JP3925890B2 - Method and apparatus for treating PCB-contaminated waste cleaning exhaust gas - Google Patents
Method and apparatus for treating PCB-contaminated waste cleaning exhaust gas Download PDFInfo
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Description
【0001】
【発明の属する技術分野】
本発明は、ポリ塩化ビフェニール(以下、「PCB」という)類汚染物洗浄排ガスの処理方法およびその装置に関し、更に詳しくは、PCB類汚染物の溶剤洗浄で生じる排ガスの処理方法およびその処理装置に関する。
【0002】
【従来の技術】
PCB類は、かって有用な物質として熱媒体、トランス・コンデンサ等の電気機器用の絶縁油、ノーカーボン紙の他、潤滑油、各種可塑剤、塗料、シーラント剤等に生産・使用されていた。PCB類とは、PCB及びその誘導体を含む概念である。PCB類は、カネミ油症事件等をきっかけに生体・環境への影響が明らかになり、昭和47年までに生産が中止され、昭和49年度までに製造・輸入、開放系用途での使用、新規使用が禁じられた。閉鎖系用途については、その後熱媒体用のPCB類は大部分が回収されたが、電気機器用のPCB類は現在も継続して使用されているか、使用事業者で保管されている。
しかし、使用済PCB電気機器等の保管が長期化する中で、機器の紛失・行方不明、PCBの漏出、事故による漏洩等の恐れが大きくなってきている。既に、平成5年の厚生省の調査によれば、約7%が行方不明になっている。PCB類は環境中あるいは生体中で広く検出され、種々の経路を通って環境中に侵入している可能性が示唆されている。
従ってPCB類廃棄物の早期処理が世界的に求められているが、日本では1987年11月から約2年間にわたる鐘淵化学工業(株)高砂事業所における液状廃PCB類の高温熱分解処理を唯一の例外として、「PCB廃棄物の処理」が認められた例はなく、全国各地で多数計画された他の処理施設は、立地の問題で実現していない。
PCB使用電気機器等を完全に処分するためには、充填されている絶縁油だけでなく、PCB類が付着含浸している容器等の汚染物を浄化する必要がある。PCB類汚染物(廃プラスチック類又は金属くず)の処分又は再生の方法としては、焼却及び洗浄設備を用いてPCB類を十分に除去する方法が定められている。判定基準としては表面付着量として0.1μg/100cm2、または含有量として0.01mg/kgが定められ、この基準は北米等に比較して100倍厳しい。
【0003】
【発明が解決しようとする課題】
「PCB汚染物の処分又は再生の方法」として「洗浄設備を用いてPCBを十分に除去する方法」を用いた場合、廃洗浄剤が発生し、加熱乾燥や廃洗浄剤の蒸留再生をおこなう場合には洗浄剤蒸気を含む排ガスも発生する。この排ガス処理には通常、活性炭が使用される。
この場合、日本では浄化の判定基準が厳しいため、使用する溶剤量が必然的に多くなり、副次的に排ガス発生量及び活性炭使用量も多くなる。PCB類を含有する使用済の活性炭は、現在のところ、許可されている処理・処分方法も判定基準も無いため、保管せざるをえない。
【0004】
洗浄剤として溶剤を用いる場合、溶剤の回収と活性炭の使用量の低減のために、排ガス処理では活性炭処理の前に、冷却凝縮処理することが一般的である。PCB類に比較して洗浄溶剤の沸点は通常低いため、冷却凝縮後のガス中に含まれる非凝縮成分はほとんどが溶剤であり、PCB類の量は少ない。しかし多くの場合、洗浄溶剤自体も有害性があるため、洗浄溶剤で破過した活性炭は交換しなければならない。従って、従来の使用条件ではPCB類をごく僅かに吸着した使用済活性炭が大量に発生することになる。
