GB1560730A - Electrolytic cell for treatment of water - Google Patents

Electrolytic cell for treatment of water Download PDF

Info

Publication number
GB1560730A
GB1560730A GB27000/76A GB2700076A GB1560730A GB 1560730 A GB1560730 A GB 1560730A GB 27000/76 A GB27000/76 A GB 27000/76A GB 2700076 A GB2700076 A GB 2700076A GB 1560730 A GB1560730 A GB 1560730A
Authority
GB
United Kingdom
Prior art keywords
cell
particles
pipe
water
grid
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.)
Expired
Application number
GB27000/76A
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.)
Einhell Germany AG
Original Assignee
Hans Einhell GmbH Industriegelande
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
Priority claimed from DE19752531850 external-priority patent/DE2531850A1/en
Priority claimed from DE19762607906 external-priority patent/DE2607906A1/en
Application filed by Hans Einhell GmbH Industriegelande filed Critical Hans Einhell GmbH Industriegelande
Publication of GB1560730A publication Critical patent/GB1560730A/en
Expired 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
    • 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
    • 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
    • C02F1/4672Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
    • C02F1/4674Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation with halogen or compound of halogens, e.g. chlorine, bromine
    • 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
    • C02F1/4602Treatment of water, waste water, or sewage by electrochemical methods for prevention or elimination of deposits
    • 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
    • C02F1/4606Treatment of water, waste water, or sewage by electrochemical methods for producing oligodynamic substances to disinfect the water
    • 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
    • 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
    • C02F1/4672Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46109Electrodes
    • C02F2001/46119Cleaning the electrodes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46109Electrodes
    • C02F2001/46133Electrodes characterised by the material
    • C02F2001/46138Electrodes comprising a substrate and a coating
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • C02F1/46109Electrodes
    • C02F2001/46152Electrodes characterised by the shape or form
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/42Nature of the water, waste water, sewage or sludge to be treated from bathing facilities, e.g. swimming pools
    • 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
    • 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
    • C02F2201/4618Supplying or removing reactants or electrolyte
    • C02F2201/46185Recycling the cathodic or anodic feed
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/02Fluid flow conditions
    • C02F2301/024Turbulent
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection

