JPH09150159A - Cod-related component removing method for the component containing water - Google Patents

Cod-related component removing method for the component containing water

Info

Publication number
JPH09150159A
JPH09150159A JP31448495A JP31448495A JPH09150159A JP H09150159 A JPH09150159 A JP H09150159A JP 31448495 A JP31448495 A JP 31448495A JP 31448495 A JP31448495 A JP 31448495A JP H09150159 A JPH09150159 A JP H09150159A
Authority
JP
Japan
Prior art keywords
water
cod
iron
anode chamber
containing water
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.)
Granted
Application number
JP31448495A
Other languages
Japanese (ja)
Other versions
JP3400627B2 (en
Inventor
Katsuyuki Kataoka
克之 片岡
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Ebara Corp
Original Assignee
Ebara Corp
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Ebara Corp filed Critical Ebara Corp
Priority to JP31448495A priority Critical patent/JP3400627B2/en
Publication of JPH09150159A publication Critical patent/JPH09150159A/en
Application granted granted Critical
Publication of JP3400627B2 publication Critical patent/JP3400627B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Treatment Of Water By Oxidation Or Reduction (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

PROBLEM TO BE SOLVED: To improve the removing ratio of COD-related component in waste water without using chemicals such as alkaline agent by subjecting the component-containing water to an electrolytic oxidation at an anode chamber of a diaphragm electrolytic cell under the copresence of hydrogen peroxide and iron ion, then neutralizing the water in a cathode chamber. SOLUTION: The COD-related component containing water 1 is supplied to the anode chamber 6 of the diaphragm electrolytic cell 2 having an acidic atmosphere of about pH3-4. Fenton's reaction is progressed together with an electrolytically oxidizing reaction by simultaneously adding hydrogen peroxide 9 and iron salt or metal iron (iron ion) 10. Then the water to be electrolytically oxidized flowing out from the anode chamber 6 through a bypass 11 is introduced to a cathode chamber 7. The introduced water to be electrolytically oxidized is neutralized with a hydroxide ion produced at the cathode chamber 7 by the electrolytic reaction. Therefore, a neutral treated water 12 from which the COD-related component is removed is obtained, and a clear treated water is obtained by subjecting the neutral treated water 12 to a solid-liq. separation to remove incorporated iron hydroxide particulates.

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、各種の排水中の難
生物分解性CODを効果的に酸化分解する技術、特に糞
尿の生物処理水中の黄褐色の色度成分を効果的に酸化分
解する技術に関するものである。
TECHNICAL FIELD The present invention relates to a technique for effectively oxidatively decomposing poorly biodegradable COD in various wastewaters, and in particular, it effectively oxidatively decomposes a yellowish brown chromaticity component in biotreated water of manure. It is about technology.

【0002】[0002]

【従来の技術】従来より、各種の排水中の難生物分解性
CODを酸化分解する技術として、フエントン法(過酸
化水素−鉄塩併用法)、紫外線−過酸化水素併用法、紫
外線−光触媒併用法、紫外線−オゾン酸化併用法、オゾ
ン−過酸化水素併用法などが知られているが、いずれの
方法も処理コストが高価につく割にCODの除去率が劣
り、超純水製造分野以外への実用例はほとんどなかっ
た。
2. Description of the Related Art Hitherto, as a technique for oxidatively decomposing poorly biodegradable COD in various kinds of waste water, the Fenton method (hydrogen peroxide-iron salt combination method), ultraviolet ray-hydrogen peroxide combination method, ultraviolet ray-photocatalyst combination method has been used. Method, UV-ozone oxidation combined use method, ozone-hydrogen peroxide combined use method, etc. are known, but all of them are not suitable for the ultrapure water production field because of the high treatment cost but poor COD removal rate. There were few practical examples.

