JP2008100166A - Method for separating and recovering pcb, and apparatus therefor - Google Patents

Method for separating and recovering pcb, and apparatus therefor Download PDF

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JP2008100166A
JP2008100166A JP2006284899A JP2006284899A JP2008100166A JP 2008100166 A JP2008100166 A JP 2008100166A JP 2006284899 A JP2006284899 A JP 2006284899A JP 2006284899 A JP2006284899 A JP 2006284899A JP 2008100166 A JP2008100166 A JP 2008100166A
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pcb
separating
aprotic organic
organic polar
hydrocarbon solvent
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Kenji Suzuki
健二 鈴木
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AIT KK
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D11/00Solvent extraction
    • B01D11/04Solvent extraction of solutions which are liquid
    • B01D11/0446Juxtaposition of mixers-settlers
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D17/00Separation of liquids, not provided for elsewhere, e.g. by thermal diffusion
    • B01D17/02Separation of non-miscible liquids
    • B01D17/0208Separation of non-miscible liquids by sedimentation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D17/00Separation of liquids, not provided for elsewhere, e.g. by thermal diffusion
    • B01D17/02Separation of non-miscible liquids
    • B01D17/04Breaking emulsions
    • B01D17/047Breaking emulsions with separation aids
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G21/00Refining of hydrocarbon oils, in the absence of hydrogen, by extraction with selective solvents
    • C10G21/006Refining of hydrocarbon oils, in the absence of hydrogen, by extraction with selective solvents of waste oils, e.g. PCB's containing oils
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01BCABLES; CONDUCTORS; INSULATORS; SELECTION OF MATERIALS FOR THEIR CONDUCTIVE, INSULATING OR DIELECTRIC PROPERTIES
    • H01B3/00Insulators or insulating bodies characterised by the insulating materials; Selection of materials for their insulating or dielectric properties
    • H01B3/18Insulators or insulating bodies characterised by the insulating materials; Selection of materials for their insulating or dielectric properties mainly consisting of organic substances
    • H01B3/20Insulators or insulating bodies characterised by the insulating materials; Selection of materials for their insulating or dielectric properties mainly consisting of organic substances liquids, e.g. oils

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  • Oil, Petroleum & Natural Gas (AREA)
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  • Spectroscopy & Molecular Physics (AREA)
  • Vaporization, Distillation, Condensation, Sublimation, And Cold Traps (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
  • Extraction Or Liquid Replacement (AREA)
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for extracting, separating and recovering PCB in order to treating low concentration PCB-containing insulation oil with safety and at a low cost, and to provide an apparatus therefor. <P>SOLUTION: In separating and recovering PCB from the low concentration PCB-containing insulation oil, the method comprises (1) mixing the PCB-containing insulation oil with an aprotic organic polar solvent and separating the insulation oil and the solution of the aprotic organic polar solvent of PCB, (2) adding water and a hydrocarbon solvent to the solution of the aprotic organic polar solvent of PCB to mix and separating the same to water, the solution of the aprotic organic polar solvent and the solution of the hydrocarbon solvent of PCB, and then (3) recovering the hydrocarbon solvent from the solution of the hydrocarbon solvent of PCB and recovering and separating PCB. Also the apparatus used for the method is obtained. <P>COPYRIGHT: (C)2008,JPO&INPIT

Description

本発明は、低濃度のPCBを含有する絶縁油から、PCBを分離・回収する方法と、それに使用する装置に関する。 The present invention relates to a method for separating / recovering PCB from insulating oil containing low-concentration PCB, and an apparatus used therefor.

ポリ塩化ビフェニル類(PCB)やダイオキシン類等のハロゲン化有機物は、一般的に人体に有害で、環境を汚染する物が多い。特に、PCBは、難分解性で長期にわたり残存しその影響が続くため、環境汚染物質として大きな社会問題となっている。更に、PCBは化学的に非常に安定な物質であるために、廃棄等に際して無害化の処理が困難であるという問題もある。 Halogenated organic substances such as polychlorinated biphenyls (PCBs) and dioxins are generally harmful to humans and often contaminate the environment. In particular, PCB is a serious social problem as an environmental pollutant because it is persistent and remains persistent for a long time. Further, since PCB is a chemically very stable substance, there is a problem that it is difficult to make it harmless upon disposal.

現在、PCBを含む廃油等の処理について規制する、廃棄物処理法で認められている方法としては、高温熱分解法、脱塩素化分解法、水熱酸化分解法、還元熱化学分解法、光分解法、プラズマ分解法が知られている。これらの中では、格別に大型・特殊な分解装置が必要ではない点、あるいは有害な副生物が生じない点、副生物の再利用が可能となるなどの点で脱塩素化分解法が好ましい。 Currently, the methods recognized as waste treatment methods that regulate the treatment of waste oils including PCBs include the high temperature pyrolysis method, dechlorination decomposition method, hydrothermal oxidation decomposition method, reductive thermochemical decomposition method, light A decomposition method and a plasma decomposition method are known. Among these, the dechlorination decomposition method is preferable in that a particularly large and special decomposition apparatus is not required, no harmful by-products are generated, and by-products can be reused.

そして一般的に脱ハロゲン化分解法においては、金属ナトリウムや有機アルカリ金属あるいは触媒等をハロゲン化有機物と混合し化学反応させることにより、ハロゲン化有機物中のハロゲンを水素等に置換することが行われる。しかしながら、脱ハロゲン化分解に用いる金属や触媒は高価である上、無水の有機溶媒中で反応を行わなければならない等の欠点や問題点があった(特許文献1〜3参照)。
特開2002−756号公報 特開2001−269673号公報 特開平8−66494号公報
In general, in the dehalogenation decomposition method, metal halogen, organic alkali metal, catalyst, or the like is mixed with a halogenated organic substance and chemically reacted to replace the halogen in the halogenated organic substance with hydrogen or the like. . However, metals and catalysts used for dehalogenation decomposition are expensive and have drawbacks and problems such as the need to carry out the reaction in an anhydrous organic solvent (see Patent Documents 1 to 3).
JP 2002-756 A JP 2001-269673 A JP-A-8-66494

比較的単純な操作・手段でPCB等を無害化する方法として、PCB等のアルコール溶液に金属カルシウムを添加混合し、還元・脱ハロゲン化を行う方法も提案されている(特許文献4参照)。しかし、この方法も有機溶媒を用いなければならないという問題がある。
特開2002−265391号公報
As a method for detoxifying PCB or the like by a relatively simple operation / means, a method of reducing and dehalogenating by adding metallic calcium to an alcohol solution such as PCB and mixing it has also been proposed (see Patent Document 4). However, this method also has a problem that an organic solvent must be used.
JP 2002-265391 A

