JP2005261993A - Treating system and treating method for pcb-polluted substance - Google Patents

Treating system and treating method for pcb-polluted substance Download PDF

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JP2005261993A
JP2005261993A JP2004073936A JP2004073936A JP2005261993A JP 2005261993 A JP2005261993 A JP 2005261993A JP 2004073936 A JP2004073936 A JP 2004073936A JP 2004073936 A JP2004073936 A JP 2004073936A JP 2005261993 A JP2005261993 A JP 2005261993A
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cleaning
pcb
solvent
tank
washing
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Takeshi Matsumura
豪 松村
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Mitsui and Co Ltd
Toyo Engineering Corp
Nichiyo Engineering Corp
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Mitsui and Co Ltd
Toyo Engineering Corp
Nichiyo Engineering Corp
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Abstract

<P>PROBLEM TO BE SOLVED: To provide an effective de-polluting method for a PCB-polluted substance. <P>SOLUTION: The treating system for de-polluting a washing object obtained by dismantling and/or crushing electric apparatuses containing PCB (polychlorobiphenyls) is provided with a washing tank, a solvent washing means, a steam washing means, a decompressing means, and a waste treating means. Washing or drying is performed in the washing tank where the washing or drying is performed in a prescribed temperature and pressure condition in the washing tank. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明はPCB汚染物の除染処理方法に関するものであって、詳しくは分別されたPCB汚染物を洗浄し、汚染物への残留洗浄剤(溶剤)、PCB濃度(PCB量)を効率良く低減する方法に関する。   The present invention relates to a method for decontamination of PCB contaminants. Specifically, the separated PCB contaminants are cleaned, and the residual cleaning agent (solvent) and PCB concentration (PCB amount) on the contaminants are efficiently reduced. On how to do.

PCBはその優れた化学的安定性、高耐熱性、電気絶縁性が良好などの特性を有していることから、電機機器のトランス、コンデンサの絶縁油、蛍光灯の安定器あるいは熱媒体等に多量に使用されてきた。しかしながら、PCBの人体への有害性が明らかになり、1974年までに製造、輸入、開放系用途での使用が禁止された。また、1992年には廃PCB、PCBを含む廃油およびPCB汚染物が、廃棄物処理法に基づき特別管理産業廃棄物に指定され、トランスをはじめ、PCB含有機器類やPCB含有廃油の相当量が事業所等で保管されている。   PCB has characteristics such as its excellent chemical stability, high heat resistance, and good electrical insulation, so it can be used as a transformer for electrical equipment, insulating oil for capacitors, ballasts for fluorescent lamps, or heat media. It has been used in large quantities. However, the harmful effects of PCBs on the human body became apparent, and by 1974, use in manufacturing, importing, and open systems was prohibited. In 1992, waste PCBs, waste oil containing PCBs and PCB contaminants were designated as specially managed industrial wastes based on the Waste Management Law, and a considerable amount of PCB-containing equipment and PCB-containing waste oil including transformers It is stored at offices.

さらに、「ポリ塩化ビフェニル廃棄物の適正な処理の推進に関する特別措置法」(2001年7月15日施行)により、PCB、PCBを含む廃油などを15年以内(2016年7月まで)に処理することが義務化された。PCBの処理については、保有者自ら又は環境事業団若しくは廃棄物の処理及び清掃に関する法律(廃棄物処理法)に基づく許可を受けたポリ塩化ビフェニルに係る特別管理産業廃棄物処分業者に委託して、適正にポリ塩化ビフェニルを処分しなければならないとされ、現在、各所で処理設備が建設され処分が始まっているところである。   Furthermore, according to the “Special Measures Law for Promotion of Proper Treatment of Polychlorinated Biphenyl Waste” (enforced on July 15, 2001), waste oil including PCB and PCB is treated within 15 years (until July 2016). It became mandatory to do. About disposal of PCB, we entrust with specially controlled industrial waste disposal contractor pertaining to polychlorinated biphenyl which received permission based on law (waste disposal law) about the disposal itself and environmental corporation or waste disposal and cleaning It is said that polychlorinated biphenyls must be disposed of properly, and treatment facilities are being constructed at various places and disposal is beginning.

PCBはポリ塩化ビフェニル化合物の総称であり、その分子内に保有する塩素の数やその位置の違いにより、理論的に209種の異性体が存在し、中でも、コプラナーPCBと呼ばれるPCBの毒性は極めて強く、ダイオキシン類として総称されるものの一つとされている。   PCB is a general term for polychlorinated biphenyl compounds, and there are theoretically 209 isomers depending on the number and position of chlorine in the molecule, and among them, the toxicity of PCB called coplanar PCB is extremely high. It is strongly regarded as one of the generic names for dioxins.

PCBに汚染された電気機器類を解体し、PCBを除去(除染)して電気機器類のリサイクルを行ったり、最終処分を行うための処理方法が多く考案されている(例えば、特許文献1参照)。このうち、紙に代表されるPCB油を含浸しやすいものを効率的に洗浄してPCB含有濃度を下げることが課題の一つとしてあり、そのための方法が各種提案されている。   Many processing methods have been devised for disassembling electrical equipment contaminated with PCB, removing (decontaminating) PCB, recycling electrical equipment, and performing final disposal (for example, Patent Document 1). reference). Among these, one of the problems is to efficiently wash what is easily impregnated with PCB oil typified by paper to lower the PCB content concentration, and various methods have been proposed.

特許文献1には、PCB汚染物を洗浄難易度毎に解体分別し、分別されたそれぞれのPCB汚染物に対して適切な洗浄処理等を施すことによって、効率的な洗浄処理等を実現して、PCB汚染物の除去処理を適切に行う方法が記載されている。特に、特許文献1の第二実施形態では、第一実施形態において説明されている洗浄方法に真空加熱乾燥処理を加えることによって、より高い除染処理を行うことを可能とした方法が開示されている(特許文献1段落[0067])。   In Patent Document 1, an efficient cleaning process and the like are realized by disassembling and separating PCB contaminants for each degree of cleaning difficulty and performing an appropriate cleaning process or the like on each separated PCB contaminant. , A method for appropriately performing a PCB contaminant removal process is described. In particular, the second embodiment of Patent Document 1 discloses a method that enables a higher decontamination process by adding a vacuum heat drying process to the cleaning method described in the first embodiment. (Patent Document 1, paragraph [0067]).

