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JP2000334462A - Packed bed type electrochemical water treating device and method therefor - Google Patents

Packed bed type electrochemical water treating device and method therefor

Info

Publication number
JP2000334462A
JP2000334462A JP11149559A JP14955999A JP2000334462A JP 2000334462 A JP2000334462 A JP 2000334462A JP 11149559 A JP11149559 A JP 11149559A JP 14955999 A JP14955999 A JP 14955999A JP 2000334462 A JP2000334462 A JP 2000334462A
Authority
JP
Japan
Prior art keywords
electrochemical
granular
raw water
medium
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.)
Pending
Application number
JP11149559A
Other languages
Japanese (ja)
Inventor
Hosho Ro
呂芳鐘
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.)
TSUKEIKO YUGENKOSHI
Original Assignee
TSUKEIKO YUGENKOSHI
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 TSUKEIKO YUGENKOSHI filed Critical TSUKEIKO YUGENKOSHI
Priority to JP11149559A priority Critical patent/JP2000334462A/en
Publication of JP2000334462A publication Critical patent/JP2000334462A/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
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46109Electrodes
    • 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
    • C02F1/46114Electrodes in particulate form or with conductive and/or non conductive particles between them

Landscapes

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

Abstract

PROBLEM TO BE SOLVED: To remove contamination substances such as organic matters and inorganic matters in water by simultaneously applying an oxidation work, are reduction work, an electrolytic corrosion work, an electric neutralization work and a flotation work, and the like, with respect to water. SOLUTION: Granular media 4 are provided between a minus and a plus electrodes 2,3 in an electrochemical tank, and an electric field work is formed between the minus and plus electrodes 2, 3 so that electrical chemistry is utilized. Between the contamination substances in the raw water in the tank and the granular media 4, an electron transfer mechanism is generated. Fine air bubbles generated by utilizing the oxidation-reduction reaction and an aggregation work or the oxidation-reduction reaction alone, float flocks generated by the aggregation work on a water level and the flocks are removed, and simultaneously, the organic and inorganic contamination substances in the waste water are 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】本発明は水処理装置とその方
法に関し、特に電気化学反応を利用して水処理を行う技
術に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a water treatment apparatus and method, and more particularly to a technique for performing water treatment using an electrochemical reaction.

【0002】[0002]

【従来の技術】水は人類が生存するのに必要な重要な元
素の一つで、食用或いは日常生活の入浴、食器等の洗浄
水に限らず、全ての水は使用した後に川や池に排水す
る。その水は有機物或いは無機物等の雑質を多少とも含
んで汚染されている。地球上の水資源は限られているた
め、使用後あるいは汚染された水は処理を行い、処理後
の水は再使用して、水資源を有効に利用する。しかし従
来の濾過式或いは薬剤等による処理方法では有機物或い
は無機物等の雑質を有効に除去することができなかっ
た。
2. Description of the Related Art Water is one of the important elements necessary for the survival of mankind, and is not limited to edible or everyday life bathing, washing water for dishes, etc. Drain. The water is contaminated by containing some impurities such as organic substances or inorganic substances. Since the water resources on the earth are limited, the used or contaminated water is treated, and the treated water is reused to effectively use the water resources. However, conventional filtration methods or treatment methods using chemicals or the like cannot effectively remove impurities such as organic substances and inorganic substances.

【0003】[0003]

【発明が解決しようとする課題】電流の作用により電気
化学反応を発生させて、電気エネルギーを化学エネルギ
ーに変換する。水に対して酸化作用、還元作用、電食作
用、電気中和作用及び浮選作用等を同時に行い、水中の
有機物、無機物等の汚物除去を行う。
The electric energy is converted into chemical energy by generating an electrochemical reaction by the action of an electric current. Simultaneously performs an oxidizing action, a reducing action, an electrolytic corrosion action, an electrical neutralizing action, a flotation action, and the like on water, and removes dirt such as organic and inorganic substances in the water.

【0004】[0004]

【課題を解決するための手段】槽内のマイナスとプラス
極間に顆粒状の媒介質を設置、マイナスとプラス極間に
電場作用を形成して電気化学を利用する。この電気化学
槽の原水中の汚染物質と顆粒状媒介質に電子移転メカニ
ズムを発生させる。酸化還元反応と凝結作用、また酸化
還元反応を利用して発生させた細微気泡が凝結作用で発
生したフロック(floc)を水面上に浮き上がらせて除去
し、同時に廃水中の有機及び無機汚染物を除去する。
Means for Solving the Problems A granular medium is provided between a negative electrode and a positive electrode in a tank, and an electric field action is formed between the negative electrode and the positive electrode to utilize electrochemistry. An electron transfer mechanism is generated for pollutants and granular media in the raw water of this electrochemical tank. Oxidation-reduction reaction and coagulation action, and fine bubbles generated using the oxidation-reduction reaction float off the flocs generated by coagulation action on the water surface and remove them, and at the same time remove organic and inorganic pollutants in wastewater. Remove.

