JPH08155461A - Method and apparatus for removing nitric-and/or nitrous-nitrogen - Google Patents

Method and apparatus for removing nitric-and/or nitrous-nitrogen

Info

Publication number
JPH08155461A
JPH08155461A JP32961894A JP32961894A JPH08155461A JP H08155461 A JPH08155461 A JP H08155461A JP 32961894 A JP32961894 A JP 32961894A JP 32961894 A JP32961894 A JP 32961894A JP H08155461 A JPH08155461 A JP H08155461A
Authority
JP
Japan
Prior art keywords
anode
cathode
gas
nitrogen
electrode
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
JP32961894A
Other languages
Japanese (ja)
Other versions
JP3615814B2 (en
Inventor
Takayuki Shimamune
孝之 島宗
Takahiro Ashida
高弘 芦田
Yoshinori Nishiki
善則 錦
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.)
De Nora Permelec Ltd
Original Assignee
Permelec Electrode Ltd
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 Permelec Electrode Ltd filed Critical Permelec Electrode Ltd
Priority to JP32961894A priority Critical patent/JP3615814B2/en
Publication of JPH08155461A publication Critical patent/JPH08155461A/en
Application granted granted Critical
Publication of JP3615814B2 publication Critical patent/JP3615814B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/467Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
    • C02F1/4676Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electroreduction
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46109Electrodes
    • C02F2001/46152Electrodes characterised by the shape or form
    • C02F2001/46157Perforated or foraminous electrodes
    • C02F2001/46161Porous electrodes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • C02F2101/163Nitrates

Landscapes

  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

PURPOSE: To provide a technical way to conveniently and economically decompose nitric-nitrogen etc., and to solve a problem caused by a conventional electrochemical decomposition technique that nitric-and/or nitrous-nitrogen is reduced and decomposed by a cathode, but since the reaction in an anode, an opposite electrode to the cathode, is a highly electric power-consuming oxygen-producing reaction, the economical decomposition can not be carried out. CONSTITUTION: An object solution for treatment in which nitric-nitrogen is dissolved is supplied to a cathode chamber 4, nitric-nitrogen is converted into gases, and together with hydrogen produced by hydrolysis of water, these gases are circulated to an anode chamber 3 through a circulating line 9 to change an electrolytic reaction in a gas diffusion anode 5 from a highly electric power- consuming oxygen-producing reaction to a low electric power-consuming reaction. Consequently, nitric-nitrogen etc., can be decomposed and removed economically.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、排水処理分野等で用い
られる液中に存在する硝酸性及び/又は亜硝酸性窒素成
分を除去する方法及び装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for removing nitric and / or nitrite nitrogen components present in a liquid used in the field of wastewater treatment and the like.

【0002】[0002]

【従来技術とその問題点】近年水や空気等の汚染を防止
し環境衛生を改善することが最も重要な技術課題として
顕在化している。上水や排水に含まれる硝酸性窒素や亜
硝酸性窒素成分は生体内に取り込まれると変異原性を発
現するため厳しく規制されている。前記硝酸性窒素等を
分解し水中から除去する方法として従来から生物学的処
理(例えば「工業用水」第419 号37頁)及び電気透析等
が知られている。
2. Description of the Related Art In recent years, prevention of pollution of water, air, etc. and improvement of environmental hygiene have emerged as the most important technical problem. Nitrate nitrogen and nitrite nitrogen components contained in tap water and waste water are strictly regulated because they show mutagenicity when taken up in the living body. Biological treatment (for example, “Industrial water”, No. 419, page 37), electrodialysis and the like have been known as methods for decomposing and removing the nitrate nitrogen and the like from water.

【0003】この他に電気化学的に分解除去する試みも
以前から報告され、有力な除去方法の1つとして注目さ
れている。前記硝酸性及び亜硝酸性窒素は陰極で電解還
元することにより窒素やアンモニアに変換され、かつ中
間生成物としてNO2 やN2O等のNOxを副生する。
この電解還元による硝酸性窒素等の分解は、溶液抵抗が
高く、又陽極反応が酸素発生反応であるため電力消費が
大きいという欠点がある。又隔膜を使用しないと陰極生
成物が陽極で酸化されて硝酸イオン等を副生するいとう
不都合が生ずる。
In addition to this, attempts to electrochemically decompose and remove it have been reported before, and have been attracting attention as one of the effective removal methods. The nitric acid and nitrite nitrogen are converted into nitrogen and ammonia by electrolytic reduction at the cathode, and NOx such as NO 2 and N 2 O are by-produced as an intermediate product.
Decomposition of nitrate nitrogen and the like by this electrolytic reduction has a drawback that the solution resistance is high and that the anodic reaction is an oxygen generation reaction, so that power consumption is large. If the diaphragm is not used, the cathode product is oxidized at the anode and nitrate ions and the like are produced as a by-product.

【0004】[0004]

【発明の目的】本発明は、上述の従来の硝酸性及び亜硝
酸性窒素の分解技術の欠点を解消し、簡便かつ低電力消
費量で硝酸性及び亜硝酸性窒素を分解する方法及び装置
を提供することを目的とする。
SUMMARY OF THE INVENTION The present invention solves the above-mentioned drawbacks of the conventional nitric acid and nitrite nitrogen decomposing technology, and provides a method and apparatus for decomposing nitric acid and nitrite nitrogen simply and with low power consumption. The purpose is to provide.

