JPS61502450A - Method and apparatus for automatically controlling electrochemical purification process of wastewater - Google Patents

Method and apparatus for automatically controlling electrochemical purification process of wastewater

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JPS61502450A
JPS61502450A JP50376584A JP50376584A JPS61502450A JP S61502450 A JPS61502450 A JP S61502450A JP 50376584 A JP50376584 A JP 50376584A JP 50376584 A JP50376584 A JP 50376584A JP S61502450 A JPS61502450 A JP S61502450A
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consumable electrode
electrode
wastewater
purification process
current density
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ナザリアン、ミロン ミグラノヴイチ
エフイモフ、ヴヤチエスラフ チホノヴイチ
ポグレロフ、ユリイ イグナチエヴイチ
エサウロフ、セルゲイ ミハイロヴイチ
バソフ、アレクサンドル フエドロヴイチ
ベレズツキイ、ヴヤチエスラフ ウラデイミロヴイチ
マニユイロフ、ミハイル ボリソヴイチ
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ハリコフスキイ ポリテフニ−チエスキイ インスチトウト イ−メニ ベ イ レ−ニナ
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    • 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
    • C02F1/463Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrocoagulation
    • 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
    • C02F2201/4612Controlling or monitoring
    • C02F2201/46125Electrical variables

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  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)
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Abstract

(57)【要約】本公報は電子出願前の出願データであるため要約のデータは記録されません。 (57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.

Description

【発明の詳細な説明】 廃水の電気化学的浄化工程を自動制御する方法および装置発明の分野 本発明は廃水浄化の工程を保守する方法および装置に関し、より詳細には廃水の 電気化学的浄化の工程を自動制御する方法および該方法を行なう装置に関するも のである。[Detailed description of the invention] Field of the invention: Method and device for automatically controlling the electrochemical purification process of wastewater The present invention relates to a method and apparatus for maintaining the process of wastewater purification, and more particularly to a method and apparatus for maintaining the process of wastewater purification. Also relates to a method for automatically controlling the process of electrochemical purification and an apparatus for carrying out the method. It is.

先行技術 現在、廃水中の汚染物質の量を合格衛生基準まで低減することを確実にする、廃 水の電気化学的浄化工程を自動制御する最も効率的な方法および装置は、電極上 の電流の密度を変えることに関連したものである。prior art Currently, wastewater treatment systems are in place to ensure that the amount of pollutants in wastewater is reduced to acceptable sanitary standards. The most efficient method and apparatus for automatically controlling the electrochemical purification process of water is It is related to changing the density of the current.

西独特許第2,016,448号(IPC: BOIK 3100.1974年 公告)に例示されているように、電極上の電流密度を調節することによって廃水 の電気化学的浄化工程を自動制御する方法および該方法を行なう装置が知られて いる。前記装置は電源、および電極上の電流密度の調整装置に接続した電極質量 監視装置を備えている。調整装置は電極上の所要電流密度をプリセットする装置 、および質量監視装置および電流密度プリセント装置によって発せられる信号を 比較する信号比較回路を備えており、こうして電流密度の実際値の変化が電源に 送られる制御信号を発生する。West German Patent No. 2,016,448 (IPC: BOIK 3100.1974) wastewater by adjusting the current density on the electrodes, as exemplified in A method for automatically controlling an electrochemical purification process and an apparatus for carrying out the method are known. There is. The device has an electrode mass connected to a power source and a device for adjusting the current density on the electrode. Equipped with monitoring equipment. The adjustment device is a device that presets the required current density on the electrodes. , and the signals emitted by the mass monitoring device and the current density precent device. It is equipped with a signal comparator circuit to compare the actual value of the current density, thus changing the actual value of the current density to the power supply. Generates control signals to be sent.

しかしながらこれら既知の廃水の電気化学的浄化工程を自動制御する方法および 装置は、浄化のため供給される廃水中の汚染物質の割合が不変である場合のみ効 率的な浄化をもたらす。というのは電極上で一定の電流密度を保持することによ って、汚染物質を凝集するのに十分な一定の所定量の金属水酸化物が生成される ためである。廃水中の汚染物質の割合が増加すると電極上の電流密度が大きくな ければならず、この既知の装置では間に合わない。However, these known methods for automatically controlling the electrochemical purification process of wastewater and The device is only effective if the proportion of pollutants in the wastewater supplied for purification remains unchanged. Brings about efficient purification. This is because by maintaining a constant current density on the electrodes, This produces a certain amount of metal hydroxide sufficient to clump the contaminants. It's for a reason. The current density on the electrode increases as the proportion of pollutants in the wastewater increases. This known device is not sufficient.

