JPH05292A - Method and apparatus for treating wastewater containing organic chlorine compounds - Google Patents
Method and apparatus for treating wastewater containing organic chlorine compoundsInfo
- Publication number
- JPH05292A JPH05292A JP17892391A JP17892391A JPH05292A JP H05292 A JPH05292 A JP H05292A JP 17892391 A JP17892391 A JP 17892391A JP 17892391 A JP17892391 A JP 17892391A JP H05292 A JPH05292 A JP H05292A
- Authority
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- Japan
- Prior art keywords
- wastewater
- organic chlorine
- gas
- chlorine compound
- container
- 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.)
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- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
(57)【要約】
【目的】 本発明は、有機塩素化合物含有排水、例えば
トリクロロエチレン、テトラクロロエチレン等を含む排
水の処理方法及びその処理装置を提供する。
【構成】 有機塩素化合物含有排水を鉄系金属多孔体と
過酸化水素の存在下で酸化分解処理するに際して、密閉
可能な容器に収納した上記有機塩素化合物含有排水を強
制循環させると共に該排水の強制循環力を利用して、上
記密閉容器内の有機塩素化合物含有ガスを主体とする気
相を上記排水中に循環させながら酸化分解処理する方法
及びエジェクターを使用し、1台のポンプで二つの循環
路を作動させる装置。
(57) [Summary] [Object] The present invention provides a method for treating wastewater containing an organic chlorine compound, for example, wastewater containing trichlorethylene, tetrachloroethylene, and the like, and a treatment apparatus therefor. [Structure] When oxidative decomposition treatment of organochlorine compound-containing wastewater is performed in the presence of an iron-based metal porous body and hydrogen peroxide, the organochlorine compound-containing wastewater contained in a sealable container is forcibly circulated and the wastewater is forcibly circulated. Using the circulation force, a method of oxidizing and decomposing while circulating the gas phase mainly containing the organochlorine compound-containing gas in the closed vessel in the wastewater and using an ejector, two circulations with one pump A device that activates a road.
Description
【0001】[0001]
【産業上の利用分野】本発明は、有機塩素化合物含有排
水、例えばトリクロロエチレン、テトラクロロエチレン
等を含む排水の処理方法及びその処理装置に関するもの
である。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating wastewater containing organic chlorine compounds, for example, wastewater containing trichlorethylene, tetrachloroethylene and the like, and a treatment apparatus therefor.
【0002】[0002]
【従来の技術】トリクロロエチレン、テトラクロロエチ
レン等の有機塩素化合物を含有する排水は環境衛生上の
見地から各種の法規制が施行されているので、これらの
排水の処理には高度な処理技術の確立が望まれている。2. Description of the Related Art Wastewater containing organic chlorine compounds such as trichlorethylene and tetrachloroethylene is subject to various laws and regulations from the viewpoint of environmental hygiene, so it is desirable to establish advanced treatment technology for the treatment of these wastewaters. It is rare.
【0003】これら有機塩素化合物含有排水の一般的な
処理方法としては、例えば曝気槽による曝気処理法、充
填(エアレーション)塔による放散処理法、活性炭を用
いた吸着処理法、あるいはこれらを適宜組み合わせた方
法が知られている。As a general treatment method for these organic chlorine compound-containing wastewater, for example, an aeration treatment method using an aeration tank, a diffusion treatment method using a filling (aeration) tower, an adsorption treatment method using activated carbon, or a combination thereof is appropriately used. The method is known.
【0004】また、被酸化性物質を含む排水にフェント
ン試薬を作用させる処理法、例えば特開昭50―136947
号、特開昭63―158188号で知られている。Further, a treatment method in which Fenton's reagent is allowed to act on wastewater containing an oxidizable substance, for example, Japanese Patent Laid-Open No. 50-136947.
No. 6/158188.
【0005】[0005]
【発明が解決しようとする課題】しかしながら、上記曝
気法、放散法、吸着法等はいずれも物理的な処理法であ
って、排水から除去した有機塩素化合物を含む物質、例
えば活性炭を二次処理して無害化する必要があり、活性
炭の吸着能力がなくなる時期を管理して取替えなければ
ならない等の処理管理上にも難点が多い。However, the above-mentioned aeration method, desorption method, adsorption method, etc. are all physical treatment methods, and a secondary treatment of a substance containing an organic chlorine compound, such as activated carbon, removed from wastewater is carried out. Therefore, it is necessary to detoxify it, and it is necessary to replace the activated carbon when the adsorption capacity of the activated carbon is lost.