Description

(54) AN ELECTROLYTIC CELL FOR TREATMENT OF WATER (71) We, HANS EINHELL G.m.b.H., a German limited liability company, of Indus triegelände, D-8380 Landau, Federal Republic of Germany, do hereby declare the invention, for which we pray that a patent may be granted to us, and the method by which it is to be performed, to be particularly described in and by the following statement: This invention relates to a continuous process for treatment of water and simultaneously for keeping clean electrodes in an electrolytic water treatment cell. The invention also includes an electrolytic cell for carrying out the process. Such treatment may for example be purification and sterilization of water. The invention relates in particular to a multipole electrolytic cell, which can be used in various ways for treatment, and more particularly for purification and sterilization, of water and comprises a closed container with a lower inlet opening and an upper outlet opening for the water and electrodes within the container, which are arranged to be connected to the positive and negative poles of a DC source.
Various electrolytic cells are known for treatment, and more particularly for purification and sterilization, of water. With these known cells it is possible to remove dissolved and suspended contaminating materials in the water to be treated electrolytically by using either consumable or non-consumable electrodes of iron, aluminium, copper, silver, platinum, or carbon. However during operation of such electrolytic cells problems are encountered due to different causes.
Normally during electrolysis of water, especially hard water, the cathode is rapidly covered by a coating of calcium carbonate which inhibits flow of the electric current; anodes of silver, copper, iron, or aluminium during electrolysis are covered with oxide films. In the case of aluminium anodes the formed aluminium oxide prevents flow of current. In the case of silver, iron or copper anodes the formed oxide film is highly conductive, so that dissolution of the metal is prevented and oxygen is produced at the electrodes.
Another problem encountered is that water to be treated usually has only a small number of ions and that, although platinum anodes can provide oxidation, the oxidation-reduction potential of the water remains low. For example, if chlorine is to be produced, the chloride concentration in the water must be high and this concentration is normally not encountered in fresh water, particularly drinking water.
The standard electrolytic technique to chlorinate water in a swimming-pool is to provide a separate cell containing a high concentration of common salt which upon electrolysis gives sodium hypochlorite or chlorine which is fed into the swimmingpool. Theoretically it is possible to add sufficient common salt to the swimming-pool water and to electrolyze it directly. This technique has the disadvantage that the water tastes salty and that the calcium in the water deposits on the cathodes to such an extent that the flow of current stops. Changing polarity to remove the calcium deposit on the cathodes has been found in practice only to lead to corrosion of the cathodes, and aggravates the problem.
It is an object of the invention to prevent as far as possible formation of deposits on the electrodes which hinder the flow of current and the dissolution of metal electrodes required for water purification.
According to this invention there is provided a continuous process for treatment of water and simultaneously for keeping clean electrodes in an electrolytic cell, comprising flowing a stream of water to be treated upwardly past electrodes in the cell which contains freely movable particles whose density is greater than that of the water, controlling the velocity of the flowing stream so as to form a fluidized bed of the particles in the cell and so as mechanically to keep the electrodes clean by virtue of the kinetic energy generated by fluidization of the particlefs.
Also according to this invention there is provided an electrolytic cell when used for carrying out the process, the cell comprising a closed container with a lower inlet opening and an upper outlet opening for the water to be treated, electrodes in the container for connection to the positive and the negative poles of a D.C. source, particles whose density is greater than that of the water to be treated, and means for retaining the particles within the container, wherein the particles are freely movable and are fluidized by the flowing movement of water to be treated at a velocity such as to form a fluidized bed whose particles mechanically keep the electrodes clean.