【0005】[0005]

【発明の実施の形態】本発明は電気化学原理を利用した
もので、水処理の方法と装置に関する。電流の作用で電
気化学反応を発生させ、電気エネルギーを化学エネルギ
ーに変化させて水を電気化学機内で酸化作用、還元作
用、電食作用、電気中和作用及び浮選作用等を同時に進
め、水中の有機物或いは無機物等の混合物を除去する。
その各作用は下記の通りである。 酸化作用:プラス電極上の二つの基本酸化反応を利用す
る。 (一)直接酸化:プラス電極の極板で酸素分子を発生さ
せ、直接に有機物の酸化反応を進める。 (二)間接反応:水中の塩化ナトリウム(NaCl)電解を
利用して次亜塩素イオン(OC1−)或いは次亜塩素酸(H
OC1−)を発生させ水中の汚染物を破壊する。 還元作用:マイナス電極の極板上に発生する水素(H
2)と酸化水素イオン(OH−)の酸化状態の雑質に対
する還元作用を利用して浄化効果を達成する。 電食作用:適当な電場強度と電流密度の条件下、プラス
電極は金属解離の作用を発生する。この解離した金属イ
オン純度は市販されている凝結剤が含む金属イオンより
はるかに高く、より強い凝結効果がある。 電気中和作用:水中雑質の電荷が中和し、その安定度を
破壊して、雑質を簡単に凝結させる。 浮選作用:酸化、還元作用で発生した水素(H2)と酸
素(O2)の気泡直径は非常に小さくて均等であるた
め、とても有効的に雑質を凝結させて水面上に浮き上が
らせ固液分離設備でとる。
DETAILED DESCRIPTION OF THE INVENTION The present invention is based on electrochemical principles and relates to a method and apparatus for water treatment. An electrochemical reaction is generated by the action of electric current, the electric energy is changed to chemical energy, and water is simultaneously oxidized, reduced, eroded, neutralized, flotated, etc. A mixture of organic substances or inorganic substances.
The actions are as follows. Oxidation: utilizes two basic oxidation reactions on the positive electrode. (1) Direct oxidation: Oxygen molecules are generated by the positive electrode plate to directly promote the oxidation reaction of organic substances. (2) Indirect reaction: Using sodium chloride (NaCl) electrolysis in water, hypochlorite (OC1-) or hypochlorous acid (H
OC1−) is generated, destroying pollutants in water. Reduction action: Hydrogen generated on the negative electrode plate (H
(2) A purifying effect is achieved by utilizing the reducing action of hydrogen oxide ions (OH-) on impurities in the oxidized state. Electrolytic corrosion: Under appropriate electric field strength and current density, the positive electrode produces a metal dissociation effect. The purity of the dissociated metal ions is much higher than the metal ions contained in the commercially available coagulants, and has a stronger coagulation effect. Electro-neutralization action: neutralizes the charge of the underwater foreign matter, destroys its stability, and easily contaminates the foreign matter. Flotation: Hydrogen (H2) and oxygen (O2) generated by oxidation and reduction have very small and uniform bubble diameters, so they can effectively condense and float on the water surface and solid-liquid. Take in separation equipment.