【0006】一方、フェントン反応を利用する場合、例
えばFeSO4等の2価イオン化合物を利用する場合は、Fe
++イオンとH2O2の反応が極めて急激に起こる、一方、排
水中の有機塩素化合物が、含有量としては通常数十ppm
〜数百ppmと極めて低いレベルにあるため、有機塩素化
合物の酸化に消費されるよりは、大半は酸素ガスとして
放出されている。On the other hand, when the Fenton reaction is used, for example, when a divalent ionic compound such as FeSO 4 is used, Fe is used.
++ Reaction of H 2 O 2 with ions occurs extremely rapidly, while the content of organic chlorine compounds in wastewater is usually several tens ppm
Since it is at a very low level of ~ several hundred ppm, most of it is released as oxygen gas rather than being consumed for the oxidation of organochlorine compounds.
【0007】そのため有機塩素化合物を酸化除去するに
は大量のH2O2、FeSO4を添加する必要があり、結果とし
て排水中の有機塩素化合物は除去されるものの、一方排
水中のCOD、Feイオン、pHの処理が大がかりになる欠点
がある。Therefore, in order to oxidize and remove the organic chlorine compounds, it is necessary to add a large amount of H 2 O 2 and FeSO 4 , and as a result, the organic chlorine compounds in the wastewater are removed, while COD and Fe in the wastewater are removed. There is a drawback that the treatment of ions and pH becomes large.
【0008】また、Fe2(SO4)3等のFe3価イオンを利用
するフェントン反応では、Fe2価イオンのような急激な
反応は起こらないものの、Fe3価化合物が水に溶解しに
くいため、使用にあたっては酸溶解してから使用するこ
とが必要で、処理後のCOD、Feイオン、pHの処理に、Fe
2価イオンの場合と同様の大がかりな処理が必要とな
る。[0008] In the Fenton reaction utilizing the Fe3 divalent ions such as Fe 2 (SO 4) 3, but does not occur abrupt reactions like Fe2 valent ions, for Fe3 valent compound is hardly soluble in water, use In that case, it is necessary to dissolve the acid before use, and to treat COD, Fe ions, and pH after treatment, use Fe.
The same large-scale processing as in the case of divalent ions is required.
【0009】本発明は、有機塩素化合物含有排水を鉄系
金属多孔体と過酸化水素で処理する方法に着目し、この
有機塩素化合物の酸化分解除去をより効率的に実施する
方法及び装置を提供するものである。The present invention focuses on a method for treating wastewater containing an organic chlorine compound with an iron-based metal porous body and hydrogen peroxide, and provides a method and an apparatus for more efficiently performing oxidative decomposition removal of this organic chlorine compound. To do.
【0010】[0010]
【課題を解決するための手段】本発明は、(1)有機塩
素化合物含有排水を鉄系金属多孔体と過酸化水素の存在
下で酸化分解処理するに際して、密閉可能な容器に収納
した上記有機塩素化合物含有排水を強制循環させると共
に該排水の強制循環力を利用して、上記密閉容器内の有
機塩素化合物含有ガスを主体とする気相を上記排水中に
循環させながら酸化分解処理することを特徴とする有機
塩素化合物含有排水の処理方法。Means for Solving the Problems The present invention provides (1) an organic chlorine compound-containing wastewater, which is housed in a hermetically sealed container when oxidatively decomposed in the presence of an iron-based metal porous body and hydrogen peroxide. By forcibly circulating the chlorine compound-containing wastewater and utilizing the forced circulation force of the wastewater, it is possible to oxidize and decompose while circulating a gas phase mainly composed of an organochlorine compound-containing gas in the closed container in the wastewater. A method for treating wastewater containing a characteristic organic chlorine compound.
【0011】(2)密閉可能な容器内に鉄系金属多孔体
を配置し、該容器内に収容する被処理排水の水面上と水
面下に、それぞれ被処理排水及び有機塩素化合物含有ガ
スを主体とする気相の循環路の一端を連結し、上記被処
理排水の循環路にポンプを設け、該ポンプの下流側の循
環路にエジェクターを設け、該エジェクターに上記気相
の循環路の他端を連結し、該エジェクターと、上記容器
内の鉄系金属多孔体の下部に設置した曝気管とを連結し
たことを特徴とする有機塩素化合物含有排水の処理装
置。(2) A ferrous metal porous body is placed in a hermetically sealed container, and the treated wastewater and the organic chlorine compound-containing gas are mainly contained above and below the treated wastewater contained in the container. And one end of the gas-phase circulation path is connected, a pump is provided in the circulation path for the wastewater to be treated, an ejector is provided in the circulation path on the downstream side of the pump, and the other end of the gas-phase circulation path is provided in the ejector. Is connected to the ejector and an aeration pipe installed below the iron-based metal porous body in the container to connect the organic chlorine compound-containing wastewater.
