JP2010179239A - Pretreatment method and pretreatment equipment in plasma melting decomposition treatment of material to be treated - Google Patents

Pretreatment method and pretreatment equipment in plasma melting decomposition treatment of material to be treated Download PDF

Info

Publication number
JP2010179239A
JP2010179239A JP2009024960A JP2009024960A JP2010179239A JP 2010179239 A JP2010179239 A JP 2010179239A JP 2009024960 A JP2009024960 A JP 2009024960A JP 2009024960 A JP2009024960 A JP 2009024960A JP 2010179239 A JP2010179239 A JP 2010179239A
Authority
JP
Japan
Prior art keywords
treated
storage container
plasma melting
pretreatment
container
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
JP2009024960A
Other languages
Japanese (ja)
Other versions
JP5069703B2 (en
Inventor
Yasuki Motai
泰樹 馬渡
Terufumi Hirashima
輝文 平嶋
Takashi Kerakawachi
隆 螻川内
Makoto Yamazaki
良 山崎
Shigeyoshi Tagashira
成能 田頭
Yoshiaki Shimizu
由章 清水
Yutaka Ishii
豊 石井
Yasushi Kajiwara
康司 梶原
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.)
Shinko Pantec Co Ltd
Nippon Steel Engineering Co Ltd
Nippon Steel Plant Designing Corp
Original Assignee
Nittetsu Plant Designing Corp
Nippon Steel Engineering Co Ltd
Kobelco Eco Solutions Co Ltd
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 Nittetsu Plant Designing Corp, Nippon Steel Engineering Co Ltd, Kobelco Eco Solutions Co Ltd filed Critical Nittetsu Plant Designing Corp
Priority to JP2009024960A priority Critical patent/JP5069703B2/en
Publication of JP2010179239A publication Critical patent/JP2010179239A/en
Application granted granted Critical
Publication of JP5069703B2 publication Critical patent/JP5069703B2/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a pretreatment method and equipment therefor which, prior to a plasma melting decomposition treatment of a material to be treated such as sludge, waste, pressure sensitive copying paper, fluorescent lamp stabilizer and waste activated carbon which are contaminated with PCB, efficiently perform the following pretreatment while keeping a tightly closed state: classifying the material to be treated according to the properties and condition of the material be treated; managing the weight of classified material to be treated; and repacking the material to be treated from a carrying-in storage container that has been carried in a PCB waste material treating facility into a prescribed repacking container for charging. <P>SOLUTION: In making the material to be treated harmless by melting decomposition in a plasma melting decomposition furnace, the pretreatment is performed in which the material to be treated is repacked from the carrying-in storage container that has been carried in the PCB waste material treating facility into the repacking storage container for charging which charges the material to be treated to the PCB waste treatment facility. In the pretreatment, the material to be treated is classified according to the properties and condition of the material be treated, the material to be treated is carried in a tightly closed chamber set for each classified group, and the material to be treated of prescribed mass treatable by the plasma melting decomposition furnace is repacked from the carrying-in storage container into the repacking container for charging. <P>COPYRIGHT: (C)2010,JPO&INPIT

Description

本発明は、PCB廃棄物処理施設において蛍光灯安定器、汚泥等のPCBに汚染された処理対象物をプラズマ溶融分解して無害化処理するに先だって、処理対象物を仕分けし、PCB廃棄物処理施設に搬入された搬入保管容器から、プラズマ溶融分解炉へ投入する投入用詰替容器にプラズマ溶融分解処理に適するように詰め替える、処理対象物のプラズマ溶融分解処理における前処理方法及び前処理設備に関する。   The present invention sorts a processing object before detoxifying it by plasma melting and decomposing the processing object contaminated by PCB such as a fluorescent lamp stabilizer and sludge in a PCB waste treatment facility, The present invention relates to a pretreatment method and a pretreatment facility in a plasma melting decomposition treatment of an object to be processed, which is refilled from a carry-in storage container carried into a facility into a refilling container to be charged into a plasma melting decomposition furnace so as to be suitable for the plasma melting decomposition treatment. .

PCB(ポリ塩化ビフェニル)は、トランス、コンデンサ、蛍光灯安定器等の電気機器の絶縁油、ボイラ等の熱媒体等に使用されていたが、毒性があり且つ残留性があるため蓄積して人の健康や生活環境に大きな被害を及ぼすことから、PCB廃棄物処理施設で無害化処理されている。   PCBs (polychlorinated biphenyls) have been used as insulating oils in electrical equipment such as transformers, capacitors, and fluorescent ballasts, and in heat media such as boilers. It is detoxified at the PCB waste disposal facility because it causes serious damage to the health and living environment of the city.

従来のPCBの分解技術としては、高温焼却法、アルカリ剤によってPCBから塩素を脱離する脱塩素分解法、紫外線と触媒による光分解法及びPCBをプラズマによって、溶融分解するプラズマ溶融分解法が知られている(特許文献1、2参照)。   Conventional PCB decomposition techniques include high-temperature incineration, dechlorination decomposition by desorbing chlorine from PCBs with an alkaline agent, photolysis using ultraviolet light and a catalyst, and plasma melt decomposition where PCB is melted and decomposed by plasma. (See Patent Documents 1 and 2).

特開2004−121801号公報JP 2004-121801 A 特開2007−296415号公報JP 2007-296415 A

PCB廃棄物のうち、高圧トランス、高圧コンデンサ及びこれらと同程度の大型の電気機器はPCB廃棄物の大部分を占め、その無害化処理は、その技術的条件及び環境・安全対策について整理されており、これを踏まえて各地における拠点的広域処理施設の整備が進められている。   Among PCB wastes, high-voltage transformers, high-voltage capacitors, and large electrical equipment of the same size occupy the majority of PCB waste, and its detoxification treatment is organized in terms of technical conditions, environmental and safety measures. Based on this, the development of regional wide-area treatment facilities in various places is being promoted.

しかしながら、上記の大型の電気機器を除く、汚泥、ウェス、感圧複写紙、蛍光灯安定器、排気浄化用として使用される廃活性炭などのPCB汚染物の無害化については、個々のPCB汚染物によって性状等が大きく異なることから、処理方法が確立されておらず、開発が行われている段階である。   However, for the detoxification of PCB contaminants such as sludge, waste, pressure-sensitive copying paper, fluorescent light stabilizers, and waste activated carbon used for exhaust purification, except for the above-mentioned large electrical equipment, individual PCB contaminants Since the properties and the like vary greatly depending on the method, a processing method has not been established and development is in progress.

