JP4022267B2 - PCB waste detoxification and product recycling - Google Patents

PCB waste detoxification and product recycling Download PDF

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Publication number
JP4022267B2
JP4022267B2 JP24049494A JP24049494A JP4022267B2 JP 4022267 B2 JP4022267 B2 JP 4022267B2 JP 24049494 A JP24049494 A JP 24049494A JP 24049494 A JP24049494 A JP 24049494A JP 4022267 B2 JP4022267 B2 JP 4022267B2
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Japan
Prior art keywords
biphenyl
pcb
sodium
chlorine
aqueous solution
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.)
Expired - Lifetime
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JP24049494A
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Japanese (ja)
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JPH0866494A (en
Inventor
亨 久保田
Original Assignee
亨 久保田
高原 貞夫
菊地 武志
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Priority to JP24049494A priority Critical patent/JP4022267B2/en
Publication of JPH0866494A publication Critical patent/JPH0866494A/en
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Description

【0001】
【産業上の利用分野】
本発明は水酸化ナトリウムの水溶液で処理するPCB廃棄物の無害化処理方法とそれによる生成物の再利用法に関するもので、特に有害なPCBをビフェニルナトリウムに置換し、さらに加水分解によりビフェニルとして再利用すると共に塩化ナトリウムを含む沈殿物は焼却灰と共に固化処理することを特徴とするPCB廃棄物の処理方法に関するものである。
【0002】
【従来の技術】
PCBは有機塩素化合物であり、ポリ・クロリネーテッド・ビフェニルの略称である。ベンゼン環の水素原子がそれぞれ1個ずつとれて2個のベンゼン環が結合したものをビフェニルと云いビフェニルは塩素を含まない炭化水素なので燃料にすることもできる。このビフェニルに塩素が水素と置換されることにより有害な塩素化合物ができるのであり、塩素の数や位置により種々の性質を示すことになる。
【0003】
従来PCBは移動禁止の有害物質として国で管理保管されている。また最近温度1800℃の高温にて酸化熱分解する方法が提案されているが、PCBは熱に強く、うっかり低温で酸化熱分解を行うとPCBよりもっと有毒なダイオキシンが発生、環境を更に破壊することからも知られるように今日まで完全なる処理方法は知られていない。
【0004】
【発明が解決しようとする課題】
熱分解されたPCBの問題点は、PCBに含有されている塩素原子が酸化作用により有害塩素化合物として気体に分解され、大気汚染されることである。このように有害成分を含む気体を大気中に排出することは環境に悪影響を与える。従って有害な塩素化合物を無害な無機塩素化合物にして、有害物が溶出しない処理を施した上で廃棄しなければならない。
【0005】
本発明は、PCBを無機塩素化合物に分解する方法に係るものであり、該無機塩素化合物を焼却灰と共にセメントで固化処理することを可能とし、それによって得られる固化生成物及びビフェニルの再利用を目的とするものである。
【0006】
【課題を解決するための手段】
本発明は有機塩素化合物を無水炭酸ナトリウム、酸化カリウム、窒素、硼素、カルシウム等のイオン水溶液と攪拌、コロイド状となった時、溶媒としてジエチルエーテルとエタノールを混入、110℃の温度で加熱した後撹拌を更に続けながら触媒として塩化コバルト、木酢を加えて攪拌し、最後に水酸化ナトリウム水溶液を混入撹拌することにより無機塩素化合物とビフェニルを生成させるものでそれによって焼却灰セメントによる安定固化物と、塩素の含まれないビフェニルを得るものである。
【0007】
すなわち本発明のPCB安定処理方法はベンゼン環の水素原子と塩素原子の置換により生成された、有機塩素化合物の塩素原子をナトリウム原子の置換によりビフェニル化合物と塩素化合物に分解、更に必要に応じてビフェニルナトリウムを加水分解することによって、ビフェニルと苛性ソーダとするものである。ビフェニルナトリウム及びビフェニルが生成される反応の一部を簡略化して図示すると以下の通りである。
【0008】
【化1】
【0009】
【実施例】
以下に本発明の実施例を示すが、本発明はこの実施例によって限定されるのでなく、これらの実施例は単に本発明の理解を助けるものに過ぎないものであることは当然理解されなければならない。
【0010】
実施例1
二酸化珪素SiO 2.1%、ふっ化水素HF 0.3%、酸化カルシウムCaO 3.2%、無水炭酸ナトリウムNaCO 7.3%、酸化アルミニウムAl 1.7%、無水硼酸B 1.3%、酸化カリウムKO2.1%、アンモニアNH3 1.0%、食塩NaCl 1.0%、塩化コバルトCoCl・6HO 0.3%、酸化第二鉄Fe 0.2%、木酢酸鉄液2% 、エチレンジアミンNHCHCHNH 1%、PCB4000cc(トランス油)にエタノールC・OH 40cc、ジエチルエーテルC−O−C 80ccを混合して30分攪拌する。攪拌したものを110℃に加熱、上記の主原料と副原料を攪拌したものを250cc混合攪拌する。
【0011】
最後に水酸化ナトリウム50gを100ccの水に溶かして、PCB混合溶液に混合攪拌する。24時間後、ビフェニルは上層に溶剤下層に沈殿物の二層に分かれる。この溶媒抽出法により、ビフェニルを抽出した。下層に沈殿した沈殿物を焼却灰と共にセメントで固化して得た固化物について溶出試験を行った。溶出試験はPCBについてのみ行った。結果は表1及び2に示すようにN.D.mg/lとPCBを検出できなかった。
【0012】
【表1】
【0013】
【表2】
【0014】
【発明の効果】
表1・2の結果からも知られるように、本発明の方法によって処理された焼却灰による固化生成物にはPCBを検出することができなかった。また、副生成物として燃料(ビフェニル)を得ることができる。
[0001]
[Industrial application fields]
The present invention relates to a method for detoxifying PCB waste treated with an aqueous solution of sodium hydroxide and a method for reusing the resulting product. In particular, this method replaces harmful PCB with biphenyl sodium and recycles it as biphenyl by hydrolysis. The present invention relates to a method for treating PCB waste, characterized in that a precipitate containing sodium chloride is solidified with incinerated ash.
[0002]
[Prior art]
PCB is an organochlorine compound and is an abbreviation for poly chlorinated biphenyl. Biphenyl is a combination of two benzene rings bonded to each hydrogen atom of the benzene ring. Biphenyl is a hydrocarbon that does not contain chlorine and can be used as a fuel. By replacing chlorine with hydrogen in this biphenyl, a harmful chlorine compound is produced, and various properties are exhibited depending on the number and position of chlorine.
[0003]
