JPH11319773A - Continuous decomposition of pcb and device therefor - Google Patents

Continuous decomposition of pcb and device therefor

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Publication number
JPH11319773A
JPH11319773A JP10170440A JP17044098A JPH11319773A JP H11319773 A JPH11319773 A JP H11319773A JP 10170440 A JP10170440 A JP 10170440A JP 17044098 A JP17044098 A JP 17044098A JP H11319773 A JPH11319773 A JP H11319773A
Authority
JP
Japan
Prior art keywords
tank
pcb
reaction
reaction medium
sodium chloride
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
JP10170440A
Other languages
Japanese (ja)
Inventor
Takeshi Hatanaka
武史 畑中
Hisashi Endo
久 遠藤
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.)
ELSON KK
Original Assignee
ELSON KK
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 ELSON KK filed Critical ELSON KK
Priority to JP10170440A priority Critical patent/JPH11319773A/en
Publication of JPH11319773A publication Critical patent/JPH11319773A/en
Pending legal-status Critical Current

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  • Fire-Extinguishing Compositions (AREA)
  • Processing Of Solid Wastes (AREA)
  • Physical Or Chemical Processes And Apparatus (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a method for continuously decomposing PCB and a device therefor in which PCB is continuously subjected to detoxification treatment without generating corrosive gas and heat loss is reduced and running costs are decreased. SOLUTION: Mixed liquid of both a PCB solution and a PCB decomposer consisting of sodium ethoxide, a surfactant and a carbonate is mixed and heated in a reaction tank 22 to produce an emulsionlike reaction medium. A neutralizer and the emulsionlike reaction medium are vaporized in a thermal decomposition tank 42 and subjected to a catalytic contact reaction. Thereby, sodium chloride and a gaseous reaction medium are separated. This sodium chloride is scraped by a screw drum 66 and discharged from a discharged means 70. Further, the gaseous reaction medium is cooled by a condenser 86 and separated into decomposition oil and the neutralizer in a separation tank 90. Accordingly, PCB is efficiently subjected to detoxification treatment and heat loss is reduced and both energy consumption and running costs are decreased and load of maintenance and inspection is reduced.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】この発明はPCBの連続分解方法
およびその装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for continuously decomposing a PCB.

【0002】[0002]

【従来の技術】近年、トランス用絶縁油、切削油、潤滑
油、プレス油、熱処理用の加熱媒体、ペンキや印刷用イ
ンキの添加剤、あるいはノーカーボン紙用溶媒に含有さ
れるPCB(以下、PCB溶液と称する)の処理法とし
て焼却法が試みられたが、ダイオキシン等の有毒ガスが
発生し、実用化に至っていない。
2. Description of the Related Art In recent years, PCBs contained in insulating oil for transformers, cutting oils, lubricating oils, press oils, heating media for heat treatment, additives for paints and printing inks, or solvents for carbonless paper have been developed. An incineration method has been attempted as a method of treating PCB solution, but toxic gas such as dioxin is generated, and has not been put to practical use.

【0003】米国特許第5,075,017号(’01
7特許)には超臨界水を利用した有機塩素化合物の連続
処理法が開示されている。超臨界状態において、リアク
タでは反応中に塩化水素ガスや塩素ガスが多量に発生し
て金属部分を著しく腐食させるため、設備の寿命が極め
て短かくなるため、実用化が困難である。これを防ぐた
め、アルカリを中和剤としてリアクタ内に注入すること
が考えられるが、その場合でも、分解中に発生した腐食
性ガスが高温高圧下で異常に金属部分に損傷を与えるた
め、設備の寿命を実用化レベルまで延ばすことはできな
い。しかも、リアクタ内には反応生成物として塩化ナト
リウム等の固形物が生成し、これがリアクタの内壁に付
着・堆積し、ついには装置内部を閉塞するため、保守・
点検の負担が大きい。
[0003] US Patent No. 5,075,017 ('01
Patent No. 7) discloses a continuous treatment method of an organic chlorine compound using supercritical water. In a supercritical state, in a reactor, a large amount of hydrogen chloride gas or chlorine gas is generated during the reaction and significantly corrodes a metal portion, so that the life of the equipment is extremely short, so that practical use is difficult. In order to prevent this, it is conceivable to inject alkali into the reactor as a neutralizing agent.However, even in such a case, the corrosive gas generated during decomposition may abnormally damage metal parts under high temperature and high pressure. Life cannot be extended to a practical level. In addition, solids such as sodium chloride are produced as reaction products in the reactor, which adhere to and accumulate on the inner wall of the reactor, and eventually block the inside of the apparatus, so that maintenance and
The burden of inspection is heavy.