従って浄化効率は処理中の廃水中の汚染物質の濃度が変化する間影響を受ける。Purification efficiency is therefore affected while the concentration of pollutants in the wastewater being treated changes.

というのはこの場合に生成される金属水酸化物の量は汚染物質の濃度に比例しな いためである。This is because the amount of metal hydroxide produced in this case is proportional to the concentration of the pollutant. This is for a good reason.

廃水中の汚染物質の変化する濃度に応答して電極上の電流密度を変えることによ って、廃水を浄化する電気浮選工程を自動制御する方法および咳方法を行なう装 置が知られている。(参照:ソ連邦発明者証第453,360号 IPC: C 02F 3100.1972年公告)。by varying the current density on the electrodes in response to changing concentrations of pollutants in the wastewater. Therefore, a method for automatically controlling the electroflotation process for purifying wastewater and a device for performing the coughing method are proposed. location is known. (Reference: Soviet Union Inventor's Certificate No. 453,360 IPC: C 02F 3100. Published in 1972).

浄化水中の浮遊物の残留濃度に基いて監視装置によって発せられる信号は、調整 装置において基準信号と比較されて、エラーの場合電源の入力に与えられる制御 信号を発生する。The signal emitted by the monitoring device based on the residual concentration of suspended solids in the purified water is A control that is compared with a reference signal in the device and given to the input of the power supply in case of an error. Generate a signal.

上述の方法および装置は工程の動特性を考慮に入れた場合のみ、浄化工程の効率 的な制御を確実にする。さもなければ制御可能なバラメークはかなりの不安定性 を示し、浄化工程を不安定にするおそれがある。The methods and devices described above will only improve the efficiency of the purification process if the dynamics of the process are taken into account. ensure proper control. Otherwise controllable variation is highly unstable This may make the purification process unstable.

また、浄化している水中の溶解金属の濃度に応答して電気凝集装置の消耗電極上 の電流密度を調節することを特徴とする廃水の電気化学的浄化工程を自動制御す る方法も知られている(参照:ソ連邦発明者証第555,056号 IPC:  C02F 3100)。この方法は浄化している水中の電極の熔解金属を所定の 浄化度に対して十分な最適濃度に保持することに基いている。というのは廃水中 に浮遊している汚染物質の凝集は、一定量の水中の溶解金属で十分に高い速度で 生じることが知られているためである。水中に溶解金属が過剰に存在すると水の 浄化度に影響を及ぼし、水が浄化される度合が処理中の廃水中の溶解金属の濃度 に橿端に左右されるというパターンをたどる。しかしながら、処理中の水に様々 な不純物が存在することにより熔解金属濃度を監視することは厄介であるという 事実によって、水中の溶解金属の所望濃度を正確に保持することは不可能である 。Additionally, in response to the concentration of dissolved metals in the water being purified, Automatic control of wastewater electrochemical purification process characterized by adjusting the current density of (Reference: USSR Inventor's Certificate No. 555,056 IPC: C02F 3100). In this method, the molten metal of the electrode in the water being purified is It is based on maintaining the optimum concentration sufficient for the degree of purification. That is in waste water. The flocculation of pollutants suspended in water occurs at a sufficiently high rate for a given amount of dissolved metal in water This is because it is known to occur. Excessive presence of dissolved metals in water The concentration of dissolved metals in the wastewater being treated affects the degree of purification and the degree to which the water is purified. It follows a pattern of being influenced by the edge of the head. However, there are various It is said that monitoring the melt metal concentration is difficult due to the presence of impurities. Due to the fact that it is impossible to precisely maintain the desired concentration of dissolved metals in water .

この方法を行なう装置は、電気凝集装置の消耗電極に接続した可制御電源、およ び電流密度調整装置を備えている。電流密度調整装置は消耗電極上の電流密度の 所要値をプリセットする装置、およびその出力を可制御電源に接続した比較回路 を備えている。The equipment for this method consists of a controllable power supply connected to the consumable electrode of the electroconcentrator, and and a current density adjustment device. The current density regulator adjusts the current density on the consumable electrode. A device for presetting the required value and a comparator circuit with its output connected to a controllable power supply It is equipped with