Conventionally, PCBs are managed and stored in the country as hazardous substances prohibited from movement. Recently, a method of oxidative pyrolysis at a high temperature of 1800 ° C has been proposed, but PCB is resistant to heat, and if oxidative pyrolysis is inadvertently performed at low temperature, more toxic dioxins are generated than PCB and the environment is further destroyed. As is known from the above, a complete processing method is not known to date.
[0004]
[Problems to be solved by the invention]
The problem with thermally decomposed PCBs is that chlorine atoms contained in the PCB are decomposed into gases as harmful chlorine compounds by oxidation and are polluted into the air. Thus, discharging a gas containing harmful components into the atmosphere has an adverse effect on the environment. Therefore, harmful chlorine compounds must be made harmless inorganic chlorine compounds, treated after which no harmful substances are eluted, and discarded.
[0005]
The present invention relates to a method for decomposing PCBs into inorganic chlorine compounds and the like , and enables the inorganic chlorine compounds to be solidified with cement together with incinerated ash, and reuse of the solidified product and biphenyl obtained thereby. It is intended.
[0006]
[Means for Solving the Problems]
In the present invention, an organic chlorine compound is stirred with an aqueous ionic solution of anhydrous sodium carbonate, potassium oxide, nitrogen, boron, calcium, etc., and when colloidal, diethyl ether and ethanol are mixed as a solvent and heated at a temperature of 110 ° C. While further stirring, cobalt chloride and pyroligneous acid are added as a catalyst and stirred. Finally, an aqueous sodium hydroxide solution is mixed and stirred to produce an inorganic chlorine compound and biphenyl, thereby stabilizing and solidifying the incinerated ash cement, Biphenyl containing no chlorine is obtained.
[0007]
That is, the PCB stabilizing treatment method of the present invention decomposes a chlorine atom of an organic chlorine compound, which is generated by substitution of a hydrogen atom and a chlorine atom of a benzene ring, into a biphenyl compound and a chlorine compound by substitution of a sodium atom , and further, if necessary, biphenyl. By hydrolyzing sodium, biphenyl and caustic soda are obtained. A part of the reaction for producing biphenyl sodium and biphenyl is simplified and illustrated as follows.
[0008]
[Chemical 1]
[0009]
【Example】
Examples of the present invention will be shown below, but the present invention is not limited to these examples, and it should be understood that these examples are merely to help the understanding of the present invention. Don't be.
[0010]
Example 1
Silicon dioxide SiO 2 2.1%, hydrogen fluoride HF 0.3%, calcium oxide CaO 3.2%, anhydrous sodium carbonate Na 2 CO 3 7.3%, aluminum oxide Al 2 O 3 1.7%, anhydrous boric acid B 2 O 3 1.3%, 2 O2.1% potassium oxide K, ammonia NH3 1.0%, 1.0% sodium chloride NaCl, cobalt chloride CoCl 2 · 6H 2 O 0.3% , ferric oxide Fe 2 O 3 0.2%, wood pyroacetate 2%, ethylenediamine NH 2 CH 2 CH 2 NH 3 1%, PCB 4000 cc ( trans oil ), ethanol C 2 H 5 .OH 40 cc, diethyl ether C 2 H 5 − Mix 80 cc of O—C 2 H 5 and stir for 30 minutes. The agitated material is heated to 110 ° C., and the agitated main raw material and auxiliary raw material are mixed and stirred for 250 cc.
[0011]
Finally, 50 g of sodium hydroxide is dissolved in 100 cc of water, and mixed and stirred in the PCB mixed solution. After 24 hours, the biphenyl splits into two layers, the upper layer and the lower solvent layer. Biphenyl was extracted by this solvent extraction method. An elution test was conducted on the solidified product obtained by solidifying the sediment precipitated in the lower layer with cement together with incineration ash. The dissolution test was performed only on PCB. The results are shown in Tables 1 and 2. D. mg / l and PCB could not be detected.
[0012]
[Table 1]
[0013]
[Table 2]
[0014]
【The invention's effect】
As can be seen from the results in Tables 1 and 2, PCB could not be detected in the solidified product of incinerated ash treated by the method of the present invention. Moreover, a fuel (biphenyl) can be obtained as a by-product.

