9.0 μΩm 1900 N / m 2 0.15% --- ----------------------------------------- The results in Table 2 were in conformity with the criteria described in JIS R7201.
【0039】[0039]
【発明の効果】以上説明したように、本発明のプラスチ
ックの再資源化方法においては、熱分解反応に従って生
じる固体残渣の吸着能が高く、気体・液体の浄化用吸着
剤として利用することが可能となる。産業廃棄物に含ま
れる廃プラスチックを無駄なく再資源化することができ
るものであり、その工業的価値は極めて大である。As described above, in the plastic recycling method of the present invention, the solid residue produced by the thermal decomposition reaction has a high adsorption ability and can be used as a gas / liquid purification adsorbent. Becomes Waste plastic contained in industrial waste can be recycled without waste, and its industrial value is extremely large.
【図1】本発明の再資源化方法を実施する熱分解装置の
一例を示す概念図である。FIG. 1 is a conceptual diagram showing an example of a thermal decomposition apparatus for carrying out the recycling method of the present invention.
【図2】本発明の再資源化方法に従って得られる炭素材
から炭素電極を製造するプロセスの一例を示すフロー図
である。FIG. 2 is a flow chart showing an example of a process for producing a carbon electrode from a carbon material obtained according to the recycling method of the present invention.
1 熱分解装置 3 熱分解槽 7 添加剤槽 15 容器 17 恒温部 19 温度制御装置 21 ポンプ 1 Thermal Decomposition Device 3 Thermal Decomposition Tank 7 Additives Tank 15 Container 17 Constant Temperature Section 19 Temperature Control Device 21 Pump
フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C08J 11/12 ZAB 9547−4H C10G 1/10 11/16 CEV H01M 4/96 B C10G 1/10 C25B 11/12 H01M 4/96 B09B 3/00 ZAB // C25B 11/12 302A Continuation of front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display area C08J 11/12 ZAB 9547-4H C10G 1/10 11/16 CEV H01M 4/96 B C10G 1/10 C25B 11 / 12 H01M 4/96 B09B 3/00 ZAB // C25B 11/12 302A
Claims (3)
炭素質の固体分解残渣とを得る熱分解工程と、該固体分
解残渣を700℃以上で加熱する熱処理工程と、該固体
分解残渣と前記油状生成物とを混合し残渣成形物を形成
する成形工程と、前記残渣成形物を焼結して炭素電極を
生成する焼結工程とを有することを特徴とするプラスチ
ックの再資源化方法。1. A thermal decomposition step of thermally decomposing a plastic to obtain an oily product and a carbonaceous solid decomposition residue; a heat treatment step of heating the solid decomposition residue at 700 ° C. or higher; A method for recycling plastics, comprising: a molding step of mixing with an oily product to form a residual molded article; and a sintering step of sintering the residual molded article to generate a carbon electrode.
回収した後に残存する炭素質の固体分解残渣を700℃
以上で熱処理することを特徴とする炭素電極製造用炭素
材の製造方法。2. A carbonaceous solid decomposition residue remaining after the decomposition product is recovered by thermally decomposing a plastic at 700 ° C.
A method for producing a carbon material for producing a carbon electrode, which is characterized by performing heat treatment as described above.
アルカリ存在下で熱分解され、更に、前記熱処理工程前
に、固体分解残渣を水洗する水洗工程を有することを特
徴とする請求項1記載の製造方法。3. The method according to claim 1, wherein the plastic is thermally decomposed in the presence of an alkali in the thermal decomposition step, and a washing step of washing the solid decomposition residue with water is further carried out before the heat treatment step. .
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP23743695A JPH0978070A (en) | 1995-09-14 | 1995-09-14 | Method for recycling plastic and method for producing carbon material for producing carbon electrode |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP23743695A JPH0978070A (en) | 1995-09-14 | 1995-09-14 | Method for recycling plastic and method for producing carbon material for producing carbon electrode |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH0978070A true JPH0978070A (en) | 1997-03-25 |
Family
ID=17015338
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP23743695A Pending JPH0978070A (en) | 1995-09-14 | 1995-09-14 | Method for recycling plastic and method for producing carbon material for producing carbon electrode |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0978070A (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2021080151A (en) * | 2019-11-18 | 2021-05-27 | 阿部 良博 | Carbon-producing apparatus |
| JP2022071547A (en) * | 2020-10-28 | 2022-05-16 | 日本ゼトック株式会社 | Composite material and its manufacturing method |
-
1995
- 1995-09-14 JP JP23743695A patent/JPH0978070A/en active Pending
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2021080151A (en) * | 2019-11-18 | 2021-05-27 | 阿部 良博 | Carbon-producing apparatus |
| JP2022071547A (en) * | 2020-10-28 | 2022-05-16 | 日本ゼトック株式会社 | Composite material and its manufacturing method |
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