US3082160A - Electrolytic method - Google Patents
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- US3082160A US3082160A US760971A US76097158A US3082160A US 3082160 A US3082160 A US 3082160A US 760971 A US760971 A US 760971A US 76097158 A US76097158 A US 76097158A US 3082160 A US3082160 A US 3082160A
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/463—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrocoagulation
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- C—CHEMISTRY; METALLURGY
- C25—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
- C25B—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES FOR THE PRODUCTION OF COMPOUNDS OR NON-METALS; APPARATUS THEREFOR
- C25B1/00—Electrolytic production of inorganic compounds or non-metals
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- Electrolytic cells have long been in use in conjunction with various processes. Such cells, however, normally have consisted of an anode and a cathode or e plurality of anodes and cathodes connected in parallel. With certain processes in which conventional electrolytic cells are used, it has been found that large amounts of power are required for removing substances in solution from the electrolyte. It is readily apparent, therefore, that there is a need for an electrolytic cell which can be utilized for removing substances from solution from the electrolyte with low amounts of energy.
- Another object of the invention is to provide an electrolytic apparatus and method of the above character which is particularly adapted for removing substances from sea water.
- Another object of the invention is to provide an electrolytic apparatus and method of the above character which can be utilized for the removal of minerals and the like from water to reduce the hardness of the water.
- Another object of the invention is to provide an electrolytic apparatus and method of the above character which can be utilized for the treatment and reclamation of waste water.
- Another object of the invention is to provide an electrolytic apparatus and method of the above character which can be utilized for the treatment of sewage.
- Another object of the invention is to provide a method and apparatus of the above character which does not require ion migration through substantial distances.
- Another object of the invention is to provide an apparatus and method of the above character which has reduced energy requirements.
- Another object of the invention is to provide an electrolytic apparatus which is particularly adapted for removing dissolved substances from an electrolyte.
- FIGURE 1 is a cross-sectional view taken along the line 1-1 of FIGURE 2 showing electrolytic apparatuswith certain parts schematically illustrated incorporating the present invention and which can be utilized in performing my method.
- FIGURE 2 is a cross-sectional view taken along the line 2-2 of FIGURE 1.
- the present invention consists of an electrolytic apparatus which has a particularly novel construction.
- the electrolytic cell consists of three separate electrodes which are immersed in the electrolyte.
- Circuit means including a D.-C. power supply is provided for impressing a currentfiow between the first and second electrodes so that the first electrode serves as an anode and the second electrode serves as a cathode with respect to the first electrode.
- Additional circuit means is provided for connecting the second electrode to the third electrode so that the second electrode serves as an anode with respect to the third electrode.
- Means is provided for adjusting the current flow through both of the circuit means so that desired polarization levels are maintained on the electrodes. It has been found that an electrolytic cell which will be referred to as a tri-electrode cell, has many commercial applications particularly in the fields of removing dissolved substances from electrolytes.
- sea water as an electrolyte and the removal of substances therefrom.
- the composition of sea water is generally as follows:
- Such an electrolytic cell consists of a tank 11, provided with a cover 12 both of which are formed of suitable insulating material such as clear plastic.
- the tank is filled with sea water 13 to the level shown.
- a plurality of electrodes 14 which form a part of the electrolytic cell are immersed or submerged in the electrolyte or sea water 13.
- Three. different types of electrodes 14 are utilized within the electrolytic cell. They are the cathode 16, cathode-anode 17 and the anode 18.
- These electrodes can be formed of any suitable material and in any desired manner.
- the cathodes 16 as shown can be formed of a plurality of horizontal vertically spaced star-shaped steel plates 21 mounted on a rod 22. each of which is provided with three points 21a, 21b and 210, spaced apart.
- the cathode 16 is centrally disposed within the tank 11 and is oriented in such a manner that the points 21a, 21b and 210 are directed toward the cathode-anodes 17.
- the cathode-anodes 17 can also be of any desired shape and formed of any suitable material. For example, as shown, they can be in the form of magnesium alloy rods.
- the anodes 18 were spaced between the cathodeanodes 17 and can be formed of a suitable material such as platinum wire.