この装置はさらに、電流密度調整装置の比較回路に接続して、処理している水中 の熔解金属の成る濃度に対応して電極上の電流密度の実際値に関する情報を伝え る信号を発生する、処理中の水中の電極の熔解金属濃度を計測する装置を備えて いる。電極上の電流密度の実際値および所要値に関する情報を搬送し比較回路の 入力に与えられる信号間の不整合には、電極上の電流密度を変化させることによ って応答する。電流密度調整装置としては、処理中の水中の熔解金属濃度に応答 して電極上の電流密度の段階的変化を介して、電気凝集装置中の廃水の電気化学 的浄化の最適工程条件を持続することを可能にする最適化段階制御装置を使用す る。The device also connects to the comparison circuit of the current density regulator to conveys information about the actual value of the current density on the electrode corresponding to the concentration of molten metal in the Equipped with a device that measures the concentration of dissolved metal at the electrode in the water being treated, which generates a signal that There is. It carries information about the actual and desired current density on the electrodes and is used in the comparator circuit. The mismatch between the signals applied to the inputs can be addressed by varying the current density on the electrodes. I respond. As a current density adjustment device, it responds to the concentration of dissolved metal in the water being treated. Electrochemistry of wastewater in an electrocoagulator through stepwise changes in current density on the electrodes Using an optimization stage controller that allows maintaining optimal process conditions for Ru.

しかしながら、浄化している水中の熔解金属の濃度を判定する既知の監視装置に は5%を上回る測定誤差があり、これは浄化水の品質に影響を及ぼす。However, known monitoring devices that determine the concentration of molten metals in the water being purified has a measurement error of more than 5%, which affects the quality of purified water.

発明の要旨 本発明は、不純物の凝集を加速し水を浄化する度合を増大させることを目的とし て、消耗電極の質量を連続的に監視することによって処理中の水中の電極の熔解 金属の最適量を正確に保持することを可能にする、廃水の電気化学的浄化工程を 自動制御する方法および装置の提供を目的としている。Summary of the invention The purpose of the present invention is to accelerate the agglomeration of impurities and increase the degree of water purification. The melting of electrodes in water during processing can be monitored by continuously monitoring the mass of consumable electrodes. An electrochemical purification process of wastewater that allows to precisely retain the optimum amount of metals. The object of the present invention is to provide a method and device for automatic control.

本発明の目的は、電気化学的浄化が行われる電気凝集装置の消耗電極上の電流密 度を変えることによって、廃水の電気化学的浄化工程を自動制御する方法におい て、本発明によれば、電極の溶解が進行する間に時間と共に電極の質量が変化す るのに応答して消耗電極上の電流密度を調節することによって連成される。The object of the invention is to provide a current density on the consumable electrode of an electrocoagulator in which electrochemical purification is carried out. In a method for automatically controlling the electrochemical purification process of wastewater by varying the Therefore, according to the present invention, the mass of the electrode changes with time while dissolution of the electrode progresses. by adjusting the current density on the consumable electrode in response to the

好ましくは消耗電極上の電流密度は0.005〜0.02A/−の範囲内に保持 する。Preferably the current density on the consumable electrode is kept within the range of 0.005 to 0.02 A/- do.

また本発明の目的は、電気凝集装置の消耗電極に接続した可制御電源、および出 力を可制御電源に接続し消耗電極上の電流密度の所要値をプリセットする装置と 消耗電極上の電流密度の所要値および実際値に対応する信号を比較する信号比較 回路とを含む電流密度調整装置を備えている、廃水の電気化学的浄化工程を自動 制御する方法を行なう装置において、本発明によれば、消耗電極の質量を監視す る装置が設けられており、該質量監視装置が消耗電極上の電流密度の調整装置に 接続しかつ可撓性サスペンションおよび絶縁板を介して前記消耗電極に接続して 、いかなる所定の瞬間にも消耗電極の質量に対応する該電極上の電流密度の実際 値に関する情報を搬送する信号を発生することによって達成される。It is also an object of the present invention to provide a controllable power supply connected to the consumable electrode of the electroconcentrator, and an output a device for connecting the power to a controllable power supply and presetting the desired value of the current density on the consumable electrode; Signal comparison, which compares the signals corresponding to the desired and actual values of the current density on the consumable electrode Automatic electrochemical purification process of wastewater, equipped with circuit and current density regulating device According to the invention, in an apparatus for carrying out a method of controlling, the mass of a consumable electrode is monitored. A device is provided for adjusting the current density on the consumable electrode. and connected to the consumable electrode through a flexible suspension and an insulating plate. , the actual current density on the consumable electrode corresponding to its mass at any given moment. This is accomplished by generating a signal that conveys information about the value.

好ましくは、装置は誘電材料から作り導電液を充虜した容器を有しており、該容 器中で電源に接続した導線の自由端は液浸しており、絶縁板に接続した導線の自 由端も導電液を入れた容器中で液浸している。Preferably, the device includes a container made of dielectric material and filled with a conductive liquid; The free end of the conductor connected to the power supply inside the device is immersed in liquid, and the conductor connected to the insulating plate is exposed to the liquid. The far end is also immersed in a container containing conductive liquid.

導電液として水銀を使用するのが望ましい。Preferably, mercury is used as the conductive liquid.

