JP2013184089A - Treatment method and treatment device for pcb-containing waste - Google Patents

Treatment method and treatment device for pcb-containing waste Download PDF

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JP2013184089A
JP2013184089A JP2012049419A JP2012049419A JP2013184089A JP 2013184089 A JP2013184089 A JP 2013184089A JP 2012049419 A JP2012049419 A JP 2012049419A JP 2012049419 A JP2012049419 A JP 2012049419A JP 2013184089 A JP2013184089 A JP 2013184089A
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pcb
waste
heating furnace
containing waste
gas
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Takeshi Tayama
武志 田山
Takeshi Ikeda
武史 池田
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Dowa Eco Systems Co Ltd
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Dowa Eco Systems Co Ltd
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/82Recycling of waste of electrical or electronic equipment [WEEE]

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  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a treatment method and treatment device for PCB-containing waste capable of smoothly controlling a temperature in heating, capable of evenly heating the waste, and capable of volatilizing PCB in treatment for detoxifying the PCB in which a small amount of PCB adheres to electric equipment or the like.SOLUTION: In a method for treating PCB-containing waste, the PCB-containing waste 4 is carried into a continuous heating furnace 2, and heated at 850-950°C for 4-6 hours, the PCB is volatilized from the waste 4, and then, the gas discharged from the heating furnace 2 is heated in a gas combustion furnace 24 at a temperature of 1,100°C or higher for two seconds or more, and the gas containing PCB is burned at a high temperature, and is detoxified. The atmosphere in the heating furnace 2 is stirred by a fan 31.

Description

本発明は、PCBで汚染された廃棄物を無害化するためのPCB含有廃棄物の処理方法および処理装置に関する。   The present invention relates to a method and apparatus for treating PCB-containing waste for detoxifying waste contaminated with PCB.

PCBとは、ビフェニルの水素が塩素に置換された化合物の総称であり、化学的に安定で絶縁性に優れることから、かつてはコンデンサやトランスの絶縁油などに幅広く用いられていた。しかし、一方で毒性の高さから、1972年には製造、輸入、使用が禁止され、さらに平成13年には「PCB特別措置法」が施行され、平成28年までに処理しなければならないことになっている。   PCB is a general term for compounds in which hydrogen of biphenyl is substituted with chlorine, and has been widely used in insulating oils for capacitors and transformers because it is chemically stable and excellent in insulating properties. However, due to its high toxicity, manufacturing, importation and use were prohibited in 1972, and the “PCB Special Measures Law” was enacted in 2001 and must be processed by 2016. It has become.

従来、PCB処理として、溶剤洗浄や、真空加熱分離方式での処理が行われている。例えば特許文献1には、ロータリーキルン内で低濃度PCBを含有する処理対象物を焼却または焼成処理し、ロータリーキルンから排出された排ガスを二次燃焼室で分解する処理方法が記載されている。また、バッチ式の焼却処理では、処理物を炉に出し入れする際に加熱を止めなければならず、不可避的にロスが発生するため、例えば特許文献2に記載されているような連続式の焼却処理システムが提案されている。   Conventionally, as PCB processing, solvent cleaning or vacuum heating separation processing has been performed. For example, Patent Document 1 describes a processing method in which a processing object containing low-concentration PCB is incinerated or baked in a rotary kiln, and exhaust gas discharged from the rotary kiln is decomposed in a secondary combustion chamber. In addition, in the batch type incineration process, heating must be stopped when the processed product is put into and out of the furnace, and inevitably loss occurs. For example, continuous incineration as described in Patent Document 2 is performed. A processing system has been proposed.

特許文献3には、電気機器等に付着している微量PCB含有絶縁油を連続炉内で加熱して揮発させ、その燃焼ガスを排ガス処理手段で焼却する加熱分離処理方式を採用することにより、微量PCB含有廃棄電気機器を効率よく安全に処理できることが記載されている。   In Patent Document 3, by adopting a heat separation treatment method in which a trace amount of PCB-containing insulating oil adhering to electrical equipment or the like is heated and volatilized in a continuous furnace, and the combustion gas is incinerated by an exhaust gas treatment means, It is described that a small amount of PCB-containing waste electrical equipment can be processed efficiently and safely.