そこで、本発明は、大型電気機器を除く、汚泥、ウェス、感圧複写紙、蛍光灯安定器、廃活性炭などのPCBに汚染された処理対象物をプラズマ溶融分解処理する前に、処理対象物を性状に応じて分類し、分類された処理対象物の重量を管理して、PCB廃棄物処理施設へ搬入された搬入保管容器から所定の投入用詰替容器に詰め替える前処理を、密閉状態を維持しながら効率よく実施することができる処理対象物のプラズマ溶融分解処理における前処理方法及びその設備を提供するものである。   Therefore, the present invention provides a processing object before plasma melting and decomposition treatment of a processing object contaminated with PCB such as sludge, waste, pressure-sensitive copying paper, fluorescent light stabilizer, waste activated carbon, etc., excluding large electric devices. In accordance with the properties, the weight of the classified processing object is managed, and the pre-processing for refilling the specified refill container from the carry-in storage container carried into the PCB waste disposal facility is performed in a sealed state. The present invention provides a pretreatment method and equipment for plasma melt decomposition treatment of an object to be treated that can be efficiently carried out while maintaining the same.

本発明は、汚泥、ウェス、感圧複写紙、蛍光灯安定器、排気浄化用として使用された廃活性炭などの処理対象物を性状に応じた分類を行い、分類された処理対象物群毎の前処理内容に応じた密閉室(グローブボックスあるいはドラフトチャンバ)を用い、PCB廃棄物処理施設へ搬入された搬入保管容器から所定のプラズマ溶融分解炉への投入用詰替容器への詰め替え及び塩基度調整剤の投入等を実施することが可能な前処理方法である。本発明では、処理対象物の投入重量を詰替容器単位で管理することが重要である。また、プラズマ溶融分解炉へ投入されるまで密閉状態を維持し、投入後は処理対象物のガス化膨張前に確実に膨張ガスを抜くことができるようにする。   The present invention classifies treatment objects such as sludge, waste, pressure-sensitive copying paper, fluorescent ballasts, waste activated carbon used for exhaust gas purification according to properties, and provides a classification for each classified treatment object group. Using a sealed chamber (glove box or draft chamber) according to the pretreatment content, refilling and refilling from the storage container carried into the PCB waste treatment facility to the refilling container for loading into the predetermined plasma melting decomposition furnace This is a pretreatment method capable of carrying out a charging agent and the like. In the present invention, it is important to manage the input weight of the processing object in units of refill containers. Further, the sealed state is maintained until it is put into the plasma melting cracking furnace, and after the filling, the expanded gas can be surely extracted before gasification and expansion of the object to be processed.

請求項1のプラズマ溶融分解処理における前処理方法は、PCB廃棄物処理施設において処理対象物をプラズマ溶融分解炉で溶融分解して無害化処理する際に、PCB廃棄物処理施設へ搬入された搬入保管容器から、処理対象物をプラズマ溶融分解炉に投入する投入用詰替容器に詰め替える前処理方法であって、処理対象物の性状に応じて分類を行い、分類された群毎に定められた密閉室内に搬入し、搬入保管容器からプラズマ溶融分解炉で処理可能な所定の質量を投入用詰替容器に詰め替えることを特徴とする。   The pretreatment method in the plasma melting and decomposing process according to claim 1 is the carrying-in carried into the PCB waste processing facility when the object to be processed is melted and decomposed by the plasma melting and decomposing furnace in the PCB waste processing facility. A pretreatment method for refilling a processing object from a storage container into a refill container for charging into a plasma melting cracking furnace, classifying according to the properties of the processing object, and deciding for each classified group It is carried into a sealed chamber, and a predetermined mass that can be processed in the plasma melting decomposition furnace from the carry-in storage container is refilled into a refill container for charging.

請求項2の発明は、1種類以上の塩基度調整剤を投入用詰替容器に詰めることを特徴とする。   The invention of claim 2 is characterized in that one or more basicity adjusting agents are packed in a refill container for input.

請求項3の発明は、1種類以上の処理対象物を所定の質量で搬入保管容器から投入用詰替容器に詰め替えることを特徴とする。   The invention according to claim 3 is characterized in that one or more types of processing objects are refilled from a carry-in storage container to a charging refill container with a predetermined mass.

請求項4の発明は、搬入保管容器に封入された液状物を吸着材が投入されている投入用詰替容器に投入して吸着材により液状物を固形化することを特徴とする。   The invention of claim 4 is characterized in that the liquid material sealed in the carry-in storage container is charged into the charging refill container in which the adsorbent is charged and the liquid material is solidified by the adsorbent.

請求項5の発明は、投入用詰替容器の蓋に穴加工を行い、可溶性の栓で密閉することを特徴とする。   The invention of claim 5 is characterized in that a hole is formed in the lid of the charging refill container and the lid is sealed with a soluble stopper.

請求項6のプラズマ溶融分解処理設備における前処理設備は、PCB廃棄物処理施設において処理対象物をプラズマ溶融分解炉で溶融分解して無害化処理する際に、PCB廃棄物処理施設へ搬入された搬入保管容器から、処理対象物をプラズマ溶融分解炉に投入する投入用詰替容器に詰め替える前処理設備において、処理対象物の性状に応じて分類された群毎に定められた密閉室(例えばグローブボックスまたはドラフトチャンバ内)に、処理対象物を収納した搬入保管容器を傾斜させる傾斜機と、傾斜した搬入保管容器から掻き出された処理対象物を秤量する秤量器と、秤量されて所定の質量を詰め替えた投入用詰替容器を搬出するコンベアを備えたことを特徴とする。   The pretreatment equipment in the plasma melt decomposition treatment facility according to claim 6 was carried into the PCB waste treatment facility when the object to be treated was melted and decomposed in the PCB waste treatment facility by the plasma melt decomposition furnace. In the pretreatment facility for refilling the processing object from the carry-in storage container into the refill container for charging into the plasma melting cracking furnace, a sealed chamber (for example, a globe) defined for each group classified according to the properties of the processing object In a box or a draft chamber), a tilting machine for tilting the carry-in storage container containing the processing object, a weigher for weighing the processing object scraped from the tilted carry-in storage container, and a predetermined mass It is characterized by having a conveyor for carrying out the refilling container for refilling.

請求項7の発明は、感圧複写紙を含水させる水槽を備えたことを特徴とする。   The invention of claim 7 is characterized by comprising a water tank for containing the pressure-sensitive copying paper.

請求項8の発明は、投入用詰替容器へ塩基度調整剤を供給する塩基度調整剤供給装置を備えたことを特徴とする。   The invention of claim 8 is characterized by comprising a basicity adjusting agent supply device for supplying a basicity adjusting agent to the charging refill container.

請求項9の発明は、搬入保管容器に封入された液状物を吸着材が投入されている投入用詰替容器に投入する詰替用ポンプを備えたことを特徴とする。   The invention according to claim 9 is characterized in that a refill pump is provided for feeding the liquid material sealed in the carry-in storage container into the refill container for loading in which the adsorbent is charged.