そこで本発明は、PCB類汚染物の溶剤洗浄時の排ガスを活性炭処理する場合に、活性炭を随時再生し、できる限り長寿命化を図ることができるPCB類汚染物洗浄排ガスの処理方法及びその装置を提供することを目的とする。
【0005】
【課題を解決するための手段】
(1)ポリ塩化ビフェニール類汚染物を溶剤で洗浄し、生じるポリ塩化ビフェニール類と溶剤を含有する排ガスを活性炭層に導き吸着させる活性炭吸着工程を有するポリ塩化ビフェニール類汚染物洗浄排ガスの処理方法において、並列した2以上の活性炭層のうち、先に吸着工程にあった活性炭層への該排ガス供給を停止し、該活性炭層を減圧及び/又は加熱して前記活性炭吸着工程で吸着したポリ塩化ビフェニール類と溶剤のうち溶剤を脱離させる脱離工程と、該脱離した溶剤を含む脱離ガスを冷却凝縮させて非凝縮性物質は吸着能力のある別の活性炭層に導いて吸着させる工程を有し、先に吸着工程にあった活性炭層のポリ塩化ビフェニール類汚染物洗浄排ガス吸着能を再生することを特徴とするポリ塩化ビフェニール類汚染物洗浄排ガスの処理方法。
(2)前記活性炭層の加熱温度は200℃以下であることを特徴とする前記(1)記載のポリ塩化ビフェニール類汚染物洗浄排ガスの処理方法。
(3)ポリ塩化ビフェニール類汚染物を溶剤で洗浄することにより生じるポリ塩化ビフェニール類と溶剤を含有する洗浄排ガスを吸着する並列に設けた2以上の活性炭層と、該洗浄排ガスを吸着する活性炭層を加温及び/又は減圧することにより吸着しているポリ塩化ビフェニール類と溶剤のうち溶剤を脱離する脱離手段と、該活性炭層から脱離した溶剤の脱離ガス中で、凝縮性物質は冷却凝縮させる冷却手段と、該冷却凝縮物を分離する分離手段と、非凝縮性物質は再吸着する活性炭層を有することを特徴とするポリ塩化ビフェニール類汚染物洗浄排ガスの処理装置。
(4)複数の活性炭層各々の活性炭層の入り口側には、ポリ塩化ビフェニール類汚染物の洗浄排ガスの導入口と、冷却手段から非冷却凝縮物を含むガスの導入口とを、切替え可能に配備し、該活性炭層の出口は冷却手段に連通するよう配備されたことを特徴とする前記(3)に記載のポリ塩化ビフェニール類汚染物洗浄排ガスの処理装置。
【0006】
【発明の実施の形態】
活性炭を減圧又は加熱すると吸着容量が低下するため、吸着物質が脱離するが、脱離効率は吸着物質の沸点、蒸気圧、分子量、疎水性などによる。吸着物質を完全に脱離させ、活性炭を完全に再生するためには数百度以上の高温状態と水蒸気供給等が必要となるが、洗浄溶剤のような低沸点物質は比較的脱離しやすい。本発明を実施するにあたっては、例えば以下のような装置で実施するとよい。図1、2は、本発明の実施の形態の例を示す図である。洗浄時と活性炭再生時とはプラント装置間をつなぐ配管をバルブで切り替えて駆動する。
図1は洗浄時の乾燥工程における排ガス処理流路の例を示す。洗浄槽11には加熱器12で加温した気体を供給し、洗浄槽11からの排ガスは冷却凝縮器13で冷却凝縮後、活性炭1で処理したのち再度加熱器12に供給する形で、加温気体を洗浄槽11に循環供給して、被洗浄物を乾燥させる。
図2は活性炭層1再生時のガス流路を示す。活性炭層1には加熱器12で加温した気体を洗浄時と逆方向から供給し、活性炭層1からの排ガスは冷却凝縮して溶剤等を回収した後、活性炭層2で吸着処理させる。活性炭層2で吸着しなかった成分ガスは再度加熱器12で加温して活性炭層1に循環供給する。
ここで、図では冷却凝縮器13の下流側に真空ポンプ14を示しているが、排ガス中の溶剤濃度が低くなる各処理工程の後半では真空ポンプ14を冷却凝縮器13の上流側に変更できるように配管及びバルブを設置しておくことが望ましい。
【0007】
このようにすると、活性炭層1の吸着物質を脱離させて、凝縮液として回収することができる。回収した凝縮液は溶剤再生装置15に送り再生する。洗浄溶剤又はPCB類の熱変成の防止、及び活性炭の発火防止のため、活性炭の加熱温度は加温気体として不活性ガスを用いた場合でも200℃程度が上限であるため、脱離される吸着物質は沸点の低い溶剤が主体となる。
