JP3474349B2 - Decomposition method of halogen-containing organic compounds - Google Patents

Decomposition method of halogen-containing organic compounds

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Publication number
JP3474349B2
JP3474349B2 JP4169296A JP4169296A JP3474349B2 JP 3474349 B2 JP3474349 B2 JP 3474349B2 JP 4169296 A JP4169296 A JP 4169296A JP 4169296 A JP4169296 A JP 4169296A JP 3474349 B2 JP3474349 B2 JP 3474349B2
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JP
Japan
Prior art keywords
halogen
containing organic
water
organic compound
decomposition
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 - Fee Related
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JP4169296A
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Japanese (ja)
Other versions
JPH09225294A (en
Inventor
美穂 鈴木
典男 竹山
輝信 早田
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Toshiba Corp
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Toshiba Corp
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  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)

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、含ハロゲン有機化
合物を無害な物質に分解する方法に関し、特に、紫外線
照射によって液相中の含ハロゲン有機化合物を分解する
分解方法に関する。
TECHNICAL FIELD The present invention relates to a method for decomposing a halogen-containing organic compound into a harmless substance, and more particularly to a method for decomposing a halogen-containing organic compound in a liquid phase by irradiation with ultraviolet rays.

【0002】[0002]

【従来の技術】トリクレン、ポリクロロビフェニル(P
CB)、フロン等の含ハロゲン有機化合物は、電子部品
工業、化学工業等の各種分野で広く使われている。しか
し、トリクレン、PCB等の塩素化合物については人体
に対する毒性が明らかになり、フロン等のフッ素化合物
はオゾン層の破壊に見られるように地球環境破壊の面で
問題点が近年明らかにされている。このような状況か
ら、含ハロゲン有機化合物を分解して無害化する方法が
求められ、様々な方法が検討されている。その方法の1
つに、紫外線分解法があり、工場排水などの水に溶解し
ているトリクレン等の微量の含ハロゲン有機化合物の分
解処理方法として開発が進められている。
2. Description of the Related Art Trichlorene, polychlorobiphenyl (P
The halogen-containing organic compounds such as CB) and chlorofluorocarbon are widely used in various fields such as the electronic component industry and the chemical industry. However, toxicity of chlorine compounds such as trichlene and PCB has been revealed to the human body, and problems of fluorine compounds such as CFCs have been clarified in recent years in terms of global environmental destruction as seen in ozone layer destruction. Under such circumstances, a method for decomposing the halogen-containing organic compound to render it harmless is required, and various methods have been studied. Method 1
Finally, there is an ultraviolet decomposition method, which is being developed as a method for decomposing a minute amount of halogen-containing organic compounds such as trichlene dissolved in water such as factory wastewater.

【0003】上記方法において分解処理される含ハロゲ
ン有機化合物の濃度はppmレベル以下であり、含ハロ
ゲン有機化合物の水への溶解度は非常に低いので、この
方法で多量の含ハロゲン有機化合物を分解処理するのは
困難と考えられていた。
Since the concentration of the halogen-containing organic compound decomposed in the above method is below the ppm level and the solubility of the halogen-containing organic compound in water is very low, a large amount of the halogen-containing organic compound is decomposed by this method. It was considered difficult to do.

【0004】このため、改良方法として、含ハロゲン有
機化合物を溶解するためにアルコールを溶媒として使用
して紫外線照射する方法が提案されている(特開平6−
63177号公報)。この方法では、紫外線照射によっ
て生じるハロゲン化水素等を塩析除去するためにアルカ
リが添加される。
Therefore, as an improved method, a method has been proposed in which alcohol is used as a solvent in order to dissolve the halogen-containing organic compound, and ultraviolet irradiation is carried out (JP-A-6-
63177 publication). In this method, an alkali is added in order to salt out and remove hydrogen halide and the like generated by ultraviolet irradiation.

