JPH06296992A - Method for decomposing waste liquid containing organic acid - Google Patents
Method for decomposing waste liquid containing organic acidInfo
- Publication number
- JPH06296992A JPH06296992A JP8602793A JP8602793A JPH06296992A JP H06296992 A JPH06296992 A JP H06296992A JP 8602793 A JP8602793 A JP 8602793A JP 8602793 A JP8602793 A JP 8602793A JP H06296992 A JPH06296992 A JP H06296992A
- Authority
- JP
- Japan
- Prior art keywords
- organic acid
- waste liquid
- acid
- org
- ozone
- 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.)
- Withdrawn
Links
Landscapes
- Physical Water Treatments (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
- Water Treatment By Electricity Or Magnetism (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は有機酸含有廃液の分解法
に関し、例えば給食センター、水産加工場、果物缶詰め
工場、ビール工場、酒などの醸造工場、畜産場やし尿処
理度などの廃水処理に適用しうる同方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for decomposing an organic acid-containing waste liquid, for example, a lunch center, a seafood processing plant, a fruit canning factory, a beer factory, a brewing factory for liquor, etc. Applicable to the same method.
【0002】[0002]
【従来の技術】有機酸を含有する排水は河川や沼などの
汚染、すなわち富栄養化の原因となるため、有機酸を除
去して放流する必要がある。従来法として、高濃度の有
機酸を含有する場合は水中燃焼法、蒸発法、噴霧燃焼法
が行なわれている。比較的低濃度の有機酸(1000m
g/リットル以下)については微生物による活性汚泥処
理法が行なわれている。2. Description of the Related Art Wastewater containing organic acids causes pollution of rivers and swamps, that is, causes eutrophication, and therefore it is necessary to remove the organic acids before discharging. As a conventional method, an underwater combustion method, an evaporation method, and a spray combustion method are used when a high concentration of organic acid is contained. Relatively low concentration of organic acid (1000m
g / l or less), a method for treating activated sludge with microorganisms is used.
【0003】[0003]
【発明が解決しようとする課題】微生物による活性汚泥
処理法は反応速度が遅いため、大容量処理を実施する場
合には、大きな敷地が必要とする。有機物のTOC
(Total Organic Carbon)成分がかなり残留する。p
Hや温度管理、特に冬場では加温などを必要とする。
常時一定の濃度保持が要求され、一時的にも被毒物の混
入ならびに昇温、例えば50℃程度でも許されない。
微生物の生理作用を犯す物質の混入も許されないなどの
問題がある。Since the reaction rate of the activated sludge treatment method using microorganisms is slow, a large site is required to carry out a large volume treatment. TOC of organic matter
(Total Organic Carbon) component remains considerably. p
It requires H and temperature control, especially in winter.
It is required to maintain a constant concentration at all times, and even temporary mixing of poisonous substances and temperature rise, for example, about 50 ° C. are not allowed.
There are problems such as the inability to mix in substances that violate the physiological action of microorganisms.
【0004】本発明は上記技術水準に鑑み、微生物によ
る活性汚泥処理法のような不具合がなく、安定した操作
で水中の有機酸を分解することができる方法を提供しよ
うとするものである。In view of the above-mentioned state of the art, the present invention is intended to provide a method capable of decomposing organic acids in water by a stable operation without the problems of the activated sludge treatment method by microorganisms.
【0005】[0005]
【課題を解決するための手段】本発明は有機酸含有廃液
の分解において、電解処理、オゾン処理、紫外線照射処
理を同時に行うことにより、廃液中の有機酸を炭酸ガス
まで分解することを特徴とする有機酸含有廃液の分解法
である。The present invention is characterized in that, in the decomposition of an organic acid-containing waste liquid, the organic acid in the waste liquid is decomposed to carbon dioxide gas by simultaneously performing electrolytic treatment, ozone treatment, and ultraviolet irradiation treatment. It is a method for decomposing waste liquid containing organic acid.
