JPH11192469A - Treatment of plastics, and solid fuel and reducing agent for ore obtained by the treatment - Google Patents

Treatment of plastics, and solid fuel and reducing agent for ore obtained by the treatment

Info

Publication number
JPH11192469A
JPH11192469A JP3027998A JP3027998A JPH11192469A JP H11192469 A JPH11192469 A JP H11192469A JP 3027998 A JP3027998 A JP 3027998A JP 3027998 A JP3027998 A JP 3027998A JP H11192469 A JPH11192469 A JP H11192469A
Authority
JP
Japan
Prior art keywords
plastic
plastics
temperature
low
cooling
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.)
Granted
Application number
JP3027998A
Other languages
Japanese (ja)
Other versions
JP3924897B2 (en
Inventor
Tatsuya Nobusawa
達也 信澤
Toshihide Suzuki
利英 鈴木
Masabumi Komatsu
正文 小松
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
JFE Steel Corp
Original Assignee
Kawasaki Steel Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kawasaki Steel Corp filed Critical Kawasaki Steel Corp
Priority to JP3027998A priority Critical patent/JP3924897B2/en
Publication of JPH11192469A publication Critical patent/JPH11192469A/en
Application granted granted Critical
Publication of JP3924897B2 publication Critical patent/JP3924897B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Abstract

PROBLEM TO BE SOLVED: To obtain a plastic treated material easy to pulverize by heating plastics at a specified temperature, then removing low boiling point components, and cooling and solidifying the residue. SOLUTION: In the case that solid fuel is produced from waste plastic and container packing material contained in municipal refuse, industrial waste, or the like, and waste plastics generated in a disassembling process of electric products, automobiles, or the like, when pulverizing the plastics, it is heated to a temperature of 150 deg.C or more, thereby cutting a part of bonding of the plastics by heat, or disentangling the entanglement of plastic molecules. After that, by removing decomposed products of the plastics and low boiling point components such as a plasticizer in the plastics, a plastic treated material easy to pulverize is obtained. The treated material obtained by removing the low boiling point components is preferably cooled and solidified from treating temperature at the removal of the low boiling point components to 100 deg.C or less within 10 min after start of cooling.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、粉砕が容易なプラ
スチック処理物を得ることが可能なプラスチックの処理
方法、および該処理方法によって得られる固体燃料、鉱
石用還元剤に関し、さらには、ポリ塩化ビニルなどの塩
素含有プラスチックを含むプラスチックを、実質的に塩
素を含有しないプラスチック処理物に転化することが可
能なプラスチックの処理方法、および該処理方法によっ
て得られる固体燃料、鉱石用還元剤に関する。
[0001] The present invention relates to a method for treating plastic from which a plastic product that can be easily pulverized can be obtained, and a solid fuel and an ore reducing agent obtained by the treatment method. The present invention relates to a plastic processing method capable of converting a plastic containing chlorine-containing plastics such as vinyl into a plastic processing product containing substantially no chlorine, and a solid fuel and an ore reducing agent obtained by the processing method.

【0002】[0002]

【従来の技術】近年の廃プラスチックの有効利用の一つ
の解決手段として、廃プラスチックから固体燃料を製造
する方法が考えられる。これは、プラスチックは、微粉
化することによって燃焼性が飛躍的に向上し、有用な燃
料資源となり得るからである。
2. Description of the Related Art As one solution to the effective use of waste plastics in recent years, a method of producing a solid fuel from waste plastics can be considered. This is because the plasticity of the plastic is significantly improved by pulverization, and can be a useful fuel resource.

【0003】プラスチックを固体燃料に転化する従来の
技術は、例えば「プラスチックス Vol.47, No.7, p60」
に解説されているように、プラスチックを直接粉砕機で
微粉砕するものである。しかし、この方法の場合、堅い
プラスチックを1〜2mmの粒度にまで粉砕しなければな
らず、しかもこの粉砕に多大の時間と費用を要し、ま
た、繊維状やフィルム状のプラスチックは粉砕が困難な
ため、別途、溶融固化後に粉砕しなければならず、工程
が複雑になるなどの問題があった。
A conventional technique for converting plastic to a solid fuel is described in, for example, "Plastics Vol. 47, No. 7, p60".
As described in the above, plastics are directly pulverized with a pulverizer. However, in this method, a hard plastic must be ground to a particle size of 1 to 2 mm, and this grinding requires a lot of time and expense, and it is difficult to grind a fibrous or film-like plastic. Therefore, it has to be separately pulverized after the solidification, which causes a problem that the process becomes complicated.

【0004】さらに、ポリ塩化ビニルなどの塩素を含有
するプラスチックは、焼却すると有害物質であるダイオ
キシンを発生し、加熱処理を行うと塩化水素ガスが発生
して容器や配管を腐食させるため、他のプラスチックと
は別にして、熱処理などによって脱塩化水素する必要が
ある。
Furthermore, plastics containing chlorine such as polyvinyl chloride generate dioxin, which is a harmful substance, when incinerated, and when heated, generate hydrogen chloride gas and corrode containers and pipes. Apart from plastic, it is necessary to dehydrochlorinate by heat treatment or the like.

【0005】[0005]

【発明が解決しようとする課題】本発明は、前記した従
来技術の問題点を解決し、フィルム類が混合していても
処理が可能で、しかも、脱塩化水素処理も同時に行え、
粉砕が容易なプラスチック処理物を得ることが可能なプ
ラスチックの処理方法、および該処理方法による固体燃
料、鉱石用還元剤を提供することを目的とする。
DISCLOSURE OF THE INVENTION The present invention solves the above-mentioned problems of the prior art, and enables processing even when films are mixed, and also allows simultaneous dehydrochlorination.
An object of the present invention is to provide a plastic processing method capable of obtaining a plastic processing product that can be easily pulverized, and a solid fuel and an ore reducing agent by the processing method.