特開2010−75848号公報JP 2010-75848 A 特開2011−110450号公報JP 2011-110450 A 特開2011−56504号公報JP 2011-56504 A

しかしながら、従来の焼却方法にあっては、焼却炉の構成が複雑化するうえ、処理に手間がかかるため、低コスト化を図ることが困難であるという問題があった。さらに、特許文献3に記載されたような連続炉による加熱処理においては、炉内が均等に加熱されず、一部に焼き付けが起こる場合があった。   However, in the conventional incineration method, the configuration of the incinerator is complicated, and the processing is troublesome, so that it is difficult to reduce the cost. Furthermore, in the heat treatment by a continuous furnace as described in Patent Document 3, the inside of the furnace is not heated evenly, and there are cases where baking occurs in part.

本発明は、上記の課題に鑑みてなされたものであり、電気機器等に微量のPCBが付着したPCB含有廃棄物を無害化する処理において、加熱時の温度コントロールが円滑に行えて、廃棄物を均等に加熱し、PCBを揮発させることができるPCB含有廃棄物の処理方法および処理装置を提供することを目的とする。   The present invention has been made in view of the above problems, and in the process of detoxifying PCB-containing waste having a small amount of PCB attached to electrical equipment or the like, temperature control during heating can be smoothly performed, and waste An object of the present invention is to provide a processing method and a processing apparatus for PCB-containing waste that can uniformly heat the PCB and volatilize the PCB.

上記問題を解決するため、本発明は、PCB含有廃棄物を、連続式の加熱炉内に搬入し、850℃〜950℃で4時間〜6時間加熱して、前記廃棄物からPCBを揮発させた後、前記加熱炉から排出されたガスを、ガス燃焼炉において1100℃以上で2秒以上加熱し、PCBを含むガスを高温燃焼させて無害化するPCB含有廃棄物の処理方法において、前記加熱炉内の雰囲気をファンで撹拌することを特徴とする、PCB含有廃棄物の処理方法を提供する。   In order to solve the above problems, the present invention carries PCB-containing waste into a continuous heating furnace and heats it at 850 ° C. to 950 ° C. for 4 to 6 hours to volatilize PCB from the waste. Then, in the method for treating PCB-containing waste, the gas discharged from the heating furnace is heated in a gas combustion furnace at 1100 ° C. or more for 2 seconds or more, and the gas containing PCB is burned at a high temperature to render it harmless. Provided is a method for treating PCB-containing waste, wherein the atmosphere in the furnace is stirred with a fan.

この処理方法において、前記ファンは、前記加熱炉を850℃以上に昇温するまでの区間に配置してもよい。前記廃棄物の加熱を、酸化雰囲気下で行うことが好ましい。また、前記廃棄物が、微量PCB含有絶縁油を液抜きした後のトランスであってもよい。   In this processing method, the fan may be arranged in a section until the temperature of the heating furnace is raised to 850 ° C. or higher. It is preferable to heat the waste in an oxidizing atmosphere. Further, the waste may be a transformer after draining a trace amount of PCB-containing insulating oil.

また、本発明によれば、PCB含有廃棄物を850℃〜950℃で4時間〜6時間加熱してPCBを連続的に揮発させる加熱炉と、前記加熱炉のガス排出口から排出されたガスを処理する排ガス処理手段と、を有し、前記加熱炉は、搬入待機室と、昇温部および温度保持部を有する処理室と、搬出待機室とを順に備えた連続炉であり、搬入待機室と加熱室の間、及び処理室と搬出待機室の間に、開閉可能な扉が設けられ、前記処理室の天井部に、前記処理室内の雰囲気を撹拌するファンが設けられていることを特徴とする、PCB含有廃棄物の処理装置が提供される。   In addition, according to the present invention, the PCB-containing waste is heated at 850 ° C. to 950 ° C. for 4 to 6 hours to continuously volatilize PCB, and the gas discharged from the gas outlet of the heating furnace The heating furnace is a continuous furnace including a carry-in standby chamber, a treatment chamber having a temperature raising unit and a temperature holding unit, and a carry-out standby chamber in order, A door that can be opened and closed is provided between the chamber and the heating chamber, and between the processing chamber and the unloading standby chamber, and a fan for stirring the atmosphere in the processing chamber is provided at the ceiling of the processing chamber. A PCB-containing waste treatment apparatus is provided.

この処理装置において、前記ファンは、前記昇温部に設けられていることが好ましい。また、前記排ガス処理手段は、前記加熱炉から排出されたガスを1100℃以上で燃焼させるガス燃焼炉、冷却塔、中和・集塵機、および煙突で構成されてもよい。   In this processing apparatus, the fan is preferably provided in the temperature raising unit. Further, the exhaust gas treatment means may be constituted by a gas combustion furnace for burning the gas discharged from the heating furnace at 1100 ° C. or higher, a cooling tower, a neutralization / dust collector, and a chimney.