According to a preferred embodiment of the invention, the electrolytic cell comprises a cylindrical container with a lower inlet opening and an upper outlet opening for the water flow, radially disposed cathodes, and a centrally located anode surrounded by a porous electrodialysis diaphragm completely surrounding it and forming a closed anode compartment having a small upper aperture for the escape of produced gases and of liquids that have permeated through the porous diaphragm.
Near the inlet and outlet, grids may be located whose function is to prevent particles in the cell from escaping through the inlet or outlet. The particles, due to the velocity of the water flow, are agitated thus forming an unrestricted fluidized bed of particles surrounding the cathodes, and by their movement continuously clean the electrode in a mechanical way. Due to the electrical potential difference between the electrodes, a concentration gradient is established which serves through the electrodialysis to concentrate the anions within the anode compartment. For example, if water containing 3 ppm chloride ions is electrolyzed without using an electrodialysis diaphragm no chlorine is produced, but only oxygen is produced at the anode. Once the diaphragm is used, the chloride concentration increases within the anode compartment up to a level which causes formation of free chlorine. If chloride ions are absent, other ions for example carbonate ions or sulphate ions in the water, concentrate in the anode compartment forming through electrolysis percarbonate or persulphate which are also excellent oxidizing agents. In the same way any organic acid will be oxidized.
In another preferred embodiment of the invention an electrolytic cell comprises a transparent cylinder as the container having a lower inlet opening and an upper outlet opening, each provided with a grid. In the interior of the cylinder are radially disposed electrodes whose length in the axial direction of the cylinder is about 1/2 to 2/3 the length of the cylinder, and in the centre of the cylinder there is a concentric cylindrical anode ring compartment defined by an outer cylindrical diaphragm and an inner concentric cylindrical pipe with the anode between them. The anode ring compartment is closed at both ends and has at least one upper small opening to permit escape of products formed within the anode compartment. The axial length of anode, anode compartment and inner pipe is substantially the same as that of the cathodes outside the anode compartment. Within the cylinder (i.e. the outer wall of the cell) and outside the anode compartment, there are sufficient particles whose size is greater than that of the openings of the grids. These particles are agitated by the flowing water in the cell and rise up to surround the cathodes (in the cathode compartment), thereby cleaning them mechanically through impact and scratching. The upper free space in the interior of the cell serves as a disengaging space for the particles so that, in case the water flow rate is too high, the particles do not become entrained and held at the upper grid. The purpose of the central pipe (inner boundary of the anode ring compartment) is to permit recirculation of the particles flowing upwardly in the cathode compartment and downwardly through the inner pipe, especially when the lower grid below the lower end of the central pipe is blocked at its centre, i.e. has no apertures.
The invention will now be described by way of example, with reference to the drawings, in which: Fig.1 is a section through a first embodiment; Fig. 2 is a section through a second embodiment; Fig. 3 is a section through a third embodiment; and Fig. 4 is a section through a fourth embodiment.
Referring to Figure 1 an electrolytic cell has a cylindrical container 1 with a lower inlet 2 and an upper outlet 3 for water flow radially disposed cathodes 4, and a central axial anode 5 with a porous electrodialysis diaphragm 6 completely surrounding it and forming a closed anode compartment 7 having a small upper aperture 8 for the escape of produced gases and of liquids that have permeated through the porous diaphragm 6.
Located below, near the inlet 2 and above, near the outlet 3 there are grids 9 and 10, respectively, whose function is to prevent particles 11 within the cell escaping through the inlet 2 or outlet 3 of the cell.
Fig. 2 shows an electrolytic cell comprising a cylinder 1 having a lower inlet 2 and an upper outlet 3 with grids 9 and 10, respectively. In the cylinder 1 are radially disposed cathodes 4 whose length in the axial direction of the cylinder 1 is shorter than the total length of the cylinder 1. The axial length of the anode 5, anode compartment 7 and an inner pipe 12 is the same as that of the cathodes 4. The compartment 7 has the small upper aperture 8. Within the cylinder 1 are sufficient particles 11 whose size is greater than that of the openings of grids 9, 10. The upper free space in the interior of cell 1 serves as a disengaging space 13 for the particles. The central part 9' of lower grid 9 has no apertures. The upper grid 10 has apertures both in the horizontal portions and in the vertical cylindrical portions 10' to provide a greater area. The distances between the pipe 12 and each grid is greater than the largest particle size. The distance between the upper end of the pipe 12 and the upper grid is not less than 10% of the length of the pipe.