また、PCBと水又はアセトニトリル等の溶媒を混合し、PCBを電気分解により処理するという方法も提案されている。この方法は比較的簡単にPCB等を無害化できるので優れた方法ではあるが、ただ通常の方法・装置で電気分解を行ったのでは、必ずしも脱ハロゲン化が完全には進行しない、という問題があった(特許文献5参照)。
特開2002−345991号公報
There has also been proposed a method in which PCB is mixed with a solvent such as water or acetonitrile and the PCB is treated by electrolysis. This method is excellent because it can detoxify PCBs and the like relatively easily. However, there is a problem that dehalogenation does not always proceed completely if electrolysis is performed using a normal method or apparatus. (See Patent Document 5).
Japanese Patent Laid-Open No. 2002-349591

本発明者は、ハロゲン化有機物又はその含有液を電気分解し脱ハロゲン化を行うに際し、陽極と陰極が隔てられた隔膜電解槽を用いると共に、超音波発生手段を用いてハロゲン化有機物含有液をエマルジョン化し、同時に常温常圧下でありながら1000気圧、5000℃の真空状態を作るといわれるキャビテーション効果を利用し、且つ攪拌手段による液の攪拌をしながら、電気分解を行うことを特徴とするハロゲン化有機物の脱ハロゲン化方法を提案した(特許文献6参照)。かかる方法によれば、電気分解によって完全にかつ十分にハロゲン化有機物を脱ハロゲン化し、無害化物質として回収・除去できた。
国際公開特許WO2005/92448号公報
The present inventor used a diaphragm electrolytic cell in which an anode and a cathode are separated when electrolyzing a halogenated organic substance or a liquid containing the same to perform dehalogenation, and using the ultrasonic wave generating means to remove the halogenated organic substance-containing liquid. Halogenation characterized in that it is emulsified and electrolysis is carried out while utilizing the cavitation effect that is said to create a vacuum state of 1000 atm and 5000 ° C. at normal temperature and pressure, and stirring the liquid by a stirring means. A method for dehalogenating organic substances has been proposed (see Patent Document 6). According to this method, the halogenated organic substance was completely and fully dehalogenated by electrolysis, and recovered and removed as a detoxifying substance.
International Patent Publication No. WO2005 / 92448

ところで、PCBの製造禁止以前に生産されたコンデンサーやトランスは、絶縁油としてPCBが使用されており、PCBの含有量によって高濃度PCBと低濃度PCBに分けられ、コンデンサーの絶縁油と大型トランスの絶縁油は高濃度PCBとされている。コンデンサーは他の油はなくPCBのみが使用され、大型コンデンサーでは6割のPCBと4割のトリクロロベンゼンが使用されている。一方、柱上トランス等の小型機器のトランス油では、大量の鉱油の中に数十ppm程度のPCBが使用されており、低濃度PCBと呼ばれている。 By the way, the capacitors and transformers produced before the PCB manufacturing ban uses PCB as insulating oil, and is divided into high-concentration PCB and low-concentration PCB depending on the PCB content. The insulating oil is a high concentration PCB. The condenser uses only PCB without any other oil, and 60% PCB and 40% trichlorobenzene are used for large condensers. On the other hand, in transformer oil for small equipment such as a pole transformer, PCB of about several tens of ppm is used in a large amount of mineral oil, which is called low-concentration PCB.

現在、高濃度PCBを処理する技術は多く開発されており、高濃度PCBの処理も事業として開始されている。しかし、低濃度PCBを高濃度PCBと同様に処理した場合は、処理コストが高くなり、国の施策としても高濃度PCBの処理と同様な方法では処理しない方針が出されている。従って、現在、低濃度PCBを安く処理する方法の開発が望まれており、本発明者が提案した前記電気分解によるハロゲン化有機物の脱ハロゲン化は非常に期待の持てる方法である。しかしながら、対象が大量の鉱油と低濃度PCBとの混合物の場合には、前記電気分解による方法は好適に応用できないという問題があった。 Currently, many technologies for processing high-concentration PCBs have been developed, and processing of high-concentration PCBs has been started as a business. However, when low-concentration PCBs are processed in the same manner as high-concentration PCBs, the processing costs are high, and there is a policy that the national policy is not to treat them in the same way as high-concentration PCB processing. Therefore, at present, development of a method for treating low-concentration PCB at low cost is desired, and dehalogenation of halogenated organic substances by electrolysis proposed by the present inventor is a very promising method. However, when the target is a mixture of a large amount of mineral oil and low-concentration PCB, there is a problem that the method by electrolysis cannot be applied suitably.

本発明の課題は、安全且つ低コストで、比較的低濃度のPCBを含有する絶縁油を処理するために、PCBの抽出・分離・回収方法を提供することにある。特に、本発明者が先に提案した超音波電気分解処理装置によるPCBの処理の前処理として、例えば、トランス油等の絶縁油からPCBを抽出・分離・回収する方法を提供することにある。 An object of the present invention is to provide a PCB extraction / separation / recovery method for processing insulating oil containing PCB having a relatively low concentration at a safe and low cost. In particular, the present invention provides a method for extracting, separating and recovering PCB from insulating oil such as transformer oil as pre-processing of PCB processing by the ultrasonic electrolysis apparatus previously proposed by the present inventor.

本発明の請求項1に記載の発明は、比較的低濃度、即ち、1000ppm以下のPCBを含有する絶縁油からPCBを分離・回収するに際し、(1)PCBを含有する絶縁油と非プロトン性有機極性溶媒を混合し、絶縁油と、PCBの非プロトン性有機極性溶媒溶液とを分離し、(2)該PCBの非プロトン性有機極性溶媒溶液に水と炭化水素溶媒を添加混合し、水と非プロトン性有機極性溶媒の混合液とPCBの炭化水素溶媒溶液に分離し、次いで(3)該PCBの炭化水素溶媒溶液からの炭化水素溶媒を回収すると共にPCBを分離・回収する方法である。 According to the first aspect of the present invention, when separating and recovering PCB from insulating oil containing PCB having a relatively low concentration, that is, 1000 ppm or less, (1) insulating oil containing PCB and aprotic The organic polar solvent is mixed to separate the insulating oil from the PCB aprotic organic polar solvent solution. (2) Water and a hydrocarbon solvent are added to and mixed with the PCB aprotic organic polar solvent solution. And a mixture of aprotic organic polar solvent and a hydrocarbon solvent solution of PCB, and then (3) a method of recovering the hydrocarbon solvent from the hydrocarbon solvent solution of PCB and separating and recovering PCB. .