- Circuit means 26 including a D.-C. power supply 27 is connected between the anodes l8 and the cathodeanodes 17 to impress a current flow between the same. It will be noted that all of the anodes 18 and all the cathode-anodes 17 are connected in parallel to the D.-C. power supply 27.
- the circuit means 26 also includes a potentiometer 28 for adjusting the rate of current flow through the circuit means 26.
- Circuit means 29 is provided for connecting the cathode-anodes 17 to the cathode 16, and includes a potentiometer 31 for varying the current flow in this circuit.
- the potentiomcters 28 and 31 serve to vary the polarization levels on the electrodes as hereinafter described.
- Cone-like members 33 and 34 are formed on the cover 12 and overlie the anodes 18 and the cathodeanodes 17. These cone-like members are connected to lead-out pipes '36 and 37. Skirts 38 of suitable material such as asbestos cloth are secured to the lower ends of the cone-like members 34 and encompass or surround the platinum anodes 18 for a purpose hereinafter described.
- a D.-C. power supply 27 of seven volts was utilized.
- the potentiometers 28 and 31 were adjusted so that the magnesium alloy cathode-anodes had a polarization level of 3300 millivolts with respect to a silver-silver chloride half cell and the cathode 16 had a polarization level of 1100 millivolts with respect to a silver-silver chloride half cell.
- one electrolytic cell utilized for carrying out my method consisted of a tank 11 which held approximately 20 gallons of water.
- the steel starshaped plates 21 were formed of 20 gauge steel and provided a cathode surface area of approximately 20 square feet.
- the magnesium anodes were approximately inch in diameter and had a length of 10 inches.
- the platinum anodes 18 were formed of 14 gauge wire approximately 6 inc-hes in length. With this apparatus, a current flow of amperes was impressed through the circuit means 26..
- magnesium hydroxide is removed from the sea water with a very small amount of power e.g. for removing the magnesium hydroxide from approximately 20 gallons of water, 17.5 watt hours were consumed.
- the low power requirement can be explained by the fact that my electrolytic apparatus or cell contains an electrode, the cathode-anodes 17, which serves as a cathode and as an anode and thus serves to attract both positive ions and negative ions which are normally cations and anions respectively.
- the magnesium ions which are cations and the hydroxide ions which are anions are both attracted to the cathode-anodes 17 to permit the discharge of their ions at the cathode-anode electrode and to permit ready formation of magnesium hydroxide in this area.
- the ions must generally migrate through long distances in the electrolyte in the electrolytic cell.
- the magnesium ions would be attracted to one electrode and the other hydroxide ions would be attracted to the opposite electrode which generally would be far removed from each other and, therefore, inhibiting the formation of magnesium hydroxide.
- my method and process is also adapted for a continuous flow process as well as a batch process.
- it could be passed through a plurality of electrolytic cells after which the magnesium hydroxide could be readily removed by screening.
- the screened magnesium hydroxide may then be dehydrated.
- the magnesium hydroxide may be used for any desired purpose such as for the production of magnesium in a manner well known to those skilled in the art.
- the use of the tri-electrode cell is particularly advantageous in removing elements of hardness from sea water and also from fresh water.
- the water will have a much lower mineral content.
- the use of the trielectrode cell or system is particularly advantageous in the treatment of sewage.
- Heat is given off at the anode which serves as a secondary digester' for the sewage.
- migration of ions through the sewage breaks down the entrapped gases in the sewage and thereby liberates sulfides, chlorides and/or other organic acids. This has a particular advantage in that it decreases the chlorine required for sewage treatment and also in that it reduces the quantity of the solids.
- one electrode, cell or system utilized for treatment of sewage utilized 1.7 amperes of 12 volt direct current in which a steel cathode was maintained at a polarization of 1500 millivolts with respect to a silver-silver chloride half cell and the magnesium cathode-anode at a polarization level of 4000 millivolts.
- the temperature of the sludge around the platinum anode had been raised from a temperature of 75 -F. to 118 F.