Fig. 3 shows an electrolytic cell comprising a cylinder 1 having a lower inlet 2 and an upper outlet 3 provided with grids 9 and 10, respectively. In the interior of the cylinder 1 are radially disposed alternate cathodes 4 and anodes 5'. The centre of the cell 1 has a pipe 12 open at both ends which serves to direct the particles 11 downwardly. Below pipe 12 there is positioned a grid 9 whose central part 9' is closed to the flow of water, and above the electrodes 4 and 5' and the pipe 12 is a disengaging space 13 for the particles.
Fig. 4 shows a cell 1 in which the inlet 2 and the outlet 3 are connected to a by-pass conduit 15 outside the cell 1. In the by-pass conduit 15 is interposed a pump 14 which recirculates water through the cell 1 to provide a sufficient flow rate to agitate and entrain the particles within the cell 1. It is also provided with an inlet 16 for the untreated water and an outlet 17 for treated water.
With reference to Fig. 2 another embodiment is obtained by omitting the electrodialysis diaphragm 6 and by using corrodable metals for anode 5.
It is also possible to dispose an energized turbine or propeller (not shown) within pipe 12 of Figs. 2 and 4 to provide additional reflux and to ensure enough contact time between particles 11 and electrodes 4, 5'.
With reference to Figs 1 to 4 it is also possible to provide an additional outer pipe (not shown) between the radially disposed electrodes 4 or 4, 5' and the outer cylinder 1.
The distance between this pipe and the cylin der 1 must be large enough to allow free downward flow of particles 11. The holes in the lower grid 9 can be closed along the periphery of grid 9 at least to an extent cor responding to the distance between the outer pipe and cylinder 1.
The materials for constructing the electrolytic cell of the invention, e.g. as illustrated in Figs. 1 and 2, are as follows: The anodes are preferably of platinized titanium or niobium in mesh form, although they also can be of any other metal of the platinum family that resists corrosion, or they can be of graphite or carbon or metal oxides. The anodes can be solid or in the form of a grid.
The corrodable anodes of Figs. 3 and 4 are preferably chosen from the metals commonly used in water treatment, for example aluminium, iron and copper for the provision of flocking materials in water treatment processes, or metals for example silver and copper to provide oligodynamic disinfecting ions to the water being treated.
As material for the cathodes, any conductive material can be used, preferably stainless steel or copper.
Materials for the construction of the cylinder, inlet, outlet, grids, pipes and supports are e.g. plastics, porcelain, glass, hard rubber and concrete, or a metal which can act as cathode.
Materials for the electrodialysis diaphragms are e.g. porous porcelain, microporous plastics for example polyolefines and polyvinylchloride, cellulose nitrate, and ion exchange resins. In case the porous diaphragms are mechanically sensitive to impact by the particles they can be shielded with a protective grid of a non-conductive material, for example a plastics material.
The particles in the cell can be spheres of porcelain, hard plastics, stone, glass, alumina and any other hard materials whose density is greater than that of the water to be treated.
Of course, the size of these particles must be larger than that of the openings of the grids which are to retain them within the cell.
The cell need not be cylindrical, but can be elliptical or hexagonal in section. Also the closed grid area can have other shapes depending on the flow pattern required within the cell. It is also possible, for example, to combine the central anode with additional radially disposed anodes of the same or other metals, with or without centrally or outwardly located downflow pipes, or any other combination thereof.
WHAT WE CLAIM IS: 1. A continuous process for treatment of water and simultaneously for keeping clean electrodes in an electrolytic cell, comprising flowing a stream of water to be treated upwardly past electrodes in the cell which contains freely movable particles whose density is greater than that of the water, controlling the velocity of the flowing stream so as to form a fluidized bed of the particles in the cell and so as mechanically to keep the electrodes clean by virtue of the kinetic energy generated by fluidization of the particles.
**WARNING** end of DESC field may overlap start of CLMS **.