【0003】[0003]

【発明が解決しようとする課題】従来のフエントン法
は、酸性条件下で過酸化水素と鉄塩を被処理水に添加
し、ヒドロキシラジカルを発生させ、被処理水中のCO
Dを分解した後、アルカリ剤を添加して中和する方法で
あるが、ラジカル生成量が少ないのでCOD除去率が期
待したほど大きくなく、またアルカリ剤のような劇薬を
取り扱う必要があるという欠点があった。本発明は、フ
エントン法を改良し、排水中のCODを高い除去率で除
去し、かつアルカリ剤のような劇薬を取り扱う必要が避
けられる新技術を提供することを課題とする。
In the conventional Fenton method, hydrogen peroxide and an iron salt are added to water to be treated under acidic conditions to generate hydroxy radicals, and CO in the water to be treated is generated.
This is a method of decomposing D and then neutralizing it by adding an alkaline agent, but since the amount of radicals generated is small, the COD removal rate is not as large as expected, and it is necessary to handle a powerful drug such as an alkaline agent. was there. An object of the present invention is to improve the Fenton method, to provide a new technology capable of removing COD in wastewater at a high removal rate and avoiding the need to handle a powerful drug such as an alkaline agent.

【0004】[0004]

【課題を解決するための手段】本発明の上記課題は、
(1)COD含有水を隔膜電解槽の陽極室に供給し、前
記陽極室において過酸化水素と鉄イオンの共存下で電解
酸化した後、隔膜電気分解槽の陰極室に導き中和するこ
とを特徴とするCOD含有水のCOD除去方法。好まし
くは、(2)前記陽極室に配備する陽極の電極材質を鉄
とすることを特徴とする前記(1)に記載のCOD含有
水のCOD除去方法によって達成される。
The above-mentioned problems of the present invention are as follows.
(1) Supplying COD-containing water to the anode chamber of the diaphragm electrolyzer, electrolytically oxidizing it in the anode chamber in the presence of hydrogen peroxide and iron ions, and then introducing it to the cathode chamber of the diaphragm electrolysis tank for neutralization. A method for removing COD-containing water. Preferably, (2) it is achieved by the method for removing COD-containing water COD according to the above (1), characterized in that the electrode material of the anode provided in the anode chamber is iron.

【0005】[0005]

【発明の実施の形態】排水中のCODを除去するための
隔膜電解槽を主体とする本発明の処理工程のフローを図
1に示し、以下に図1を用いて本発明を説明する。ちな
みに、酸性条件下で過酸化水素と鉄塩の共存下で起こる
フエントン反応は以下の反応式で示される。 H2 2 +Fe2+→Fe3++HO- +・OH
BEST MODE FOR CARRYING OUT THE INVENTION A flow chart of a treatment process of the present invention, which mainly includes a diaphragm electrolyzer for removing COD in waste water, is shown in FIG. 1, and the present invention will be described below with reference to FIG. Incidentally, the Fenton reaction that occurs in the presence of hydrogen peroxide and iron salts under acidic conditions is shown by the following reaction formula. H 2 O 2 + Fe 2+ → Fe 3+ + HO + .OH

【0006】図1において、隔膜電解槽2の構造は、槽
2を槽内に設けた隔膜5により2室に分割し、各室にそ
れぞれを陽極3と陰極4を設置して陽極室6と陰極室7
とする。陽極3と陰極4は共に白金メッキのチタン電極
もしくは鉄材で製作された電極が好適である。隔膜5に
は通常有機性精密ろ過膜(MF膜とよばれる。)が使用
される。前記構造の隔膜電解槽2を被処理水で満たし、
電源8から直流を通電すると隔膜電解槽2の陽極室6で
は電解反応によって水素イオンが生成しpH3〜4の酸
性の雰囲気となる。この電解反応を反応式で示すと次の
ようである。 H2 O →1/2O2 +2H+ +2e-
In FIG. 1, the structure of the diaphragm electrolysis tank 2 is divided into two chambers by a diaphragm 5 provided in the tank, and an anode chamber 6 and an anode chamber 6 are provided in each chamber by disposing an anode 3 and a cathode 4. Cathode chamber 7
And Both the anode 3 and the cathode 4 are preferably platinum-plated titanium electrodes or electrodes made of iron material. An organic microfiltration membrane (called an MF membrane) is usually used for the diaphragm 5. Filling the diaphragm electrolyzer 2 of the above structure with water to be treated,
When a direct current is applied from the power source 8, hydrogen ions are generated by an electrolytic reaction in the anode chamber 6 of the diaphragm electrolyzer 2 to create an acidic atmosphere of pH 3-4. This electrolytic reaction is represented by the following reaction formula. H 2 O → 1 / 2O 2 + 2H + + 2e -