請求項10の発明は、投入用詰替容器へ廃活性炭を供給する廃活性炭供給装置を備えたことを特徴とする。   According to a tenth aspect of the present invention, there is provided a waste activated carbon supply device that supplies waste activated carbon to the charging refill container.

請求項11の発明は、傾斜した搬入保管容器から掻き出された処理対象物を受ける詰替ホッパを備え、ロードセルと底部に開閉可能なフラップダンパを備えた第1段目ホッパの上方に、第1段目ホッパの上部の開口に対して前進後退可能に移動式スクリーンが配置され、第1段目ホッパの下方に、第1段目ホッパの底部に対して前進後退可能な第2段目のホッパが配置され、第2段目のホッパは底部にフラップダンパを備えていることを特徴とする。   The invention of claim 11 is provided with a refill hopper for receiving a processing object scraped from an inclined carry-in storage container, above a first stage hopper provided with a load cell and a flap damper that can be opened and closed at the bottom. A movable screen is disposed so as to be capable of moving forward and backward with respect to the opening at the top of the first stage hopper, and the second stage capable of moving forward and backward with respect to the bottom of the first stage hopper below the first stage hopper. A hopper is disposed, and the second hopper has a flap damper at the bottom.

請求項1の発明では、処理対象物を搬入保管容器から所定の詰め替え仕様にプラズマ溶融分解炉への投入用詰替容器に詰替えることにより、投入用詰替容器単位のバッチ投入が可能となりプラズマ溶融分解炉の安定した運転とを可能とする。また、密閉室内で詰め替え作業を実施することにより作業員のPCB暴露を防止できる。詰め替え前に搬入保管容器内の検査(内容物検査)を行い、危険物の混入を発見し、除去できる。処理対象物の性状による分類を行うことにより処理作業が類似となり、作業の効率化が図れる。   According to the first aspect of the present invention, by refilling the object to be processed from the carry-in storage container into the refilling container for charging into the plasma melting decomposition furnace to the predetermined refilling specification, it is possible to batch-feed the charging refilling container unit. It enables stable operation of the melting cracking furnace. In addition, it is possible to prevent workers from being exposed to PCB by performing refilling work in a sealed room. Perform inspection (content inspection) in the carry-in storage container before refilling to find out and remove dangerous substances. By classifying the processing objects according to their properties, the processing operations become similar, and the efficiency of the operation can be improved.

請求項2、3の発明により、処理対象物の溶融時間特性により、二つ以上の処理対象物を混合することで溶融時間の節約、溶融性状の改質等のプラズマ溶融分解炉の操業効率を改善することができる。   According to the inventions of claims 2 and 3, the operation efficiency of the plasma melting cracking furnace such as melting time saving and melting property reforming can be improved by mixing two or more processing objects according to the melting time characteristics of the processing objects. Can be improved.

請求項4の発明により、吸着材により液状物を固形化することで取り扱いやすくなる。   According to the invention of claim 4, it becomes easy to handle by solidifying the liquid with the adsorbent.

請求項5の発明により、処理対象物は、可燃性のものや揮発性のものも含まれており、プラズマ溶融分解処理を行う際にその熱によりガス化し投入用詰替容器内で膨張し投入用詰替容器が破裂する危険性があるが、上記可溶栓付蓋を利用した投入用詰替容器を使用することによりそれを防止することができる。   According to the invention of claim 5, the object to be treated includes flammable and volatile substances, which are gasified by the heat when performing the plasma melting decomposition treatment and expanded and charged in the charging refill container. Although there is a risk that the refilling container will burst, this can be prevented by using the charging refilling container using the lid with the fusible plug.

請求項3、5の発明により、多種多様の処理対象物に対して、最適な詰め替え仕様を操業実績データに基づき変更することで最適なプラズマ溶融分解処理を実現することができる。   According to the third and fifth aspects of the invention, the optimum plasma melting and decomposing process can be realized by changing the optimum refilling specifications based on the operation result data for a wide variety of processing objects.

本発明による蛍光灯安定器類の前処理工程のブロック図である。It is a block diagram of the pre-processing process of the fluorescent lamp ballasts by this invention. 本発明による蛍光灯安定器類の前処理工程のレイアウトである。2 is a layout of a pretreatment process for fluorescent ballasts according to the present invention. 本発明による汚泥の前処理工程のブロック図である。It is a block diagram of the pretreatment process of the sludge by this invention. (a)は本発明による汚泥の前処理工程のレイアウトの平面図、(b)は同正面図である。(A) is a top view of the layout of the pretreatment process of the sludge by this invention, (b) is the same front view. 汚泥の詰め替えホッパの概略図である。It is the schematic of the refilling hopper of sludge.

本発明の前処理について図により説明する。   The pretreatment of the present invention will be described with reference to the drawings.

別工程で処理される大型のPCB電気機器やPCB含有廃油など以外の、安定器、小型トランス・コンデンサ(小型トラコン)、感圧複写紙、塗料、シーリング材、汚泥、ウェスなどのPCBに汚染された処理対象物は、その種類、充填する投入用詰替容器の容量、塩基度調整剤の添加の有無に応じて分類される。本実施例では蛍光灯安定器、小型トラコン、感圧複写紙はグループAに、汚泥、ウェスはグループBに、廃活性炭はグループCなどに分類される。   Contaminated by PCBs such as ballasts, small transformers / condensers (small tracons), pressure-sensitive copying paper, paints, sealing materials, sludge, waste cloths, etc. The objects to be treated are classified according to the type, the capacity of the filling refill container to be filled, and the presence or absence of the addition of the basicity adjusting agent. In this embodiment, fluorescent ballasts, compact turcons, and pressure-sensitive copying papers are classified into group A, sludge and waste are classified into group B, and waste activated carbon is classified into group C.

次いで分類された処理対象物ごとに前処理される。   Next, each classified processing object is preprocessed.

図1は本発明による安定器類の前処理工程のブロック図である。図2は本発明による安定器類の前処理工程のレイアウトである。   FIG. 1 is a block diagram of a pretreatment process for ballasts according to the present invention. FIG. 2 is a layout of a ballast pretreatment process according to the present invention.

(1)蛍光灯安定器、小型トラコン、感圧複写紙、塗料・シーリング材、殺虫剤含浸蚊取りマット(グループA)の前処理 (1) Pretreatment of fluorescent lamp ballast, compact turcon, pressure-sensitive copying paper, paint / sealing material, insecticide-impregnated mosquito mat (Group A)

(a)蛍光灯安定器、小型トラコン
処理対象物である蛍光灯安定器が収納され、蓋がされた搬入保管容器(ドラム缶)2(ドラム缶:200リットル)がクレーン等で入側供給装置1に搬入される。搬入された搬入保管容器(ドラム缶)2は、コンベヤ等でエアロック可能な前室3を経て負圧に維持されたグローブボックス4内へ搬入される。
(A) Fluorescent light ballast, compact turcon The fluorescent light ballast, which is the object to be processed, is housed and the lidded carry-in storage container (drum can) 2 (drum can: 200 liters) is connected to the inlet side supply device 1 with a crane or the like It is brought in. The carried-in storage container (drum can) 2 is carried into a glove box 4 maintained at a negative pressure through a front chamber 3 that can be air-locked by a conveyor or the like.