【0006】[0006]

【課題を解決するための手段】本発明者らは、前記した
目的を達成するために各種方法を検討する過程で、プラ
スチックを150 ℃以上の温度に加熱することによって、
プラスチックの結合の一部が熱により切断されるか、ま
たはプラスチック分子鎖の絡み合いがほぐされ、さら
に、上記した加熱後、プラスチックの分解生成物やプラ
スチック中の可塑剤などの低沸点成分を除去することに
より、粉砕し易いプラスチック処理物を得ることが可能
であることを見出した。
Means for Solving the Problems In the course of studying various methods to achieve the above-mentioned object, the present inventors heated plastics to a temperature of 150 ° C. or more.
Part of the plastic bond is broken by heat or the entanglement of the plastic molecular chains is loosened, and after the above-mentioned heating, low boiling components such as decomposition products of the plastic and plasticizer in the plastic are removed. As a result, it has been found that it is possible to obtain a plastic processed product that is easily crushed.

【0007】また、異種のプラスチックを2種類以上併
用すると、熱処理工程で異種のプラスチック同士の溶
融、混合などが生じ、ポリマー鎖の配列が不規則にな
り、得られる処理物が脆くなり、この結果、粉砕し易い
プラスチック処理物が得られることを見出した。さらに
は、本発明によれば、熱処理工程で脱塩化水素も同時に
行え、低沸点成分の除去工程でプラスチック処理物から
塩化水素など塩素化合物を除去できるため、本発明のプ
ラスチック処理物を固体燃料などとして使用したときに
ダイオキシンや塩化水素ガスなどの発生もない。
When two or more different kinds of plastics are used in combination, melting and mixing of the different kinds of plastics occur in the heat treatment step, the arrangement of the polymer chains becomes irregular, and the resulting treated material becomes brittle. It was found that a plastic processed product that could be easily crushed was obtained. Furthermore, according to the present invention, dehydrochlorination can be simultaneously performed in the heat treatment step, and chlorine compounds such as hydrogen chloride can be removed from the plastic processed material in the low boiling point component removing step. There is no generation of dioxin or hydrogen chloride gas when used as.

【0008】すなわち、第1の発明は、プラスチックを
150℃以上の温度で加熱処理した後、低沸点成分を除去
し、冷却、固化することを特徴とするプラスチックの処
理方法である。第2の発明は、プラスチックを 150℃以
上の温度で加熱処理した後、低沸点成分を除去し、冷
却、固化した後、粉砕を施すことを特徴とするプラスチ
ックの処理方法である。
[0008] That is, the first invention uses plastic.
This is a plastic processing method characterized by removing low-boiling components after heating at a temperature of 150 ° C. or higher, and cooling and solidifying. The second invention is a method for treating plastic, which comprises subjecting the plastic to heat treatment at a temperature of 150 ° C. or higher, removing low-boiling components, cooling, solidifying, and then pulverizing.

【0009】前記した第1の発明、第2の発明において
は、低沸点成分を除去して得られた処理物を、低沸点成
分除去時の処理温度から冷却開始後10分以内に100 ℃以
下に冷却、固化することが好ましい。また、前記した第
1の発明、第2の発明においては、前記プラスチック
が、塩素含有プラスチックであることが好ましい。
In the first and second aspects of the present invention, the treated product obtained by removing the low-boiling components is cooled to 100 ° C. or less within 10 minutes after the start of cooling from the processing temperature at the time of removing the low-boiling components. It is preferable to cool and solidify. In the first and second aspects of the present invention, it is preferable that the plastic is a chlorine-containing plastic.

【0010】また、前記した第1の発明、第2の発明に
おいては、前記プラスチックが、二種類以上のプラスチ
ックを含む混合物であることが、より好ましい。さらに
は、前記した第1の発明、第2の発明においては、前記
プラスチックが、塩素含有プラスチックおよび該塩素含
有プラスチックとは異なる他の1種類以上のプラスチッ
クを含む混合物であることが、より好ましい。
In the first and second aspects of the present invention, it is more preferable that the plastic is a mixture containing two or more types of plastics. Further, in the first and second inventions described above, it is more preferable that the plastic is a mixture containing chlorine-containing plastic and at least one other plastic different from the chlorine-containing plastic.

【0011】さらに、前記した第1の発明、第2の発明
においては、前記した低沸点成分の除去方法として蒸留
法を用いることが好ましく、さらには、該蒸留法とし
て、被処理物の雰囲気圧力≦(大気圧−500Torr )の圧
力条件下での減圧蒸留法を用いることが、より好まし
い。さらに、前記した第1の発明、第2の発明において
は、プラスチックを 150℃以上の温度で加熱処理した
後、および/または低沸点成分を除去した後、処理物中
の不溶分を除去し、その後、冷却、固化することが、、
より好ましい。
Further, in the first and second aspects of the present invention, it is preferable to use a distillation method as a method for removing the low-boiling components, and furthermore, as the distillation method, it is preferable to use an atmospheric pressure of an object to be treated. It is more preferable to use a vacuum distillation method under a pressure condition of ≤ (atmospheric pressure-500 Torr). Further, in the above first and second inventions, after heat-treating the plastic at a temperature of 150 ° C. or more and / or after removing low-boiling components, insoluble components in the treated product are removed, After that, it can be cooled and solidified,
More preferred.

【0012】第3の発明は、前記した第1の発明、第2
の発明のプラスチックの処理方法で得られたプラスチッ
ク処理物である固体燃料である。第4の発明は、前記し
た第1の発明、第2の発明のプラスチックの処理方法で
得られたプラスチック処理物である鉱石用還元剤であ
る。
A third aspect of the present invention is the first aspect of the present invention,
A solid fuel which is a plastic processed product obtained by the method for processing a plastic according to the present invention. A fourth invention is a reducing agent for ore, which is a processed plastic product obtained by the method for processing a plastic according to the first invention or the second invention.