【0006】本発明における有機酸含有廃液の分解にお
いて採用される電解処理、オゾン処理、及び紫外線照射
の一般的な条件は下記のとおりである。 電解処理条件 陽電極 : フェライト、PbO2 など 陰電極 : フェライト、SUS316、Ti、Cuな
ど 電流密度: 1A/dm2 〜20A/dm2 攪 拌 : 攪拌機による攪拌(または後述のオゾン含
有酸素ガスによる攪拌) 極 間 : 10〜50mm、20V オゾン処理条件 オゾン濃度 : 10〜50mg/リットル 紫外線照射条件 20ワット以上、1時間以上の照射The general conditions of the electrolytic treatment, ozone treatment, and ultraviolet irradiation adopted in the decomposition of the organic acid-containing waste liquid in the present invention are as follows. Electrolytic treatment conditions Positive electrode: Ferrite, PbO 2, etc. Negative electrode: Ferrite, SUS316, Ti, Cu, etc. Current density: 1 A / dm 2 to 20 A / dm 2 Stirring: Stirring with a stirrer (or stirring with ozone-containing oxygen gas described later) ) Gap: 10 to 50 mm, 20 V Ozone treatment condition Ozone concentration: 10 to 50 mg / liter UV irradiation condition 20 watts or more, 1 hour or more irradiation
【0007】[0007]
【作用】オゾン−電解−紫外線の同時反応では以下に示
すような反応により、・OH,・OH2 ,O3 - ,O2
- ,O- 等の活性ラジカル種が生成され、それらにより
TOC成分の分解が起こる。 〇 電解処理 OH3 + + OH- → O2 - + OH2 OH3 + + ・OH → O2 - + ・OH2 OH3 + + OH- → O3 - + ・OH ・OH + OH- → O- + H2 O O- + OH2 → O3 - 〇 オゾン処理、紫外線処理 O3 + H2 O + hν → 2・OH + O2 このようにオゾン−電解−紫外線の同時反応により強力
な酸化性ラジカルである・OH等が多量に発生する。[Action] Ozone - electrolyte - by reaction as is shown below in simultaneous reaction of the ultraviolet, · OH, · OH 2, O 3 -, O 2
- , O-, and other active radical species are generated, and these cause decomposition of the TOC component. 〇 electrolytic processing OH 3 + + OH - → O 2 - + OH 2 OH 3 + + · OH → O 2 - + · OH 2 OH 3 + + OH - → O 3 - + · OH · OH + OH - → O - + H 2 O O - + OH 2 → O 3 - 〇 ozone treatment, ultraviolet treatment O 3 + H 2 O + hν → 2 · OH + O 2 Thus ozone - electrolyte - strong oxidizing by simultaneous reaction of the ultraviolet A large amount of OH etc., which is a characteristic radical, is generated.
【0008】[0008]
【実施例】以下、本発明の一実施例を図1によって説明
する。反応槽4は内径11cm、高さ40cmのアクリ
ル樹脂製の円筒型塔からなり、槽底に紫外線ランプ(内
部照射型低圧水銀灯)7とオゾン吹込用散気ボール13
を設け、槽の上部には50mm平方のフェライト電極板
8を極間30mmで天井部から懸吊して設置した。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENT An embodiment of the present invention will be described below with reference to FIG. The reaction tank 4 is composed of an acrylic resin cylindrical tower having an inner diameter of 11 cm and a height of 40 cm, and has an ultraviolet lamp (internal irradiation type low pressure mercury lamp) 7 and an ozone blowing diffuser ball 13 at the bottom of the tank.
The ferrite electrode plate 8 of 50 mm square was placed above the tank by suspending it from the ceiling with a gap of 30 mm.
【0009】酸素ガスボンベ1から送気量2リットル/
minの酸素をオゾン発生機2でオゾン濃度を30mg
/リットルに調整し、このオゾン化ガスを流量計3を介
してオゾン吹込用散気ボール13を通して下記表1の試
料溶液中に送気し、また紫外線電源6を調整して紫外線
ランプ7より30ワットの紫外線を試料溶液に照射し、
電極板8間に電液密度2.5A/dm2 、電流1Aを流
がして電解酸化を行った。なお、図1中、5は試料溶液
のサンプリングコック、9は定電流装置、10は電流
計、11はオゾンメータ、12は排ガスオゾン吸収塔を
示す。Amount of air fed from the oxygen gas cylinder 1 is 2 liters /
Oxygen concentration of min oxygen is 30mg with ozone generator 2.