【0004】米国特許第5,558,783号(’78
3特許)ではリアクタを外管と内管との二重管構造にし
て、セラミック多孔材により内管を形成して、この中に
超臨界水を噴出させて反応をさせているが、内管内で発
生した腐食性ガスは内管を傷めるとともに外管を腐食さ
せる。したがって、連続的に長期にわたって設備を運転
することができない。なお、反応ゾーンの下流に冷却水
を噴出させて内管への塩の付着を防止しているが、熱損
失が大きい。
US Pat. No. 5,558,783 ('78)
No. 3 patent), the reactor has a double tube structure of an outer tube and an inner tube, and an inner tube is formed by a ceramic porous material, and supercritical water is jetted into the inner tube to cause a reaction. The corrosive gas generated in the above will damage the inner tube and corrode the outer tube. Therefore, the equipment cannot be operated continuously for a long time. Although cooling water is jetted downstream of the reaction zone to prevent salt from adhering to the inner tube, heat loss is large.

【0005】[0005]

【発明が解決しようとする課題】’017特許および’
783特許ではいずれも高温高圧時にリアクタ内で大量
に発生する腐食性ガスによるトラブルの解決が困難であ
るため、連続的に使用可能な処理設備を実用化できな
い。第2に、’783特許では反応ゾーンの下部に塩溶
解用の冷却水を供給しているため、水の消費や熱損失が
大きく、ランニングコストが高くなる。
The '017 patent and'
In any of the 783 patents, it is difficult to solve a trouble caused by a large amount of corrosive gas generated in the reactor at a high temperature and a high pressure. Second, in the '783 patent, cooling water for salt dissolution is supplied to the lower part of the reaction zone, so that water consumption and heat loss are large and running costs are high.

【0006】本発明は反応容器内の腐食性ガスの発生を
最少にすることにより、設備の寿命を実用化レベルまで
延長させ、反応容器内における固形物の付着を防止し、
PCBを連続的に長期にわたって無害化処理できるPC
Bの連続分解法およびその装置を提供することを目的と
する。
The present invention minimizes the generation of corrosive gas in the reaction vessel, extends the life of the equipment to a practical level, prevents solids from adhering in the reaction vessel,
PC that can continuously detoxify PCB for long term
An object of the present invention is to provide a continuous decomposition method of B and an apparatus therefor.

【0007】[0007]

【問題を解決するための手段】本願第1の発明は、反応
槽でPCB溶液と、ナトリウムエトキシド、界面活性剤
および炭酸塩からなるPCB分解剤とを100℃〜25
0℃で加熱混合して乳化状反応媒体を生成する工程と、
250℃〜450℃に維持された熱分解槽にタンニンお
よび木酢液から選ばれた少くとも1つの反応促進剤と水
酸化ナトリウム溶液からなる中和剤を供給する工程と、
熱分解槽で乳化状反応媒体と中和剤とを接触反応させて
塩化ナトリウムとガス状反応媒体を分離する工程と、熱
分解槽の上部および下部からそれぞれガス状反応媒体お
よび塩化ナトリウムを排出する工程と、ガス状反応媒体
を冷却して液化することにより分離槽の上相および下相
にそれぞれ分解油と中和剤を生成する工程とからなるP
CBの連続分解方法である。
Means for Solving the Problems In the first invention of the present application, a PCB solution and a PCB decomposing agent comprising sodium ethoxide, a surfactant and a carbonate are reacted in a reaction vessel at 100 ° C. to 25 ° C.
Heating and mixing at 0 ° C. to produce an emulsified reaction medium;
Supplying a pyrolysis tank maintained at 250 ° C. to 450 ° C. with at least one reaction accelerator selected from tannin and wood vinegar and a neutralizing agent comprising a sodium hydroxide solution;
Contacting the emulsified reaction medium and the neutralizing agent in the pyrolysis tank to separate sodium chloride and the gaseous reaction medium, and discharging the gaseous reaction medium and sodium chloride from the upper and lower parts of the pyrolysis tank, respectively And a step of producing a cracked oil and a neutralizing agent in the upper and lower phases of the separation tank by cooling and liquefying the gaseous reaction medium, respectively.
This is a continuous decomposition method of CB.