【0005】[0005]

【発明が解決しようとする課題】しかし、上述のような
アルコール溶剤を使用する場合、アルコールが紫外線に
よる副反応を引き起こし、溶液が着色したり副生成物と
して高分子様の沈澱物が生じたりする。このため、紫外
線透過率が減少したり、生成塩と沈澱物との混合によっ
て反応液の廃棄や再利用のための後処理が複雑になり、
費用もかさむといった問題がある。
However, when the alcohol solvent as described above is used, the alcohol causes a side reaction due to ultraviolet rays, so that the solution is colored and a polymer-like precipitate is produced as a by-product. . Therefore, the ultraviolet transmittance is reduced, and the post-treatment for discarding or reusing the reaction solution is complicated due to the mixing of the produced salt and the precipitate,
There is also the problem of increased costs.

【0006】[0006]

【課題を解決するための手段】本発明は、上述のような
問題を生じることなく、効率よく含ハロゲン有機化合物
を分解無害化でき、後処理が容易な含ハロゲン有機化合
物の分解方法を提供することを目的とする。
The present invention provides a method for decomposing a halogen-containing organic compound, which can efficiently decompose and detoxify a halogen-containing organic compound without causing the above-mentioned problems and facilitate post-treatment. The purpose is to

【0007】本発明の含ハロゲン有機化合物の分解方法
は、含ハロゲン有機化合物と水とからなる液、又は、
ハロゲン有機化合物と水とアルカリ物質とからなる液
攪拌しエマルジョン状態に分散させながら紫外線を照射
することを特徴とするものである。
The method for decomposing a halogen-containing organic compound according to the present invention is a method of stirring a liquid containing a halogen-containing organic compound and water or a liquid containing a halogen-containing organic compound, water and an alkaline substance while dispersing them in an emulsion state. It is characterized by irradiation with ultraviolet rays.

【0008】[0008]

【0009】上記方法に従って、水は、該含ハロゲン有
機化合物に対して容積比で5倍以上用いられる。
According to the above method, water is used in a volume ratio of 5 times or more with respect to the halogen-containing organic compound.

【0010】含ハロゲン有機化合物及び水は攪拌によっ
てあるいは分散液を形成することによってその接触面積
が増す。この状態で紫外線照射を施すことによって、界
面を介して起こる分解反応が促進されるため、含ハロゲ
ン有機化合物の分解率が向上する。これにより、水中で
飽和量以上の含ハロゲン有機化合物の紫外線分解が可能
となる。
The contact area of the halogen-containing organic compound and water increases by stirring or by forming a dispersion. By irradiating with ultraviolet rays in this state, the decomposition reaction that occurs through the interface is promoted, so that the decomposition rate of the halogen-containing organic compound is improved. As a result, it becomes possible to decompose the halogen-containing organic compound having a saturated amount or more in water by ultraviolet light.

【0011】[0011]

【発明の実施の形態】以下、本発明について詳細に説明
する。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention will be described in detail below.

【0012】含ハロゲン有機化合物の水に対する飽和溶
解量は約4000 ppm以下と低いため、両者を合わせて
も殆ど溶解せずに分離する。分離状態で紫外線を照射し
ても、含ハロゲン有機化合物の分解速度は非常に遅く、
穏やかに攪拌しながら照射すると分解速度は若干改善さ
れるが、十分な改善ではない。しかし、激しく攪拌して
含ハロゲン有機化合物を水中に分散させ、エマルジョン
状態で紫外線を照射すると、水中のハロゲンイオン濃度
がかなり増加する。つまり、分解率が向上する。このこ
とから、分解反応のプロセスは水相と含ハロゲン有機化
合物相との接触界面を介して進行し、接触界面を介する
反応段階が律速となることが理解される。つまり、分解
速度は水相と有機相との接触面積に依存する。従って、
2相の接触面積をできる限り多くすることが、含ハロゲ
ン有機化合物の水中での紫外線分解反応を進行させるた
めに重要となる。
Since the saturated dissolution amount of the halogen-containing organic compound in water is as low as about 4000 ppm or less, even if both are combined, they are separated with almost no dissolution. Even when UV rays are irradiated in the separated state, the decomposition rate of halogen-containing organic compounds is very slow,
Irradiation with gentle stirring improves the decomposition rate slightly, but not sufficiently. However, when the halogen-containing organic compound is dispersed in water with vigorous stirring and irradiated with ultraviolet rays in an emulsion state, the concentration of halogen ions in water considerably increases. That is, the decomposition rate is improved. From this, it is understood that the process of the decomposition reaction proceeds through the contact interface between the aqueous phase and the halogen-containing organic compound phase, and the reaction step through the contact interface is rate-determining. That is, the decomposition rate depends on the contact area between the aqueous phase and the organic phase. Therefore,
It is important to increase the contact area between the two phases as much as possible in order to promote the ultraviolet decomposition reaction of the halogen-containing organic compound in water.