しかし、この特許文献1記載の処理方法では、洗浄槽と真空加熱炉とが別個独立に設けられているため(特許文献1段落[0084]等)、それぞれの設備が必要であり設立コストがかかるという問題があった。また、真空状態での浸漬洗浄(特許文献1段落[0045]等)をした後に、大気圧に戻して真空加熱炉に被処理物を搬送し、再び真空引きを行い、次いで200〜300℃程度に加熱し、窒素を添加して100〜200℃程度に冷却し、その後空気を炉内に入れて60℃程度以下まで冷却するという工程を行うため、洗浄槽および真空加熱炉における減圧、被処理物の搬送、並びに真空加熱炉での昇温および降温の時間が必要であり、処理に要する時間が必然的に長くなるという問題があった。
特開2003−285041号公報
However, in the processing method described in Patent Document 1, since the cleaning tank and the vacuum heating furnace are provided separately and independently (paragraph [0084] in Patent Document 1, etc.), each facility is required and the establishment cost is high. There was a problem. In addition, after immersion cleaning in a vacuum state (paragraph [0045] in Patent Document 1, etc.), the object is returned to atmospheric pressure, the object to be processed is transported to a vacuum heating furnace, evacuated again, and then about 200 to 300 ° C. In order to perform the process of cooling to about 100 to 200 ° C. by adding nitrogen and then cooling the air to about 60 ° C. or less by putting the air in the furnace, the pressure is reduced in the washing tank and the vacuum heating furnace. There is a problem in that it takes time to transport the objects and to raise and lower the temperature in the vacuum heating furnace, and the time required for the treatment is inevitably increased.
JP 2003-285041 A

本発明は、PCB汚染物の効率的な除染処理方法を提供することを目的とする。   An object of this invention is to provide the efficient decontamination processing method of PCB contaminant.

本発明者らは、鋭意検討を重ねた結果、PCBの沸点条件を実現する温度・圧力条件の下で、洗浄処理及び乾燥処理を洗浄槽において行うことにより、従来の除染処理方法よりも処理に必要な時間を短縮し、効率的にPCB汚染物を除染処理できることを見い出した。本発明は、このような知見に基づきなされるに至ったものである。   As a result of intensive investigations, the present inventors have performed a cleaning process and a drying process in a cleaning tank under a temperature / pressure condition that realizes a boiling point condition of PCB, so that the processing can be performed more than the conventional decontamination processing method. It has been found that PCB contamination can be efficiently decontaminated by shortening the time required for the process. The present invention has been made based on such findings.

すなわち、本発明は、
(1)PCBを含有した電気機器を解体および/または破砕して得られた洗浄対象物を除染処理する処理システムであって、洗浄槽、溶剤洗浄手段、蒸気洗浄手段、減圧手段、および廃棄処理手段を具備し、該洗浄槽において洗浄・乾燥手段が一定の温度圧力条件下で行われることを特徴とするPCB汚染物の処理システム、
(2)前記洗浄槽における洗浄・乾燥手段が、13322Pa(100Torr)〜1333(10Torr)に減圧して洗浄を行い、洗浄対象物温度が110〜150℃になるように加熱した後に、その温度でPCBが蒸発する圧力に圧力を調節して、PCB及び溶剤を除去することにより行われることを特徴とする(1)項に記載のPCB汚染物の処理システム、
(3)前記電気機器がトランス又はコンデンサであることを特徴とする(1)又は(2)項に記載のPCB汚染物の処理システム、
(4)溶剤が炭化水素系であることを特徴とする(1)〜(3)のいずれか1項に記載のPCB汚染物の処理システム、および
(5)前記(1)〜(4)のいずれか1項に記載の処理システムを用いたことを特徴とするPCB汚染物の処理方法
を提供するものである。
なお、本明細書においてPCBとは、PCB自体およびPCBを含んだ絶縁油をいう。また、本明細書において、紙類や木、ゴム、プラスチックの中で油を含みやすい構成要素を含浸性部材ともいい、金属(鉄、銅など)、比較的油を含みにくい(含まない)構成要素を非含浸性部材ともいう。
That is, the present invention
(1) A processing system for decontaminating an object to be cleaned obtained by disassembling and / or crushing an electrical device containing PCB, including a cleaning tank, a solvent cleaning unit, a steam cleaning unit, a decompression unit, and a disposal A PCB contaminant treatment system comprising a treatment means, wherein the washing and drying means are performed under a constant temperature and pressure condition in the washing tank;
(2) The cleaning / drying means in the cleaning tank performs cleaning by reducing the pressure to 13322 Pa (100 Torr) to 1333 (10 Torr), and heats the object to be cleaned to 110 to 150 ° C. The PCB contaminant treatment system according to item (1), which is performed by adjusting the pressure to a pressure at which PCB evaporates and removing PCB and solvent.
(3) The PCB contaminant treatment system according to (1) or (2), wherein the electrical device is a transformer or a capacitor,
(4) The PCB contaminant treatment system according to any one of (1) to (3), wherein the solvent is a hydrocarbon system, and (5) the above (1) to (4) The present invention provides a method for treating PCB contaminants, characterized in that the treatment system according to any one of the above items is used.
In the present specification, PCB means PCB itself and insulating oil containing PCB. In this specification, a component that easily contains oil in paper, wood, rubber, and plastic is also referred to as an impregnating member, and is a metal (iron, copper, etc.) that is relatively difficult to contain (does not contain) oil. The element is also referred to as a non-impregnated member.

本発明の処理方法によれば、洗浄槽内で洗浄処理及び乾燥処理を行うことにより装置を簡素化することができ、かつ、洗浄開始から乾燥終了までの時間を、具体的には約3時間以内にまで短縮することができ、低コストで効率的にPCB汚染物の除染処理を行うことができる。また、本発明の処理方法は、処理条件を低温で実施できるため、紙などの有機質の構成要素を処分しやすいという効果を奏する。
本発明は、従来PCB濃度を低減する処理(洗浄・乾燥等)に多くの時間がかかっていた含浸性部材の処理を改善するものであり、また、非含浸性部材に対しても適用できるものである。
According to the processing method of the present invention, the apparatus can be simplified by performing the cleaning process and the drying process in the cleaning tank, and the time from the start of cleaning to the end of drying is specifically about 3 hours. PCB contamination can be efficiently decontaminated at a low cost. In addition, since the treatment method of the present invention can be carried out at a low temperature, the organic constituent elements such as paper can be easily disposed of.
The present invention improves the treatment of impregnating members that previously took a lot of time to reduce the PCB concentration (cleaning, drying, etc.), and can also be applied to non-impregnating members. It is.