【問題点を解決するための手段】本発明方法は、隔膜に
より陽極室及び陰極室に区画された電解槽の陰極として
気液透過性多孔性電極、三次元電極及び流動床電極から
選択される電極を使用し、硝酸性及び/又は亜硝酸性窒
素を前記陰極で還元除去する硝酸性及び/又は亜硝酸性
窒素の除去方法において、陽極としてガス拡散電極を使
用し、主に水素ガスの酸化反応を行なうことを特徴とす
る硝酸性及び/又は亜硝酸性窒素の除去方法であり、本
発明装置は本方法に適用でき更に生成する酸化窒素を分
解できる装置である。
The method of the present invention is selected from a gas-liquid permeable porous electrode, a three-dimensional electrode and a fluidized bed electrode as a cathode of an electrolytic cell divided into an anode chamber and a cathode chamber by a diaphragm. In a method for removing nitric acid and / or nitrite nitrogen by reducing nitric acid and / or nitrite nitrogen at the cathode by using an electrode, a gas diffusion electrode is used as an anode, and mainly hydrogen gas is oxidized. A method for removing nitric and / or nitrite nitrogen, which is characterized by carrying out a reaction. The apparatus of the present invention can be applied to this method and can further decompose the generated nitric oxide.

【0005】以下本発明を詳細に説明する。本発明は、
安価に分解処理を行ないにくい硝酸性及び亜硝酸性窒素
を電気化学的に分解して窒素、NOx、アンモニア等と
して気化させて系外に除去し、前記硝酸性及び亜硝酸性
窒素を分解除去する。電解槽の陰極室に前記硝酸性及び
/又は亜硝酸性窒素を含有する溶液を電解液として供給
すると、硝酸イオン及び亜硝酸イオンは下記の式に従っ
て還元分解される。
The present invention will be described in detail below. The present invention
Nitrate and nitrite nitrogen, which are difficult to decompose at low cost, are electrochemically decomposed and vaporized as nitrogen, NOx, ammonia, etc. and removed to the outside of the system to decompose and remove the nitrate and nitrite nitrogen. . When the solution containing the nitric and / or nitrite nitrogen is supplied as an electrolytic solution to the cathode chamber of the electrolytic cell, the nitrate ion and the nitrite ion are reductively decomposed according to the following formula.

【0006】 2NO3 - +12H+ +10e- → N2 +6H2 0+2NO3 - 1.246 V 2NO3 - +10H+ +8e- → N2 O+5H2 0 1.116 V NO3 - +4H+ +3e- → NO+2H2 0 0.937 V NO3 - +2H+ +2e- → NO2 - +H2 0 0.835 V 硝酸イオン濃度が低いと2e+2H+ →H2 (又は2H
2 0+e→H2 +2OH- )により水素発生の割合が増
加する。
2NO 3 + 12H + + 10e → N 2 + 6H 2 0 + 2NO 3 1.246 V 2NO 3 + 10H + + 8e → N 2 O + 5H 2 0 1.116 V NO 3 + 4H + + 3e → NO + 2H 2 0 0.937 V NO 3 - + 2H + + 2e - → NO 2 - + H 2 0 0.835 V nitrate ion concentration is low 2e + 2H + → H 2 (or 2H
2 0 + e → H 2 + 2OH -) ratio of hydrogen generation is increased by.

【0007】生成したNOxや窒素は一部がガスとして
除去され、残部は更に還元されて下記の式に従ってアン
モニウムイオンNH4 + を生ずる。このアンモニウムイ
オンは中性から酸性下ではガス化されず、イオンのまま
溶液に溶解している。 NO+6H+ +5e- → NH4 + +H2 0 0.835 V N2 O+10H+ +8e- → 2NH4 + +H2 0 0.647 V N2 +8H+ +6e- → 2NH4 + 0.275 V 電解の進行に伴い、陰極液がアルカリ域に達すると、N
4 + →NH3 の反応が進行し、水素ガスのバブリング
効果によりNH3 がストリッピングされ、気相へ除去さ
れる。
The produced NOx and nitrogen are partially removed as gas, and the rest is further reduced to produce ammonium ion NH 4 + according to the following formula. The ammonium ions are not gasified under neutral to acidic conditions and are dissolved in the solution as ions. NO + 6H + + 5e → NH 4 + + H 2 0 0.835 V N 2 O + 10H + + 8e → 2NH 4 + + H 2 0 0.647 V N 2 + 8H + + 6e → 2NH 4 + 0.275 V As the electrolysis progresses, the catholyte becomes alkaline. When the area is reached, N
The reaction of H 4 + → NH 3 proceeds, NH 3 is stripped by the bubbling effect of hydrogen gas, and is removed to the gas phase.

【0008】前述の式で生成した亜硝酸イオンは下記
の式に従って更に還元されNOx及び窒素を生成する。 NO2 - +2H+ +e- → NO+H2 0 1.202 V 2NO2 - +6H+ +4e- → N2 O+3H2 0 1.396 V 2NO2 - +8H+ +6e- → N2 +4H2 0 1.520 V(10) このように陰極反応に従って硝酸性及び亜硝酸性窒素か
ら生成するNOxや窒素、アンモニアは容易に気化する
ため、そのまま系外に取り出すことも可能であるが、本
発明では前記NOxや窒素、及び他に生成する水素等の
陰極室で発生するガスを陽極室に循環しても良い。
The nitrite ion produced by the above equation is further reduced according to the following equation to produce NOx and nitrogen. NO 2 + 2H + + e → NO + H 2 0 1.202 V 2NO 2 + 6H + + 4e → N 2 O + 3H 2 0 1.396 V 2NO 2 + 8H + + 6e → N 2 + 4H 2 0 1.520 V (10) Thus the cathode Since NOx, nitrogen, and ammonia produced from nitrate and nitrite nitrogen according to the reaction are easily vaporized, they can be taken out of the system as they are. However, in the present invention, NOx, nitrogen, and hydrogen produced in addition Gas generated in the cathode chamber such as the above may be circulated to the anode chamber.