本発明によれば、加熱炉内の対流を促進し、温度コントロールを円滑に行って、適正な加熱処理を行い、PCBを揮発させることができる。   According to the present invention, it is possible to promote convection in a heating furnace, perform temperature control smoothly, perform proper heat treatment, and volatilize PCB.

本発明にかかるPCB含有廃棄物の処理装置の概要図である。It is a schematic diagram of the processing device of PCB content waste concerning the present invention. 図2の加熱炉の平断面図である。It is a plane sectional view of the heating furnace of FIG.

以下、本発明の実施の形態を、図を参照して説明する。   Hereinafter, embodiments of the present invention will be described with reference to the drawings.

図1は、本発明に係るPCB含有廃棄物の処理装置の例を示す。処理装置1は、PCB含有廃棄物4を加熱する連続式の加熱炉2と、加熱炉2で発生する排ガスを処理する排ガス処理手段3を有する。加熱炉2は、搬入待機室11と、処理室12と、搬出待機室13とで構成されている。処理室12は、被処理物であるPCB含有廃棄物4を850℃以上に昇温させる昇温部14と、廃棄物4を搬出方向に搬送しながら850℃〜950℃で4時間〜6時間加熱する温度保持部15と、冷却部16とを有する。昇温部14および保持部15には、加熱炉2内を所定温度に加熱するバーナー(図示省略)が、適宜台数設置されている。搬入待機室11と昇温部14との間、及び、冷却部16と搬出待機室13との間には、油圧等により開閉可能な扉17、18が設けられている。また、処理室12内の温度保持部15と冷却部16との間にも、扉を設けてもよい。加熱炉2を連続炉とすることにより、バッチ方式の炉で加熱処理を行うよりも温度のロスが少なく効率的であり、且つ大量の廃棄物を処理することができる。   FIG. 1 shows an example of a PCB-containing waste processing apparatus according to the present invention. The processing apparatus 1 includes a continuous heating furnace 2 that heats the PCB-containing waste 4 and an exhaust gas processing means 3 that processes the exhaust gas generated in the heating furnace 2. The heating furnace 2 includes a carry-in standby chamber 11, a processing chamber 12, and a carry-out standby chamber 13. The processing chamber 12 includes a temperature raising unit 14 that raises the temperature of the PCB-containing waste 4 to be processed to 850 ° C. or higher, and 4 to 6 hours at 850 ° C. to 950 ° C. while conveying the waste 4 in the carrying-out direction. A heating temperature holding unit 15 and a cooling unit 16 are provided. The heating unit 14 and the holding unit 15 are appropriately provided with a number of burners (not shown) for heating the inside of the heating furnace 2 to a predetermined temperature. Doors 17 and 18 that can be opened and closed by hydraulic pressure or the like are provided between the carry-in standby chamber 11 and the temperature raising unit 14 and between the cooling unit 16 and the carry-out standby chamber 13. Further, a door may be provided between the temperature holding unit 15 and the cooling unit 16 in the processing chamber 12. By using the heating furnace 2 as a continuous furnace, the temperature loss is less than that in a batch-type furnace, which is efficient, and a large amount of waste can be processed.

処理室12の天井には、加熱炉2の処理室12内の排ガスを排出するガス排出口21が設けられている。ガス排出口21は、850℃以上に加熱される昇温部14の天井に設けられる。ガス排出口21は、煙道22を介して、排ガス処理手段3のガス燃焼炉24のガス導入口23に連結される。ガス燃焼炉24は、例えばロータリーキルンなど、十分な温度及び滞留時間を得ることができる燃焼炉からなり、加熱炉2からの排ガスを1100℃以上で2秒以上燃焼する。   A gas discharge port 21 for discharging exhaust gas in the processing chamber 12 of the heating furnace 2 is provided on the ceiling of the processing chamber 12. The gas discharge port 21 is provided on the ceiling of the temperature raising unit 14 heated to 850 ° C. or higher. The gas discharge port 21 is connected to the gas introduction port 23 of the gas combustion furnace 24 of the exhaust gas processing means 3 through the flue 22. The gas combustion furnace 24 is a combustion furnace that can obtain a sufficient temperature and residence time, such as a rotary kiln, and burns the exhaust gas from the heating furnace 2 at 1100 ° C. or more for 2 seconds or more.