【0013】[0013]

【発明の実施の形態】以下、本発明を、本発明に係わる
プラスチック、熱処理工程、低沸点成分の除去工程、不
溶分の除去工程、冷却、固化工程および粉砕工程の順
に、さらに詳細に説明する。〔プラスチック:〕本発明
の対象とするプラスチックは、バージン材プラスチック
以外に、都市ゴミ、産業廃棄物などに含まれる廃プラス
チックや容器包装材料、および電機製品、自動車などの
解体の過程で発生する廃プラスチックなどが例示され
る。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention will be described in more detail below in the order of the plastic, heat treatment step, low boiling point component removing step, insoluble matter removing step, cooling, solidifying step and pulverizing step according to the present invention. . [Plastic:] In addition to virgin plastics, plastics that are subject to the present invention include waste plastics and container packaging materials contained in municipal waste and industrial waste, and waste generated in the process of dismantling electric appliances and automobiles. Plastic is exemplified.

【0014】具体的には、ポリエチレン、ポリプロピレ
ンなどのポリオレフィン、ポリ塩化ビニル、ポリスチレ
ン、ポリエチレンテレフタレート、ポリカーボネートお
よびナイロンやその他の熱可塑性樹脂や熱硬化性樹脂な
ど全てのものが適用可能であり、上記したプラスチック
の内のいずれか1種のみを用いることも可能であり、2
種以上を併用して用いることも可能である。
[0014] Specifically, all materials such as polyolefins such as polyethylene and polypropylene, polyvinyl chloride, polystyrene, polyethylene terephthalate, polycarbonate, nylon, and other thermoplastic resins and thermosetting resins are applicable. It is also possible to use only one of the plastics,
It is also possible to use more than one kind in combination.

【0015】なお、本発明の方法では、全てのプラスチ
ックが溶融状態で低分子化した状態になる必要はなく、
得られた固体燃料中に、熱硬化性樹脂などの一部不融物
が残存していても、粉砕などに著しい障害がなければよ
い。本発明では、異なる種類のプラスチック混合物を用
いることにより、後述する熱処理工程で、異種のプラス
チックの溶融、混合などが生じ、ポリマー鎖の配列が不
規則になり、得られるプラスチック処理物が脆くなり、
プラスチック処理物の粉砕がより容易になる。
In the method of the present invention, it is not necessary that all the plastics are in a molten state and have a low molecular weight.
Even if some infusible matter such as a thermosetting resin remains in the obtained solid fuel, it is sufficient if there is no significant obstacle to pulverization and the like. In the present invention, by using different types of plastic mixtures, in the heat treatment step described later, melting of different types of plastics, mixing, etc. occur, the arrangement of polymer chains becomes irregular, and the resulting plastic processed product becomes brittle.
It becomes easier to grind the processed plastic.

【0016】特に、本発明によれば、プラスチックに含
まれる塩素などのハロゲン元素は、処理中に塩化水素な
どのハロゲン化水素となり、分離が容易になるため、ポ
リ塩化ビニル、ポリ塩化ビニリデンなど塩素を含有する
塩素含有プラスチックが含まれていてもよい。したがっ
て、本発明によれば、廃プラスチックの選別が不要であ
り、この点でも、極めて有利である。
In particular, according to the present invention, a halogen element such as chlorine contained in a plastic becomes a hydrogen halide such as hydrogen chloride during processing and is easily separated, so that a chlorine element such as polyvinyl chloride or polyvinylidene chloride is used. May be contained. Therefore, according to the present invention, it is not necessary to sort waste plastic, which is also very advantageous.

【0017】すなわち、本発明の方法に従って処理を行
うと、実質的に塩素などのハロゲン元素をほとんど含ま
ないプラスチック処理物を得ることができる。また、本
発明で用いるプラスチックの形状寸法は、粗く粉砕した
ものでよく、10cm角程度の大きさで十分であり、一般的
な廃プラスチックでは、改めて粉砕する必要がなく、回
収されたままの状態で処理可能であり、フィルム状、シ
ート状、繊維状のプラスチックもそのままの形で処理で
きる。
That is, when the treatment is performed in accordance with the method of the present invention, a plastic processed product substantially containing almost no halogen element such as chlorine can be obtained. The shape and size of the plastic used in the present invention may be roughly pulverized, and a size of about 10 cm square is sufficient.In general, waste plastic does not need to be pulverized again, and is in a state of being recovered. And film-like, sheet-like and fibrous plastics can be treated as they are.

【0018】細かく破砕した方が加熱が容易になるが、
その分、破砕のコストは高くなる。 〔熱処理工程:〕プラスチックを 150℃以上の温度に加
熱する方法は特に限定されない。すなわち、プラスチッ
クを収納した容器を、単に加熱する方法やプラスチック
と高温の媒体を容器内で混合する方法など、いかなる方
法でもよい。
[0018] The finer crushing makes heating easier,
The cost of crushing increases accordingly. [Heat treatment step:] The method of heating the plastic to a temperature of 150 ° C. or higher is not particularly limited. That is, any method such as a method of simply heating a container containing plastic or a method of mixing plastic and a high-temperature medium in the container may be used.