【0008】本願第2の発明は、PCB溶液と、ナトリ
ウムエトキシド、界面活性剤および炭酸塩からなるPC
B分解剤とを加熱混合して乳化状反応媒体を生成する反
応槽と、反応槽に接続された熱分解槽と、タンニンおよ
び木酢液から選ばれた少くとも1つの反応促進剤と水酸
化ナトリウム溶液からなる中和剤を熱分解槽に供給する
第1供給手段と、乳化状反応媒体を熱分解槽に供給する
第2供給手段と、熱分解槽で乳化状反応媒体と中和剤と
を撹拌しながら接触反応させて塩化ナトリウムとガス状
反応媒体を分離生成する撹拌手段と、熱分解槽の内壁に
付着する塩化ナトリウムを掻き取りながら下部から排出
するスクリュー手段と、熱分解槽の上部に連結されてい
てガス状反応媒体を液化して上相および下相にそれぞれ
分解油と中和剤とを分離する分離槽とを備えたPCBの
連続分解装置である。
[0008] The second invention of the present application is a PC solution comprising a PCB solution, a sodium ethoxide, a surfactant and a carbonate.
A reaction vessel for producing an emulsified reaction medium by heating and mixing the B-decomposing agent, a thermal decomposition vessel connected to the reaction vessel, at least one reaction accelerator selected from tannin and wood vinegar, and sodium hydroxide First supply means for supplying a neutralizing agent composed of a solution to the thermal decomposition tank, second supply means for supplying the emulsified reaction medium to the thermal decomposition tank, and the emulsified reaction medium and the neutralizing agent in the thermal decomposition tank. A stirring means for causing a contact reaction while stirring to separate and generate a gaseous reaction medium with sodium chloride, a screw means for discharging sodium chloride adhering to the inner wall of the pyrolysis tank from the lower part while scraping the same, and an upper part of the pyrolysis tank This is a continuous cracking apparatus for PCB, which is connected to a liquefied gaseous reaction medium and separates a decomposed oil and a neutralizing agent into an upper phase and a lower phase, respectively.

【0009】[0009]

【作用】本発明のPCBの連続分解方法およびその装置
において、PCB溶液と、ナトリウムエトキシド、界面
活性剤および炭酸塩からなるPCB分解剤とを加熱混合
することにより乳化状反応媒体を生成して、有機塩素化
合物を98%以上反応させた後、これを熱分解槽に供給
し、さらに、反応促進剤および水酸化ナトリウム溶液を
含む中和剤と熱分解槽で接触反応させてPCBを99.
99%以上分解処理するようにしたため、熱分解槽内の
腐食性ガスの発生を最少にして設備の寿命を実用化レベ
ルまで延長させることが可能となる。しかも、熱分解槽
内で塩化ナトリウムとガス状反応媒体とを分離生成し、
前者をスクリュー手段により熱分解槽下部から連続的に
取り出し、一方、後者を熱分解槽上部から取り出して液
化して分離油と中和剤とに分離するようにしたため、熱
損失を少なくし、処理コストを著しく低減することがで
きる。反応促進剤は熱分解槽で強力なキレート剤的作用
を持ち、乳化状反応媒体における未反応のPCB中の塩
素を置換してPCBを効率的に無害化する機能がある。
In the method and apparatus for continuously decomposing PCB of the present invention, an emulsified reaction medium is produced by heating and mixing a PCB solution and a PCB decomposing agent comprising sodium ethoxide, a surfactant and a carbonate. , 98% or more of the organochlorine compound is supplied to a pyrolysis tank, and further reacted with a reaction accelerator and a neutralizing agent containing a sodium hydroxide solution in the pyrolysis tank to form PCB.
Since the decomposition treatment is performed at 99% or more, it is possible to minimize the generation of corrosive gas in the thermal decomposition tank and extend the life of the equipment to a practical level. Moreover, sodium chloride and the gaseous reaction medium are separated and generated in the pyrolysis tank,
The former is continuously taken out from the lower part of the pyrolysis tank by screw means, while the latter is taken out from the upper part of the pyrolysis tank and liquefied and separated into separated oil and neutralizing agent, so that heat loss is reduced and processing is performed. The cost can be significantly reduced. The reaction accelerator has a strong chelating agent effect in the thermal decomposition tank, and has a function of effectively replacing the chlorine in unreacted PCB in the emulsified reaction medium to make the PCB harmless.

【0010】[0010]

