USRE47092E1 - Flow-through oxygenator - Google Patents
Flow-through oxygenator Download PDFInfo
- Publication number
- USRE47092E1 USRE47092E1 US15/085,741 US201615085741A USRE47092E US RE47092 E1 USRE47092 E1 US RE47092E1 US 201615085741 A US201615085741 A US 201615085741A US RE47092 E USRE47092 E US RE47092E
- Authority
- US
- United States
- Prior art keywords
- electrodes
- electrode
- outside
- emitter
- chamber
- 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 - Lifetime
Links
Images
Classifications
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G31/00—Soilless cultivation, e.g. hydroponics
- A01G31/02—Special apparatus therefor
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G31/00—Soilless cultivation, e.g. hydroponics
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01K—ANIMAL HUSBANDRY; AVICULTURE; APICULTURE; PISCICULTURE; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
- A01K63/00—Receptacles for live fish, e.g. aquaria; Terraria
- A01K63/04—Arrangements for treating water specially adapted to receptacles for live fish
- A01K63/042—Introducing gases into the water, e.g. aerators, air pumps
-
- 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
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/46109—Electrodes
-
- 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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/727—Treatment of water, waste water, or sewage by oxidation using pure oxygen or oxygen rich gas
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/12—Activated sludge processes
- C02F3/26—Activated sludge processes using pure oxygen or oxygen-rich gas
-
- 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
- C25B1/01—Products
- C25B1/02—Hydrogen or oxygen
- C25B1/04—Hydrogen or oxygen by electrolysis of water
-
- 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
- C25B15/00—Operating or servicing cells
- C25B15/02—Process control or regulation
-
- 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
- C25B9/00—Cells or assemblies of cells; Constructional parts of cells; Assemblies of constructional parts, e.g. electrode-diaphragm assemblies; Process-related cell features
- C25B9/17—Cells comprising dimensionally-stable non-movable electrodes; Assemblies of constructional parts thereof
-
- 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
- C02F1/46104—Devices therefor; Their operating or servicing
-
- 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
- C02F1/467—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
- C02F1/4672—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
-
- 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
- C02F1/68—Treatment of water, waste water, or sewage by addition of specified substances, e.g. trace elements, for ameliorating potable water
-
- 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
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/46109—Electrodes
- C02F2001/46133—Electrodes characterised by the material
-
- 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
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/46109—Electrodes
- C02F2001/46133—Electrodes characterised by the material
- C02F2001/46138—Electrodes comprising a substrate and a coating
-
- 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
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/46109—Electrodes
- C02F2001/46152—Electrodes characterised by the shape or form
-
- 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
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/46109—Electrodes
- C02F2001/46152—Electrodes characterised by the shape or form
- C02F2001/46157—Perforated or foraminous electrodes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/46—Apparatus for electrochemical processes
- C02F2201/461—Electrolysis apparatus
- C02F2201/46105—Details relating to the electrolytic devices
- C02F2201/4612—Controlling or monitoring
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/46—Apparatus for electrochemical processes
- C02F2201/461—Electrolysis apparatus
- C02F2201/46105—Details relating to the electrolytic devices
- C02F2201/4612—Controlling or monitoring
- C02F2201/4615—Time
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/02—Temperature
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/44—Time
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/26—Reducing the size of particles, liquid droplets or bubbles, e.g. by crushing, grinding, spraying, creation of microbubbles or nanobubbles
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F7/00—Aeration of stretches of water
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E60/00—Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
- Y02E60/30—Hydrogen technology
- Y02E60/36—Hydrogen production from non-carbon containing sources, e.g. by water electrolysis
-
- Y02E60/366—
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P60/00—Technologies relating to agriculture, livestock or agroalimentary industries
- Y02P60/20—Reduction of greenhouse gas [GHG] emissions in agriculture, e.g. CO2
- Y02P60/21—Dinitrogen oxide [N2O], e.g. using aquaponics, hydroponics or efficiency measures
-
- Y02P60/216—
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
-
- Y02W10/15—
Definitions
- This invention relates to the electrolytic generation of microbubbles of oxygen for increasing the oxygen content of flowing water.
