JP2003300050A - Method for removing polychlorinated aromatic compound from pyrolysis product contaminated with polychlorinated aromatic compound - Google Patents

Method for removing polychlorinated aromatic compound from pyrolysis product contaminated with polychlorinated aromatic compound

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Publication number
JP2003300050A
JP2003300050A JP2002105416A JP2002105416A JP2003300050A JP 2003300050 A JP2003300050 A JP 2003300050A JP 2002105416 A JP2002105416 A JP 2002105416A JP 2002105416 A JP2002105416 A JP 2002105416A JP 2003300050 A JP2003300050 A JP 2003300050A
Authority
JP
Japan
Prior art keywords
aromatic compound
polychlorinated aromatic
polychlorinated
extraction
solvent
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.)
Pending
Application number
JP2002105416A
Other languages
Japanese (ja)
Inventor
Masayuki Ono
正之 大野
Naoshi Kaneda
尚士 金田
Masaaki Hosomi
正明 細見
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.)
Kansai Tech Corp
Original Assignee
Kansai Tech Corp
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 Kansai Tech Corp filed Critical Kansai Tech Corp
Priority to JP2002105416A priority Critical patent/JP2003300050A/en
Publication of JP2003300050A publication Critical patent/JP2003300050A/en
Pending legal-status Critical Current

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  • Processing Of Solid Wastes (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for removing polychlorinated aromatic compound from pyrolysis by-products contaminated with polychlorinated aromatic compound when a material contaminated with polychlorinated aromatic compound is treated with a vacuum heating separating apparatus. <P>SOLUTION: When the polychlorinated aromatic compound is separated from the material contaminated with polychlorinated aromatic compound with the vacuum heating separating apparatus, the pyrolysis by-products contaminated with the polychlorinated aromatic compound are extracted by a hydrocarbon solvent to remove the polychlorinated aromatic compound from the pyrolysis products. <P>COPYRIGHT: (C)2004,JPO

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、環境汚染物質であ
る多塩素化芳香族化合物、たとえば多塩素化ビフェニル
を含有する多塩素化ビフェニル汚染物からの多塩素化ビ
フェニルの除去方法及び分解処理方法に関するものであ
る。
TECHNICAL FIELD The present invention relates to a method for removing polychlorinated biphenyl from a polychlorinated biphenyl pollutant containing a polychlorinated aromatic compound which is an environmental pollutant, for example, polychlorinated biphenyl, and a decomposition treatment method. It is about.

【0002】[0002]

【従来の技術】現在、多塩素化ビフェニル汚染物から多
塩素化ビフェニルを除去する方法として法律上認められ
ている方法としては、溶剤による洗浄方法及び真空加熱
分離設備による分離方法がある。真空加熱分離設備によ
り多塩素化ビフェニルに汚染された紙、木くず、等を分
離する場合、分離回収した多塩素化芳香族化合物ととも
に、紙、木くず等の熱分解生成物が発生する。この熱分
解生成物には常温で液状の一般に木酢液といわれるもの
と、常温で樹脂状の一般に木タールといわれるものがあ
る。これらの熱分解生成物は高濃度の多塩素化ビフェニ
ルに汚染された状態にある。回収した液状多塩素化ビフ
ェニルはすでに公知の技術、たとえば、アルカリ金属タ
ーシャリーブトキシドを用いた分解処理方法(特開平8
−10352号)、パラジウムカーボン触媒の存在下で
水素化脱塩素反応による分解処理方法(特開平9−19
4401号)等で無害化処理が可能である。一方、多塩
素化ビフェニルに汚染された熱分解生成物は、有機酸、
フルフラール、アルコール類などからなる複雑な組成の
親水性液体であり、このままでは上記の公知の技術での
無害化処理は困難である。
2. Description of the Related Art Currently, as methods legally recognized for removing polychlorinated biphenyls from polychlorinated biphenyl contaminants, there are a washing method using a solvent and a separation method using a vacuum heating separation facility. When separating paper, wood waste, etc. contaminated with polychlorinated biphenyls by a vacuum heating separation facility, thermal decomposition products such as paper, wood waste, etc. are generated together with the separated and recovered polychlorinated aromatic compounds. The thermal decomposition products include those generally called wood vinegar which are liquid at room temperature and those generally called wood tar which are resinous at room temperature. These thermal decomposition products are contaminated with high concentrations of polychlorinated biphenyls. The recovered liquid polychlorinated biphenyls are already known in the art, for example, a decomposition treatment method using an alkali metal tertiary butoxide (Japanese Patent Laid-Open No. H8 (1998) -8163).
No. -10352), a decomposition treatment method by hydrodechlorination in the presence of a palladium carbon catalyst (JP-A-9-19).
No. 4401) and the like can be detoxified. On the other hand, the thermal decomposition products contaminated with polychlorinated biphenyl are organic acid,
It is a hydrophilic liquid having a complicated composition composed of furfural, alcohols and the like, and if it is left as it is, it is difficult to make it harmless by the known technique.

【0003】[0003]

【発明が解決しようとする課題】このような状況下、多
塩素化ビフェニルの処理を推進するためには、真空加熱
分離設備から発生する多塩素化ビフェニルに汚染された
熱分解生成物中に含まれる多塩素化ビフェニルを最終的
に無害なものに処理する必要がある。本発明は、こうし
た多塩素化芳香族化合物で汚染された熱分解生成物から
多塩素化芳香族化合物を除去する方法を提供することを
目的とするものである。
Under such circumstances, in order to promote the treatment of polychlorinated biphenyls, the pyrolysis products contaminated with polychlorinated biphenyls generated from a vacuum heating separation equipment contain the same. The polychlorinated biphenyls to be treated need to be finally treated to be harmless. It is an object of the present invention to provide a method for removing polychlorinated aromatic compounds from thermal decomposition products contaminated with such polychlorinated aromatic compounds.

【0004】[0004]

【課題を解決するための手段】本発明者らは、鋭意検討
した結果、炭化水素系溶剤により真空加熱分離設備から
発生する熱分解生成物(この熱分解生成物について本明
細書中においては以下単に熱分解生成物ともいう)から
多塩素化芳香族化合物を効果的に除去する方法を見出す
とともに、熱分解生成物から除去・回収した多塩素化芳
香族化合物については公知の無害化処理技術を適用して
無害化が可能となることを見出し、本発明に至った。
Means for Solving the Problems As a result of intensive studies, the inventors of the present invention have found that a thermal decomposition product generated from a vacuum heating separation facility by a hydrocarbon solvent (this thermal decomposition product is referred to as We also found a method to effectively remove polychlorinated aromatic compounds from the thermal decomposition products), and to use known detoxification treatment technology for polychlorinated aromatic compounds removed / recovered from the pyrolysis products. The inventors have found that it can be rendered harmless by applying it, and have reached the present invention.