【実施例】以下、本発明について図面を用いてより詳細
に説明する。図1は、本願発明によるPCBの連続分解
方法を実行するための第1実施例による連続分解装置の
概略図である。PCBはトランス絶縁油、切削油、潤滑
油、除草剤などの農薬を製造する段階で発生する廃油等
に含まれているが、ここではPCB溶液として説明す
る。連続分解装置10はPCB溶液を貯蔵する貯蔵タン
ク12と、ポンプ14と、PCB溶液を供給するための
フィード・タンク16を備える。PCB溶液はフィード
・タンク16からポンプ18およびコントロール・バル
ブ20を介して反応槽22に供給される。反応槽22に
はPCB剤としてナトリウムエトキシド、界面活性剤お
よび炭酸塩がそれぞれ供給タンク24、26、28から
ロータリ・バルブ24a、26a、28aを介して供給
される。ナトリウムエトキシドと、界面活性剤と、炭酸
塩の重量eeは10:0.5:1程度が望ましい。界面
活性剤としてはパルミチン酸、ステアリン酸およびオレ
イン酸等の高級脂肪酸から選ばれ、炭酸塩は炭酸ナトリ
ウムおよび炭酸水素ナトリウムから選ばれる。PCB溶
液に対するPCB分解剤の混合ee率は重量eeで5〜
25%が望ましい。PCB分解剤が5%より少ないとP
CB溶液の乳化・ゲル化が不充分となり、25%より多
いと処理効果が変わらないばかりでなく、処理費が高く
なる。反応槽22はPCB溶液とPCB分解剤とを撹拌
するためのモータ駆動撹拌器30と加熱手段32を備え
る。加熱手段32は反応槽22の混合液を100〜25
0℃の温度に加熱する。加熱混合は5〜10分間行なわ
れる。このとき、PCB溶液はPCB分解剤と反応して
乳化・ゲル化され、約98%の有機塩素化合物が分解さ
れ、乳化状反応媒体が生成する。この乳化状反応媒体は
チェック弁34、36およびプランジャポンプ38から
なる圧入手段39およびコントロール・バルブ40を介
して熱分解槽42に圧入される。熱分解槽42内には水
熱溶媒タンク44から水熱溶媒が供給される。水熱溶媒
タンク44には水酸化ナトリウム溶液と反応促進剤との
混合溶媒からなる中和剤が貯蔵されている。水酸化ナト
リウム溶液には1〜10重量%の割合で反応促進剤が混
合されている。反応促進剤は強力なキレート剤的作用を
持つタンニンおよび木酢液から選ばれた少くとも1つの
溶液からなる。このように反応促進剤と水酸化ナトリウ
ム溶液との混合溶液からなる中和剤はチェック弁46、
48および高圧ポンプ52からなる圧入手段54を介し
て加熱手段56に供給され、250℃〜450℃に加熱
された後、コントロール・バルブ58を介して熱分解槽
42に圧入される。熱分解槽42はバンドヒータ等の加
熱手段60により250℃〜450℃に加熱される反応
容器62と、撹拌ブレード64およびスクリュードラム
66とを備える。撹拌ブレート64は反応容器62内で
気化した乳化状反応媒体および中和剤を撹拌混合すると
ともに容器内壁に付着する塩化ナトリウムを掻き取る作
用をする。スクリュードラム66は反応容器62との間
に乳化状反応媒体を99.99%熱分解するための環状
反応室68を形成し、同時に反応容器62の内壁に付着
する塩化ナトリウムを掻き取りながら、下部に排出する
機能を有する。このように、熱分解槽42は乳化状反応
媒体をガス状反応媒体と固形物である塩化ナトリウムと
に分離する機能を有する。熱分解槽42の下部は塩排出
口42aを備え、その中に掻き取られた塩化ナトリウム
を強制的に下部に排出するためのモータ駆動押し出しス
クリュー70が配置されている。押し出しスクリュー7
0の排出側はロータリバルブ72を介して排出タンク7
4に接続されており、排出タンク74の出口はロータリ
バルブ76を備え、ここから塩化ナトリウムは外部へ排
出される。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS Hereinafter, the present invention will be described in more detail with reference to the drawings. FIG. 1 is a schematic diagram of a continuous decomposition apparatus according to a first embodiment for executing a continuous decomposition method of a PCB according to the present invention. PCB is contained in waste oil and the like generated at the stage of producing agricultural chemicals such as transformer insulating oil, cutting oil, lubricating oil, and herbicide, but is described here as a PCB solution. The continuous decomposition apparatus 10 includes a storage tank 12 for storing a PCB solution, a pump 14, and a feed tank 16 for supplying the PCB solution. The PCB solution is supplied from a feed tank 16 to a reaction tank 22 via a pump 18 and a control valve 20. To the reaction tank 22, sodium ethoxide, a surfactant, and a carbonate as PCB agents are supplied from supply tanks 24, 26, and 28 via rotary valves 24a, 26a, and 28a, respectively. The weight ee of the sodium ethoxide, the surfactant, and the carbonate is preferably about 10: 0.5: 1. The surfactant is selected from higher fatty acids such as palmitic acid, stearic acid and oleic acid, and the carbonate is selected from sodium carbonate and sodium hydrogen carbonate. The mixing ee ratio of the PCB decomposing agent to the PCB solution is 5 to 5 by weight ee.
25% is desirable. If the PCB decomposer is less than 5%, P
If the CB solution is insufficiently emulsified and gelled, if it exceeds 25%, not only the treatment effect does not change but also the treatment cost increases. The reaction tank 22 includes a motor-driven stirrer 30 for stirring the PCB solution and the PCB decomposing agent, and a heating unit 32. The heating means 32 converts the mixed solution in the reaction tank 22 to 100 to 25.
Heat to a temperature of 0 ° C. Heat mixing is performed for 5 to 10 minutes. At this time, the PCB solution reacts with the PCB decomposing agent to be emulsified and gelled, and about 98% of the organic chlorine compound is decomposed, thereby generating an emulsified reaction medium. The emulsified reaction medium is press-fitted into a pyrolysis tank 42 through a press-fitting means 39 comprising check valves 34 and 36 and a plunger pump 38 and a control valve 40. A hydrothermal solvent is supplied from a hydrothermal solvent tank 44 into the thermal decomposition tank 42. The hydrothermal solvent tank 44 stores a neutralizing agent comprising a mixed solvent of a sodium hydroxide solution and a reaction accelerator. A reaction accelerator is mixed in the sodium hydroxide solution at a ratio of 1 to 10% by weight. The reaction accelerator comprises at least one solution selected from tannin and wood vinegar having a strong chelating action. As described above, the neutralizing agent composed of the mixed solution of the reaction accelerator and the sodium hydroxide solution is supplied to the check valve 46,
After being supplied to the heating means 56 through the press-fitting means 54 comprising the pressure pump 48 and the high-pressure pump 52 and heated to 250 ° C. to 450 ° C., it is press-fitted into the pyrolysis tank 42 through the control valve 58. The thermal decomposition tank 42 includes a reaction vessel 62 heated to 250 ° C. to 450 ° C. by a heating means 60 such as a band heater, a stirring blade 64 and a screw drum 66. The stirring plate 64 functions to stir and mix the emulsified reaction medium and the neutralizing agent vaporized in the reaction vessel 62 and scrape sodium chloride adhering to the inner wall of the vessel. The screw drum 66 forms an annular reaction chamber 68 with the reaction vessel 62 for thermally decomposing the emulsified reaction medium by 99.99%, and simultaneously scrapes sodium chloride adhering to the inner wall of the reaction vessel 62 while lowering it. It has the function of discharging to As described above, the pyrolysis tank 42 has a function of separating the emulsified reaction medium into the gaseous reaction medium and the solid sodium chloride. The lower part of the pyrolysis tank 42 is provided with a salt discharge port 42a, in which a motor driven extrusion screw 70 for forcibly discharging the scraped sodium chloride to the lower part is arranged. Extrusion screw 7
The discharge side of the discharge tank 7 through the rotary valve 72
The outlet of the discharge tank 74 is provided with a rotary valve 76 from which sodium chloride is discharged.

