JP3730251B2 - Purification method and apparatus for solid substances contaminated with organic halogen compounds - Google Patents

Purification method and apparatus for solid substances contaminated with organic halogen compounds Download PDF

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JP3730251B2
JP3730251B2 JP2004310559A JP2004310559A JP3730251B2 JP 3730251 B2 JP3730251 B2 JP 3730251B2 JP 2004310559 A JP2004310559 A JP 2004310559A JP 2004310559 A JP2004310559 A JP 2004310559A JP 3730251 B2 JP3730251 B2 JP 3730251B2
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organic halogen
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隆夫 川井
勉 中西
嘉雄 小西
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Shinko Pantec Co Ltd
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Kobelco Eco Solutions Co Ltd
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Description

本発明は、有機ハロゲン化合物で汚染された固形物の浄化方法とその装置、さらに詳しくは、ポリ塩化ビフェニル、ダイオキシン、農薬等の有機ハロゲン化合物で汚染された土壌や汚泥等の固形物を浄化して無害化するための浄化方法と装置に関する。   The present invention relates to a method and apparatus for purifying solids contaminated with organic halogen compounds, and more particularly, to purify solids such as soil and sludge contaminated with organic halogen compounds such as polychlorinated biphenyls, dioxins and agricultural chemicals. The present invention relates to a purification method and an apparatus for detoxifying and detoxifying.

周知のように、有機ハロゲン化合物の一種であるポリ塩化ビフェニルは非常に安定で分解され難く、しかも絶縁性(電気抵抗)が高いことから、従前においては変圧器やコンデンサー等の絶縁材料や熱媒体或いはカーボンレス複写紙等に用いられていたが、現在では環境上の理由から使用が禁止されている。しかし、従前から用いられていたものが残存する等、現在でも土壌や汚泥等の固形物中に微量成分として残存している場合があり、これらをどのように分解,処理するかは重要な課題となっている。   As is well known, polychlorinated biphenyl, a kind of organic halogen compound, is very stable and difficult to be decomposed, and has high insulation (electrical resistance), so in the past, insulation materials such as transformers and capacitors, and heat media Or it was used for carbonless copy paper, but now it is prohibited to use for environmental reasons. However, there are cases where traces remain in solids such as soil and sludge even if they have been used for some time, and how to decompose and treat them is an important issue. It has become.

また、近年では、ダイオキシン等の有機ハロゲン化合物も環境破壊や安全性の観点から、その処理が問題となっており、このようなダイオキシンも土壌や汚泥等の固形物中に微量成分として残存している場合がある。   In recent years, the treatment of organic halogen compounds such as dioxins has also become a problem from the viewpoint of environmental destruction and safety, and such dioxins also remain as trace components in solids such as soil and sludge. There may be.

このような有機ハロゲン化合物で汚染された汚染物を浄化する方法として、浄化対象物を300 〜400 ℃以上に加熱し、酸素を送り込んで燃焼させる熱分解法、有機ハロゲン化合物の蒸発温度以上(たとえば300 ℃以上)に加熱し、蒸発させた後に冷却する熱脱着法、300 〜400 ℃以上に加熱し、主としてNaOHやKOH等のアルカリ化合物を加え、炭化水素系溶媒の存在下で有機ハロゲン化合物の無害化を図る化学的な方法(BCD法)等が行われている。   As a method for purifying contaminants contaminated with such an organic halogen compound, a thermal decomposition method in which the object to be purified is heated to 300 to 400 ° C. or more and oxygen is supplied for combustion, or a temperature higher than the evaporation temperature of the organic halogen compound (for example, 300 ° C. or higher), evaporating and then cooling, heat desorption method, heating to 300 to 400 ° C. or higher, mainly adding an alkaline compound such as NaOH or KOH, and in the presence of a hydrocarbon solvent, A chemical method (BCD method) for detoxification is performed.

しかし、いずれの方法も高温で加熱されるため、その加熱により有機ハロゲン化合物が蒸発することとなり、その結果、周辺の環境に及ぼす影響が無視できず、環境破壊をもたらすという問題点があった。このような有機ハロゲン化合物の飛散を防止することも不可能ではないが、そのために大がかりな装置が必要となっていた。また、いずれの方法も高温で処理されるので、多大な熱エネルギーを要することとなっていた。   However, since both methods are heated at a high temperature, the organic halogen compound is evaporated by the heating. As a result, there is a problem that the influence on the surrounding environment cannot be ignored and the environment is destroyed. Although it is not impossible to prevent such scattering of the organic halogen compound, a large-scale apparatus is required for that purpose. In addition, since any method is processed at a high temperature, a great amount of heat energy is required.