【0006】図1に示すのは本発明の基本組立図で、相
関電気化学の作用力を結合、また単体構造方式により製
作して、電気化学機1はどんなタイプの柱状の主体でも
よい。中空状を呈する内部が内部充填区17で、大量の
顆粒状媒介質4を設置するのに使用する(図5参照)。
顆粒状媒介質4は導電性を有する、例えば鉄(Fe)、ア
ルミニウム(Al)、マグネシウム(Mg)、鉛(Pb)等の
材料で、その形状は規則或いは不規則の顆粒状で、原水
の特性に適合する材質を選択する。内部充填区17の上
下にそれぞれ多孔板2を設け、下方の多孔板2を傾斜さ
せ顆粒状媒介質4及び水中雑質が顆粒状媒介質排出口1
5で電気化学機1から排出されやすいようにする。電気
化学機1の進出口端部にそれぞれ多孔電極板3を設け、
多孔電極板3の材質は例えばステンレス、グラファイト
等の不活性金属で、多孔電極板3をそれぞれ直流電流供
給器のマイナス、プラス極上に接続し、電気化学機1が
必要な電場と電流を提供し、相関の電気化学作用を進め
る。電気化学機1の外側上下端部にそれぞれ原水進流口
12と処理水出口13を設ける。他に多孔板2外側の電
気化学機1の適当な位置にそれぞれ顆粒状媒介質補充口
14及び顆粒状媒介質排出口15を設ける。顆粒状媒介
質4は電気化学の電食作用で消耗したとき、或いは原水
中の雑質が内部充填区17を流れて、濾過作用で内部充
填区17が詰まった時、ただちに顆粒状媒介質排出口1
5から定時排出される。同時に再び顆粒状媒介質補充口
14から洗浄或いは再生後の顆粒状媒介質4を補充し、
電気化学機1の効率を維持する。さらに電気化学機1の
下端部に沈積物排出口16を設ける。原水を電気化学機
1に入れ、原水が含む比較的大きい雑質、或いは内部充
填区17の作用により小さくなった雑質は下方の多孔板
2から流れ落ちて沈積物排出口16から排出される。原
水進流口12、沈積物排出口16及び顆粒状媒介質補充
口14及び顆粒状媒介質排出口15の適当な位置にそれ
ぞれ電動或いは手動のバルブ11を設け、全自動或いは
手動方式により原水排入、雑質排出或いは顆粒状媒介質
4の補充、排出をコントロールする事ができる。
FIG. 1 is a basic assembly drawing of the present invention, in which the correlated electrochemical action force is combined and manufactured by a single structure method, and the electrochemical machine 1 may be any type of columnar main body. The interior having a hollow shape is an internal filling section 17 which is used for installing a large amount of granular media 4 (see FIG. 5).
The granular medium 4 is a material having conductivity, for example, iron (Fe), aluminum (Al), magnesium (Mg), lead (Pb) or the like. Select a material that meets the characteristics. The perforated plates 2 are respectively provided above and below the inner filling section 17, and the perforated plates 2 are inclined downward so that the granular medium 4 and the underwater foreign substances are discharged into the granular medium outlet 1.
5 makes it easier to discharge from the electrochemical machine 1. A porous electrode plate 3 is provided at each of the entrance and exit ends of the electrochemical machine 1,
The material of the porous electrode plate 3 is, for example, an inert metal such as stainless steel or graphite. The porous electrode plate 3 is connected to the minus and plus poles of the DC current supply, respectively, and the electrochemical machine 1 provides the necessary electric field and current. Advance the correlated electrochemical action. A raw water inflow port 12 and a treated water outlet 13 are provided at the outer upper and lower ends of the electrochemical machine 1, respectively. In addition, a granular medium replenishing port 14 and a granular medium discharging port 15 are provided at appropriate positions on the electrochemical machine 1 outside the perforated plate 2. When the granular medium 4 is consumed by electrochemical erosion, or when impurities in raw water flow through the internal filling section 17 and the internal filling section 17 is clogged by filtration, the granular medium 4 is immediately discharged. Exit 1
5 to be discharged on a regular basis. At the same time, replenish the granular medium 4 after washing or regeneration from the granular medium replenishing port 14 again,
Maintain the efficiency of the electrochemical machine 1. Further, a deposit 16 is provided at the lower end of the electrochemical machine 1. The raw water is put into the electrochemical machine 1, and the relatively large impurities contained in the raw water or the impurities reduced by the action of the internal filling section 17 flow down from the perforated plate 2 below and are discharged from the sludge discharge port 16. An electric or manual valve 11 is provided at an appropriate position of the raw water inflow port 12, the sludge discharge port 16, the granular medium replenishment port 14, and the granular medium discharge port 15, respectively, and the raw water is discharged by a fully automatic or manual method. It is possible to control the input, discharge of foreign substances, or the replenishment and discharge of the granular medium 4.