【0013】これを実現する1つの方法が前述の攪拌や
振とう等の機械的方法であり、攪拌(又は振とう)速
度、攪拌翼あるいは攪拌子の形状、容器の形状のような
分散効率を左右する要素が反応効率の改善を左右する要
素となる。又、含ハロゲン有機化合物と水との配合比率
も接触面積を効率よく増加させるための重要な要素であ
る。水量を増加すると、攪拌によって形成される分散液
の安定性が増し、分散液がエマルジョン状から再度2つ
の相に分離するまでに要する放置時間も長くなる。含ハ
ロゲン有機化合物を水に効果的に分散させるためには、
含ハロゲン有機化合物に対して容積比で約5倍以上、好
ましくは約10倍以上の量の水が用いられ、特に水量が
25倍以上になると分解反応の進行は特に顕著になる。
但し、分解装置の容積当りの処理効率を好適なものにす
るためには使用する水量を、含ハロゲン有機化合物が飽
和可能な量以下、好ましくは50倍以下程度に設定する
のが望ましい。
One method for achieving this is the mechanical method such as stirring and shaking described above, and the dispersion efficiency such as the stirring (or shaking) speed, the shape of the stirring blade or stirrer, and the shape of the container is controlled. The factors that influence control the factors that affect the improvement of reaction efficiency. Further, the mixing ratio of the halogen-containing organic compound and water is also an important factor for efficiently increasing the contact area. Increasing the amount of water increases the stability of the dispersion formed by stirring, and also increases the standing time required for the dispersion to separate from the emulsion state into two phases again. In order to effectively disperse the halogen-containing organic compound in water,
A volume ratio of water to the halogen-containing organic compound is about 5 times or more, preferably about 10 times or more, and particularly when the amount of water is 25 times or more, the progress of the decomposition reaction becomes remarkable.
However, in order to optimize the treatment efficiency per volume of the decomposition apparatus, it is desirable to set the amount of water used to an amount that can saturate the halogen-containing organic compound or less, preferably about 50 times or less.

【0014】他の方法としては、界面活性剤などを乳化
剤として使用してエマルジョンを調製し、これに紫外線
を照射するものがある。但し、界面活性剤の使用量はで
きる限り少なく抑えるのが望ましい。この理由は、多量
の界面活性剤が界面に密集することによってエマルジョ
ン内外の流通が実質的に阻止されるのを防止するためで
ある。従って、界面活性剤の量は含ハロゲン有機化合物
の量に対して体積比で等量以下であるのが望ましい。
Another method is to prepare an emulsion using a surfactant or the like as an emulsifier and irradiate it with ultraviolet rays. However, it is desirable to keep the amount of the surfactant used as small as possible. The reason for this is to prevent a large amount of the surfactant from being concentrated at the interface and substantially preventing the flow inside and outside the emulsion. Therefore, it is desirable that the amount of the surfactant be equal to or less than the amount of the halogen-containing organic compound in a volume ratio.