本発明のシステムの好ましい実施の態様について、添付の図面に基づいて詳細に説明をする。図1は、本発明のシステムの構成概念図である。図1に示すように、本発明のシステムは、洗浄槽1、溶剤洗浄手段2、蒸気洗浄手段3、減圧手段4、および廃棄処理手段5を具備する。
洗浄槽1には、槽内部を減圧するための減圧手段4、槽内部に洗浄液が入出される溶剤洗浄手段2、溶剤洗浄手段2の洗浄液を気化させ槽内部に送り込む蒸気洗浄手段3が接続されている。減圧手段4には、回収し再生した溶剤を送り込むために溶剤洗浄手段2が接続されており、また、濃縮・減量された第二次PCB汚染物を廃棄処理するための廃棄処理手段5が接続されている。
Preferred embodiments of the system of the present invention will be described in detail with reference to the accompanying drawings. FIG. 1 is a conceptual diagram of the configuration of the system of the present invention. As shown in FIG. 1, the system of the present invention includes a cleaning tank 1, a solvent cleaning means 2, a steam cleaning means 3, a decompression means 4, and a disposal processing means 5.
Connected to the cleaning tank 1 are a decompression means 4 for decompressing the inside of the tank, a solvent cleaning means 2 for entering and leaving the cleaning liquid into the tank, and a vapor cleaning means 3 for vaporizing the cleaning liquid of the solvent cleaning means 2 and feeding it into the tank. ing. Solvent cleaning means 2 is connected to the decompression means 4 in order to send the recovered and regenerated solvent, and a disposal processing means 5 for discarding the concentrated and reduced secondary PCB contaminants. Has been.

(洗浄対象物)
洗浄対象物としては、トランス(変圧器)やコンデンサを構成する、例えば金属、碍子等の陶器、鉄芯、トランス・コンデンサ本体(容器)、コイルの銅線・絶縁紙、ゴム・プラスチックなどの樹脂類、絶縁用の木やその他の有機質(紙、紙の加工品等)、ボルト、ネジやコンデンサ素子のアルミ箔、絶縁紙、樹脂フィルムなどが挙げられる(これらを総称して解体物という)。これらの解体物、解体物を破砕処理したもの、解体物をさらに分離・分解したものについても本発明を適用できる。
(Object to be cleaned)
Objects to be cleaned include transformers (transformers) and capacitors, for example, ceramics such as metal and insulators, iron cores, transformer / capacitor bodies (containers), coil copper wires / insulation paper, rubber / plastic resins, etc. Insulating wood and other organic materials (paper, processed paper products, etc.), bolts, screws and capacitor element aluminum foil, insulating paper, resin films, etc. (collectively referred to as dismantled materials). The present invention can also be applied to these disassembled products, those obtained by crushing the disassembled products, and those obtained by further separating and disassembling the disassembled products.

(洗浄槽)
洗浄槽1では、槽内に設けたバスケット(図示しない)に洗浄対象物を投入し洗浄を行う。なお、バスケットは洗浄槽1内に固定されているものに必ずしも限定されず、バスケット自体を移動可能として洗浄槽1内に設けるようにしてもよい。
洗浄槽1は、真空度を保つことができる構造を有し、かつ、洗浄バスケットを浸漬できる容器(シンク等)、溶剤を供給・排出できる配管等、および溶剤やPCB蒸気を供給・排出(吸引)できる配管等を備えているものであれば特に限定されない。
(Washing tank)
In the cleaning tank 1, cleaning is performed by putting an object to be cleaned into a basket (not shown) provided in the tank. The basket is not necessarily limited to the one fixed in the cleaning tank 1, and the basket itself may be movable and provided in the cleaning tank 1.
The cleaning tank 1 has a structure capable of maintaining a degree of vacuum, and a container (sink or the like) in which the cleaning basket can be immersed, a pipe capable of supplying and discharging a solvent, and a solvent and PCB vapor are supplied and discharged (suction). ) There is no particular limitation as long as it is provided with piping that can be used.

洗浄バスケットの形状は洗浄対象物を収容し、洗浄に差し障りのない形状であれば特に限定されない。洗浄バスケットの形状としては、例えば、カゴ型(角型、丸型など)が挙げられる。
また、洗浄バスケットのうち、円筒形洗浄バスケットなどの場合には、洗浄対象物を洗浄バスケット内に閉じ込め、洗浄槽の中で回転させつつ洗浄する回転カゴとし、洗浄バスケット(洗浄バレル)を回転させる駆動機構(駆動装置)を洗浄槽に備えているものとすることができる。以下、洗浄回転カゴを洗浄バスケットあるいはバスケットと呼ぶことがある。
The shape of the cleaning basket is not particularly limited as long as it accommodates an object to be cleaned and does not interfere with cleaning. Examples of the shape of the cleaning basket include a cage shape (such as a square shape and a round shape).
Further, in the case of a cylindrical washing basket or the like among the washing baskets, the washing object is confined in the washing basket, and the washing basket (washing barrel) is rotated by using a rotating basket for washing while rotating in the washing tank. A drive mechanism (drive device) may be provided in the cleaning tank. Hereinafter, the cleaning rotating basket may be referred to as a cleaning basket or a basket.

(溶剤洗浄手段)
溶剤洗浄手段2は、洗浄槽1へ供給する洗浄液(溶剤)を有する。洗浄液(溶剤)は、炭化水素系の洗浄液(例えばノルマルパラフィン系など)から洗浄対象物の汚染度、除去するPCBの種類等にあった洗浄液を選択することができる。
溶剤洗浄手段2は、洗浄槽1や減圧手段4の冷却器から回収したPCBを含む溶剤を再生する装置(例えば蒸留装置)を備えていることが好ましい。溶剤再生装置を備えることで、新たな溶剤の使用量(補給する溶剤量)を減らすことができる。また、溶剤洗浄手段2を洗浄槽1よりも低い位置に設置することが好ましい。このような配置により、洗浄槽1の液を抜く際に重力によって溶剤を溶剤洗浄手段2に流下させることができ、ポンプ等の機器を省略することができる。
(Solvent cleaning means)
The solvent cleaning means 2 has a cleaning liquid (solvent) supplied to the cleaning tank 1. As the cleaning liquid (solvent), a cleaning liquid suitable for the degree of contamination of the object to be cleaned, the type of PCB to be removed, and the like can be selected from a hydrocarbon-based cleaning liquid (for example, normal paraffin type).
The solvent cleaning means 2 is preferably provided with an apparatus (for example, a distillation apparatus) for regenerating the solvent containing PCB recovered from the cooler of the cleaning tank 1 or the decompression means 4. By providing the solvent regeneration device, the amount of new solvent used (the amount of solvent to be replenished) can be reduced. Moreover, it is preferable to install the solvent cleaning means 2 at a position lower than the cleaning tank 1. With such an arrangement, the solvent can be caused to flow down to the solvent cleaning means 2 by gravity when the liquid in the cleaning tank 1 is drained, and equipment such as a pump can be omitted.