- This invention also relates to the use of superoxygenated water to enhance the growth and yield of plants.
- the flow-through model is useful for oxygenating water for hydroponic plant culture, drip irrigation and waste water treatment.
- Contaminated water is described as having an increased biological oxygen demand (BOD) and water treatment is aimed at decreasing the BOD so as to make more oxygen available for fish and other life forms.
- BOD biological oxygen demand
- U.S. Pat. No. 5,534,143 discloses a microbubble generator that achieves a bubble size of about 0.10 millimeters to about 3 millimeters in diameter.
- U.S. Pat. No. 6,394,429 (“the '429 patent”) discloses a device for producing microbubbles, ranging in size from 0.1 to 100 microns in diameter, by forcing air into the fluid at high pressure through a small orifice.
- oxygenate the water either air, with an oxygen content of about 21%, or pure oxygen may be used.
- oxygen and hydrogen by the electrolysis of water is well known.
- a current is applied across an anode and a cathode which are immersed in an aqueous medium.
- the current may be a direct current from a battery or an AC/DC converter from a line.
- Hydrogen gas is produced at the cathode and oxygen gas is produced at the anode.
- the reactions are:
- the gasses form bubbles which rise to the surface of the fluid and may be collected. Either the oxygen or the hydrogen may be collected for various uses.
- the “electrolytic water” surrounding the anode becomes acidic while the electrolytic water surrounding the cathode becomes basic. Therefore, the electrodes tend to foul or pit and have a limited life in these corrosive environments.
- U.S. Pat. No. 5,982,609 discloses cathodes comprising a metal or metallic oxide of at least one metal selected from the group consisting of ruthenium, iridium, nickel, iron, rhodium, rhenium, cobalt, tungsten, manganese, tantalum, molybdenum, lead, titanium, platinum, palladium and osmium.
- Anodes are formed from the same metallic oxides or metals as cathodes. Electrodes may also be formed from alloys of the above metals or metals and oxides co-deposited on a substrate. The cathode and anodes may be formed on any convenient support in any desired shape or size.
- Holding vessels for live animals generally have a high population of animals which use up the available oxygen rapidly. Pumps to supply oxygen have high power requirements and the noise and bubbling may further stress the animals.
- the available electrolytic generators likewise have high power requirements and additionally run at high voltages and produce acidic and basic water which are detrimental to live animals. Many of the uses of oxygenators, such as keeping bait or caught fish alive, would benefit from portable devices that did not require a source of high power. The need remains for quiet, portable, low voltage means to oxygenate water.
- This invention provides an oxygen emitter which is an electrolytic cell which generates very small microbubbles and nanobubbles of oxygen in an aqueous medium, which bubbles are too small to break the surface tension of the medium, resulting in a medium supersaturated with oxygen.
- the electrodes may be a metal or oxide of at least one metal selected from the group consisting of ruthenium, iridium, nickel, iron, rhodium, rhenium, cobalt, tungsten, manganese, tantalum, molybdenum, lead, titanium, platinum, palladium and osmium or oxides thereof.
- the electrodes may be formed into open grids or may be closed surfaces.
- the most preferred cathode is a stainless steel mesh.
- the most preferred mesh is a 1/16 inch grid.
- the most preferred anode is platinum and iridium oxide on a support.
- a preferred support is titanium.
- the anode and cathode are separated by a critical distance.
- the critical distance ranges from 0.005 inches to 0.140 inches.
- the preferred critical distance is from 0.045 to 0.060 inches.
- Models of different size are provided to be applicable to various volumes of aqueous medium to be oxygenated.
- the public is directed to choose the applicable model based on volume and power requirements of projected use. Those models with low voltage requirements are especially suited to oxygenating water in which animals are to be held.
- Controls are provided to regulate the current and timing of electrolysis.
- a flow-through model is provided which may be connected in-line to a watering hose or to a hydroponic circulating system.
- the flow-through model can be formed into a tube with triangular cross-section.
- the anode is placed toward the outside of the tube and the cathode is placed on the inside, contacting the water flow.
- the anodes and cathodes may be in plates parallel to the long axis of the tube, or may be plates in a wafer stack.