【0015】上記に従って水に含ハロゲン有機化合物を
分散させ、紫外線を照射する。紫外線照射による分解反
応は、比較的高エネルギーの紫外線によってほぼ完全に
進行する。遠紫外域、つまり約300nm以下の波長での
照射が好ましい。分解速度は照射波長が長くなると遅く
なるが、増感剤を用いると、より低エネルギーの近紫外
域(400 〜300nm )の紫外線を使用することも可能であ
る。増感剤としては、アセトン、エチルメチルケトン、
アセトアルデヒド等のケトン構造もしくはアルデヒド構
造を有するものが用いられる。光増感剤の添加量は、分
解条件によって適宜変更するのが好ましいが、概して、
分解する含ハロゲン有機化合物に対して等モル量以下の
量で十分な効力が得られる。
According to the above, the halogen-containing organic compound is dispersed in water and irradiated with ultraviolet rays. The decomposition reaction by irradiation with ultraviolet rays proceeds almost completely by ultraviolet rays of relatively high energy. Irradiation in the far-ultraviolet region, that is, a wavelength of about 300 nm or less is preferable. The decomposition rate becomes slower as the irradiation wavelength becomes longer, but when a sensitizer is used, it is also possible to use lower energy ultraviolet light in the near ultraviolet region (400 to 300 nm). As the sensitizer, acetone, ethyl methyl ketone,
Those having a ketone structure such as acetaldehyde or an aldehyde structure are used. The addition amount of the photosensitizer is preferably appropriately changed depending on the decomposition conditions, but in general,
Sufficient efficacy is obtained with an equimolar amount or less with respect to the halogen-containing organic compound that decomposes.

【0016】更に、アルカリ物質を使用すると分解反応
の進行を促進することができる。アルカリ物質は、含ハ
ロゲン有機化合物から脱離して水中にイオンとして存在
するハロゲンを捕捉し中和する働きをする。又、フロン
HCFC−21、HCFC−22、CFC−12のよう
な含ハロゲン有機化合物は、アルカリが存在すると分解
し易い。同様に、フロンCFC−11の紫外線分解にお
ける2つ目以降のハロゲンが脱離する段階の反応が、ア
ルカリ物質の存在によって進み易くなる。従って、含ハ
ロゲン有機化合物が二酸化炭素にまで完全に分解するの
を促進するためにはアルカリ物質を添加するのが望まし
い。アルカリ物質としては、水相でハロゲンを捕捉する
ために、水溶性のアルカリ物質を使用するのが好まし
く、例えば、水酸化ナトリウム、水酸化カリウム、水酸
化カルシウム等の金属水酸化物、アンモニア、石鹸のよ
うなアルカリ金属による有機化合物の鹸化物等が挙げら
れる。石鹸は界面活性剤でもあるので、分散液の安定化
にも有効である。
Further, use of an alkaline substance can accelerate the progress of the decomposition reaction. The alkaline substance has a function of desorbing from the halogen-containing organic compound and capturing and neutralizing the halogen existing as an ion in water. Further, halogen-containing organic compounds such as Freon HCFC-21, HCFC-22, and CFC-12 are easily decomposed in the presence of alkali. Similarly, the presence of the alkaline substance facilitates the reaction of the second and subsequent halogen elimination steps in the ultraviolet decomposition of CFC-11. Therefore, it is desirable to add an alkaline substance in order to accelerate the complete decomposition of the halogen-containing organic compound into carbon dioxide. As the alkaline substance, it is preferable to use a water-soluble alkaline substance in order to capture halogen in the aqueous phase, and examples thereof include metal hydroxides such as sodium hydroxide, potassium hydroxide and calcium hydroxide, ammonia and soap. Examples thereof include saponified products of organic compounds with alkali metals. Since soap is also a surfactant, it is effective in stabilizing the dispersion.

【0017】上述のアルカリ物質は、予め水に添加して
用いても、あるいは紫外線照射中に水に添加してもよ
い。
The above-mentioned alkaline substance may be added to water in advance, or may be added to water during the irradiation of ultraviolet rays.