【0005】すなわち、本発明は、 (1)多塩素化芳香族化合物汚染物から真空加熱分離装
置で多塩素化芳香族化合物を分離する際に、副生する多
塩素化芳香族化合物に汚染された熱分解生成物を炭化水
素系溶剤で抽出することにより、熱分解生成物から多塩
素化芳香族化合物を除去する方法。 (2)流動性を向上するために炭化水素系溶剤に不溶性
の極性溶剤を加える前記(1)記載の多塩素化芳香族化
合物を除去する方法。 (3)抽出を40℃〜100℃の温度範囲で行う前記
(1)記載の多塩素化芳香族化合物を除去する方法。 (4)多塩素化芳香族化合物汚染物が、多塩素化芳香族
化合物を含む鉱油系電気絶縁油が充填されていた変圧器
あるいはその解体物、多塩素化芳香族化合物が充填され
たコンデンサ及び変圧器あるいはその解体物である前記
(1)記載の多塩素化芳香族化合物を除去する方法。 (5)前記(1)記載の多塩素化芳香族化合物を除去す
る方法において、更に抽出溶剤中に移行した多塩素化芳
香族化合物を脱塩素化処理することを特徴とする多塩素
化芳香族化合物を除去する方法。 (6)抽出溶剤中の多塩素化芳香族化合物の脱塩素化処
理が水素化脱塩素化反応であることを特徴とする前記
(5)記載の多塩素化芳香族化合物を除去する方法。 (7)抽出溶剤中の多塩素化芳香族化合物の脱塩素化処
理が金属アルコラートによる脱塩素化反応であることを
特徴とする前記(5)記載の多塩素化芳香族化合物を除
去する方法に関する。
That is, the present invention is as follows: (1) When a polychlorinated aromatic compound is separated from a polychlorinated aromatic compound contaminant by a vacuum heating separator, the polychlorinated aromatic compound is contaminated by-product polychlorinated aromatic compound. A method of removing a polychlorinated aromatic compound from a thermal decomposition product by extracting the thermal decomposition product with a hydrocarbon solvent. (2) The method for removing a polychlorinated aromatic compound according to (1) above, wherein an insoluble polar solvent is added to a hydrocarbon solvent to improve fluidity. (3) The method for removing a polychlorinated aromatic compound according to (1) above, wherein the extraction is performed in a temperature range of 40 ° C to 100 ° C. (4) A transformer in which the pollutant of polychlorinated aromatic compound is filled with a mineral oil-based electrical insulating oil containing the polychlorinated aromatic compound or a dismantled product thereof, a capacitor filled with the polychlorinated aromatic compound, and The method for removing a polychlorinated aromatic compound according to (1), which is a transformer or a dismantled product thereof. (5) In the method for removing a polychlorinated aromatic compound described in (1) above, the polychlorinated aromatic compound transferred to the extraction solvent is further subjected to dechlorination treatment. A method of removing a compound. (6) The method for removing a polychlorinated aromatic compound according to (5) above, wherein the dechlorination treatment of the polychlorinated aromatic compound in the extraction solvent is a hydrodechlorination reaction. (7) A method for removing a polychlorinated aromatic compound according to (5), wherein the dechlorination treatment of the polychlorinated aromatic compound in the extraction solvent is a dechlorination reaction with a metal alcoholate. .

【0006】本発明において熱分解生成物から多塩素化
芳香族化合物を炭化水素系溶剤により抽出する際の好ま
しい温度は、常温〜100℃、好ましくは40〜100
℃である。熱分解生成物に炭化水素系溶剤を加え、この
温度条件下において、攪拌、混合を行い、熱分解生成物
中に含まれる多塩素化芳香族化合物を炭化水素系溶剤に
より抽出する。次いで抽出混合物を静置、分離する。こ
の静置分離により炭化水素系溶剤層と熱分解生成物層に
分離することができる。
In the present invention, the preferred temperature for extracting the polychlorinated aromatic compound from the thermal decomposition product with a hydrocarbon solvent is room temperature to 100 ° C., preferably 40 to 100.
℃. A hydrocarbon solvent is added to the thermal decomposition product, and the mixture is stirred and mixed under this temperature condition, and the polychlorinated aromatic compound contained in the thermal decomposition product is extracted with the hydrocarbon solvent. The extraction mixture is then allowed to stand and separate. By this stationary separation, the hydrocarbon solvent layer and the thermal decomposition product layer can be separated.

【0007】上記の操作により、熱分解生成物中の多塩
素化芳香族化合物は、炭化水素系溶剤層へ移行し、熱分
解生成物から効率的に除去されるので、必要に応じてそ
の操作を繰り返すことにより、例えば、多塩素化芳香族
化合物が多塩素化ビフェニルである場合には、熱分解生
成物中の多塩素化ビフェニル濃度は多塩素化ビフェニル
汚染物の判定基準値以下の値となる。すなわち、本発明
の処理法を行った結果、熱分解生成物はもはや多塩素化
芳香族化合物の汚染物ではなくなるので、これについて
は特別な処分法を要せずに、通常の廃棄物として処分が
可能となる。
By the above operation, the polychlorinated aromatic compound in the thermal decomposition product migrates to the hydrocarbon solvent layer and is efficiently removed from the thermal decomposition product. By repeating, for example, when the polychlorinated aromatic compound is polychlorinated biphenyl, the concentration of polychlorinated biphenyl in the thermal decomposition product should be a value equal to or lower than the judgment reference value of the polychlorinated biphenyl contaminant. Become. That is, as a result of carrying out the treatment method of the present invention, the thermal decomposition products are no longer pollutants of polychlorinated aromatic compounds, so that no special disposal method is required for this, and they are disposed of as ordinary waste. Is possible.

【0008】一方、抽出操作により、多塩素化芳香族化
合物が移行した炭化水素溶剤は、公知の技術での無害化
処理が可能である。例えば、アルカリ金属ターシャリー
ブトキシドを用いた分解処理方法(特開平8−1035
2号)、パラジウムカーボン触媒の存在下での水素化脱
塩素化反応による分解処理方法(特開平9−19440
1号)等を利用して無害化することが可能である。
On the other hand, the hydrocarbon solvent to which the polychlorinated aromatic compound is transferred by the extraction operation can be detoxified by a known technique. For example, a decomposition treatment method using an alkali metal tertiary butoxide (JP-A-8-1035).
No. 2), a decomposition treatment method by a hydrodechlorination reaction in the presence of a palladium carbon catalyst (JP-A-9-19440).
It is possible to make it harmless by using No. 1).