冷却凝縮で除去できない残余の非凝縮成分は活性炭層2で除去されるため、この活性炭再生工程によって環境中に吸着物質が放出されることはない。
活性炭層2の再生も同様におこなう。
循環に用いる気体は大気でもよいが、活性炭の発火防止、吸着物質の変成防止のため、窒素等の不活性ガスを用いることが望ましい。洗浄工程又は再生工程終了後、浄化済み気体であるから大気放出しても問題はないが、不活性ガスを使用している場合、加圧タンク等に保管して再利用することがより望ましい。
排ガス処理工程において活性炭槽にかける負荷は、できる限り少ないことが望ましいため冷却温度はできるだけ低いことが望ましく、具体的には0℃以下が望ましく、−10℃以下がより望ましい。
上記の形態では、洗浄排ガス処理設備の冷却凝縮器及び活性炭を流用しているが、溶剤洗浄処理時に生じる排ガスを処理する工程の一部として設定されている冷却凝縮器及び活性炭とは別の新たな冷却凝縮器及び活性炭を使用してもよい。流用する場合は、新たな機器を別個に設ける必要がなく、その分で機器数が少なくてすむ利点がある。これは特に間欠的に溶剤洗浄を行う場合に有効である。新たに別に設けた場合には、溶剤洗浄の状況に限定されずに活性炭の吸引再生が出来る利点がある。
【0008】
吸着していた低沸点溶剤の変質・劣化、活性炭の引火等を防止するため、加熱温度としては、キャリアガスとして付加性ガスを供給する場合、200℃程度以下がよい。酸素を含む一般空気が存在する場合には100℃程度以下にしておくことが望ましい。
本形態の減圧吸引による再生は、活性炭を完全に再生するわけではなく、やがてPCB類が蓄積し、交換することになる。それでも、使用済み活性炭の使用量は大幅に削減できる。
上記の形態は、2系列以上の活性炭を順次その場で再生するという考えを採用している。こうした方法は、TCE(トリクロロエチレン)PCE(テトラエチレン)等の揮発性溶剤で汚染された地下水の浄化処理に使われている。2系列以上の繊維状活性炭を加熱蒸気で定期的に再生する。再生時の加熱蒸気と揮発性溶剤等を含む排ガスは冷却して凝縮し、揮発性溶剤と水とを比重差で分離する。比重差で分離した水は、さらに処理した後、有害物を含まない水として排出している。
しかし、PCB類を含む活性炭を加熱蒸気で処理すれば、加熱PCBも活性炭から一部脱離する可能性があるため凝縮後の水の処理が困難である。排水処理に活性炭を使う必要があり、液相吸着は吸着効率が低いため、逆に使用済み活性炭が増加することになる。
【0009】
【発明の効果】
本発明は上記のような構成でなるから、洗浄溶剤とPCB類を含むガスを吸着した活性炭を、できる限り再生することで吸着能を自主的に回復させ、活性炭の効率的な長寿命化を図ることができる。すなわち、活性炭を繰り返し使用することも簡単になる。
【図面の簡単な説明】
【図1】洗浄工程での排ガス処理を表す概念図である。
【図2】活性炭層再生工程でのガス処理を表す概念図である。
【符号の説明】
1 活性炭層
2 活性炭層
11 洗浄槽
12 加熱器
13 冷却凝縮器
14 真空ポンプ
15 溶剤再生装置[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a method and apparatus for treating exhaust gas for cleaning polychlorinated biphenyls (hereinafter referred to as “PCB”), and more particularly to a method and apparatus for treating exhaust gas generated by solvent cleaning of PCBs. .