【0009】これにより主な陽極反応を水電解による酸
素ガス発生から水素酸化による水生成反応に変換するこ
とができ、これによりセル電圧が低減され、低過電圧
下、低電力で反応を進行させることができる。前記陽極
反応を円滑に進行させるための供給水素が陰極室からの
循環水素のみでは不十分な場合には、水素ガスを別途直
接陽極室に又は陰極室を通して間接的に供給することが
望ましい。陰極における硝酸等のイオンの分解が全反応
の一部に過ぎないときは副生するガスの大部分が水素で
ありこれを陽極反応の主原料とすることができるため別
途供給する水素の量は僅かである。
As a result, the main anodic reaction can be converted from oxygen gas generation by water electrolysis to water generation reaction by hydrogen oxidation, which reduces the cell voltage and allows the reaction to proceed under low overvoltage and low power. You can When the circulating hydrogen from the cathode chamber is not sufficient as the hydrogen supply for the smooth progress of the anode reaction, it is desirable to separately supply hydrogen gas directly to the anode chamber or indirectly through the cathode chamber. When the decomposition of ions such as nitric acid at the cathode is only a part of the whole reaction, most of the by-produced gas is hydrogen and this can be used as the main raw material for the anodic reaction, so the amount of hydrogen supplied separately is Few.

【0010】別途供給する水素は市販のボンベから供給
しても、電解槽に隣接して水素ガス発生用電解槽を設置
して発生水素を前記陽極室又は陰極室へ供給しても良
い。更に前記ガス拡散電極を有する陽極室内に隔膜なし
に水素発生用陰極を設置し、隔膜を介して別に陽極室内
に設置された多孔性陽極と前記水素発生用陰極間に通電
して水素を発生させこの水素を直接前記ガス拡散電極へ
供給するよう構成することも可能である。又隔膜として
陽イオン交換膜を使用すると、溶液の電導度が小さい対
象溶液の処理も速やかに行なうことができる。更に陽イ
オン交換膜を使用すると、前述の陰極室で発生するアン
モニウムイオンの一部が陽極室側に濃度拡散し、水素ガ
ス陽極において再酸化され、窒素やNOxに分解され
る。このとき水素酸化電位にある陽極では、NO2 -
NO3 - のような反応物を再生することがない。
Hydrogen to be separately supplied may be supplied from a commercially available cylinder, or an electrolytic cell for hydrogen gas generation may be installed adjacent to the electrolytic cell to supply the generated hydrogen to the anode chamber or the cathode chamber. Further, a hydrogen generating cathode is installed without a diaphragm in the anode chamber having the gas diffusion electrode, and hydrogen is generated by passing electricity between the porous anode separately installed in the anode chamber and the hydrogen generating cathode through the diaphragm. It is also possible to supply the hydrogen directly to the gas diffusion electrode. Further, when a cation exchange membrane is used as the diaphragm, the target solution having a low electric conductivity can be quickly processed. Further, when a cation exchange membrane is used, a part of the ammonium ions generated in the cathode chamber is diffused in the anode chamber side, reoxidized in the hydrogen gas anode, and decomposed into nitrogen and NOx. At this time, the anode such as NO 2 and NO 3 does not regenerate at the anode at the hydrogen oxidation potential.

【0011】このように硝酸性及び/又は亜硝酸性窒素
を電気化学的にNOxや窒素等のガス及びアンモニウム
イオンに陰極還元し、かつ発生するガスの少なくとも一
部を陽極室へ循環すると、前記硝酸性及び/又は亜硝酸
性窒素をガスに変換して系外に除去できるとともに、陽
極反応を高電力消費型の酸素発生反応から低電力消費型
の水素酸化による水生成反応に変換し、経済的に脱窒反
応を進行させることができる。本発明に使用する陰極と
しては、気液透過性を有する多孔性電極を使用すること
が好ましく、前記硝酸性窒素等が溶解した被処理液の導
電度が低い場合や硝酸又は亜硝酸イオン濃度が低い場合
には、三次元電極(ガス拡散電極を含む)や流動床電極
の使用が効率の面から望ましい。多孔性電極を構成する
場合にはカーボンやステンレス等の多孔性基材に、銅及
び銀、あるいはパラジウム、白金等の白金族金属等の触
媒を担持させる。三次元電極や流動床電極の場合にはカ
ーボン粒子等を使用して構成することが望ましい。カー
ボン材料は濃硝酸中で腐食する傾向があるが,安価であ
り他の性能も良いため、消耗に配慮しながら使用するこ
とが望ましい。
In this way, when nitric acid and / or nitrite nitrogen is electrochemically reduced to gases such as NOx and nitrogen and ammonium ions, and at least a part of the generated gas is circulated to the anode chamber, It is possible to convert nitric acid and / or nitrite nitrogen into gas and remove it from the system, and also to convert the anodic reaction from a high power consumption type oxygen generation reaction to a low power consumption type water generation reaction by hydrogen oxidation, which is economical. The denitrification reaction can be promoted. As the cathode used in the present invention, it is preferable to use a porous electrode having gas-liquid permeability, when the conductivity of the liquid to be treated in which the nitrate nitrogen or the like is low or nitric acid or nitrite ion concentration is low. When it is low, use of a three-dimensional electrode (including a gas diffusion electrode) or a fluidized bed electrode is desirable from the viewpoint of efficiency. When forming a porous electrode, a catalyst such as copper and silver, or a platinum group metal such as palladium or platinum is supported on a porous substrate such as carbon or stainless steel. In the case of a three-dimensional electrode or a fluidized bed electrode, it is desirable to use carbon particles or the like. Although carbon materials tend to corrode in concentrated nitric acid, they are cheap and have other performances, so it is desirable to use them while considering consumption.

【0012】陽極に使用するガス拡散電極は従来のもの
を使用すれば良く、例えば支持体であるカーボンペーパ
ークロス表面に撥水性を高めるためにテフロン(商品
名)、フッ化カーボンを添加したカーボン粉末から成る
ガス供給層を形成し、前記支持体の反対面に、白金、ル
テニウム、金等の触媒を担持したカーボン粉末より成る
触媒層を形成してガス拡散電極とすることができる。前
記支持体の特性によりガス拡散電極が若干の液体透過性
を有することは電解反応を速やかに進行させる上で重要
である。
As the gas diffusion electrode used for the anode, a conventional one may be used. For example, carbon powder to which Teflon (trade name) or carbon fluoride is added to the surface of the carbon paper cloth as a support to improve water repellency. A gas diffusion layer can be formed by forming a gas supply layer made of and a catalyst layer made of carbon powder carrying a catalyst such as platinum, ruthenium or gold on the opposite surface of the support. It is important for the gas diffusion electrode to have some liquid permeability due to the characteristics of the support in order to accelerate the electrolytic reaction.