/ L, and this ozonized gas is fed into the sample solution shown in the following Table 1 through the ozone metering diffuser ball 13 via the flow meter 3 and the ultraviolet power source 6 is adjusted to 30 from the ultraviolet lamp 7. Irradiate the sample solution with watts of ultraviolet light,
An electrolytic solution density of 2.5 A / dm 2 and a current of 1 A were passed between the electrode plates 8 to carry out electrolytic oxidation. In FIG. 1, 5 is a sample solution sampling cock, 9 is a constant current device, 10 is an ammeter, 11 is an ozone meter, and 12 is an exhaust gas ozone absorption tower.
【0010】[0010]
【表1】 この結果を下記表2に示す。[Table 1] The results are shown in Table 2 below.
【0011】[0011]
【表2】 上記表2の結果より、電解酸化+オゾン処理+紫外線照
射による総合処理法により有機酸のTOC除去率99%
を達成することができたことが明らかであろう。[Table 2] From the results of Table 2 above, the TOC removal rate of the organic acid is 99% by the comprehensive treatment method of electrolytic oxidation + ozone treatment + ultraviolet irradiation.
It will be clear that was achieved.
【0012】[0012]
【発明の効果】本発明により、微生物による活性汚泥処
理法のような不具合がなく、安定した操作で廃水中の有
機酸を分解することができる。EFFECTS OF THE INVENTION According to the present invention, organic acids in wastewater can be decomposed by a stable operation without the problems of the activated sludge treatment method by microorganisms.
【図1】本発明の一実施例の説明図。FIG. 1 is an explanatory diagram of an embodiment of the present invention.
フロントページの続き (51)Int.Cl.5 識別記号 庁内整理番号 FI 技術表示箇所 C02F 1/78 ZAB 9045−4D Continuation of the front page (51) Int.Cl. 5 Identification code Office reference number FI technical display location C02F 1/78 ZAB 9045-4D
Claims (1)
理、オゾン処理、紫外線照射処理を同時に行うことによ
り、廃液中の有機酸を炭酸ガスまで分解することを特徴
とする有機酸含有廃液の分解法。1. Decomposition of an organic acid-containing waste liquid, characterized in that in the decomposition of an organic acid-containing waste liquid, an organic acid in the waste liquid is decomposed to carbon dioxide gas by simultaneously performing electrolytic treatment, ozone treatment, and ultraviolet irradiation treatment. Law.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP8602793A JPH06296992A (en) | 1993-04-13 | 1993-04-13 | Method for decomposing waste liquid containing organic acid |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP8602793A JPH06296992A (en) | 1993-04-13 | 1993-04-13 | Method for decomposing waste liquid containing organic acid |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH06296992A true JPH06296992A (en) | 1994-10-25 |
Family
ID=13875180
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP8602793A Withdrawn JPH06296992A (en) | 1993-04-13 | 1993-04-13 | Method for decomposing waste liquid containing organic acid |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH06296992A (en) |
Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20010048824A (en) * | 1999-11-23 | 2001-06-15 | 정경숙 | The waterwaste treatment system for simultaneously occurring electrolysis reaction and photooxidation reaction |
JP2003502154A (en) * | 1999-06-18 | 2003-01-21 | バイエル アクチェンゲゼルシャフト | How to decompose organic compounds in water |
JP2005103391A (en) * | 2003-09-29 | 2005-04-21 | Mitsubishi Heavy Ind Ltd | Wastewater treatment method and apparatus |
KR100830147B1 (en) * | 2007-04-03 | 2008-05-19 | (주) 시온텍 | Ultraviolet rays sterilizer using electrolytic cell and ultrasonic waves |
WO2012114999A1 (en) * | 2011-02-21 | 2012-08-30 | 東洋炭素株式会社 | Organic acid-containing liquid degradative treatment method, organic acid-containing liquid degradative treatment device, and electrode for organic acid-containing liquid degradative treatment |