Claims (3)

PCBを触媒及び溶媒と共に水酸化ナトリウムの水溶液で処理することによってビフェニルナトリウムと塩化ナトリウムに分解することを特徴とするPCBの処理方法で、上記触媒が塩化コバルト、酸化第二鉄、エチレンジアミン、木酢、上記溶媒がエタノール、ジエチルエーテルから選ばれるものであるPCBの処理方法。 The PCB is decomposed into sodium biphenyl and sodium chloride by treating the PCB with an aqueous solution of sodium hydroxide together with a catalyst and a solvent , wherein the catalyst is cobalt chloride, ferric oxide, ethylenediamine, wood vinegar, A method for treating PCB, wherein the solvent is selected from ethanol and diethyl ether. ビフェニルナトリウムを加熱してビフェニルに加水分解する請求項1の方法。  2. The process of claim 1 wherein biphenyl sodium is heated to hydrolyze to biphenyl. 水酸化ナトリウム水溶液での処理がナトリウム以外にカリウム、カルシウム、アルミニウム、弗素、珪素、硼素等の複数種類のイオンを含んだ水溶液で処理するものである請求項1の方法。2. The method according to claim 1, wherein the treatment with an aqueous solution of sodium hydroxide comprises treatment with an aqueous solution containing a plurality of types of ions such as potassium, calcium, aluminum, fluorine, silicon and boron in addition to sodium.
JP24049494A 1994-08-29 1994-08-29 PCB waste detoxification and product recycling Expired - Lifetime JP4022267B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP24049494A JP4022267B2 (en) 1994-08-29 1994-08-29 PCB waste detoxification and product recycling

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP24049494A JP4022267B2 (en) 1994-08-29 1994-08-29 PCB waste detoxification and product recycling

Publications (2)

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JP4022267B2 true JP4022267B2 (en) 2007-12-12

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Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH1024276A (en) * 1996-07-10 1998-01-27 Toyohisa Eto Method for making harmful waste harmless and treating agent for making harmless used for method thereof
DE19903986A1 (en) * 1999-02-02 2000-08-10 Friedrich Boelsing Reductive dehalogenation of halohydrocarbons under mild conditions, e.g. for removing toxic chloroaromatic compounds from waste oil or soil, using reducing metal in presence of amine

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