(蒸気洗浄手段)
本発明のシステムは、溶剤洗浄手段2から直接洗浄槽1へ洗浄液を流入させる手段に加えて、蒸発気化させた洗浄液を洗浄槽1へ流入させる手段をも有する。洗浄液を蒸発させ、気化させるのに必要な熱量を供給するための蒸気洗浄手段3(蒸気発生器(熱交換器)等)が溶剤洗浄手段2から洗浄槽1への配管の途中に設置されている。蒸気発生器に供給される熱源は、水蒸気や加熱油等の熱媒体を適宜使用することができる。電気ヒーターは、洗浄液が漏洩した場合に引火の原因となる可能性があるため使用しないことが好ましい。
(Vapor cleaning means)
The system of the present invention also has means for allowing the evaporated cleaning liquid to flow into the cleaning tank 1 in addition to the means for allowing the cleaning liquid to flow directly from the solvent cleaning means 2 into the cleaning tank 1. A steam cleaning means 3 (steam generator (heat exchanger), etc.) for supplying the amount of heat necessary for evaporating and evaporating the cleaning liquid is installed in the middle of the pipe from the solvent cleaning means 2 to the cleaning tank 1. Yes. As a heat source supplied to the steam generator, a heat medium such as water vapor or heating oil can be appropriately used. The electric heater is preferably not used because it may cause ignition when the cleaning liquid leaks.

(減圧手段)
減圧手段4(真空ポンプ等)は、洗浄槽1内部を減圧するために用いられる。真空ポンプは、使用する条件(洗浄液に対するポンプの耐性、必要とする真空度等)を満足するポンプを適宜選択することができる。また、より効率的に必要とする真空度に達するように、複数台の真空ポンプを利用することがより好ましい。複数台のポンプを使用することにより、選択できるポンプの種類が多くなり、また、ポンプに無理な負荷をかけないで運転できるため、装置の稼動率を高めることができる。
減圧手段4の前後には、気体の洗浄溶剤(洗浄液)を冷却するための冷却器が設置されていることが好ましい。冷却器を備えることにより、溶剤やPCBを液化して溶剤洗浄手段に送り、溶剤を再生利用することができる。また、気体状のPCBを廃棄処理手段に送る量が減らせ、処理量が大きくなりがちな気体処理部分の負荷(処理量)を低減することができる。
(Pressure reduction means)
The decompression means 4 (such as a vacuum pump) is used to decompress the inside of the cleaning tank 1. As the vacuum pump, it is possible to appropriately select a pump that satisfies the conditions to be used (the resistance of the pump to the cleaning liquid, the required degree of vacuum, etc.). It is more preferable to use a plurality of vacuum pumps so as to reach the required degree of vacuum more efficiently. By using a plurality of pumps, the types of pumps that can be selected are increased, and the pump can be operated without applying an excessive load, so that the operating rate of the apparatus can be increased.
It is preferable that a cooler for cooling the gaseous cleaning solvent (cleaning liquid) is installed before and after the decompression means 4. By providing the cooler, the solvent or PCB can be liquefied and sent to the solvent cleaning means to recycle the solvent. In addition, the amount of gaseous PCB sent to the disposal processing means can be reduced, and the load (processing amount) of the gas processing part that tends to increase the processing amount can be reduced.

(廃棄処理手段)
廃棄処理手段5では、濃縮・減量された第二次PCB汚染物を廃棄処理する。
洗浄槽から真空ポンプにつながる配管には、PCBを含んだ洗浄液(洗浄蒸気)が存在するため、大気へ排気する前に冷却器で蒸気(気体状のPCBや溶剤)を液化させて回収し溶剤洗浄手段へ送り、溶剤の再利用を図る。排気はさらに活性炭フィルタなどを通してから大気放出され、環境中にPCBが拡散しないようにしている。廃棄処理手段5では、再生溶剤以外の廃液や上記活性炭フィルタなどの第二次PCB汚染物について廃棄処理を行う。
(Disposal method)
The discard processing means 5 discards the concentrated / reduced secondary PCB contaminant.
Since the pipe connected from the cleaning tank to the vacuum pump contains cleaning liquid (cleaning steam) containing PCB, the steam (gaseous PCB or solvent) is liquefied and recovered with a cooler before exhausting to the atmosphere. Send to cleaning means to reuse the solvent. Further, the exhaust gas is discharged into the atmosphere through an activated carbon filter or the like, so that PCB does not diffuse into the environment. In the disposal processing means 5, disposal processing is performed on waste liquid other than the regenerated solvent and secondary PCB contaminants such as the activated carbon filter.

本発明のシステムにおいては、洗浄槽への洗浄バスケット搬入、搬出や洗浄槽の扉の開閉などは自動化することが、作業員がPCBに曝露する危険性を低減できるため好ましい。また、本発明のシステムにおいては、ポンプ、エジェクタ等の移送手段、バルブ、流量計等の構成機器を適宜用いることができる。   In the system of the present invention, it is preferable to automate the loading / unloading of the cleaning basket into / from the cleaning tank, the opening / closing of the door of the cleaning tank, etc., because the risk of exposure of the worker to the PCB can be reduced. Further, in the system of the present invention, components such as transfer means such as pumps and ejectors, valves, and flow meters can be used as appropriate.

次に、本発明のシステムを用いた処理方法について説明する。本発明の好ましい実施態様を図2に示す。以下、作業工程を図1及び図2を参照しながら説明する。
<作業工程>
洗浄対象物6は洗浄対象物毎に異なったバスケットに投入され、洗浄対象物に適した洗浄・乾燥条件で処理が行われる。
Next, a processing method using the system of the present invention will be described. A preferred embodiment of the present invention is shown in FIG. Hereinafter, the work process will be described with reference to FIGS.
<Work process>
The objects to be cleaned 6 are put into different baskets for each object to be cleaned, and are processed under cleaning and drying conditions suitable for the object to be cleaned.

バスケット搬入〜真空引き(工程21、22、23)
まず、前工程からバスケットに入れられた洗浄対象物6が運ばれ、洗浄槽1にセットされる。洗浄槽1の扉が閉められ、真空ポンプ4によって真空引きが始まり、圧力1333Pa(10Torr)〜13332Pa(100Torr)程度、好ましくは5333Pa(40Torr)〜8000Pa(60Torr)程度にされる。
Bring basket to vacuum (steps 21, 22, and 23)
First, the cleaning object 6 put in the basket from the previous process is carried and set in the cleaning tank 1. The door of the cleaning tank 1 is closed, and evacuation is started by the vacuum pump 4, and the pressure is set to about 1333 Pa (10 Torr) to 13332 Pa (100 Torr), preferably about 5333 Pa (40 Torr) to 8000 Pa (60 Torr).

揚液−1(工程24)
真空引き終了後、溶剤洗浄手段2から溶剤(洗浄液A)を洗浄槽1に送り、洗浄バスケットと洗浄対象物を浸漬する。
Pumped liquid-1 (process 24)
After completion of evacuation, the solvent (cleaning liquid A) is sent from the solvent cleaning means 2 to the cleaning tank 1, and the cleaning basket and the object to be cleaned are immersed.