【0009】本発明の対象となる多塩素化芳香族汚染熱
分解生成物とは、多塩素化ビフェニル変圧器、多塩素化
ビフェニルコンデンサ、多塩素化ビフェニル汚染紙く
ず、多塩素化ビフェニル汚染木くずを真空加熱分離設備
で分離処理した際に、副生し、回収される多塩素化ビフ
ェニルに汚染された熱分解生成物等である。この熱分解
生成物には常温で液状の木酢液と樹脂状の木タールがあ
るが、本発明の方法は、いずれの熱分解生成物にも適用
できる。
The polychlorinated aromatic pollutant thermal decomposition products which are objects of the present invention are polychlorinated biphenyl transformers, polychlorinated biphenyl capacitors, polychlorinated biphenyl contaminated paper scraps, and polychlorinated biphenyl contaminated wood scraps in vacuum. These are thermal decomposition products and the like contaminated with polychlorinated biphenyls that are by-produced and recovered when separated by a heating separation facility. The pyrolysis products include wood vinegar liquid and resinous wood tar at room temperature, but the method of the present invention can be applied to any of the pyrolysis products.

【0010】本発明に用いる抽出溶媒の炭化水素系溶剤
は特に限定されず鎖式又は環式等の分子構造のものを広
く用いることができる。本発明では鎖式炭化水素として
直鎖状のものと炭素鎖に枝のある分枝状のものが含まれ
る。炭素数nは溶媒として用い得る範囲のものであれば
よいが、操作上n=5以上であり、上限は加温加圧下で
液状となるものまで広く用いることができる。この中で
n=6(へキサン)以上のものが好ましく、n=10
(デカン)以上のものがより好ましく、n=14(テト
ラデカン)以上のものがさらに好ましい。
The hydrocarbon solvent of the extraction solvent used in the present invention is not particularly limited, and those having a chain or cyclic molecular structure can be widely used. In the present invention, the chain hydrocarbon includes a straight chain type and a branched type having a branched carbon chain. The number of carbon atoms n may be in the range that can be used as a solvent, but is n = 5 or more in the operation, and the upper limit can be widely used such that it becomes a liquid under heating and pressurization. Among these, n = 6 (hexane) or more is preferable, and n = 10
(Decane) or higher is more preferable, and n = 14 (tetradecane) or higher is further preferable.

【0011】環式炭化水素としては1個の環を有する単
環式炭化水素、又はこれらの鎖式炭化水素誘導体、2個
以上の環を有する多環式炭化水素、縮合環式炭化水素又
はこれらの鎖式炭化水素誘導体が含まれる。又、不飽和
炭化水素の水素化物、例えば水素化ナフタレン、水素化
インダセン、水素化フルオレン等も用いることができ
る。
As the cyclic hydrocarbon, a monocyclic hydrocarbon having one ring, or a chain hydrocarbon derivative thereof, a polycyclic hydrocarbon having two or more rings, a condensed ring hydrocarbon or these Chain hydrocarbon derivatives of are included. Further, hydrides of unsaturated hydrocarbons such as hydrogenated naphthalene, hydrogenated indacene, hydrogenated fluorene and the like can also be used.

【0012】抽出溶媒として用いる炭化水素の量は特に
制限されるものではないが、熱分解生成物中の多塩素化
芳香族化合物濃度に応じて、適切な量及び抽出回数を選
定することが好ましい。又、多段向流抽出操作を行うこ
とで抽出溶媒の使用量を低減させると共に、熱分解生成
物中の残存多塩素化芳香物化合物を低減させることもで
きる。
The amount of hydrocarbon used as the extraction solvent is not particularly limited, but it is preferable to select an appropriate amount and the number of extractions according to the concentration of polychlorinated aromatic compound in the thermal decomposition product. . Further, by performing a multi-stage countercurrent extraction operation, it is possible to reduce the amount of the extraction solvent used and also reduce the residual polychlorinated aromatic compound in the thermal decomposition product.

【0013】抽出対象物が樹脂状の熱分解生成物の場
合、抽出工程で十分な流動性が得られないため、熱分解
生成物中の多塩素化芳香族化合物が十分に除去されない
場合がある。このような場合には、高粘性の樹脂状熱分
解生成物に対し高い溶解性を示す極性溶媒、例えば、ア
ルコール類を加えることで、抽出操作に必要な流動性を
確保することができる。
When the object to be extracted is a resin-like thermal decomposition product, sufficient fluidity cannot be obtained in the extraction step, so that the polychlorinated aromatic compound in the thermal decomposition product may not be sufficiently removed. . In such a case, by adding a polar solvent having a high solubility to the highly viscous resinous thermal decomposition product, for example, alcohols, the fluidity necessary for the extraction operation can be secured.

【0014】流動性の改良のため加えるアルコール類と
しては、メタノール、エタノール、エチレングリコール
などの樹脂状熱分解性生成物に対し高い溶解性を示し、
かつ、炭化水素系抽出溶媒と分離するアルコール類が用
いられる。
Alcohols added to improve fluidity have high solubility in resinous pyrolyzable products such as methanol, ethanol and ethylene glycol.
In addition, alcohols that are separated from the hydrocarbon extraction solvent are used.

【0015】抽出溶媒の使用量については特に限定され
ない。
The amount of extraction solvent used is not particularly limited.

【0016】流動性を向上させるために加えるアルコー
ル類の使用量については特に限定されるものではなく、
抽出対象物の粘性等の性状に応じて適切な量の使用が好
ましい。
The amount of alcohol used to improve the fluidity is not particularly limited,
It is preferable to use an appropriate amount depending on properties such as viscosity of the extraction target.

【0017】抽出操作温度は常温から100℃で行われ
るが、流動性の向上及び低沸点物の気化を防ぐために
は、60℃付近が好ましい。
The extraction operation temperature is from room temperature to 100 ° C., but in order to improve the fluidity and prevent vaporization of low boiling point substances, it is preferably around 60 ° C.

【0018】抽出操作後は重力分離等の方法で二層に分
離する。熱分解生成物層からは、効果的に多塩素化芳香
族化合物が除去されており、例えば、多塩素化芳香族化
合物が多塩素化ビフェニルである場合には、基準値を超
える多塩素化ビフェニルは存在しないので、通常の廃油
または廃酸として処分することが可能となる。
After the extraction operation, it is separated into two layers by a method such as gravity separation. The polychlorinated aromatic compound is effectively removed from the thermal decomposition product layer. For example, when the polychlorinated aromatic compound is polychlorinated biphenyl, the polychlorinated biphenyl exceeding the standard value is used. Since it does not exist, it can be disposed of as ordinary waste oil or waste acid.