ガス排出口21の位置は、図1の例に限らないが、搬入待機室11と処理室12との間の扉17が過熱されないために、搬入待機室11側の扉17付近で排気が行われることが好ましい。さらに、昇温部14は燃焼ガスの発生量が多いために、昇温部14の排気を行うことが好ましく、これにより、温度保持部15において、搬出側から搬入側へ熱を移動させ、熱効率を上昇させることができる。したがって、図1に示すように、搬入待機室11付近に設けることが好ましい。また、昇温部14に複数のガス排出口21を設けて排気してもよい。   Although the position of the gas discharge port 21 is not limited to the example of FIG. 1, the door 17 between the carry-in standby chamber 11 and the processing chamber 12 is not overheated, so that exhaust is performed near the door 17 on the carry-in standby chamber 11 side. Are preferred. Further, since the temperature raising unit 14 generates a large amount of combustion gas, it is preferable to exhaust the temperature raising unit 14. As a result, in the temperature holding unit 15, heat is transferred from the carry-out side to the carry-in side. Can be raised. Therefore, as shown in FIG. 1, it is preferable to provide near the carry-in waiting room 11. Further, the temperature raising unit 14 may be provided with a plurality of gas discharge ports 21 for exhaust.

排ガス処理手段3は、前述のガス燃焼炉24と、ガス燃焼炉24に連結された冷却塔25、バグフィルタ26、脱臭塔27、誘引排風機28、煙突29により構成される。なお、本発明において、排ガス処理手段3は、これらの構成に限ることはない。   The exhaust gas treatment means 3 includes the gas combustion furnace 24 described above, a cooling tower 25 connected to the gas combustion furnace 24, a bag filter 26, a deodorization tower 27, an induction exhaust fan 28, and a chimney 29. In the present invention, the exhaust gas treatment means 3 is not limited to these configurations.

さらに、本発明では、処理室12の昇温部14の天井部に、複数のファン31が設けられている。ファン31は、昇温部14の複数箇所、例えば図1、2に示すように、廃棄物4の搬送方向に適宜間隔を有して幅方向左右に2箇所ずつ、合計6箇所程度設置される。これらのファン31は、加熱炉2の稼働時は、常に運転させる。ファン31の位置や台数は図示の例に限らないが、昇温部14または少なくとも温度保持部15の前半部分に設けることにより、温度分布を均一にし、温度調整が円滑に行える効果が得られるとともに、ガス排出口21に向けてガスを排出させる対流が効率良く生じる。   Furthermore, in the present invention, a plurality of fans 31 are provided on the ceiling of the temperature raising unit 14 of the processing chamber 12. As shown in FIGS. 1 and 2, for example, the fan 31 is installed at a total of about six locations, two at the left and right in the width direction with appropriate intervals in the conveyance direction of the waste 4. . These fans 31 are always operated when the heating furnace 2 is in operation. The position and the number of fans 31 are not limited to the example shown in the figure, but by providing them in the temperature raising unit 14 or at least the first half of the temperature holding unit 15, the temperature distribution can be made uniform and the temperature can be adjusted smoothly. The convection for discharging the gas toward the gas discharge port 21 is efficiently generated.

PCB含有廃棄物4は、例えばドラム缶等の容器に収納され、容器の上方を開放した状態で台車32に載せて、連続加熱処理される。廃棄物4は、図1に示すように、火格子33等を介して台車32に載せて、加熱炉2内を搬送することが望ましい。火格子33の格子の隙間を通って廃棄物4の底面から加熱されるうえ、廃棄物4または廃棄物4を収容した容器の底面にゆがみや変形等があっても、格子上であれば安定して設置できる。   The PCB-containing waste 4 is stored in a container such as a drum can, for example, and placed on the carriage 32 in a state where the upper part of the container is opened, and subjected to continuous heat treatment. As shown in FIG. 1, the waste 4 is preferably carried on the carriage 32 via a grate 33 or the like and conveyed in the heating furnace 2. Heated from the bottom surface of the waste 4 through the lattice gap of the grate 33, and even if the waste 4 or the bottom surface of the container containing the waste 4 is distorted or deformed, it is stable on the lattice. Can be installed.

加熱炉2の扉17、18は、油圧等により押されることで、確実に密閉できるようにする。なお、加熱炉2内には、焼却ガスなどにより炉内圧力が生じるが、誘引排風機28により、常にガス排出口21を介して加熱炉2内のガスを吸引しているため、処理室12内は外部の大気圧に対して負圧となり、処理室12内のガスが加熱炉2の外部へ漏洩することはない。   The doors 17 and 18 of the heating furnace 2 can be reliably sealed by being pushed by hydraulic pressure or the like. In the heating furnace 2, the pressure in the furnace is generated by incineration gas or the like, but the gas in the heating furnace 2 is always sucked through the gas discharge port 21 by the induced exhaust fan 28, and thus the processing chamber 12. The inside becomes a negative pressure with respect to the external atmospheric pressure, and the gas in the processing chamber 12 does not leak to the outside of the heating furnace 2.