- a method for electrolytically removing magnesium hydroxide from sea water by precipitation impressing a current flow from an external source of direct current between a platinum anode and a magnesium electrode, permitting current flow between the magnesium electrode and a steel cathode and regulating the current flow between the anode and the magnesium electrode and between the magnesium electrode and the cathode so that the polarization level on the magnesium electrode is approximately 3300 millivolts and the polarization level on the cathode is approximately 1100 millivolts.
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Description
March '19, 1963 R. c. SABINS 3,082,160
mmc'mou'rrc METHOD Filed Sept. 15, 1958 ALLOY INVENTOR.
Ga/land C. fab/n:
A TTOIPNE YJ' United. States Patent Ofifice 3,082,160 Patented Mar. 19, 1963 3,082,160 ELECTROLYTIC METHOD Rolland C. Sabins, 522 Catalina Blvd San Diego, Calif. Filed Sept. 15, 1958, Ser. No. 760,971 1 Claim. (Cl. 204-96) This invention relates generally to an electrolytic apparatus and method and more particularly to an electrolytic apparatus and method for removing substances in solution from the electrolyte.
This application is a continuation in part of my co pending application Serial No. 586,969, new Patent No. 2,903,405, and my co-pending application Serial No. 645,353, filed. March 11, 1957, now abandoned, and which was a continuation of the aforementioned application Serial No. 586,969, now Patent No. 2,867,913 entitled "Electrolytic Cell Employing a Cathode, Anode, and a Cathode-Anode-Electrodc.
Electrolytic cells have long been in use in conjunction with various processes. Such cells, however, normally have consisted of an anode and a cathode or e plurality of anodes and cathodes connected in parallel. With certain processes in which conventional electrolytic cells are used, it has been found that large amounts of power are required for removing substances in solution from the electrolyte. It is readily apparent, therefore, that there is a need for an electrolytic cell which can be utilized for removing substances from solution from the electrolyte with low amounts of energy.
In general, it is an object of the present invention to provide an electrolytic apparatus and methodwhich can,v
be utilized for removing substances in solution from electrolytes or, in other words for causing decomposition of the electrolyte.
Another object of the invention is to provide an electrolytic apparatus and method of the above character which is particularly adapted for removing substances from sea water.
Another object of the invention is to provide an electrolytic apparatus and method of the above character which can be utilized for the removal of minerals and the like from water to reduce the hardness of the water.
Another object of the invention is to provide an electrolytic apparatus and method of the above character which can be utilized for the treatment and reclamation of waste water.
Another object of the invention is to provide an electrolytic apparatus and method of the above character which can be utilized for the treatment of sewage.
Another object of the invention is to provide a method and apparatus of the above character which does not require ion migration through substantial distances.
Another object of the invention is to provide an apparatus and method of the above character which has reduced energy requirements.
Another object of the invention is to provide an electrolytic apparatus which is particularly adapted for removing dissolved substances from an electrolyte.
Additional objects and features of the invention will appear from the following description in which the preferred embodiment of the invention has been set forth in detail in conjunction with the accompanying drawing.
Referring to the drawing:
FIGURE 1 is a cross-sectional view taken along the line 1-1 of FIGURE 2 showing electrolytic apparatuswith certain parts schematically illustrated incorporating the present invention and which can be utilized in performing my method.
FIGURE 2 is a cross-sectional view taken along the line 2-2 of FIGURE 1.
In general, the present invention consists of an electrolytic apparatus which has a particularly novel construction. The electrolytic cell consists of three separate electrodes which are immersed in the electrolyte. Circuit means including a D.-C. power supply is provided for impressing a currentfiow between the first and second electrodes so that the first electrode serves as an anode and the second electrode serves as a cathode with respect to the first electrode. Additional circuit means is provided for connecting the second electrode to the third electrode so that the second electrode serves as an anode with respect to the third electrode. Means is provided for adjusting the current flow through both of the circuit means so that desired polarization levels are maintained on the electrodes. It has been found that an electrolytic cell which will be referred to as a tri-electrode cell, has many commercial applications particularly in the fields of removing dissolved substances from electrolytes.