本発明は、このような問題点を解決するためになされたもので、浄化のための処理温度を有機ハロゲン化合物の蒸気圧以下に下げることが可能であり、それによって有機ハロゲン化合物の飛散による周辺の環境破壊を防止することを課題とする。   The present invention has been made in order to solve such problems, and it is possible to lower the treatment temperature for purification below the vapor pressure of the organic halogen compound, thereby preventing the surroundings due to the scattering of the organic halogen compound. The issue is to prevent environmental destruction.

本発明は、このような課題を解決するために、有機ハロゲン化合物で汚染された固形物の浄化方法とその装置としてなされたもので、浄化方法としての特徴は、有機ハロゲン化合物で汚染された固形物中の水分を減圧蒸留によって除去した後、該有機ハロゲン化合物で汚染された固形物にアルカリ金属を添加し、有機ハロゲン化合物を分解処理して固形物を浄化することである。 In order to solve such problems, the present invention has been made as a purification method and apparatus for a solid substance contaminated with an organic halogen compound. The purification method is characterized by a solid substance contaminated with an organic halogen compound. After removing moisture in the product by distillation under reduced pressure , an alkali metal is added to the solid material contaminated with the organic halogen compound, and the organic halogen compound is decomposed to purify the solid material.

また、浄化装置としての特徴は、有機ハロゲン化合物で汚染された固形物を供給するとともに、アルカリ金属を添加して、固形物中の有機ハロゲン化合物とアルカリ金属とを反応させる反応装置1と、該反応装置1で固形物中の有機ハロゲン化合物とアルカリ金属とを反応させる前に予め固形物中の水分を除去するための水分除去装置とが具備されてなることである。   The purification device is characterized by supplying a solid substance contaminated with an organic halogen compound and adding an alkali metal to react the organic halogen compound in the solid substance with the alkali metal, Before the reaction apparatus 1 reacts the organic halogen compound and the alkali metal in the solid with each other, a water removal apparatus for removing the water in the solid is provided.

固形物中の水分を除去する水分除去装置としては、減圧蒸留を行う蒸留装置2が用いられる。 The water removal apparatus for removing moisture solids in the distillation apparatus 2 is used to perform the reduced pressure distillation.

本発明においては、常温以上好ましくは60℃以上200 ℃以下の加熱温度で反応する金属ナトリウム等のアルカリ金属を、有機ハロゲン化合物を含有する土壌、汚泥等の固形物に添加するため、沸点が上記温度よりはるかに高いポリ塩化ビフェニルやダイオキシン等の有機ハロゲン化合物が蒸発するおそれがなく、従って、周辺の環境に影響を及ぼすこともなく、環境破壊をもたらすこともないという効果がある。   In the present invention, an alkali metal such as sodium metal that reacts at a heating temperature of normal temperature or higher, preferably 60 ° C. or higher and 200 ° C. or lower, is added to solids such as soil and sludge containing organic halogen compounds, so that the boiling point is the above. There is no possibility that organic halogen compounds such as polychlorinated biphenyl and dioxin which are much higher than the temperature will evaporate, and therefore there is an effect that the surrounding environment is not affected and the environment is not destroyed.

この結果、従来のように、蒸発する有機ハロゲン化合物を捕獲するための大がかりな装置を設ける必要もなく、設備を小型化することができるという効果がある。   As a result, there is no need to provide a large-scale device for capturing the evaporated organic halogen compound as in the conventional case, and there is an effect that the facility can be reduced in size.

また、従来の方法に比べて低い温度で処理することができるので、従来のように多大な熱エネルギーを要することもない。   Moreover, since it can process at low temperature compared with the conventional method, much heat energy is not required unlike the past.

さらに、固形物にアルカリ金属を添加する前に、予め固形物中の水分を除去するので、金属ナトリウムが土壌中の水分と反応して苛性ソーダになるおそれもなく、金属ナトリウムとポリ塩化ビフェニル等の有機ハロゲン化合物との反応に支障を生ずることもないという効果がある。   Furthermore, since the moisture in the solid is removed in advance before adding the alkali metal to the solid, there is no possibility that the sodium metal reacts with the moisture in the soil to become caustic soda, such as sodium metal and polychlorinated biphenyl. There is an effect that the reaction with the organic halogen compound is not hindered.

