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JP2008189750A - Method for crushing waste material and device for the same, and method for treating the waste material and device for the same - Google Patents

Method for crushing waste material and device for the same, and method for treating the waste material and device for the same Download PDF

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JP2008189750A
JP2008189750A JP2007024115A JP2007024115A JP2008189750A JP 2008189750 A JP2008189750 A JP 2008189750A JP 2007024115 A JP2007024115 A JP 2007024115A JP 2007024115 A JP2007024115 A JP 2007024115A JP 2008189750 A JP2008189750 A JP 2008189750A
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waste
tank
crushing
heating
steam
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Tomoaki Ito
智章 伊藤
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Orient Instrument Computer Co Ltd
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling

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  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for crushing waste materials for crushing the waste materials of thermosetting resins, and a method for treating the waste materials and a device for the same. <P>SOLUTION: This waste material-crushing device 2 is equipped with a liquefying vessel 21 for heating the waste materials fed to the inside of the vessel, a steam-generating device 11 for filling the steam in the liquefying vessel 21 and a crushing device 22 for crushing the heated waste materials in the liquefying vessel 21. Also, the waste material-treating device 1 is provided by installing a vaporized material-taking out port 21a for taking out the volatilized vaporized material at the liquefying vessel 21 of the waste material-crushing device 2 and an oil and water-separating device 25 for separating the oils and water of the vaporized material taken out from the vaporized material-taking out port 21. <P>COPYRIGHT: (C)2008,JPO&INPIT

Description

この発明は、例えば熱硬化性樹脂の一種であるFRP(Fiber Reinforced Plastics)で形成された車のバンパーやモーターボートの筐体など、熱硬化性樹脂が原料となっている廃棄物を破砕するような廃棄物破砕方法とその装置、および廃棄物処理方法とその装置に関する。   The present invention, for example, crushes waste made from thermosetting resin, such as car bumpers and motor boat casings, which are made of FRP (Fiber Reinforced Plastics), which is a kind of thermosetting resin. The present invention relates to a waste crushing method and apparatus, and a waste treatment method and apparatus.

従来、使用の終了した廃棄物は、破壊等されて廃棄されるか、分別して再利用されている。廃棄物を破壊する方法としては、例えば、廃プラスチックを約140°で加熱し、廃プラスチック中の発砲スチロールを減容し、廃プラスチックを微粉砕する廃プラスチック分別回収方法が提案されている(特許文献1参照)。また、電子部品搭載プリント配線基板を低温乾留して可燃部分を炭化させ、冷却して破砕する電子部品搭載プリント配線基板の処理方法が提案されている(特許文献2参照)。   Conventionally, waste that has been used has been destroyed and discarded, or separated and reused. As a method for destroying the waste, for example, a waste plastic separation and recovery method is proposed in which the waste plastic is heated at about 140 °, the volume of foamed polystyrene in the waste plastic is reduced, and the waste plastic is pulverized (patent). Reference 1). In addition, a method for processing an electronic component-mounted printed wiring board has been proposed in which the electronic component-mounted printed wiring board is carbonized at a low temperature to carbonize the combustible portion, and is cooled and crushed (see Patent Document 2).

しかし、これらの方法は、車のバンパー、およびモーターボートの筐体等、熱硬化素材に難燃剤や熱可塑性素材を含有させた熱硬化性樹脂による廃棄物を破壊できるものではなかった。このため、このような部材による廃棄物は、破壊されずにそのまま廃棄されているのが現状であった。   However, these methods cannot destroy wastes caused by thermosetting resins containing flame retardants or thermoplastic materials in thermosetting materials such as car bumpers and motor boat casings. For this reason, the present condition is that the waste by such a member is discarded as it is, without destroying.

特開2000−153525号公報JP 2000-153525 A 特開2001−81519号公報JP 2001-81519 A

この発明は、上述の問題に鑑み、熱硬化性樹脂の廃棄物を破砕する廃棄物破砕方法とその装置、および廃棄物処理方法とその装置を提供することを目的とする。   In view of the above-described problems, an object of the present invention is to provide a waste crushing method and apparatus for crushing thermosetting resin waste, and a waste treatment method and apparatus.