【0019】高温媒体を用いる場合は、高温媒体として
熱風、熱砂などが例示される。熱砂などの固体の高温媒
体を用いた場合は、後工程に沈降分離法や濾過法などに
よる固液分離工程を組み込めばよい。処理温度は 150℃
以上である。プラスチックを 150℃以上の温度に加熱す
ることにより、プラスチックの結合の一部が熱により切
断されたり、プラスチック分子鎖の絡み合いがほぐされ
て、冷却後に得られる固形物の強度が弱まるものと考え
られ、さらに、異種のプラスチックが溶融、混合される
と、ポリマー鎖の配列が不規則になり、得られるプラス
チック処理物が脆くなり、粉砕が容易となる。
When a high-temperature medium is used, examples of the high-temperature medium include hot air and hot sand. When a solid high-temperature medium such as hot sand is used, a solid-liquid separation step such as a sedimentation separation method or a filtration method may be incorporated in a subsequent step. Processing temperature is 150 ℃
That is all. It is thought that heating plastic at a temperature of 150 ° C or higher may break some of the plastic bonds by heat or loosen the entanglement of the plastic molecular chains, weakening the strength of the solid obtained after cooling. Further, when different types of plastics are melted and mixed, the arrangement of polymer chains becomes irregular, the resulting plastic processed product becomes brittle, and pulverization becomes easy.

【0020】処理温度が 150℃未満では、冷却後に得ら
れるプラスチック処理物の硬さは元のプラスチックと殆
ど変わらず、その微粉砕が困難であり、処理温度が高い
程、前記結合の切断などがより多く生じると考えられ、
冷却後に得られるプラスチック処理物の粉砕性が良好と
なる。一方、処理温度が高すぎると、プラスチックのガ
ス化や油化によって、冷却後の固形物の収率が低下す
る。
If the processing temperature is lower than 150 ° C., the hardness of the plastic processed product obtained after cooling is almost the same as that of the original plastic, and it is difficult to pulverize the plastic. Is likely to occur more,
The pulverizability of the plastic processed product obtained after cooling is improved. On the other hand, if the treatment temperature is too high, the gasification or oilification of the plastic lowers the yield of the solid after cooling.

【0021】したがって、処理温度は 150℃以上と規定
するが、その上限は450 ℃とすることがよく、より好ま
しくは200 〜400 ℃、さらに好ましくは250 〜380 ℃の
温度範囲である。プラスチックは組成にも依存するが、
約140 ℃以上で、溶融状態となり、好ましくはこのとき
に撹拌・混合すれば、得られる物質の均質性が高まり、
また、前記した靱性の低下も促進され、冷却後に得られ
るプラスチック処理物の粉砕がより容易となる。
Therefore, the processing temperature is specified to be 150 ° C. or higher, but the upper limit is preferably 450 ° C., more preferably 200 to 400 ° C., and further preferably 250 to 380 ° C. Plastic depends on its composition,
Above about 140 ° C, it becomes a molten state, and if it is preferably stirred and mixed at this time, the homogeneity of the obtained substance is increased,
Further, the decrease in the toughness described above is also promoted, and the pulverized plastic product obtained after cooling becomes easier.

【0022】プラスチックを 150℃以上の温度に昇温し
た後は、 150℃以上の温度に一定時間保持することが好
ましい。この保持時間は長い方が脱塩化水素が確実に行
え、また、低沸点成分除去後に得られるプラスチック処
理物が脆くなるので好ましいが、長すぎるとプラスチッ
クの分解、ガス化が進行して目的とする固体の収率が低
下したり、設備の処理能力が低下するなどの問題が生じ
る。
After the temperature of the plastic is raised to 150 ° C. or higher, it is preferable to maintain the temperature at 150 ° C. or higher for a certain period of time. The longer the retention time, the more reliable the dehydrochlorination can be performed, and the more the processed plastic obtained after the removal of the low boiling components becomes brittle. Problems such as a decrease in the yield of the solid and a decrease in the processing capacity of the facility occur.

【0023】好ましい保持時間は10分〜6時間であり、
より好ましくは20分〜3時間である。熱処理を行ってい
る間は、撹拌や、空気または不活性ガスを用いたバブリ
ングを行った方が脱塩化水素が効率的に行われるので好
ましい。 〔低沸点成分の除去工程:〕前記した加熱処理の終了
後、プラスチックから低沸点成分を除去した後、冷却
し、プラスチック処理物の塊を得る。
The preferred holding time is between 10 minutes and 6 hours,
More preferably, it is 20 minutes to 3 hours. During the heat treatment, it is preferable to perform stirring or bubbling using air or an inert gas because dehydrochlorination is efficiently performed. [Low Boiling Component Removal Step:] After the completion of the above-described heat treatment, the plastic is subjected to removal of the low boiling component, followed by cooling to obtain a lump of the processed plastic.

【0024】この低沸点成分の除去工程で、プラスチッ
ク中の可塑剤、塩化水素などの反応生成物、プラスチッ
クの分解生成物などの低沸点成分が除去され、得られた
プラスチック処理物の粉砕性が向上する。また、常温で
液体の成分がプラスチック処理物中に残留していると粉
砕後に凝集が生じたり粉砕性が低下することがあるた
め、低沸点成分の除去を行う。
In the process of removing low boiling components, low boiling components such as plasticizers, reaction products such as hydrogen chloride, and decomposition products of plastics in the plastic are removed, and the pulverizability of the obtained processed plastic is reduced. improves. In addition, if a liquid component at room temperature remains in the processed plastic, coagulation may occur after pulverization or the pulverizability may be reduced. Therefore, low boiling components are removed.

【0025】低沸点成分の除去は、蒸留法、乾燥法など
を用いることができる。蒸留で行う場合は、簡単な単蒸
留でも可能であり、バッチ式、連続式いずれの方法でも
よい。いずれの場合でも、蒸留後に得られるピッチ状の
釜残は任意の方法で抜き出し、冷却して目的物であるプ
ラスチック処理物を得ることができる。
For the removal of the low-boiling components, a distillation method, a drying method and the like can be used. In the case of performing distillation, simple simple distillation is also possible, and either a batch method or a continuous method may be used. In any case, the pitch-shaped bottom obtained after distillation can be extracted by an arbitrary method and cooled to obtain a target plastic processed product.