以下、本発明の実施形態について、図面に従って説明する。
先ず、一実施形態としての、有機ハロゲン化合物で汚染された固形物の浄化装置について説明する。
Hereinafter, embodiments of the present invention will be described with reference to the drawings.
First, a solid purification device contaminated with an organic halogen compound as one embodiment will be described.

図1において、1は、有機ハロゲン化合物の一例としてのポリ塩化ビフェニルを含有する土壌を供給するとともに、金属ナトリウムの粉末を絶縁油に分散させたナトリウム分散剤を添加して、ポリ塩化ビフェニルと金属ナトリウムを反応させるための反応装置で、この反応装置1には、さらに反応促進物質であるイソプロピルアルコールが添加される。   In FIG. 1, 1 supplies a soil containing polychlorinated biphenyl as an example of an organic halogen compound, and also adds a sodium dispersant in which metal sodium powder is dispersed in insulating oil, so that polychlorinated biphenyl and metal are added. In this reaction apparatus 1 for reacting sodium, isopropyl alcohol which is a reaction promoting substance is further added.

2は、ナトリウム分散剤が添加される前に、予め土壌中の水分を減圧蒸留で除去するための蒸留装置で、前記反応装置1の前段に設けられている。3は、前記蒸留装置2で除去された水分を活性炭で吸着するための吸着装置を示す。   2 is a distillation apparatus for removing moisture in the soil in advance by vacuum distillation before the sodium dispersant is added, and is provided in the preceding stage of the reaction apparatus 1. 3 shows an adsorption device for adsorbing the water removed by the distillation device 2 with activated carbon.

4は、前記反応装置1で添加されたナトリウム分散剤のうち、未反応のナトリウム分散剤を土壌から分離するための分離装置で、その分離されたナトリウム分散剤を前記反応装置1へ返送するための返送ライン5が、該反応装置1と前記分離装置4とに接続されている。   4 is a separator for separating unreacted sodium dispersant from the soil among the sodium dispersant added in the reactor 1, and for returning the separated sodium dispersant to the reactor 1. The return line 5 is connected to the reactor 1 and the separator 4.

6は、ナトリウム分散剤を分離した後の土壌からイソプロピルアルコールを減圧蒸留で分離するための蒸留装置で、その分離されたイソプロピルアルコールを前記反応装置1へ返送するための返送ライン7が、該反応装置1と前記蒸留装置6とに接続されている。   6 is a distillation apparatus for separating isopropyl alcohol from the soil after separating the sodium dispersant by vacuum distillation, and a return line 7 for returning the separated isopropyl alcohol to the reaction apparatus 1 comprises the reaction The apparatus 1 and the distillation apparatus 6 are connected.

次に、このような浄化装置を用いて、有機ハロゲン化合物で汚染された固形物の浄化する方法を、図1及び図2に従って説明する。   Next, a method for purifying a solid substance contaminated with an organic halogen compound using such a purification apparatus will be described with reference to FIGS.

先ず、ポリ塩化ビフェニルを含有する汚染土壌を蒸留装置2へ供給し、その蒸留装置2で土壌を減圧蒸留する。これによって、土壌中の水分が蒸発して一定量の水分が除去されることとなる。   First, contaminated soil containing polychlorinated biphenyl is supplied to the distillation apparatus 2, and the soil is distilled under reduced pressure by the distillation apparatus 2. As a result, moisture in the soil evaporates and a certain amount of moisture is removed.

すなわち、土壌中に水分が多量が含有されていると、後に添加される金属ナトリウムが土壌中の水分と反応して苛性ソーダになるおそれがあり、金属ナトリウムとポリ塩化ビフェニルとの反応に支障を生ずるおそれがあるため、上記減圧蒸留によって予め水分が除去されるのである。除去された水蒸気は、吸着装置3の活性炭で吸着して処理される。   In other words, if the soil contains a large amount of water, metal sodium added later may react with the water in the soil to become caustic soda, which hinders the reaction between metal sodium and polychlorinated biphenyl. Since there exists a possibility, a water | moisture content is previously removed by the said vacuum distillation. The removed water vapor is adsorbed by the activated carbon of the adsorption device 3 and processed.