[0002]
[Prior art]
PCBs have been produced and used as useful materials for heat transfer media, insulating oils for electrical equipment such as transformers and capacitors, carbonless paper, lubricating oils, various plasticizers, paints, sealant agents, and the like. PCBs are a concept including PCB and its derivatives. PCBs were affected by living things and the environment after the Kanemi oil affairs incident, etc., and production was discontinued by 1972. Manufacturing, importing, use for open systems, and new use by 1979 Forbidden. For closed-system applications, most of the PCBs for heat transfer media have been recovered since then, but PCBs for electrical equipment are still being used or stored by operators.
However, as the storage of used PCB electrical equipment has been prolonged, the risk of equipment loss / missing, PCB leakage, accidental leakage, etc. has increased. Already, according to a survey by the Ministry of Health and Welfare in 1993, about 7% are missing. PCBs are widely detected in the environment or in the living body, and it is suggested that they may enter the environment through various routes.
Therefore, early treatment of PCB waste is demanded globally. In Japan, high temperature pyrolysis treatment of liquid waste PCBs at Takasago Works, Kaneka Chemical Industry Co., Ltd. for about two years from November 1987 is required. The only exception is that no “PCB waste disposal” has been approved, and many other treatment facilities planned throughout the country have not been realized due to location problems.
In order to completely dispose of electrical equipment using PCBs, it is necessary to purify not only the filled insulating oil but also contaminants such as containers in which PCBs are adhered and impregnated. As a method for disposal or recycling of PCBs contaminants (waste plastics or metal scrap), a method for sufficiently removing PCBs using incineration and cleaning equipment is defined. As a criterion, 0.1 μg / 100 cm 2 is determined as the surface adhesion amount, or 0.01 mg / kg as the content, and this criterion is 100 times stricter than that in North America and the like.
[0003]
[Problems to be solved by the invention]
When “Method to sufficiently remove PCB using cleaning equipment” is used as the “disposal or recycling method for PCB contaminants”, waste cleaning agent is generated and heat drying or distillation cleaning of waste cleaning agent is performed. In addition, exhaust gas containing cleaning agent vapor is also generated. Normally, activated carbon is used for this exhaust gas treatment.
In this case, since the criteria for purification are strict in Japan, the amount of solvent used is inevitably increased, and the amount of exhaust gas generated and the amount of activated carbon used are also increased. At present, spent activated carbon containing PCBs must be stored because there are no authorized treatment / disposal methods and judgment criteria.
[0004]
In the case of using a solvent as a cleaning agent, in order to recover the solvent and reduce the amount of activated carbon used, in the exhaust gas treatment, a cooling condensation treatment is generally performed before the activated carbon treatment. Since the boiling point of the cleaning solvent is usually lower than that of PCBs, most of the non-condensed components contained in the gas after cooling and condensation are solvents, and the amount of PCBs is small. However, in many cases, since the cleaning solvent itself is also harmful, the activated carbon that has been broken through with the cleaning solvent must be replaced. Therefore, a large amount of used activated carbon with a slight amount of PCBs adsorbed under conventional use conditions.
Accordingly, the present invention provides a method and apparatus for treating PCB pollutant cleaning exhaust gas, which can regenerate the activated carbon at any time when the exhaust gas at the time of solvent cleaning of PCB pollutants is treated, and thereby extend the life as much as possible. The purpose is to provide.