【0013】この陽極に密着させて使用する隔膜好まし
くは陽イオン交換膜は通常市販されているもので良く、
炭化水素系、フッ素樹脂系があり、耐食性の面から後者
が優れている。水素を陽極に供給せずかつイオン交換膜
を用いない場合には、陰極での還元生成物が陽極に達し
て再酸化されNO3 - やNO2 - を生成するため、結果
として硝酸性、亜硝酸性窒素を減らすことができない。
印加する電圧は被処理液の濃度にも依存するが発生する
ガスのリフト効果による攪拌を効率的に行なうためにも
高電流密度が得られるように印加することが望ましく、
一方電力原単位的には低電流密度であることが好まし
く、従って一般に電流密度が0.05〜1cm2 となるよう
に電圧を印加する。電解槽の温度や圧力は特に限定され
ない。
The diaphragm, preferably a cation exchange membrane, used in close contact with the anode may be a commercially available one.
There are hydrocarbon type and fluororesin type, and the latter is superior in terms of corrosion resistance. When hydrogen is not supplied to the anode and an ion exchange membrane is not used, the reduction product at the cathode reaches the anode and is reoxidized to produce NO 3 or NO 2 , resulting in nitric acid, suboxide Nitrate nitrogen cannot be reduced.
The applied voltage depends on the concentration of the liquid to be treated, but it is desirable to apply it so that a high current density can be obtained in order to efficiently perform stirring due to the lift effect of the generated gas.
On the other hand, it is preferable to have a low current density in terms of power consumption, and therefore, a voltage is generally applied so that the current density is 0.05 to 1 cm 2 . The temperature and pressure of the electrolytic cell are not particularly limited.

【0014】このような硝酸性及び/又は亜硝酸性窒素
の分解方法では、触媒にも依存するが、分解生成物の一
部がNOxやNH3 であり、この分解生成物は被処理液
から容易に除去できるとしても、そのまま大気中に放出
することは環境衛生上好ましくない。従って本発明装置
では必要に応じて、陽極室から排出するガスを酸化窒素
分解触媒を充填した酸化窒素分解装置を通してNOxを
窒素に変換した後、大気中に放出する。この酸化窒素分
解触媒としては自動車の廃ガス触媒等として使用されて
いる通常白金を含む3元触媒が使用される。該触媒によ
る分解効率を高めるために加熱しても良い。又前記触媒
の劣化を抑制するために前記陽極室と酸化窒素分解装置
の間にミストキャッチャーを設置しても良い。又本発明
の装置では、前記酸化窒素分解触媒の前段に、パラジウ
ム等の触媒あるいはアルカリ水溶液と空気によるストリ
ッピング法等に基づくアンモニア除去装置を設置しても
良い。
In such a method of decomposing nitric acid and / or nitrite nitrogen, although depending on the catalyst, a part of decomposition products are NOx and NH 3 , and these decomposition products are generated from the liquid to be treated. Even if it can be easily removed, it is not preferable in terms of environmental hygiene to release it as it is into the atmosphere. Therefore, in the device of the present invention, the gas discharged from the anode chamber is converted into nitrogen through a nitric oxide decomposing device filled with a nitric oxide decomposing catalyst, if necessary, and then released into the atmosphere. As the nitric oxide decomposition catalyst, a three-way catalyst containing platinum, which is usually used as a waste gas catalyst for automobiles, is used. You may heat in order to raise the decomposition efficiency by this catalyst. A mist catcher may be installed between the anode chamber and the nitric oxide decomposing device in order to suppress the deterioration of the catalyst. Further, in the apparatus of the present invention, an ammonia removing apparatus based on a stripping method using a catalyst such as palladium or an alkaline aqueous solution and air may be installed before the nitric oxide decomposing catalyst.

【0015】図1は本発明の硝酸性及び亜硝酸性窒素の
分解装置の一例を示す概略縦断面図である。電解槽本体
1は、隔膜である陽イオン交換膜2により陽極室3と陰
極室4に区画され、前記陽イオン交換膜2の陽極室3側
には触媒を担持したカーボン粉末とフッ素樹脂粉末の混
合焼結体から成るガス拡散電極5が密着形成され、又前
記陽イオン交換膜2の陰極室4側にはカーボンクロス等
のシート状の陰極6が接触状態で設置されている。
FIG. 1 is a schematic vertical sectional view showing an example of the apparatus for decomposing nitrate and nitrite nitrogen according to the present invention. The electrolytic cell body 1 is divided into an anode chamber 3 and a cathode chamber 4 by a cation exchange membrane 2 which is a diaphragm, and a carbon powder and a fluororesin powder carrying a catalyst are provided on the cation exchange membrane 2 side of the anode chamber 3. A gas diffusion electrode 5 made of a mixed sintered body is closely formed, and a sheet-shaped cathode 6 such as carbon cloth is placed in contact with the cation exchange membrane 2 on the side of the cathode chamber 4.