In describing in detail one procedure for carrying out the invention, reference will be made to the use of sea water as an electrolyte and the removal of substances therefrom. The composition of sea water is generally as follows:
Table I.Comp0siti0n of Sea Water [In grams per liter of sp. gr.=1.0241
In the treatment of sea water in its natural condition in accordance with the present invention, it is desirable to utilize an electrolytic apparatus or cell such as that illustrated partially in schematic form in FIGURES 1 and 2 of the drawing.
Such an electrolytic cell consists of a tank 11, provided with a cover 12 both of which are formed of suitable insulating material such as clear plastic. The tank is filled with sea water 13 to the level shown. A plurality of electrodes 14 which form a part of the electrolytic cell are immersed or submerged in the electrolyte or sea water 13. Three. different types of electrodes 14 are utilized within the electrolytic cell. They are the cathode 16, cathode-anode 17 and the anode 18. These electrodes can be formed of any suitable material and in any desired manner. For example, the cathodes 16 as shown can be formed of a plurality of horizontal vertically spaced star-shaped steel plates 21 mounted on a rod 22. each of which is provided with three points 21a, 21b and 210, spaced apart.
The cathode 16 is centrally disposed within the tank 11 and is oriented in such a manner that the points 21a, 21b and 210 are directed toward the cathode-anodes 17. The cathode-anodes 17 can also be of any desired shape and formed of any suitable material. For example, as shown, they can be in the form of magnesium alloy rods. The anodes 18 were spaced between the cathodeanodes 17 and can be formed of a suitable material such as platinum wire.
Circuit means 26 including a D.-C. power supply 27 is connected between the anodes l8 and the cathodeanodes 17 to impress a current flow between the same. It will be noted that all of the anodes 18 and all the cathode-anodes 17 are connected in parallel to the D.-C. power supply 27. The circuit means 26 also includes a potentiometer 28 for adjusting the rate of current flow through the circuit means 26. Circuit means 29 is provided for connecting the cathode-anodes 17 to the cathode 16, and includes a potentiometer 31 for varying the current flow in this circuit. The potentiomcters 28 and 31 serve to vary the polarization levels on the electrodes as hereinafter described.
Cone- like members 33 and 34 are formed on the cover 12 and overlie the anodes 18 and the cathodeanodes 17. These cone-like members are connected to lead-out pipes '36 and 37. Skirts 38 of suitable material such as asbestos cloth are secured to the lower ends of the cone-like members 34 and encompass or surround the platinum anodes 18 for a purpose hereinafter described.
In operation of the electrolytic apparatus or cell, in
one specific embodiment a D.-C. power supply 27 of seven volts was utilized. The potentiometers 28 and 31 were adjusted so that the magnesium alloy cathode-anodes had a polarization level of 3300 millivolts with respect to a silver-silver chloride half cell and the cathode 16 had a polarization level of 1100 millivolts with respect to a silver-silver chloride half cell.
In practicing my method as soon as the cathode-anodes 17 and the cathode 16 have been approximately adjusted to the above polarization levels, the sea water within the tank -11 immediately will begin to cloud up which is caused by a flocking of magnesium hydroxide. Within approximately 30 minutes a large quantity of magnesium hydroxide will have formed and will have settled to the bottom of the tank.
By way of example, one electrolytic cell utilized for carrying out my method consisted of a tank 11 which held approximately 20 gallons of water. The steel starshaped plates 21 were formed of 20 gauge steel and provided a cathode surface area of approximately 20 square feet. The magnesium anodes were approximately inch in diameter and had a length of 10 inches. The platinum anodes 18 were formed of 14 gauge wire approximately 6 inc-hes in length. With this apparatus, a current flow of amperes was impressed through the circuit means 26..