次に、減圧蒸留後の土壌を反応装置1へ供給し、約100 ℃で加熱した状態で、反応装置1に金属ナトリウムの粉末を絶縁油に分散させたナトリウム分散剤を添加し、さらにイソプロピルアルコールを添加する。これによって、土壌中のポリ塩化ビフェニルとナトリウム分散剤中の金属ナトリウムとが反応し、ポリ塩化ビフェニルが脱塩素化されることとなる。また、イソプロピルアルコールが添加されることにより、ポリ塩化ビフェニルと金属ナトリウムとの反応が促進されることとなる。   Next, the soil after vacuum distillation is supplied to the reactor 1 and heated at about 100 ° C., a sodium dispersant in which metal sodium powder is dispersed in insulating oil is added to the reactor 1, and isopropyl alcohol is further added. Add. As a result, polychlorinated biphenyl in the soil reacts with metallic sodium in the sodium dispersant to dechlorinate the polychlorinated biphenyl. Further, by adding isopropyl alcohol, the reaction between polychlorinated biphenyl and metallic sodium is promoted.

さらに、土壌に含有されているポリ塩化ビフェニルは、一般に絶縁油に含まれているため、上述のように添加するアルカリ金属を絶縁油に分散させることで親和性が向上し、アルカリ金属と有機ハロゲン化合物との反応がより確実に行われることとなる。   Furthermore, since polychlorinated biphenyl contained in soil is generally contained in insulating oil, the affinity is improved by dispersing the alkali metal added in the insulating oil as described above. The reaction with the compound will be carried out more reliably.

上記のような反応後、土壌は分離装置4へ供給され、その分離装置でナトリウム分散剤のみが分離され、返送ライン5を介して前記反応装置1へ返送される。この分離後のナトリウム分散剤は未反応のものであり、上記反応装置1に返送されて再利用されることとなるのである。一方、分離後の土壌は蒸留装置6へ供給され、その蒸留装置6で減圧蒸留されてイソプロピルアルコールが分離される。この減圧蒸留の際に分離されたイソプロピルアルコールは、返送ライン7を介して前記反応装置1へ返送される。   After the reaction as described above, the soil is supplied to the separation device 4, and only the sodium dispersant is separated by the separation device and is returned to the reaction device 1 through the return line 5. The sodium dispersant after the separation is unreacted and is returned to the reactor 1 for reuse. On the other hand, the separated soil is supplied to the distillation apparatus 6 and is distilled under reduced pressure by the distillation apparatus 6 to separate isopropyl alcohol. The isopropyl alcohol separated in this vacuum distillation is returned to the reaction apparatus 1 via the return line 7.

このイソプロピルアルコールは反応装置1へ返送されて、ポリ塩化ビフェニルと金属ナトリウムとの反応促進剤として再利用されるのである。蒸留装置で分離された土壌は、無害化された乾燥物として得られることとなる。   This isopropyl alcohol is returned to the reactor 1 and reused as a reaction accelerator between polychlorinated biphenyl and metallic sodium. The soil separated by the distillation apparatus will be obtained as a detoxified dry matter.

以上のように、本実施形態においては、金属ナトリウムの粉末を絶縁油に分散させたナトリウム分散剤をポリ塩化ビフェニルと反応させてポリ塩化ビフェニルを脱塩素化処理するため、金属ナトリウムが反応する温度である常温以上好ましくは60℃以上200 ℃以下の範囲で処理できることとなり、従って沸点が約300 度であるポリ塩化ビフェニルが蒸発して土壌から飛散することがなく、周辺に影響を及ぼすこともないのである。   As described above, in the present embodiment, the sodium dispersant in which metallic sodium powder is dispersed in insulating oil is reacted with polychlorinated biphenyl to dechlorinate polychlorinated biphenyl. The polychlorinated biphenyl having a boiling point of about 300 degrees is not evaporated and scattered from the soil and does not affect the surroundings. It is.