浸漬洗浄−1(工程25)
洗浄槽1に洗浄液Aを満たした後、液温度を40℃〜60℃、好ましくは50℃程度、洗浄槽圧力を6666Pa(50Torr)程度にして、所定時間保持する。この浸漬中にバスケット中の洗浄対象物6に対して超音波を照射し、洗浄効果を高めることが除染効率の点から好ましい。浸漬洗浄時間(洗浄槽での保持時間)は洗浄対象物6が何(紙、金属等)であるか、どの程度PCBを含んでいるか等を勘案し、最適な時間(10〜60分程度)を選択することができる。洗浄槽1でどのくらいの時間保持するかは、別途洗浄対象物に応じた試験を行い、洗浄対象物6の温度とPCB除去率等から最適時間を予め決めておく。
Immersion cleaning-1 (Step 25)
After the cleaning tank 1 is filled with the cleaning liquid A, the liquid temperature is set to 40 ° C. to 60 ° C., preferably about 50 ° C., the cleaning tank pressure is set to about 6666 Pa (50 Torr), and held for a predetermined time. From the viewpoint of decontamination efficiency, it is preferable to irradiate the cleaning object 6 in the basket with ultrasonic waves during this immersion to enhance the cleaning effect. Immersion cleaning time (holding time in the cleaning tank) is an optimal time (about 10 to 60 minutes) considering what the object to be cleaned 6 is (paper, metal, etc.) and how much PCB is contained. Can be selected. For how long the cleaning tank 1 holds, a test corresponding to the object to be cleaned is separately conducted, and the optimum time is determined in advance from the temperature of the object to be cleaned 6 and the PCB removal rate.

降液−1(工程26)
洗浄液Aを洗浄槽1から抜取る。このとき、ポンプ等の移送手段を利用する、重力流下式とするなど適宜設計することができる。
Falling down-1 (step 26)
The cleaning liquid A is extracted from the cleaning tank 1. At this time, it is possible to design appropriately such as using a transfer means such as a pump or a gravity flow type.

蒸気洗浄−1(工程27)
次に、真空引きで到達した圧力を保持したまま、溶剤洗浄手段2から蒸気発生器3に洗浄液Aが送られ、洗浄対象物6の温度が130℃程度になるように蒸気発生器3で洗浄液Aに熱を与え、溶剤(洗浄液)が蒸気となって(例えば洗浄剤蒸気温度160℃で)洗浄槽1に送られる。洗浄槽1に洗浄液の蒸気を所定時間(例えば10分)供給する。蒸気を供給して圧力が変化しても、圧力のコントロールは行わなくても良い。蒸気洗浄時間(蒸気供給時間)は洗浄対象物が何(紙、金属等)であるか、どの程度PCBを含んでいるか等を勘案し、最適な時間(10分程度〜60分程度)を採用することができる。洗浄槽1でどのくらいの時間保持するかは、別途洗浄対象物に応じた試験を行い、洗浄対象物6の温度とPCB除去率等から最適時間を予め決めておく。
揚液−2(工程28)
蒸気洗浄−1(工程27)の終了後、溶剤洗浄手段からより清浄な溶剤(洗浄液B)を洗浄槽に送り、洗浄バスケットと洗浄対象物を浸漬する。
Steam cleaning-1 (step 27)
Next, while maintaining the pressure reached by evacuation, the cleaning liquid A is sent from the solvent cleaning means 2 to the steam generator 3, and the cleaning liquid is cleaned by the steam generator 3 so that the temperature of the object 6 to be cleaned becomes about 130 ° C. Heat is applied to A, and the solvent (cleaning liquid) is vaporized (for example, at a cleaning agent vapor temperature of 160 ° C.) and sent to the cleaning tank 1. A cleaning liquid vapor is supplied to the cleaning tank 1 for a predetermined time (for example, 10 minutes). Even if the pressure is changed by supplying steam, the pressure need not be controlled. For the steam cleaning time (steam supply time), the optimum time (about 10 to 60 minutes) is adopted in consideration of what the object to be cleaned (paper, metal, etc.) and how much PCB is contained. can do. For how long the cleaning tank 1 holds, a test corresponding to the object to be cleaned is separately conducted, and the optimum time is determined in advance from the temperature of the object to be cleaned 6 and the PCB removal rate.
Pumped liquid-2 (process 28)
After completion of the steam cleaning-1 (step 27), a cleaner solvent (cleaning liquid B) is sent from the solvent cleaning means to the cleaning tank, and the cleaning basket and the object to be cleaned are immersed.

浸漬洗浄−2(工程29)
洗浄液Bを満たした後、浸漬洗浄−1(工程25)と同じ条件で浸漬洗浄を行う。
Immersion cleaning-2 (Step 29)
After the cleaning liquid B is filled, immersion cleaning is performed under the same conditions as immersion cleaning-1 (step 25).

降液−2(工程30)
降液−1(工程26)と同じように洗浄槽から洗浄液Bを抜取る。
Falling liquid-2 (process 30)
The cleaning liquid B is extracted from the cleaning tank in the same manner as the falling liquid-1 (step 26).

蒸気洗浄−2(工程31)
降液が終了したら、蒸気洗浄−1(工程27)と同じ条件で蒸気洗浄を行う。(揚液−2(工程28)からの工程をくり返して、浸漬洗浄−2(工程29)と蒸気洗浄−2(工程31)を複数回繰り返して実施してもよい。
Steam cleaning-2 (process 31)
When the liquid drop is completed, steam cleaning is performed under the same conditions as in steam cleaning-1 (step 27). (Steps from pumping liquid-2 (step 28) may be repeated, and immersion cleaning-2 (step 29) and steam cleaning-2 (step 31) may be repeated a plurality of times.

真空乾燥(工程32)
蒸気洗浄によって130℃程度の温度になった洗浄対象物について、洗浄槽の圧力を更に下げることによって、洗浄液およびPCBの除去を確実(効率的)に行う。
蒸気洗浄後の洗浄槽の圧力を真空ポンプによって、まず400Pa(3Torr)〜1333Pa(10Torr)程度、好ましくは533Pa(4Torr)〜800Pa(6Torr)程度に下げる。このとき、主に溶剤(洗浄液)が洗浄対象物から除去される。次に、真空ポンプでさらに洗浄槽の圧力を50Pa(0.38Torr)以下、好ましくは5Pa(0.038Torr)〜10Pa(0.075Torr)程度まで下げる。この圧力は低いほど良い。このときに主にPCBが洗浄対象物から除去される。
真空乾燥時の圧力を達成するための真空ポンプは、この圧力を達成できれば、複数台を切り替えて使用しても、複数台を連続して使用してもよく、1台で実現しても良い。このとき洗浄槽の温度は特に制御する必要はない。
Vacuum drying (process 32)
The cleaning liquid and the PCB are removed reliably (efficiently) by further lowering the pressure of the cleaning tank with respect to the object to be cleaned that has reached a temperature of about 130 ° C. by the steam cleaning.
The pressure of the cleaning tank after the steam cleaning is first reduced to about 400 Pa (3 Torr) to 1333 Pa (10 Torr), preferably about 533 Pa (4 Torr) to 800 Pa (6 Torr) by a vacuum pump. At this time, the solvent (cleaning liquid) is mainly removed from the object to be cleaned. Next, the pressure of the washing tank is further lowered to 50 Pa (0.38 Torr) or less, preferably 5 Pa (0.038 Torr) to 10 Pa (0.075 Torr) with a vacuum pump. The lower this pressure, the better. At this time, PCB is mainly removed from the object to be cleaned.
As long as the vacuum pump for achieving the pressure at the time of vacuum drying can achieve this pressure, a plurality of units may be used by switching them, or a plurality of units may be used continuously, or a single unit may be realized. . At this time, it is not necessary to control the temperature of the washing tank.