Claims (10)

  1. **WARNING** start of CLMS field may overlap end of DESC **.
    upper outlet 3 with grids 9 and 10, respectively. In the cylinder 1 are radially disposed cathodes 4 whose length in the axial direction of the cylinder 1 is shorter than the total length of the cylinder 1. The axial length of the anode 5, anode compartment 7 and an inner pipe 12 is the same as that of the cathodes 4. The compartment 7 has the small upper aperture 8. Within the cylinder 1 are sufficient particles 11 whose size is greater than that of the openings of grids 9, 10. The upper free space in the interior of cell 1 serves as a disengaging space 13 for the particles. The central part 9' of lower grid 9 has no apertures. The upper grid 10 has apertures both in the horizontal portions and in the vertical cylindrical portions 10' to provide a greater area. The distances between the pipe 12 and each grid is greater than the largest particle size. The distance between the upper end of the pipe 12 and the upper grid is not less than 10% of the length of the pipe.
    Fig. 3 shows an electrolytic cell comprising a cylinder 1 having a lower inlet 2 and an upper outlet 3 provided with grids 9 and 10, respectively. In the interior of the cylinder 1 are radially disposed alternate cathodes 4 and anodes 5'. The centre of the cell 1 has a pipe 12 open at both ends which serves to direct the particles 11 downwardly. Below pipe 12 there is positioned a grid 9 whose central part 9' is closed to the flow of water, and above the electrodes 4 and 5' and the pipe 12 is a disengaging space 13 for the particles.
    Fig. 4 shows a cell 1 in which the inlet 2 and the outlet 3 are connected to a by-pass conduit 15 outside the cell 1. In the by-pass conduit 15 is interposed a pump 14 which recirculates water through the cell 1 to provide a sufficient flow rate to agitate and entrain the particles within the cell 1. It is also provided with an inlet 16 for the untreated water and an outlet 17 for treated water.
    With reference to Fig. 2 another embodiment is obtained by omitting the electrodialysis diaphragm 6 and by using corrodable metals for anode 5.
    It is also possible to dispose an energized turbine or propeller (not shown) within pipe
    12 of Figs. 2 and 4 to provide additional reflux and to ensure enough contact time between particles 11 and electrodes 4, 5'.
    With reference to Figs 1 to 4 it is also possible to provide an additional outer pipe (not shown) between the radially disposed electrodes 4 or 4, 5' and the outer cylinder 1.
    The distance between this pipe and the cylin der 1 must be large enough to allow free downward flow of particles 11. The holes in the lower grid 9 can be closed along the periphery of grid 9 at least to an extent cor responding to the distance between the outer pipe and cylinder 1.
    The materials for constructing the electrolytic cell of the invention, e.g. as illustrated in Figs. 1 and 2, are as follows: The anodes are preferably of platinized titanium or niobium in mesh form, although they also can be of any other metal of the platinum family that resists corrosion, or they can be of graphite or carbon or metal oxides. The anodes can be solid or in the form of a grid.
    The corrodable anodes of Figs. 3 and 4 are preferably chosen from the metals commonly used in water treatment, for example aluminium, iron and copper for the provision of flocking materials in water treatment processes, or metals for example silver and copper to provide oligodynamic disinfecting ions to the water being treated.
    As material for the cathodes, any conductive material can be used, preferably stainless steel or copper.
    Materials for the construction of the cylinder, inlet, outlet, grids, pipes and supports are e.g. plastics, porcelain, glass, hard rubber and concrete, or a metal which can act as cathode.
    Materials for the electrodialysis diaphragms are e.g. porous porcelain, microporous plastics for example polyolefines and polyvinylchloride, cellulose nitrate, and ion exchange resins. In case the porous diaphragms are mechanically sensitive to impact by the particles they can be shielded with a protective grid of a non-conductive material, for example a plastics material.
    The particles in the cell can be spheres of porcelain, hard plastics, stone, glass, alumina and any other hard materials whose density is greater than that of the water to be treated.
    Of course, the size of these particles must be larger than that of the openings of the grids which are to retain them within the cell.
    The cell need not be cylindrical, but can be elliptical or hexagonal in section. Also the closed grid area can have other shapes depending on the flow pattern required within the cell. It is also possible, for example, to combine the central anode with additional radially disposed anodes of the same or other metals, with or without centrally or outwardly located downflow pipes, or any other combination thereof.
    WHAT WE CLAIM IS: 1. A continuous process for treatment of water and simultaneously for keeping clean electrodes in an electrolytic cell, comprising flowing a stream of water to be treated upwardly past electrodes in the cell which contains freely movable particles whose density is greater than that of the water, controlling the velocity of the flowing stream so as to form a fluidized bed of the particles in the cell and so as mechanically to keep the electrodes clean by virtue of the kinetic energy generated by fluidization of the particles.
  2. 2. An electrolytic cell when used for car
    rying out the process of claim 1, the cell comprising a closed container with a lower inlet opening and an upper outlet opening for the water to be treated, electrodes in the container for connection to the positive and the negative poles of a D.C. source, particles whose density is greater than that of the water to be treated, and means for retaining the particles within the container, wherein the particles are freely movable and are fluidized by the flowing movement of water to be treated at a velocity such as to form a fluidized bed whose particles mechanically keep the electrodes clean.
  3. 3. A cell according to claim 2, wherein a closed anode compartment in the container is defined by an electodialysis diaphragm with an anode therein and provided with a small upper aperture and wherein at least one cathode in the container is outside the anode compartment.
  4. 4. A cell according to claim 2 or claim 3, having radially disposed electrodes in the container.
  5. 5. A cell according to any of claims 2 to 4, wherein a pipe open at both ends is disposed in the container, the lower end of the pipe being spaced from a lower grid covering the lower inlet opening, and the upper end of the pipe being spaced from an upper grid upstream of the upper outlet opening, the distances between the pipe and each grid being greater than the largest particle size.
  6. 6. A cell according to claim 5, wherein the distance between the upper end of the pipe and the upper grid is at least 10 percent of the length of the pipe.
  7. 7. A cell according to claim 5 or claim 6, wherein a propeller is disposed in the interior of the pipe.
  8. 8. A cell according to any of claims 2 to 6, wherein a bypass conduit is disposed outside the container, the conduit being connected at its respective ends to the outlet and inlet openings, and having a pump in the bypass conduit.
  9. 9. A cell according to any of claims 2 to 8, wherein the container is cylindrical and within the container a closed anode ring compartment is disposed centrally and axially, the ring compartment being defined by an inner tube open at both ends and an outer concentric electrodialysis diaphragm which contains an anode and which is provided with an upper small aperture.
  10. 10. An electrolytic cell constructed and arranged substantially as herein described and shown in the drawings.
GB27000/76A 1975-07-16 1976-06-29 Electrolytic cell for treatment of water Expired GB1560730A (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
DE19752531850 DE2531850A1 (en) 1975-07-16 1975-07-16 ELECTROLYSIS CELL FOR WATER TREATMENT
DE19762607906 DE2607906A1 (en) 1976-02-26 1976-02-26 ELECTROLYSIS CELL FOR WATER TREATMENT