【0007】電気化学機1の断面積を処理したい原水量
に合わせて変化させ、電気化学機1の断面積は処理量の
増加に合わせて増やすことができる。電気化学機1の長
さは原水の雑質量に合わせて変化させ、雑質の量が多け
れば多いほどその長さを長くする(図2、図3、図4参
照)。電気化学機1は直列或いは並列式の組合せにし、
処理能率を上げたいとき直列方式を採用し、処理量を増
やしたいときは並列方式を採用する。またニーズに合わ
せて直並列合併方式を組み合わせて、直立式、水平式或
いはあらゆる角度の組み合わせ方式で取り付ける。これ
らは全て電気化学機1単体の処理量及び処理効果に影響
がない。図5に示すように、顆粒状媒介質4の装置はラ
ンダム方式で投入し、堆積方式は媒介質ランダム方式で
成型し、顆粒状媒介質4は両端が直流電流電場の作用を
受けて感応しプラス、マイナス方式に並ぶ(図6参
照)。顆粒状媒介質4間の隙間は原水が流れる隙間を提
供し、それぞれの隙間は微小電池のメカニズムを構成
し、相関の電気化学作用を進める。また隙間が微小のた
め、電気化学の反応がより速く完全となる。図7に示す
のは本発明の処理システム流れ図で、原水槽Aは原水の
収集と流れを調節するのに使用し、原水輸送ポンプBで
原水を電気化学システムへ送る。安定した流れにするた
め管線上に流量計C及び流量コントロールバルブDを設
け、電気化学システムに入る原水量をコントロールして
設定する。原水が電気化学機1に入る前の、電気化学機
1前に快速ミキサーEを設ける。快速ミキサーEはph値
を調整し、ph値が低くなりすぎて(ph<3)処理システ
ムを腐食させないようにすることである。快速ミキサー
Eで調整後の原水を電気化学機1内に入れて処理する。
電気化学機1単体が並列、直列或いは直並列方式を組み
合わせて構成し、各種の違う特性の原水水質と水量に対
応させる。電気化学機1が必要な電場及び電流は直流電
気供給器Hが提供する。
The cross-sectional area of the electrochemical machine 1 is changed according to the amount of raw water to be treated, and the cross-sectional area of the electrochemical machine 1 can be increased in accordance with an increase in the amount of treatment. The length of the electrochemical machine 1 is changed in accordance with the coarse mass of the raw water, and the longer the amount of the impurities, the longer the length (see FIGS. 2, 3, and 4). The electrochemical machine 1 is a combination of series or parallel,
The serial system is used to increase the processing efficiency, and the parallel system is used to increase the processing amount. In addition, according to the needs of the series and parallel merger, the system can be mounted upright, horizontal or at any angle. All of these do not affect the processing amount and processing effect of the electrochemical machine 1 alone. As shown in FIG. 5, the apparatus of the granular medium 4 is charged in a random manner, the deposition method is formed by a medium random method, and both ends of the granular medium 4 respond to the action of a direct current electric field. It is lined up in plus and minus systems (see FIG. 6). The gaps between the granular media 4 provide gaps through which the raw water flows, and each gap constitutes the mechanism of the microbattery and drives the correlated electrochemical action. Also, because the gap is very small, the electrochemical reaction is faster and more complete. Shown in FIG. 7 is a flow diagram of the treatment system of the present invention, where raw water tank A is used to regulate the collection and flow of raw water, and raw water transport pump B sends raw water to the electrochemical system. A flow meter C and a flow control valve D are provided on the pipeline for a stable flow, and the amount of raw water entering the electrochemical system is controlled and set. Before the raw water enters the electrochemical machine 1, a rapid mixer E is provided in front of the electrochemical machine 1. Rapid mixer E adjusts the ph value so that the ph value is not too low (ph <3) to corrode the processing system. Raw water adjusted by the high-speed mixer E is put into the electrochemical machine 1 for processing.
The single electrochemical device 1 is configured by combining the parallel, series or series-parallel systems to correspond to the raw water quality and amount of various different characteristics. The electric field and current required by the electrochemical machine 1 are provided by a DC electric supply H.