【0007】本発明においては、前記pH3〜4の酸性
の雰囲気の隔膜電解槽2の陽極室6に、COD含有水1
を供給すると同時に過酸化水素9と鉄塩もしくは金属鉄
(鉄粉など)10を添加し、電解酸化反応と共にフエン
トン反応を進行させる。本発明においては、隔膜電解槽
2の陽極室6では電解反応により水素イオンが生成して
いるので、硫酸など酸を添加しなくても効果的に電解酸
化反応と共にフエントン反応が進み、被処理水中のCO
Dが高度に除去されることがわかった。なお、陽極3の
材質を鉄とすると電極から媒体に鉄イオンが供給される
ので外部から鉄塩もしくは金属鉄などを添加しなくても
すむので好適である。
In the present invention, the COD-containing water 1 is added to the anode chamber 6 of the diaphragm electrolyzer 2 in the acidic atmosphere of pH 3 to 4.
At the same time as the supply of hydrogen peroxide, hydrogen peroxide 9 and iron salt or metallic iron (iron powder or the like) 10 are added, and the Fenton reaction proceeds together with the electrolytic oxidation reaction. In the present invention, hydrogen ions are generated in the anode chamber 6 of the diaphragm electrolyzer 2 by an electrolytic reaction. Therefore, even if an acid such as sulfuric acid is not added, the Fenton reaction effectively proceeds together with the electrolytic oxidation reaction, and CO
It was found that D was highly removed. If the material of the anode 3 is iron, iron ions are supplied to the medium from the electrode, so that it is not necessary to add iron salt or metallic iron from the outside, which is preferable.

【0008】前記したように、COD含有水を酸性の雰
囲気の隔膜電解槽の陽極室に供給すると同時に過酸化水
素と鉄塩もしくは金属鉄(鉄粉など)を添加し、電解酸
化反応と共にフエントン反応を進行させるとCOD含有
水から高度にCODが除去されるのは、電極界面におい
て、フエントン反応によると同時に電解反応によってヒ
ドロキシラジカルなどの活性酸素種が効果的に発生する
ためであろうと推定される。
As described above, COD-containing water is supplied to the anode chamber of the diaphragm electrolyzer in an acidic atmosphere, and at the same time, hydrogen peroxide and iron salt or metallic iron (iron powder, etc.) are added to carry out the Fenton reaction together with the electrolytic oxidation reaction. It is presumed that COD is highly removed from the COD-containing water by advancing the hydrogen peroxide because the active oxygen species such as hydroxy radicals are effectively generated at the electrode interface by the Fenton reaction and the electrolytic reaction at the same time. .

【0009】次に、陽極室6からバイパス11を経て流
出した電解酸化処理水を陰極室7に導くと、陰極室7で
は次の電解反応式、 H2 O+e- →1/2H2 +OH- で示される反応によって水酸イオンが生成しているので
酸性の電解酸化処理水は中和され、CODが除去された
中性の処理水12が得られる。処理水12には水酸化鉄
微粒子が含まれるので固液分離して清澄な処理水とす
る。本発明の場合のようにフエントン反応によると同時
に電解反応を行うのでなく、フエントン反応のみによっ
てCODを含有する被処理水を処理してもCOD除去効
果は少ない。また、過酸化水素と鉄塩を供給せずに隔膜
電解処理を行ってもやはりCOD除去効果は本発明の方
法よりかなり劣る。
Next, when the electrolytically oxidized water that has flowed out from the anode chamber 6 via the bypass 11 is guided to the cathode chamber 7, the following electrolytic reaction formula is used in the cathode chamber 7, H 2 O + e → 1 / 2H 2 + OH . Since hydroxyl ions are generated by the reaction shown, the acidic electrolytically oxidized treated water is neutralized, and neutral treated water 12 from which COD has been removed is obtained. Since the treated water 12 contains iron hydroxide fine particles, solid-liquid separation is performed to obtain clear treated water. Even if the water to be treated containing COD is treated only by the Fenton reaction instead of performing the electrolytic reaction simultaneously with the Fenton reaction as in the case of the present invention, the COD removing effect is small. Even if the electrolytic treatment of the diaphragm is performed without supplying hydrogen peroxide and iron salt, the COD removing effect is still considerably inferior to the method of the present invention.