【0011】熱分解槽42内の反応生成物のうち固形物
は塩排出口42aから排出され、ガス状反応媒体はアウ
トレット42bを介して凝縮器86に給送され、そこで
冷却水により冷却され、減圧弁88により減圧されて分
離槽90に排出される。分離槽90において分解油92
と、反応促進剤と水酸化ナトリウム溶液からなる中和剤
94とはそれぞれ上相と下相に分離する。分解油92は
バルブ96を介して取り出した後、油中のPCB濃度を
測定して、PCB濃度が基準値以上であれば分離油を再
度貯蔵タンク12に循環してPCB溶液と混合して再処
理する。一方、分離槽90の下側部にはレベルルスイッ
チ98が取り付けられていて、このレベルスイッチ98
に中和剤の液面が接触すると、レベルスイッチ98が作
動して制御弁100を開く。このとき、中和剤はポンプ
101および配管102を介して撹拌器付濃度調整タン
ク104に供給される。タンク104の中和剤はバルブ
106を介して一部排出され、中和剤中の反応促進剤と
アルカリの濃度が所定値以下の場合はアルカリ溶液タン
ク108からポンプ110およびコントロールバルブ1
12を介して反応促進剤と水酸化ナトリウム溶液との高
濃度溶液が濃度調整タンク104に供給されて反応促進
剤とアルカリの濃度が所定値に調整される。濃度調整さ
れた水酸化ナトリウム溶液と反応促進剤からなる中和剤
はポンプ114およびコントロール・バルブ116を介
して水熱溶媒タンク44に循環されて再利用される。
[0011] Among the reaction products in the pyrolysis tank 42, solids are discharged from the salt discharge port 42a, and the gaseous reaction medium is supplied to the condenser 86 through the outlet 42b, where it is cooled by cooling water. The pressure is reduced by the pressure reducing valve 88 and discharged to the separation tank 90. In the separation tank 90, the decomposed oil 92
And the neutralizing agent 94 composed of a sodium hydroxide solution and a reaction accelerator separate into an upper phase and a lower phase, respectively. After the cracked oil 92 is taken out through the valve 96, the PCB concentration in the oil is measured, and if the PCB concentration is equal to or higher than the reference value, the separated oil is circulated again to the storage tank 12, mixed with the PCB solution, and recycled. To process. On the other hand, a level switch 98 is attached to the lower side of the separation tank 90.
When the liquid level of the neutralizing agent comes into contact with, the level switch 98 is operated to open the control valve 100. At this time, the neutralizing agent is supplied to the concentration adjusting tank 104 with a stirrer via the pump 101 and the pipe 102. The neutralizing agent in the tank 104 is partially discharged through a valve 106. When the concentrations of the reaction accelerator and the alkali in the neutralizing agent are lower than a predetermined value, a pump 110 and a control valve 1
A high concentration solution of the reaction accelerator and the sodium hydroxide solution is supplied to the concentration adjusting tank 104 via 12 to adjust the concentrations of the reaction accelerator and the alkali to a predetermined value. The neutralized agent composed of the sodium hydroxide solution and the reaction accelerator whose concentration has been adjusted is circulated to the hydrothermal solvent tank 44 via the pump 114 and the control valve 116 to be reused.

