JP2002186972A - Method and device for electrochemically removing nitrate nitrogen - Google Patents

Method and device for electrochemically removing nitrate nitrogen

Info

Publication number
JP2002186972A
JP2002186972A JP2000384335A JP2000384335A JP2002186972A JP 2002186972 A JP2002186972 A JP 2002186972A JP 2000384335 A JP2000384335 A JP 2000384335A JP 2000384335 A JP2000384335 A JP 2000384335A JP 2002186972 A JP2002186972 A JP 2002186972A
Authority
JP
Japan
Prior art keywords
diaphragm
water
nitrate nitrogen
cathode
treated
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.)
Pending
Application number
JP2000384335A
Other languages
Japanese (ja)
Inventor
Hajime Mimura
元 三村
Shotei Cho
書廷 張
Toshiki Yoshimura
敏機 吉村
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.)
Able Corp
Ebara Jitsugyo Co Ltd
Original Assignee
Able Corp
Ebara Jitsugyo Co 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 Able Corp, Ebara Jitsugyo Co Ltd filed Critical Able Corp
Priority to JP2000384335A priority Critical patent/JP2002186972A/en
Publication of JP2002186972A publication Critical patent/JP2002186972A/en
Pending legal-status Critical Current

Links

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
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • C02F2101/163Nitrates
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/46Apparatus for electrochemical processes
    • C02F2201/461Electrolysis apparatus
    • C02F2201/46105Details relating to the electrolytic devices
    • C02F2201/4611Fluid flow
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/46Apparatus for electrochemical processes
    • C02F2201/461Electrolysis apparatus
    • C02F2201/46105Details relating to the electrolytic devices
    • C02F2201/46115Electrolytic cell with membranes or diaphragms

Landscapes

  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

PROBLEM TO BE SOLVED: To conduct electrochemical denitrification with high efficiency at low cost though denitrification of waste water is mainly conducted biologically. SOLUTION: The device is provided with an ion-permeable diaphragm and a cathode plate and an anode plate disposed parallel with the diaphragm inbetween in a treatment bath, wherein moldings made of a conductive material are packed between the diaphragm and the cathode plate, and treated water is made to flow among the moldings with DC voltage or pulse voltage applied between the cathode plate and the anode plate, thereby reducing nitrate nitrogen in the treated water into nitrogen gas, and the nitrate nitrogen in the treated water is thus removed.

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】本発明は各種廃水の水処理に
関するもので、更に詳しく述べるならば、生活排水、食
品工場、化学工場、石油プラント、製紙工場、半導体工
場、産業廃棄物貯留場からの廃水等に含まれる硝酸態窒
素を還元し除去する方法および装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to the treatment of various types of wastewater, and more specifically, from domestic wastewater, food factories, chemical factories, petroleum plants, paper mills, semiconductor factories, and industrial waste storage sites. The present invention relates to a method and an apparatus for reducing and removing nitrate nitrogen contained in wastewater and the like.

【0002】[0002]

【従来の技術】廃水中の硝酸態窒素を除去する方法とし
ては、いわゆる生物処理のうち、嫌気−好気処理によっ
て硝酸態窒素を窒素ガスに変換して除去する生物脱窒法
があるが、硝酸還元細菌の同化作用を利用するため処理
する硝酸濃度に限界がある。
2. Description of the Related Art Among the so-called biological treatments, there is a biological denitrification method of converting nitrate nitrogen into nitrogen gas by anaerobic-aerobic treatment to remove nitrate nitrogen from so-called biological treatment. There is a limit to the concentration of nitric acid to be treated in order to utilize the assimilation action of reducing bacteria.

【0003】[0003]

【発明が解決しようとする課題】本発明は上記事情に鑑
みてなされたもので、生物脱窒法と比較して、より処理
時間が短く、処理経費の安価な処理法および装置を提供
することを目的とする。
SUMMARY OF THE INVENTION The present invention has been made in view of the above circumstances, and an object of the present invention is to provide a processing method and apparatus which require a shorter processing time and a lower processing cost as compared with the biological denitrification method. Aim.