提案した発明によって、消耗電極の質量の変化に応答して、あるいは基いて該電 極上の所要電流密度が確実になり、これによって高度の水の浄化と共に陽極金属 の損失を最小限にすることが可能になる。平均して、付随する利益としては消耗 電極の金属の消耗が77%に低減するとともに、廃水が浄化される度合が3.2 〜4.8%増大する。The proposed invention allows the consumable electrode to be adjusted in response to or based on a change in its mass. The highest required current density is ensured, which results in a high degree of water purification as well as anode metal This makes it possible to minimize losses. On average, the associated benefits are depleted The metal consumption of the electrode is reduced to 77%, and the degree of wastewater purification is increased to 3.2%. ~4.8% increase.

図面の簡単な説明 本発明を以下、廃水の電気化学的浄化工程を自動制御する提案した方法を行なう 装置の概略図である添付図面と関連した種々の特定の実施例を参照してより詳細 に説明する。Brief description of the drawing Hereinafter, the present invention will carry out the proposed method for automatically controlling the electrochemical purification process of wastewater. More details may be found with reference to various specific embodiments in connection with the accompanying drawings, which are schematic illustrations of the apparatus. Explain.

本発明を実施する好適な態様 廃水の電気化学的浄化工程を自動制御する提案した方法の本質は、廃水の電気化 学的処理が行われる電気凝集装置の消耗電極上の電流密度を、消耗電極の熔解中 時間と共に該電極の質量が変化するのに応答して調節し、電流密度は好ましくは O,OO5〜0.02A/cffl内に保持するところにある。Preferred modes for carrying out the invention The essence of the proposed method to automatically control the electrochemical purification process of wastewater is the electrification of wastewater. The current density on the consumable electrode of the electrocoagulation device where the chemical treatment is carried out is The current density is preferably adjusted in response to changes in the mass of the electrode over time. It is to be maintained within the range of O, OO5 to 0.02 A/cffl.

廃水の電気化学的浄化においては、水を浄化する度合および電気凝集装置の効率 は、電極に電圧を印加した陸水に付与される消耗電極の金属の量により大きな影 響を受ける。電流の作用の下で処理中の水に付与される消耗電極のイオンは水酸 化物イオンと相互作用して、水中に含まれている不純物の凝集を促進する高い収 着能力が可能である金属水酸化物の粒子を生成する。その後凝集した不純物の凝 集体は凝集装置中で浄化水から分離される。In electrochemical purification of wastewater, the degree of water purification and the efficiency of the electrocoagulation device is greatly influenced by the amount of metal in the consumable electrode that is applied to land water with a voltage applied to the electrode. Receive the sound. The ions of the consumable electrode that are imparted to the water during treatment under the action of an electric current are hydroxyl High yield that interacts with oxide ions to promote agglomeration of impurities contained in water. It produces metal hydroxide particles that are capable of adhesion. Then the condensed impurities The aggregates are separated from the purified water in a flocculator.

水中に送られる金属の量は水中に含まれる不純物の量に比例しなければならない 。上述の事実は廃水の電気化学的浄化を行なうのに役立ち、この場合所要の水の 浄化度および工程効率を確実にする。これは消耗’!電極上所定の電流密度を保 持して該電極の高速度の溶解を促進することによって達成される。理論的には陽 極熔解金属の量mはファラデーの法則すなわちm=K −J ・ t によって設定することができる。但しKは消耗電極の金属の電気化学的等量1. Jは消耗電極上の電流の量、tは消耗電極の金属の熔解に必要な時間である。The amount of metal sent into the water must be proportional to the amount of impurities contained in the water. . The above-mentioned facts are useful for carrying out electrochemical purification of wastewater, in which case the required water Ensures cleanliness and process efficiency. This is consumption’! Maintains a given current density on the electrode. This is achieved by promoting high rate dissolution of the electrode. Theoretically positive The amount m of extremely molten metal is determined by Faraday's law, that is, m = K - J ・t Can be set by However, K is the electrochemical equivalent of the metal of the consumable electrode 1. J is the amount of current on the consumable electrode and t is the time required to melt the metal on the consumable electrode.