以下、本発明の処理装置1を用いた処理手順について説明する。   Hereinafter, a processing procedure using the processing apparatus 1 of the present invention will be described.

本発明により処理される被処理物は、微量のPCBを含む絶縁油によって汚染された電気機器やケーブル等のPCBを含有する廃棄物4であり、具体的には、例えば微量PCB含有絶縁油を液抜きした後のトランス、または切断したOFケーブル(油浸紙絶縁ケーブル)等である。このような廃棄物4は、有姿のままで、またはケーブル等の場合には容器に収納して、台車32上に載置する。トランスの場合は、PCB含有絶縁油を液抜きした後に、上方を開放した状態で台車32に乗せる。OFケーブルの場合は、断面が露出するようにケーブルの軸方向に垂直に切断し、容器に入れて台車32に乗せる。この容器は、切断したOFケーブルを立てた状態で収容できて、且つ加熱炉2内の熱に耐える材質のものであり、例えばスチールドラム缶などが用いられる。そして、加熱により発生するガスをケーブルに残留させないように、容器の上方を開放する。本発明の実施において、OFケーブルを容器に収容せずに処理してもよいが、容器に入れて処理することで、効率良く処理できる。   The object to be treated according to the present invention is waste 4 containing PCB such as electrical equipment and cables contaminated by insulating oil containing a trace amount of PCB. Specifically, for example, a trace amount of PCB containing insulating oil is used. A transformer after draining, or a cut OF cable (oil-insulated paper insulated cable). The waste 4 is placed on the carriage 32 as it is or in a container such as a cable. In the case of a transformer, after draining the PCB-containing insulating oil, it is placed on the carriage 32 with its upper part opened. In the case of an OF cable, it is cut perpendicular to the axial direction of the cable so that the cross section is exposed, put in a container and placed on the carriage 32. This container is made of a material that can hold the cut OF cable in an upright state and can withstand the heat in the heating furnace 2. For example, a steel drum can is used. And the upper part of a container is open | released so that the gas generated by heating may not remain in a cable. In the implementation of the present invention, the OF cable may be processed without being accommodated in the container, but can be processed efficiently by being processed in the container.

台車32上に載置したPCB含有廃棄物4は、加熱炉2の搬入待機室11から扉17を開けて処理室12内へ搬入し、搬送方向に搬送しながら、バーナーにより昇温部14が昇温されて850℃以上になってから、温度保持部15において、850℃〜950℃に保持された状態で、4時間〜6時間加熱する。この加熱は、酸化雰囲気下で行うのがよい。加熱温度が低いと、油分などの揮発が進まないことがあり、高すぎると、コストの増大を招く。また、加熱の際には、一定の昇温幅であることが、燃焼ガスの発生量を一定に制御できる点で好ましい。さらに、処理室12での加熱処理は、酸化雰囲気下で行うことが、焼却残物の量(質量、体積)が減量する点で好ましく、酸素濃度は10%以上であることが好ましい。廃棄物4の搬送は、例えばプッシャーにより行い、図中矢印方向に一定の速度で搬送する。この加熱により、PCBで汚染された廃棄物4からPCB含有液とともにPCBを揮発させ、除去することができる。処理後の廃棄物4は、その後、冷却部16で冷却される。本発明では、加熱炉2の処理室12内にファン31を設けたことにより、処理室12の内部の温度が効率的且つ均等に上昇し、排ガスの排ガス処理手段3への流れをスムーズにする。したがって、従来起こっていた焼き付き等のトラブルを防ぎ、安定してPCB含有廃棄物4の処理を行うことができる。冷却部16で冷却された廃棄物4は、扉18を開けて搬出待機室13へ搬送される。   The PCB-containing waste 4 placed on the carriage 32 opens the door 17 from the carry-in standby chamber 11 of the heating furnace 2 and carries it into the processing chamber 12. After the temperature is raised to 850 ° C. or higher, the temperature holding unit 15 is heated for 4 hours to 6 hours while being held at 850 ° C. to 950 ° C. This heating is preferably performed in an oxidizing atmosphere. If the heating temperature is low, volatilization of oil or the like may not progress, and if it is too high, the cost increases. Further, when heating, a constant temperature increase width is preferable because the amount of combustion gas generated can be controlled to be constant. Further, the heat treatment in the treatment chamber 12 is preferably performed in an oxidizing atmosphere from the viewpoint of reducing the amount (mass, volume) of the incineration residue, and the oxygen concentration is preferably 10% or more. The waste 4 is transported by a pusher, for example, and transported at a constant speed in the direction of the arrow in the figure. By this heating, the PCB can be volatilized and removed from the waste 4 contaminated with the PCB together with the PCB-containing liquid. The treated waste 4 is then cooled by the cooling unit 16. In the present invention, by providing the fan 31 in the processing chamber 12 of the heating furnace 2, the temperature inside the processing chamber 12 rises efficiently and evenly, and the flow of the exhaust gas to the exhaust gas treatment means 3 is made smooth. . Therefore, troubles such as burn-in that have conventionally occurred can be prevented, and the PCB-containing waste 4 can be treated stably. The waste 4 cooled by the cooling unit 16 is conveyed to the unloading standby chamber 13 with the door 18 opened.