- the electrodes may be placed in a side tube (“T” model) out of the direct flow of water. Protocols are provided to produce superoxygenated water at the desired flow rate and at the desired power usage. Controls are inserted to activate electrolysis when water is flowing and deactivate electrolysis at rest.
- This invention includes a method to promote growth and increase yield of plants by application of superoxygenated water.
- the water treated with the emitter of this invention is one example of superoxygenated water.
- Plants may be grown in hydroponic culture or in soil. The use of the flow-through model for drip irrigation of crops and waste water treatment is disclosed.
- FIG. 1 is the O 2 emitter of the invention.
- FIG. 2 is an assembled device.
- FIG. 3 is a diagram of the electronic controls of the O 2 emitter.
- FIG. 4 shows a funnel or pyramid variation of the O 2 emitter.
- FIG. 5 shows a multilayer sandwich O 2 emitter.
- FIG. 6 shows the yield of tomato plants watered with superoxygenated water.
- FIG. 7 shows an oxygenation chamber suitable for flow-through applications.
- FIG. 7A is a cross section showing arrangement of three plate electrodes.
- FIG. 7B is a longitudinal section showing the points of connection to the power source.
- FIG. 8 is a graph showing the oxygenation of waste water.
- “Critical distance” means the distance separating the anode and cathode at which evolved oxygen forms microbubbles and nanobubbles.
- “Critical distance” means the distance separating the anode and cathode at which evolved oxygen forms microbubbles and nanobubbles.
- O 2 emitter means a cell comprised of at least one anode and at least one cathode separated by the critical distance.
- Metal means a metal or an alloy of one or more metals.
- Microbubble means a bubble with a diameter less than 50 microns.
- Nanobubble means a bubble with a diameter less than that necessary to break the surface tension of water. Nanobubbles remain suspended in the water, giving the water an opalescent or milky appearance.
- “Supersaturated” means oxygen at a higher concentration than normal calculated oxygen solubility at a particular temperature and pressure.
- Superoxygenated water means water with an oxygen content at least 120% of that calculated to be saturated at a temperature.
- Water means any aqueous medium with resistance less than one ohm per square centimeter; that is, a medium that can support the electrolysis of water.
- the lower limit of resistance for a medium that can support electrolysis is water containing more than 2000 ppm total dissolved solids.
- the present invention produces microbubbles and nanobubbles of oxygen via the electrolysis of water.
- molecular oxygen radical atomic weight 8
- O 2 molecular oxygen
- O 2 forms bubbles which are too small to break the surface tension of the fluid. These bubbles remain suspended indefinitely in the fluid and, when allowed to build up, make the fluid opalescent or milky. Only after several hours do the bubbles begin to coalesce on the sides of the container and the water clears. During that time, the water is supersaturated with oxygen. In contrast, the H 2 formed readily coalesces into larger bubbles which are discharged into the atmosphere, as can be seen by bubble formation at the cathode.
- the first objective of this invention was to make an oxygen emitter with low power demands, low voltage and low current for use with live animals. For that reason, a small button emitter was devised.
- the anode and cathode were set at varying distances. It was found that electrolysis took place at very short distances before arcing of the current occurred. Surprisingly, at slightly larger distances, the water became milky and no bubbles formed at the anode, while hydrogen continued to be bubbled off the cathode. At distance of 0.140 inches between the anode and cathode, it was observed that the oxygen formed bubbles at the anode. Therefore, the critical distance for microbubble and nanobubble formation was determined to be between 0.005 inches and 0.140 inches.
- the oxygen evolving anode 1 selected as the most efficient is an iridium oxide coated single sided sheet of platinum on a support of titanium (Eltech, Fairport Harbor, Ohio).
- the cathode 2 is a (fraction ( 1/16) ⁇ inch mesh (size 8 mesh) marine stainless steel screen.
- the anode and cathode are separated by a non-conducting spacer 3 containing a gap 4 for the passage of gas and mixing of anodic and cathodic water and connected to a power source through a connection point 5 .
- FIG. 2 shows a plan view of the assembled device.