しかしながら実際には、電気の作用の下で電気凝集装置中で溶解可能な金属の量 は理論収量とは異なる。これに関連して、所望の浄化度を達成するには消耗電極 の電気化学的溶解中に廃水に付与される金属の量を正確に判定す、ることが重要 である。監視計器手段の水中の熔解金属の量を判定する先行技術の方法には、精 度がかなり低いという問題がある(既知の計器の測定誤差は4〜5%にもなる) 。最も正確なのは電流の作用の下で熔解可能な電極の質量の変化を測定する装置 である。従って提案した装置は、消耗電極から処理中の水中に送られる金属の量 を、水の浄化工程が進行する間に時間と共に連続的に判定する技術を利用してい る。However, in reality, the amount of metal that can be dissolved in an electrocoagulator under the action of electricity is different from the theoretical yield. In this context, consumable electrodes are required to achieve the desired degree of purification. It is important to accurately determine the amount of metals added to the wastewater during the electrochemical dissolution of It is. Prior art methods of determining the amount of molten metal in water in monitoring instrument means include The problem is that the degree of measurement is quite low (the measurement error of known meters is as high as 4-5%). . The most accurate are devices that measure the change in the mass of a meltable electrode under the action of an electric current It is. The proposed device therefore reduces the amount of metal delivered from the consumable electrode into the water being treated. It utilizes technology that continuously determines the water purification process over time as the water purification process progresses. Ru.

最大の利益は、消耗電極がo、oos〜0.02A/−の電極上の電流密度で熔 解する際に達成される。0.005A/a11を下回る電流密度では電極熔解の 速度が低減する結果となり、これは電気凝集装置の効率に影響を及ぼす。逆に0 .02A/ciを上回る電流密度は電極からのガスのより活発な遊離を示し、そ の結果処理中の廃水の混合が過度になり浄化工程が悪化する。The greatest benefit is when the consumable electrode melts at a current density on the electrode of o, oos ~ 0.02 A/-. This is achieved when understanding. At current density below 0.005A/a11, the electrode melts. This results in a reduction in speed, which affects the efficiency of the electrocoagulator. On the other hand, 0 .. A current density above 0.2 A/ci indicates a more active liberation of gas from the electrode, which This results in excessive mixing of wastewater during treatment, which deteriorates the purification process.

廃水の電気化学的浄化工程を自動制御する方法は添付図面に概略的に示した装置 によって行なう。装置は可制御電源1を備え、該電源1は、電気凝集装置3の消 耗電極2に接続し、かつ消耗電極2上の所要電流密度をブリセントする装置5、 および電流の所要密度値と質量測定装置7によって発生される実際の密度値に対 応する信号を比較する比較回路6を備えている既知の適当な構造の電流密度調整 装置4に接続する。(参照:13. pJ、 Kosharsky編集のロシア 語便覧”Pr1bory i upravlyajuschie sistem ydlja khimicheskikh proizvodstv″ (Ma shinostroenie ”出版社、モスクワ 1976年))。A method for automatically controlling the electrochemical purification process of wastewater is provided by the apparatus schematically shown in the attached drawings. It is done by The device comprises a controllable power source 1, which is used to turn off the electroconcentrator 3. a device 5 connected to the consumable electrode 2 and for briscenting the required current density on the consumable electrode 2; and the required density value of the current and the actual density value generated by the mass measuring device 7. Current density adjustment of any known suitable structure, comprising a comparator circuit 6 for comparing the corresponding signals. Connect to device 4. (Reference: 13. Russia edited by pJ, Kosharsky Glossary “Pr1bory i upravlyajuschie system” ydlja khimicheskikh proizvodstv'' (Ma shinostroenie” Publisher, Moscow, 1976)).

装置7は可撓性サスペンション8および絶縁板9を介して消耗電極2に接続して いる。可制御電源1は、誘電材料から作って電源1との電気的接触を防止し水銀 等の導電液を充堪した容器12中にその自由端を液浸した導線10および11を 介して消耗電極2に(妾続している。The device 7 is connected to the consumable electrode 2 via a flexible suspension 8 and an insulating plate 9. There is. The controllable power source 1 is made of dielectric material to prevent electrical contact with the power source 1 and is free from mercury. Conductive wires 10 and 11 with their free ends immersed in a container 12 filled with a conductive liquid such as It is connected to the consumable electrode 2 through the consumable electrode 2.

消耗電極2は電気凝集装置3の電気凝集室13の下部で、電極2の金属が熔解す る純粋な電解液を供給する入口管14のほぼ上方に配設し、電気凝集室に汚染液 を供給する管15は電極2の上方に配設する。The consumable electrode 2 is located at the lower part of the electrocoagulation chamber 13 of the electrocoagulation device 3, and the metal of the electrode 2 is melted. The electrolyte is placed almost above the inlet pipe 14 that supplies pure electrolyte to the electrocoagulation chamber. A tube 15 for supplying is arranged above the electrode 2.

電気凝集室13は沈降室16の内側に同軸上に配設してこの室16の一部を占め ている。沈降室16には浄化水および廃物を各々排出する出口管17および18 が設けられている。The electrocoagulation chamber 13 is arranged coaxially inside the settling chamber 16 and occupies a part of this chamber 16. ing. The settling chamber 16 has outlet pipes 17 and 18 for discharging purified water and waste, respectively. is provided.