【0012】(3)上記気相の循環路の途中に逆止弁と
開閉弁を備えた曝気用ガス供給管を接続したことを特徴
とする(2)の有機塩素化合物含有排水の処理装置であ
る。(3) In the treatment apparatus for wastewater containing an organic chlorine compound according to (2), an aeration gas supply pipe equipped with a check valve and an opening / closing valve is connected in the middle of the vapor phase circulation path. is there.
【0013】[0013]
【作用】有機塩素化合物、例えばテトラクロロエチレン
を含む水を鉄系金属多孔体と接触させるとFeの還元反応
によって、次の反応が生じ分解除去できることを特願平
1―249008号で開示した。
CCl2:CCl2+4Fe+4H2O→CH2:CH2+4Fe+++4OH-+4Cl- [Function] When the water containing an organic chlorine compound such as tetrachloroethylene is brought into contact with the iron-based metal porous body, the following reaction occurs due to the reduction reaction of Fe, and it can be decomposed and removed.
It was disclosed in No. 1-249008. CCl 2 : CCl 2 + 4Fe + 4H 2 O → CH 2 : CH 2 + 4Fe ++ + 4OH − + 4Cl −
【0014】また、有機塩素化合物含有排水を鉄系金属
多孔体と過酸化水素との共存下で反応させると比較的短
時間で分解除去できることを特願平2―214289号で開示
した。Further, it was disclosed in Japanese Patent Application No. 2-214289 that the organic chlorine compound-containing wastewater can be decomposed and removed in a relatively short time by reacting it in the presence of a ferrous metal porous material and hydrogen peroxide.
【0015】(1)還元性金属である鉄を主体とする鉄
系金属多孔体とテトラクロロエチレンの還元分解反応;
CCl2:CCl2+4Fe+4H2O→CH2:CH2+4Fe+++4OH-+4Cl- (1) Reductive decomposition reaction of an iron-based metal porous body mainly composed of iron, which is a reducing metal, and tetrachloroethylene; CCl 2 : CCl 2 + 4Fe + 4H 2 O → CH 2 : CH 2 + 4Fe ++ + 4OH − + 4Cl −
【0016】(2)H2O2と生成Fe++イオンのフェントン
反応による酸化分解反応;
Fe+++H2O2→Fe++++OH-+・OH(ラジカル)
CCl2:CCl2+4・OH→2CO2+4H Cl (2) H2O2And generate Fe++Ionic fenton
Oxidative decomposition reaction by reaction;
Fe+++ H2O2→ Fe++++ OH-+ ・ OH (Radical)
CCl2: CCl2+4 ・ OH → 2CO2+ 4H Cl
【0017】(3)H2O2の鉄系金属多孔体との酸化に伴
うFe++によるフェントン反応による酸化分解反応;
Fe+H2O2→Fe+++2OH-
Fe+++H2O2→Fe++++OH-+・OH(ラジカル)
CCl2:CCl2+4・OH→2CO2+4HCl [0017] (3) oxidative degradation by Fenton reaction by Fe ++ with the oxidation of the iron-based porous metal body of the H 2 O 2; Fe + H 2 O 2 → Fe ++ + 2OH - Fe ++ + H 2 O 2 → Fe +++ + OH − + ・ OH (radical) CCl 2 : CCl 2 +4 ・ OH → 2CO 2 + 4HCl
【0018】この(1)〜(3)の還元反応、酸化反応
が同時に起こっており、(1)の反応により生成するFe
++イオン、または(2)、(3)の反応によって生成す
るFe++イオンの生成速度が、例えばFeSO4を直接排水中
に添加して生成するFe++イオン生成速度に比較して、極
めて遅いため、FeSO4+H2O の如き急激な反応でなく、効
率的な有機塩素化合物のフェントン酸化分解反応が進
み、結果として処理後のCOD、Feイオン等の極めて低い
値を示すものと想定している。The reduction reaction and oxidation reaction of (1) to (3)
Occur at the same time, and Fe generated by the reaction of (1)
++Ions, or generated by the reaction of (2) and (3)
Fe++Ion generation rate is, for example, FeSOFourDuring direct drainage
Fe produced by adding to++Compared to the ion production rate, the pole
FeSO is so slowFour+ H2O It is not a sudden reaction like
Fenton's oxidative decomposition reaction of organic chlorine compounds progresses efficiently
As a result, COD and Fe ions after treatment are extremely low
It is assumed to indicate a value.