この発明は、加熱槽内に蒸気を充満させる蒸気供給工程と、蒸気の充満している加熱槽の槽内に供給された廃棄物を加熱する加熱工程と、該前記加熱槽で加熱された廃棄物を破砕手段で破砕する破砕工程とを有する廃棄物破砕方法、およびその装置であることを特徴とする。   The present invention includes a steam supply process for filling a steam in a heating tank, a heating process for heating waste supplied in a tank of a heating tank filled with steam, and a waste heated in the heating tank. A waste crushing method having a crushing step of crushing an object with a crushing means, and an apparatus therefor.

またこの発明は、加熱槽内に蒸気を充満させる蒸気供給工程と、蒸気の充満している加熱槽の槽内に供給された廃棄物を加熱する加熱工程と、該前記加熱槽で加熱された廃棄物を破砕手段で破砕する破砕工程と、前記加熱槽内で揮発した気化物を取り出して該気化物を油水分離装置で油水分離する油水分離工程とを有する廃棄物処理方法、およびその装置であることを特徴とする。   Also, the present invention is a steam supply process for filling the heating tank with steam, a heating process for heating the waste supplied to the tank of the heating tank filled with steam, and the heating tank heated by the heating tank. A waste treatment method having a crushing step of crushing waste with a crushing means, and an oil-water separation step of taking out the vaporized material volatilized in the heating tank and separating the vaporized material with an oil-water separator, and the apparatus It is characterized by being.

この発明により、熱硬化素材に難燃剤や熱可塑性素材が含有された部材の廃棄物を破砕する廃棄物破砕方法とその装置、および廃棄物処理方法とその装置を提供することができる。   According to the present invention, it is possible to provide a waste crushing method and apparatus, and a waste treatment method and apparatus for crushing waste of a member in which a thermosetting material contains a flame retardant or a thermoplastic material.

この発明の一実施形態を以下図面と共に説明する。
図1は、廃棄物処理装置1および廃棄物破砕装置2の構成を示す構成図であり、図2は廃棄物処理装置1が実施する工程のフローチャートである。
An embodiment of the present invention will be described below with reference to the drawings.
FIG. 1 is a configuration diagram showing configurations of the waste treatment apparatus 1 and the waste crushing apparatus 2, and FIG. 2 is a flowchart of steps performed by the waste treatment apparatus 1.

廃棄物処理装置1には、水蒸気発生装置11と、減容槽12と、脱臭装置13と、油化槽21と、破砕装置22と、塩素除去装置23と、冷却装置24と、油水分離装置25と、油槽26と、ミックスチェンジャー27と、水槽28とが設けられている。
このうち、水蒸気発生装置11と、減容槽12と、油化槽21と、破砕装置22とにより、廃棄物破砕装置2が構成されている。
The waste treatment apparatus 1 includes a steam generator 11, a volume reduction tank 12, a deodorizing apparatus 13, an oiling tank 21, a crushing apparatus 22, a chlorine removing apparatus 23, a cooling apparatus 24, and an oil / water separation apparatus. 25, an oil tank 26, a mix changer 27, and a water tank 28 are provided.
Among these, the waste crushing apparatus 2 is comprised by the water vapor generator 11, the volume reduction tank 12, the oilification tank 21, and the crushing apparatus 22. FIG.

水蒸気発生装置11は、加熱した水蒸気を減容槽12と油化槽21に供給する水蒸気供給工程を実施する(ステップS1)。減容槽12に供給する水蒸気の温度は、図示省略する温度調整機構により、減容槽12の加熱温度(摂氏200°程度)と同一かほぼ同一の温度にしている。また、油化槽21に供給する水蒸気の温度は、図示省略する温度調整機構により、油化槽21の加熱温度(摂氏400°〜500°程度、好ましくは摂氏450°程度)と同一かほぼ同一の温度にしている。   The steam generator 11 performs a steam supply step of supplying the heated steam to the volume reduction tank 12 and the oilification tank 21 (step S1). The temperature of the water vapor supplied to the volume reduction tank 12 is set to the same or substantially the same temperature as the heating temperature (about 200 degrees Celsius) of the volume reduction tank 12 by a temperature adjusting mechanism (not shown). The temperature of the water vapor supplied to the oilification tank 21 is the same as or substantially the same as the heating temperature of the oilification tank 21 (about 400 to 500 degrees Celsius, preferably about 450 degrees Celsius) by a temperature adjusting mechanism (not shown). The temperature is at.