作業者はグローブボックス4内にグローブを介してエアーインパクトドライバーなどの手工具を用いて搬入保管容器(ドラム缶)2から蓋を取り外す(図1の蓋外し)。   The operator removes the lid from the carry-in storage container (drum can) 2 using a hand tool such as an air impact driver through the glove in the glove box 4 (removal of the lid in FIG. 1).

次いで、搬入保管容器(ドラム缶)2を反転エリアの反転装置5に移動させて反転させ、内容物(処理対象物)をテーブル6に掻き出し、プラズマ溶融分解炉で爆発する危険物などの異物を除去する。   Next, the carry-in storage container (drum) 2 is moved to the reversing device 5 in the reversing area and reversed, the contents (processed object) are scraped to the table 6, and foreign substances such as dangerous materials exploding in the plasma melting decomposition furnace are removed. To do.

異物を除去した処理対象物は、秤量エリアの秤量器7で秤量しながら、新しい投入用詰替容器(ドラム缶)8(ドラム缶:100リットルまたは200リットル)に詰め替える。重量管理することにより、後工程のプラズマ溶融分解炉で効率よく溶融分解処理することが可能となる。   The processing object from which the foreign matter has been removed is refilled into a new charging refill container (drum can) 8 (drum can: 100 liters or 200 liters) while being weighed by the weighing device 7 in the weighing area. By managing the weight, it is possible to efficiently perform the melting / decomposing treatment in the plasma melting / decomposing furnace in the subsequent process.

さらに、投入用詰替容器(ドラム缶)8には、廃活性炭が施設に搬入されていれば、必要に応じて廃活性炭を廃活性炭ホッパ9から秤量して併せて充填する。さらに、次工程のプラズマ溶融分解の際に溶融物の流動性を良好にするために、珪砂や石灰石などの塩基度調整剤を塩基度調整剤ホッパ10から秤量して必要量を充填する。   Furthermore, if the waste activated carbon is carried into the facility, the input refill container (drum can) 8 is weighed from the waste activated carbon hopper 9 and filled together as necessary. Further, in order to improve the fluidity of the melt during the plasma melting decomposition in the next step, a basicity adjusting agent such as silica sand or limestone is weighed from the basicity adjusting agent hopper 10 and filled with a necessary amount.

投入用詰替容器(ドラム缶)8に詰める処理対象物、廃活性炭、塩基度調整剤の混合割合などの重量管理は、操業管理データに基づいて適正な量に調整する。   Weight management, such as the mixing ratio of the processing object, waste activated carbon, and the basicity adjusting agent to be packed in the refilling container (drum can) 8 is adjusted to an appropriate amount based on the operation management data.

充填後の投入用詰替容器(ドラム缶)8にエアーインパクトドライバーなどの手工具を用いて蓋を取り付ける。   A lid is attached to the refill container (drum) 8 after filling using a hand tool such as an air impact driver.

なお、処理対象物には、可燃性のものや揮発性のものも含まれており、プラズマ溶融分解処理を行う際にその熱によりガス化し投入用詰替容器(ドラム缶)8内で膨張し投入用詰替容器(ドラム缶)8が破裂する危険性があるので、可溶栓付蓋を利用した投入用詰替容器を使用することによりそれを防止することができる。また、可溶栓の材質は、処理対象物がガス化する前に溶解するPE樹脂等を用いる。   In addition, combustible materials and volatile materials are also included in the processing object, which is gasified by the heat during the plasma melting and decomposition process and expanded and charged in the charging refill container (drum can) 8. Since there is a risk that the refilling container (drum can) 8 may rupture, it can be prevented by using a charging refillable container using a lid with a fusible stopper. Further, as the material of the fusible plug, PE resin or the like that dissolves before the object to be processed is gasified is used.

蓋をした投入用詰替容器(ドラム缶)8は、エアロックされた後流側の前室11を経て出側搬出装置12に送られる。出側搬出装置12により後工程のプラズマ溶融分解工程へと送られる。   The charging refill container (drum can) 8 with the lid is sent to the outlet carrying-out device 12 via the air-locked front chamber 11 on the downstream side. It is sent to the plasma melting and decomposing process of the subsequent process by the delivery side unloading device 12.

蛍光灯安定器と同じ分類の小型トラコンは、蛍光灯安定器と同様の手順により処理される。   Small tracons of the same category as fluorescent ballasts are processed in the same manner as fluorescent ballasts.

表1に蛍光灯安定器等の詰替内容の例を示す。   Table 1 shows examples of refill contents such as fluorescent ballasts.

Figure 2010179239
Figure 2010179239

処理対象物の詰替質量は、表1に示す質量の±10%の範囲がよい。   The refill mass of the object to be processed is preferably in the range of ± 10% of the mass shown in Table 1.

(b)感圧複写紙
感圧複写紙については、グローブボックス内でダンボール等で搬入された感圧複写紙を取り出して、かごに入れて水槽13に浸漬し含水させた後、秤量器7で秤量する。水槽13に浸けて含水させることにより、感圧複写紙がプラズマ溶融分解炉で燃焼により発生した灰が飛散して炉から排出されるのを防止する。含水後に秤量し、その後蛍光灯安定器と同様の手順で処理する。ただし、感圧複写紙単独で処理する場合にはプラズマ溶融分解炉でガス化させるので、塩基度調整剤の添加は必要としない。感圧複写紙の詰替内容の例は、表1のとおりである。
(B) Pressure-sensitive copying paper
Regarding the pressure-sensitive copying paper, the pressure-sensitive copying paper carried in cardboard or the like in the glove box is taken out, placed in a basket, immersed in the water tank 13 and hydrated, and then weighed by the weighing device 7. By soaking in the water tank 13 and containing water, the ash generated by combustion of the pressure-sensitive copying paper in the plasma melting decomposition furnace is prevented from being scattered and discharged from the furnace. Weigh after hydration and then process in the same manner as a fluorescent light ballast. However, when processing with pressure-sensitive copying paper alone, it is gasified in a plasma melting decomposition furnace, so that it is not necessary to add a basicity adjusting agent. Table 1 shows examples of the contents of pressure-sensitive copying paper.

感圧複写紙の他、塗料・シーリング材、殺虫剤含浸蚊取りマットも同様の手順で処理することが可能である。   In addition to pressure-sensitive copying paper, paint / sealant and insecticide-impregnated mosquito mats can be treated in the same procedure.