排ガス処理手段3においては、加熱炉2から排出される排ガスを無害にするための処理が行われる。加熱炉2の処理室12内で発生したPCBを含む排ガスは、ガス排出口21から煙道22を通ってガス燃焼炉24へ送られ、ガス燃焼炉24において、1100℃以上で2秒以上加熱される。排ガスを1100℃以上で2秒以上高温燃焼することにより、排ガス中のPCBを含む有機成分を分解することができる。煙道22は、昇温部14で発生する多量の燃焼ガスの排気効率を高めるため、廃棄物4の進行方向に複数設け、それらをガス燃焼炉24に接続してもよい。また、温度保持部15の余熱を昇温部14で利用するための煙道を設けることもできる。さらに、搬入待機室11の天井に煙道を設けて、温度上昇を緩和する調整を行ってもよい。   In the exhaust gas treatment means 3, a treatment for making the exhaust gas discharged from the heating furnace 2 harmless is performed. The exhaust gas containing PCB generated in the processing chamber 12 of the heating furnace 2 is sent from the gas discharge port 21 to the gas combustion furnace 24 through the flue 22 and heated in the gas combustion furnace 24 at 1100 ° C. or more for 2 seconds or more. Is done. The organic component containing PCB in the exhaust gas can be decomposed by burning the exhaust gas at 1100 ° C. or higher for 2 seconds or more. In order to increase the exhaust efficiency of a large amount of combustion gas generated in the temperature raising unit 14, a plurality of the flue 22 may be provided in the traveling direction of the waste 4 and connected to the gas combustion furnace 24. Further, a flue for using the remaining heat of the temperature holding unit 15 in the temperature raising unit 14 can be provided. Further, a flue may be provided on the ceiling of the carry-in waiting room 11 to adjust the temperature rise.

ガス燃焼炉24でPCBが高温燃焼された後の排ガスは、冷却塔25で冷却された後、消石灰や活性炭等の中和剤を加えて中和され、バグフィルタ26で集塵されて固形物は飛灰となり、気体は脱臭塔27で脱臭された後、煙突29から排出される。   The exhaust gas after the PCB is burned at a high temperature in the gas combustion furnace 24 is cooled in the cooling tower 25, neutralized by adding a neutralizing agent such as slaked lime or activated carbon, collected by the bag filter 26, and collected as solid matter. Becomes fly ash, and the gas is deodorized by the deodorization tower 27 and then discharged from the chimney 29.

なお、処理済みのトランスは、解体し、ケースは、電炉や転炉のスクラップ源として利用される。ケースから取り出されたトランスコアは、モービルシャーにより銅コイルを切断し、コイル線とコアを分離する。分離したコアのうち、特別管理産業廃棄物の判定基準を満たす場合は、スクラップ源としてそのまま利用することができる。また、分離した銅コイルや可燃物は、燃焼させて銅コイルを溶融し、銅としてリサイクルすることができる。   The treated transformer is disassembled, and the case is used as a scrap source for electric furnaces and converters. The transformer core taken out from the case cuts the copper coil by a mobile shear and separates the coil wire and the core. Of the separated cores, if they meet the criteria for specially managed industrial waste, they can be used directly as scrap sources. Moreover, the separated copper coil and combustible material can be burned to melt the copper coil and be recycled as copper.

以上、本発明の好適な実施形態について説明したが、本発明はかかる例に限定されない。当業者であれば、特許請求の範囲に記載された技術的思想の範疇内において、各種の変更例または修正例に想到しうることは明らかであり、それらについても当然に本発明の技術的範囲に属するものと了解される。   As mentioned above, although preferred embodiment of this invention was described, this invention is not limited to this example. It is obvious for those skilled in the art that various changes or modifications can be conceived within the scope of the technical idea described in the claims. It is understood that it belongs to.