減容槽12は、投入口から投入された廃棄物を摂氏200°程度に加熱して容積を減少させる装置である。この減容槽12により減容工程(ステップS2)を実施する。この減容槽12の投入口は、FRP(Fiber Reinforced Plastics)、廃プラスチック、および廃油等の廃棄物の投入を許容する。この減容槽12の後段には、油化槽21が設けられており、減容槽12は、減容後の固形物および液体を油化槽21に送り出す。また、減容槽12は、臭気を伴う気体を後段の脱臭装置13に送り出す。   The volume reduction tank 12 is a device that reduces the volume by heating the waste introduced from the inlet to about 200 degrees Celsius. A volume reduction process (step S2) is performed by the volume reduction tank 12. The inlet of the volume reduction tank 12 allows the input of waste such as FRP (Fiber Reinforced Plastics), waste plastic, and waste oil. An oiling tank 21 is provided at the subsequent stage of the volume reducing tank 12, and the volume reducing tank 12 sends the solid and liquid after volume reduction to the oiling tank 21. Moreover, the volume reduction tank 12 sends out the gas with an odor to the deodorizing apparatus 13 of a back | latter stage.

脱臭装置13は、減容槽12から供給される気体を脱臭し燃焼して、クリーンにした気体を排気する。この脱臭装置13により脱臭工程(ステップS3)を実施する。この脱臭装置13は、脱臭と燃焼を1つの装置で実行しているが、脱臭装置と燃焼装置とを分けてこの順で設け、脱臭の後に燃焼する構成としてもよい。   The deodorizing device 13 deodorizes and burns the gas supplied from the volume reduction tank 12 and exhausts the cleaned gas. A deodorizing step (step S3) is performed by the deodorizing device 13. The deodorizing device 13 performs deodorization and combustion with a single device, but the deodorizing device and the combustion device may be provided separately in this order and burned after deodorization.

油化槽21は、減容槽12から供給される減容後の廃棄物を加熱して油化する油化工程(ステップS4)を実施する。この油化槽21は、槽(釜)自体の温度を摂氏400°〜500°程度、好ましくは摂氏450°程度に加熱し、水蒸気発生装置11から供給された同温度若しくはほぼ同温度の水蒸気を槽内に充満させ、この環境内で廃棄物を加熱する。   The oilification tank 21 performs an oilification process (step S4) in which the waste after volume reduction supplied from the volume reduction tank 12 is heated to oily. The oil tank 21 heats the temperature of the tank (kettle) itself to about 400 to 500 degrees Celsius, preferably about 450 degrees Celsius, and supplies the steam at the same temperature or substantially the same temperature supplied from the steam generator 11. The tank is filled and the waste is heated in this environment.

ここで、油化槽21の温度は、投入許容する廃棄物に含まれる可燃物が通常であれば燃える温度にまで上げることが好ましく、この実施例では、再生油としてA重油を取得する目的も加味して400°〜500°程度としている。   Here, it is preferable to raise the temperature of the oilification tank 21 to a temperature at which combustibles contained in the waste permitted to be charged are normally burned. In this embodiment, the purpose of acquiring A heavy oil as recycled oil is also used. Taking into account, it is set to about 400 ° to 500 °.

油化槽21の槽内の廃棄物は、水蒸気の存在により燃えることなく温度上昇する。そして、廃棄物中の油成分は揮発して気化物となり、気化物取出口21aから塩素除去装置23へ送られる。   The waste in the liquefaction tank 21 rises in temperature without burning due to the presence of water vapor. Then, the oil component in the waste is volatilized to become a vaporized substance, and is sent to the chlorine removing device 23 from the vaporized substance outlet 21a.