【0019】抽出操作後の分離した多塩素化芳香族化合
物を含む抽出溶剤は公知の多塩素化芳香族化合物分解技
術、例えば、アルカリ金属・ターシャリー・ブトキシド
を用いた分解処理方法(特開平8−10352号)、パ
ラジウムカーボン触媒の存在下にて水素化脱塩素反応に
よる分解処理方法(特開平9−194401)で脱塩素
化処理が可能である。
The extraction solvent containing the separated polychlorinated aromatic compound after the extraction operation is a known polychlorinated aromatic compound decomposition technique, for example, a decomposition treatment method using an alkali metal / tertiary / butoxide (Japanese Patent Laid-Open No. H8 (1998) -8163). No. -10352), a dechlorination treatment can be performed by a decomposition treatment method by hydrodechlorination reaction in the presence of a palladium carbon catalyst (JP-A-9-194401).

【0020】[0020]

【実施例】以下に、本発明を実施例で説明するが、実施
例は本発明の範囲を限定するものではない。
EXAMPLES The present invention will be described below with reference to examples, but the examples do not limit the scope of the present invention.

【0021】実施例1 攪拌装置、還流冷却管、温度計を備えた500mlのス
テンレス製セパラブル四つ口フラスコに多塩素化ビフェ
ニル汚染木タール97g、多塩素化ビフェニル汚染木酢
液102g、炭化水素系抽出溶剤(沸点範囲277〜3
96℃、平均分子量264の流動パラフィン、以下単に
「炭化水素系抽出溶媒」という)159gを加え、抽出
温度80℃にて60分間攪拌を行い抽出操作を行った。
Example 1 97 g of polychlorinated biphenyl-contaminated wood tar, 102 g of polychlorinated biphenyl-contaminated wood vinegar, and hydrocarbon-based extraction were placed in a 500 ml stainless separable four-necked flask equipped with a stirrer, a reflux condenser and a thermometer. Solvent (boiling point range 277-3
159 g of liquid paraffin having an average molecular weight of 264 at 96 ° C., hereinafter simply referred to as “hydrocarbon-based extraction solvent”) was added, and the mixture was stirred at an extraction temperature of 80 ° C. for 60 minutes for extraction operation.

【0022】抽出操作終了後、分液ロートで上層の炭化
水素系抽出溶剤と下層の木タール、木酢液混合溶液を分
離した。
After the extraction operation was completed, the upper layer hydrocarbon extraction solvent and the lower layer wood tar / wood vinegar solution mixed solution were separated with a separating funnel.

【0023】前記、抽出操作後の炭化水素系抽出溶剤の
1gを分析試料として採取し、これにnーヘキサンで1
0mlとし、フロリジル/シリカゲル二層カラムでクリ
ンナップした後,ECD検出器付ガスクロマトグラフで
定量分析を行った。
1 g of the hydrocarbon-based extraction solvent after the extraction operation was sampled as an analytical sample, and 1 g of this was extracted with n-hexane.
After making it 0 ml and cleaning it with a florisil / silica gel two-layer column, quantitative analysis was carried out by a gas chromatograph with an ECD detector.

【0024】分析の結果、炭化水素系抽出溶剤中の多塩
素化ビフェニル濃度は5000mg/kgであった。
As a result of the analysis, the concentration of polychlorinated biphenyl in the hydrocarbon-based extraction solvent was 5000 mg / kg.

【0025】前記、炭化水素系溶剤抽出操作後の木ター
ル、木酢液混合溶液の11gを分析試料として採取し、
これにメタノール100mlを加え、nーヘキサン50
mlで3回抽出を行った。ヘキサン抽出層を無水硫酸ナ
トリウムで脱水した後、KD濃縮及びフロリジルシリカ
ゲル二層カラムでクリンナップした後、ECD検出器付
ガスクロマトグラフで定量分析を行った。
11 g of the mixed solution of wood tar and wood vinegar after the above hydrocarbon solvent extraction operation was taken as an analytical sample,
To this, 100 ml of methanol was added, and n-hexane 50 was added.
Extraction was performed 3 times with ml. The hexane extract layer was dehydrated with anhydrous sodium sulfate, concentrated with KD, cleansed with a florisil silica gel two-layer column, and quantitatively analyzed with a gas chromatograph equipped with an ECD detector.

【0026】分析の結果、抽出操作後の木タール、木酢
液混合溶液中の多塩素化ビフェニル濃度は49mg/kgで
あった。
As a result of the analysis, the concentration of polychlorinated biphenyl in the mixed solution of wood tar and wood vinegar after the extraction operation was 49 mg / kg.

【0027】実施例2 攪拌装置、還流冷却管、温度計を備えた500mlのス
テンレス製セパラブル四つ口フラスコに実施例1で得ら
れた炭化水素系溶剤抽出操作後の木タール、木酢液混合
溶液137g及び炭化水素系抽出溶剤139gを加え、
抽出温度80℃にて60分間攪拌を行い抽出操作を行っ
た。
Example 2 A 500 ml stainless separable four-necked flask equipped with a stirrer, a reflux condenser and a thermometer was placed in a stainless tar separable four-necked flask, and the mixed solution of wood tar and wood vinegar obtained after the extraction operation of the hydrocarbon solvent obtained in Example 1 was carried out. 137 g and a hydrocarbon extraction solvent 139 g are added,
The extraction operation was performed by stirring for 60 minutes at the extraction temperature of 80 ° C.

【0028】抽出操作終了後、分液ロートで上層の炭化
水素系抽出溶剤と下層の木タール、木酢液混合溶液を分
離した。
After completion of the extraction operation, the upper layer hydrocarbon extraction solvent and the lower layer wood tar / wood vinegar solution mixed solution were separated with a separating funnel.

【0029】前記、抽出操作後の炭化水素系抽出溶剤の
1gを分析試料として採取し、これにnーヘキサンで1
0mlとし、フロリジル/シリカゲル二層カラムでクリ
ンナップした後,ECD検出器付ガスクロマトグラフで
定量分析を行った。
1 g of the hydrocarbon-based extraction solvent after the extraction operation was sampled as an analytical sample, and 1 g of this was extracted with n-hexane.
After making it 0 ml and cleaning it with a florisil / silica gel two-layer column, quantitative analysis was carried out by a gas chromatograph with an ECD detector.