(2)汚泥、ウェス(グループB)の前処理
汚泥やウェスの前処理は、負圧に維持されたドラフトチャンバにおいて外側からゴム手袋をした手を入れて安全に作業を行うことができる。
(2) Pretreatment of sludge and waste (Group B) Pretreatment of sludge and waste can be performed safely by putting a hand wearing rubber gloves from the outside in a draft chamber maintained at a negative pressure.

図3は本発明による汚泥の前処理工程のブロック図、図4(a)は本発明による汚泥の前処理工程のレイアウトの平面図、(b)は正面図、図5は詰め替えホッパの概略図である。   3 is a block diagram of the sludge pretreatment process according to the present invention, FIG. 4A is a plan view of the layout of the sludge pretreatment process according to the present invention, FIG. 3B is a front view, and FIG. 5 is a schematic view of the refill hopper. It is.

(a)汚泥
汚泥は含有する油分などの性状に応じてプラズマ溶融分解炉への投入量が異なるので、投入用詰替容器は、200リットルのドラム缶と、これより容量の小さいペール缶(例えば、20リットル)を使用する。
(A) Sludge Sludge has a different amount of input into the plasma melting cracking furnace depending on the properties of the oil content and the like, so the refill container for charging is a 200-liter drum can and a pail can with a smaller capacity (for example, 20 liters).

処理室には固形物を前処理する固形物用ドラフトチャンバ14と液状物を前処理する液状物用ドラフトチャンバ15が配置されている。   The processing chamber is provided with a solid material draft chamber 14 for pre-processing solid materials and a liquid material draft chamber 15 for pre-processing liquid materials.

有機質汚泥を除く汚泥については、扉を開けて搬入コンベヤ16で固形物用ドラフトチャンバ14へ汚泥が収納された搬入保管容器(ドラム缶)が搬入される。   As for the sludge excluding organic sludge, the door is opened, and a carry-in storage container (drum) in which the sludge is stored in the solid material draft chamber 14 is carried in by the carry-in conveyor 16.

作業者はエアーインパクトドライバーなどの手工具を用いて搬入保管容器(ドラム缶)から蓋を取り外す。   The operator removes the lid from the carry-in storage container (drum) using a hand tool such as an air impact driver.

搬入保管容器(ドラム缶)の内部を点検し、遊離水があれば吸着材により吸着する。吸着後の吸着材は吸着材用ペール缶へ入れる。   The inside of the carry-in storage container (drum can) is inspected, and if there is free water, it is adsorbed by the adsorbent. The adsorbent after adsorption is put into an adsorbent pail.

次いで、搬入保管容器(ドラム缶)を反転装置27に移動させて反転させ、内容物を詰め替えホッパ17へ掻き出す。   Next, the carry-in storage container (drum can) is moved to the reversing device 27 to be reversed, and the contents are scraped out to the refill hopper 17.

図5に示す詰め替えホッパ17は、第1段目ホッパ18の上方に、メッシュからなる移動式スクリーン19が第1段目ホッパ18の開口に対して前進後退可能に配置される。第1段目ホッパ18の底部には開閉可能なフラップダンパ20が設けられている。第1段目ホッパ18は移動式スクリーン19を通過した汚泥の量を秤量する秤量器としてロードセルを備えている。フラップダンパ20を開けることにより汚泥は投入用詰替容器(ドラム缶)21に移される。   In the refill hopper 17 shown in FIG. 5, a movable screen 19 made of a mesh is disposed above the first stage hopper 18 so as to be capable of moving forward and backward with respect to the opening of the first stage hopper 18. An openable / closable flap damper 20 is provided at the bottom of the first stage hopper 18. The first-stage hopper 18 includes a load cell as a weighing device for weighing the amount of sludge that has passed through the movable screen 19. By opening the flap damper 20, the sludge is transferred to a charging refill container (drum can) 21.

第1段目ホッパ18の下方に第1段目ホッパ18の底部に対して前進後退可能な第2段目ホッパ22が配置されている。第2段目ホッパ22の底部には開閉可能なフラップダンパ23が設けられ、フラップダンパ23を開けることにより汚泥が投入用詰替容器(ペール缶)24に移される。   A second stage hopper 22 that can be moved forward and backward with respect to the bottom of the first stage hopper 18 is disposed below the first stage hopper 18. An openable / closable flap damper 23 is provided at the bottom of the second stage hopper 22, and the sludge is transferred to a charging refill container (pail can) 24 by opening the flap damper 23.

搬入保管容器(ドラム缶)2より掻き出された汚泥は、詰め替えホッパの第1段目ホッパ18上の移動式スクリーン19のメッシュ上に掻き出して、約50mm以上の比較的大型の異物を除去する。除去した異物は、異物用ペール缶へ入れる。異物のうち、スプレー缶など危険物はプラズマ溶融分解炉での爆発を防止するため、孔開けなどの前処理をする。   The sludge scraped from the carry-in storage container (drum can) 2 is scraped onto the mesh of the movable screen 19 on the first-stage hopper 18 of the refill hopper to remove relatively large foreign matters of about 50 mm or more. The removed foreign matter is put in a foreign matter pail can. Among foreign materials, dangerous materials such as spray cans are pre-treated such as drilling to prevent explosion in the plasma melting cracking furnace.

搬入保管容器(ドラム缶)2から掻き出される汚泥は、移動式スクリーン19を通過し、第1段目ホッパ18に落下し、底部に溜まる。所定重量になると、掻き出しを停止する。その後、フラップダンパ20を開いて汚泥を第1段目ホッパ18の下方に配置した投入用詰替容器(ドラム缶)21へ落とす。このとき、第2段目ホッパ22は待機位置に後退している。   The sludge scraped from the carry-in storage container (drum can) 2 passes through the movable screen 19, falls on the first stage hopper 18, and accumulates at the bottom. When the weight reaches a predetermined level, the scraping is stopped. Thereafter, the flap damper 20 is opened and the sludge is dropped into a charging refill container (drum can) 21 disposed below the first-stage hopper 18. At this time, the second stage hopper 22 is retracted to the standby position.

汚泥の種類は予め分かっているので、有機汚泥の場合は、投入用詰替容器(ペール缶)24へ移すので、第1段目のホッパで有機汚泥の重量を測定した後、フラップダンパを開いて第1段目のホッパの下方へ位置している第2段目ホッパ22へ落とす。次いで第2段目ホッパ22を後退させて投入用詰替容器(ペール缶)24の上に位置させ、フラップダンパ23を開いて有機汚泥を投入用詰替容器(ペール缶)24に移す。   Since the type of sludge is known in advance, in the case of organic sludge, it is transferred to the refill container (pale can) 24 for input. After measuring the weight of the organic sludge with the first-stage hopper, the flap damper is opened. To the second-stage hopper 22 located below the first-stage hopper. Next, the second-stage hopper 22 is moved backward to be positioned on the charging refill container (pail can) 24, the flap damper 23 is opened, and the organic sludge is transferred to the charging refill container (pail can) 24.