請求項2記載の発明は、1000ppm以下のPCBを含有する絶縁油からPCBを分離・回収するに際し、(1)PCBを含有する絶縁油と非プロトン性有機極性溶媒と炭化水素溶媒を混合し、絶縁油と炭化水素溶媒の混合液と、PCBの非プロトン性有機極性溶媒溶液とを分離し、(2)該PCBの非プロトン性有機極性溶媒溶液に水と炭化水素溶媒を添加混合し、水と非プロトン性有機極性溶媒の混合液とPCBの炭化水素溶媒溶液に分離し、次いで(3)該PCBの炭化水素溶媒溶液から炭化水素溶媒を回収すると共にPCBを分離・回収する方法である。 In the invention according to claim 2, when separating and collecting PCB from insulating oil containing PCB of 1000 ppm or less, (1) mixing insulating oil containing PCB, aprotic organic polar solvent and hydrocarbon solvent, A mixed liquid of insulating oil and hydrocarbon solvent and an aprotic organic polar solvent solution of PCB are separated. (2) Water and a hydrocarbon solvent are added to and mixed with the aprotic organic polar solvent solution of PCB. And a mixture of aprotic organic polar solvent and a hydrocarbon solvent solution of PCB, and then (3) a method of recovering the hydrocarbon solvent from the hydrocarbon solvent solution of PCB and separating and recovering PCB.

そして、請求項4記載の発明は、PCBを含有する絶縁油、非プロトン性有機極性溶媒、水、炭化水素溶媒を混合し攪拌するための混合攪拌装置と、共にこれに連結された、PCBと炭化水素溶媒を蒸留により分離するため蒸留装置Aと、水と非プロトン性有機極性溶媒を蒸留により分離するため蒸留装置Bとからなり、請求項1又は2のPCBを分離・回収する方法において用いられる装置である。 The invention described in claim 4 includes a mixing stirrer for mixing and stirring an insulating oil containing PCB, an aprotic organic polar solvent, water, and a hydrocarbon solvent, and a PCB connected to the mixing stirrer. A distillation apparatus A for separating a hydrocarbon solvent by distillation and a distillation apparatus B for separating water and an aprotic organic polar solvent by distillation, which are used in the method for separating and recovering PCBs according to claim 1 or 2. Device.

本発明の方法はいずれも、特に、本発明者が先に提案した超音波電気分解処理装置によるPCBの処理方法の前処理方法として適している。本発明の方法によると、トランス油等の絶縁油からPCBを効率良く抽出・分離・回収することができ、この方法により得られたPCBを用いることによって、前記超音波電気分解処理装置によってトランス等の低濃度PCBを処理する際に、他の油も一緒に処理する必要がなくなり、大幅に処理効率が上がり処理コストも下がる。また、本発明の装置は、かかる方法において効果的に用いられる装置を提供する。 Any of the methods of the present invention is particularly suitable as a pretreatment method for a PCB processing method by the ultrasonic electrolysis apparatus previously proposed by the present inventor. According to the method of the present invention, PCB can be efficiently extracted / separated / recovered from insulating oil such as transformer oil. By using the PCB obtained by this method, a transformer or the like can be obtained by the ultrasonic electrolysis apparatus. When processing a low-concentration PCB, it is not necessary to process other oils together, which significantly increases the processing efficiency and the processing cost. The apparatus of the present invention also provides an apparatus that can be used effectively in such a method.

本発明の対象は、PCBを低濃度、即ち、1000ppm以下、好ましくは100ppm以下の濃度で含有する絶縁油である。絶縁油とは、トランスやコンデンサー等の電気機器に広く使用されている、機器の絶縁と冷却を目的とした鉱油、合成油、あるいはそれらの混合油等を主成分とした油である。 The subject of the present invention is an insulating oil containing PCB at a low concentration, i.e. 1000 ppm or less, preferably 100 ppm or less. Insulating oil is an oil mainly used in electrical equipment such as transformers and condensers, which is mainly composed of mineral oil, synthetic oil, or mixed oil for the purpose of insulation and cooling of equipment.

そして、本発明において、非プロトン性有機極性溶媒とは、ジメチルスルホキシド、スルホラン、N−メチル−2−ピロリドン、ジメチルホルムアミド、ジメチルアセトアミド、アセトリトリル、N−メチルアセトアミド、ヘキサメチルホスホリックトリアミド、アセトン、ニトロベンゼン、ピリジン、プロピレンカーボネート等の非プロトン性溶媒である。これらの中では、ジメチルスルホキシド、スルホラン、N−メチル−2−ピロリドン、ジメチルホルムアミド、ジメチルアセトアミド、アセトリトリル又はこれらの混合溶媒が好ましく、特にジメチルスルホキシドが好ましい。 In the present invention, the aprotic organic polar solvent is dimethyl sulfoxide, sulfolane, N-methyl-2-pyrrolidone, dimethylformamide, dimethylacetamide, acetolitol, N-methylacetamide, hexamethylphosphoric triamide, acetone, Aprotic solvents such as nitrobenzene, pyridine and propylene carbonate. Among these, dimethyl sulfoxide, sulfolane, N-methyl-2-pyrrolidone, dimethylformamide, dimethylacetamide, acetolitol, or a mixed solvent thereof is preferable, and dimethyl sulfoxide is particularly preferable.

また、炭化水素溶媒としては、炭素数5〜18の常温で液体のものが適当であり、例えば、ヘキサン、ヘプタン、シクロヘキサンが好ましい。 Moreover, as a hydrocarbon solvent, a liquid thing at normal temperature of C5-C18 is suitable, for example, hexane, heptane, and a cyclohexane are preferable.