[0005]
[Means for Solving the Problems]
(1) In a method for treating polychlorinated biphenyl pollutant cleaning exhaust gas having an activated carbon adsorption step in which polychlorinated biphenyl contaminants are washed with a solvent and the resulting polychlorinated biphenyls and the exhaust gas containing the solvent are guided to the activated carbon layer and adsorbed. The polychlorinated biphenyl adsorbed in the activated carbon adsorption step by stopping the supply of the exhaust gas to the activated carbon layer that was previously in the adsorption step among the two or more activated carbon layers arranged in parallel and depressurizing and / or heating the activated carbon layer A desorption step of desorbing the solvent out of the solvent and the solvent, and a step of cooling and condensing the desorbed gas containing the desorbed solvent and introducing the non-condensable substance to another activated carbon layer having adsorption ability Recycled polychlorinated biphenyl pollutant cleaning exhaust gas, which has an activated carbon layer that has been previously in the adsorption process, and regenerates the exhaust gas adsorption capacity Method of processing.
(2) The method for treating polychlorinated biphenyl pollutant cleaning exhaust gas according to (1), wherein the heating temperature of the activated carbon layer is 200 ° C. or less.
(3) Two or more activated carbon layers arranged in parallel for adsorbing the cleaning exhaust gas containing polychlorinated biphenyls and the solvent generated by washing the polychlorinated biphenyls with a solvent , and the activated carbon layer adsorbing the cleaning exhaust gas Of polychlorinated biphenyls adsorbed by heating and / or depressurizing and desorbing means for desorbing the solvent, and in the desorbed gas of the solvent desorbed from the activated carbon layer, a condensable substance The apparatus for treating exhaust gas for cleaning polychlorinated biphenyl pollutants, comprising: a cooling means for cooling and condensing; a separating means for separating the cooling condensate; and an activated carbon layer on which non-condensable substances are re-adsorbed.
(4) On the inlet side of each activated carbon layer, it is possible to switch between an inlet for cleaning exhaust gas of polychlorinated biphenyl contaminants and an inlet for gas containing uncooled condensate from the cooling means. The apparatus for treating exhaust gas for cleaning polychlorinated biphenyls contaminants according to (3), wherein the activated carbon layer is disposed so that an outlet of the activated carbon layer communicates with a cooling means.
[0006]
DETAILED DESCRIPTION OF THE INVENTION
When the activated carbon is depressurized or heated, the adsorption capacity decreases, so that the adsorbed material is desorbed. The desorption efficiency depends on the boiling point, vapor pressure, molecular weight, hydrophobicity, etc. of the adsorbed material. In order to completely desorb the adsorbed material and completely regenerate the activated carbon, a high temperature state of several hundred degrees or more and steam supply are required, but a low boiling point material such as a cleaning solvent is relatively easily desorbed. In carrying out the present invention, for example, the following apparatus may be used. 1 and 2 are diagrams showing examples of embodiments of the present invention. During cleaning and activated carbon regeneration, the piping connecting the plant equipment is switched by a valve and driven.
FIG. 1 shows an example of an exhaust gas treatment channel in a drying process at the time of cleaning. The cleaning tank 11 is supplied with the gas heated by the heater 12, and the exhaust gas from the cleaning tank 11 is cooled and condensed by the
FIG. 2 shows a gas flow path when the activated
Here, although the
[0007]
If it does in this way, the adsorption substance of activated
Since the remaining non-condensable components that cannot be removed by cooling condensation are removed by the activated
The regeneration of the activated
The gas used for the circulation may be air, but it is desirable to use an inert gas such as nitrogen in order to prevent the activated carbon from igniting and to prevent the adsorbed material from changing. There is no problem even if it is released into the atmosphere after completion of the cleaning process or the regeneration process, but it is more desirable to store it in a pressurized tank and reuse it when an inert gas is used.
Since the load applied to the activated carbon tank in the exhaust gas treatment process is desirably as small as possible, the cooling temperature is desirably as low as possible, specifically 0 ° C. or lower, more preferably −10 ° C. or lower.