Using sea water from the San Diego Bay, the following results were obtained with this apparatus:
Table II Analysis 0! Analysis of Seawater Seawater Before After Treatment Treatment Total Hardness (CaCOa) 6, 200 800 Calcium Hardness (C8001) 1.000 800 Magnesium Hardness (CaCOa)- 5,200 0 Alkalinity P (CaCOs) 0 8 Alkalinity M (CaCOQ 100 6,000 Caustic Alkalinity (Oil) (CaCOg) Free Carbon Dioxide (00:) (CaCOz) 123 0 Chlorides (Cl) 18,000 8,800 sulphates (S04) 3. 840 3.100 Total Dissolved Solids (conductivity 41,000 38,000 Iron (Fe) M Silica (SlOz) H 7. 4 l2. 9 Eurbidity none none Color clear clear Hydroxide (Olir) 0 815 The units used in the above water analysis are expressed in parts per million. The hardness is expressed in a conventional manner, that is, in terms of the dissolved calcium and magnesium salts calculated as a calcium carbonate equivalent CaCO;.
The above analysis also indicates that the total hardness (scale forming elements) in the sea water was reduced by 87%. Seventy-six (76) pounds of chlorine gas were recovered per 1,000 galons of sea water and twenty-four (24) pounds of magnesium hydroxide (MgOlh) in relatively pure form were also obtained per 1,000 gallons of sea water.
Qil
During the time the process was carried out, it was found that large amounts of hydrogen gas were also released from the sea water at the magnesium anodes 17. The hydrogen was carried away by the cone-shaped members 33 and into the pipe 36. The chlorine was released at the platinum anode 18 and was collected by the conical members 3 4 and led away by the pipes 37.
During operation of the electrolytic cell, it was found that it was difiicult to prevent hydrochloric acid from forming within the electrolytic cell which tended to decrease the rate of flocking of the magnesium hydroxide. The formation of this hydrochloric acid was eliminated by the placement of the asbestos skirts 38 around the platinum anodes 18. As is well known to those skilled in the art, asbestos cloth is not adversely affected by the chlorine.
It was found that the flocks which formed within the cell and precipitated to the bottom of the tank was a relatively pure magnesium hydroxide. The above analysis of the sea water discloses that practically all of the magnesium ions had been removed from the sea water by treatment with my process.
It is apparent from the foregoing that the magnesium hydroxide is removed from the sea water with a very small amount of power e.g. for removing the magnesium hydroxide from approximately 20 gallons of water, 17.5 watt hours were consumed.
It is believed that the low power requirement can be explained by the fact that my electrolytic apparatus or cell contains an electrode, the cathode-anodes 17, which serves as a cathode and as an anode and thus serves to attract both positive ions and negative ions which are normally cations and anions respectively. Thus in a sea water solution, the magnesium ions which are cations and the hydroxide ions which are anions are both attracted to the cathode-anodes 17 to permit the discharge of their ions at the cathode-anode electrode and to permit ready formation of magnesium hydroxide in this area. In conventional electrolytic cells, the ions must generally migrate through long distances in the electrolyte in the electrolytic cell. In addition, the magnesium ions would be attracted to one electrode and the other hydroxide ions would be attracted to the opposite electrode which generally would be far removed from each other and, therefore, inhibiting the formation of magnesium hydroxide.
It is believed by the utilization of other polarization levels on the cathode and the cathode anode, other substances can be removed from the sea water. However, additional experimentation will be required to establish this belief.
It is readily apparent to one skilled in the art that my method and process is also adapted for a continuous flow process as well as a batch process. For example, in moving streams of sea water, it could be passed through a plurality of electrolytic cells after which the magnesium hydroxide could be readily removed by screening. The screened magnesium hydroxide may then be dehydrated. The magnesium hydroxide may be used for any desired purpose such as for the production of magnesium in a manner well known to those skilled in the art.
As hereinbefore explained, various elements may be used for the electrodes 17. However, when a magnesium alloy is used as a cathode-anode, care must be taken so that the polarization level of the magnesium is high enough to prevent dissolution of the magnesium in the sea water. It has been found that a steel cathode in a of the type shown in the drawing normally has a imtential level of approximately 630 millivolts with reference to a silver-silver chloride half cell, that the magnesium alloy has a potential of 1590 millivolts and that the platinum anode has a reverse potential of minus 850 millivolts. Platinum, of which the anode is formed, is a relatively inert material which is low in the electrochemical series with respect to magnesium.