【0012】図2は本発明の第2実施例によるPCB連
続分解装置の概略図を示し、図1と同一部品については
同一符号が使用され、類似部品についてはシングル・ア
ポストロフィが付けてある。PCB連続分解装置10’
において、反応槽22’および熱分解槽42’はバーナ
120を備えた加熱炉122により280℃〜450℃
に加熱される。PCB溶液はタンク16からコントロー
ル・バルブ20を介して反応槽22’に供給され、ナト
リウムエトキシド、界面活性剤および炭酸塩はそれぞれ
タンク24、26、28からロータリ・バルブ24a、
26a、28aを介して反応槽22’に供給され、PC
B溶液と加熱混合されて乳化状反応媒体が生成される。
乳化状反応媒体はスクリュー等からなる定量供給装置1
24により熱分解槽42’に供給される。熱分解槽4
2’には濃度調整タンク104から反応促進剤と水酸化
ナトリウムの混合溶液からなる中和剤が供給される。乳
化状反応媒体は環状反応室68’で熱分解され、塩化ナ
トリウムとガス状反応媒体が分離される。塩化ナトリウ
ムはスクリュードラムにより反応容器62’の内壁から
掻き取られて下方に移送され、ここで、押し出しスクリ
ュー70およびロータリ・バルブ72を介して排出タン
ク74に排出される。ガス状反応媒体はアウトレット4
2’bから凝縮器86を介して分離槽90に供給され、
分解油92と混合溶液94とに分離される。分離槽90
の分離油92はコントロール・バルブ96、ポンプ12
6およびバルブ128を介して燃料油タンク130に供
給され、他の燃料油と適当な割合で混合された後、ポン
プ132でバーナ120に供給される。
FIG. 2 is a schematic view of a continuous PCB disassembling apparatus according to a second embodiment of the present invention. In FIG. 2, the same parts as those in FIG. 1 are denoted by the same reference numerals, and similar parts are denoted by single apostrophes. PCB continuous decomposition device 10 '
, The reaction tank 22 ′ and the thermal decomposition tank 42 ′ are heated at 280 ° C. to 450 ° C.
Heated. The PCB solution is supplied from tank 16 to reaction vessel 22 'via control valve 20, and sodium ethoxide, surfactant and carbonate are supplied from tanks 24, 26 and 28, respectively, to rotary valve 24a,
26a and 28a, and supplied to the reaction tank 22 '.
The mixture is heated and mixed with the solution B to form an emulsified reaction medium.
The emulsified reaction medium is a fixed-quantity feeding device 1 composed of a screw or the like.
24 feeds to a pyrolysis tank 42 '. Pyrolysis tank 4
2 ′ is supplied with a neutralizing agent comprising a mixed solution of a reaction accelerator and sodium hydroxide from the concentration adjusting tank 104. The emulsified reaction medium is thermally decomposed in the annular reaction chamber 68 'to separate the sodium chloride and the gaseous reaction medium. The sodium chloride is scraped off the inner wall of the reaction vessel 62 ′ by a screw drum and transported downward, where it is discharged to a discharge tank 74 via an extrusion screw 70 and a rotary valve 72. Gaseous reaction medium is outlet 4
2′b is supplied to the separation tank 90 via the condenser 86,
The cracked oil 92 and the mixed solution 94 are separated. Separation tank 90
Separation oil 92 is supplied to control valve 96 and pump 12
The fuel is supplied to the fuel oil tank 130 via the valve 6 and the valve 128, mixed with other fuel oil at an appropriate ratio, and then supplied to the burner 120 by the pump 132.