【0026】蒸留温度は、150 〜400 ℃であることが好
ましい。蒸留温度は、より好ましくは200 〜400 ℃、さ
らに好ましくは250 〜380 ℃である。蒸留法としては、
常圧蒸留、減圧蒸留いずれでもかまわないが、減圧蒸留
の方が低沸点成分の除去効率が高いため好ましく、被処
理物の雰囲気圧力≦(大気圧−500Torr )の圧力条件下
での減圧蒸留法を用いることが、より好ましい。
The distillation temperature is preferably from 150 to 400 ° C. The distillation temperature is more preferably from 200 to 400 ° C, even more preferably from 250 to 380 ° C. As a distillation method,
Either normal pressure distillation or reduced pressure distillation may be used, but reduced pressure distillation is preferred because the efficiency of removing low-boiling components is higher, and reduced pressure distillation is performed under the condition of atmospheric pressure of the object to be treated ≦ (atmospheric pressure−500 Torr). It is more preferable to use

【0027】乾燥法で行う場合は、任意の大きさの容器
に収納し、キルン内で処理するなどの方法を用いること
が可能である。乾燥法の場合の処理温度は、150 〜400
℃が好ましい。乾燥法の場合の処理温度は、より好まし
くは200 〜400 ℃、さらに好ましくは250 〜380 ℃であ
る。
When the drying method is used, it is possible to use a method of storing in a container of an arbitrary size and treating in a kiln. The processing temperature for the drying method is 150 to 400
C is preferred. The treatment temperature in the case of the drying method is more preferably from 200 to 400 ° C, further preferably from 250 to 380 ° C.

【0028】本発明においては、噴霧乾燥法で低沸点成
分の除去を行うことも可能である。この場合、150 〜40
0 ℃の温度のプラスチックを噴霧させるのが好ましい。
低沸点成分の除去工程の温度が低すぎると、低沸点成分
の除去が困難となり、逆に、高すぎると、プラスチック
のガス化や油化が生じ、冷却後の固形物の収率が低下す
る。
In the present invention, it is possible to remove low-boiling components by a spray drying method. In this case, 150-40
It is preferred to spray the plastic at a temperature of 0 ° C.
If the temperature of the step of removing the low-boiling components is too low, it becomes difficult to remove the low-boiling components. Conversely, if the temperature is too high, gasification or oiling of the plastic occurs, and the yield of solids after cooling decreases. .

【0029】本工程で除去される低沸点成分は、プラス
チックが分解した低分子量成分、プラスチック中の可塑
剤などの添加剤や塩化水素などの反応生成物質である。
低沸点成分除去時の温度は、熱処理工程の温度と同一で
も異なっていてもよい。低沸点成分除去時の温度が熱処
理工程の温度より高い方が、低沸点成分を除去し易く、
好ましい。
The low-boiling components removed in this step are low-molecular-weight components obtained by decomposing the plastic, additives such as a plasticizer in the plastic, and reaction products such as hydrogen chloride.
The temperature at the time of removing the low boiling component may be the same as or different from the temperature of the heat treatment step. If the temperature at the time of low boiling point component removal is higher than the temperature of the heat treatment step, it is easy to remove the low boiling point component,
preferable.

【0030】〔不溶分の除去工程:〕本発明において
は、前記した熱処理工程後または低沸点成分の除去工程
後または両工程の後において、処理物から不溶分を除去
することが、より好ましい。前記した熱処理工程の後工
程および/または低沸点成分の除去工程の後工程とし
て、遠心分離法、静置分離法、濾過法などによる固液分
離工程を組み込んだ場合は、プラスチック中にガラス、
金属などの無機物や紙類などを含んでいても処理可能で
あり、例えば、金属キャップがついたままのボトル類を
も処理可能である。
[Step of Removing Insolubles:] In the present invention, it is more preferable to remove insolubles from the processed material after the above-mentioned heat treatment step or after the step of removing low boiling components or both steps. When a solid-liquid separation step such as a centrifugal separation method, a stationary separation method, or a filtration method is incorporated as a post-step of the heat treatment step and / or a post-step of removing the low-boiling-point component, glass,
It can be processed even if it contains an inorganic substance such as metal or paper, and for example, can also process bottles with a metal cap attached.

【0031】また、不溶分を除去することによって、金
属などの無機物が除去され、後工程における粉砕が容易
となるばかりでなく、含塩素量の少ないプラスチック処
理物が得られる。すなわち、ポリ塩化ビニルなどの塩素
含有プラスチックを脱塩化水素する場合、炭化物が生じ
易く、また、この炭化物中には塩素成分が含まれ易く、
前記した熱処理工程の後工程および/または低沸点成分
の除去工程の後工程において不溶分を除去することによ
って、得られるプラスチック処理物中の含塩素量をより
一層低減できる。
In addition, by removing the insoluble matter, inorganic substances such as metals are removed, and not only the pulverization in the subsequent step is facilitated, but also a plastic processed product having a small chlorine content is obtained. That is, when dechlorinating a chlorine-containing plastic such as polyvinyl chloride, a carbide is easily generated, and a chlorine component is easily contained in the carbide.
By removing insoluble components in the post-process of the heat treatment process and / or the post-process of removing the low boiling components, the chlorine content in the obtained plastic processed product can be further reduced.

【0032】〔冷却、固化工程:〕低沸点成分除去後の
処理物を冷却して、固化したプラスチック処理物を得
る。冷却方法、冷却速度は特には限定されないが、冷却
速度が速い方が、得られたプラスチック処理物が粉砕し
易いものになる。本発明においては、低沸点成分の除去
時の温度から100 ℃以下の温度迄冷却する時間を、冷却
開始から10分以内とすることが好ましい。
[Cooling and solidifying step:] The treated material after the removal of the low-boiling components is cooled to obtain a solidified plastic treated material. The cooling method and the cooling rate are not particularly limited, but the higher the cooling rate, the easier the obtained plastic processed product is to be crushed. In the present invention, it is preferable that the cooling time from the temperature at the time of removing the low-boiling components to a temperature of 100 ° C. or lower be within 10 minutes from the start of cooling.