【0019】本発明者等は、上記特願平2―214289号に
基づく反応をさらに短時間に進行させることについて種
々検討を重ねた結果、上記した有機塩素のフェントン酸
化分解反応の進行過程において蒸発し、処理容器内に有
機塩素化合物含有ガスの気相を形成し、排水中の有機塩
素のフェントン酸化処理の進行に若干遅れて追随して気
相から有機塩素化合物含有ガスが排水中に再溶解してい
ることを知見した。The inventors of the present invention have made various investigations on the progress of the reaction based on the above-mentioned Japanese Patent Application No. 2-214289 in a shorter time, and as a result, as a result, evaporation in the course of the above-described Fenton oxidative decomposition reaction of organic chlorine Then, a gas phase of the organochlorine compound-containing gas is formed in the treatment vessel, and the organochlorine compound-containing gas is redissolved in the wastewater from the gas phase following the progress of the Fenton oxidation treatment of the organochlorine in the wastewater with some delay. I found out that it is doing.
【0020】即ち、液相から有機塩素化合物含有物の蒸
発、気相から液相への有機塩素化合物含有ガスの溶解と
いう挙動が上記系全体のフェントン反応の遅延をもたら
しているといえる。That is, it can be said that the behaviors of evaporation of the organochlorine compound-containing material from the liquid phase and dissolution of the organochlorine compound-containing gas from the gas phase to the liquid phase delay the Fenton reaction of the entire system.
【0021】以上のような知見に基づき本発明は、被処
理排水を強制的に循環させながら、この被処理排水の強
制循環力を利用して気相中の有機塩素化合物含有ガスを
積極的にフェントン反応系内に循環供給することによ
り、有機塩素化合物を速やかに酸化分解除去できること
を見出した。Based on the above findings, the present invention uses the forced circulation force of this treated wastewater to positively circulate the organic chlorine compound-containing gas in the gas phase while forcibly circulating the treated wastewater. It was found that organochlorine compounds can be rapidly oxidatively removed by circulating the supply into the Fenton reaction system.
【0022】具体的には、有機塩素化合物含有排水を鉄
系金属多孔体と過酸化水素の存在下で酸化分解処理する
に際して、密閉可能な容器に収納した上記有機塩素化合
物含有排水を強制循環させると共に該排水の強制循環力
を利用して、上記密閉容器内の有機塩素化合物含有ガス
を主体とする気相を上記排水中に循環させながら酸化分
解処理を行うものである。Specifically, when the organic chlorine compound-containing wastewater is oxidatively decomposed in the presence of the iron-based metal porous body and hydrogen peroxide, the organic chlorine compound-containing wastewater stored in a sealable container is forcedly circulated. At the same time, by utilizing the forced circulation force of the waste water, the oxidative decomposition treatment is performed while circulating the gas phase mainly containing the organic chlorine compound-containing gas in the closed container in the waste water.
【0023】上記本発明の被処理排水の強制循環はフェ
ントン反応を加速し、また、有機塩素化合物含有ガスの
気相循環は該ガスをフェントン反応系内に直接接触させ
ると共に有機塩素化合物含有排水を攪拌し、上記フェン
トン反応を加速する作用をももたらす。The forced circulation of the waste water to be treated according to the present invention accelerates the Fenton reaction, and the gas phase circulation of the organochlorine compound-containing gas causes the gas to come into direct contact with the Fenton reaction system and the wastewater containing the organochlorine compound. Stirring also brings about an action of accelerating the Fenton reaction.
【0024】本発明で使用する鉄系金属多孔体とは、鉄
を主成分とし、他にCu、Cr、Ni、Sn、Zn等の鉄の耐食性
を向上させる金属を含むものでもよい。The iron-based metal porous body used in the present invention may contain iron as a main component and also a metal such as Cu, Cr, Ni, Sn, or Zn which improves the corrosion resistance of iron.
【0025】多孔体形状としては、金属を成形した球
状、柱状の積層体、多孔板またはその積層体、ファイバ
ー状、ハニカム状にしたものあるいは鉄系金属粉末をウ
レタンホーム等の3次元成形体に塗着した担体またはそ
れを焼結したもの等がある。As the shape of the porous body, a spherical or columnar laminated body formed by molding a metal, a porous plate or a laminated body thereof, a fiber-shaped or honeycomb-shaped one, or an iron-based metal powder into a three-dimensional molded body such as a urethane home. Examples of the carrier include a coated carrier and a sintered product thereof.