CN104671361A (en) * | 2015-02-11 | 2015-06-03 | 清华大学 | Method for removing PPCPs micropollutants in secondary sedimentation tank wastewater |
CN105727725A (en) * | 2016-04-18 | 2016-07-06 | 江苏大学 | Method and device for removing VOCs from photoelectrolysis induced free radicals |
CN105833676A (en) * | 2016-04-18 | 2016-08-10 | 江苏大学 | Method and device for removing VOCs (Volatile Organic Compounds) in waste gas by light radiation on chlorine atoms and hydroxyl |
CN106166438A (en) * | 2016-04-18 | 2016-11-30 | 江苏大学 | A kind of method and device of photodissociation chlorine aqueous solution induced radical removing hydrogen sulfide |
CN106215644A (en) * | 2016-04-18 | 2016-12-14 | 江苏大学 | A kind of method and device of photoelectrolysis induced radical removing hydrogen sulfide |
-
1993
- 1993-04-13 JP JP8602793A patent/JPH06296992A/en not_active Withdrawn
Cited By (16)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2003502154A (en) * | 1999-06-18 | 2003-01-21 | バイエル アクチェンゲゼルシャフト | How to decompose organic compounds in water |
JP4641691B2 (en) * | 1999-06-18 | 2011-03-02 | バイエル アクチェンゲゼルシャフト | Method for decomposing organic compounds in water |
KR20010048824A (en) * | 1999-11-23 | 2001-06-15 | 정경숙 | The waterwaste treatment system for simultaneously occurring electrolysis reaction and photooxidation reaction |
JP2005103391A (en) * | 2003-09-29 | 2005-04-21 | Mitsubishi Heavy Ind Ltd | Wastewater treatment method and apparatus |
KR100830147B1 (en) * | 2007-04-03 | 2008-05-19 | (주) 시온텍 | Ultraviolet rays sterilizer using electrolytic cell and ultrasonic waves |
WO2012114999A1 (en) * | 2011-02-21 | 2012-08-30 | 東洋炭素株式会社 | Organic acid-containing liquid degradative treatment method, organic acid-containing liquid degradative treatment device, and electrode for organic acid-containing liquid degradative treatment |
CN104671361A (en) * | 2015-02-11 | 2015-06-03 | 清华大学 | Method for removing PPCPs micropollutants in secondary sedimentation tank wastewater |
CN104671361B (en) * | 2015-02-11 | 2017-05-24 | 清华大学 | Method for removing PPCPs micropollutants in secondary sedimentation tank wastewater |
CN105833676A (en) * | 2016-04-18 | 2016-08-10 | 江苏大学 | Method and device for removing VOCs (Volatile Organic Compounds) in waste gas by light radiation on chlorine atoms and hydroxyl |
CN106166438A (en) * | 2016-04-18 | 2016-11-30 | 江苏大学 | A kind of method and device of photodissociation chlorine aqueous solution induced radical removing hydrogen sulfide |
CN106215644A (en) * | 2016-04-18 | 2016-12-14 | 江苏大学 | A kind of method and device of photoelectrolysis induced radical removing hydrogen sulfide |
CN105727725A (en) * | 2016-04-18 | 2016-07-06 | 江苏大学 | Method and device for removing VOCs from photoelectrolysis induced free radicals |
CN105727725B (en) * | 2016-04-18 | 2018-08-21 | 江苏大学 | A kind of photoelectrolysis induced radical takes off the method and device of VOCs |
CN105833676B (en) * | 2016-04-18 | 2018-11-06 | 江苏大学 | The method and device of VOCs in a kind of light radiation chlorine atom and hydroxyl removing exhaust gas |
CN106166438B (en) * | 2016-04-18 | 2018-12-14 | 江苏大学 | A kind of method and device of photodissociation chlorine aqueous solution induced radical removing hydrogen sulfide |
CN106215644B (en) * | 2016-04-18 | 2019-01-08 | 江苏大学 | A kind of method and device of photoelectrolysis induced radical removing hydrogen sulfide |
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Legal Events
Date | Code | Title | Description |
---|---|---|---|
A300 | Withdrawal of application because of no request for examination |
Free format text: JAPANESE INTERMEDIATE CODE: A300 Effective date: 20000704 |