【0030】分析の結果、炭化水素系抽出溶剤中の多塩
素化ビフェニル濃度は58mg/kgであった。
As a result of the analysis, the concentration of polychlorinated biphenyl in the hydrocarbon-based extraction solvent was 58 mg / kg.

【0031】前記、抽出操作後の木タール、木酢液、混
合溶液の24gを分析試料として採取し、これにメタノ
ール100mlを加え、nーヘキサン50mlで3回抽
出を行った。ヘキサン抽出層を無水硫酸ナトリウムで脱
水した後、KD濃縮及びフロリジル/シリカゲル二層カ
ラムでクリンナップした後、ECD検出器付ガスクロマ
トグラフで定量分析を行った。
24 g of the above-mentioned wood tar, wood vinegar solution and mixed solution after the extraction operation were sampled as an analytical sample, 100 ml of methanol was added thereto, and extraction was performed 3 times with 50 ml of n-hexane. The hexane extract layer was dehydrated with anhydrous sodium sulfate, concentrated KD, and cleansed with a florisil / silica gel two-layer column, and then quantitatively analyzed by a gas chromatograph with an ECD detector.

【0032】分析の結果、抽出操作後の木タール、木酢
液混合溶液中の多塩素化ビフェニル濃度は0.35mg/
kgであった。
As a result of the analysis, the polychlorinated biphenyl concentration in the mixed solution of wood tar and wood vinegar after the extraction operation was 0.35 mg /
It was kg.

【0033】実施例3 攪拌装置、還流冷却管、温度計を備えた500mlのス
テンレス製セパラブル四つ口フラスコに実施例2で得ら
れた炭化水素系溶剤抽出操作後の木タール、木酢液混合
溶液99g及び炭化水素系抽出溶剤98gを加え、抽出
温度80℃にて60分間攪拌を行い抽出操作を行った。
Example 3 A 500 ml stainless separable four-necked flask equipped with a stirrer, a reflux condenser, and a thermometer was placed in a 500 ml stainless separable four-necked flask. 99 g and 98 g of a hydrocarbon-based extraction solvent were added, and the mixture was stirred at an extraction temperature of 80 ° C. for 60 minutes for extraction operation.

【0034】抽出操作終了後、分液ロートで上層の炭化
水素系抽出溶剤と下層の木タール、木酢液混合溶液を分
離した。
After the extraction operation was completed, the upper layer hydrocarbon extraction solvent and the lower layer wood tar / wood vinegar solution mixed solution were separated with a separating funnel.

【0035】前記、抽出操作後の炭化水素系抽出溶剤の
1gを分析試料として採取し、これにnーヘキサンで1
0mlとし、フロリジル/シリカゲル二層カラムでクリ
ンナップした後,ECD検出器付ガスクロマトグラフで
定量分析を行った。
1 g of the hydrocarbon-based extraction solvent after the above extraction operation was sampled as an analytical sample, and 1 g of this was extracted with n-hexane.
After making it 0 ml and cleaning it with a florisil / silica gel two-layer column, quantitative analysis was carried out by a gas chromatograph with an ECD detector.

【0036】分析の結果、炭化水素系抽出溶剤中の多塩
素化ビフェニル濃度は0.21mg/kgであった。
As a result of the analysis, the concentration of polychlorinated biphenyl in the hydrocarbon-based extraction solvent was 0.21 mg / kg.

【0037】前記、抽出操作後の木タール、木酢液混合
溶液の77gを分析試料として採取し、これにメタノー
ル100mlを加え、nーヘキサン50mlで3回抽出
を行った。ヘキサン抽出層を無水硫酸ナトリウムで脱水
した後、KD濃縮及びフロリジル/シリカゲル二層カラ
ムでクリンナップした後、ECD検出器付ガスクロマト
グラフで定量分析を行った。
77 g of the mixed solution of wood tar and wood vinegar after the above extraction operation was sampled as an analytical sample, 100 ml of methanol was added thereto, and extraction was performed 3 times with 50 ml of n-hexane. The hexane extract layer was dehydrated with anhydrous sodium sulfate, concentrated KD, and cleansed with a florisil / silica gel two-layer column, and then quantitatively analyzed by a gas chromatograph with an ECD detector.

【0038】分析の結果、抽出操作後の木タール、木酢
液混合溶液中の多塩素化ビフェニル濃度は0.097mg
/kgであった。
As a result of the analysis, the polychlorinated biphenyl concentration in the mixed solution of wood tar and wood vinegar after the extraction operation was 0.097 mg.
It was / kg.

【0039】実施例4 攪拌装置、還流冷却管、温度計を備えた500mlのス
テンレス製セパラブル四つ口フラスコに多塩素化ビフェ
ニル汚染木タール71g、多塩素化ビフェニル汚染木酢
液70g、メタノール69g、炭化水素系抽出溶剤74
gを加え、抽出温度60℃にて30分間攪拌を行い抽出
操作を行った。
Example 4 71 g of polychlorinated biphenyl-contaminated wood tar, 70 g of polychlorinated biphenyl-contaminated wood vinegar, 69 g of methanol, carbonized in a 500 ml stainless separable four-necked flask equipped with a stirrer, a reflux condenser and a thermometer. Hydrogen-based extraction solvent 74
g was added, and the mixture was stirred at an extraction temperature of 60 ° C. for 30 minutes for extraction operation.

【0040】抽出操作終了後、分液ロートで上層の炭化
水素系抽出溶剤と下層の木タール、木酢液混合溶液を分
離した。
After the extraction operation was completed, the upper layer hydrocarbon extraction solvent and the lower layer wood tar and wood vinegar solution mixed solution were separated with a separating funnel.

【0041】前記、抽出操作後の炭化水素系抽出溶剤の
1gを分析試料として採取し、これにnーヘキサンで1
0mlとし、フロリジル/シリカゲル二層カラムでクリ
ンナップした後,ECD検出器付ガスクロマトグラフで
定量分析を行った。
1 g of the hydrocarbon-based extraction solvent after the above extraction operation was sampled as an analytical sample, and 1 g of this was extracted with n-hexane.
After making it 0 ml and cleaning it with a florisil / silica gel two-layer column, quantitative analysis was carried out by a gas chromatograph with an ECD detector.

【0042】分析の結果、炭化水素系抽出溶剤中の多塩
素化ビフェニル濃度は14000mg/kgであった。
As a result of the analysis, the concentration of polychlorinated biphenyl in the hydrocarbon-based extraction solvent was 14000 mg / kg.