【0033】〔粉砕工程:〕本発明においては、冷却、
固化したプラスチック処理物の塊を所定の大きさに粉砕
することが好ましい。この段階での粉砕は未処理のプラ
スチックの粉砕よりも極めて容易である。したがって、
あらゆるタイプの粉砕機で粉砕可能であり、例えばジョ
ークラッシャー、ロールクラッシャー、ボールミル、遠
心ミルなどを用いることができる。
[Pulverizing step:] In the present invention, cooling,
It is preferable to pulverize the lump of the solidified plastic processed product to a predetermined size. Grinding at this stage is much easier than grinding untreated plastic. Therefore,
It can be crushed by any type of crusher, for example, a jaw crusher, a roll crusher, a ball mill, a centrifugal mill and the like can be used.

【0034】粉砕後の粒度は使用対象に応じて決めれば
よく、所定の粒度となるように粒度調節を行えば、例え
ば、鉄鉱石などの鉱石還元剤、すなわち、高炉用の還元
剤などの原燃料や、ボイラー、キルンなどの燃焼用燃料
として使用できる。さらに、本発明の処理方法で得られ
たプラスチック処理物は、粉砕性が優れているため、上
記した用途以外にも、微粉で燃焼性に優れた固体燃料、
還元剤として使用できる。
The particle size after grinding may be determined according to the object to be used. If the particle size is adjusted to a predetermined particle size, for example, an ore reducing agent such as iron ore, that is, an original material such as a reducing agent for a blast furnace is used. It can be used as fuel or combustion fuel for boilers and kilns. Furthermore, the plastic processed product obtained by the processing method of the present invention is excellent in pulverizability, in addition to the above-mentioned applications, solid fuel excellent in flammability with fine powder,
Can be used as a reducing agent.

【0035】[0035]

【実施例】以下、本発明を実施例に基づいて具体的に説
明する。 (実施例1)内容積5lのステンレス製反応器に、ポリ
エチレン(フィルム状)、ポリプロピレン(板状)、ポ
リスチレン(板状)、ポリエチレンテレフタレート(繊
維状)を、それぞれ約10cm角または約10cm長に切断した
ものを各300g投入し、反応器外壁のヒーターによって昇
温を開始した。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be specifically described below based on embodiments. (Example 1) A polyethylene (film), polypropylene (plate), polystyrene (plate), and polyethylene terephthalate (fibrous) were placed in a stainless steel reactor having an internal volume of 5 liters to a length of about 10 cm square or about 10 cm, respectively. 300 g of each of the cut pieces was added, and heating was started by a heater on the outer wall of the reactor.

【0036】なお、上記した4種類のプラスチックの上
記配合量における混合物の成分分析値は、C:81wt%,
H:11wt%,O:8wt%であった。昇温開始後、反応器
内の温度が 180℃を超えた時点でプラスチックの大部分
が溶融したので撹拌を開始し、最終的には 330℃まで昇
温し、その温度で2時間保持した。
In addition, the component analysis value of the mixture of the above four kinds of plastics in the above-mentioned compounding amount is as follows: C: 81 wt%,
H: 11 wt%, O: 8 wt%. When the temperature inside the reactor exceeded 180 ° C. after the start of heating, stirring was started because most of the plastic was melted, and finally the temperature was raised to 330 ° C. and maintained at that temperature for 2 hours.

【0037】次に同温度で50Torr(絶対圧)の減圧蒸留
を2時間行い、その後、常温まで冷却した結果褐色の固
体が得られた。得られた褐色の塊状の固体5gを回転刃
式粉砕機に装入して粉砕したところ、容易に粉砕され、
粉砕時間20秒で平均粒径が1mmの微粉固体が得られた。
本実施例において使用したプラスチックの種類、形状、
寸法、反応器への投入量(:添加量)、その他の処理条
件および得られた塊の成分分析値、粉砕試験結果などの
試験結果を表1に示す。
Next, vacuum distillation at 50 Torr (absolute pressure) was carried out at the same temperature for 2 hours, and thereafter, the mixture was cooled to room temperature to obtain a brown solid. When 5 g of the obtained brown lump solid was charged into a rotary blade type pulverizer and pulverized, it was easily pulverized,
A pulverized solid having an average particle size of 1 mm was obtained in a grinding time of 20 seconds.
The type and shape of the plastic used in this example,
Table 1 shows the test results such as the dimensions, the amount charged to the reactor (: addition amount), other processing conditions, the component analysis values of the obtained lump, and the results of the pulverization test.

【0038】(実施例2〜12、比較例1、2)実施例1
とは配合量の異なる各種プラスチック(混合物の成分分
析値 C:73wt%,H:9wt%,O:7wt%,Cl:11wt
%)を用い、熱処理条件、脱低沸点成分の条件などを変
化させた以外は実施例1と同様に処理して、プラスチッ
ク処理物を得た。
(Examples 2 to 12, Comparative Examples 1 and 2) Example 1
And plastics with different blending amounts (Chemical analysis value of mixture: C: 73 wt%, H: 9 wt%, O: 7 wt%, Cl: 11 wt%)
%) And the same conditions as in Example 1 were used except that the heat treatment conditions and the conditions for the components having low boiling points were changed.