必要に応じてこの真空乾燥工程を複数回繰り返して、PCB、溶剤の除去をさらに行っても良い。
本発明の一連(浸漬洗浄、蒸気洗浄、真空乾燥)の条件では、紙などの有機物質が炭化せず、また、槽内を窒素等で置換することなくPCBの除染を行うことができ、処理したものはリサイクルあるいは次の工程に送ることができる。
If necessary, this vacuum drying step may be repeated a plurality of times to further remove the PCB and the solvent.
Under the conditions of the present invention (immersion cleaning, steam cleaning, vacuum drying), organic substances such as paper do not carbonize, and PCB decontamination can be performed without replacing the inside of the tank with nitrogen, The treated material can be recycled or sent to the next process.

この工程で減圧手段にはPCBおよび洗浄液(溶剤)がポンプによって吸引されてくるので、減圧手段に備えた冷却器によってそれらを冷却して凝縮(液化)させて溶剤洗浄手段に送り、溶剤洗浄手段で溶剤とPCBを分離し、PCBは処理(無害化)設備で無害化され、溶剤は一定の条件を満たしていれば再利用される。   In this step, since the PCB and the cleaning liquid (solvent) are sucked into the decompression means by the pump, they are cooled and condensed (liquefied) by the cooler provided in the decompression means and sent to the solvent cleaning means. Then, the solvent and PCB are separated, and the PCB is detoxified in a treatment (detoxification) facility, and the solvent is reused if certain conditions are satisfied.

大気解放〜バスケット搬出(工程33、34、35)
真空乾燥終了後、空気導入配管(図示せず)から徐々に空気を導入して洗浄槽1内部の圧力を大気圧まで回復させる。
洗浄槽圧力を大気圧まで回復させた後、洗浄槽の扉を開き、洗浄バスケットを搬出する。搬出されたバスケットは次の工程に送られる。このとき、必要に応じて洗浄バスケットから搬送用の容器などに移しかえてもよい。
Release to atmosphere-unload basket (process 33, 34, 35)
After completion of the vacuum drying, air is gradually introduced from an air introduction pipe (not shown) to restore the pressure inside the cleaning tank 1 to atmospheric pressure.
After the washing tank pressure is restored to atmospheric pressure, the washing tank door is opened and the washing basket is unloaded. The unloaded basket is sent to the next process. At this time, it may be transferred from the washing basket to a container for transporting as necessary.

上記の各工程は、各種センサ類(温度センサ、圧力センサ等)や接触(近接)スイッチ等、任意の自動化技術を利用して自動化することができる。
また、洗浄バスケットの搬送方法についても、各種コンベア(ローラコンベア、ベルトコンベア等)やAGV(Automated Guided Vehicle)等の自動搬送装置、クレーンなど、任意の方法により行うことができる。
Each of the above steps can be automated using any automation technology such as various sensors (temperature sensor, pressure sensor, etc.) and contact (proximity) switch.
Also, the cleaning basket can be transported by any method such as an automatic transport device such as various conveyors (roller conveyor, belt conveyor, etc.), AGV (Automated Guided Vehicle), or a crane.

次に本発明を実施例に基づき更に詳細に説明するが、本発明はこれらの実施例に限定されるものではない。   EXAMPLES Next, although this invention is demonstrated further in detail based on an Example, this invention is not limited to these Examples.

基準値を満たしているかどうかの確認(卒業判定)は、公定法によって実施した。すなわち、金属類(鉄、銅など)・碍子等については、部材採取試験法(基準値 0.01mg/kg以下:PCB/部材)、拭き取り試験法(基準値 0.1μg/100cm2以下:PCB/部材)、洗浄液試験法(基準値 0.5mg/kg以下:PCB/洗浄液)のいずれかの方法で行った。
また、紙類(紙、木屑、繊維くず等)については、基準値 0.003mg/リットル以下:PCB/検液とした。なお、紙類についての具体的な検定方法は現在未制定であるため、ここでは環境庁告示第13号にある溶出試験の試験手順とおり実施した。
Confirmation (graduation judgment) whether or not the standard value is satisfied was carried out by the official method. That is, for metals (iron, copper, etc.) and insulators, member sampling test method (reference value 0.01 mg / kg or less: PCB / member), wiping test method (reference value 0.1 μg / 100 cm 2 or less: PCB / Member) and cleaning liquid test method (reference value 0.5 mg / kg or less: PCB / cleaning liquid).
For papers (paper, wood chips, fiber scraps, etc.), the standard value was 0.003 mg / liter or less: PCB / test solution. In addition, since the concrete verification method about paper is not yet established, it carried out according to the test procedure of the dissolution test in the Environment Agency Notification No. 13 here.

実施例1
図1に示した構成のシステムを用い、図2に示した工程に従って洗浄および真空乾燥を実施した。洗浄対象物としては、破砕工程で3mmスクリーンを通過した破砕紙類(絶縁紙)を使用した。
洗浄バレル、洗浄槽は次のような大きさのものを使用した。
洗浄バレル:直径(Φ)400×長さ400mmの回転かご
洗浄槽の液容量:約150リットル
Example 1
Using the system having the configuration shown in FIG. 1, cleaning and vacuum drying were performed according to the steps shown in FIG. As the object to be cleaned, crushed paper (insulating paper) that passed through a 3 mm screen in the crushing step was used.
The cleaning barrel and cleaning tank were as follows.
Cleaning barrel: Liquid capacity of rotating basket cleaning tank with diameter (Φ) 400 x length 400 mm: about 150 liters

まず、上記の紙4kgを洗浄バレル(回転カゴ)に入れ、6000Paまで減圧した後、溶剤洗浄手段2から溶剤を洗浄槽1に送り洗浄槽1に洗浄液を満たし、洗浄バレルと洗浄対象物を浸漬し、洗浄バレル中の紙(洗浄対象物)に対して超音波を照射しながら、洗浄槽圧力6666Pa(50Torr)、洗浄液温度約50℃の条件で10分保持した(浸漬洗浄−1)。   First, 4 kg of the above paper is put into a cleaning barrel (rotary basket), and the pressure is reduced to 6000 Pa. Then, the solvent is sent from the solvent cleaning means 2 to the cleaning tank 1 to fill the cleaning tank 1, and the cleaning barrel and the object to be cleaned are immersed. Then, while irradiating the paper (object to be cleaned) in the cleaning barrel with ultrasonic waves, it was held for 10 minutes under conditions of a cleaning tank pressure of 6666 Pa (50 Torr) and a cleaning liquid temperature of about 50 ° C. (immersion cleaning-1).