(実施例)
PCBについて反応装置での分解処理を行う際の温度を、常温、60℃、75℃、90℃、110 ℃に変えて、それぞれ残留PCB率の経時変化を試験した。ここで、残留PCB率は次式で示される。
残留PCB率(%)=(反応後PCB濃度)/(反応前PCB濃度)×100
(Example)
The PCB was subjected to a decomposition treatment in the reactor at room temperature, 60 ° C., 75 ° C., 90 ° C., and 110 ° C., and the changes in the residual PCB rate over time were tested. Here, the residual PCB rate is expressed by the following equation.
Residual PCB rate (%) = (post-reaction PCB concentration) / (pre-reaction PCB concentration) × 100

尚、PCBの初期濃度は360ppmで行った。試験結果を図3に示す。図3からも明らかなように、110 ℃では約5分でPCBが完全に分解し、90℃では約10分で完全に分解し、75分では約15分で分解し、60℃では約95分で分解した。   The initial PCB concentration was 360 ppm. The test results are shown in FIG. As is apparent from FIG. 3, PCB is completely decomposed in about 5 minutes at 110 ° C., completely decomposed in about 10 minutes at 90 ° C., decomposed in about 15 minutes at 75 minutes, and about 95 at 60 ° C. Decomposed in minutes.

常温でも、残留PCB率は約120 時間で約75%まで低減することができ、常温でもPCBの分解反応が可能であることが確認できた。これらより、常温でも分解処理は可能であるが、処理にかかる時間を考慮すると、60℃以上で処理するのが好ましい。また、処理温度を高くすると、短時間に処理できるようになるが、200 ℃を超えるとPCBの蒸発が顕著になるため、200 ℃以下で分解処理を行うのが好ましい。   Even at room temperature, the residual PCB rate could be reduced to about 75% in about 120 hours, and it was confirmed that the PCB decomposition reaction was possible even at room temperature. From these, decomposition treatment is possible even at room temperature, but it is preferable to perform the treatment at 60 ° C. or higher in consideration of the time required for the treatment. In addition, if the treatment temperature is increased, the treatment can be performed in a short time. However, if the temperature exceeds 200 ° C., the PCB will evaporate significantly. Therefore, the decomposition treatment is preferably performed at 200 ° C. or less.

尚、上記実施形態で用いた金属ナトリウムは安価で一般的に入手し易い利点があるが、これに限らず、金属カリウム、金属ストロンチウム、金属リチウムやその合金を用いることも可能である。要は、アルカリ金属を油等の分散媒に分散させた分散剤が用いられればよいのである。   The metal sodium used in the above embodiment has an advantage that it is inexpensive and generally easily available. However, the present invention is not limited to this, and metal potassium, metal strontium, metal lithium and alloys thereof can also be used. The point is that a dispersant in which an alkali metal is dispersed in a dispersion medium such as oil may be used.

また、該実施形態では、反応促進剤としてイソプロピルアルコールを用い、このイソプロピルアルコールは官能基(反応基)が多く、低粘度のため反応性に優れていること、消毒薬等の医薬品に使用されるため安全性に優れていること、生物分解性があること等の利点があるが、反応促進剤の種類はこれに限定されるものではなく、たとえばエタノールやメタノール等を用いることも可能である。   Further, in this embodiment, isopropyl alcohol is used as a reaction accelerator, and this isopropyl alcohol has many functional groups (reactive groups) and is excellent in reactivity due to low viscosity, and is used for pharmaceuticals such as disinfectants. Therefore, there are advantages such as excellent safety and biodegradability, but the type of reaction accelerator is not limited to this, and ethanol, methanol, and the like can also be used, for example.

さらに、上記実施形態では、分離後のナトリウム分散剤や蒸留後のイソプロピルアルコールを返送したため、これらを再利用できるという利点が得られたが、このように返送して再利用することも本発明に必須の条件ではない。   Furthermore, in the above embodiment, since the sodium dispersant after separation and the isopropyl alcohol after distillation are returned, there is an advantage that they can be reused. However, such return and reuse are also included in the present invention. This is not a requirement.

さらに、上記実施形態では、金属ナトリウムを絶縁油等の分散媒に分散させたため、親和性が向上し、アルカリ金属と有機ハロゲン化合物との反応がより確実に行われるという好ましい効果が得られたが、このような分散媒に分散させることは本発明に必須の条件ではない。   Furthermore, in the above embodiment, since metallic sodium is dispersed in a dispersion medium such as insulating oil, the affinity is improved, and a favorable effect that the reaction between the alkali metal and the organic halogen compound is performed more reliably is obtained. The dispersion in such a dispersion medium is not an essential condition for the present invention.