【0018】分解反応は、ハロゲンイオンを反応系外へ
除去する機能を有するものを添加することによっても促
進することができる。例えば、陰イオン交換樹脂を添加
すると、脱離して水中に存在するハロゲンイオンが陰イ
オン交換樹脂に吸着されるので、反応系からハロゲンイ
オンが除去される。これにより、逆反応に従って分解中
間物質と脱離ハロゲンとが再結合することを抑制でき
る。あるいは、カルシウムのようなハロゲンイオンと難
溶性化合物を形成するものを反応系に導入することによ
っても、ハロゲンを沈澱析出させて分解反応系から除去
することができる。
The decomposition reaction can also be promoted by adding one having a function of removing halogen ions out of the reaction system. For example, when an anion exchange resin is added, the halogen ions existing in water after being desorbed are adsorbed by the anion exchange resin, so that the halogen ions are removed from the reaction system. As a result, it is possible to suppress the recombination of the decomposition intermediate substance and the eliminated halogen due to the reverse reaction. Alternatively, the halogen can be precipitated and removed from the decomposition reaction system by introducing into the reaction system a compound that forms a sparingly soluble compound with a halogen ion such as calcium.

【0019】上述の分解方法は、例えば図1に示される
ような分解装置1で実施することができる。分解装置1
は、分解槽3と磁気攪拌器5と攪拌子7と紫外線ランプ
9とから構成され、分解槽3に投入された水及び含ハロ
ゲン有機化合物中で攪拌子7を磁気攪拌器5によって回
転させて水及び含ハロゲン有機化合物を攪拌し、含ハロ
ゲン有機化合物を水に分散させる。含ハロゲン有機化合
物が分散した水Wに紫外線ランプ9で紫外線を照射する
ことによって、含ハロゲン有機化合物を分解する。紫外
線照射と平行してアルカリ物質を添加する場合には、ア
ルカリ添加装置が分解槽3に付設される。
The above-described disassembling method can be carried out by the disassembling apparatus 1 as shown in FIG. 1, for example. Disassembly device 1
Is composed of a decomposition tank 3, a magnetic stirrer 5, a stirrer 7 and an ultraviolet lamp 9, and the stirrer 7 is rotated by the magnetic stirrer 5 in the water and the halogen-containing organic compound charged into the decomposition tank 3. Water and the halogen-containing organic compound are stirred to disperse the halogen-containing organic compound in water. The halogen-containing organic compound is decomposed by irradiating the water W, in which the halogen-containing organic compound is dispersed, with ultraviolet rays from the ultraviolet lamp 9. When the alkaline substance is added in parallel with the ultraviolet irradiation, an alkali adding device is attached to the decomposition tank 3.

【0020】上述のように、本発明に係る分解方法は、
含ハロゲン有機化合物を水と共に紫外線照射することに
よって分解するものであり、塩化メチル、塩化メチレ
ン、クロロホルム、四塩化炭素、トリクレン、PCB、
フロン、ジクロロエテン等の分解に適用できる。分解後
の反応液はハロゲンイオンをアルカリで中和すれば安全
に廃棄することができる。この際、未分解の含ハロゲン
有機化合物は水と分離するため、水から除去して再度分
解反応処理を行うことが容易である。微量の未分解の含
ハロゲン有機化合物が水に溶解しているときは、再度紫
外線分解処理を施せばよい。従って、分解反応後の処理
が極めて容易で、経済的な負担も少ない。
As described above, the decomposition method according to the present invention is
It decomposes by irradiating a halogen-containing organic compound with water together with ultraviolet light. Methyl chloride, methylene chloride, chloroform, carbon tetrachloride, trichlene, PCB,
It can be applied to the decomposition of freon, dichloroethene, etc. The reaction liquid after decomposition can be safely discarded by neutralizing halogen ions with alkali. At this time, since the undecomposed halogen-containing organic compound is separated from water, it is easy to remove it from water and perform the decomposition reaction treatment again. When a trace amount of undecomposed halogen-containing organic compound is dissolved in water, the ultraviolet decomposition treatment may be performed again. Therefore, the treatment after the decomposition reaction is extremely easy and the economical burden is small.

【0021】[0021]

【実施例】以下、実施例を参照して本発明を更に説明す
る。
The present invention will be further described below with reference to examples.