【0016】陰極室4の側壁の下部及び上部にはそれぞ
れ被処理液導入口7及び被処理液取出口8が形成され、
陰極室4の上面には陰極生成ガスの循環ライン9の一端
が接続され、該ライン9には脱湿用のミストキャッチャ
ー10と酸化窒素分解触媒が充填された酸化窒素分解装置
11あるいはアンモニア分解装置が設置されている。陽極
室3の側壁上部には処理済ガスの排出ライン12の一端が
接続され、該排出ライン12には前述の同様のミストキャ
ッチャー10と酸化窒素分解装置11あるいはアンモニア分
解装置が設置されている。なお13は水電解槽等の水素ガ
ス発生器で、発生した水素ガスは前記電解槽本体1の陰
極室4へ水素ガス供給口14から供給されて陰極発生ガス
中の水素ガス濃度を上昇させる。15はガス拡散陽極5へ
ガスを供給するためのガス供給管で、供給ガスは陰極6
で発生した水素ガスとし、これを循環ライン9を通して
供給するか、あるいは直接水素ボンベから供給する。
A treatment liquid introduction port 7 and a treatment liquid extraction port 8 are formed in the lower and upper portions of the side wall of the cathode chamber 4, respectively.
One end of a cathode production gas circulation line 9 is connected to the upper surface of the cathode chamber 4, and the line 9 is filled with a mist catcher 10 for dehumidification and a nitric oxide decomposition catalyst.
11 or ammonia decomposition device is installed. One end of a treated gas discharge line 12 is connected to the upper side wall of the anode chamber 3, and the same mist catcher 10 and nitric oxide decomposing device 11 or ammonia decomposing device as described above are installed in the exhaust line 12. Reference numeral 13 is a hydrogen gas generator such as a water electrolysis cell. The generated hydrogen gas is supplied to the cathode chamber 4 of the electrolysis cell main body 1 from the hydrogen gas supply port 14 to increase the hydrogen gas concentration in the cathode generation gas. Reference numeral 15 is a gas supply pipe for supplying gas to the gas diffusion anode 5, and the supply gas is the cathode 6.
The hydrogen gas generated in 1) is supplied through the circulation line 9 or directly from a hydrogen cylinder.

【0017】このような構成から成る電解槽本体1へ被
処理液導入口7から硝酸性及び/又は亜硝酸性窒素が溶
解した被処理液を供給し、水素ガス供給口14から水素ガ
スを供給しながら陽極5及び陰極6間に通電し、更に陰
極室4で生成するガスを循環ライン9を通して陽極5表
面に供給すると、陰極6表面で硝酸性及び/又は亜硝酸
性窒素が前述の〜(10)式に従って分解し、窒素、NO
x及びアンモニウムイオン等が生ずる。このうちアンモ
ニウムイオンの一部は陽イオン交換膜2を通って陽極室
3に浸透し、水素陽極で酸化されてN2 やNOx等に変
換され、排出ライン10から取り出される。
A liquid to be treated in which nitric acid and / or nitrite nitrogen is dissolved is supplied from a liquid to be treated inlet 7 to the electrolytic cell body 1 having such a structure, and hydrogen gas is supplied from a hydrogen gas supply port 14. While energizing between the anode 5 and the cathode 6, and further supplying the gas generated in the cathode chamber 4 to the surface of the anode 5 through the circulation line 9, the nitrate and / or nitrite nitrogen on the surface of the cathode 6 is reduced to the above-mentioned ( Decomposes according to formula 10), nitrogen, NO
x and ammonium ions are generated. Among them, a part of ammonium ions permeates the anode chamber 3 through the cation exchange membrane 2, is oxidized by the hydrogen anode and converted into N 2 or NOx, and is taken out from the discharge line 10.

【0018】又陰極室4で発生する窒素やNOxは、水
の電解により発生する水素ガスとともに循環ライン9を
通って陽極室3に供給され、陽極5で消費される。これ
により陽極反応が電力消費の大きい酸素発生反応から水
素の酸化による水生成反応に変化し、電力消費が大きく
低減される。そして陽極反応はこの水生成反応だけでな
く他の酸化反応も生じNOx等が発生する。これらの陽
極ガスは排出ライン12から排出され、場合によってはア
ンモニア除去装置11で脱アンモニアした後、ミストキャ
ッチャー10で脱湿され次いで酸化窒素分解装置12で酸化
窒素の分解が行なわれた後、大気中に放出される。
Nitrogen and NOx generated in the cathode chamber 4 are supplied to the anode chamber 3 through the circulation line 9 together with hydrogen gas generated by electrolysis of water, and consumed in the anode 5. As a result, the anodic reaction changes from the oxygen generation reaction, which consumes a large amount of power, to the water generation reaction, which is caused by the oxidation of hydrogen, and the power consumption is greatly reduced. Then, the anodic reaction causes not only this water formation reaction but also another oxidation reaction to generate NOx and the like. These anode gases are exhausted from the exhaust line 12, and after deammonification by the ammonia removing device 11 in some cases, dehumidifying by the mist catcher 10 and then decomposing nitrogen oxides by the nitric oxide decomposing device 12, and then the atmosphere. Released inside.

【0019】図2は本発明の硝酸性及び亜硝酸性窒素の
分解装置の他の例を示す概略縦断面図である。この例は
図1の装置の改良に係わるもので、同一部材似は同一符
号を付して説明を省略する。陰極室3の上面に連結され
た循環ライン9′は2度折り曲げられてその先端がガス
拡散陽極5の下部表面に達し、該循環ライン9′には廃
ガス取出口16が形成されている。図示の例では、陰極6
で発生する水素ガスは循環ライン9′を通る際に廃ガス
取出口16から生成する廃ガスが除去され、陽極5に供給
され、図1の場合と同様に被処理液の処理が行なわれ
る。
FIG. 2 is a schematic vertical sectional view showing another example of the apparatus for decomposing nitrate and nitrite nitrogen according to the present invention. This example relates to the improvement of the apparatus shown in FIG. 1, and the same members and components are designated by the same reference numerals and the description thereof will be omitted. A circulation line 9'connected to the upper surface of the cathode chamber 3 is bent twice so that its tip reaches the lower surface of the gas diffusion anode 5, and a waste gas outlet 16 is formed in the circulation line 9 '. In the illustrated example, the cathode 6
The hydrogen gas generated in 1 is removed from the waste gas generated from the waste gas outlet 16 when passing through the circulation line 9 ', and is supplied to the anode 5, where the liquid to be treated is treated as in the case of FIG.