【0026】過酸化水素の添加量については、水中の有
機塩素化合物またはその他含有される共存イオンの量に
よって変わるが、処理水量に対して一般には、0.05〜2.
00wt%あれば十分である。The amount of hydrogen peroxide added varies depending on the amount of organic chlorine compounds or other coexisting ions contained in the water, but is generally 0.05 to 2.
00wt% is enough.
【0027】上記処理においては、密閉容器中で、有機
塩素化合物含有排水をまず鉄系金属多孔体と接触させ、
還元分解により有機塩素化合物を一次処理した後、過酸
化水素を添加し、酸化分解により有機塩素化合物を二次
処理することもできる。In the above treatment, the organic chlorine compound-containing wastewater is first contacted with the iron-based metal porous body in a closed container,
It is also possible to firstly treat the organic chlorine compound by reductive decomposition, then add hydrogen peroxide, and secondarily treat the organic chlorine compound by oxidative decomposition.
【0028】即ち、金属鉄と有機塩素化合物含有排水を
接触させると、有機塩素化合物が還元分解されると同時
にFe++イオン濃度が数十ppmとなるので、その後でH2O2
を添加すると、H2O2と金属鉄の反応より優先的にFeイオ
ンとH2O2のフェントン反応による有機塩素化合物の酸化
分解に利用できる。[0028] That is, when contacting the metallic iron and an organic chlorine compounds containing waste water, since the Fe ++ ion concentration at the same time the organic chlorine compounds is reductive decomposition is several tens of ppm, then H 2 O 2
When added, it can be utilized for the oxidative decomposition of organochlorine compounds by the Fenton reaction of Fe ions and H 2 O 2 preferentially over the reaction of H 2 O 2 and metallic iron.
【0029】以上のように被処理排水の強制循環力を利
用した気相循環併用方式による、有機塩素化合物含有排
水の酸化分解処理は有機塩素化合物を環境規制値まで低
減できるのみならず、運転動力費用を軽減できる。As described above, the oxidative decomposition treatment of wastewater containing an organochlorine compound by the combined use of vapor phase circulation utilizing the forced circulation force of the wastewater to be treated can not only reduce the organochlorine compound to the environmental regulation value, but also reduce the operating power. The cost can be reduced.
【0030】本発明の他の態様は、排水中の有機塩素化
合物濃度が所定の濃度まで低減された以降に、例えば10
mg/l以下になった段階から上記密閉容器の上部を開放し
た条件下で、上記有機塩素化合物含有排水を曝気しなが
ら処理することによって速やかなフェントン反応による
酸化分解を進行させることにある。Another embodiment of the present invention is, for example, 10% after the concentration of the organic chlorine compound in the waste water is reduced to a predetermined concentration.
Under the condition that the upper part of the closed container is opened from the stage when the concentration becomes mg / l or less, the organic chlorine compound-containing wastewater is treated while being aerated, so that the oxidative decomposition by the Fenton reaction is promoted rapidly.
【0031】排気中の有機塩素化合物含有濃度が低減す
るほど酸化分解効率が低下し、例えば排水中の有機塩素
化合物濃度を0.1mg/l以下にまで酸化分解処理するため
には長時間を要する。The oxidative decomposition efficiency decreases as the concentration of the organic chlorine compound contained in the exhaust gas decreases. For example, it takes a long time to oxidize and decompose the organic chlorine compound in the waste water to 0.1 mg / l or less.
【0032】しかして、処理排水を曝気によって強制攪
拌することにより上記フェントン反応は促進される。However, the Fenton reaction is promoted by forcibly stirring the treated wastewater by aeration.
【0033】上記曝気によって系内に供給された曝気ガ
ス、即ち空気は上記密閉容器の上端に設けられている開
放端から排気される。The aeration gas supplied to the system by the aeration, that is, the air, is exhausted from the open end provided at the upper end of the closed container.
【0034】上記処理容器の開放端からの排気中には環
境規制値範囲内の極微量の有機塩素化合物ガスが混在し
ている。The exhaust gas from the open end of the processing container contains a very small amount of organic chlorine compound gas within the environmental regulation value range.