【0013】[0013]

【発明の効果】以上説明したように、本発明によりPC
Bは反応槽により98%以上分解処理された後に熱分解
槽で熱分解されるため、塩化水素ガスや塩素ガスの発生
が押えられ、設備の損傷を少なくしてPCBを効率良く
連続的に分解することができる。しかも、反応の副産物
である固形物の塩化ナトリウムを熱分解の時点で他の反
応媒体から完全分離して、スクリュー手段により塩化ナ
トリウムを反応槽の下部より排出するようにしたため、
冷却水による塩の溶解作業ならびにその後の分離作業を
不要にして、熱分解槽の熱効率を著しく改善し、ランニ
ングコストを大幅に低減できる。しかも、反応容器内に
塩を溶解するための冷却水の供給を不要にしたため、大
量の水の消費を防止し、熱損失を最少にすることができ
る。
As described above, according to the present invention, the PC
Since B is decomposed by 98% or more in the reaction tank and then pyrolyzed in the pyrolysis tank, the generation of hydrogen chloride gas and chlorine gas is suppressed, the damage to the equipment is reduced, and the PCB is decomposed efficiently and continuously. can do. Moreover, the solid by-product sodium chloride, which is a by-product of the reaction, was completely separated from the other reaction medium at the time of thermal decomposition, and sodium chloride was discharged from the lower part of the reaction tank by screw means.
The operation of dissolving the salt with the cooling water and the subsequent separation operation are not required, so that the thermal efficiency of the pyrolysis tank is significantly improved, and the running cost can be greatly reduced. In addition, since it is not necessary to supply cooling water for dissolving the salt in the reaction vessel, consumption of a large amount of water can be prevented and heat loss can be minimized.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明の望ましい第1実施例によるPCBの連
続分解装置と反応系統を示す図。
FIG. 1 is a view showing a continuous decomposition apparatus and a reaction system of a PCB according to a first preferred embodiment of the present invention.

【図2】本発明の望ましい第2実施例によるPCBの連
続分解装置と反応系統を示す図。
FIG. 2 is a view showing a continuous PCB decomposition apparatus and a reaction system according to a second preferred embodiment of the present invention;

【符号の説明】[Explanation of symbols]

16 フィード・タンク 22
反応槽 24 ナトリウムエトキシド供給タンク 26
界面活性剤供給タンク 28 炭酸塩 32
加熱手段 42 熱分解槽 44
水熱溶媒供給タンク 46 酸化剤供給タンク 62
高温高圧容器 64 撹拌ブレード 66
スクリュードラム 68 環状反応室 70
押し出しスクリュー 74 塩排出タンク 86
凝縮器 90 分離槽 104
濃度調整タンク 108 アルカリ溶液タンク 120
バーナー 122 加熱炉 124
定量供給装置
16 Feed tank 22
Reaction tank 24 Sodium ethoxide supply tank 26
Surfactant supply tank 28 Carbonate 32
Heating means 42 Pyrolysis tank 44
Hydrothermal solvent supply tank 46 Oxidant supply tank 62
High temperature and high pressure vessel 64 Stirrer blade 66
Screw drum 68 Annular reaction chamber 70
Extrusion screw 74 Salt discharge tank 86
Condenser 90 Separation tank 104
Concentration adjusting tank 108 Alkaline solution tank 120
Burner 122 Heating furnace 124
Metering device