さらに、投入用詰替容器(ドラム缶)21には、廃活性炭が施設に搬入されていれば廃活性炭を廃活性炭ホッパ9から秤量して充填する。さらに、次工程のプラズマ溶解時の流動性を調整するために、珪砂や石灰石などの塩基度調整剤を塩基度調整剤ホッパ10から秤量して必要量を充填する。   Furthermore, if the waste activated carbon is carried into the facility, the input refill container (drum can) 21 is weighed and filled from the waste activated carbon hopper 9. Furthermore, in order to adjust the fluidity at the time of plasma melting in the next step, a basicity adjusting agent such as silica sand or limestone is weighed from the basicity adjusting agent hopper 10 and filled with a necessary amount.

充填後の投入用詰替容器(ドラム缶)21及び投入用詰替容器(ペール缶)24へエアーインパクトドライバーなどの手工具を用いて蓋を取り付ける。蓋をした投入用詰替容器(ドラム缶)21又は投入用詰替容器(ペール缶)24は、コンベヤ16cでドラフトチャンバから搬出され、プラズマ溶融分解工程へ送られる。   A lid is attached to the charging refill container (drum can) 21 and the charging refill container (pail can) 24 after filling using a hand tool such as an air impact driver. The charging refill container (drum can) 21 or the charging refill container (pail can) 24 with the lid is carried out of the draft chamber by the conveyor 16c and sent to the plasma melting and decomposing process.

表2に汚泥等の詰替内容の例を示す。   Table 2 shows examples of refill contents such as sludge.

Figure 2010179239
Figure 2010179239

液状物用ドラフトチャンバ15では、液状物の封入された搬入保管容器(ドラム缶)2は搬入コンベヤ16aによりドラフトチャンバ15内に搬入され、ドラフトチャンバ15の搬送コンベヤ16b上で待機する投入用詰替容器(ドラム缶)21に詰替用ポンプ25を介して液状物は詰め替えられる。詰め替えられた投入用詰替容器(ドラム缶)21はプラズマ処理待機室へ搬送される。また、投入用詰替容器(ドラム缶)21には液状物を擬似固形化する吸着材を投入しており、液状物が詰替用ポンプにより投入用詰替容器(ドラム缶)21に投入されると吸着材により液状物は固形化される。   In the liquid material draft chamber 15, the carry-in storage container (drum can) 2 filled with the liquid material is carried into the draft chamber 15 by the carry-in conveyor 16 a and waits on the transport conveyor 16 b of the draft chamber 15. The liquid material is refilled in the (drum) 21 via the refill pump 25. The refilled refill container (drum) 21 that has been refilled is transported to the plasma processing standby chamber. In addition, an adsorbent for quasi-solidifying the liquid material is introduced into the charging refill container (drum can) 21. When the liquid material is charged into the charging refill container (drum can) 21 by a refilling pump. The liquid is solidified by the adsorbent.

また、PCB廃棄物処理施設内の別工程で発生した液状物は、パイプライン26によりドラフトチャンバ15内に運ばれ、投入用詰替容器(ドラム缶21)内に投入される。   In addition, the liquid material generated in a separate process in the PCB waste treatment facility is conveyed into the draft chamber 15 by the pipeline 26 and is charged into the charging refill container (drum 21).

(a)ウェス
汚泥と同じ分類のウェスについては、汚泥を処理する固形物用ドラフトチャンバにコンベヤ16により搬入保管容器(ドラム缶)が搬入される。
(A) Waste For waste of the same classification as sludge, a carry-in storage container (drum can) is carried by the conveyor 16 into a solid material draft chamber for treating the sludge.

作業者はエアーインパクトドライバーなどの手工具を用いて搬入保管容器(ドラム缶)の蓋を取り外す。   The operator removes the lid of the carry-in storage container (drum can) using a hand tool such as an air impact driver.

搬入保管容器(ドラム缶)の内部を点検後、搬入保管容器(ドラム缶)を反転装置27に移動させて反転させ、詰め替えホッパの第1段目のホッパ上の移動式スクリーンのメッシュ上に掻き出して、異物を除去する。除去した異物は、異物用ペール缶へ入れる。   After inspecting the inside of the carry-in storage container (drum can), the carry-in storage container (drum can) is moved to the reversing device 27, reversed, scraped on the movable screen mesh on the first hopper of the refill hopper, Remove foreign material. The removed foreign matter is put in a foreign matter pail can.

充填後の投入用詰替容器(ドラム缶)へエアーインパクトドライバーなどの手工具を用いて蓋を取り付ける。蓋をした投入用詰替ドラム缶は、コンベヤ16cでドラフトチャンバから搬出され、プラズマ溶融分解工程へ送られる。ウェスの詰替内容の例は、表2のとおりである。   Use a hand tool such as an air impact driver to attach the lid to the refill container (drum can) for filling after filling. The charged refill drum with the lid is unloaded from the draft chamber by the conveyor 16c and sent to the plasma melting and decomposing process. Table 2 shows examples of the contents of refilling waste cloths.

1:入側供給装置
2:搬入保管容器(ドラム缶)
3:前室
4:グローブボックス
5:反転装置
6:テーブル
7:秤量器
8:投入用詰替容器(ドラム缶)
9:廃活性炭ホッパ
10:塩基度調整剤ホッパ
11:前室
12:出側搬出装置
13:水槽
14:固形物用ドラフトチャンバ
15:液状物用ドラフトチャンバ
16:投入コンベヤ
16a:搬入コンベヤ
16b:搬送コンベヤ
16c:搬送コンベヤ
17:詰め替えホッパ
18:第1段目ホッパ
19:移動式スクリーン
20:フラップダンパ
21:投入用詰替容器(ドラム缶)
22:第2段目ホッパ
23:フラップダンパ
24:投入用詰替容器(ペール缶)
25:詰替用ポンプ
26:パイプライン
27:反転装置
1: Entry side supply device 2: Carrying storage container (drum)
3: Front chamber 4: Glove box 5: Reversing device 6: Table 7: Weighing instrument 8: Refill container for input (drum can)
9: Waste activated carbon hopper 10: Basicity adjusting agent hopper 11: Front chamber 12: Outlet delivery device 13: Water tank 14: Draft chamber for solid matter 15: Draft chamber for liquid matter 16: Input conveyor 16a: Conveyor 16b: Conveyance Conveyor 16c: Conveyor 17: Refill hopper 18: First stage hopper 19: Mobile screen 20: Flap damper 21: Refill container for input (drum can)
22: Second stage hopper 23: Flap damper 24: Refill container for loading (pail can)
25: Refill pump 26: Pipeline 27: Reversing device