【0008】原水を電気化学機1で各種反応メカニズム
作用後、原水中の有機性及び無機性雑質は集まって比較
的大きいフロック(floc)を形成し、同時に電気化学機
1の反応メカニズム作用で発生した水素(H2)と酸素
(O2)の微小気泡はフロック(floc)上に付着し、こ
の時、原水はもう一つの快速ミキサーG内へ入る。固液
分離メカニズムの速度率を加速し、快速ミキサーG内に
凝結剤と凝結補助剤を選択して加える。顆粒状媒介質4
は電食作用で解離の金属イオンのため優れた凝結剤であ
る。原水が快速ミキサーG内に進入した後、凝結剤と凝
結補助剤を素早く混ぜ、混合後の原水は浮選槽I中に入
り、付着して集まった多くの微小気泡のフロックは浮力
により素早く浮選槽Iの水面上に浮き上がり、スカム除
去器I2を利用して取って分離する。さらにスカム除去
器I2の水平旋回により浮いたスカムをスカム収集じょ
うごI1内に入れ、処理後の水はスカム板I3を通った
後、モーターFで送り出されて排水或いは再利用する。
除去したスカムはスカム貯蔵槽Jに入れ、後続の脱水ユ
ニットの最終処理へ送る。電気化学機1内の顆粒状媒介
質4は電食作用により徐々に消耗し、同時に充填床式の
装置は原水の大顆粒状の雑質が内部充填区17内に堆積
して詰まりを発生させる。そのため顆粒状媒介質補充口
14と顆粒状媒介質排出口15を利用して適時に排出と
補充の作業を行い、処理作業を中断せずに、簡単に顆粒
状媒介質4と堆積した雑質を排出して媒介質清浄器Kへ
入れることができる。媒介質清浄器K上部には一定角度
を有するふるい網K1を設け、媒介質清浄器Kの上端に
は高圧水供給器Lを設ける。高圧水供給器Lの前端には
ノズルL1を設け、ふるい網K1上の顆粒状媒介質4と
雑質の清浄作業を進める。媒介質屑と雑質はふるい網K
1を通って媒介質清浄器K下部の貯蔵位置に落ち、再利
用の顆粒状媒介質4はふるい網K1の傾斜角度に沿って
媒介質貯蔵槽Mへ滑り入れ、電気化学機1単体内へ送っ
て再度使用する。消耗した顆粒状媒介質4を補充すると
き直接媒介質貯蔵槽M内に直接投入するだけでよく、媒
介質貯蔵槽M内は媒介質輸送器Nを設け、再使用の顆粒
状媒介質4を比較的高い媒介質補充槽P内へ送る。バル
ブ11のコントロールにより、重力を利用して顆粒状媒
介質4を適時、電気化学機1内へ送り、また媒介質清浄
器K内の洗浄水は原水槽A内に戻り再び処理して継続し
て利用する。沈積した底部の媒介質屑及び雑質は定期的
に清掃する。
After various reaction mechanisms of the raw water by the electrochemical machine 1, organic and inorganic impurities in the raw water gather to form relatively large flocs, and at the same time, by the reaction mechanism of the electrochemical machine 1. The generated microbubbles of hydrogen (H2) and oxygen (O2) adhere to flocs, and at this time, raw water enters another high-speed mixer G. The rate of the solid-liquid separation mechanism is accelerated, and a coagulant and a coagulant are selectively added into the high-speed mixer G. Granular medium 4
Is an excellent coagulant for metal ions dissociated by electrolytic corrosion. After the raw water enters the high-speed mixer G, the coagulant and the coagulant are mixed quickly, and the mixed raw water enters the flotation tank I, and flocs of many attached microbubbles float quickly by buoyancy. It floats on the water surface of the selection tank I, and is taken out and separated using the scum remover I2. Further, the scum floated by the horizontal turning of the scum remover I2 is put into the scum collecting funnel I1, and the water after treatment passes through the scum plate I3 and is sent out by the motor F to be drained or reused.
The removed scum is put into the scum storage tank J and sent to the final processing of the subsequent dewatering unit. The granular medium 4 in the electrochemical machine 1 is gradually consumed by the electrolytic erosion, and at the same time, the packed bed type apparatus causes large granular impurities of raw water to accumulate in the inner filling section 17 to cause clogging. . Therefore, using the granular medium replenishing port 14 and the granular medium discharging port 15, the discharging and replenishing operations are performed in a timely manner, so that the foreign substances deposited with the granular medium 4 can be easily accumulated without interrupting the processing operation. Can be discharged into the medium purifier K. A sieve net K1 having a certain angle is provided above the medium purifier K, and a high-pressure water supply L is provided at an upper end of the medium purifier K. A nozzle L1 is provided at the front end of the high-pressure water supply device L to purify the granular medium 4 on the sieve net K1 and other impurities. Intermediate debris and impurities are sieve net K
1 and fall into a storage position below the medium purifier K, and the reusable granular medium 4 slides into the medium storage tank M along the inclination angle of the sieve net K1, into the electrochemical machine 1 alone. Send and use again. When replenishing the exhausted granular medium 4, it is only necessary to directly charge it into the medium storage tank M. In the medium storage tank M, the medium transporter N is provided, and the reused granular medium 4 is stored. It is sent into a relatively high medium replenishment tank P. By controlling the valve 11, the granular medium 4 is timely sent into the electrochemical machine 1 using gravity, and the washing water in the medium purifier K returns to the raw water tank A and is processed again to continue. Use. Periodically clean deposited bottom debris and dirt.

【0009】[0009]

【発明の効果】本発明の優れた点は下記の通りである。 1.各種廃水(汚水)処理の働きを有する。 2.電気化学機は処理したい原水量に合わせて変更する
ことができるためあらゆる処理水量に適用する事ができ
る。 3.電気化学機は直列、並列或いは直並列の方式で組み
合わせる事ができるため、その処理の実用効果を高める
事ができる。 4.電気化学機は水に同時に酸化作用、還元作用、電食
作用、電気中和作用及び浮選作用等を進める事ができ、
水中の有機物、無機物等の雑物を同時に除去する事がで
きる。 5.電気化学機は適時に排出と補充の作業を行うことが
でき処理作業を中断する必要がない。 6.産業利用価値を有する。 7.実用性が高い。
The advantages of the present invention are as follows. 1. Has the function of various wastewater (sewage) treatment. 2. Since the electrochemical machine can be changed according to the amount of raw water to be treated, it can be applied to any amount of treated water. 3. Since the electrochemical machines can be combined in a series, parallel or series-parallel manner, the practical effect of the processing can be enhanced. 4. The electrochemical machine can simultaneously perform oxidizing action, reducing action, electrolytic corrosion action, electrical neutralizing action and flotation action on water,
Miscellaneous substances such as organic substances and inorganic substances in water can be removed at the same time. 5. The electrochemical machine can perform discharge and replenishment operations in a timely manner, and there is no need to interrupt processing operations. 6. Has industrial value. 7. High practicality.