本発明のうち請求項1に記載された発明は、先ず、(1)PCBを含有する絶縁油と非プロトン性有機極性溶媒を混合し、絶縁油と、PCBの非プロトン性有機極性溶媒溶液とを分離し、(2)該PCBの非プロトン性有機極性溶媒溶液に水と炭化水素溶媒を添加混合し、水と非プロトン性有機極性溶媒の溶液とPCBの炭化水素溶媒溶液に分離し、次いで(3)該PCBの炭化水素溶媒溶液からの炭化水素溶媒を回収すると共にPCBを分離・回収するものである。以下、各工程を図1のフローチャートを用いて説明する。 The invention described in claim 1 of the present invention is, first, (1) an insulating oil containing PCB and an aprotic organic polar solvent are mixed, and the insulating oil, an aprotic organic polar solvent solution of PCB, (2) Water and a hydrocarbon solvent are added to and mixed with the PCB aprotic organic polar solvent solution, and then separated into a water and aprotic organic polar solvent solution and a PCB hydrocarbon solvent solution; (3) The hydrocarbon solvent is recovered from the hydrocarbon solvent solution of the PCB, and the PCB is separated and recovered. Hereinafter, each process is demonstrated using the flowchart of FIG.

図1には、低濃度のPCBを含有するトランス油(PCB以外は鉱油からなる)を、非プロトン性有機極性溶媒としてDMSOを用い、炭化水素溶媒としてヘキサンを用いて処理する場合の例を示した。先ず、(1)トランス油を1倍から1000倍のDMSOに混合し攪拌する。かかる操作で、鉱油からPCBが分離・抽出されDMSOに溶解し、上層の鉱油と下層のPCB+DMSOの二層に分離する。この段階で、上層の鉱油にPCBが残存していない場合には、鉱油は廃油として処理されるが、PCBが残存している場合には、再び前記(1)に戻しDMSOによる分離・抽出工程を繰り返す。 FIG. 1 shows an example in which a trans-oil containing a low concentration of PCB (made of mineral oil other than PCB) is treated with DMSO as an aprotic organic polar solvent and hexane as a hydrocarbon solvent. It was. First, (1) Trans oil is mixed with 1 to 1000 times DMSO and stirred. By this operation, PCB is separated and extracted from mineral oil, dissolved in DMSO, and separated into two layers of upper layer mineral oil and lower layer PCB + DMSO. At this stage, if PCB does not remain in the upper mineral oil, the mineral oil is processed as waste oil, but if PCB remains, the process returns to (1) above and the separation / extraction step by DMSO again. repeat.

次に、(2)PCB+DMSOの溶液に水を加え攪拌する。この操作で、DMSOは水と混ざり、PCBは分離又は遊離する。更に、分離したPCBと、水とDMSOの混合液に、ヘキサンを入れて混合攪拌する。かかる操作で、分離したPCBはヘキサンに溶解し、PCB+ヘキサンとDMSO+水の二層に分離する。 Next, (2) water is added to the PCB + DMSO solution and stirred. In this operation, DMSO is mixed with water and PCB is separated or released. Further, hexane is added to a mixed solution of the separated PCB, water and DMSO and mixed and stirred. By this operation, the separated PCB is dissolved in hexane and separated into two layers of PCB + hexane and DMSO + water.

次に、(3)上層のPCB+ヘキサン層を分離し、ヘキサンを留去しPCBを分離する。ヘキサンは回収しリサイクルする。一方、下層のDMSO+水層からは、水を留去しDMSOを回収しリサイクルする。そして、分離されたPCBは、別に設置されている超音波電気分解装置にかけて分解処理される。 Next, (3) the upper PCB + hexane layer is separated, and hexane is distilled off to separate the PCB. Hexane is recovered and recycled. On the other hand, from the lower layer DMSO + water layer, water is distilled off and DMSO is recovered and recycled. Then, the separated PCB is decomposed by an ultrasonic electrolyzer installed separately.

図2には、本発明のうち請求項2に記載された発明、即ち、低濃度のPCBを含有するトランス油(PCB以外は鉱油からなる)を、非プロトン性有機極性溶媒としてDMSOを用い、炭化水素溶媒としてヘキサンを用いて処理するもう一つの例を示した。先ず、(1)トランス油を1倍から1000倍のDMSOとヘキサンの混合液に混合し攪拌する。かかる操作によって鉱油とヘキサンからなる上層と、PCBが溶解したDMSOの下層に分離する。この段階で、上層の鉱油とヘキサン層にPCBが残存していない場合には、鉱油とヘキサンは廃油として処理されるが、PCBが残存している場合には、再び前記(1)に戻しDMSOによる分離・抽出工程を繰り返す。次に、(2)PCB+DMSOの溶液に水とヘキサンを加え攪拌する。この操作で、DMSOは水と混ざり、PCBを溶解したヘキサンと分離する。 In FIG. 2, the invention described in claim 2 of the present invention, that is, a transformer oil containing a low concentration of PCB (made of mineral oil other than PCB) is used as DMSO as an aprotic organic polar solvent, Another example was given using hexane as the hydrocarbon solvent. First, (1) Trans oil is mixed with 1 to 1000 times of a mixed solution of DMSO and hexane and stirred. By this operation, it is separated into an upper layer composed of mineral oil and hexane and a lower layer of DMSO in which PCB is dissolved. At this stage, if no PCB remains in the upper mineral oil and hexane layers, the mineral oil and hexane are treated as waste oil, but if PCB remains, return to (1) above again to return to DMSO. Repeat the separation and extraction process. Next, (2) water and hexane are added to the PCB + DMSO solution and stirred. In this operation, DMSO is mixed with water and separated from hexane in which PCB is dissolved.

以後は図1の場合と同様に処理してPCBは分離され、別に設置されている超音波電気分解装置にかけて分解処理される。 Thereafter, the PCB is separated by the same processing as in FIG. 1, and is decomposed by a separate ultrasonic electrolyzer.

前記本発明の方法は図3に示したような装置を用いることによって、効果的に実施することができる。即ち、PCBを含有する絶縁油(トランス油)、非プロトン性有機極性溶媒(DMSO)、水、炭化水素溶媒(ヘキサン)を混合し攪拌するための混合攪拌装置と、共にこれに連結された、PCBと炭化水素溶媒を蒸留により分離するため蒸留装置Aと、水と非プロトン性有機極性溶媒を蒸留により分離するため蒸留装置Bとからなる装置である。 The method of the present invention can be effectively carried out by using an apparatus as shown in FIG. That is, an insulating oil containing PCB (trans oil), an aprotic organic polar solvent (DMSO), water, and a mixing and stirring device for mixing and stirring a hydrocarbon solvent (hexane), both connected to this, It is an apparatus comprising a distillation apparatus A for separating PCB and hydrocarbon solvent by distillation, and a distillation apparatus B for separating water and aprotic organic polar solvent by distillation.