- the O 2 emitter 6 with the anode connecting wire 7 and the cathode connecting wire 8 is contained in an enclosure 9 , connected to the battery compartment 10 .
- the spacer thickness is critical as it sets the critical distance. It must be of sufficient thickness to prevent arcing of the current, but thin enough to separate the electrodes by no more than 0.140 inches. Above that thickness, the power needs are higher and the oxygen bubbles formed at higher voltage will coalesce and escape the fluid.
- the spacer is from 0.005 to 0.075 inches thick. At the lower limits, the emitter tends to foul more quickly. Most preferably, the spacer is about 0.050 inches thick.
- the spacer may be any nonconductive material such as nylon, fiberglass, Teflon®, polymer or other plastic. Because of the criticality of the space distance, it is preferable to have a non-compressible spacer. It was found that Buna, with a durometer measure of 60 was not acceptable due to decomposition. Viton, a common fluoroelastomer, has a durometer measure of 90 and was found to hold its shape well.
- FIG. 3 shows a block diagram of a timer control with anode 1 , cathode 2 , thermistor temperature sensor 3 , timer control circuit 4 and wire from a direct current power source 5 .
- the oxygen emitter of this invention may be shaped as a circle, rectangle, cone or other model.
- One or more may be set in a substrate that may be metal, glass, plastic or other material.
- the substrate is not critical as long as the current is isolated to the electrodes by the nonconductor spacer material of a thickness from 0.005 to 0.075 inches, preferably 0.050 inches. It has been noticed that the flow of water seems to be at the periphery of the emitter, while the evolved visible bubbles (H 2 ) arise at the center of the emitter. Therefore, a funnel or pyramidal shaped emitter was constructed to treat larger volumes of fluid.
- FIG. 4 is a cross sectional diagram of such an emitter.
- the anode 1 is formed as an open grid separated from a marine grade stainless steel screen cathode 2 by the critical distance by spacer 3 around the periphery of the emitter and at the apex. This flow-through embodiment is suitable for treating large volumes of water rapidly.
- a round emitter for oxygenating a bait bucket may be about 2 inches in diameter, while a 3-inch diameter emitter is adequate for oxygenating a 10 to 40 gallon tank.
- the live well of a fishing boat will generally hold 40 to 80 gallons of water and require a 4-inch diameter emitter. It is within the scope of this invention to construct larger emitters or to use several in a series to oxygenate larger volumes. It is also within the scope of this invention to vary the model to provide for low voltage and amperage in cases where the need for oxygen is moderate and long lasting or conversely, to supersaturate water very quickly at higher voltage and amperage.
- FIG. 5 An O 2 emitter was made in a multilayer sandwich embodiment.
- An iridium oxide coated platinum anode 1 was formed into a grid to allow good water flow and sandwiched between two stainless steel screen cathodes 2 . Spacing was held at the critical distance by nylon spacers 3 .
- the embodiment illustrated is held in a cassette 4 which is secured by nylon bolt 5 with a nylon washer 6 .
- the dimensions selected were:
- an embodiment may easily be constructed with this sequence: cathode, spacer, anode, spacer, cathode, spacer, anode, spacer, cathode, spacer, anode, spacer, cathode, spacer, anode, spacer, cathode.
- the number of layers in the sandwich is limited only by the power requirements acceptable for an application.
- Circulation protocols were identical except that the 2 1 ⁇ 2 gallon water reservoir for the Control plant was eroated with and aquarium bubbler and that for the Test plant was oxygenated with a five-inch strip emitter for two minutes prior to pumping. The cycle was set at four minutes of pumping, followed by four minutes of rest.
- the control water had an oxygen content of about 97% to 103% saturation, that is, it was saturated with oxygen.
- the test water had an oxygen content of about 153% to 165% saturation, that is, it was supersaturated.
- the test plant was at least four times the volume of the control plant and began to show what looked like fertilizer burn.