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

【図1】本発明の電気化学機の分解斜視図である。FIG. 1 is an exploded perspective view of an electrochemical machine according to the present invention.

【図2】本発明を直列に組み立てた実施例の断面図であ
る。
FIG. 2 is a sectional view of an embodiment in which the present invention is assembled in series.

【図3】本発明を並列に組み立てた実施例の断面図であ
る。
FIG. 3 is a sectional view of an embodiment in which the present invention is assembled in parallel.

【図4】本発明を直並列に組み立てた実施例の断面図で
ある。
FIG. 4 is a sectional view of an embodiment in which the present invention is assembled in series and parallel.

【図5】本発明の顆粒状媒介質装置の断面図である。FIG. 5 is a cross-sectional view of the granular media device of the present invention.

【図6】本発明の微粒状媒介質の隙間に微小電池形成を
示す断面図である。
FIG. 6 is a cross-sectional view showing formation of a micro battery in a gap between fine particulate media of the present invention.

【図7】本発明の処理システム流れ図である。FIG. 7 is a flowchart of the processing system of the present invention.

【符号の説明】[Explanation of symbols]

1 電気化学機 11 バルブ 12 原水進流口 13 処理水出口 14 顆粒状媒介質補充口 15 顆粒状媒介質排出口 16 沈積物排出口 17 内部充填区 2 多孔板 3 多孔電極板 4 顆粒状媒介質 A 原水槽 B 原水輸送ポンプ C 流量計 D 流量コントロールバルブ E 快速ミキサー F モーター G 快速ミキサー H 直流電気供給器 I 浮選槽(Flotation Tank) I1 スカム収集じょうご I2 スカム除去器 I3 スカム板 J スカム貯蔵槽 K 媒介質清浄器 K1 ふるい網 L 高圧水供給器 L1 ノズル M 媒介質貯蔵槽 N 媒介質輸送器 P 媒介質補充槽 DESCRIPTION OF SYMBOLS 1 Electrochemical machine 11 Valve 12 Raw water inflow port 13 Treated water outlet 14 Granular medium replenishment port 15 Granular medium discharge 16 Sludge discharge 17 Internal filling section 2 Perforated plate 3 Perforated electrode plate 4 Granular medium A Raw water tank B Raw water transport pump C Flow meter D Flow control valve E Rapid mixer F Motor G Rapid mixer H DC electric supply I Flotation tank I1 Scum collecting funnel I2 Scum remover I3 Scum plate J Scum storage tank K medium purifier K1 sieve net L high-pressure water supply L1 nozzle M medium storage tank N medium transporter P medium replenishment tank

フロントページの続き Fターム(参考) 4D050 AA12 AB07 BA20 BB20 BD02 BD03 4D061 DA08 DB10 DB15 DC06 EA03 EA04 EA06 EA08 EB01 EB04 EB16 EB24 EB26 Continuation of the front page F term (reference) 4D050 AA12 AB07 BA20 BB20 BD02 BD03 4D061 DA08 DB10 DB15 DC06 EA03 EA04 EA06 EA08 EB01 EB04 EB16 EB24 EB26

Claims (9)