前記混合攪拌装置には、例えば、PCBを含有する絶縁油、非プロトン性有機極性溶媒、水又は炭化水素溶媒のタンクから、それぞれの液体をパイプ等によって導入するための手段を設けることができる。また、蒸留装置A及びBには、分離生成物を分取するための手段や加熱、冷却手段等を適宜設けることができる。混合攪拌装置と蒸留装置A及びBとの連結方法・手段においても特に制限はなく、公知のものを使用することができる。図3に示したように、非プロトン性有機極性溶媒(DMSO)、水、炭化水素溶媒(ヘキサン)は再利用することもできる。 The mixing and stirring device can be provided with means for introducing each liquid through a pipe or the like from a tank of insulating oil containing PCB, aprotic organic polar solvent, water or hydrocarbon solvent, for example. Further, the distillation apparatuses A and B can be appropriately provided with means for separating the separated product, heating and cooling means, and the like. There are no particular restrictions on the method and means for connecting the mixing and stirring apparatus and the distillation apparatuses A and B, and known ones can be used. As shown in FIG. 3, an aprotic organic polar solvent (DMSO), water, and a hydrocarbon solvent (hexane) can be reused.

本発明の方法・装置で分離・回収されたPCBあるいはPCBを含む回収液は、以下のようにして処理することができる。トランス油等の絶縁油からPCBを抽出した後の油は、PCB含有率が0.5ppm以下であり廃油として通常の処理が可能となる。そして、抽出・回収されたPCBは、従来の処理施設に運んで処理することも可能となる。あるいは、全国に散在しているPCBを含む絶縁油のある現場に、本発明の方法を実施するための本発明の装置(抽出機)と、本発明者が既に提案しているPCBの超音波電気分解装置を持ち込んで、現場で容易にPCB処理が出来る。 The PCB separated or collected by the method / apparatus of the present invention or the collected liquid containing PCB can be treated as follows. The oil after extracting PCB from insulating oil such as transformer oil has a PCB content of 0.5 ppm or less, and can be processed normally as waste oil. Then, the extracted / collected PCB can be carried to a conventional processing facility for processing. Alternatively, the apparatus of the present invention (extractor) for carrying out the method of the present invention on the site where the insulating oil containing PCBs scattered throughout the country is present, and the ultrasonic wave of the PCB already proposed by the present inventor PCB can be easily processed on site by bringing in an electrolyzer.

本発明者が既に提案しているPCBの超音波電気分解装置は、PCB等のハロゲン化有機物又はその含有液を電気分解し脱ハロゲン化を行うに際し、陽極と陰極が隔てられた隔膜電解槽を用いると共に、超音波発生手段を用いてハロゲン化有機物含有液をエマルジョン化し、同時に常温常圧下でありながら1000気圧、5000℃の真空状態を作るといわれるキャビテーション効果を利用し、且つ攪拌手段による液の攪拌をしながら、電気分解を行うことを特徴とするPCB等のハロゲン化有機物の脱ハロゲン化方法である。この場合において、ハロゲン化有機物又はその含有液を陰極側に入れ、陰極側で超音波発生手段を用いて超音波を与え、且つ攪拌手段で攪拌しながら、電気分解を行う方法がより効率的である。陰極として水素吸蔵金属又は合金を用いるのが好ましく、また、超音波付与や攪拌は、必ずしも常時行う必要はなく、状況に応じ断続的に行っても良い。 The ultrasonic electrolysis apparatus for PCB already proposed by the present inventor has a diaphragm electrolytic cell in which an anode and a cathode are separated in electrolyzing a halogenated organic substance such as PCB or a liquid containing the same to perform dehalogenation. While using the ultrasonic wave generation means, the halogenated organic substance-containing liquid is emulsified, and at the same time, utilizing the cavitation effect that is said to create a vacuum state of 1000 atm. This is a method for dehalogenating halogenated organic substances such as PCB, wherein electrolysis is performed while stirring. In this case, it is more efficient to put the halogenated organic substance or a liquid containing the same on the cathode side, apply ultrasonic waves on the cathode side using ultrasonic wave generation means, and perform electrolysis while stirring with the stirring means. is there. It is preferable to use a hydrogen storage metal or alloy as the cathode, and the application of ultrasonic waves and stirring are not always required, and may be performed intermittently depending on the situation.

電解条件としては、対象とするハロゲン化有機物又はその含有液の状態によって異なるが、通常、電圧は5〜500V、電流は5〜100Aの範囲で調節される。電気分解は直流電源を用いるのが適当であるが、例えば50〜60Hzの交流電源、あるいは例えば1KHzの高周波電源を用いても良い。また、電気分解に際しては、電気伝導度を上げるために、ハロゲン化有機物又はその含有液に、あるいはそれらを含む処理液に、アルカリ金属又はアルカリ土類金属の水酸化物や塩化物等の塩を添加して、電気分解を行うのも好ましい。その際、例えば、水で200V必要な電圧は、十分の一の20V位に下がり、処理液の温度上昇を抑えることが出るので望ましい。添加する量は、処理液1L当たり1〜50g、好ましくは3〜10gである。 As electrolysis conditions, although it changes with the state of the halogenated organic substance made into object or its containing liquid, a voltage is normally adjusted in 5-500V and an electric current in the range of 5-100A. For the electrolysis, it is appropriate to use a DC power source. For example, an AC power source of 50 to 60 Hz or a high frequency power source of 1 KHz may be used. In electrolysis, in order to increase the electrical conductivity, a salt such as a hydroxide or chloride of an alkali metal or alkaline earth metal is added to the halogenated organic substance or a liquid containing the same, or a treatment liquid containing them. Addition and electrolysis are also preferred. At that time, for example, the voltage required for water of 200 V is desirable, because it drops to about one tenth of 20 V, and the temperature rise of the treatment liquid can be suppressed. The amount to be added is 1 to 50 g, preferably 3 to 10 g, per liter of the treatment liquid.