【0004】[0004]

【発明が解決するための手段】本発明の請求項1記載の
処理方法は、処置槽内にイオン通過性の隔膜を設け、該
隔膜を挟んで並行に陰極および陽極の電極板を設置した
装置において、陰極と隔膜の間に導電性を有する材料で
成型された成型物を充填し、該成型物間に被処理水を通
水し、陰極と陽極間に直流電圧またはパルス電圧を印加
し、被処理水に含有されている硝酸態窒素を還元して窒
素ガス又は揮発性窒素酸化物に変換し、被処理水に含有
されている硝酸態窒を除去する硝酸態窒素の電気化学的
除去方法である。この場合、隔膜は陰極側の液体が陽極
への流体混合を阻止すると同時に該成型物と陽極の直接
接触を防止する機能を有し、イオン特に硝酸イオン透過
性でであれば何でも良いが、具体的には連続気泡のある
ポリウレタン膜、不織布膜等が利用できる。また、隔膜
は導電性のない素材のほうが望ましい。また、電極の素
材は元素の周期表におけるるる3属A,4属A、5属A,6
属A、7属A,8属、1属B、2属Bに含まれる元素および
その酸化物であり、一般に遷移金属と称される元素およ
びその酸化物を中心としてものであるが、ステンレスス
チールのような合金、炭素、炭素と金属や金属酸化物の
混合物も含まれ、導電性があるものであれば全ての素材
が利用可能である。なお、隔膜と陽極は直接接触せず空
間を形成し、陰極と成型物は直接接触しても良いし、接
触しなくても良い。成型物と隔膜は直接接触しても良い
し、接触しなくても良い。
According to a first aspect of the present invention, there is provided a treatment method comprising providing an ion-permeable diaphragm in a treatment tank, and installing a cathode and an anode electrode plate in parallel across the diaphragm. In, filling a molding molded with a material having conductivity between the cathode and the diaphragm, water to be treated is passed between the moldings, applying a DC voltage or a pulse voltage between the cathode and the anode, A method for electrochemically removing nitrate nitrogen, which reduces nitrate nitrogen contained in water to be treated and converts it into nitrogen gas or volatile nitrogen oxides to remove nitrate nitrogen contained in the water to be treated. It is. In this case, the diaphragm has a function of preventing the liquid on the cathode side from mixing the fluid with the anode and at the same time preventing a direct contact between the molded product and the anode. Specifically, a polyurethane film or a nonwoven fabric film having open cells can be used. Further, the diaphragm is preferably made of a material having no conductivity. In addition, the material of the electrode is the same as that in the Periodic Table of the Elements.
The elements and their oxides belonging to the genera A, 7A, 8A, 1B, and 2B, and mainly the elements and oxides generally called transition metals, Alloy, carbon, and a mixture of carbon and a metal or a metal oxide are also included, and all materials having conductivity can be used. The diaphragm and the anode do not directly contact each other to form a space, and the cathode and the molded product may or may not directly contact. The molding and the diaphragm may or may not directly contact.

【0005】また、印加する電圧は直流電圧およびパル
ス電圧であるが、この場合、パルス電圧とは直流電圧以
外全ての波形の電流を指している。さらに、被処理水が
成型物間を通過する方法は上向流および下向流のいずれ
でも良い。
The applied voltage is a DC voltage and a pulse voltage. In this case, the pulse voltage indicates a current having all waveforms other than the DC voltage. Further, the method of passing the water to be treated between the moldings may be either an upward flow or a downward flow.