【特許請求の範囲】[Claims] 【請求項1】本発明は電流の作用で発生する電気化学反
応を利用したもので、電気エネルギーを化学エネルギー
に変化させて水体に酸化作用、還元作用、電食作用、電
気中和作用及び浮選作用等を同時に進め、それは単体構
造方式で製作し、電気化学機単体はどんなタイプの柱状
体の主体でもよく、中空状を呈する内部が内部充填区
で、大量の顆粒状媒介質を設置するのに使用し、該顆粒
状媒介質は導電性を有した材料で、内部充填区の上下に
それぞれ多孔板を設け、下方の多孔板を傾斜させ、電気
化学機単体の進出口端部にそれぞれ多孔電極板を設け、
多孔電極板の材質は不活性金属で、多孔電極板をそれぞ
れ直流電流供給器のマイナス、プラス極上に接続し、電
気化学機単体が必要な電場と電流を提供し、電気化学機
の長さ、体積及び内部顆粒状媒介質の数量、処理したい
原水特性の違い、及び処理効果により変化させ、多孔電
極板間の電場強度の大きさを原水の特性により変え、 電気化学機単体の外側上下端部にそれぞれ原水進流口と
処理水出口を設け、多孔板外側の電気化学機単体の適当
な位置にそれぞれ顆粒状媒介質補充口及び顆粒状媒介質
排出口を設け、さらに電気化学機単体の下端部に沈積物
排出口を設け、原水進流口、沈積物排出口及び顆粒状媒
介質補充口及び顆粒状媒介質排出口の適当な位置にそれ
ぞれ電動或いは手動のバルブを設け、全自動或いは手動
方式により原水排入、雑質排出或いは顆粒状媒介質の補
充、排出をコントロールし、処理作業を中断する必要が
なく連続して水体処理をする事ができることを特徴とす
る充填床式電気化学水処理装置及びその方法。
The present invention utilizes an electrochemical reaction generated by the action of an electric current, and converts electrical energy into chemical energy to oxidize, reduce, electrolytically erode, neutralize, and float water bodies. At the same time, the selection operation is performed, it is manufactured by a single structure method, the electrochemical machine alone may be the main body of any type of columnar body, the hollow inside is the inner filling section, and a large amount of granular media is installed The granular medium is a material having conductivity, and a perforated plate is provided above and below the inner filling section, and the perforated plate below is inclined. Provide a porous electrode plate,
The material of the perforated electrode plate is an inert metal, and the perforated electrode plates are connected to the minus and plus poles of the DC current supply, respectively, and the electrochemical machine alone provides the necessary electric field and current, and the length of the electrochemical machine, The volume and number of internal granular media, the difference in the characteristics of raw water to be treated, and the effect of treatment, and the magnitude of the electric field between the porous electrode plates are changed according to the characteristics of the raw water. Are provided with a raw water inflow port and a treated water outlet respectively, and a granular medium replenishing port and a granular medium discharging port are respectively provided at appropriate positions of the electrochemical machine outside the perforated plate, and further, the lower end of the electrochemical machine alone A sludge discharge port is provided in the section, and a motorized or manual valve is provided at an appropriate position of the raw water inflow port, the sludge discharge port, the granular medium replenishment port and the granular medium discharge port, respectively, fully automatic or manual. Raw water discharge by method A packed-bed type electrochemical water treatment apparatus and a method thereof, which can control the discharge of foreign substances or the replenishment and discharge of granular media, and can continuously perform water treatment without interrupting the treatment operation. .
【請求項2】電気化学機単体の断面積を処理したい原水
量に合わせて変化させ、電気化学機の断面積は処理量の
増加に合わせて増やすことができ、電気化学機単体の長
さは原水の雑質量に合わせて変化させることを特徴とす
る請求項1記載の充填床式電気化学水処理装置及びその
方法。
2. The cross-sectional area of the electrochemical machine alone is changed according to the amount of raw water to be treated, and the cross-sectional area of the electrochemical machine can be increased in accordance with an increase in the treatment amount. 2. The packed-bed type electrochemical water treatment apparatus and method according to claim 1, wherein the apparatus is changed in accordance with the coarse mass of raw water.
【請求項3】電気化学機単体を直列式或いは並列式に組
み合わせて応用、あるいは直並列併用方式を組み合わせ
て使用することを特徴とする請求項1記載の充填床式電
気化学水処理装置及びその方法。
3. The packed-bed type electrochemical water treatment apparatus according to claim 1, wherein the single electrochemical apparatus is combined in series or parallel to apply, or used in combination with series-parallel combination. Method.
【請求項4】電気化学機単体或いは組み合わせ式電気化
学機の設置は直立式、水平式或いはどのような角度の方
式でも、電気化学機単体の処理量及び処理効果に影響が
ないことを特徴とする請求項1記載の充填床式電気化学
水処理装置及びその方法。
4. The installation of the electrochemical machine alone or the combination type electrochemical machine is characterized in that the processing amount and the processing effect of the electrochemical machine alone are not affected by the upright type, the horizontal type or any angle type. The packed bed type electrochemical water treatment apparatus and method according to claim 1.
【請求項5】前記顆粒状媒介質はランダム方式で電気化
学機単体内に投入され、該顆粒状媒介質は両端が直流電
流電場の作用を受けて感応しプラス、マイナス方式に並
び、顆粒状媒介質間の隙間は小さく、それぞれの隙間は
微小電池のメカニズムを形成して比較的高い電流密度を
提供し、また隙間が微小のため、電気化学の反応がより
速く完全となり、全体の処理速度が速いことを特徴とす
る請求項1記載の充填床式電気化学水処理装置及びその
方法。
5. The granular medium is introduced into a single electrochemical machine in a random manner, and the granular medium is sensitive to both ends under the action of a direct current electric field, and is arranged in a plus and minus manner. The gaps between the media are small, each gap forming a microcellular mechanism to provide a relatively high current density, and the small gaps make the electrochemical reaction faster and more complete and the overall processing speed 2. The packed bed type electrochemical water treatment apparatus and method according to claim 1, wherein the temperature is fast.
【請求項6】前記顆粒状媒介質は電食作用で金属イオン
を解離し、金属イオンは優れた凝結剤で、凝縮作用は雑
質を凝縮してフロックにして除去し、顆粒状媒介質はど
んな導電性の材質でも良く、その形状は規則或いは不規
則の顆粒状であることを特徴とする請求項1或いは請求
項5記載の充填床式電気化学水処理装置及びその方法。
6. The granular medium dissociates metal ions by electrolytic erosion, the metal ions are excellent coagulants, and the condensing action is to condense and remove flocs to remove the foreign substances. The packed-bed type electrochemical water treatment apparatus and method according to claim 1 or 5, wherein any conductive material may be used, and the shape is a regular or irregular granular form.
【請求項7】原水進流口、沈積物排出口及び顆粒状媒介
質補充口及び顆粒状媒介質排出口の適当な位置にそれぞ
れ電動或いは手動のバルブを設け、全自動或いは手動方
式により原水排入、雑質排出或いは顆粒状媒介質の補
充、排出をコントロールすることを特徴とする請求項1
記載の充填床式電気化学水処理装置及びその方法。
7. An electric or manual valve is provided at an appropriate position of the raw water inflow port, the sludge discharge port, the granular medium replenishing port and the granular medium discharge port, respectively, and the raw water is discharged by a fully automatic or manual method. 2. The method according to claim 1, wherein the input, the discharge of foreign substances, or the replenishment and discharge of granular media are controlled.
A packed bed type electrochemical water treatment apparatus and method as described above.
【請求項8】前記電気化学機単体の顆粒状媒介質補充口
及び顆粒状媒介質排出口を設置或いは不設置の方式を採
用して構成し、処理システムの自動、半自動或いは手動
方式に合わせることを特徴とする請求項1或いは請求項
7記載の充填床式電気化学水処理装置及びその方法。
8. The method of claim 1, wherein the replenishing port and the rejecting port of the granular medium of the single electrochemical machine are installed or not installed, so that the processing system can be automatically, semi-automatically or manually operated. 8. A packed bed type electrochemical water treatment apparatus and method according to claim 1 or 7, characterized in that:
【請求項9】媒介質清浄器、媒介質貯蔵槽、媒介質補充
槽等の装置を処理システムに合わせて適時設置すること
を特徴とする請求項1記載の充填床式電気化学水処理装
置及びその方法。
9. A packed-bed type electrochemical water treatment apparatus according to claim 1, wherein apparatuses such as a medium purifier, a medium storage tank, and a medium replenishment tank are installed in a timely manner in accordance with the treatment system. That way.
JP11149559A 1999-05-28 1999-05-28 Packed bed type electrochemical water treating device and method therefor Pending JP2000334462A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11149559A JP2000334462A (en) 1999-05-28 1999-05-28 Packed bed type electrochemical water treating device and method therefor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11149559A JP2000334462A (en) 1999-05-28 1999-05-28 Packed bed type electrochemical water treating device and method therefor