また、熱硬化性樹脂の一種であるFRP部材で構成された車のバンパーやモーターボートの筐体など、熱硬化性樹脂で構成された廃棄物については、加熱によって部材中に含有されている難燃性部材(ブロム)や熱可塑性部材が溶け、硬化材や金属類、臭素、三酸化アンチモンといった残留物質と分離する。従って、廃棄物の表面付近の難燃性部材や熱可塑性部材は廃棄物の外へ流れ出し、廃棄物の内側に埋設されている難燃性部材や熱可塑性部材といった成分は内部で分離して残る。
また、自動車等に用いられるタイヤの廃棄物が投入された場合も、ゴム系素材が溶けて液体となり、残留する固形物と分離される。
In addition, for wastes made of thermosetting resin, such as car bumpers and motor boat casings made of FRP members, which are a kind of thermosetting resin, the flame retardant contained in the members by heating The soluble material (bromine) and thermoplastic member melt and separate from residual materials such as hardeners, metals, bromine and antimony trioxide. Therefore, the flame-retardant member and thermoplastic member near the surface of the waste flow out of the waste, and components such as the flame-retardant member and thermoplastic member embedded inside the waste remain separated inside. .
Also, when tire waste used in automobiles or the like is thrown in, the rubber-based material melts into a liquid and is separated from the remaining solid matter.

この油化槽21により加熱された後に残留した固形物は、上述したように成分が分離して脆化した状態となっている。このため、例えば非常に硬く破砕の難しいFRPであっても、油化槽21から出てきた固形物は、普通人が素手で力を加えると破壊できる。従って、水蒸気発生装置11と減容槽12と油化槽21とで廃棄物脆化装置を構成することができる。   The solid matter remaining after being heated by the oil bath 21 is in a state where the components are separated and embrittled as described above. For this reason, even if it is FRP which is very hard and difficult to crush, for example, the solid matter that has come out of the oilification tank 21 can be destroyed when an ordinary person applies force with bare hands. Therefore, the waste embrittlement apparatus can be constituted by the steam generator 11, the volume reduction tank 12, and the oilification tank 21.

破砕装置22は、油化槽21で加熱されて残った固形物の供給を受け、この固形物を粉々に破砕する破壊工程(ステップS5)を実施する。ここで、FRP等の熱硬化性樹脂は、硬化材と可塑性材や難燃材が混合された素材であるため、通常であればそのまま破砕することが非常に困難である。しかし、油化槽21にて熱硬化性樹脂と難燃性部材や熱可塑性部材が分離することで、残留物である固形物は破壊しやすくなっている。また、タイヤについても、本来であれば破砕が困難であるが、ゴム系素材が溶け出しているために残った固形物は破壊しやすくなっている。従って、破砕装置22は、供給された固形物を問題なく容易に破砕することができる。   The crushing device 22 receives the supply of the solid matter that has been heated in the oil bath 21 and performs a breaking step (step S5) that crushes the solid matter into pieces. Here, since a thermosetting resin such as FRP is a material in which a curing material, a plastic material, and a flame retardant material are mixed, it is usually very difficult to crush as it is. However, since the thermosetting resin and the flame retardant member or the thermoplastic member are separated in the oilification tank 21, the solid matter that is a residue is easily destroyed. Also, tires are difficult to crush if originally intended, but the remaining solid matter is easily destroyed because the rubber-based material has melted. Therefore, the crushing device 22 can easily crush the supplied solid matter without any problem.

塩素除去装置23は、油化槽21の気化物取出口21aから供給された気化物の塩素(ハロゲン)を除去する塩素除去工程(ステップS6)を実施する。この塩素除去装置23は、塩素除去後の気化物を後段の冷却装置24へ送り出す。   The chlorine removing device 23 performs a chlorine removing step (step S6) for removing chlorine (halogen) from the vaporized material supplied from the vaporized material outlet 21a of the oil tank 21. The chlorine removing device 23 sends the vaporized material after chlorine removal to the subsequent cooling device 24.

冷却装置24は、塩素除去装置23から供給された気化物を冷却して液化する冷却工程(ステップS7)を実施する。この冷却装置24は、液化した液体を後段の油水分離装置25へ送り出す。   The cooling device 24 performs a cooling process (step S7) in which the vaporized material supplied from the chlorine removing device 23 is cooled and liquefied. The cooling device 24 sends the liquefied liquid to the oil / water separator 25 at the subsequent stage.