次いで、洗浄液を洗浄槽1から抜取り、真空引きで到達した圧力を保持したまま、溶剤洗浄手段2から蒸気発生器3に洗浄液を送り、約160℃の洗浄液蒸気を洗浄槽1に10分間供給した(蒸気洗浄−1)。蒸気洗浄の終了後、溶剤洗浄手段からより清浄な溶剤(洗浄液)を洗浄槽に送り、洗浄バレルと洗浄対象物を浸漬し、再び浸漬洗浄を行った(浸漬洗浄−2)。この浸漬洗浄は先の浸漬洗浄(浸漬洗浄−1)と同じ条件で行った。   Next, the cleaning liquid is extracted from the cleaning tank 1 and the cleaning liquid is sent from the solvent cleaning means 2 to the steam generator 3 while maintaining the pressure reached by evacuation, and about 160 ° C. cleaning liquid vapor is supplied to the cleaning tank 1 for 10 minutes. (Vapor cleaning-1). After completion of the steam cleaning, a cleaner solvent (cleaning liquid) was sent from the solvent cleaning means to the cleaning tank, the cleaning barrel and the object to be cleaned were immersed, and immersion cleaning was performed again (immersion cleaning-2). This immersion cleaning was performed under the same conditions as the previous immersion cleaning (immersion cleaning-1).

次いで、洗浄液を洗浄槽1から抜取り、再び蒸気洗浄を行った。真空引きで到達した圧力を保持したまま、溶剤洗浄手段2から蒸気発生器3に洗浄液を送り、約160℃の洗浄液蒸気を洗浄槽1に30分間供給した(蒸気洗浄−2)。   Next, the cleaning liquid was extracted from the cleaning tank 1 and again subjected to steam cleaning. While maintaining the pressure reached by evacuation, the cleaning liquid was sent from the solvent cleaning means 2 to the steam generator 3 and about 160 ° C. cleaning liquid vapor was supplied to the cleaning tank 30 for 30 minutes (vapor cleaning-2).

蒸気洗浄後の洗浄槽の圧力を真空ポンプによって667Pa(5Torr)に下げて10分保持した後、さらに5Pa(0.038Torr)に下げて30分保持した(真空乾燥)。   The pressure of the cleaning tank after the steam cleaning was lowered to 667 Pa (5 Torr) by a vacuum pump and held for 10 minutes, and then lowered to 5 Pa (0.038 Torr) and kept for 30 minutes (vacuum drying).

各洗浄工程における洗浄液(溶剤)の種類は全てノルマルパラフィン系の炭化水素系洗浄液を使用した。揚液工程ではポンプを使用し、降液工程では溶剤洗浄手段を洗浄槽下方に設置したので、重力流下にて降液した。
真空乾燥では、2台の真空ポンプを使用し、1台目の真空ポンプで667Pa(5Torr)程度まで圧力を下げ、2台目のポンプで5Pa(0.038Torr)程度まで圧力を下げた。
The type of cleaning liquid (solvent) used in each cleaning process was a normal paraffin hydrocarbon cleaning liquid. In the pumping process, a pump was used, and in the liquid dropping process, the solvent cleaning means was installed below the cleaning tank, so the liquid was dropped under gravity flow.
In vacuum drying, two vacuum pumps were used, and the pressure was reduced to about 667 Pa (5 Torr) with the first vacuum pump, and the pressure was reduced to about 5 Pa (0.038 Torr) with the second pump.

上記の結果、洗浄後の部材からのPCB溶出濃度は0.0009mg/リットル(溶出試験法による)となり、基準値である0.003mg/リットルを充分に満足することがわかった。上記の洗浄開始から乾燥終了までの時間は、2時間であった。
また、浸漬洗浄−2と蒸気洗浄−2を3回繰り返した試験も行ったところ、その結果、洗浄後の部材からのPCB溶出濃度は0.0004mg/リットル(溶出試験法による)と半減することがわかった。
As a result, it was found that the PCB elution concentration from the cleaned member was 0.0009 mg / liter (according to the elution test method), sufficiently satisfying the standard value of 0.003 mg / liter. The time from the start of washing to the end of drying was 2 hours.
Moreover, when the test which repeated immersion cleaning-2 and steam cleaning-2 was also performed 3 times, as a result, the PCB elution density | concentration from the member after washing | cleaning was reduced to 0.0004 mg / liter (by the elution test method) and halved. I understood.

実施例2
洗浄対象物として破砕工程で7mmスクリーンを通過した金属を使用した。この金属は変圧器(トランス)のコイル部分を洗浄、解体して、絶縁紙を分離した銅の破砕物である。上記銅破砕物20kgを洗浄バスケットに入れたこと以外は実施例1と同様にして、洗浄および真空乾燥を実施した。洗浄バスケットは、500(縦)×400(横)×250(深さ)mmの大きさのものを使用した。
その結果、洗浄後の部材のPCB含有量は0.003mg/kg(部材採取試験法による)となり、基準値0.01mg/kgを充分に満足することがわかった。また、上記の洗浄開始から乾燥終了までの時間は、2時間であった。洗浄後の銅破砕物のPCB濃度はその後の処理に問題ない濃度であったので、次の工程で最終処分(リサイクル)を行えることがわかった。
Example 2
A metal that passed through a 7 mm screen in the crushing process was used as an object to be cleaned. This metal is a crushed copper material obtained by washing and dismantling the coil portion of the transformer and separating the insulating paper. Cleaning and vacuum drying were performed in the same manner as in Example 1 except that 20 kg of the crushed copper was put in a cleaning basket. A washing basket having a size of 500 (vertical) × 400 (horizontal) × 250 (depth) mm was used.
As a result, it was found that the PCB content of the cleaned member was 0.003 mg / kg (according to the member sampling test method), sufficiently satisfying the standard value of 0.01 mg / kg. Further, the time from the start of washing to the end of drying was 2 hours. Since the PCB concentration of the crushed copper after washing was such a concentration that there was no problem in subsequent processing, it was found that final disposal (recycling) can be performed in the next step.