Claims (11)

PCB廃棄物処理施設において処理対象物をプラズマ溶融分解炉で溶融分解して無害化処理する際に、PCB廃棄物処理施設へ搬入された搬入保管容器から、処理対象物をプラズマ溶融分解炉に投入する投入用詰替容器に詰め替える前処理方法であって、
処理対象物の性状に応じて分類を行い、分類された群毎に定められた密閉室内に搬入し、搬入保管容器からプラズマ溶融分解炉で処理可能な所定の質量を投入用詰替容器に詰め替えることを特徴とするプラズマ溶融分解処理における前処理方法。
When a processing object is melted and decomposed in a PCB waste treatment facility and detoxified by a plasma melting and decomposing furnace, the processing object is put into the plasma melting and decomposing furnace from a carry-in storage container carried into the PCB waste processing facility. A pretreatment method for refilling into a refill container for input,
Classification is performed according to the properties of the object to be processed, and it is carried into a sealed room defined for each classified group, and a predetermined mass that can be processed in the plasma melting cracking furnace is refilled into the refill container for input from the storage container. A pretreatment method in plasma melt decomposition treatment characterized by the above.
1種類以上の塩基度調整剤を投入用詰替容器に詰めることを特徴とする請求項1記載のプラズマ溶融分解処理における前処理方法。   2. The pretreatment method in plasma melt decomposition treatment according to claim 1, wherein one or more kinds of basicity adjusting agents are packed in a refill container for charging. 1種類以上の処理対象物を所定の質量で搬入保管容器から投入用詰替容器に詰め替えることを特徴とする請求項1または2記載のプラズマ溶融分解処理における前処理方法。   3. The pretreatment method in the plasma melting and decomposing process according to claim 1, wherein one or more kinds of objects to be processed are refilled from a carry-in storage container into a refill container for input at a predetermined mass. 搬入保管容器に封入された液状物を吸着材が投入されている投入用詰替容器に投入して吸着材により液状物を固形化することを特徴とする請求項1記載のプラズマ溶融分解処理における前処理方法。   2. The plasma melting and decomposing process according to claim 1, wherein the liquid material sealed in the carry-in storage container is charged into an input refill container into which the adsorbent is charged, and the liquid material is solidified by the adsorbent. Pre-processing method. 投入用詰替容器は本体と蓋の構成であり、その蓋に穴加工を行い、可溶性の栓で密閉することを特徴とする請求項1〜4のいずれかに記載のプラズマ溶融分解処理における前処理方法。   The charging refill container has a structure of a main body and a lid, the hole is processed in the lid, and the lid is sealed with a soluble stopper, before the plasma melting decomposition treatment according to any one of claims 1 to 4 Processing method. PCB廃棄物処理施設において処理対象物をプラズマ溶融分解炉で溶融分解して無害化処理する際に、PCB廃棄物処理施設へ搬入された搬入保管容器から、処理対象物をプラズマ溶融分解炉に投入する投入用詰替容器に詰め替える前処理設備において、
処理対象物の性状に応じて分類された群毎に定められた密閉室内に、
処理対象物を収納した搬入保管容器を傾斜させる傾斜機と、
傾斜した搬入保管容器から掻き出された処理対象物を秤量する秤量器と、
秤量されて所定の質量を詰め替えた投入用詰替容器を搬出するコンベアを備えたことを特徴とするプラズマ溶融分解処理設備における前処理設備。
When a processing object is melted and decomposed in a PCB waste treatment facility and detoxified by a plasma melting and decomposing furnace, the processing object is put into the plasma melting and decomposing furnace from a carry-in storage container carried into the PCB waste processing facility. In the pre-processing equipment for refilling into the refill container for input,
In a sealed room defined for each group classified according to the properties of the processing object,
A tilting machine for tilting the carry-in storage container storing the processing object;
A weigher for weighing a processing object scraped from an inclined carry-in storage container;
A pretreatment facility in a plasma melting and decomposing treatment facility, comprising a conveyor that carries out a refill container for weighing that has been weighed and refilled with a predetermined mass.
感圧複写紙を含水させる水槽を備えたことを特徴とする請求項6に記載のプラズマ溶融分解処理設備における前処理設備。   The pretreatment facility in a plasma melt decomposition treatment facility according to claim 6, further comprising a water tank for containing pressure-sensitive copying paper. 投入用詰替容器へ1種類以上の塩基度調整剤を供給する塩基度調整剤供給装置を備えたことを特徴とする請求項6に記載のプラズマ溶融分解処理設備における前処理設備。   The pretreatment facility in the plasma melt decomposition treatment facility according to claim 6, further comprising a basicity adjusting agent supply device that supplies one or more types of basicity adjusting agents to the charging refill container. 搬入保管容器に封入された液状物を吸着材が投入されている投入用詰替容器に投入する詰替用ポンプを備えたことを特徴とする請求項6に記載のプラズマ溶融分解処理設備における前処理設備。   7. The apparatus according to claim 6, further comprising a refilling pump for charging the liquid material sealed in the carry-in storage container into the charging refilling container in which the adsorbent is charged. Processing equipment. 投入用詰替容器へ廃活性炭を供給する廃活性炭供給装置を備えたことを特徴とする請求項6に記載のプラズマ溶融分解処理設備における前処理設備。   The pretreatment facility in the plasma melting and decomposition treatment facility according to claim 6, further comprising a waste activated carbon supply device that supplies the waste activated carbon to the charging refill container. 傾斜した搬入保管容器から掻き出された処理対象物を受ける詰替ホッパを備え、ロードセルと底部に開閉可能なフラップダンパを備えた第1段目ホッパの上方に、第1段目ホッパの上部の開口に対して前進後退可能に移動式スクリーンが配置され、第1段目ホッパの下方に、第1段目ホッパの底部に対して前進後退可能な第2段目のホッパが配置され、第2段目のホッパは底部にフラップダンパを備えていることを特徴とする請求項6に記載のプラズマ溶融分解処理設備における前処理設備。   A refill hopper for receiving a processing object scraped from an inclined carry-in storage container is provided above the first-stage hopper having a load cell and a flap damper that can be opened and closed at the bottom, above the first-stage hopper. A movable screen is disposed so as to be capable of moving forward and backward with respect to the opening, and a second stage hopper capable of moving forward and backward with respect to the bottom of the first stage hopper is disposed below the first stage hopper. The pretreatment facility in a plasma melting and decomposition treatment facility according to claim 6, wherein the hopper at the stage has a flap damper at the bottom.
JP2009024960A 2009-02-05 2009-02-05 Pretreatment method and pretreatment equipment in plasma melt decomposition treatment of processing object Expired - Fee Related JP5069703B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2009024960A JP5069703B2 (en) 2009-02-05 2009-02-05 Pretreatment method and pretreatment equipment in plasma melt decomposition treatment of processing object