Publications (1)

Publication Number Publication Date
GB1560730A true GB1560730A (en) 1980-02-06

Family

ID=25769165

Family Applications (1)

Application Number Title Priority Date Filing Date
GB27000/76A Expired GB1560730A (en) 1975-07-16 1976-06-29 Electrolytic cell for treatment of water

Country Status (16)

Country Link
JP (1) JPS5212752A (en)
AT (1) AT353707B (en)
AU (1) AU504005B2 (en)
BR (1) BR7604451A (en)
CA (1) CA1090292A (en)
CH (1) CH598138A5 (en)
DK (1) DK320376A (en)
ES (1) ES449887A1 (en)
FR (1) FR2318115A1 (en)
GB (1) GB1560730A (en)
IL (1) IL49852A (en)
IN (1) IN143282B (en)
MX (1) MX143221A (en)
NL (1) NL7607843A (en)
NO (1) NO762273L (en)
SE (1) SE7607833L (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1880980A1 (en) * 2006-07-20 2008-01-23 Hydrotech International Ltd. Device for electromagnetic desalination of sea water
WO2009030668A1 (en) * 2007-09-03 2009-03-12 Siemens Aktiengesellschaft Device and process for breaking down pollutants in a liquid and also use of such a device
EP2460768A1 (en) * 2010-12-01 2012-06-06 Premier Tech Technologies Ltee. A self-cleaning electro-reaction unit for wastewater treatment and related process

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
NL1035953C (en) * 2008-09-18 2010-03-19 Stichting Wetsus Ct Excellence Sustainable Water Technology Device and method for disinfection and/or purification of a fluid.
FR3092841B1 (en) * 2019-02-15 2021-01-29 A S Pool Electrolysis cell for electrolytic treatment of a liquid

Family Cites Families (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR409753A (en) * 1909-11-27 1910-04-30 Auguste Cauchemez Tank intended for the electrolysis of liquids and, in particular, water
FR880435A (en) * 1940-07-27 1943-03-25 Advanced diaphragm electrolytic cell
US2563903A (en) * 1949-12-07 1951-08-14 Zadra John Benjamin Electrolytic cell for the deposition of gold and/or silver from solutions
NL128653C (en) * 1964-11-30
US3580061A (en) * 1970-01-16 1971-05-25 Federal Mogul Corp Seal-testing device
JPS5128938B1 (en) * 1970-11-26 1976-08-23
IT953306B (en) * 1971-04-14 1973-08-10 Hooker Chemical Corp PROCEDURE FOR THE REDUCTION OF THE METALLIC CONTENT OF LIQUIDS BY AN ELECTROCHEMICAL TECHNIQUE
DE2244244C3 (en) * 1972-09-15 1981-07-02 Dart Industries Inc., 90048 Los Angeles, Calif. Electrolytic process for removing a contaminant dissolved in an aqueous spent solution and regenerative electrolytic cell which can be used for this purpose
GB1423369A (en) * 1973-09-24 1976-02-04 Electricity Council Electrolytic cells
FR2316196A1 (en) * 1975-06-30 1977-01-28 Sorapec Electrochemical purification of industrial effluent - esp. from paper mills, by continuous anodic oxidation of organic pollutants