【0020】[0020]

【実施例】次に本発明の硝酸性窒素等の分解に関する実
施例を記載するが、該実施例は本発明を限定するもので
はない。
EXAMPLES Next, examples of the decomposition of nitrate nitrogen etc. of the present invention will be described, but the examples do not limit the present invention.

【実施例1】電気めっきにより投影面として100 g/m
2 になるように白金を担持させたステンレス繊維焼結体
を積層して5mm厚の陰極を構成し、3mm厚のグラッ
シーカーボン給電板に接続した。陽イオン交換膜として
ナフィオン117 (デュポンジャパン社製)を用いた。白
金を担持したファーネスブラックカーボン粉末とPTF
E水懸濁液(30J、三井フロロケミカル社製)をカーボ
ン粉末とPTFEが重量比で1:1となるようにソルベ
ントナフサ中で十分に混合しカーボンクロス上に塗布し
て気液透過性のガス拡散陽極を構成した。両電極の電極
面積は15cm2 とした。
[Example 1] 100 g / m as a projection surface by electroplating
A stainless fiber sintered body supporting platinum so as to be 2 was laminated to form a cathode having a thickness of 5 mm and connected to a glassy carbon power supply plate having a thickness of 3 mm. Nafion 117 (manufactured by DuPont Japan) was used as a cation exchange membrane. Furnace black carbon powder supporting platinum and PTF
E water suspension (30J, manufactured by Mitsui Fluorochemicals Co., Ltd.) was thoroughly mixed in solvent naphtha so that the carbon powder and PTFE were in a weight ratio of 1: 1 and coated on carbon cloth to obtain gas-liquid permeability. A gas diffusion anode was constructed. The electrode area of both electrodes was 15 cm 2 .

【0021】この陽極と前記イオン交換膜を重ね、該膜
の反対面には前述の陰極を接触させこれらの3部材を締
め付けて一体化し電解槽内に設置した。陽極室体積は10
0 cm3 、陰極室体積は100 cm3 であった。この電解
槽の陰極室に、ビーカーに硝酸イオン10g/リットルを
溶解した被処理液500 ミリリットルを作製し毎分10ミリ
リットルの割合で供給し、再びビーカーに戻した。純水
電解装置で生成した理論量の50%の水素ガスを水素ガス
供給口から陰極室下部に供給した。陰極室上部に接続し
た循環ラインを通して陰極生成ガスを陽極室内の前記ガ
ス拡散陽極表面に循環させた。
The above-mentioned anode and the above-mentioned ion exchange membrane were superposed, and the above-mentioned cathode was brought into contact with the opposite surface of the membrane, and these three members were fastened together to be integrated and placed in the electrolytic cell. Anode chamber volume is 10
The volume of the cathode chamber was 0 cm 3 , and the volume of the cathode chamber was 100 cm 3 . In the cathode chamber of this electrolytic cell, 500 ml of a liquid to be treated in which 10 g / l of nitrate ions were dissolved was prepared in a beaker, supplied at a rate of 10 ml / min, and returned to the beaker again. 50% of the theoretical amount of hydrogen gas generated by the pure water electrolysis apparatus was supplied to the lower part of the cathode chamber from the hydrogen gas supply port. A cathode generated gas was circulated on the surface of the gas diffusion anode in the anode chamber through a circulation line connected to the upper part of the cathode chamber.

【0022】更に陽極室の側壁には排出ラインを接続
し、該ラインにミストキャッチャー及び酸化窒素分解装
置(触媒:白金−ロジウム−パラジウム系)を接続し
た。このような硝酸性窒素等の分解系の両電極間に3A
の電流(電流密度20A/dm2 )を流して電解を行なっ
たところ、液温40℃においてセル電圧として1.2 Vが得
られた。硝酸イオンの濃度は1g/リットルであり、硝
酸イオンの分解率は90%であった。陰極液及び陰極室出
口の硝酸イオン、亜硝酸イオン、アンモニウムイオン、
pH、アンモニア及びNOxガスの濃度を、吸光度法、
pHメーター、ガス検知管、ガスクロマトグラフィーを
用いて測定したところ、表1に示す通りであった。又6
時間後の硝酸イオンの分解率は90%であり、酸化窒素触
媒出口のNOx濃度は0.1 ppm以下であった。
Further, a discharge line was connected to the side wall of the anode chamber, and a mist catcher and a nitric oxide decomposing device (catalyst: platinum-rhodium-palladium system) were connected to the line. Between both electrodes of the decomposition system such as nitrate nitrogen, 3A
When electrolysis was carried out by applying the current (current density 20 A / dm 2 ) of 1., a cell voltage of 1.2 V was obtained at a liquid temperature of 40 ° C. The nitrate ion concentration was 1 g / liter, and the nitrate ion decomposition rate was 90%. Nitrate ions, nitrite ions, ammonium ions at the outlet of the catholyte and cathode chamber,
pH, concentration of ammonia and NOx gas, absorbance method,
It was as shown in Table 1 when measured using a pH meter, a gas detector tube, and gas chromatography. Again 6
The decomposition rate of nitrate ions after the lapse of time was 90%, and the NOx concentration at the outlet of the nitric oxide catalyst was 0.1 ppm or less.

【0023】[0023]

【表1】 [Table 1]

【0024】[0024]

【実施例2】硝酸イオンの被処理液中への溶解量を1000
ppmとしたこと以外は実施例1と同一条件で硝酸イオ
ンの分解を行なったところ、セル電圧2.4 Vが得られ、
6時間後の硝酸イオン分解効率は85%であった。
[Example 2] The amount of nitrate ions dissolved in the liquid to be treated was 1000.
When the nitrate ions were decomposed under the same conditions as in Example 1 except that the concentration was changed to ppm, a cell voltage of 2.4 V was obtained.
The nitrate ion decomposition efficiency after 6 hours was 85%.