0.67〜0.68mg/kgのPCBを含む絶縁油で汚染されたトランス及び内部部材を、本発明の処理装置で処理した。先ずトランス及び内部部材を加熱炉2で875℃、4時間加熱した。加熱炉2による処理後のPCB濃度は、鉄心が0.01μg/100cm未満、コイルが0.001mg/kg未満、燃え殻が0.99ng/g−dryであった。加熱炉2の排ガスをガス燃焼炉24で1125℃、2秒以上燃焼させたものを、図1に示す冷却塔25、バグフィルタ26、脱臭塔27を経て煙突29から排出した。バグフィルタ26で集塵した集塵灰のPCB含有量は1.2ng/g−dry、煙突29から排出された排ガスのPCB含有量は2.5ng/Nmであった。いずれも極めて低く、PCB処理が適切に行われた。 Transformers and internal components contaminated with insulating oil containing 0.67 to 0.68 mg / kg PCB were processed with the processing apparatus of the present invention. First, the transformer and the internal member were heated in the heating furnace 2 at 875 ° C. for 4 hours. The PCB concentration after the treatment by the heating furnace 2 was less than 0.01 μg / 100 cm 2 for the iron core, less than 0.001 mg / kg for the coil, and 0.99 ng / g-dry for the burning shell. The exhaust gas from the heating furnace 2 burned in the gas combustion furnace 24 at 1125 ° C. for 2 seconds or more was discharged from the chimney 29 through the cooling tower 25, bag filter 26 and deodorization tower 27 shown in FIG. The PCB content of the dust collection ash collected by the bag filter 26 was 1.2 ng / g-dry, and the PCB content of the exhaust gas discharged from the chimney 29 was 2.5 ng / Nm 3 . Both were very low and PCB processing was performed properly.

一方、加熱炉内にファンを設けない場合には、焼き付けが生じ、PCB処理が行えなかった。   On the other hand, when a fan was not provided in the heating furnace, baking occurred and PCB processing could not be performed.

本発明のPCB含有廃棄物の処理方法及びPCB含有廃棄物の処理装置は、トランス及びOFケーブル(油浸紙絶縁ケーブル)等の廃棄電気機器に付着している微量PCB含有絶縁油を効率よく安全に処理することができる。   The PCB-containing waste processing method and PCB-containing waste processing apparatus of the present invention efficiently and safely removes trace amounts of PCB-containing insulating oil adhering to waste electrical equipment such as transformers and OF cables (oil-immersed paper insulating cables). Can be processed.

1 処理装置
2 加熱炉
3 排ガス処理手段
4 廃棄物
11 搬入待機室
12 処理室
13 搬出待機室
14 昇温部
15 温度保持部
16 冷却部
17、18 扉
21 ガス排出口
22 煙道
23 ガス導入口
24 ガス燃焼炉
25 冷却塔
26 バグフィルタ
27 脱臭塔
28 誘引排風機
29 煙突
31 ファン
DESCRIPTION OF SYMBOLS 1 Processing apparatus 2 Heating furnace 3 Exhaust gas treatment means 4 Waste 11 Carry-in waiting room 12 Processing chamber 13 Carry-out waiting room 14 Temperature rising part 15 Temperature holding part 16 Cooling parts 17 and 18 Door 21 Gas discharge port 22 Flue 23 Gas introduction port 24 gas combustion furnace 25 cooling tower 26 bag filter 27 deodorization tower 28 induction exhaust fan 29 chimney 31 fan

Claims (7)