【0035】これを殆ど零にする場合は、排気管路の途
中に吸着剤、例えば活性炭、鉄系金属多孔体あるいはシ
リカゲル等を設置することにより、排気から吸着、除去
でき、しかもこの活性炭等は排気中の有機塩素化合物が
微量のため長期間に渡って機能する。In order to make this almost zero, it is possible to adsorb and remove it from the exhaust gas by installing an adsorbent, for example, activated carbon, iron-based metal porous material or silica gel in the middle of the exhaust pipe. The amount of organic chlorine compounds in the exhaust gas is very small so that it functions for a long time.
【0036】次に、本発明の処理装置を図1にもとづい
て説明する。Next, the processing apparatus of the present invention will be described with reference to FIG.
【0037】1は密閉可能な容器である。該容器1内に
は鉄系金属多孔体2を配置する。この鉄系金属多孔体2
の下方、容器1の底部分には曝気管3を設置してある。
かかる容器1内には所定量の有機塩素化合物含有排水4
を収容する。Reference numeral 1 is a container that can be closed. An iron-based metal porous body 2 is placed in the container 1. This iron-based metal porous body 2
An aeration pipe 3 is installed in the lower part of the container 1 and at the bottom of the container 1.
Waste water 4 containing a predetermined amount of organic chlorine compounds is contained in the container 1.
To house.
【0038】この収容した被処理排水4の水面より上部
位置に気相5を循環させる循環路6の一端を連結する。One end of a circulation path 6 for circulating the gas phase 5 is connected to a position above the water surface of the housed wastewater 4 to be treated.
【0039】また、被処理排水4の水面より下部位置に
は被処理排水4を循環させる循環路7一端を連結する。Further, one end of a circulation path 7 for circulating the treated wastewater 4 is connected to a position below the water surface of the treated wastewater 4.
【0040】該循環路7の途中にはポンプ8を設ける。
この循環路7のポンプ8の下流側の端部にはエジェクタ
ー9を設け、このエジェクター9は上記曝気管3と連結
する。A pump 8 is provided in the middle of the circulation path 7.
An ejector 9 is provided at the downstream end of the pump 8 in the circulation path 7, and the ejector 9 is connected to the aeration pipe 3.
【0041】該エジェクター9の側部には上記気相循環
路6の他端を連結する。The other end of the vapor phase circulation path 6 is connected to the side portion of the ejector 9.
【0042】上記容器1の上部には、酸化分解処理に要
求される量の過酸化水素を収納する過酸化水素添加装置
10を設ける。At the upper part of the container 1, a hydrogen peroxide addition device for storing the amount of hydrogen peroxide required for the oxidative decomposition treatment.
Provide 10.
【0043】この装置10は開閉弁11を備えており、所定
時間毎に開閉して所定量の過酸化水素を添加したり、あ
るいは所定開度に維持し、所定量の過酸化水素をほぼ連
続的に添加することができる。12は安全弁である。This apparatus 10 is provided with an opening / closing valve 11 which is opened / closed at a predetermined time to add a predetermined amount of hydrogen peroxide or is maintained at a predetermined opening so that the predetermined amount of hydrogen peroxide is substantially continuous. Can be added in a positive manner. 12 is a safety valve.
【0044】以上のように構成した処理装置において、
有機塩素化合物含有排水の処理に際しては、まず、容器
1に被処理排水4を所定量収納した後、ポンプ8を起動
させると被処理排水4が強制循環され、この被処理排水
の強制循環によって気相5の循環が実施され、容器1内
での酸化分解処理が効果的に進行する。In the processing apparatus configured as described above,
In the treatment of wastewater containing an organic chlorine compound, first, a predetermined amount of the wastewater 4 to be treated is stored in the container 1, and then the pump 8 is started to forcibly circulate the wastewater 4 to be treated. The circulation of phase 5 is carried out, and the oxidative decomposition treatment in the container 1 effectively proceeds.
【0045】上記処理装置の気相循環路6の途中に、逆
止弁13及び開閉弁14を備えた曝気用ガス吸い込み管15を
連結し、上記容器1の上部に開閉弁16を設けた排気管17
を連結した構成を付加すると、上記酸化分解処理を曝気
しながら実行できる。An aeration gas suction pipe 15 equipped with a check valve 13 and an on-off valve 14 is connected in the middle of the gas-phase circulation path 6 of the processing apparatus, and an exhaust valve provided with an on-off valve 16 at the upper part of the container 1 Tube 17
By adding a configuration in which the above are connected, the oxidative decomposition treatment can be performed while aerating.