廃水の浄化度および電気凝集装置3の通過容量は、主に消耗電極2の電気化学的 溶解が進行する間に電解液中で生成される金属水酸化物の量によって決定される 。従って浄化工程の効率は、電解液中に送られる金属水酸化物の量を特徴付ける 消耗電極2の質量に関する連続情illの利用度に左右される。虚って消耗電極 2の質量に関するデータを連続的に与える質量監視装置7は、廃水の電気化学的 浄化工程を自動制御する装置の主要な素子である。The degree of purification of wastewater and the passing capacity of the electrocoagulator 3 are mainly determined by the electrochemical effect of the consumable electrode 2. Determined by the amount of metal hydroxide produced in the electrolyte while dissolution proceeds . The efficiency of the purification process therefore characterizes the amount of metal hydroxide delivered into the electrolyte. It depends on the availability of continuous information regarding the mass of the consumable electrode 2. Empty and consumable electrode A mass monitoring device 7 that continuously provides data regarding the mass of wastewater This is the main element of the device that automatically controls the purification process.

質量監視装置7は、ノズルとゲートの間の距離に基く「ノズル−ゲート」装置中 の圧力に対応する出力信号を形成しようとする「ノズル−ゲート」空気式装置( 参照: V、 M、 Kulakov″Pr1bory旧ja khimich eskjkh proizvodstv ” (ロシア語、” Khimiya  ″出版社、モスクワ、1983年、p、500 ) )であってもよく、リン ク装置によって可撓性サスペンション8に接続することができる。消耗電極2の 質量が変化するとリンク装置中の張力も異なって、ノズルに対するゲートの運動 および電極2の質量の変化に対応する装置中の圧力の変化を生じる。電極2は水 銀等の導電液を充議した容器12中でそれらの自由端を液浸した導線10および 11によって、電源1に接続している。The mass monitoring device 7 is a "nozzle-gate" device based on the distance between the nozzle and the gate. A "nozzle-gate" pneumatic device ( Reference: V, M, Kulakov"Pr1bory old ja khimich eskjkh proizvodstv” (Russian, “Khimiya "Publisher, Moscow, 1983, p. 500))" The flexible suspension 8 can be connected to the flexible suspension 8 by a link device. consumable electrode 2 As the mass changes, the tension in the linkage also changes, causing movement of the gate relative to the nozzle. and a change in the pressure in the device corresponding to the change in the mass of the electrode 2. Electrode 2 is water Conductor wires 10 whose free ends are immersed in a container 12 filled with a conductive liquid such as silver; 11, it is connected to the power supply 1.

本発明に従って廃水の電気化学的浄化工程を自動制御する提案した方法を行なう 装置は、下記のように動作する。Carrying out the proposed method for automatically controlling the electrochemical purification process of wastewater according to the present invention The device operates as follows.

廃水は、例えばアルミニウムから作り電気凝集室13の下部に位置決めした消耗 電極2の上方に配設した管15を介して、電気凝集室13の中間部に連続的に供 給される。同時に工業的に純粋な水等の電解液を入口管14を介して電気凝集室 13に供給し、この電解液は消耗電極2の間の電極間ギャップを介して上昇流で 流れる。電極2に印加される電圧は電極を電解液中で熔解させ、よって高い収着 能力の金属水酸化物の粒子を生成し、これには電解液の上昇流によって電気凝集 室13の中間部に送られる高度に分散したガスの水の電気分解の結果、電極2か らのエマネーションが伴なう。The waste water is collected in a consumable tube made of aluminum, for example, and positioned at the bottom of the electrocoagulation chamber 13. It is continuously supplied to the middle part of the electrocoagulation chamber 13 through a pipe 15 disposed above the electrode 2. be provided. At the same time, an electrolytic solution such as industrially pure water is introduced into the electrocoagulation chamber through the inlet pipe 14. 13, and this electrolyte flows upward through the interelectrode gap between the consumable electrodes 2. flows. The voltage applied to electrode 2 causes the electrode to dissolve in the electrolyte, thus resulting in a high sorption ability to produce metal hydroxide particles, which are electrocoagulated by an upward flow of electrolyte As a result of the electrolysis of highly dispersed gas water sent to the middle part of chamber 13, electrode 2 It is accompanied by the emanation of et al.