油水分離装置25は、冷却装置24から供給された液体の油水分離する油水分離工程(ステップS8)を実施する。この油水分離装置25は、分離された油を油槽26へ供給し、分離された水をミックスチェンジャー27へ供給する。   The oil / water separator 25 performs an oil / water separation step (step S <b> 8) for separating the liquid oil supplied from the cooling device 24. The oil / water separator 25 supplies the separated oil to the oil tank 26 and supplies the separated water to the mix changer 27.

油槽26は、油水分離装置25から供給された油を貯留し、この油を再生油として取り出し許容する。この実施例では、再生油としてA重油が得られる。また、油槽26は、一部の油を水蒸気発生装置11のバーナー用の油として再利用する。   The oil tank 26 stores the oil supplied from the oil / water separator 25 and allows the oil to be taken out as recycled oil. In this embodiment, A heavy oil is obtained as recycled oil. Further, the oil tank 26 reuses a part of the oil as the oil for the burner of the water vapor generator 11.

ミックスチェンジャー27は、油槽26から供給された水を分離して浄化する装置である。このミックスチェンジャー27は、浄化した水を後段の水槽28へ送り出す。   The mix changer 27 is a device that separates and purifies water supplied from the oil tank 26. The mix changer 27 sends the purified water to the subsequent water tank 28.

水槽28は、ミックスチェンジャー27から供給される水を貯留し、必要に応じて排水する装置である。また、水槽28の後段には水蒸気発生装置11が設けられており、水の一部を水蒸気発生装置11に再利用する。   The water tank 28 is a device that stores water supplied from the mix changer 27 and drains it as necessary. In addition, the water vapor generator 11 is provided at the subsequent stage of the water tank 28, and a part of the water is reused in the water vapor generator 11.

以上の構成と動作により、廃棄物処理装置1は、廃棄物を油化してA重油を取得することができ、かつ、廃棄物破砕装置2部分によりFRPなどの熱硬化性樹脂を破砕することができる。
熱硬化性樹脂の破砕は、水蒸気が充満している油化槽21にて加熱することで硬化性物質と難燃性部材や熱可塑性部材を分離させた後に行うため、本来非常に破砕が困難である熱硬化性樹脂を容易に破砕することができる。
With the above configuration and operation, the waste treatment apparatus 1 can liquefy the waste to obtain A heavy oil, and crush the thermosetting resin such as FRP by the waste crushing apparatus 2 portion. it can.
Crushing of the thermosetting resin is performed after separating the curable substance from the flame-retardant member and the thermoplastic member by heating in the oil bath 21 filled with water vapor. The thermosetting resin can be easily crushed.

また、油化槽21の槽内は、水蒸気が充満されて酸素が除去されているため、摂氏400°〜500°という高温に加熱しても可燃物が燃えることを防止できる。これにより、硬化性物質と難燃性部材や熱可塑性部材の分離の確実性を高めることができ、また、油化槽21の槽表面にすすが付くことを防止できる。   Moreover, since the inside of the oilification tank 21 is filled with water vapor and oxygen is removed, it is possible to prevent combustibles from burning even when heated to a high temperature of 400 to 500 degrees Celsius. Thereby, the certainty of isolation | separation of a sclerosing | hardenable substance, a flame-retardant member, and a thermoplastic member can be improved, and it can prevent that the tank surface of the oilification tank 21 is sooted.

この廃棄物処理装置1により、FRP、廃プラスチック、または廃油等を廃棄物として投入すれば、この廃棄物から油分と水分を抽出して再利用することができると共に、残った固形物を確実に破砕することができる。したがって、廃棄物を効率よく処理することができる。   If FRP, waste plastic, waste oil, or the like is introduced as waste by this waste treatment apparatus 1, oil and moisture can be extracted from this waste and reused, and the remaining solids can be reliably Can be crushed. Therefore, waste can be processed efficiently.