【0046】上記排気管17の途中には吸着剤、例えば活
性炭を着脱できる空所18を準備してある。19は排水管、
20は開閉弁、21はドレン抜き管、22はフィルターであ
る。In the middle of the exhaust pipe 17, there is prepared a space 18 in which an adsorbent such as activated carbon can be attached and detached. 19 is a drain pipe,
20 is an on-off valve, 21 is a drain pipe, and 22 is a filter.
【0047】本装置はドライクリーニング排水のよう
に、排水量1 l〜10 l/日、テトラクロロエチレン濃度
50mg/l前後のケースに適しており、過酸化水素の添加量
は被処理排水にたいして0.05〜2wt%あれば十分であ
る。This device is like dry cleaning wastewater, and has a discharge of 1 l to 10 l / day and a tetrachloroethylene concentration.
It is suitable for cases of around 50 mg / l, and the amount of hydrogen peroxide added should be 0.05 to 2 wt% with respect to the wastewater to be treated.
【0048】[0048]
【実施例1】図1に示した装置を用い、初期濃度62mg/l
のテトラクロロエチレン含有排水を6 l装入し、メッシ
ュ13番の鉄系金属多孔体を360g入れ、密閉状態で、20
℃、7時間被処理排水を循環させた。過酸化水素は1.5w
t%添加して第1工程をおこなった処理経過3時間時点
でH2O2を0.75wt%追加添加した。被処理排水の成分は表
1に示す。Example 1 Using the apparatus shown in FIG. 1, an initial concentration of 62 mg / l
Charge 6 liters of waste water containing tetrachloroethylene, and put 360g of iron-based metal porous body with mesh No. 13 in a sealed state for 20
The treated wastewater was circulated for 7 hours at ℃. Hydrogen peroxide is 1.5w
When the first step was performed with t% added, 0.75 wt% of H 2 O 2 was additionally added at 3 hours after the treatment. The components of the wastewater to be treated are shown in Table 1.
【0049】[0049]
【実施例2】実施例1と同様の条件で、3時間処理した
後、続いて容器1を開放状態にして曝気手段4を作動
し、過酸化水素を0.75wt%添加して処理した。被処理排
水の成分は表1に示す。Example 2 After treating for 3 hours under the same conditions as in Example 1, the container 1 was opened and the aeration means 4 was operated to add 0.75 wt% of hydrogen peroxide for treatment. The components of the wastewater to be treated are shown in Table 1.
【0050】[0050]
【表1】 [Table 1]
【0051】[0051]
【発明の効果】本発明によれば、鉄系金属多孔体と過酸
化水素で処理することにより、過酸化水素の利用が効率
的であり、かつ、気相をフェントン反応系に循環させる
ので効果的に有機塩素化合物の含有濃度を極微量にまで
分解、除去できる。EFFECTS OF THE INVENTION According to the present invention, the treatment with the iron-based metal porous body and hydrogen peroxide makes it possible to use hydrogen peroxide efficiently and to circulate the gas phase in the Fenton reaction system. Therefore, the concentration of the organic chlorine compound can be decomposed and removed to an extremely small amount.
【図1】本発明に係わる処理装置の概要説明図。FIG. 1 is a schematic explanatory diagram of a processing apparatus according to the present invention.
1 処理容器 2 鉄系金属多孔体 3 曝気管 4 被処理排水 5 気相 6 気相循環路 7 被処理排水循環路 8 ポンプ 9 エジェクター 10 過酸化水素添加用装置 11、14、16、20 開閉弁 12 安全弁 13 逆止弁 15 曝気用ガス吸い込み管 17 排気管 18 空所 19 排水管 21 ドレン抜き管路 22 フィルター 1 processing container 2 Iron-based porous metal 3 aeration pipe 4 treated wastewater 5 gas phase 6 Gas phase circuit 7 Wastewater circulation path to be treated 8 pumps 9 ejector 10 Hydrogen peroxide addition device 11, 14, 16, 20 Open / close valve 12 Safety valve 13 Check valve 15 Gas suction pipe for aeration 17 Exhaust pipe 18 vacant place 19 drainage pipe 21 Drainage line 22 filters
───────────────────────────────────────────────────── フロントページの続き (72)発明者 渡辺 健次 東海市東海町5―3 新日本製鐵株式会社 名古屋製鐵所内 ─────────────────────────────────────────────────── ─── Continued front page (72) Inventor Kenji Watanabe 5-3 Tokai-cho, Tokai City Nippon Steel Corporation Inside Nagoya Steel Works
Claims (3)
体と過酸化水素の存在下で酸化分解処理するに際して、
密閉可能な容器に収納した上記有機塩素化合物含有排水
を強制循環させると共に該排水の強制循環力を利用し
て、上記密閉容器内の有機塩素化合物含有ガスを主体と
する気相を上記排水中に循環させながら酸化分解処理す
ることを特徴とする有機塩素化合物含有排水の処理方
法。1. When oxidative decomposition treatment of organic chlorine compound-containing wastewater in the presence of an iron-based metal porous body and hydrogen peroxide,
By forcibly circulating the organic chlorine compound-containing wastewater stored in a sealable container and utilizing the forced circulation force of the wastewater, a gas phase mainly composed of the organic chlorine compound-containing gas in the closed container is introduced into the wastewater. A method for treating wastewater containing an organic chlorine compound, which comprises oxidative decomposition treatment while circulating.