Publications (1)

Publication Number Publication Date
JP2000334462A true JP2000334462A (en) 2000-12-05

Family

ID=15477832

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP2000334462A (en)

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Publication number Priority date Publication date Assignee Title
KR100743226B1 (en) 2006-05-19 2007-07-27 주식회사 에스디알앤디 Water treatment system
WO2009015683A1 (en) * 2007-08-01 2009-02-05 Holger Blum Device for filtering activated sludge with an electro-flocculation cell
JP2009541036A (en) * 2006-06-21 2009-11-26 ゴンザレス アルコセアー,ユアン ヨルゲ デイアズ Cooling towers requiring silica removal from water and methods and integrated systems for water treatment in various processes
JP2010510876A (en) * 2006-11-30 2010-04-08 エクサジャン テクノロジーズ インコーポレイテッド Removal of pollutants from waste streams by production and use of oxyhydrogen gas
WO2010092265A1 (en) * 2009-02-16 2010-08-19 Orege Method and device for scrubbing effluents
US9296629B2 (en) 2002-11-19 2016-03-29 Xogen Technologies Inc. Treatment of a waste stream through production and utilization of oxyhydrogen gas
CN109179871A (en) * 2018-09-19 2019-01-11 郑州工程技术学院 A kind of chemical waste liquid processing unit

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US9296629B2 (en) 2002-11-19 2016-03-29 Xogen Technologies Inc. Treatment of a waste stream through production and utilization of oxyhydrogen gas
KR100743226B1 (en) 2006-05-19 2007-07-27 주식회사 에스디알앤디 Water treatment system
JP2009541036A (en) * 2006-06-21 2009-11-26 ゴンザレス アルコセアー,ユアン ヨルゲ デイアズ Cooling towers requiring silica removal from water and methods and integrated systems for water treatment in various processes
JP2010510876A (en) * 2006-11-30 2010-04-08 エクサジャン テクノロジーズ インコーポレイテッド Removal of pollutants from waste streams by production and use of oxyhydrogen gas
WO2009015683A1 (en) * 2007-08-01 2009-02-05 Holger Blum Device for filtering activated sludge with an electro-flocculation cell
WO2010092265A1 (en) * 2009-02-16 2010-08-19 Orege Method and device for scrubbing effluents
CN109179871A (en) * 2018-09-19 2019-01-11 郑州工程技术学院 A kind of chemical waste liquid processing unit

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