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】反応槽でPCB溶液と、ナトリウムエトキ
シド、界面活性剤および炭酸塩からなるPCB分解剤と
を100℃〜250℃で加熱混合して乳化状反応媒体を
生成する工程と、250℃〜450℃に維持された熱分
解槽にタンニンおよび木酢液から選ばれた少くとも1つ
の反応促進剤と水酸化ナトリウム溶液からなる中和剤を
供給する工程と、熱分解槽で乳化状反応媒体と中和剤と
を接触反応させて塩化ナトリウムとガス状反応媒体を分
離する工程と、熱分解槽の上部および下部からそれぞれ
ガス状反応媒体およひ塩化ナトリウムを排出する工程
と、ガス状反応媒体を冷却して液化することにより分離
槽の上相および下相にそれぞれ分解油と中和剤を生成す
る工程とからなるPCBの連続分解方法。
(1) a step of heating and mixing a PCB solution and a PCB decomposing agent comprising sodium ethoxide, a surfactant and a carbonate at 100 ° C. to 250 ° C. in a reaction vessel to form an emulsified reaction medium; A step of supplying at least one reaction accelerator selected from tannin and wood vinegar and a neutralizing agent comprising a sodium hydroxide solution to a pyrolysis tank maintained at a temperature of from 450 ° C to 450 ° C; Contacting the medium with a neutralizing agent to separate sodium chloride from the gaseous reaction medium; discharging the gaseous reaction medium and sodium chloride from the upper and lower parts of the pyrolysis tank, respectively; Cooling the reaction medium to liquefy it to produce cracked oil and a neutralizing agent in the upper and lower phases of the separation tank, respectively.
【請求項2】請求項1において、さらに、中和剤中の反
応促進剤および水酸化ナトリウム溶液の濃度を調整して
中和剤の供給工程に循環させる工程を含むPCBの連続
分解方法。
2. The method for continuously decomposing PCB according to claim 1, further comprising the step of adjusting the concentrations of the reaction accelerator and the sodium hydroxide solution in the neutralizing agent and circulating them in the neutralizing agent supply step.
【請求項3】請求項1または2において、熱分解槽の内
壁に付着する塩化ナトリウムをスクリュードラムにより
掻き取る工程を含むPCBの連続分解方法。
3. The continuous PCB decomposing method according to claim 1, further comprising a step of scraping sodium chloride adhering to the inner wall of the thermal decomposition tank with a screw drum.
【請求項4】PCB溶液と、ナトリウムエトキシド、界
面活性剤および炭酸塩からなるPCB分解剤とを加熱混
合して乳化状反応媒体を生成する反応槽と、反応槽に接
続された熱分解槽と、タンニンおよび木酢液から選ばれ
た少くとも1つの反応促進剤と水酸化ナトリウム溶液か
らなる中和剤を熱分解槽に供給する第1供給手段と、乳
化状反応媒体を熱分解槽に供給する第2供給手段と、熱
分解槽で乳化状反応媒体と中和剤とを撹拌しながら接触
反応させて塩化ナトリウムとガス状反応媒体を分離生成
する撹拌手段と、熱分解槽の内壁に付着する塩化ナトリ
ウムを掻き取りながら下部から排出するスクリュー手段
と、熱分解槽の上部に連結されていてガス状反応媒体を
液化して上相および下相にそれぞれ分解油と中和剤とを
分離する分離槽とを備えたPCBの連続分解装置。
4. A reaction tank for producing an emulsified reaction medium by heating and mixing a PCB solution and a PCB decomposing agent comprising sodium ethoxide, a surfactant and a carbonate, and a thermal decomposition tank connected to the reaction tank. First supply means for supplying at least one reaction accelerator selected from tannin and wood vinegar and a neutralizing agent comprising a sodium hydroxide solution to the pyrolysis tank; and supplying an emulsified reaction medium to the pyrolysis tank. A second supply means, a stirring means for causing a contact reaction between the emulsified reaction medium and the neutralizing agent in the pyrolysis tank while stirring to separate and generate sodium chloride and a gaseous reaction medium, and adhering to the inner wall of the pyrolysis tank. A screw means for discharging sodium chloride from the bottom while scraping off, and a liquefied gaseous reaction medium connected to the upper part of the pyrolysis tank to separate cracked oil and neutralizer into upper and lower phases, respectively. Separation tank and PCB continuous decomposition device equipped.
【請求項5】請求項4において、熱分解槽が反応容器
と、その中に回転可能に配置されていて内壁に付着する
塩化ナトリウムを掻き取るスクリュードラムと、反応容
器とスクリュードラムとの間に形成された環状反応室と
を備え、スクリュードラムが環状反応室の内壁に付着し
た塩化ナトリウムを掻き取りながら高圧容器の下部に給
送するPCBの連続分解装置。
5. The reaction vessel according to claim 4, wherein a pyrolysis tank is rotatably disposed in the reaction vessel, a screw drum for scraping sodium chloride adhering to the inner wall, and between the reaction vessel and the screw drum. A continuous decomposition apparatus for PCB, comprising: a formed annular reaction chamber; and a screw drum that feeds the lower part of the high-pressure vessel while scraping off sodium chloride adhering to the inner wall of the annular reaction chamber.
JP10170440A 1998-05-15 1998-05-15 Continuous decomposition of pcb and device therefor Pending JPH11319773A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10170440A JPH11319773A (en) 1998-05-15 1998-05-15 Continuous decomposition of pcb and device therefor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10170440A JPH11319773A (en) 1998-05-15 1998-05-15 Continuous decomposition of pcb and device therefor

Publications (1)

Publication Number Publication Date
JPH11319773A true JPH11319773A (en) 1999-11-24

Family

ID=15904968

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10170440A Pending JPH11319773A (en) 1998-05-15 1998-05-15 Continuous decomposition of pcb and device therefor

Country Status (1)

Country Link
JP (1) JPH11319773A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100697562B1 (en) 2006-01-26 2007-03-21 한국원자력연구소 Method of Destruction Treatment of Insulating Oil Containing Polychlorinated Biphenyls Using High Temperature Alkali Molten Salt
WO2013061824A1 (en) * 2011-10-27 2013-05-02 クリーンメカニカル株式会社 Mixing system

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100697562B1 (en) 2006-01-26 2007-03-21 한국원자력연구소 Method of Destruction Treatment of Insulating Oil Containing Polychlorinated Biphenyls Using High Temperature Alkali Molten Salt
WO2013061824A1 (en) * 2011-10-27 2013-05-02 クリーンメカニカル株式会社 Mixing system

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