【0010】[0010]

【実施例】【Example】

実施例、比較例 図1の装置を用いて、糞尿の生物処理水をUF膜で膜分
離した分離水を対象として、本発明のCOD除去を行っ
た。処理に使用したCOD含有水の水質を第1表に示
す。
Example, Comparative Example Using the apparatus of FIG. 1, COD removal of the present invention was performed on separated water obtained by subjecting biologically treated water of feces and urine to membrane separation with a UF membrane. Table 1 shows the water quality of the COD-containing water used for the treatment.

【0011】[0011]

【表1】 [Table 1]

【0012】COD含有水を供給する隔膜電気分解槽の
陽極室および陰極室の能力と操作条件などを第2表およ
び第3表に示す。なお、COD含有水の隔膜電気分解槽
の陽極室への供給量は1日あたり5リットルである。
Tables 2 and 3 show the capabilities and operating conditions of the anode chamber and cathode chamber of the diaphragm electrolysis tank for supplying COD-containing water. The amount of COD-containing water supplied to the anode chamber of the diaphragm electrolysis tank was 5 liters per day.

【0013】[0013]

【表2】 [Table 2]

【0014】[0014]

【表3】 [Table 3]

【0015】次に、隔膜電気分解槽の陽極室から陰極室
に陽極処理水を移送し、陰極室で電解すると、水酸イオ
ンが発生し酸性の陽極処理水が中和され、CODが除去
されたpH中性の処理水が得られる。処理水には水酸化
鉄微粒子が含まれるので、これを固液分離して清澄な処
理水とする。処理水の水質を第4表に示す。なお、比較
のために第1表の水質のCOD含有水をフエントン単独
処理、あるいは電解単独処理した結果も併記した。
Next, when anodized water is transferred from the anode chamber of the diaphragm electrolysis tank to the cathode chamber and electrolyzed in the cathode chamber, hydroxide ions are generated to neutralize the acidic anodized water and remove COD. A pH-neutral treated water is obtained. Since iron hydroxide fine particles are contained in the treated water, this is solid-liquid separated to obtain clear treated water. Table 4 shows the quality of treated water. For comparison, the COD-containing water having the water quality shown in Table 1 is also shown together with the results obtained by treating Fenton alone or electrolytically.

【0016】[0016]

【表4】 [Table 4]

【0017】[0017]

【発明の効果】【The invention's effect】

1.生物学的に分解できないCODをフエントン−隔膜
電解複合法により効果的に除去できる。 2.隔膜電解陽極室におけるpH低下効果をフエントン
酸化の効率化に利用できる。 3.隔膜電解陰極室におけるpH上昇効果をフエントン
酸化後の中和に利用できる。 4.劇物である酸やアルカリ剤を使用する必要がない。
1. COD, which cannot be biodegraded, can be effectively removed by the Fenton-diaphragm electrolytic composite method . 2. The pH lowering effect in the diaphragm electrolysis anode chamber can be used to improve the efficiency of Fenton oxidation. 3. The pH increasing effect in the diaphragm electrocathode chamber can be utilized for neutralization after Fuenton oxidation. 4. There is no need to use acid or alkaline agents that are deleterious substances.

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

【図1】隔膜電解槽を主体とする本発明のCOD除去工
程のフローの1例を示す説明図である。
FIG. 1 is an explanatory diagram showing an example of a flow of a COD removal process of the present invention mainly using a diaphragm electrolyzer.