【0025】[0025]

【比較例1】イオン交換膜の代わりに中性隔膜(商品
名:ユミクロンMF−40、湯浅アイオニクス社製)を
用い、陽極として塩化イリジウム水溶液をチタンメッシ
ュ上に塗布し熱分解法により作製した酸化イリジウム電
極(イリジウムとして20g/m2 )を用い、陽極室に水
素ガスを供給しなかったこと以外は、実施例1と同様の
電解条件で電解したところ、セル電圧として4.0 Vが得
られ、6時間後の硝酸イオンの分解率は55%であった。
[Comparative Example 1] A neutral diaphragm (trade name: Yumicron MF-40, manufactured by Yuasa Ionics) was used in place of the ion-exchange membrane, and an aqueous solution of iridium chloride was applied on a titanium mesh as an anode to prepare by a thermal decomposition method. Electrolysis was performed under the same electrolysis conditions as in Example 1 except that an iridium oxide electrode (20 g / m 2 as iridium) was used and hydrogen gas was not supplied to the anode chamber, and a cell voltage of 4.0 V was obtained. The decomposition rate of nitrate ion after 6 hours was 55%.

【0026】[0026]

【比較例2】イオン交換膜の代わりに中性隔膜を用いた
こと以外は実施例2と同様の電解槽を組立て同様の電解
条件で電解したところ、セル電圧として約15Vが得ら
れ、6時間後の硝酸イオンの分解率は80%であった。
Comparative Example 2 An electrolytic cell similar to that of Example 2 was assembled except that a neutral diaphragm was used instead of the ion exchange membrane, and electrolysis was performed under the same electrolysis conditions. As a result, a cell voltage of about 15 V was obtained for 6 hours. The subsequent decomposition rate of nitrate ions was 80%.

【0027】[0027]

【発明の効果】本発明は、隔膜により陽極室及び陰極室
に区画された電解槽の陰極として気液透過性多孔性電
極、三次元電極及び流動床電極から選択される電極を使
用し、硝酸性及び/又は亜硝酸性窒素を前記陰極で還元
除去する硝酸性及び/又は亜硝酸性窒素の除去方法にお
いて、陽極としてガス拡散電極を使用し、主に水素ガス
の酸化反応を行なうことを特徴とする硝酸性及び/又は
亜硝酸性窒素の除去方法。である。本発明によると硝酸
性及び/又は亜硝酸性窒素が陰極還元により窒素やNO
xやアンモニア等のガスに変換されてこれらのガスは気
化して陰極室から除去され、あるいは水の電解により発
生する水素とともに陽極室に循環されて陽極反応を高電
力消費型の酸素発生反応から低電力消費型の水素の酸化
反応へ変換する。
The present invention uses an electrode selected from a gas-liquid permeable porous electrode, a three-dimensional electrode and a fluidized bed electrode as a cathode of an electrolytic cell divided into an anode chamber and a cathode chamber by a diaphragm. In the method for removing nitric and / or nitrite nitrogen by reducing and removing volatile and / or nitrite nitrogen at the cathode, a gas diffusion electrode is used as an anode, and an oxidation reaction of hydrogen gas is mainly performed. And a method for removing nitric and / or nitrite nitrogen. Is. According to the present invention, nitric and / or nitrite nitrogen is converted to nitrogen or NO by cathodic reduction.
x is converted into gas such as ammonia and these gases are vaporized and removed from the cathode chamber, or are circulated to the anode chamber along with hydrogen generated by electrolysis of water, and the anode reaction is changed from the high power consumption type oxygen generation reaction. Converts to low power consumption type hydrogen oxidation reaction.

【0028】従って水質環境に悪影響を及ぼす硝酸性及
び/又は亜硝酸性窒素の分解を簡便かつ経済的に行なう
ことができる。又隔膜として陽イオン交換膜を使用する
と、陰極で生成した還元物の陽極での再酸化によるNO
3 - やNO2 - の生成を防ぐことができる。又被処理液
の電導度が小さい場合にも電解反応が容易に進行する。
Therefore, the decomposition of nitric and / or nitrite nitrogen, which adversely affects the water quality environment, can be carried out easily and economically. When a cation exchange membrane is used as the diaphragm, the NO produced by the reoxidation of the reduced product produced at the cathode at the anode.
3 - and NO 2 - can be prevented generation of. Further, even when the liquid to be treated has a low electric conductivity, the electrolytic reaction easily proceeds.

【0029】本発明装置は、実質的に前述の本発明方法
に使用する装置の陽極生成ガスの排出ラインに陽極で生
成するガス中の酸化窒素を分解するための酸化窒素分解
装置を接続した装置である。本発明により硝酸性及び/
又は亜硝酸性窒素を分解した後も、陽極室で生成するガ
ス中には酸化窒素が含まれている。この酸化窒素をその
まま放出すると大気汚染を招くため、自動車廃ガス等で
利用されている前述の酸化窒素分解装置を利用して前記
酸化窒素を分解すると無害なガスに変換され、大気中へ
の放出が可能になる。
The apparatus of the present invention is substantially the same as the apparatus used in the above-described method of the present invention, except that the discharge line for the anode-producing gas is connected to a nitric oxide decomposing device for decomposing nitric oxide in the gas produced at the anode. Is. Nitrate and / or
Alternatively, even after the nitrite nitrogen is decomposed, the gas generated in the anode chamber contains nitric oxide. If this nitric oxide is released as it is, it causes air pollution. Therefore, if the above-mentioned nitric oxide decomposing device used in automobile waste gas is used to decompose the nitric oxide, it is converted into a harmless gas and released into the atmosphere. Will be possible.

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

【図1】本発明の硝酸性及び/又は亜硝酸性窒素分解装
置の一例を示す概略縦断面図。
FIG. 1 is a schematic vertical cross-sectional view showing an example of a nitrate and / or nitrite nitrogen decomposing apparatus of the present invention.

【図2】図1の装置の改良した装置の例を示す概略縦断
面図。
2 is a schematic vertical sectional view showing an example of an improved device of the device of FIG.