なお、以上の実施形態では、減容槽12と油化槽21を別々に設けたが、一体化して油化槽として設けても良い。この場合、廃棄物処理装置1および廃棄物破砕装置2を小型化することができる。   In addition, in the above embodiment, although the volume reduction tank 12 and the oilification tank 21 were provided separately, you may integrate and provide as an oilification tank. In this case, the waste treatment apparatus 1 and the waste crushing apparatus 2 can be reduced in size.

また、廃棄物処理装置1若しくは廃棄物破砕装置2は、病院や老人施設などの施設に設置して、減容化炭化装置として使用してもよい。この場合、例えばプラスチック、食器、シーツ、注射針など、病院で使用した廃棄物を減容槽12に投入すれば、減容化されて滅菌された破砕物が破砕装置22から排出されることになる。つまり、投入された廃棄物は、減容槽12で減容化され、油化槽21で炭化および滅菌され、破砕装置22に粉々に粉砕される。これにより、病院で用いられて菌が付着している可能性のある廃棄物を、安全に滅菌すると共に減容化することができ、その後の取り扱いを容易化することができる。   Further, the waste treatment apparatus 1 or the waste crushing apparatus 2 may be installed in a facility such as a hospital or an elderly facility and used as a volume-reducing carbonization apparatus. In this case, if wastes used in the hospital, such as plastic, tableware, sheets, and injection needles, are put into the volume reduction tank 12, the crushed material that has been reduced in volume and sterilized is discharged from the crushing device 22. Become. That is, the input waste is reduced in volume in the volume reduction tank 12, carbonized and sterilized in the oilification tank 21, and crushed into pieces by the crushing device 22. As a result, it is possible to safely sterilize and reduce the volume of waste that may be used in hospitals and to which bacteria are attached, and facilitate subsequent handling.

この発明の構成と、上述の実施形態との対応において、
この発明の蒸気供給手段は、実施形態の水蒸気発生装置11に対応し、
以下同様に、
加熱槽は、油化槽21に対応し、
槽は、油化槽21の釜に対応し、
気化物取出部は、気化物取出口21aに対応し、
破砕手段は、破砕装置22に対応し、
蒸気供給工程は、ステップS1に対応し、
加熱工程は、ステップS4に対応し、
破砕工程は、ステップS5に対応し、
油水分離工程は、ステップS8に対応するも、
この発明は、上述の実施形態の構成のみに限定されるものではなく、多くの実施の形態を得ることができる。
In correspondence between the configuration of the present invention and the above-described embodiment,
The steam supply means of the present invention corresponds to the steam generator 11 of the embodiment,
Similarly,
The heating tank corresponds to the oil tank 21,
The tank corresponds to the hook of the oilification tank 21,
The vaporization take-out part corresponds to the vaporization take-out port 21a,
The crushing means corresponds to the crushing device 22,
The steam supply process corresponds to step S1,
The heating process corresponds to step S4,
The crushing process corresponds to step S5,
The oil / water separation step corresponds to step S8,
The present invention is not limited only to the configuration of the above-described embodiment, and many embodiments can be obtained.

廃棄物処理装置および廃棄物破砕装置の構成図。The block diagram of a waste disposal apparatus and a waste crushing apparatus. 廃棄物処理装置が実施する工程のフローチャート。The flowchart of the process which a waste disposal apparatus implements.

符号の説明Explanation of symbols

1…廃棄物処理装置、2…廃棄物破砕装置、11…水蒸気発生装置、21…油化槽21a…気化物取出口、22…破砕装置、25…油水分離装置 DESCRIPTION OF SYMBOLS 1 ... Waste processing apparatus, 2 ... Waste crushing apparatus, 11 ... Water vapor generation apparatus, 21 ... Oilification tank 21a ... Vaporized material removal outlet, 22 ... Crushing apparatus, 25 ... Oil-water separation apparatus

Claims (9)