置し、該容器内に収容する被処理排水の水面上と水面下
に、それぞれ被処理排水及び有機塩素化合物含有ガスを
主体とする気相の循環路の一端を連結し、上記被処理排
水の循環路にポンプを設け、該ポンプの下流側の循環路
にエジェクターを設け、該エジェクターに上記気相の循
環路の他端を連結し、該エジェクターと、上記容器内の
鉄系金属多孔体の下部に設置した曝気管とを連結したこ
とを特徴とする有機塩素化合物含有排水の処理装置。2. An iron-based metal porous body is placed in a container that can be sealed, and the treated wastewater and the organic chlorine compound-containing gas are mainly contained above and below the treated wastewater contained in the container. Connecting one end of the gas-phase circulation path, a pump is provided in the circulation path of the wastewater to be treated, an ejector is provided in the circulation path on the downstream side of the pump, and the other end of the gas-phase circulation path is provided in the ejector. An apparatus for treating wastewater containing an organic chlorine compound, characterized in that the ejector and the aeration pipe installed below the iron-based metal porous body in the container are connected to each other.
弁を備えた曝気用ガス供給管を接続したことを特徴とす
る請求項2の有機塩素化合物含有排水の処理装置。3. The apparatus for treating wastewater containing an organochlorine compound according to claim 2, wherein an aeration gas supply pipe equipped with a check valve and an opening / closing valve is connected in the middle of the vapor phase circulation path.
Priority Applications (4)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP17892391A JPH05292A (en) | 1991-06-25 | 1991-06-25 | Method and apparatus for treating wastewater containing organic chlorine compounds |
| US07/979,851 US5376284A (en) | 1991-06-25 | 1992-06-25 | Method and apparatus for treating effluent containing organic chlorine compound |
| EP19920913995 EP0544924A4 (en) | 1991-06-25 | 1992-06-25 | Method and device for treating waste water containing organic chlorine compounds |
| PCT/JP1992/000810 WO1993000301A1 (en) | 1991-06-25 | 1992-06-25 | Method and device for treating waste water containing organic chlorine compounds |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP17892391A JPH05292A (en) | 1991-06-25 | 1991-06-25 | Method and apparatus for treating wastewater containing organic chlorine compounds |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH05292A true JPH05292A (en) | 1993-01-08 |
Family
ID=16057011
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP17892391A Pending JPH05292A (en) | 1991-06-25 | 1991-06-25 | Method and apparatus for treating wastewater containing organic chlorine compounds |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH05292A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6462250B1 (en) | 1999-06-22 | 2002-10-08 | Canon Kabushiki Kaisha | Method for decomposing halogenated aliphatic hydrocarbon compounds having adsorption process and apparatus for decomposition having adsorption means |
Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS63158188A (en) * | 1986-12-23 | 1988-07-01 | Sumitomo Metal Ind Ltd | Method and apparatus for treating waste water |
| JPH03101893A (en) * | 1989-09-14 | 1991-04-26 | Kyoritsu Yuki Co Ltd | Treatment of waste water |
-
1991
- 1991-06-25 JP JP17892391A patent/JPH05292A/en active Pending
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS63158188A (en) * | 1986-12-23 | 1988-07-01 | Sumitomo Metal Ind Ltd | Method and apparatus for treating waste water |
| JPH03101893A (en) * | 1989-09-14 | 1991-04-26 | Kyoritsu Yuki Co Ltd | Treatment of waste water |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US6462250B1 (en) | 1999-06-22 | 2002-10-08 | Canon Kabushiki Kaisha | Method for decomposing halogenated aliphatic hydrocarbon compounds having adsorption process and apparatus for decomposition having adsorption means |
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