【0043】前記、抽出操作後の木タール、木酢液、メ
タノール混合溶液の24gを分析試料として採取し、こ
れにメタノール100mlを加え、nーヘキサン50m
lで3回抽出を行った。ヘキサン抽出層を無水硫酸ナト
リウムで脱水した後、KD濃縮及びフロリジル/シリカ
ゲル二層カラムでクリンナップした後、ECD検出器付
ガスクロマトグラフで定量分析を行った。
24 g of the above-mentioned wood tar, wood vinegar solution, and methanol mixed solution after the extraction operation were sampled as an analytical sample, and 100 ml of methanol was added to this to obtain 50 m of n-hexane.
Extraction was performed 3 times with 1. The hexane extract layer was dehydrated with anhydrous sodium sulfate, concentrated KD, and cleansed with a florisil / silica gel two-layer column, and then quantitatively analyzed by a gas chromatograph with an ECD detector.

【0044】分析の結果、抽出操作後の木タール、木酢
液混合溶液中の多塩素化ビフェニル濃度は510mg/kg
であった。
As a result of the analysis, the polychlorinated biphenyl concentration in the mixed solution of wood tar and wood vinegar after extraction was 510 mg / kg.
Met.

【0045】実施例5 攪拌装置、還流冷却管、温度計を備えた500mlのス
テンレス製セパラブル四つ口フラスコに実施例4で得ら
れた前記抽出操作後の木タール、木酢液とメタノール混
合溶液153g及び炭化水素系抽出溶剤153gを加
え、抽出温度60℃にて30分間攪拌を行い抽出操作を
行った。
Example 5 In a 500 ml stainless separable four-necked flask equipped with a stirrer, a reflux condenser and a thermometer, 153 g of a mixed solution of wood tar, wood vinegar and methanol obtained in Example 4 was obtained. And 153 g of a hydrocarbon-based extraction solvent were added, and the mixture was stirred at an extraction temperature of 60 ° C. for 30 minutes for extraction operation.

【0046】抽出操作終了後、分液ロートで上層の炭化
水素系抽出溶剤と下層の木タール、木酢液、メタノール
混合溶液を分離した。
After completion of the extraction operation, the upper layer hydrocarbon extraction solvent and the lower layer wood tar, wood vinegar solution and methanol mixed solution were separated with a separating funnel.

【0047】前記、抽出操作後の炭化水素系抽出溶剤の
1gを分析試料として採取し、これにnーヘキサンで1
0mlとし、フロリジル/シリカゲル二層カラムでクリ
ンナップした後,ECD検出器付ガスクロマトグラフで
定量分析を行った。
1 g of the hydrocarbon-based extraction solvent after the extraction operation was sampled as an analytical sample, and 1 g of this was extracted with n-hexane.
After making it 0 ml and cleaning it with a florisil / silica gel two-layer column, quantitative analysis was carried out by a gas chromatograph with an ECD detector.

【0048】分析の結果、炭化水素系抽出溶剤中の多塩
素化ビフェニル濃度は460mg/kgであった。
As a result of the analysis, the concentration of polychlorinated biphenyl in the hydrocarbon-based extraction solvent was 460 mg / kg.

【0049】前記、抽出操作後の木タール、木酢液、メ
タノール混合溶液の42gを分析試料として採取し、こ
れにメタノール100mlを加え、nーヘキサン50m
lで3回抽出を行った。ヘキサン抽出層を無水硫酸ナト
リウムで脱水した後、KD濃縮及びフロリジル/シリカ
ゲル二層カラムでクリンナップした後、ECD検出器付
ガスクロマトグラフで定量分析を行った。
42 g of the above-mentioned wood tar, wood vinegar solution and methanol mixed solution after the extraction operation were sampled as an analytical sample, to which 100 ml of methanol was added, and 50 m of n-hexane was added.
Extraction was performed 3 times with 1. The hexane extract layer was dehydrated with anhydrous sodium sulfate, concentrated KD, and cleansed with a florisil / silica gel two-layer column, and then quantitatively analyzed by a gas chromatograph with an ECD detector.

【0050】分析の結果、抽出操作後の木タール、木酢
液混合溶液中の多塩素化ビフェニル濃度は13mg/kgで
あった。
As a result of the analysis, the concentration of polychlorinated biphenyl in the mixed solution of wood tar and wood vinegar after the extraction operation was 13 mg / kg.

【0051】実施例6 攪拌装置、還流冷却管、温度計を備えた500mlのス
テンレス製セパラブル四つ口フラスコに実施例5で得ら
れた抽出操作後の木タール、木酢液、メタノール混合溶
液100g及び炭化水素系抽出溶剤107gを加え、抽
出温度60℃にて30分間攪拌を行い抽出操作を行っ
た。
Example 6 In a 500 ml stainless separable four-necked flask equipped with a stirrer, a reflux condenser and a thermometer, 100 g of a mixed solution of wood tar, wood vinegar and methanol after the extraction operation obtained in Example 5 and The extraction operation was performed by adding 107 g of a hydrocarbon-based extraction solvent and stirring the mixture at an extraction temperature of 60 ° C. for 30 minutes.

【0052】抽出操作終了後、分液ロートで上層の炭化
水素系抽出溶剤と下層の木タール、木酢液、メタノール
混合溶液を分離した。
After completion of the extraction operation, the upper layer hydrocarbon extraction solvent and the lower layer wood tar, wood vinegar solution and methanol mixed solution were separated with a separating funnel.

【0053】前記、抽出操作後の炭化水素系抽出溶剤の
1gを分析試料として採取し、これにnーヘキサンで1
0mlとし、フロリジル/シリカゲル二層カラムでクリ
ンナップした後,ECD検出器付ガスクロマトグラフで
定量分析を行った。
1 g of the hydrocarbon-based extraction solvent after the above extraction operation was sampled as an analytical sample, and 1 g of this was extracted with n-hexane.
After making it 0 ml and cleaning it with a florisil / silica gel two-layer column, quantitative analysis was carried out by a gas chromatograph with an ECD detector.

【0054】分析の結果、炭化水素系抽出溶剤中の多塩
素化ビフェニル濃度は7.2mg/kgであった。
As a result of the analysis, the concentration of polychlorinated biphenyl in the hydrocarbon-based extraction solvent was 7.2 mg / kg.