本発明者が既に提案している発明は、電気分解の陰極における還元反応として、ハロゲン化有機物のハロゲンと、水の電気分解により発生する水素との置換反応を起こさせるものである。しかし、陽極において可逆反応が起こる可能性があるので、陰極での生成物を物理的に陽極に接触させないことにより、可逆反応を防止することが望ましい。その方法として陽極室と陰極室を分ける隔膜電解槽が用いられる。隔膜としては、イオン交換膜、有機又は無機の微多孔膜等があり、これらの中から耐食性、機械的強度、気孔径・分布、電気抵抗等を勘案して、適当なものを容易に選択することができる。形状は特に限定されるものではなく、陽極と陰極で発生、存在する物質が電解液に溶解し、それが拡散対流によって混合するのを防げるようなものであれば良い。 The invention already proposed by the present inventor causes a substitution reaction between a halogen of an organic halide and hydrogen generated by electrolysis of water as a reduction reaction at an electrolysis cathode. However, since a reversible reaction may occur at the anode, it is desirable to prevent the reversible reaction by not physically contacting the product at the cathode with the anode. As the method, a diaphragm electrolytic cell that separates the anode chamber and the cathode chamber is used. Examples of diaphragms include ion exchange membranes, organic or inorganic microporous membranes, etc., and appropriate ones can be easily selected in consideration of corrosion resistance, mechanical strength, pore diameter / distribution, electrical resistance, etc. be able to. The shape is not particularly limited as long as it can prevent substances generated and present at the anode and the cathode from being dissolved in the electrolytic solution and mixed by diffusion convection.

PCB等のハロゲン化有機物又はその含有液は、そのまま、あるいは有機溶媒溶液あるいは水性エマルジョンや水との混合液の形(処理液)で電気分解に使用される。例えば、本発明の方法によって、低濃度のPCBを含有する絶縁油から分離・回収されたPCBの場合には、回収PCB又はPCBを高濃度に含む炭化水素溶媒溶液に、適量の水を加えて混合液とするか、又は適当な界面活性剤でエマルジョンとし、得られた液を電気分解に用いれば良い。反応に際しては、もちろん、電気・機械的な攪拌手段により処理液を攪拌しても良い。 A halogenated organic substance such as PCB or a liquid containing the same is used for electrolysis as it is or in the form of an organic solvent solution, an aqueous emulsion, or a mixed solution with water (treatment liquid). For example, in the case of PCB separated and recovered from insulating oil containing low-concentration PCB by the method of the present invention, an appropriate amount of water is added to the recovered PCB or a hydrocarbon solvent solution containing PCB at a high concentration. A mixed solution or an emulsion with an appropriate surfactant may be used, and the obtained solution may be used for electrolysis. In the reaction, of course, the treatment liquid may be stirred by an electric / mechanical stirring means.

電気分解により脱ハロゲン化反応を行うに際して、超音波発生手段、例えば、超音波発生装置を用いて、反応系に超音波を与えると、超音波によって反応液が、キャビテーション効果だけでなく、ハロゲン化有機物あるいはそれと他の液体とがエマルジョン効果により微小なクラスターを形成し、反応がより効率的に進行する。超音波発生手段としては、例えば、公知あるいは市販の超音波発生装置を用いることができる。超音波のパワーとしては、処理液1リットル当たり1〜100W程度、好ましくは10〜40Wである。なお、超音波発生手段とは、マイクロ波等のいわゆる超音波以外の、周波数により物体に振動を与える手段でも良い。 When performing a dehalogenation reaction by electrolysis, if an ultrasonic wave is applied to the reaction system using an ultrasonic generator, for example, an ultrasonic generator, the reaction liquid is not only cavitation effect but also halogenated by the ultrasonic wave. Organic matter or other liquid and other liquids form minute clusters by the emulsion effect, and the reaction proceeds more efficiently. As the ultrasonic wave generating means, for example, a known or commercially available ultrasonic wave generating device can be used. The ultrasonic power is about 1 to 100 W, preferably 10 to 40 W per liter of the processing liquid. The ultrasonic wave generation means may be a means for applying vibration to an object with a frequency other than so-called ultrasonic waves such as microwaves.

反応温度は一般には室温で行うのが便利であるが、ハロゲン化有機物又はその含有液が氷結しない最低の温度〜還流温度の範囲で調整することができる。反応時間は、処理量にもよるが、通常、10〜100分の間で調整される。反応雰囲気は格別の配慮は必要ではなく、開放系で常圧であっても良いが、空気の影響を出来るだけ避けるため、窒素等の不活性雰囲気下で反応を行っても良い。 The reaction temperature is generally conveniently carried out at room temperature, but it can be adjusted in the range from the lowest temperature at which the halogenated organic compound or the liquid containing it does not freeze to the reflux temperature. The reaction time depends on the amount of treatment, but is usually adjusted between 10 and 100 minutes. The reaction atmosphere does not require special consideration and may be an open system and normal pressure. However, in order to avoid the influence of air as much as possible, the reaction may be performed in an inert atmosphere such as nitrogen.

電気分解は、ハロゲン化有機物又はその含有液を電気分解し脱ハロゲン化を行うための電解槽であって、前述した隔膜によって隔てられた陽極と陰極、超音波発生手段及び攪拌手段を備えてなる電解槽を用いて行われる。陽極としては、例えば、白金、チタンや炭素が用いられる。陰極としては、例えば、パラジウム、チタン等の金属やその合金が用いられる。超音波発生手段は、処理液を十分にエマルジョン効果により乳化し、キャビテーション効果により脱ハロゲン化を促すものであればどのようなものでも良いが、超音波発生機と接続された超音波発振棒を処理液に挿入するタイプのものが適当である。攪拌手段は、公知あるいは市販の攪拌機を利用すれば良い。処理槽としては、特別な槽を用いる必要はなく、実用的にも、例えば、ステンレスやガラス製、あるいは塩化ビニール製の一般的な容器・装置を用い、電気分解を行うことができる。 Electrolysis is an electrolytic cell for electrolyzing and dehalogenating a halogenated organic substance or a liquid containing the same, and comprises an anode and a cathode separated by the above-mentioned diaphragm, ultrasonic generating means, and stirring means. This is done using an electrolytic cell. For example, platinum, titanium, or carbon is used as the anode. As the cathode, for example, a metal such as palladium or titanium or an alloy thereof is used. Any ultrasonic generator may be used as long as the treatment liquid is sufficiently emulsified by the emulsion effect and dehalogenation is promoted by the cavitation effect, but an ultrasonic oscillating rod connected to the ultrasonic generator is used. A type that is inserted into the processing solution is suitable. A known or commercially available stirrer may be used as the stirring means. As a processing tank, it is not necessary to use a special tank, and practically, for example, electrolysis can be performed using a general container / device made of stainless steel, glass, or vinyl chloride.