【0006】本発明の請求項2記載の処理方法は、請求
項1記載の除去方法のうち、導電性を有する材料で成型
された成型物が、金属、または金属の酸化物およびこれ
らの混合物を用いて成型した薄片状、球状、円筒状の成
型物である硝酸態窒素の電気化学的除去方法である。本
発明に使用される成型物の形状については特に制限がな
く、例えば薄片状、球状、円柱状などいずれでも良い
が、接触面積を増大するために珪素等の元素を混入させ
て成型物表面の祖度を増加させ、表面積を大きくするこ
ともできる。金属の種類は元素の周期表における3属
A,4属A、5属A,6属A、7属A,8属、1属B、2属B
に含まれる元素およびその酸化物であり、一般に遷移金
属と称される元素およびその酸化物を中心としてもので
あるが、ステンレススチールのような合金も含まれる。
According to a second aspect of the present invention, there is provided the treatment method according to the first aspect, wherein the molded article molded from the conductive material is formed of a metal, a metal oxide, or a mixture thereof. This is a method for electrochemically removing nitrate nitrogen, which is a flaky, spherical, or cylindrical molded product. The shape of the molded product used in the present invention is not particularly limited, and may be, for example, a flake shape, a spherical shape, a columnar shape, or the like. It can also increase ancestry and increase surface area. Kinds of metals are 3 genus A, 4 genus A, 5 genus A, 6 genus A, 7 genus A, 8 genus, 1 genus B, 2 genus B in the periodic table of elements.
And oxides thereof, which are mainly composed of elements generally called transition metals and oxides thereof, but also include alloys such as stainless steel.

【0007】本発明の請求項3記載の処理方法は、請求
項1記載の除去方法のうち、導電性を有する材料で成型
された成型物が、炭素および炭素と金属、または金属の
酸化物の混合物を用いて成型した成型物である硝酸態窒
素の電気化学的除去方法である。本発明に使用される成
型物の形状については特に制限がなく、例えば薄片状、
球状、円柱状などいずれでも良いが、接触面積を増大す
るために固形表面に微細孔を形成させても良い。炭素に
混合する素材としては、元素の周期表におけるるる3属
A,4属A、5属A,6属A、7属A,8属、1属B、2属B
に含まれる元素およびその酸化物であり、一般に遷移金
属と称される元素およびその酸化物が考えられる。炭素
のみでも電気伝導性を有するので単独で使用可能である
が、遷移金属を混入されると、硝酸の還元能力が増加す
ることが、我々の実験で確認できている。
According to a third aspect of the present invention, there is provided the treatment method according to the first aspect, wherein the molded article molded from the conductive material is formed of carbon and carbon and metal, or a metal oxide. This is a method for electrochemically removing nitrate nitrogen, which is a molded product molded using a mixture. There is no particular limitation on the shape of the molded product used in the present invention, for example, flaky,
Any of a spherical shape, a columnar shape and the like may be used, but fine holes may be formed on a solid surface to increase a contact area. As the material to be mixed with carbon, there are three genera A, four genera A, five genera A, six genera A, seven genera A, eight genera, one genera B, and two genera B in the periodic table of elements.
And oxides thereof, which are generally called transition metals and oxides thereof. Although carbon alone has electrical conductivity, it can be used alone, but it has been confirmed in our experiments that the incorporation of a transition metal increases the nitric acid reducing ability.

【0008】本発明の請求項4記載の処理方法は、請求
項1記載の除去方法のうち、隔膜と陽極間に浸出した被
処理水を隔膜と陰極間に返送する硝酸態窒素の電気化学
的除去方法である。返送の方法は循環ポンプによる方
法、水中ポンプによる方法、エアリフトによる方法、陽
極と隔膜間の底部から流出させ、被処理水の流入ライン
に合流する方法等が考えられるがいずれの方法でも良
い。
According to a fourth aspect of the present invention, there is provided a method as defined in the first aspect, wherein the water to be treated leached between the membrane and the anode is returned between the membrane and the cathode. This is the removal method. As a method of returning, a method using a circulating pump, a method using a submersible pump, a method using an air lift, a method of flowing out from the bottom between the anode and the diaphragm, and merging with the inflow line of the water to be treated can be considered, but any method may be used.