電極2の上方で廃水を電極2の金属の熔解の生成物を含有している電解液と混合 した結果、金属水酸化物と汚染粒子の間の相互作用が生じて該粒子の大きな凝集 体を生成し、これらは気泡によって液の表面に向かって送られ、こうして浮遊し ている廃物を沈降室16の上部から出口管1日を介して連続的に排出する。沈降 室16中で浄化された水は咳室の下部に設けた出口管17を介して放出する。Above electrode 2, the waste water is mixed with an electrolyte containing the products of the melting of the metal of electrode 2. As a result, interactions between metal hydroxides and contaminant particles occur, leading to large agglomerations of the particles. These bodies are carried towards the surface of the liquid by air bubbles and thus become suspended. The waste material contained in the sedimentation chamber 16 is continuously discharged from the upper part of the settling chamber 16 via an outlet pipe. sedimentation The purified water in the chamber 16 is discharged via an outlet pipe 17 provided in the lower part of the cough chamber.

水の浄化が進行する間の消耗電極2の質量の変化の連続監視は、可撓性サスペン ション8および絶縁板9を介して電極2に接続した質量監視装置7によって可能 になる。電極2の溶解にはそれらの質量の変化が伴ない、質量監視装置7の「ノ ズル−ゲート」装置に接続したサスペンション8の変位を生じる。Continuous monitoring of the change in mass of the consumable electrode 2 while water purification progresses is carried out using a flexible suspension mass monitoring device 7 connected to electrode 2 via section 8 and insulating plate 9. become. The melting of the electrodes 2 is accompanied by a change in their mass, and the “node” of the mass monitoring device 7 is This results in a displacement of the suspension 8 connected to the "Zur-Gate" device.

この結実装置7の出力で、消耗電極2の質量に関し、従って消耗電極2上の電流 密度に基いて電解液中で生成される全屈水酸化物の量に関するデータを搬送する 信号が発生される。この信号は次いで電流密度調整装置4の比較回路6の入力に 送られ、調整装置の他方の入力には消耗電極2上の電流密度の所定値に対応する 装置5からの信号が与えられる。これらの信号間の誤差によって、電流密度調整 装置4は一定の調整法則に従って電源1の作動メカニズムを制御する。この結果 電極2に印加される電流密度の比例変化が生じ、調整装置4の比較回路6の出力 で発生される誤差信号の符号に基いて消耗電極2の金属の陽極熔解の速度の増加 あるいは低減を生じる。At the output of this fruiting device 7, the mass of the consumable electrode 2 and therefore the current on the consumable electrode 2 Conveys data regarding the amount of total hydroxide produced in the electrolyte based on density A signal is generated. This signal is then input to the comparator circuit 6 of the current density regulator 4. and the other input of the regulating device corresponds to a predetermined value of the current density on the consumable electrode 2. A signal from device 5 is provided. The error between these signals allows current density adjustment. The device 4 controls the operating mechanism of the power source 1 according to certain regulation laws. As a result A proportional change in the current density applied to the electrode 2 occurs and the output of the comparator circuit 6 of the regulating device 4 The rate of anodic melting of the metal of consumable electrode 2 is increased based on the sign of the error signal generated by Or a reduction occurs.

従って電極2の質量が変化すると、電流密度調整装置4の制御信号は電源1の演 算パラメータを変え電極2上の所要電流密度を再設定するように動作し、該密度 によって電気凝集室13中の廃水の浄化に対する所定動作条件の安定化が確実に なり高品質の浄化が促進される。Therefore, when the mass of the electrode 2 changes, the control signal of the current density regulator 4 changes It operates to change the calculation parameters and reset the required current density on electrode 2, and This ensures the stabilization of the predetermined operating conditions for the purification of wastewater in the electrocoagulation chamber 13. This promotes high-quality purification.

廃水の電気化学的浄化工程を制御する効率は電極が動作する条件に基いているた め、電極間ギャップにおける電解液の流れの直線速度および電極間の距離は、そ れらの表面の不動態化を最小限にするとともにガスおよび電極2の電気化学的熔 解の生成物でそれが飽和している開演の導電性を連続させるように選択する。The efficiency of controlling the electrochemical purification process of wastewater is based on the conditions under which the electrodes operate. Therefore, the linear velocity of the electrolyte flow in the electrode gap and the distance between the electrodes are electrochemical melting of the gas and electrode 2 while minimizing passivation of their surfaces. Choose to make the conductivity continuous so that it is saturated with the products of the solution.

廃水の電気化学的浄化工程を自動制御する提案した方法および該方法を行なう装 置は、99.6%程度の廃水浄化で電極の消耗を77%に低減する。The proposed method for automatically controlling the electrochemical purification process of wastewater and the equipment for carrying out the method The device purifies wastewater by approximately 99.6% and reduces electrode wear to 77%.