加熱槽内に蒸気を充満させる蒸気供給工程と、
蒸気の充満している加熱槽の槽内に供給された廃棄物を加熱する加熱工程と、
該前記加熱槽で加熱された廃棄物を破砕手段で破砕する破砕工程とを有する
廃棄物破砕方法。
A steam supply process for filling the heating tank with steam;
A heating step for heating the waste supplied into the tank of the heating tank filled with steam;
A waste crushing method comprising a crushing step of crushing the waste heated in the heating tank with a crushing means.
槽内に供給された廃棄物を加熱する加熱槽と、
該加熱槽内に蒸気を充満させる蒸気供給手段と、
前記加熱槽で加熱された廃棄物を破砕する破砕手段とを備えた
廃棄物破砕装置。
A heating tank for heating the waste supplied in the tank;
Steam supply means for filling the heating tank with steam;
A waste crushing device comprising crushing means for crushing waste heated in the heating tank.
前記廃棄物は、熱硬化性素材が含有されている部材である
請求項2記載の廃棄物破砕装置。
The waste crushing apparatus according to claim 2, wherein the waste is a member containing a thermosetting material.
前記加熱槽の槽温度と、前記蒸気供給手段で槽内に供給される蒸気の槽内での蒸気温度を同一若しくはほぼ同一にした
請求項2または3記載の廃棄物破砕装置。
The waste crushing apparatus according to claim 2 or 3, wherein the tank temperature of the heating tank and the steam temperature in the tank of the steam supplied into the tank by the steam supply means are the same or substantially the same.
前記槽温度と前記蒸気温度を約400°から500°とした
請求項4記載の廃棄物破砕装置。
The waste crushing apparatus according to claim 4, wherein the bath temperature and the steam temperature are about 400 ° to 500 °.
加熱槽内に蒸気を充満させる蒸気供給工程と、
蒸気の充満している加熱槽の槽内に供給された廃棄物を加熱する加熱工程と、
該前記加熱槽で加熱された廃棄物を破砕手段で破砕する破砕工程と、
前記加熱槽内で揮発した気化物を取り出して該気化物を油水分離装置で油水分離する油水分離工程とを有する
廃棄物処理方法。
A steam supply process for filling the heating tank with steam;
A heating step for heating the waste supplied into the tank of the heating tank filled with steam;
A crushing step of crushing the waste heated in the heating tank by crushing means;
A waste disposal method comprising: an oil / water separation step of taking out the vaporized material volatilized in the heating tank and separating the vaporized material with an oil / water separator.
槽内に供給された廃棄物を加熱する加熱槽と、
該加熱槽内に蒸気を充満させる蒸気供給手段と、
前記加熱槽で加熱された廃棄物を破砕する破砕手段とを備え、
前記加熱槽は、揮発した気化物を取り出す気化物取出部を有し、
該気化物取出部から取り出された気化物を油水分離する油水分離装置を備えた
廃棄物処理装置。
A heating tank for heating the waste supplied in the tank;
Steam supply means for filling the heating tank with steam;
Crushing means for crushing waste heated in the heating tank,
The heating tank has a vaporized substance take-out portion for taking out vaporized vaporized substances,
A waste treatment apparatus comprising an oil / water separator for separating the vaporized substance taken out from the vaporized substance take-out section into oil / water.
加熱槽内に蒸気を充満させる蒸気供給工程と、
蒸気の充満している加熱槽の槽内に供給された廃棄物を加熱する加熱工程とを有する
廃棄物脆化方法。
A steam supply process for filling the heating tank with steam;
A waste embrittlement method comprising: a heating step of heating waste supplied into a tank of a heating tank filled with steam.
槽内に供給された廃棄物を加熱する加熱槽と、
該加熱槽内に蒸気を充満させる蒸気供給手段とを備えた
廃棄物脆化装置。
A heating tank for heating the waste supplied in the tank;
A waste embrittlement apparatus comprising a steam supply means for filling the heating tank with steam.
JP2007024115A 2007-02-02 2007-02-02 Method for crushing waste material and device for the same, and method for treating the waste material and device for the same Withdrawn JP2008189750A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5865539B1 (en) * 2015-05-21 2016-02-17 株式会社三和商会 Fine dispersion compounding apparatus and fine dispersion compounding method

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5865539B1 (en) * 2015-05-21 2016-02-17 株式会社三和商会 Fine dispersion compounding apparatus and fine dispersion compounding method

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