【0009】本発明の請求項5記載の処理装置は、請求
項4記載の除去方法のうち、被処理水および返送する被
処理水をpH8以下にする硝酸態窒素の電気化学的除去
方法である。具体的には被処理水および返送する被処理
水をpH調整槽に貯留させ塩酸、硫酸、酢酸等の酸を添
加しpH調整後処理槽に流入させる方法や流入管や返送
管にスタチィックミキサーを設置し、直接インジェクタ
ーで酸を添加する方法等が考えられる。
According to a fifth aspect of the present invention, there is provided the treatment apparatus according to the fourth aspect, wherein the water to be treated and the water to be returned are subjected to electrochemical removal of nitrate nitrogen. . More specifically, the water to be treated and the water to be returned are stored in a pH adjusting tank, and an acid such as hydrochloric acid, sulfuric acid, or acetic acid is added thereto, and the pH is adjusted. And a method of directly adding an acid with an injector can be considered.

【0010】本発明の請求項6記載の処理装置は、処置
槽内にイオン通過性の隔膜を設け、該隔膜を挟んで並行
に陰極および陽極の電極板を設置し、陰極と隔膜の間に
導電性を有する材料で成型された成型物を充填した充填
層を基本構成とした硝酸態窒素の電気化学的除去装置で
ある。
According to a sixth aspect of the present invention, in the treatment apparatus, an ion-permeable diaphragm is provided in the treatment tank, and a cathode and an anode electrode plate are installed in parallel with the diaphragm interposed therebetween. This is an apparatus for electrochemically removing nitrate nitrogen, which is basically composed of a packed bed filled with a molded product formed of a conductive material.

【0011】[0011]

【発明の実施の形態】以下に、本発明の実施の形態に係
る硝酸態窒素の電気化学的除去方法および装置について
説明する。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS A method and an apparatus for electrochemically removing nitrate nitrogen according to an embodiment of the present invention will be described below.

【0012】まず、図1に従って、本発明の実施形態に
ついて説明する。
First, an embodiment of the present invention will be described with reference to FIG.

【0013】図1は硝酸態窒素の電気化学的除去装置の
概略図である。処理槽5内にイオン通過性の隔膜6を設
け、該隔膜を挟んで並行に陰極1および陽極4の電極板
を設置してあり、陰極1と隔膜6の間に導電性を有する
材料で成型された成型物7を充填する。
FIG. 1 is a schematic view of an apparatus for electrochemically removing nitrate nitrogen. An ion-permeable diaphragm 6 is provided in the processing tank 5, and an electrode plate of the cathode 1 and the anode 4 is installed in parallel with the diaphragm interposed therebetween, and is formed of a conductive material between the cathode 1 and the diaphragm 6. The molded article 7 is filled.

【0014】被処理水は流入管2を通して、処理槽5に
流入し、成型物7を通過して、流出管8より放流され
る。必要に応じて成型物7の底面に散気管を設置し、曝
気や循環ポンプにより処理水を攪拌し成型物と処理水の
接触効率を増強しても良い。また、被処理水の流れる方
向は図1では下向流であるが上向流でも良い。
The water to be treated flows into the treatment tank 5 through the inflow pipe 2, passes through the molded product 7, and is discharged from the outflow pipe 8. If necessary, an air diffuser may be provided on the bottom surface of the molded product 7 to agitate the treated water by aeration or a circulation pump to enhance the contact efficiency between the molded product and the treated water. Further, the flow direction of the water to be treated is a downward flow in FIG. 1, but may be an upward flow.

【0015】陰極1は成型物と接触させて設置し、成型
物はマイナスの電荷を受ける。成型物間を通過する硝酸
イオンはマイナス電荷を受けて還元され亜硝酸を経て、
または直接、窒素ガスや揮発性の窒素酸化物に変換され
る。
The cathode 1 is placed in contact with a molded product, and the molded product receives a negative charge. The nitrate ions passing between the moldings are reduced by receiving a negative charge, and pass through nitrous acid.
Alternatively, it is directly converted to nitrogen gas or volatile nitrogen oxides.