【0055】前記、抽出操作後の木タール、木酢液、メ
タノール混合溶液の87gを分析試料として採取し、こ
れにメタノール100mlを加え、nーヘキサン50m
lで3回抽出を行った。ヘキサン抽出層を無水硫酸ナト
リウムで脱水した後、KD濃縮及びフロリジル/シリカ
ゲル二層カラムでクリンナップした後、ECD検出器付
ガスクロマトグラフで定量分析を行った。
87 g of the above-mentioned wood tar, wood vinegar solution, and methanol mixed solution after the extraction operation were sampled as an analytical sample, and 100 ml of methanol was added to this to add 50 m of n-hexane.
Extraction was performed 3 times with 1. The hexane extract layer was dehydrated with anhydrous sodium sulfate, concentrated KD, and cleansed with a florisil / silica gel two-layer column, and then quantitatively analyzed by a gas chromatograph with an ECD detector.

【0056】分析の結果、抽出操作後の木タール、木酢
液混合溶液中の多塩素化ビフェニル濃度は0.14mg/
kgであった。
As a result of the analysis, the polychlorinated biphenyl concentration in the mixed solution of wood tar and wood vinegar after the extraction operation was 0.14 mg /
It was kg.

【0057】実施例7 攪拌装置、還流冷却管、温度計を備えた500mlのス
テンレス製セパラブル四つ口フラスコに多塩素化ビフェ
ニル汚染木タール105g、多塩素化ビフェニル汚染木
酢液101g、メタノール99g、炭化水素系抽出溶剤
204gを加え、抽出温度60℃にて30分間攪拌を行
い抽出操作を行った。
Example 7 105 g of polychlorinated biphenyl-contaminated wood tar, 101 g of polychlorinated biphenyl-contaminated wood vinegar, 99 g of methanol, carbonized in a 500 ml stainless separable four-necked flask equipped with a stirrer, a reflux condenser and a thermometer. An extraction operation was performed by adding 204 g of a hydrogen-based extraction solvent and stirring at an extraction temperature of 60 ° C. for 30 minutes.

【0058】抽出操作終了後、分液ロートで上層の炭化
水素系抽出溶剤と下層の木タール、木酢液混合溶液を分
離した。
After the extraction operation was completed, the upper layer hydrocarbon extraction solvent and the lower layer wood tar / wood vinegar solution mixed solution were separated with a separating funnel.

【0059】前記、抽出操作後の炭化水素系抽出溶剤の
1gを分析試料として採取し、これにnーヘキサンで1
0mlとし、フロリジル/シリカゲル二層カラムでクリ
ンナップした後,ECD検出器付ガスクロマトグラフで
定量分析を行った。
1 g of the hydrocarbon-based extraction solvent after the above extraction operation was taken as an analytical sample, and 1 g of this was extracted with n-hexane.
After making it 0 ml and cleaning it with a florisil / silica gel two-layer column, quantitative analysis was carried out by a gas chromatograph with an ECD detector.

【0060】分析の結果、炭化水素系抽出溶剤中の多塩
素化ビフェニル濃度は3800mg/kgであった。
As a result of the analysis, the concentration of polychlorinated biphenyl in the hydrocarbon-based extraction solvent was 3800 mg / kg.

【0061】攪拌装置、還流冷却管、温度計を備えた5
00mlのステンレス製セパラブル四つ口フラスコに前
記、抽出操作後の炭化水素系溶剤(多塩素化ビフェニル
濃度3800mg/kg)191及びカリウム・ターシャリ
ー・ブトキシド5.8gを加え、反応温度250℃にて
60分間窒素バブリングしながら攪拌下で多塩素化ビフ
ェニルの脱塩素化反応を行った。
5 equipped with a stirrer, reflux condenser and thermometer
To the 00 ml stainless separable four-necked flask, the hydrocarbon solvent (polychlorinated biphenyl concentration 3800 mg / kg) 191 after extraction and 5.8 g of potassium tertiary butoxide were added, and the reaction temperature was 250 ° C. The dechlorination reaction of polychlorinated biphenyl was carried out with stirring for 60 minutes while bubbling nitrogen.

【0062】反応終了後、次に示す手順で多塩素化ビフ
ェニルの定量分析を行った。
After completion of the reaction, polychlorinated biphenyl was quantitatively analyzed by the following procedure.

【0063】反応混合物を常温にまで冷却した後、水2
00mlを加え分液ロートで振騰静置後、油層と水層に
分離した。
After cooling the reaction mixture to room temperature, water 2
After adding 00 ml and shaking with a separating funnel and leaving it to stand, it was separated into an oil layer and an aqueous layer.

【0064】反応後の炭化水素系抽出溶剤中の多塩素化
ビフェニルを分析するために、油層から1gを採取し、
これにnーヘキサンで10mlとし、フロリジル/シリ
カゲル二層カラムでクリンナップした後,ECD検出器
付ガスクロマトグラフで定量分析を行った。
In order to analyze the polychlorinated biphenyl in the hydrocarbon-based extraction solvent after the reaction, 1 g was taken from the oil layer,
This was adjusted to 10 ml with n-hexane, cleaned with a Florisil / silica gel two-layer column, and quantitatively analyzed with a gas chromatograph equipped with an ECD detector.

【0065】分析の結果、反応後の炭化水素溶剤中の多
塩素化ビフェニル濃度は0.13mg/kgであった。
As a result of analysis, the polychlorinated biphenyl concentration in the hydrocarbon solvent after the reaction was 0.13 mg / kg.

【0066】実施例8 攪拌装置、還流冷却管、温度計、水素導入管を備えた2
000mlのガラス製セパラブル四つ口フラスコに前
記、抽出操作後の多塩素化ビフェニルを含有する炭化水
素系溶剤120g、三塩素化PCB(KCー300)1
20g、反応溶媒(炭化水素類)960g、及びパラジ
ウムカーボン6.0gを加えた後、反応前の初期PCD
濃度測定のため約10mlを採取した。引き続き、反応
温度260℃にて120分間1.2 l/分の流量で水
素ガスを吹き込みながら攪拌下で多塩素化ビフェニルの
脱塩素化反応を行った。
Example 8 2 equipped with a stirrer, reflux condenser, thermometer, hydrogen inlet tube
In a 000 ml glass separable four-necked flask, 120 g of the hydrocarbon solvent containing polychlorinated biphenyl after extraction operation, trichlorinated PCB (KC-300) 1
After adding 20 g, reaction solvent (hydrocarbons) 960 g, and palladium carbon 6.0 g, initial PCD before reaction
About 10 ml was taken for concentration measurement. Subsequently, the dechlorination reaction of polychlorinated biphenyl was carried out at a reaction temperature of 260 ° C. for 120 minutes while stirring while blowing hydrogen gas at a flow rate of 1.2 l / min.

【0067】反応終了後、反応前の反応混合物及び反応
終了後の反応混合物をnーヘキサンで希釈し、ECD検
出器付ガスクロマトグラフで定量分析を行った。
After the reaction was completed, the reaction mixture before the reaction and the reaction mixture after the reaction were diluted with n-hexane and quantitatively analyzed by a gas chromatograph equipped with an ECD detector.