【符号の説明】 1 COD含有水 2 隔膜電解槽 3 陽極 4 陰極 5 隔膜 6 陽極室 7 陰極室 8 電源 9 過酸化水素 10 鉄イオン 11 バイパス 12 処理水[Explanation of symbols] 1 COD-containing water 2 Diaphragm electrolyzer 3 Anode 4 Cathode 5 Diaphragm 6 Anode chamber 7 Cathode chamber 8 Power supply 9 Hydrogen peroxide 10 Iron ion 11 Bypass 12 Treated water

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 COD含有水を隔膜電解槽の陽極室に供
給し、前記陽極室において過酸化水素と鉄イオンの共存
下で電解酸化した後、隔膜電気分解槽の陰極室に導き中
和することを特徴とするCOD含有水のCOD除去方
法。
1. COD-containing water is supplied to an anode chamber of a diaphragm electrolysis cell, electrolytically oxidized in the anode chamber in the presence of hydrogen peroxide and iron ions, and then introduced into a cathode chamber of the diaphragm electrolysis cell for neutralization. A method for removing COD-containing water, comprising:
【請求項2】 前記陽極室に配備する陽極の電極材質を
鉄とすることを特徴とする請求項1に記載のCOD含有
水のCOD除去方法。
2. The method of removing COD-containing water according to claim 1, wherein the material of the anode of the anode provided in the anode chamber is iron.
JP31448495A 1995-12-01 1995-12-01 Method for removing COD from water containing COD Expired - Fee Related JP3400627B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP31448495A JP3400627B2 (en) 1995-12-01 1995-12-01 Method for removing COD from water containing COD

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP31448495A JP3400627B2 (en) 1995-12-01 1995-12-01 Method for removing COD from water containing COD

Publications (2)

Publication Number Publication Date
JPH09150159A true JPH09150159A (en) 1997-06-10
JP3400627B2 JP3400627B2 (en) 2003-04-28

Family

ID=18053869

Family Applications (1)

Application Number Title Priority Date Filing Date
JP31448495A Expired - Fee Related JP3400627B2 (en) 1995-12-01 1995-12-01 Method for removing COD from water containing COD

Country Status (1)

Country Link
JP (1) JP3400627B2 (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20010068172A (en) * 2000-02-24 2001-07-23 강영 Advanced Electric Oxidaition Process
JP2010240516A (en) * 2009-04-01 2010-10-28 Omega:Kk Water treatment method
CN102531107A (en) * 2011-12-28 2012-07-04 青岛科技大学 Electrochemical advanced oxidation system and electrochemical advanced oxidation method for treating organic waste water difficult to degrade
CN103011525A (en) * 2012-12-31 2013-04-03 宜兴市银环电力电子科技有限公司 Anaerobic biochemical sewage treatment system and method
CN103351040A (en) * 2013-08-01 2013-10-16 中国水产科学研究院黄海水产研究所 Removing apparatus and removing method for inorganic arsenic in aquaculture underground seawater
CN106495369A (en) * 2016-12-05 2017-03-15 中国农业科学院农业环境与可持续发展研究所 The method and apparatus that a kind of electro-fenton process processes organic wastewater

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Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20010068172A (en) * 2000-02-24 2001-07-23 강영 Advanced Electric Oxidaition Process
JP2010240516A (en) * 2009-04-01 2010-10-28 Omega:Kk Water treatment method
CN102531107A (en) * 2011-12-28 2012-07-04 青岛科技大学 Electrochemical advanced oxidation system and electrochemical advanced oxidation method for treating organic waste water difficult to degrade
CN103011525A (en) * 2012-12-31 2013-04-03 宜兴市银环电力电子科技有限公司 Anaerobic biochemical sewage treatment system and method
CN103351040A (en) * 2013-08-01 2013-10-16 中国水产科学研究院黄海水产研究所 Removing apparatus and removing method for inorganic arsenic in aquaculture underground seawater
CN103351040B (en) * 2013-08-01 2015-01-21 中国水产科学研究院黄海水产研究所 Removing apparatus and removing method for inorganic arsenic in aquaculture underground seawater
CN106495369A (en) * 2016-12-05 2017-03-15 中国农业科学院农业环境与可持续发展研究所 The method and apparatus that a kind of electro-fenton process processes organic wastewater
CN106495369B (en) * 2016-12-05 2019-12-10 中国农业科学院农业环境与可持续发展研究所 Method and device for treating organic wastewater by electro-Fenton method

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