【0039】得られた塊状の固体を、実施例1と同じ粉
砕機を用いて粉砕し、粉砕時間と平均粒径を測定した。
本実施例、比較例において使用したプラスチックの種
類、形状、寸法、反応器への投入量(:添加量)、その
他の処理条件および得られた塊の成分分析値、粉砕試験
結果などの試験結果を表1に示す。
The obtained solid mass was pulverized using the same pulverizer as in Example 1, and the pulverization time and average particle size were measured.
Test results such as the type, shape and size of the plastic used in the present example and the comparative example, the input amount (: addition amount) to the reactor, other processing conditions, the component analysis value of the obtained lump, the pulverization test result, and the like. Are shown in Table 1.

【0040】(実施例13)ポリ塩化ビニル(成分分析値
C:41wt%,H:3wt%,O:0wt%,Cl:56wt%)
を、表1に示す条件下、実施例1と同様の方法で処理
し、得られた塊状のプラスチック処理物を評価した。得
られた塊の成分分析値、粉砕試験結果を表1に示す。
(Example 13) Polyvinyl chloride (analysis value of component C: 41 wt%, H: 3 wt%, O: 0 wt%, Cl: 56 wt%)
Was treated in the same manner as in Example 1 under the conditions shown in Table 1, and the obtained lump-shaped plastic processed product was evaluated. Table 1 shows the component analysis values and the pulverization test results of the obtained lump.

【0041】(実施例14)実施例2において、低沸点成
分除去後の処理物を、低沸点成分除去時の温度と同じ温
度で熱濾過を行い、固形の不溶分を除去した以外は実施
例2と同様にして処理物を得た後、冷却、固化した。得
られた塊の成分分析値、粉砕試験結果を表1に示す。
Example 14 The procedure of Example 2 was repeated, except that the treated product after the removal of the low-boiling components was subjected to hot filtration at the same temperature as the temperature at the time of the removal of the low-boiling components to remove solid insoluble components. After obtaining the treated product in the same manner as in 2, the sample was cooled and solidified. Table 1 shows the component analysis values and the pulverization test results of the obtained lump.

【0042】(比較例3)ポリエチレン(フィルム
状)、ポリプロピレン(板状)、ポリスチレン(板
状)、ポリ塩化ビニル(板状)、ポリエチレンテレフタ
レート(繊維状)を約1cm角または約10cm長に切断した
もの各10gを、一緒に回転刃式粉砕機に装入し粉砕を試
みた。
(Comparative Example 3) Polyethylene (film), polypropylene (plate), polystyrene (plate), polyvinyl chloride (plate), polyethylene terephthalate (fibrous) cut into about 1 cm square or about 10 cm length Each 10 g of the crushed product was put together in a rotary blade type crusher, and crushing was attempted.

【0043】しかし、フィルム状、繊維状のプラスチッ
クが回転刃に絡み付き、粉砕ができなかった。以上の結
果から、本発明の処理方法によって得られたプラスチッ
ク処理物は、粉砕が容易で、かつ塩素の含有量が少な
く、ボイラーやキルン用の固体燃料、鉄鉱石の還元剤な
どの用途向けとして優れたものであることがわかる。
However, the film-like or fibrous plastic was entangled with the rotary blade and could not be crushed. From the above results, the plastic processed product obtained by the processing method of the present invention is easily pulverized and has a low chlorine content, and is intended for applications such as solid fuel for boilers and kilns, and reducing agents for iron ore. It turns out that it is excellent.

【0044】[0044]

【表1】 [Table 1]

【0045】[0045]

【表2】 [Table 2]

【0046】[0046]

【表3】 [Table 3]

【0047】[0047]

【表4】 [Table 4]

【0048】[0048]

【表5】 [Table 5]

【0049】[0049]

【発明の効果】本発明によれば、従来の生プラスチック
を直接粉砕する方式における諸問題が大幅に改善され
る。すなわち本発明によれば下記〜の優れた効果が
得られる。 :例えば1〜2mm角へのプラスチックの直接微粉砕は
不要になり、10cm角程度への予備粉砕で十分である。
According to the present invention, various problems in the conventional method of directly pulverizing green plastic are greatly improved. That is, according to the present invention, the following excellent effects can be obtained. : For example, direct pulverization of plastic into 1 to 2 mm square is unnecessary, and preliminary pulverization to about 10 cm square is sufficient.

【0050】:冷却固化して得られるプラスチック処
理物は脆く、微粉砕が極めて容易である。 :フィルム状、繊維状のプラスチックでも他のプラス
チックと同時に処理できる。 :ポリ塩化ビニルなどの塩素含有プラスチックも同時
に処理することができる。
The plastic processed product obtained by cooling and solidifying is brittle and is extremely easy to pulverize. : Film and fibrous plastics can be processed simultaneously with other plastics. : Chlorine-containing plastics such as polyvinyl chloride can be treated at the same time.

【0051】:本発明の方法で得られるプラスチック
処理物は、粉砕性に優れ、塩素を実質的に含有しない微
粉を得ることができ、燃焼性に優れた無公害の燃料、還
元剤などとして用いることができる。また、本発明によ
れば、連続処理を行うことが可能であるため、複雑かつ
高価な装置を用いる必要がなく、また、大きな反応容器
を用いれば大量処理も可能であり、経済性にも優れてい
る。
The processed plastic product obtained by the method of the present invention is excellent in pulverizability, can obtain a fine powder substantially containing no chlorine, and is used as a non-polluting fuel, a reducing agent, etc. excellent in flammability. be able to. Further, according to the present invention, since continuous processing can be performed, it is not necessary to use a complicated and expensive apparatus, and if a large reaction vessel is used, a large amount of processing can be performed, and economic efficiency is excellent. ing.