- Tomato seeds (Burpee “Big Boy”) were planted in one-inch diameter peat and dirt plugs encased in cheese cloth and placed in a tray in a southwest window. Controls were watered once a day with tap water (“Control”) or oxygenated water (“Test”). Both Controls and Test sprouted at one week. After five weeks, the Test plants were an average of 11 inches tall while the Controls were an average of nine inches tall. At this time, May 10, when the threat of frost in Minnesota was minimal, the plants were transplanted to 13 inch diameter pots with drainage holes. Four inches of top soil was added to each pot, topped off with four inches of Scott's Potting Soil. The pots were placed outside in a sunny area with at least eight hours a day of full sun.
- the plants were watered as needed with either plain tap water (Control) or oxygenated water (Test).
- the oxygenated water was produced by use of the emitter of Example 1 run for one-half hour in a five-gallon container of water. Previous experiments showed that water thus treated had an oxygen content from 160% to 260% saturation.
- the Test plants flowered on June 4, while the Controls did not flower until June 18.
- every plant in the group first had flowers on the same day. All plants were fertilized on July 2 and a soaker hose provided because the plants were now so big that watering by hand was difficult.
- the soaker hose was run for one half to one hour each morning, depending on the weather, to a point at which the soil was saturated with water. One half hour after the soaker hose was turned off, about 750 ml of superoxygenated water was applied to each of the Test plants.
- the Test plants were bushier than the Controls although the heights were similar. At this time, there were eight Control plants and seven Test plants because one of the Test plants broke in a storm. On July 2, the control plants averaged about 17 primary branches from the vine stem, while the control plants averaged about 13 primary branches from the vine stem. As the tomatoes matured, each was weighed on a kitchen scale at harvest. The yield history is shown in Table II.
- the total yield for the eight Control plants was 15620 grams or 1952 grams of tomatoes per plant.
- the total yield for the seven Test plants was 24385 grams or 3484 grams of tomatoes per plant, an increase in yield of about 79% over the Control plants.
- FIG. 6 shows the cumulative total as plotted against time. Not only did the Test plants blossom and bear fruit earlier, but that the Control plants never caught up to the test plants in the short Minnesota growing season. It should be noted that the experiment was terminated because of predicted frost. All fruits, both green and red, were harvested and weighed at that point.
- the oxygenation chamber is comprised of three anodes 1 and cathodes 2 , of appropriate size to fit inside a tube or hose and separated by the critical distance are placed within a tube or hose 3 at 120° angles to each other.
- the anodes and cathodes are positioned with stabilizing hardware 4 .
- the stabilizing hardware which can be any configuration such as a screw, rod or washer, is preferably formed from stainless steel.
- FIG. 7(B) shows a plan view of the oxygenation chamber with stabilizing hardware 4 serving as a connector to the power source and stabilizing hardware 5 serving as a connector to the power source.
- the active area is shown at 6 .
- This invention is not limited to the design selected for this embodiment.
- Those skilled in the art can readily fabricate any of the emitters shown in FIG. 4 or 5 , or can design other embodiments that will oxygenate flowing water.
- One useful embodiment is the “T” model, wherein the emitter unit is set in a side arm. The emitted bubbles are swept into the water flow. The unit is detachable for easy servicing.
- Table III shows several models of flow through emitters. The voltage and flowrates were held constant and the current varied. The Dissolved oxygen (DO) from the source was 7.1 mg/liter. The starting temperature was 12.2° C. but the flowing water cooled slightly to 11 or 11.5° C. Without undue experimentation, anyone may easily select the embodiment that best suits desired characteristics from Table III or designed with the teachings of Table III.
- Drip irrigation is a technique wherein water is pumped through a pipe or hose with perforations at the site of each plant to be irrigated.
- the conduit may be underground or above ground. Since the water is applied directly to the plant rather than wetting the entire field, this technique is especially useful in arid climates or for plants requiring high fertilizer applications.
- the superoxygenated water will be applied by drip irrigation per the usual protocol for the respective plants. Growth and yield will be compared to the same plants given only the usual irrigation water. Pest control and fertilization will be the same between test and control plants, except that the operators of the experiments will be cautioned to be aware of the possibility of fertilizer burn in the test plants and to adjust their protocols accordingly.