陰極として水素吸蔵金属又は合金を使用するのが好ましく、パラジウム等の水素吸蔵金属あるいはチタン−鉄合金等の水素吸蔵合金を使用すると、電気分解で発生した水素が陰極に吸蔵され、その後この排出される水素が効率的にハロゲンと置換し脱ハロゲン化反応に寄与し、還元反応が効率的に行われるので好ましい。そして、この場合にも、電気分解に際し隔膜電解槽を用いる方法が好ましく、更に、超音波発生手段と攪拌手段を用いて、処理液に超音波を与え且つ攪拌しながら電気分解を行う方法を採用すると、より好ましい結果が得られる。 It is preferable to use a hydrogen storage metal or alloy as the cathode. When a hydrogen storage metal such as palladium or a hydrogen storage alloy such as a titanium-iron alloy is used, hydrogen generated by electrolysis is stored in the cathode and then discharged. Hydrogen is preferable because it efficiently substitutes for halogen and contributes to the dehalogenation reaction, and the reduction reaction is carried out efficiently. In this case as well, a method using a diaphragm electrolytic cell is preferable for the electrolysis, and furthermore, a method of applying ultrasonic waves to the treatment liquid and performing electrolysis while stirring using ultrasonic generation means and stirring means is adopted. Then, a more preferable result is obtained.

以下、実施例により本発明を詳述するが、実施例において、PCBはGC/MAS方法で測定した。 EXAMPLES Hereinafter, although an Example demonstrates this invention in detail, in the Example, PCB was measured by GC / MAS method.

図2のフローチャートに従って分離・抽出操作を行なった。(1)100ppmのPCBを含有するトランス油(PCB以外は鉱油からなる)50mlに、200mlのDMSOと250mlのヘキサンを添加混合して攪拌した。そして、二層に分離した鉱油とヘキサンからなる上層と、PCBを溶解したDMSO溶液からなる下層とを分離した。上層にPCBが検出されなくなるまで、DMSOを添加・混合・攪拌・溶液分離の操作を繰り返した。PCBが検出されなくなった鉱油とヘキサンは、廃油として別途処理することによって、ヘキサンは再利用することができる。 Separation / extraction operation was performed according to the flowchart of FIG. (1) 200 ml of DMSO and 250 ml of hexane were added to and mixed with 50 ml of trans oil containing 100 ppm of PCB (made of mineral oil except for PCB). And the upper layer which consists of mineral oil and hexane isolate | separated into two layers, and the lower layer which consists of DMSO solution which melt | dissolved PCB were isolate | separated. The operation of adding DMSO, mixing, stirring, and solution separation was repeated until no PCB was detected in the upper layer. Mineral oil and hexane from which PCB is no longer detected can be reused by separately treating them as waste oil.

次に、(2)PCBを溶解したDMSOの溶液250mlに水を250mlとヘキサンを188ml加え混合・攪拌した。この操作で、DMSOは水と混ざり、PCBとヘキサン(PCBのヘキサン溶液)は分離又は遊離したので、両者を分液した。DMSOと水の層にPCBが検出されなくなるまで、ヘキサンの添加・混合・攪拌・溶液分離の操作を繰り返した。DMSOと水の混合液は、図2に示した様に、100〜160℃で水とDMSOを蒸留により分離し、DMSOを再利用に供することができる。 Next, (2) 250 ml of water and 188 ml of hexane were added to 250 ml of DMSO solution in which PCB was dissolved, and mixed and stirred. By this operation, DMSO was mixed with water, and PCB and hexane (PCB hexane solution) were separated or released, and thus both were separated. The operation of hexane addition, mixing, stirring, and solution separation was repeated until no PCB was detected in the DMSO and water layers. As shown in FIG. 2, the mixed solution of DMSO and water can be separated from water and DMSO by distillation at 100 to 160 ° C., and DMSO can be reused.

次に、(3)分離したPCBのヘキサン溶液からヘキサンを留去し、100ppmのPCBを分離した。ヘキサンは回収しリサイクルすることができる。分離されたPCBは、別に設置されている超音波電気分解装置(特許文献6に開示された装置)にかけて下記のごとく分解処理した。 Next, (3) hexane was distilled off from the separated hexane solution of PCB to separate 100 ppm of PCB. Hexane can be recovered and recycled. The separated PCB was subjected to a decomposition treatment as described below through an ultrasonic electrolysis apparatus (apparatus disclosed in Patent Document 6) installed separately.

上記で得られたPCB100ppmを、水酸化ナトリウム100gと水20Lと混合し処理液を調整した。特許文献6に開示された電解槽(処理槽はステンレス製)を用い、この処理液を陰極室に入れ、一方、陽極室には、水酸化ナトリウム100gを含む水溶液20Lを入れ、電源として三相電源の直流を用い、超音波を与えながら、常温常圧で30分間電気分解を行った。電気分解の平均電圧は20V、平均電流は50Aであった。超音波発生手段である電波棒は、直径45mm、長さ35cmの金属棒を用い、これに20KHzの超音波を印加した。超音波のバワーは、平均255Wであった。なお、電気分解における印加電圧は、30分間ほぼ一定であったが、電流と超音波のバワーは、徐々に増加した。陰極室の処理液は、市販のミキサーを用いて1400回/mの攪拌を行った。電気分解後の処理液中のPCBの濃度は、0.5ppm以下であり、電気分解前の100ppmに比べ著しく減少していた。 100 ppm of PCB obtained above was mixed with 100 g of sodium hydroxide and 20 L of water to prepare a treatment solution. Using the electrolytic cell disclosed in Patent Document 6 (the treatment tank is made of stainless steel), this treatment solution is put into the cathode chamber, while the anode chamber is filled with 20 L of an aqueous solution containing 100 g of sodium hydroxide and used as a three-phase power source. The direct current of the power source was used, and electrolysis was performed at normal temperature and pressure for 30 minutes while applying ultrasonic waves. The average voltage of electrolysis was 20V, and the average current was 50A. As a radio wave bar as an ultrasonic wave generating means, a metal bar having a diameter of 45 mm and a length of 35 cm was used, and an ultrasonic wave of 20 KHz was applied thereto. The ultrasonic power was 255 W on average. The applied voltage in electrolysis was almost constant for 30 minutes, but the current and ultrasonic power gradually increased. The treatment liquid in the cathode chamber was stirred 1400 times / m using a commercially available mixer. The concentration of PCB in the treatment liquid after electrolysis was 0.5 ppm or less, which was significantly reduced compared to 100 ppm before electrolysis.