【0022】(実施例1)図1の分解装置の分解槽3
に、500mlの純水にフロン(CFC−113)50ml
を加え、磁気攪拌器で5分間激しく攪拌した。攪拌中、
フロンは水に分散してエマルジョン状態になった。さら
に、攪拌を続行しながらこの分散液に紫外線ランプ9で
紫外線(254nm、32W)を1時間照射し、照射終了
後の水中の塩素イオン濃度及び弗素イオン濃度を測定し
た。測定結果を表1に示す。
(Embodiment 1) Decomposition tank 3 of the decomposition apparatus shown in FIG.
In addition, 50 ml of Freon (CFC-113) in 500 ml of pure water
Was added and the mixture was vigorously stirred for 5 minutes with a magnetic stirrer. While stirring,
Freon was dispersed in water and became an emulsion. Further, while continuing stirring, this dispersion was irradiated with ultraviolet rays (254 nm, 32 W) by an ultraviolet lamp 9 for 1 hour, and the chlorine ion concentration and the fluorine ion concentration in water after the irradiation were measured. The measurement results are shown in Table 1.

【0023】(実施例2)実施例1と同様に、純水及び
フロンを磁気攪拌器5で激しく5分間攪拌した。この
後、攪拌速度を下げて穏やかな攪拌を施しながら実施例
1と同様に紫外線を照射した。照射中、攪拌液は水相と
フロン相とに分離していた。照射終了後の水中の塩素イ
オン濃度及び弗素イオン濃度を測定した結果を表1に示
す。
Example 2 As in Example 1, pure water and chlorofluorocarbon were vigorously stirred by the magnetic stirrer 5 for 5 minutes. After that, ultraviolet rays were irradiated in the same manner as in Example 1 while lowering the stirring speed and performing gentle stirring. During the irradiation, the stirring liquid was separated into a water phase and a freon phase. Table 1 shows the results of measuring the chlorine ion concentration and the fluorine ion concentration in the water after the irradiation.

【0024】(実施例3)実施例1と同様に、純水及び
フロンを磁気攪拌器で激しく5分間攪拌した。この後、
攪拌を止めて、水とフロンとに分離した液に実施例1と
同様の紫外線照射を行った。照射終了後の水中の塩素イ
オン濃度及び弗素イオン濃度を測定した結果を表1に示
す。
(Example 3) As in Example 1, pure water and chlorofluorocarbon were vigorously stirred for 5 minutes with a magnetic stirrer. After this,
The stirring was stopped, and the liquid separated into water and chlorofluorocarbon was irradiated with the same ultraviolet rays as in Example 1. Table 1 shows the results of measuring the chlorine ion concentration and the fluorine ion concentration in the water after the irradiation.

【0025】(対照例)実施例1と同量の純水及びフロ
ンを、実施例1と同様に5分間激しく攪拌し、攪拌終了
後の水中の塩素イオン濃度及び弗素イオン濃度を測定し
た結果を表1に示す。
(Comparative Example) The same amounts of pure water and Freon as in Example 1 were vigorously stirred for 5 minutes as in Example 1, and the chlorine ion concentration and the fluorine ion concentration in the water after the stirring were measured. It shows in Table 1.

【0026】[0026]

【表1】 −−−−−−−−−−−−−−−−−−−−−−−−−−−−− 塩素イオン濃度(ppm) 弗素イオン濃度(ppm) −−−−−−−−−−−−−−−−−−−−−−−−−−−−− 実施例1 115 48 実施例2 86 36 実施例3 67 25 対照例 0.03 0.28 −−−−−−−−−−−−−−−−−−−−−−−−−−−−− 上記から明かに、紫外線照射中の攪拌が激しいと照射後
の水中のハロゲンイオンが増加することから、フロンの
分解反応が促進されていることがわかる。又、水及びフ
ロンに攪拌を全く施すことなく同様の紫外線照射を行っ
た場合には、照射後の塩素イオン及び弗素イオンの濃度
は実施例3の値より更に小さくなる。このことから、実
施例3においては照射前の激しい攪拌により分散した粒
子の一部が照射中まで残存したと理解される。
[Table 1] --------------------------------------- Chloride ion concentration (ppm) Fluoride ion concentration (ppm) ----- ----------------------- Example 1 115 48 Example 2 86 36 Example 3 67 25 Control Example 0.03 0.28 --- From the above, it is clear that if the stirring during UV irradiation is intense, the number of halogen ions in the water after irradiation increases. From this, it is understood that the decomposition reaction of freon is promoted. Further, when the same ultraviolet ray irradiation is performed on water and freon without any stirring, the concentration of chlorine ions and fluorine ions after the irradiation becomes smaller than the values in Example 3. From this, it is understood that in Example 3, some of the particles dispersed by vigorous stirring before irradiation remained until irradiation.