【符号の説明】[Explanation of symbols]

1・・・電解槽本体 2・・・陽イオン交換膜 3・・
・陽極室 4・・・陰極室 5・・・ガス拡散電極 6
・・・陰極 7・・・被処理液導入口 8・・・被処理
液取出口 9、9′・・・循環ライン 10・・・ミスト
キャッチャー 11・・・酸化窒素分解装置 12・・・排出ライン 13・
・・水素ガス発生器 14・・・水素ガス供給口 15・・
・ガス供給管 16・・・廃ガス取出口
1 ... Electrolyzer main body 2 ... Cation exchange membrane 3 ...
・ Anode chamber 4 ・ ・ ・ Cathode chamber 5 ・ ・ ・ Gas diffusion electrode 6
・ ・ ・ Cathode 7 ・ ・ ・ Treatment liquid inlet 8 ・ ・ ・ Treatment liquid outlet 9, 9 '・ ・ ・ Circulation line 10 ・ ・ ・ Mist catcher 11 ・ ・ ・ Nitric oxide decomposer 12 ・ ・ ・ Discharge Line 13
..Hydrogen gas generator 14 ... Hydrogen gas supply port 15 ...
・ Gas supply pipe 16 ・ ・ ・ Waste gas outlet

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 隔膜により陽極室及び陰極室に区画され
た電解槽の陰極として気液透過性多孔性電極、三次元電
極及び流動床電極から選択される電極を使用し、硝酸性
及び/又は亜硝酸性窒素を前記陰極で還元除去する硝酸
性及び/又は亜硝酸性窒素の除去方法において、陽極と
してガス拡散電極を使用し、主に水素ガスの酸化反応を
行なうことを特徴とする硝酸性及び/又は亜硝酸性窒素
の除去方法。
1. An electrode selected from a gas-liquid permeable porous electrode, a three-dimensional electrode and a fluidized bed electrode is used as a cathode of an electrolytic cell divided into an anode chamber and a cathode chamber by a diaphragm, and a nitric acid and / or In the method for removing nitric acid and / or nitrite nitrogen by reducing and removing nitrite nitrogen at the cathode, a gas diffusion electrode is used as an anode, and an oxidation reaction of hydrogen gas is mainly performed. And / or a method for removing nitrite nitrogen.
【請求項2】 陰極で生成するガスの少なくとも一部を
陽極のガス拡散電極に供給する請求項1に記載の方法。
2. The method of claim 1, wherein at least a portion of the gas produced at the cathode is fed to the gas diffusion electrode of the anode.
【請求項3】 隔膜として陽イオン交換膜を使用する請
求項1に記載の方法。
3. The method according to claim 1, wherein a cation exchange membrane is used as the diaphragm.
【請求項4】 イオン交換膜により区画された陽極室及
び陰極室にそれぞれ収容されたガス拡散電極である陽極
及び、気液透過性多孔性電極、三次元電極及び流動床電
極から選択される陰極、前記陰極室に設置された硝酸性
及び/又は亜硝酸性窒素を含む被処理液導入口、及び前
記陰極室で生成するガスの排出口並びに陽極ガス導入口
と陽極廃ガス排出口を含んで成る硝酸性及び/又は亜硝
酸性窒素の除去装置。
4. An anode, which is a gas diffusion electrode housed in an anode chamber and a cathode chamber partitioned by an ion exchange membrane, and a cathode selected from a gas-liquid permeable porous electrode, a three-dimensional electrode and a fluidized bed electrode. A liquid to be treated containing nitric and / or nitrite nitrogen, which is installed in the cathode chamber, and an outlet for a gas generated in the cathode chamber, an anode gas inlet, and an anode waste gas outlet. A nitrate and / or nitrite nitrogen removal device comprising.
【請求項5】 陰極ガス排出口は陽極ガス導入口を接続
し、少なくとも陰極で生成するガスの一部を陽極に供給
するようにした請求項4に記載の装置。
5. The apparatus according to claim 4, wherein the cathode gas outlet is connected to the anode gas inlet so that at least a part of the gas generated at the cathode is supplied to the anode.
【請求項6】 陰極ガス排出口及び/又は陽極ガス排出
口にアンモニア及び酸化窒素分解装置を設置した請求項
4に記載の装置。
6. The apparatus according to claim 4, wherein an apparatus for decomposing ammonia and nitric oxide is installed at the cathode gas outlet and / or the anode gas outlet.
JP32961894A 1994-12-02 1994-12-02 Method and apparatus for removing nitrate and / or nitrite nitrogen Expired - Fee Related JP3615814B2 (en)

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JP3615814B2 JP3615814B2 (en) 2005-02-02

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2003066529A1 (en) * 2002-02-04 2003-08-14 Sanyo Electric Co., Ltd. Water treatment device
US6984326B2 (en) 2001-09-19 2006-01-10 Sanyo Electric Co., Ltd. Nitrogen treating method and nitrogen treating system
CN100358612C (en) * 2004-11-24 2008-01-02 黄立维 Removal of gasified harmful substance from airflow
WO2011097920A1 (en) * 2010-02-11 2011-08-18 南京大学 Method for advanced treatment of coke wastewater utilizing combination of three-dimensional electrode and coagulation

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6984326B2 (en) 2001-09-19 2006-01-10 Sanyo Electric Co., Ltd. Nitrogen treating method and nitrogen treating system
WO2003066529A1 (en) * 2002-02-04 2003-08-14 Sanyo Electric Co., Ltd. Water treatment device
CN1303005C (en) * 2002-02-04 2007-03-07 三洋电机株式会社 Water treatment device
CN100358612C (en) * 2004-11-24 2008-01-02 黄立维 Removal of gasified harmful substance from airflow
WO2011097920A1 (en) * 2010-02-11 2011-08-18 南京大学 Method for advanced treatment of coke wastewater utilizing combination of three-dimensional electrode and coagulation

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