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2009024960A JP5069703B2 (en) 2009-02-05 2009-02-05 Pretreatment method and pretreatment equipment in plasma melt decomposition treatment of processing object

Publications (2)

Publication Number Publication Date
JP2010179239A true JP2010179239A (en) 2010-08-19
JP5069703B2 JP5069703B2 (en) 2012-11-07

Family

ID=42761196

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2009024960A Expired - Fee Related JP5069703B2 (en) 2009-02-05 2009-02-05 Pretreatment method and pretreatment equipment in plasma melt decomposition treatment of processing object

Country Status (1)

Country Link
JP (1) JP5069703B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012139669A (en) * 2011-01-06 2012-07-26 Kawasaki Heavy Ind Ltd Method and facility for treating pcb waste
JP2018176052A (en) * 2017-04-11 2018-11-15 株式会社神鋼環境ソリューション Pcb pollutant volume reduction method

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003117517A (en) * 2001-10-11 2003-04-22 Nippon Steel Corp Method for treating material polluted with pcb
JP2007244969A (en) * 2006-03-15 2007-09-27 Nippon Steel Engineering Co Ltd Facility for detoxifying pcb waste
JP2007271492A (en) * 2006-03-31 2007-10-18 Chugoku Electric Power Co Inc:The Method and system for managing molten metal level
JP2007296415A (en) * 2006-03-14 2007-11-15 Nippon Steel Corp Treatment method of polybiphenyl chloride pollutant and treatment system therefor
JP2007301416A (en) * 2006-01-19 2007-11-22 Nippon Steel Engineering Co Ltd Treatment method for pcb waste and its treatment facility
JP2008214089A (en) * 2007-03-08 2008-09-18 Nippon Steel Engineering Co Ltd Impregnated object refilling device and method
JP2009006301A (en) * 2007-06-29 2009-01-15 Nippon Steel Engineering Co Ltd Plasma melting decomposition treatment method for bushing containing polychlorinated biphenyl

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003117517A (en) * 2001-10-11 2003-04-22 Nippon Steel Corp Method for treating material polluted with pcb
JP2007301416A (en) * 2006-01-19 2007-11-22 Nippon Steel Engineering Co Ltd Treatment method for pcb waste and its treatment facility
JP2007296415A (en) * 2006-03-14 2007-11-15 Nippon Steel Corp Treatment method of polybiphenyl chloride pollutant and treatment system therefor
JP2007244969A (en) * 2006-03-15 2007-09-27 Nippon Steel Engineering Co Ltd Facility for detoxifying pcb waste
JP2007271492A (en) * 2006-03-31 2007-10-18 Chugoku Electric Power Co Inc:The Method and system for managing molten metal level
JP2008214089A (en) * 2007-03-08 2008-09-18 Nippon Steel Engineering Co Ltd Impregnated object refilling device and method
JP2009006301A (en) * 2007-06-29 2009-01-15 Nippon Steel Engineering Co Ltd Plasma melting decomposition treatment method for bushing containing polychlorinated biphenyl

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012139669A (en) * 2011-01-06 2012-07-26 Kawasaki Heavy Ind Ltd Method and facility for treating pcb waste
JP2018176052A (en) * 2017-04-11 2018-11-15 株式会社神鋼環境ソリューション Pcb pollutant volume reduction method

Also Published As

Publication number Publication date
JP5069703B2 (en) 2012-11-07

Similar Documents

Publication Publication Date Title
TWI429487B (en) Appartus for treating waste
JPS6119742A (en) Method and apparatus for removing rubber or plastic materialfrom composite structure comprising metal and one of or bothof rubber and plastic material
JP5069703B2 (en) Pretreatment method and pretreatment equipment in plasma melt decomposition treatment of processing object
CN106311722A (en) Method for harmless treatment of waste paint buckets through converter
JP2010137156A (en) Device for removing isopropyl alcohol from paper element
JP6063107B2 (en) PCB waste processing method and processing equipment
JP4675804B2 (en) Polychlorinated biphenyl contaminant treatment facility
JP2003253037A (en) Method for dechlorinating chlorine-containing synthetic resin
Varshney et al. Hazardous wastes treatment, storage, and disposal facilities
JP2007209827A (en) Purifying method of polluted soil
JP2009172603A (en) Method and apparatus for treating contamination polluted with polychlorinated biphenyl
JP4733525B2 (en) PCB waste disposal method
JP2005262196A (en) Method and apparatus for treating contaminated matter contaminated with polychlorinated biphenyl
ES2742082T3 (en) Asbestos-containing steel scrap recycling process
JP2008055348A (en) Waste asbestos treatment apparatus and method, asbestos solidification additive, pellet production apparatus and method for stable fuel, and treatment apparatus and method for waste asbestos already enclosed in flexible container
JP6618501B2 (en) Method for reducing the volume of PCB contaminants
JP6034721B2 (en) Incineration method for drums
JP2005040691A (en) Separation treatment apparatus and method for light and heavy member
JP6165197B2 (en) PCB processing method
JP2017209659A (en) Pcb treatment method
JP2019193943A (en) Volume reduction method for pcb contaminated material
JP6457012B2 (en) Ballast refill method
JP2009222322A (en) System and method for converting inflammable waste into fuel
JP2003094013A (en) Treating method for rendering capacitor for fluorescent lamp ballast harmless and system therefor
JP2014108408A (en) Dehydration treatment apparatus for pcb contaminated sludge or residues, and pcb processing system using the same

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20111109

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20120412

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20120420

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20120604

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20120720

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20120817

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20150824

Year of fee payment: 3

R150 Certificate of patent or registration of utility model

Ref document number: 5069703

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150

Free format text: JAPANESE INTERMEDIATE CODE: R150

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20150824

Year of fee payment: 3

S533 Written request for registration of change of name

Free format text: JAPANESE INTERMEDIATE CODE: R313533

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20150824

Year of fee payment: 3

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20150824

Year of fee payment: 3

S533 Written request for registration of change of name

Free format text: JAPANESE INTERMEDIATE CODE: R313533

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20150824

Year of fee payment: 3

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

S533 Written request for registration of change of name

Free format text: JAPANESE INTERMEDIATE CODE: R313533

S533 Written request for registration of change of name

Free format text: JAPANESE INTERMEDIATE CODE: R313533

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

S111 Request for change of ownership or part of ownership

Free format text: JAPANESE INTERMEDIATE CODE: R313115

R350 Written notification of registration of transfer

Free format text: JAPANESE INTERMEDIATE CODE: R350

LAPS Cancellation because of no payment of annual fees