【0016】一方、陽極側は隔膜を通過した硝酸イオン
が濃縮されるので、返送管3を通じて、陰極1と隔膜6
の間に返送すると硝酸の還元が効率よく行える。図1で
は、返送を水中ポンプで行う場合について示している
が、循環ポンプやエアリフトによる方法も可能である。
また、取水の位置は処理槽の底部、表層部、中層部のい
ずれでも良いし、処理槽の陽極と隔膜間の底面に返送管
を設置し、循環ポンプを介して流入管2に返送しても良
い。
On the other hand, on the anode side, nitrate ions passing through the diaphragm are concentrated, so that the cathode 1 and the diaphragm 6 are returned through the return pipe 3.
If it is returned during the period, nitric acid can be reduced efficiently. FIG. 1 shows a case where the return is performed by a submersible pump, but a method using a circulation pump or an air lift is also possible.
In addition, the position of water intake may be any of the bottom part, the surface part, and the middle part of the treatment tank, or a return pipe is installed on the bottom surface between the anode and the diaphragm of the treatment tank, and returned to the inflow pipe 2 via the circulation pump. Is also good.

【0017】また、被処理水および陽極側よりの返送水
についてはpHを調整せずに処理できるが、pH8以下
の方が硝酸が還元される効率が高いので、被処理水およ
び陽極側よりの返送水を図示されていないpH調整槽に
収容後、pH調整をして処理槽5に流入させても良い。
また、流入管2や返送管の一部に図示していないスタテ
ィックミキサーを設けて、インジェクターから酸を直接
注入しても良い。
The water to be treated and the water returned from the anode side can be treated without adjusting the pH. However, since the efficiency of nitric acid reduction is higher at a pH of 8 or less, the pH of the water to be treated and the water returned from the anode side are higher. After returning water is stored in a pH adjusting tank (not shown), the pH may be adjusted and flown into the processing tank 5.
Further, a static mixer (not shown) may be provided in a part of the inflow pipe 2 or the return pipe, and the acid may be directly injected from the injector.

【0018】[0018]

【実施例】以下、本発明を実施例により更に説明する。
表1は硝酸イオンを含む工場排水を本装置で処理した結
果を示す。また凝集沈殿処理も同時に行い結果を比較し
た。
EXAMPLES The present invention will be further described below with reference to examples.
Table 1 shows the results of treating industrial wastewater containing nitrate ions with this device. In addition, coagulation sedimentation was performed at the same time, and the results were compared.

【0019】 実験の結果、30分処理で原水の89.7%、60分処理で97.6
%の除去率が得られたが、凝集沈殿では殆ど効果が見ら
れなかった。
[0019] As a result of the experiment, 89.7% of raw water in 30 minutes treatment, 97.6% in 60 minutes treatment
% Removal rate, but little effect was seen in coagulation sedimentation.

【0020】一方、この排水の生物脱窒処理を行うに
は、処理水を嫌気性にする必要があり嫌気槽が必要にな
るほか、BODの低い処理水では嫌気状態にすることが
難しい。
On the other hand, in order to carry out the biological denitrification treatment of this wastewater, it is necessary to make the treated water anaerobic, which requires an anaerobic tank, and it is difficult to make the treated water having a low BOD an anaerobic state.

【0021】[0021]

【発明の効果】このように、本発明を利用すると、生物
脱窒法では難しい処理水でも、効率良く脱窒することが
できる。また、本発明の処理には生物が関与しないの
で、高濃度の硝酸イオンが含まれる排水や低温化での処
理でも効率良く処理ができる。
As described above, when the present invention is utilized, it is possible to efficiently denitrify treated water which is difficult by the biological denitrification method. In addition, since the living thing does not participate in the treatment of the present invention, the treatment can be efficiently performed even in a wastewater containing a high concentration of nitrate ions or a treatment at a low temperature.

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

【図1】本発明の実施の形態に係る処理装置の概略図で
ある。
FIG. 1 is a schematic diagram of a processing apparatus according to an embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1:陰極 2:流入管 3:返送管 4:陽極 5:処理槽 6:隔膜 7:成型物充填層 8:流出管 9:返送ポンプ 10:成型物 1: Cathode 2: Inflow pipe 3: Return pipe 4: Anode 5: Treatment tank 6: Diaphragm 7: Molded bed 8: Outflow pipe 9: Return pump 10: Molded article