In order to provide for continuous operation of the electrolytic cell, it is desirable to raise the polarization level of the cathode 16 as well as that of the cathodeanode 17. Thus, to prevent the corrosion of the cathode 16 in the sea water, a potential of over 890 millivolts should be maintained. And, similarly, magnesium, to prevent it from passing into the solution should have a polarization level of 2105 millivolts.
It has been found that the use of the tri-electrode cell is particularly advantageous in removing elements of hardness from sea water and also from fresh water. Thus, after treatment in the tri-electrode cell, the water will have a much lower mineral content.
It also has been found that the use of the trielectrode cell or system is particularly advantageous in the treatment of sewage. Heat is given off at the anode which serves as a secondary digester' for the sewage. Also, migration of ions through the sewage breaks down the entrapped gases in the sewage and thereby liberates sulfides, chlorides and/or other organic acids. This has a particular advantage in that it decreases the chlorine required for sewage treatment and also in that it reduces the quantity of the solids.
By way of example, one electrode, cell or system utilized for treatment of sewage utilized 1.7 amperes of 12 volt direct current in which a steel cathode was maintained at a polarization of 1500 millivolts with respect to a silver-silver chloride half cell and the magnesium cathode-anode at a polarization level of 4000 millivolts. At the end of four hours, it was found that the temperature of the sludge around the platinum anode had been raised from a temperature of 75 -F. to 118 F. With a tank having a depth of 4 feet, it was found that at the end of 4 hours, 4 inches of solids had settled to the bottom of the tank and that after 12 hours, 6 inches of solids had settled to the bottom of the tank and that after 16 hours, the amount of solids had increased to approximately 10 inches. In a tank having similar depth which contained no tri-electrode cell, it was found that with the same sewage, only 4 inches of solids had collected at the bottom of the tank after the end of the test period. From this it is readily apparent that the tri-electrode cell facilitates the separation of the solids from the sewage and thereby facilitates treatment of the sewage. The organic gases liberated during treatment with the tri-elw trode can be utilized for fuel.
It is apparent from the foregoing that I have provided a novel type of electrolytic cell which is particularly adapted for the treatment of electrolytes to remove substances therefrom. It can be used for removing desired substances from the electrolyte such as magnesium hydroxide from sea water. It also can be utilized for removing minerals and the like from sea water and fresh water to reduce the hardness of the water.
I claim:
A method for electrolytically removing magnesium hydroxide from sea water by precipitation, impressing a current flow from an external source of direct current between a platinum anode and a magnesium electrode, permitting current flow between the magnesium electrode and a steel cathode and regulating the current flow between the anode and the magnesium electrode and between the magnesium electrode and the cathode so that the polarization level on the magnesium electrode is approximately 3300 millivolts and the polarization level on the cathode is approximately 1100 millivolts.
References Cited in the file of this patent UNITED STATES'PATENTS Webster Feb. 19, 1889 641,438 Darling Jan. 16, 1900 1,252,654 Betts Jan. 8, 1918 1,312,756 Stover Aug. 12, 1919 1,371,698 Linder Mar. 15, 1921 1,414,423 Langer May 2, 1922 1,526,644 Pinney Feb. 17, 1925 1,541,947 Hartman et al. June 16, 1925 1,567,791 Duhme Dec. 25, 1925 1,837,355 Burns et a1. Dec. 22, 1931 2,128,548 White Aug. 30, 1938 2,158,269 Bowman et al. May 16, 1939 2,316,917 Wallace Apr. 20, 1943 2,341,356 Briggs Feb. 8, 1944 2,490,730 Dublier Dec. 6, 1949 2,696,466 Beaver Dec. 7, 1954 2,752,306 Juda et al. June26, 1956 2,903,405 Sabins Sept. 8, 1959 FOREIGN PATENTS 492,347 Great Britain Sept. 19, 1938 738,520 Great Britain Oct. 12, 1955