これ以外にも、アルカリ金属を添加した土壌等の固形物をアルカリ金属の融点以上に加熱しながら攪拌する方法や、粉砕混合する方法、アルカリ金属の蒸気を固形物にあてる方法によって被処理物中にナトリウムを分散させることも可能である。   In addition to this, the solid material such as soil to which alkali metal has been added is heated in the object to be treated by the method of stirring while heating above the melting point of the alkali metal, the method of pulverizing and mixing, or the method of applying alkali metal vapor to the solid material. It is also possible to disperse sodium.

さらに、上記実施例では、ポリ塩化ビフェニルを処理する場合について説明したが、処理すべき有機ハロゲン化合物の種類も、上記実施例のポリ塩化ビフェニルに限定されるものではなく、たとえばダイオキシンのようなものであってもよい。また、DDTやBHC等の農薬類であってもよい。要は、処理すべき土壌に有機ハロゲン化合物が含有されていればよいのである。   Furthermore, in the above embodiment, the case where polychlorinated biphenyl is treated has been described. However, the type of the organic halogen compound to be treated is not limited to the polychlorinated biphenyl of the above embodiment, for example, dioxin. It may be. Moreover, pesticides, such as DDT and BHC, may be sufficient. In short, it is only necessary that the soil to be treated contains an organic halogen compound.

さらに、上記実施例では、有機ハロゲン化合物を含有する土壌を処理する場合について説明したが、土壌に限らず、たとえば有機ハロゲン化合物を含有する汚泥を処理する場合に本発明を適用することも可能である。さらに、有機ハロゲン化合物が付着した容器類や布地等の処理に本発明を適用することも可能である。要は、有機ハロゲン化合物が含有され、或いは付着等されることによって汚染された固形物であれば、本発明を適用することが可能である。   Furthermore, although the said Example demonstrated the case where the soil containing an organic halogen compound was processed, it is also possible to apply this invention when processing not only soil but the sludge containing an organic halogen compound, for example. is there. Furthermore, the present invention can also be applied to the treatment of containers, fabrics and the like to which organic halogen compounds are attached. In short, the present invention can be applied to any solid matter containing an organic halogen compound or contaminated by adhering to it.

一実施例としての固形物の浄化装置の概略ブロック図。The schematic block diagram of the purification apparatus of the solid substance as one Example. 一実施例としての固形物の浄化工程を示す概略ブロック図。The schematic block diagram which shows the purification | cleaning process of the solid substance as one Example. 反応時間と残留PCB率の相関関係を示すグラフ。The graph which shows the correlation of reaction time and residual PCB rate.

符号の説明Explanation of symbols

1…反応装置 2…蒸留装置
4…分離装置
DESCRIPTION OF SYMBOLS 1 ... Reaction apparatus 2 ... Distillation apparatus 4 ... Separation apparatus

Claims (2)

有機ハロゲン化合物で汚染された固形物中の水分を減圧蒸留によって除去した後、該有機ハロゲン化合物で汚染された固形物にアルカリ金属を添加し、有機ハロゲン化合物を分解処理して固形物を浄化することを特徴とする有機ハロゲン化合物で汚染された固形物の浄化方法。 After removing moisture in the solid contaminated with the organic halogen compound by distillation under reduced pressure , an alkali metal is added to the solid contaminated with the organic halogen compound, and the organic halogen compound is decomposed to purify the solid. A method for purifying a solid substance contaminated with an organic halogen compound. 有機ハロゲン化合物で汚染された固形物を供給するとともに、アルカリ金属を添加して、固形物中の有機ハロゲン化合物とアルカリ金属とを反応させる反応装置(1)と、該反応装置(1)で固形物中の有機ハロゲン化合物とアルカリ金属とを反応させる前に予め固形物中の水分を除去するための減圧蒸留を行う蒸留装置(2)とが具備されてなることを特徴とする有機ハロゲン化合物で汚染された固形物の浄化装置。 While supplying the solid substance contaminated with the organic halogen compound and adding an alkali metal, the reaction apparatus (1) for reacting the organic halogen compound and the alkali metal in the solid substance is solid in the reaction apparatus (1). An organic halogen compound comprising a distillation apparatus (2) for performing distillation under reduced pressure to remove moisture in a solid before reacting an organic halogen compound and an alkali metal in the product. Purification equipment for contaminated solids.
JP2004310559A 2004-10-26 2004-10-26 Purification method and apparatus for solid substances contaminated with organic halogen compounds Expired - Fee Related JP3730251B2 (en)

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