【0027】(実施例4)フロンの量を10mlに変更し
たこと以外は実施例1と同様の操作を行って、紫外線照
射後の水中の塩素イオン濃度及び弗素イオン濃度を測定
した結果を表2に示す。
(Example 4) The same operation as in Example 1 was carried out except that the amount of freon was changed to 10 ml, and the chlorine ion concentration and the fluorine ion concentration in the water after ultraviolet irradiation were measured. Shown in.

【0028】(実施例5)フロンの量を20mlに変更し
たこと以外は実施例1と同様の操作を行って、紫外線照
射後の水中の塩素イオン濃度及び弗素イオン濃度を測定
した結果を表2に示す。
(Example 5) The same operation as in Example 1 was carried out except that the amount of freon was changed to 20 ml, and the chlorine ion concentration and the fluorine ion concentration in the water after ultraviolet irradiation were measured. Shown in.

【0029】(実施例6)フロンの量を30mlに変更し
たこと以外は実施例1と同様の操作を行って、紫外線照
射後の水中の塩素イオン濃度及び弗素イオン濃度を測定
した結果を表2に示す。
(Example 6) The same operation as in Example 1 was carried out except that the amount of Freon was changed to 30 ml, and the chlorine ion concentration and the fluorine ion concentration in the water after ultraviolet irradiation were measured. Shown in.

【0030】(実施例7)フロンの量を100mlに変更
したこと以外は実施例1と同様の操作を行って、紫外線
照射後の水中の塩素イオン濃度及び弗素イオン濃度を測
定した結果を表2に示す。
(Example 7) The same operation as in Example 1 was carried out except that the amount of Freon was changed to 100 ml, and the chlorine ion concentration and the fluorine ion concentration in the water after ultraviolet irradiation were measured. Shown in.

【0031】[0031]

【表2】 −−−−−−−−−−−−−−−−−−−−−−−−−−−−− 塩素イオン濃度(ppm) 弗素イオン濃度(ppm) −−−−−−−−−−−−−−−−−−−−−−−−−−−−− 実施例4 195 104 実施例5 250 150 実施例6 134 58 実施例1 115 48 実施例7 112 46 −−−−−−−−−−−−−−−−−−−−−−−−−−−−− 表2において、実施例1と実施例7とは反応後のハロゲ
ンイオン濃度に大差がみられないが、これらの結果を単
位容積のフロンを基準にして考えると、実施例1の反応
率は実施例7の約2倍に向上していることになる。又、
実施例4、5に示されるように、水に加えるフロンの量
が減少するに従って急激にハロゲンイオンの濃度が増加
することから、実施例1及び7の結果は濃度平衡などに
よる反応抑制は受けていないと言える。更に、分散液中
の接触界面の面積及び分散粒子の安定性がフロン量の減
少によって著しく増大し、これによって分解反応速度が
向上すると考えられる。表2の結果からは、水500ml
に対するフロン量が約20ml以下(フロンに対する水容
積=約25倍)において、接触界面の面積及び分散粒子
の安定性が格段に増加することが示唆される。
[Table 2] ------------------------------------------ Chloride ion concentration (ppm) Fluoride ion concentration (ppm) ----- Example 4 195 104 Example 5 250 150 Example 6 134 58 Example 1 115 48 Example 7 112 46 − −−−−−−−−−−−−−−−−−−−−−−−−− In Table 2, there is a big difference in the halogen ion concentration after the reaction between Example 1 and Example 7. Although not seen, when these results are considered with reference to a unit volume of CFC, the reaction rate of Example 1 is about twice as high as that of Example 7. or,
As shown in Examples 4 and 5, the concentration of halogen ions rapidly increases as the amount of CFC added to water decreases. Therefore, the results of Examples 1 and 7 are not suppressed by the reaction due to concentration equilibrium. I can say no. Furthermore, it is considered that the area of the contact interface in the dispersion and the stability of the dispersed particles are remarkably increased by the decrease in the amount of freon, and thereby the decomposition reaction rate is improved. From the results in Table 2, 500 ml of water
It is suggested that the area of the contact interface and the stability of the dispersed particles are remarkably increased when the amount of CFCs to C.sub.2 is about 20 ml or less (water volume to CFCs = about 25 times).