In the above form, the cooling condenser and activated carbon of the cleaning exhaust gas treatment facility are diverted, but the cooling condenser and activated carbon that are set as a part of the process for treating the exhaust gas generated during the solvent cleaning treatment are new. A refrigerated condenser and activated carbon may be used. When diverting, it is not necessary to provide a new device separately, and there is an advantage that the number of devices can be reduced accordingly. This is particularly effective when performing solvent cleaning intermittently. When it is newly provided, there is an advantage that the activated carbon can be sucked and regenerated without being limited to the solvent cleaning situation.
[0008]
In order to prevent alteration / deterioration of the adsorbed low-boiling solvent, ignition of the activated carbon, etc., the heating temperature is preferably about 200 ° C. or lower when an additive gas is supplied as a carrier gas. When general air containing oxygen is present, it is desirable to keep the temperature at about 100 ° C. or lower.
Regeneration by vacuum suction in this embodiment does not completely regenerate the activated carbon, but eventually PCBs accumulate and are replaced. Nevertheless, the amount of used activated carbon can be significantly reduced.
The above-mentioned form employs the idea of sequentially regenerating two or more series of activated carbons on the spot. Such a method is used to purify groundwater contaminated with a volatile solvent such as TCE (trichloroethylene) PCE (tetraethylene). Two or more series of fibrous activated carbon is periodically regenerated with heated steam. Exhaust gas containing heated steam and volatile solvent during regeneration is cooled and condensed, and the volatile solvent and water are separated by a specific gravity difference. The water separated by the difference in specific gravity is discharged as water that does not contain harmful substances after further processing.
However, if the activated carbon containing PCBs is treated with heated steam, the heated PCB may be partially detached from the activated carbon, so that it is difficult to treat the water after condensation. Activated carbon needs to be used for wastewater treatment, and liquid phase adsorption has low adsorption efficiency.
[0009]
【The invention's effect】
Since the present invention is configured as described above, the activated carbon adsorbed with the gas containing the cleaning solvent and PCBs is regenerated as much as possible to independently recover the adsorption capacity, and the activated carbon can be efficiently extended in life. Can be planned. That is, it becomes easy to repeatedly use activated carbon.
[Brief description of the drawings]
FIG. 1 is a conceptual diagram showing exhaust gas treatment in a cleaning process.
FIG. 2 is a conceptual diagram showing gas treatment in an activated carbon layer regeneration step.
[Explanation of symbols]
DESCRIPTION OF
Claims (4)
Priority Applications (1)
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JP28700699A JP3925890B2 (en) | 1999-10-07 | 1999-10-07 | Method and apparatus for treating PCB-contaminated waste cleaning exhaust gas |
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JP28700699A JP3925890B2 (en) | 1999-10-07 | 1999-10-07 | Method and apparatus for treating PCB-contaminated waste cleaning exhaust gas |
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JP3925890B2 true JP3925890B2 (en) | 2007-06-06 |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103089488A (en) * | 2013-01-21 | 2013-05-08 | 北京航空航天大学 | Adjustable cavitation venturi tube for high concentration hydrogen peroxide |
CN103877935A (en) * | 2014-04-10 | 2014-06-25 | 北京爱美客生物科技有限公司 | Strong alkaline type anion activated carbon adsorbent as well as preparation method and application thereof |
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JP7055556B2 (en) * | 2018-02-08 | 2022-04-18 | ダイダン株式会社 | Activated carbon performance recovery possibility judgment method, activated carbon regeneration method, and activated carbon reuse system |
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1999
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Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103089488A (en) * | 2013-01-21 | 2013-05-08 | 北京航空航天大学 | Adjustable cavitation venturi tube for high concentration hydrogen peroxide |
CN103877935A (en) * | 2014-04-10 | 2014-06-25 | 北京爱美客生物科技有限公司 | Strong alkaline type anion activated carbon adsorbent as well as preparation method and application thereof |
CN103877935B (en) * | 2014-04-10 | 2015-11-18 | 北京爱美客生物科技有限公司 | Strong base anion acticarbon and its preparation method and application |
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JP2001104749A (en) | 2001-04-17 |
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