本発明の方法によって、トランス油等の絶縁油からPCBを抽出した後の油は、廃油として通常の処理が可能となり、抽出・回収されたPCBは、従来の処理施設に運んで処理することも可能となる。あるいは、全国に散在しているPCBを含む絶縁油のある現場に、本発明の方法を実施するための装置(抽出機)と、本発明者が既に提案しているPCBの超音波電気分解装置を持ち込んで、現場で容易にPCB処理が出来る。本発明の方法・装置によると、近年問題となっているPCB等を含んだトランスオイルその他のPCB等含有液を、比較的簡単な方法・装置で、従って非常に経済的に処理することができる。しかも操作は常温常圧下で行われるために安全で、水と電気を使用するクリーンな処理で無害化できるので、産業上や環境上その利用価値は非常に大きい。 According to the method of the present invention, oil after extracting PCB from insulating oil such as transformer oil can be processed normally as waste oil, and the extracted / collected PCB can be transported to a conventional processing facility for processing. It becomes possible. Alternatively, an apparatus (extractor) for carrying out the method of the present invention at a site where insulating oil including PCBs scattered throughout the country is present, and an ultrasonic electrolysis apparatus for a PCB already proposed by the present inventor PCB can be easily processed on site. According to the method and apparatus of the present invention, transformer oil and other PCB-containing liquids containing PCB or the like, which has been a problem in recent years, can be treated with a relatively simple method and apparatus, and therefore very economically. . In addition, since the operation is performed at normal temperature and pressure, it is safe and can be rendered harmless by a clean process using water and electricity, so its utility value is very large in industry and environment.

本発明方法のPCBの分離・抽出の流れの一例を示すフローチャートである。It is a flowchart which shows an example of the flow of separation / extraction of PCB of the method of this invention. 本発明方法のPCBの分離・抽出の流れの他の例を示すフローチャートである。It is a flowchart which shows the other example of the isolation | separation / extraction flow of PCB of this invention method. 本発明方法の実施に使用される装置の一例を示す図である。It is a figure which shows an example of the apparatus used for implementation of the method of this invention.

Claims (4)

1000ppm以下のPCBを含有する絶縁油からPCBを分離・回収するに際し、(1)PCBを含有する絶縁油と非プロトン性有機極性溶媒を混合し、絶縁油と、PCBの非プロトン性有機極性溶媒溶液とを分離し、(2)該PCBの非プロトン性有機極性溶媒溶液に水と炭化水素溶媒を添加混合し、水と非プロトン性有機極性溶媒の混合液とPCBの炭化水素溶媒溶液に分離し、次いで(3)該PCBの炭化水素溶媒溶液から炭化水素溶媒を回収すると共にPCBを分離・回収する方法。 When separating and recovering PCB from insulating oil containing PCB of 1000 ppm or less, (1) Insulating oil containing PCB and aprotic organic polar solvent are mixed, and insulating oil and PCB aprotic organic polar solvent (2) Water and a hydrocarbon solvent are added to and mixed with the aprotic organic polar solvent solution of PCB, and the mixture is separated into a mixture of water and aprotic organic polar solvent and a hydrocarbon solvent solution of PCB. Then, (3) a method of recovering a hydrocarbon solvent from the hydrocarbon solvent solution of the PCB and separating and recovering the PCB. 1000ppm以下のPCBを含有する絶縁油からPCBを分離・回収するに際し、(1)PCBを含有する絶縁油と非プロトン性有機極性溶媒と炭化水素溶媒を混合し、絶縁油と炭化水素溶媒の混合液と、PCBの非プロトン性有機極性溶媒溶液とを分離し、(2)該PCBの非プロトン性有機極性溶媒溶液に水と炭化水素溶媒を添加混合し、水と非プロトン性有機極性溶媒の混合液とPCBの炭化水素溶媒溶液に分離し、次いで(3)該PCBの炭化水素溶媒溶液から炭化水素溶媒を回収すると共にPCBを分離・回収する方法。 When separating and recovering PCB from insulating oil containing PCB of 1000ppm or less, (1) Mixing insulating oil containing PCB, aprotic organic polar solvent and hydrocarbon solvent, and mixing insulating oil and hydrocarbon solvent And an aprotic organic polar solvent solution of PCB. (2) Water and a hydrocarbon solvent are added to and mixed with the aprotic organic polar solvent solution of PCB, and water and an aprotic organic polar solvent solution are mixed. Separating the mixture into a hydrocarbon solvent solution of PCB and then (3) recovering the hydrocarbon solvent from the hydrocarbon solvent solution of PCB and separating and recovering PCB. 非プロトン性有機極性溶媒がジメチルスルホキシド、スルホラン、N−メチル−2−ピロリドン、ジメチルホルムアミド、ジメチルアセトアミド、アセトリトリル又はこれらの混合溶媒である請求項1又は2記載のPCBを分離・回収する方法。 The method for separating and recovering PCB according to claim 1 or 2, wherein the aprotic organic polar solvent is dimethyl sulfoxide, sulfolane, N-methyl-2-pyrrolidone, dimethylformamide, dimethylacetamide, acetritryl or a mixed solvent thereof. PCBを含有する絶縁油、非プロトン性有機極性溶媒、水、炭化水素溶媒を混合し攪拌するための混合攪拌装置と、共にこれに連結された、PCBと炭化水素溶媒を蒸留により分離するための蒸留装置Aと、水と非プロトン性有機極性溶媒を蒸留により分離するための蒸留装置Bとからなり、請求項1又は2のPCBを分離・回収する方法において用いられる装置。


An insulating oil containing PCB, an aprotic organic polar solvent, water, a mixing and stirring device for mixing and stirring a hydrocarbon solvent, and a PCB and a hydrocarbon solvent, both connected to this, for separating by distillation An apparatus used in the method for separating and recovering PCBs according to claim 1 or 2, comprising a distillation apparatus A and a distillation apparatus B for separating water and aprotic organic polar solvent by distillation.


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JP7464077B2 (en) 2022-05-30 2024-04-09 栗田工業株式会社 Method and device for recovering oil from oil-containing waste liquid

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KR101021690B1 (en) 2010-05-12 2011-03-22 (주)원창에너지 Method for treatment of wasted insulation oil including polychlorinated biphenyls
JP7464077B2 (en) 2022-05-30 2024-04-09 栗田工業株式会社 Method and device for recovering oil from oil-containing waste liquid

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