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Cited By (7)
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US3436320A (en) * | 1965-05-20 | 1969-04-01 | Union Oil Co | Method and apparatus for determination of redox current in redox solutions |
US3769186A (en) * | 1971-06-02 | 1973-10-30 | Mitsui Mining & Smelting Co | Method of treating waste water through electrolysis |
US4064023A (en) * | 1976-08-09 | 1977-12-20 | The United States Of America As Represented By The Department Of Health, Education And Welfare | Electrochemical growth of calcium hydroxide crystals from electrolyte solutions |
US4124481A (en) * | 1976-10-06 | 1978-11-07 | Ramer James L | Apparatus for treating sewage |
US4151051A (en) * | 1978-05-01 | 1979-04-24 | Evans Robert F | Electrodeposition mining of materials from natural water bodies |
US4356076A (en) * | 1979-08-22 | 1982-10-26 | Director-General Of Agency Of Industrial Science And Technology | Apparatus for the anodic oxidation of aluminum |
EP0499732A1 (en) * | 1991-02-20 | 1992-08-26 | IBBOTT, Jack Kenneth | Dual system using three electrodes to treat fluid |
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US1371698A (en) * | 1918-01-11 | 1921-03-15 | Western Electric Co | Process of and apparatus for electrolysis |
US1414423A (en) * | 1921-04-11 | 1922-05-02 | Langer Carl | Electrolytic separation of metals |
US1541947A (en) * | 1922-03-21 | 1925-06-16 | Electric Water Sterilizer & Oz | Electrolytic cell |
US1526644A (en) * | 1922-10-25 | 1925-02-17 | Williams Brothers Mfg Company | Process of electroplating and apparatus therefor |
US1567791A (en) * | 1924-11-01 | 1925-12-29 | Siemens Ag | Electrolytic production of metals |
US1837355A (en) * | 1926-09-08 | 1931-12-22 | Bell Telephone Labor Inc | Electrodeposition of alloys |
US2158269A (en) * | 1935-10-30 | 1939-05-16 | Anaconda Lead Products Company | Electrolytic process for the manufacture of litharge |
GB492347A (en) * | 1937-03-19 | 1938-09-19 | Sven Harald Lundberg | Method of extracting magnesium oxide from sea water and the like electro-chemically |
US2128548A (en) * | 1937-07-23 | 1938-08-30 | Clarence B White | Process for recovery of metals from scrap and metallurgical residues |
US2316917A (en) * | 1940-02-24 | 1943-04-20 | Us Rubber Co | Process for electrodepositing iron |
US2341356A (en) * | 1940-05-24 | 1944-02-08 | Robert E Briggs | Method of electrolytic precipitation of dissolved substances from solutions |
US2490730A (en) * | 1946-02-12 | 1949-12-06 | Dubilier William | Device for electrically treating liquids |
US2696466A (en) * | 1949-10-14 | 1954-12-07 | Jr John F Beaver | Method of electroplating |
GB738520A (en) * | 1952-04-25 | 1955-10-12 | Rohm & Haas | Process for electrolytically recovering magnesium from sea water |
US2752306A (en) * | 1953-04-14 | 1956-06-26 | Ionics | Production of drinking water |
US2903405A (en) * | 1956-05-24 | 1959-09-08 | Sabins Dohrmann Inc | Corrosion prevention system |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US3436320A (en) * | 1965-05-20 | 1969-04-01 | Union Oil Co | Method and apparatus for determination of redox current in redox solutions |
US3769186A (en) * | 1971-06-02 | 1973-10-30 | Mitsui Mining & Smelting Co | Method of treating waste water through electrolysis |
US4064023A (en) * | 1976-08-09 | 1977-12-20 | The United States Of America As Represented By The Department Of Health, Education And Welfare | Electrochemical growth of calcium hydroxide crystals from electrolyte solutions |
US4124481A (en) * | 1976-10-06 | 1978-11-07 | Ramer James L | Apparatus for treating sewage |
US4151051A (en) * | 1978-05-01 | 1979-04-24 | Evans Robert F | Electrodeposition mining of materials from natural water bodies |
US4356076A (en) * | 1979-08-22 | 1982-10-26 | Director-General Of Agency Of Industrial Science And Technology | Apparatus for the anodic oxidation of aluminum |
EP0499732A1 (en) * | 1991-02-20 | 1992-08-26 | IBBOTT, Jack Kenneth | Dual system using three electrodes to treat fluid |
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