PCB含有廃棄物を、連続式の加熱炉内に搬入し、850℃〜950℃で4時間〜6時間加熱して、前記廃棄物からPCBを揮発させた後、前記加熱炉から排出されたガスを、ガス燃焼炉において1100℃以上で2秒以上加熱し、PCBを含むガスを高温燃焼させて無害化するPCB含有廃棄物の処理方法において、
前記加熱炉内の雰囲気をファンで撹拌することを特徴とする、PCB含有廃棄物の処理方法。
The PCB-containing waste is carried into a continuous heating furnace, heated at 850 ° C. to 950 ° C. for 4 to 6 hours to volatilize PCB from the waste, and then discharged from the heating furnace. In a method for treating PCB-containing waste, which is heated at 1100 ° C. or higher for 2 seconds or more in a gas combustion furnace and detoxified by high-temperature combustion of a gas containing PCB,
A method for treating PCB-containing waste, wherein the atmosphere in the heating furnace is stirred with a fan.
前記ファンは、前記加熱炉を850℃以上に昇温するまでの区間に配置することを特徴とする、請求項1に記載のPCB含有廃棄物の処理方法。   2. The method for treating PCB-containing waste according to claim 1, wherein the fan is disposed in a section until the temperature of the heating furnace is increased to 850 ° C. or more. 前記廃棄物の加熱を、酸化雰囲気下で行うことを特徴とする、請求項1または2に記載のPCB含有廃棄物の処理方法。   The method for treating PCB-containing waste according to claim 1 or 2, wherein the waste is heated in an oxidizing atmosphere. 前記廃棄物が、微量PCB含有絶縁油を液抜きした後のトランスであることを特徴とする、請求項1〜3のいずれかに記載のPCB含有廃棄物の処理方法。   The method for treating PCB-containing waste according to any one of claims 1 to 3, wherein the waste is a transformer after a trace amount of PCB-containing insulating oil has been drained. PCB含有廃棄物を850℃〜950℃で4時間〜6時間加熱してPCBを連続的に揮発させる加熱炉と、前記加熱炉のガス排出口から排出されたガスを処理する排ガス処理手段と、を有し、
前記加熱炉は、搬入待機室と、昇温部および温度保持部を有する処理室と、搬出待機室とを順に備えた連続炉であり、搬入待機室と加熱室の間、及び処理室と搬出待機室の間に、開閉可能な扉が設けられ、
前記処理室の天井部に、前記処理室内の雰囲気を撹拌するファンが設けられていることを特徴とする、PCB含有廃棄物の処理装置。
A heating furnace in which PCB-containing waste is heated at 850 ° C. to 950 ° C. for 4 to 6 hours to volatilize PCB continuously, and an exhaust gas treatment means for treating the gas discharged from the gas outlet of the heating furnace, Have
The heating furnace is a continuous furnace provided in order with a carry-in standby chamber, a processing chamber having a temperature raising unit and a temperature holding unit, and a carry-out standby chamber. There is a door that can be opened and closed between the waiting rooms.
A PCB-containing waste processing apparatus, wherein a fan for stirring the atmosphere in the processing chamber is provided on the ceiling of the processing chamber.
前記ファンは、前記昇温部に設けられていることを特徴とする、請求項5に記載のPCB含有廃棄物の処理装置。   6. The PCB-containing waste processing apparatus according to claim 5, wherein the fan is provided in the temperature raising unit. 前記排ガス処理手段は、前記加熱炉から排出されたガスを1100℃以上で燃焼させるガス燃焼炉、冷却塔、中和・集塵機、および煙突で構成されることを特徴とする、請求項5または6に記載のPCB含有廃棄物の処理装置。   The exhaust gas treatment means includes a gas combustion furnace for burning the gas discharged from the heating furnace at 1100 ° C or higher, a cooling tower, a neutralization / dust collector, and a chimney. The processing apparatus of the waste containing PCB described in 1.
JP2012049419A 2012-03-06 2012-03-06 Treatment method and treatment device for pcb-containing waste Pending JP2013184089A (en)

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CN104566398A (en) * 2014-12-17 2015-04-29 兰州有色冶金设计研究院有限公司 Device and method for treating waste printed circuit boards
JP2018053303A (en) * 2016-09-28 2018-04-05 Dowaエコシステム株式会社 Recovery container for molten metal and method for treating waste

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JP2001038731A (en) * 1999-05-25 2001-02-13 Masao Umemoto Technique for reducing and melting plastic
JP2002102819A (en) * 2000-09-28 2002-04-09 E & N:Kk Heat treatment method of medical waste and its apparatus
JP2011056504A (en) * 2008-10-16 2011-03-24 Dowa Eco-System Co Ltd Method and apparatus for treating pcb-containing material

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Publication number Priority date Publication date Assignee Title
JP2001038731A (en) * 1999-05-25 2001-02-13 Masao Umemoto Technique for reducing and melting plastic
JP2002102819A (en) * 2000-09-28 2002-04-09 E & N:Kk Heat treatment method of medical waste and its apparatus
JP2011056504A (en) * 2008-10-16 2011-03-24 Dowa Eco-System Co Ltd Method and apparatus for treating pcb-containing material

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104566398A (en) * 2014-12-17 2015-04-29 兰州有色冶金设计研究院有限公司 Device and method for treating waste printed circuit boards
JP2018053303A (en) * 2016-09-28 2018-04-05 Dowaエコシステム株式会社 Recovery container for molten metal and method for treating waste

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