───────────────────────────────────────────────────── フロントページの続き (72)発明者 張 書廷 埼玉県坂戸市溝端町1丁目3番501号 (72)発明者 吉村 敏機 埼玉県川越市吉田642番13号 Fターム(参考) 4D061 DA08 DB18 DC14 EA04 EB01 EB07 EB13 EB17 EB19 EB22 EB27 EB28 EB29 EB31  ────────────────────────────────────────────────── ─── Continuing on the front page (72) Inventor Zhang Court 1-35-1, Mizobata-cho, Sakado-shi, Saitama (72) Inventor Toshiki Yoshimura 642-113, Yoshida, Kawagoe-shi, Saitama F-term (reference) 4D061 DA08 DB18 DC14 EA04 EB01 EB07 EB13 EB17 EB19 EB22 EB27 EB28 EB29 EB31

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】処置槽内にイオン通過性の隔膜を設け、該
隔膜を挟んで並行に陰極および陽極の電極板を設置した
装置において、陰極と隔膜の間に導電性を有する材料で
成型された成型物を充填し、該成型物間に被処理水を通
水し、陰極と陽極間に直流電圧またはパルス電圧を印加
し、被処理水に含有されている硝酸態窒素を還元して窒
素ガス又は揮発性窒素酸化物に変換し、被処理水に含有
されている硝酸態窒を除去する硝酸態窒素の電気化学的
除去方法。
1. An apparatus in which an ion-permeable diaphragm is provided in a treatment tank, and a cathode and an anode electrode plate are provided in parallel with the diaphragm interposed therebetween, and is formed of a conductive material between the cathode and the diaphragm. The molded product is filled, treated water is passed between the molded products, a DC voltage or a pulse voltage is applied between the cathode and the anode, and nitrate nitrogen contained in the treated water is reduced to reduce nitrogen. A method for electrochemically removing nitrate nitrogen, which converts into gas or volatile nitrogen oxides and removes nitrate nitrogen contained in the water to be treated.
【請求項2】請求項1記載の除去方法のうち、導電性を
有する材料で成型された成型物が、金属、または金属の
酸化物およびこれらの混合物を用いて成型した成型物で
ある硝酸態窒素の電気化学的除去方法。
2. The removing method according to claim 1, wherein the molded article molded from a conductive material is a molded article molded from a metal, a metal oxide, or a mixture thereof. A method for electrochemical removal of nitrogen.
【請求項3】請求項1記載の除去方法のうち、導電性を
有する材料で成型された成型物が、炭素および炭素と金
属、または金属の酸化物の混合物を用いて成型した成型
物である硝酸態窒素の電気化学的除去方法。
3. The removing method according to claim 1, wherein the molded article molded from a material having conductivity is a molded article molded using carbon and a mixture of carbon and metal, or a metal oxide. A method for electrochemical removal of nitrate nitrogen.
【請求項4】請求項1記載の除去方法のうち、隔膜と陽
極間に浸出した被処理水を隔膜と陰極間に返送する硝酸
態窒素の電気化学的除去方法。
4. The method according to claim 1, wherein the water to be treated leached between the membrane and the anode is returned between the membrane and the cathode.
【請求項5】請求項3記載の除去方法のうち、被処理水
および返送する被処理水をpH8以下に調整する硝酸態
窒素の電気化学的除去方法。
5. The method of electrochemically removing nitrate nitrogen according to claim 3, wherein the water to be treated and the water to be returned are adjusted to pH 8 or less.
【請求項6】処置槽内にイオン通過性の隔膜を設け、該
隔膜を挟んで並行に陰極および陽極の電極板を設置し、
陰極と隔膜の間に導電性を有する材料で成型された成型
物を充填した充填層を基本構成とした硝酸態窒素の電気
化学的除去装置。
6. An ion-permeable diaphragm is provided in the treatment tank, and a cathode and an anode electrode plate are installed in parallel with the diaphragm interposed therebetween.
An electrochemical device for removing nitrate nitrogen, which is basically composed of a packed bed filled with a molded product formed of a conductive material between a cathode and a diaphragm.
JP2000384335A 2000-12-18 2000-12-18 Method and device for electrochemically removing nitrate nitrogen Pending JP2002186972A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000384335A JP2002186972A (en) 2000-12-18 2000-12-18 Method and device for electrochemically removing nitrate nitrogen