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1880980A1 (en) * 2006-07-20 2008-01-23 Hydrotech International Ltd. Device for electromagnetic desalination of sea water
WO2009030668A1 (en) * 2007-09-03 2009-03-12 Siemens Aktiengesellschaft Device and process for breaking down pollutants in a liquid and also use of such a device
EP2460768A1 (en) * 2010-12-01 2012-06-06 Premier Tech Technologies Ltee. A self-cleaning electro-reaction unit for wastewater treatment and related process
US9216918B2 (en) 2010-12-01 2015-12-22 Premier Tech Technologies Ltee Self-cleaning electro-reaction unit for wastewater treatment and related process

Also Published As

Publication number Publication date
ES449887A1 (en) 1977-08-16
AT353707B (en) 1979-11-26
AU504005B2 (en) 1979-09-27
FR2318115A1 (en) 1977-02-11
MX143221A (en) 1981-04-03
CA1090292A (en) 1980-11-25
DK320376A (en) 1977-01-17
SE7607833L (en) 1977-01-17
BR7604451A (en) 1977-07-26
NL7607843A (en) 1977-01-18
IN143282B (en) 1977-10-29
IL49852A (en) 1980-07-31
IL49852A0 (en) 1976-08-31
JPS5212752A (en) 1977-01-31
NO762273L (en) 1977-01-18
CH598138A5 (en) 1978-04-28
AU1528376A (en) 1978-01-05
ATA450976A (en) 1979-04-15

Similar Documents

Publication Publication Date Title
US4121991A (en) Electrolytic cell for treatment of water
US4048030A (en) Electrolytic cell for treatment of water
US4119518A (en) Electrolytic cell for treatment of water
US5256268A (en) Water treatment method and apparatus
US4306952A (en) Electrolytic process and apparatus
US3752747A (en) Method for controlling algae pollution
US5958213A (en) Water treatment method and apparatus for water containing oil droplets
GB1567817A (en) Electrolytic cells
US4123339A (en) Method and apparatus for electrochemical contaminant removal from liquid media
KR101812008B1 (en) An electrolyzer having a porous 3-dimensional mono-polar electrodes, and water treatment method using the electrolyzer having the porous 3-dimensional mono-polar electrodes
JP2002531704A (en) Electrolytic apparatus, method for purifying aqueous solution, and method for synthesizing chemical substance
US4619745A (en) Process for the electrochemical decontamination of water polluted by pathogenic germs with peroxide formed in situ
JPS5932548B2 (en) Electrolysis method and electrolyzer
US20180354818A1 (en) Improved construction of devices for purification and disinfection of waste water with electrical current
JPS5833036B2 (en) Suiyouekichiyuunoshiankabutsu Oyobi Jiyukinzokunodoujijiyokiyonohouhou Narabini Souchi
US4243501A (en) Process and apparatus for the regeneration of chromic acid baths
US8080150B2 (en) Electrolytic cell
EP2675758B1 (en) An improved electrochemical coagulation process for the removal of nitrate from drinking water
GB1560730A (en) Electrolytic cell for treatment of water
WO2005058761A1 (en) Electrolytic cell for treating contamined water
GB1124185A (en) A method of preventing adherence of marine life to a structure in sea water
US3728238A (en) Decreasing hexavalent chromium content of liquids by an electrochemical technique
WO1994004720A1 (en) Electrolytic oxidizer
JP2006198619A (en) Process for treatment of liquid and apparatus therefor
CA2323505A1 (en) Electrolytic cell with porous membranes to concentrate anions

Legal Events

Date Code Title Description
PS Patent sealed [section 19, patents act 1949]
PCNP Patent ceased through non-payment of renewal fee