【0068】分析の結果、反応前の反応混合物中のPC
B濃度は87000mg/kgであり、反応終了後の反
応混合物中の多塩素化ビフェニル濃度は0.15mg/
kgであった。
As a result of the analysis, PC in the reaction mixture before the reaction
The B concentration was 87,000 mg / kg, and the polychlorinated biphenyl concentration in the reaction mixture after the reaction was 0.15 mg / kg.
It was kg.

【0069】[0069]

【発明の効果】以上述べた通り、本発明は環境汚染物質
である多塩素化芳香族化合物で汚染された汚染物質から
の同化合物の除去に有効であり、例えば多塩素化芳香族
化合物に汚染された親水性の熱分解生成物から効果的に
多塩素化芳香族化合物を除去することができる。さらに
は、親水性熱分解生成物から多塩素化芳香族化合物を除
去するために使用する炭化水素系抽出溶剤には多塩素化
芳香族化合物が含有されているが、公知の多塩素化芳香
族化合物の分解処理技術で好適に多塩素化芳香族化合物
を脱塩素化処理し、無害化することができる。
INDUSTRIAL APPLICABILITY As described above, the present invention is effective in removing a pollutant polluted with a polychlorinated aromatic compound, which is an environmental pollutant, for example, a polychlorinated aromatic compound is polluted. The polychlorinated aromatic compound can be effectively removed from the generated hydrophilic thermal decomposition product. Furthermore, the hydrocarbon-based extraction solvent used to remove the polychlorinated aromatic compound from the hydrophilic thermal decomposition product contains the polychlorinated aromatic compound. It is possible to detoxify a polychlorinated aromatic compound by subjecting it to a dechlorination treatment by a compound decomposition treatment technique.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) H01F 41/00 B09B 3/00 ZAB (72)発明者 細見 正明 東京都小金井市中町2−24−16 東京農工 大学 工学部 化学システム工学科内 Fターム(参考) 2E191 BA12 BA13 BC05 BD11 4D004 AA22 AB06 AC05 CA22 CA34 CC04 DA03 DA08 4D056 AB17 AC02 AC03 AC06 CA17 CA39 DA01 ─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 7 Identification code FI theme code (reference) H01F 41/00 B09B 3/00 ZAB (72) Inventor Masaaki Hosomi 2-24-16 Nakamachi, Koganei-shi, Tokyo Tokyo 2F191 BA12 BA13 BC05 BD11 4D004 AA22 AB06 AC05 CA22 CA34 CC04 DA03 DA08 4D056 AB17 AC02 AC03 AC06 CA17 CA39 DA01

Claims (7)

【特許請求の範囲】[Claims] 【請求項1】 多塩素化芳香族化合物汚染物から真空加
熱分離装置で多塩素化芳香族化合物を分離する際に、副
生する多塩素化芳香族化合物に汚染された熱分解生成物
を炭化水素系溶剤で抽出することにより、熱分解生成物
から多塩素化芳香族化合物を除去する方法。
1. When a polychlorinated aromatic compound is separated from a polychlorinated aromatic compound contaminant by a vacuum heating separator, a pyrolysis product contaminated by the polychlorinated aromatic compound produced as a by-product is carbonized. A method of removing a polychlorinated aromatic compound from a thermal decomposition product by extracting with a hydrogen-based solvent.
【請求項2】 流動性を向上するために炭化水素系溶剤
に不溶性の極性溶剤を加える請求項1記載の多塩素化芳
香族化合物を除去する方法。
2. The method for removing a polychlorinated aromatic compound according to claim 1, wherein an insoluble polar solvent is added to the hydrocarbon solvent to improve fluidity.
【請求項3】 抽出を40℃〜100℃の温度範囲で行
う請求項1記載の多塩素化芳香族化合物を除去する方
法。
3. The method for removing a polychlorinated aromatic compound according to claim 1, wherein the extraction is performed in a temperature range of 40 ° C. to 100 ° C.
【請求項4】 多塩素化芳香族化合物汚染物が、多塩素
化芳香族化合物を含む鉱油系電気絶縁油が充填されてい
た変圧器あるいはその解体物、多塩素化芳香族化合物が
充填されたコンデンサ及び変圧器あるいはその解体物で
ある請求項1記載の多塩素化芳香族化合物を除去する方
法。
4. A polychlorinated aromatic compound pollutant filled with a mineral oil-based electrical insulating oil containing a polychlorinated aromatic compound or a dismantled product thereof, and a polychlorinated aromatic compound filled The method for removing a polychlorinated aromatic compound according to claim 1, which is a capacitor and a transformer or a dismantled product thereof.
【請求項5】 請求項1記載の多塩素化芳香族化合物を
除去する方法において、更に抽出溶剤中に移行した多塩
素化芳香族化合物を脱塩素化処理することを特徴とする
多塩素化芳香族化合物を除去する方法。
5. The method for removing a polychlorinated aromatic compound according to claim 1, further comprising dechlorinating the polychlorinated aromatic compound transferred to the extraction solvent. Method for removing group compounds.
【請求項6】 抽出溶剤中の多塩素化芳香族化合物の脱
塩素化処理が水素化脱塩素化反応であることを特徴とす
る請求項5記載の多塩素化芳香族化合物を除去する方
法。
6. The method for removing a polychlorinated aromatic compound according to claim 5, wherein the dechlorination treatment of the polychlorinated aromatic compound in the extraction solvent is a hydrodechlorination reaction.
【請求項7】 抽出溶剤中の多塩素化芳香族化合物の脱
塩素化処理が金属アルコラートによる脱塩素化反応であ
ることを特徴とする請求項5記載の多塩素化芳香族化合
物を除去する方法。
7. The method for removing a polychlorinated aromatic compound according to claim 5, wherein the dechlorination treatment of the polychlorinated aromatic compound in the extraction solvent is a dechlorination reaction with a metal alcoholate. .
JP2002105416A 2002-04-08 2002-04-08 Method for removing polychlorinated aromatic compound from pyrolysis product contaminated with polychlorinated aromatic compound Pending JP2003300050A (en)

Priority Applications (1)

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Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2002105416A JP2003300050A (en) 2002-04-08 2002-04-08 Method for removing polychlorinated aromatic compound from pyrolysis product contaminated with polychlorinated aromatic compound

Publications (1)

Publication Number Publication Date
JP2003300050A true JP2003300050A (en) 2003-10-21

Family

ID=29390128

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP2003300050A (en)

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