実施例3
洗浄対象物として絶縁紙とアルミ箔からなるコンデンサ素子を破砕工程で破砕して、3mmのスクリーンを通過したものを使用した。上記破砕素子5kgを洗浄バレル(回転カゴ)に入れたこと以外は実施例1と同様にして、洗浄および真空乾燥を実施した。
その結果、洗浄後の部材のPCB含有量は0.0005mg/リットル(溶出試験法による)となり、基準値である0.003mg/リットルを充分に満足することがわかった。上記の洗浄開始から乾燥終了までの時間は、2時間であった。
Example 3
A capacitor element made of insulating paper and aluminum foil was crushed in a crushing process and passed through a 3 mm screen as a cleaning object. Cleaning and vacuum drying were performed in the same manner as in Example 1 except that 5 kg of the crushing element was put in a cleaning barrel (rotary basket).
As a result, it was found that the PCB content of the cleaned member was 0.0005 mg / liter (according to the dissolution test method), which sufficiently satisfied the standard value of 0.003 mg / liter. The time from the start of washing to the end of drying was 2 hours.

図1は、本発明のシステムの好ましい実施態様を示す構成概念図である。FIG. 1 is a conceptual diagram showing a preferred embodiment of the system of the present invention. 図2は、本発明の処理方法の好ましい実施態様を示すフロー図である。FIG. 2 is a flow diagram illustrating a preferred embodiment of the processing method of the present invention.

符号の説明Explanation of symbols

1 洗浄槽
2 溶剤洗浄手段
3 蒸気洗浄手段
4 減圧手段
5 廃棄処理手段
6 洗浄対象物
DESCRIPTION OF SYMBOLS 1 Cleaning tank 2 Solvent cleaning means 3 Vapor cleaning means 4 Depressurization means 5 Waste disposal means 6 Cleaning object

Claims (5)

PCBを含有した電気機器を解体および/または破砕して得られた洗浄対象物を除染処理する処理システムであって、洗浄槽、溶剤洗浄手段、蒸気洗浄手段、減圧手段、および廃棄処理手段を具備し、該洗浄槽において洗浄・乾燥手段が一定の温度圧力条件下で行われることを特徴とするPCB汚染物の処理システム。   A processing system for decontaminating an object to be cleaned obtained by disassembling and / or crushing electrical equipment containing PCB, comprising a cleaning tank, a solvent cleaning means, a steam cleaning means, a decompression means, and a disposal processing means And a PCB contaminant treatment system, wherein the washing / drying means is performed under a constant temperature and pressure condition in the washing tank. 前記洗浄槽における洗浄・乾燥手段が、13322Pa(100Torr)〜1333(10Torr)に減圧して洗浄を行い、洗浄対象物温度が110〜150℃になるように加熱した後に、その温度でPCBが蒸発する圧力に圧力を調節して、PCB及び溶剤を除去することにより行われることを特徴とする請求項1記載のPCB汚染物の処理システム。   The cleaning / drying means in the cleaning tank performs cleaning by reducing the pressure to 13322 Pa (100 Torr) to 1333 (10 Torr), and heats the object to be cleaned to 110 to 150 ° C., and then the PCB evaporates at that temperature. 2. The PCB contaminant treatment system according to claim 1, wherein the PCB contaminant is removed by adjusting the pressure to the pressure to be removed. 前記電気機器がトランス又はコンデンサであることを特徴とする請求項1又は2に記載のPCB汚染物の処理システム。   3. The PCB contaminant treatment system according to claim 1, wherein the electrical device is a transformer or a capacitor. 溶剤が炭化水素系であることを特徴とする請求項1〜3のいずれか1項に記載のPCB汚染物の処理システム。   The system for treating a PCB contaminant according to any one of claims 1 to 3, wherein the solvent is hydrocarbon-based. 前記請求項1〜4のいずれか1項に記載の処理システムを用いたことを特徴とするPCB汚染物の処理方法。   A method for treating PCB contaminants, wherein the treatment system according to any one of claims 1 to 4 is used.
JP2004073936A 2004-03-16 2004-03-16 Treating system and treating method for pcb-polluted substance Pending JP2005261993A (en)

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Cited By (6)

* Cited by examiner, † Cited by third party
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JP2008142615A (en) * 2006-12-08 2008-06-26 Kansai Electric Power Co Inc:The Method and apparatus for removing pcb from pcb contaminated transformer
JP2013107030A (en) * 2011-11-18 2013-06-06 Mitsubishi Heavy Ind Ltd Apparatus and method for treating pcb-contaminated film element
JP2014050826A (en) * 2012-09-10 2014-03-20 Mitsubishi Heavy Ind Ltd Treatment apparatus for pcb contaminated film element
WO2015046299A1 (en) * 2013-09-30 2015-04-02 日立金属株式会社 Process for manufacturing reclaimed alloy material and process for manufacturing reclaimed amorphous alloy ribbon
JP2018143928A (en) * 2017-03-02 2018-09-20 株式会社神鋼環境ソリューション Method for decontaminating workplace handled with pcb pollutant
JP2019107598A (en) * 2017-12-15 2019-07-04 株式会社クリンビー Water system one tank type vacuum cleaning dryer and cleaning system with automatic transportation unit

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008142615A (en) * 2006-12-08 2008-06-26 Kansai Electric Power Co Inc:The Method and apparatus for removing pcb from pcb contaminated transformer
JP2013107030A (en) * 2011-11-18 2013-06-06 Mitsubishi Heavy Ind Ltd Apparatus and method for treating pcb-contaminated film element
JP2014050826A (en) * 2012-09-10 2014-03-20 Mitsubishi Heavy Ind Ltd Treatment apparatus for pcb contaminated film element
WO2015046299A1 (en) * 2013-09-30 2015-04-02 日立金属株式会社 Process for manufacturing reclaimed alloy material and process for manufacturing reclaimed amorphous alloy ribbon
CN105531043A (en) * 2013-09-30 2016-04-27 日立金属株式会社 Process for manufacturing reclaimed alloy material and process for manufacturing reclaimed amorphous alloy ribbon
JPWO2015046299A1 (en) * 2013-09-30 2017-03-09 日立金属株式会社 Method for producing recycled alloy material and method for producing recycled amorphous alloy ribbon
KR101847752B1 (en) * 2013-09-30 2018-04-10 히다찌긴조꾸가부시끼가이사 Process for manufacturing reclaimed alloy material and process for manufacturing reclaimed amorphous alloy ribbon
US10407754B2 (en) 2013-09-30 2019-09-10 Hitachi Metals, Ltd. Process for manufacturing reclaimed alloy material and process for manufacturing reclaimed amorphous alloy ribbon
JP2018143928A (en) * 2017-03-02 2018-09-20 株式会社神鋼環境ソリューション Method for decontaminating workplace handled with pcb pollutant
JP2019107598A (en) * 2017-12-15 2019-07-04 株式会社クリンビー Water system one tank type vacuum cleaning dryer and cleaning system with automatic transportation unit

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