Claims (9)

【特許請求の範囲】[Claims] 【請求項1】 プラスチックを 150℃以上の温度で加熱
処理した後、低沸点成分を除去し、冷却、固化すること
を特徴とするプラスチックの処理方法。
1. A method for treating a plastic, comprising heating the plastic at a temperature of 150 ° C. or higher, removing low-boiling components, cooling and solidifying the plastic.
【請求項2】 プラスチックを 150℃以上の温度で加熱
処理した後、低沸点成分を除去し、冷却、固化した後、
粉砕を施すことを特徴とするプラスチックの処理方法。
2. After the plastic is heat-treated at a temperature of 150 ° C. or higher, low boiling components are removed, and the plastic is cooled and solidified.
A method for treating plastic, which comprises crushing.
【請求項3】 低沸点成分を除去して得られた処理物
を、低沸点成分除去時の処理温度から冷却開始後10分以
内に100 ℃以下に冷却、固化することを特徴とする請求
項1または2記載のプラスチックの処理方法。
3. The treated product obtained by removing the low-boiling components is cooled and solidified to 100 ° C. or less within 10 minutes after the start of cooling from the processing temperature at the time of removing the low-boiling components. 3. The method for treating plastic according to 1 or 2.
【請求項4】 前記プラスチックが、塩素含有プラスチ
ックであることを特徴とする請求項1〜3いずれかに記
載のプラスチックの処理方法。
4. The method according to claim 1, wherein the plastic is a chlorine-containing plastic.
【請求項5】 前記プラスチックが、二種類以上のプラ
スチックを含む混合物であることを特徴とする請求項1
〜3いずれかに記載のプラスチックの処理方法。
5. The method according to claim 1, wherein the plastic is a mixture containing two or more plastics.
A method for treating plastic according to any one of claims 1 to 3.
【請求項6】 前記プラスチックが、塩素含有プラスチ
ックおよび該塩素含有プラスチックとは異なる他の1種
類以上のプラスチックを含む混合物であることを特徴と
する請求項1〜3いずれかに記載のプラスチックの処理
方法。
6. A plastic treatment according to claim 1, wherein said plastic is a mixture containing chlorine-containing plastic and at least one other plastic different from said chlorine-containing plastic. Method.
【請求項7】 プラスチックを 150℃以上の温度で加熱
処理した後、および/または低沸点成分を除去した後、
処理物中の不溶分を除去し、その後、冷却、固化するこ
とを特徴とする請求項1〜6いずれかに記載のプラスチ
ックの処理方法。
7. After heating the plastic at a temperature of 150 ° C. or higher and / or after removing low boiling components,
The method for treating plastic according to any one of claims 1 to 6, wherein insolubles in the treated material are removed, and thereafter, the material is cooled and solidified.
【請求項8】 請求項1〜7いずれかに記載のプラスチ
ックの処理方法で得られたプラスチック処理物である固
体燃料。
8. A solid fuel which is a plastic processed product obtained by the method for processing plastic according to claim 1.
【請求項9】 請求項1〜7いずれかに記載のプラスチ
ックの処理方法で得られたプラスチック処理物である鉱
石用還元剤。
9. A reducing agent for ore, which is a processed plastic product obtained by the method for processing a plastic according to any one of claims 1 to 7.
JP3027998A 1997-11-04 1998-02-12 Plastic processing method, solid fuel obtained by the processing method, ore reducing agent Expired - Lifetime JP3924897B2 (en)

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JP9-301975 1997-11-04
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JP2005280347A (en) * 2004-03-04 2005-10-13 Jfe Steel Kk Manufacturing method of solid waste plastic and ore reducer and solid fuel
JP2006022337A (en) * 1997-11-04 2006-01-26 Jfe Steel Kk Processing method for plastics and solid fuel and ore reducing agent using processed plastics
JP2006143773A (en) * 2004-11-16 2006-06-08 Kobe Steel Ltd Method for dechlorination treatment of waste plastic
JP2006327189A (en) * 2005-04-28 2006-12-07 Nippon Steel Corp Molding process for waste plastics and pyrolytic process for waste plastics
WO2007125626A1 (en) * 2006-04-27 2007-11-08 Nippon Steel Corporation Method of molding waste plastic and method of pyrolyzing waste plastic
JP2008238155A (en) * 2007-02-28 2008-10-09 Jfe Steel Kk Method for crushing waste plastic
JP2011056789A (en) * 2009-09-10 2011-03-24 Jfe Steel Corp Method for manufacturing waste plastics pulverized powder, and ore reducing agent or solid fuel
JP2014030824A (en) * 2005-08-29 2014-02-20 Jfe Steel Corp Mixed plastic powder and manufacturing method of the same

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006022337A (en) * 1997-11-04 2006-01-26 Jfe Steel Kk Processing method for plastics and solid fuel and ore reducing agent using processed plastics
JP4640014B2 (en) * 1997-11-04 2011-03-02 Jfeスチール株式会社 Method for producing ore reducing agent
JP2002038172A (en) * 2000-07-24 2002-02-06 Hideyo Kano Waste plastic fuel
JP2005280347A (en) * 2004-03-04 2005-10-13 Jfe Steel Kk Manufacturing method of solid waste plastic and ore reducer and solid fuel
JP2006143773A (en) * 2004-11-16 2006-06-08 Kobe Steel Ltd Method for dechlorination treatment of waste plastic
JP2006327189A (en) * 2005-04-28 2006-12-07 Nippon Steel Corp Molding process for waste plastics and pyrolytic process for waste plastics
JP2014030824A (en) * 2005-08-29 2014-02-20 Jfe Steel Corp Mixed plastic powder and manufacturing method of the same
WO2007125626A1 (en) * 2006-04-27 2007-11-08 Nippon Steel Corporation Method of molding waste plastic and method of pyrolyzing waste plastic
JP2008238155A (en) * 2007-02-28 2008-10-09 Jfe Steel Kk Method for crushing waste plastic
JP2011056789A (en) * 2009-09-10 2011-03-24 Jfe Steel Corp Method for manufacturing waste plastics pulverized powder, and ore reducing agent or solid fuel

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