【0032】[0032]

【発明の効果】以上説明したように、本発明によれば、
含ハロゲン有機化合物の水中での紫外線分解が促進され
るので、不要となった含ハロゲン有機化合物の処理が簡
単になり、反応後の処理も容易である点も優れており、
その工業及び環境保護における価値は大である。
As described above, according to the present invention,
UV decomposition of halogen-containing organic compounds in water is promoted, which makes it easy to treat unnecessary halogen-containing organic compounds, and is also excellent in that it is easy to treat after the reaction.
Its value in industry and environmental protection is great.

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

【図1】本発明に係る含ハロゲン有機化合物の分解方法
を実施する分解装置の一例を示す概念図である。
FIG. 1 is a conceptual diagram showing an example of a decomposition apparatus for carrying out a decomposition method of a halogen-containing organic compound according to the present invention.

【符号の説明】[Explanation of symbols]

3 分解槽 5 磁気攪拌器 7 攪拌子 9 紫外線ランプ 3 decomposition tank 5 magnetic stirrer 7 Stirrer 9 UV lamp

フロントページの続き (56)参考文献 特開 平7−128318(JP,A) 特開 平6−7474(JP,A) 特開 平4−293517(JP,A) 特開 平8−206250(JP,A) (58)調査した分野(Int.Cl.7,DB名) B01J 19/12 A62D 3/00 C07B 35/06 Continuation of the front page (56) Reference JP-A-7-128318 (JP, A) JP-A-6-7474 (JP, A) JP-A-4-293517 (JP, A) JP-A-8-206250 (JP , A) (58) Fields surveyed (Int.Cl. 7 , DB name) B01J 19/12 A62D 3/00 C07B 35/06

Claims (2)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 含ハロゲン有機化合物と水とからなる
液、又は、含ハロゲン有機化合物と水とアルカリ物質と
からなる液を攪拌しエマルジョン状態に分散させながら
紫外線を照射することを特徴とする含ハロゲン有機化合
物の分解方法。
Consisting 1. A halogen-containing organic compound and water
Liquid or halogen-containing organic compound, water and alkaline substance
A method for decomposing a halogen-containing organic compound, which comprises irradiating ultraviolet rays while agitating a liquid containing the above and dispersing it in an emulsion state .
【請求項2】 前記水は、含ハロゲン有機化合物に対し
て容積比で5倍以上用いられることを特徴とする請求項
1記載の含ハロゲン有機化合物の分解方法。
2. The method for decomposing a halogen-containing organic compound according to claim 1, wherein the water is used 5 times or more in volume ratio with respect to the halogen-containing organic compound.
JP4169296A 1996-02-28 1996-02-28 Decomposition method of halogen-containing organic compounds Expired - Fee Related JP3474349B2 (en)

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Application Number Priority Date Filing Date Title
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Publication Number Publication Date
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JP3474349B2 true JP3474349B2 (en) 2003-12-08

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Country Link
JP (1) JP3474349B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3622132B2 (en) * 1997-10-28 2005-02-23 力也 半田 Treatment method of PCB mixed oil
JPH11189671A (en) * 1997-12-26 1999-07-13 Shunichi Terada Treatment of waste oil containing pcb
AU1417801A (en) * 1999-11-22 2001-06-04 Hiroshi Kashihara Method of decomposing halogenated substance, method of detecting decomposition of harmful substance, and kit for detecting decomposition of harmful substance

Also Published As

Publication number Publication date
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