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000384335A JP2002186972A (en) 2000-12-18 2000-12-18 Method and device for electrochemically removing nitrate nitrogen

Publications (1)

Publication Number Publication Date
JP2002186972A true JP2002186972A (en) 2002-07-02

Family

ID=18851816

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000384335A Pending JP2002186972A (en) 2000-12-18 2000-12-18 Method and device for electrochemically removing nitrate nitrogen

Country Status (1)

Country Link
JP (1) JP2002186972A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100404434C (en) * 2005-01-28 2008-07-23 田宝凤 Method of dynamic treating sewage of papermaking to zero discharge standard and treatment agent
JP2013027864A (en) * 2011-06-24 2013-02-07 Ihi Corp Method and device for treating exhaust gas
WO2013085022A1 (en) * 2011-12-09 2013-06-13 パナソニック株式会社 Nitrate reduction method, nitrate reduction catalyst, nitrate reduction electrode, fuel cell, and water treatment apparatus

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN100404434C (en) * 2005-01-28 2008-07-23 田宝凤 Method of dynamic treating sewage of papermaking to zero discharge standard and treatment agent
JP2013027864A (en) * 2011-06-24 2013-02-07 Ihi Corp Method and device for treating exhaust gas
WO2013085022A1 (en) * 2011-12-09 2013-06-13 パナソニック株式会社 Nitrate reduction method, nitrate reduction catalyst, nitrate reduction electrode, fuel cell, and water treatment apparatus
JP5655161B2 (en) * 2011-12-09 2015-01-14 パナソニック株式会社 Nitrate reduction method, nitrate reduction catalyst, nitrate reduction electrode, fuel cell, and water treatment apparatus

Similar Documents

Publication Publication Date Title
Ozyonar et al. Operating cost analysis and treatment of domestic wastewater by electrocoagulation using aluminum electrodes
KR100906742B1 (en) Treatment method and the apparatus including ultasonic-electrolysis-precipitator and complexed upper filter isolator for domestic sewage or wasted water
CN205313291U (en) Refrigeration cycle water integrated processing system
CN103466885A (en) Process for treating wastewater generated in solar silicon wafer production process
CN105084648A (en) Treatment method for hardly biodegraded sewage
CN206814454U (en) A kind of aeration reinforcing micro-electrolysis reaction device for sewage disposal
KR20170010679A (en) Treatnent system for organic livestock wastewater by electrolytic oxidation and treatment method thereof
CN205313289U (en) Cooling circulating water treatment system
CN207845373U (en) A kind of emulsified waste liquid processing unit
WO2022082954A1 (en) System and method for treating preparation wastewater by using multi-phase multi-dimensional electrolysis pretreatment process+a/o+mbr
JP2002186972A (en) Method and device for electrochemically removing nitrate nitrogen
KR100420314B1 (en) The Wastewater Treatment Method and its System
CN208949065U (en) A kind of electric flocculation, magnetic flocculation and the integrated sewage treatment unit of multi-stage oxidizing and system
CN110498490A (en) A kind of electric flocculation reactor and its application
CN103553278A (en) Sewage treatment method and electroflocculation membrane bioreactor thereof
CN108128942A (en) A kind of modular electrochemistry sewage disposal device
CN110668642A (en) Electrochemical coupling advanced oxidation process and device suitable for deep treatment of waste leachate
CN104496086B (en) A kind of electrolysis coupling class Fenton water treatment facilities
CN210261261U (en) Efficient nitrogen and phosphorus removal system for treating aquaculture tail water
CN209128246U (en) A kind of integrated apparatus for Sewage from Ships processing
CN201458871U (en) Waste water COD treatment equipment
JPH0148834B2 (en)
CN217418467U (en) Pesticide effluent disposal system
CN111995040B (en) High-concentration nonbiodegradable organic wastewater treatment equipment and method
JP2005246134A (en) Method for treating organic wastewater