二!的適用性 本発明は有機物および無殿物、固形物等によって汚染された廃水を浄化するのに 適用することができる。two! applicability The present invention is useful for purifying wastewater contaminated with organic matter, non-sediment matter, solid matter, etc. Can be applied.

本発明は、油およびポリメタクリ酸メチルを含有している廃水等の石油製品およ びポリマーによって汚染された廃水を浄化するのに最も有益に使用することがで きる。The present invention applies to petroleum products such as wastewater containing oil and polymethyl methacrylate. It can be most beneficially used to purify wastewater contaminated with Wear.

国際v4歪報告international v4 distortion report

Claims (5)

【特許請求の範囲】[Claims] (1)廃水の電気化学的浄化工程を行なう電気凝集装置(3)の消耗電極(2) 上の電流の密度を変えることによって廃水の電気化学的浄化工程を自動制御する 方法において、上記消耗電極(2)に印加される電流の密度を、上記電極の溶解 が進行する間に時間とともに上記電極(2)の質量が変化するのに基いて調整す ることを特徴とする上記方法。(1) Consumable electrode (2) of an electrocoagulation device (3) that performs the electrochemical purification process of wastewater Automatically control the electrochemical purification process of wastewater by changing the density of the current on the In the method, the density of the current applied to the consumable electrode (2) is adjusted to The adjustment is made based on the fact that the mass of the electrode (2) changes with time during the progress of the process. The method described above. (2)上記消耗電極(2)上の電流の密度を0.005〜0.02A/cmの範 囲内に保持することを特徴とする、特許請求の範囲第1項に記載の廃水の電気化 学的浄化工程を自動制御する方法。(2) The density of the current on the consumable electrode (2) is within the range of 0.005 to 0.02 A/cm. Electrification of wastewater according to claim 1, characterized in that it is kept within a A method for automatically controlling the chemical purification process. (3)上記電気凝集装置(3)の上記消耗電極(2)に接続した可制御電源(1 )と、出力を上記可制御電源(1)に接続するとともに、上記消耗電極(2)上 の電流密度の所要値をプリセットする装置(5)と上記消耗電極(2)上の電流 密度の所要値および実際値に対応する信号を比較する信号比較回路(6)とを含 む電流密度調整装置(4)とを備えている、特許請求の範囲第1項に記載の廃水 の電気化学的浄化工程を自動制御する方法を行なう装置において、上記消耗電極 上の電流密度の調整装置(4)に接続しかつ可撓性サスペンション(8)および 絶縁板(9)を介して上記消耗電極(2)に接続した、所定のいかなる瞬間にも 上記消耗電極(2)の質量に対応する上記電極上の電流密度の実際値に関する情 報を搬送する信号を発生する質量監視装置(7)を設けることを特徴とする上記 装置。(3) A controllable power source (1) connected to the consumable electrode (2) of the electrocoagulation device (3) ), the output is connected to the controllable power source (1), and the output is connected to the consumable electrode (2). device (5) for presetting the required value of the current density of the current on said consumable electrode (2); a signal comparison circuit (6) for comparing signals corresponding to the desired and actual values of the density; The wastewater according to claim 1, comprising: a current density adjustment device (4) comprising: In a device that performs a method for automatically controlling the electrochemical purification process of connected to the current density adjustment device (4) above and the flexible suspension (8) and At any given moment, connected to the consumable electrode (2) through an insulating plate (9) Information regarding the actual value of the current density on said electrode corresponding to the mass of said consumable electrode (2) The above, characterized in that it is provided with a mass monitoring device (7) that generates a signal conveying information. Device. (4)誘電材料から作り導電液を入れた容器(12)を備えており、上記容器( 12)において上記可制御電源の導線(10)の自由端を液浸し、上記導線(1 0)を上記可制御電源(1)に接続し更に上記絶縁板(9)に接続した導線(1 1)の自由端を液浸したことを特徴とする、特許請求の範囲第3項に記載の廃水 の電気化学的浄化工程を自動制御する方法を行なう装置。(4) A container (12) made of a dielectric material and containing a conductive liquid is provided, and the container (12) is made of a dielectric material and contains a conductive liquid. In step 12), the free end of the lead wire (10) of the controllable power source is immersed in liquid; 0) is connected to the controllable power source (1) and further connected to the insulating plate (9). 1) Wastewater according to claim 3, characterized in that the free end is immersed in liquid. A device that performs a method for automatically controlling the electrochemical purification process of (5)導電液として水銀を使用することを特徴とする特許請求の範囲第4項に記 載の装置。(5) Claim 4, characterized in that mercury is used as the conductive liquid. equipment.
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WO1986000287A1 (en) 1986-01-16
FR2566763B1 (en) 1986-12-12
SE452759B (en) 1987-12-14

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