- Waste water with a high organic content, has a high BOD, due to the bacterial flora. It is desirable to raise the oxygen content of the waste water in order to cause the flora to flocculate. However, it is very difficult to effectively oxygenate such water.
Landscapes
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Electrochemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Environmental Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Metallurgy (AREA)
- Materials Engineering (AREA)
- Biodiversity & Conservation Biology (AREA)
- General Chemical & Material Sciences (AREA)
- Marine Sciences & Fisheries (AREA)
- Animal Husbandry (AREA)
- Microbiology (AREA)
- Inorganic Chemistry (AREA)
- Automation & Control Theory (AREA)
- Electrolytic Production Of Non-Metals, Compounds, Apparatuses Therefor (AREA)
Abstract
An oxygen emitter which is an electrolytic cell is disclosed. When the anode and cathode are separated by a critical distance, very small microbubbles and nanobubbles of oxygen are generated. The very small oxygen bubbles remain in suspension, forming a solution supersaturated in oxygen. A flow-through model for oxygenating flowing water is disclosed. The use of supersaturated water for enhancing the growth of plants is disclosed. Methods for applying supersaturated water to plants manually, by drip irrigation or in hydroponic culture are described. The treatment of waste water by raising the dissolved oxygen with the use of an oxygen emitter is disclosed.
Description
More than one reissue application has been filed for the reissue of U.S. Pat. No. 7,670,495. This application is a continuation reissue application of application Ser. No. 14/601,340, filed Jan. 21, 2015, which is a continuation reissue application of application Ser. No. 13/247,241, filed Sep. 28, 2011, now U.S. Pat. No. RE45,415, which is a reissue of U.S. Pat. No. 7,670,495. U.S. Pat. No. 6,760,495 is a division of application Ser. No. 10/732,326 filed Dec. 10, 2003, which in turn is a continuation-in-part of application Ser. No. 10/372,017, filed Feb. 21, 2003, now U.S. Pat. No. 6,689,262, which claims the benefit of U.S. Provisional Application No. 60/358,534, filed Feb. 22, 2002, each of which is hereby fully incorporated herein by reference.
This invention relates to the electrolytic generation of microbubbles of oxygen for increasing the oxygen content of flowing water. This invention also relates to the use of superoxygenated water to enhance the growth and yield of plants. The flow-through model is useful for oxygenating water for hydroponic plant culture, drip irrigation and waste water treatment.
Many benefits may be obtained through raising the oxygen content of aqueous media. Efforts have been made to achieve higher saturated or supersaturated oxygen levels for applications such as the improvement of water quality in ponds, lakes, marshes and reservoirs, the detoxification of contaminated water, culture of fish, shrimp and other aquatic animals, biological culture and hydroponic culture. For example, fish held in a limited environment such as an aquarium, a bait bucket or a live hold tank may quickly use up the dissolved oxygen in the course of normal respiration and are then subject to hypoxic stress, which can lead to death. A similar effect is seen in cell cultures, where the respiring cells would benefit from higher oxygen content of the medium. Organic pollutants from agricultural, municipal and industrial facilities spread through the ground and surface water and adversely affect life forms. Many pollutants are toxic, carcinogenic or mutagenic. Decomposition of these pollutants is facilitated by oxygen, both by direct chemical detoxifying reactions or by stimulating the growth of detoxifying microflora. Contaminated water is described as having an increased biological oxygen demand (BOD) and water treatment is aimed at decreasing the BOD so as to make more oxygen available for fish and other life forms.
The most common method of increasing the oxygen content of a medium is by sparging with air or oxygen. While this is a simple method, the resulting large bubbles produced simply break the surface and are discharged into the atmosphere. Attempts have been made to reduce the size of the bubbles in order to facilitate oxygen transfer by increasing the total surface area of the oxygen bubbles. U.S. Pat. No. 5,534,143 discloses a microbubble generator that achieves a bubble size of about 0.10 millimeters to about 3 millimeters in diameter. U.S. Pat. No. 6,394,429 (“the '429 patent”) discloses a device for producing microbubbles, ranging in size from 0.1 to 100 microns in diameter, by forcing air into the fluid at high pressure through a small orifice.
When the object of generating bubbles is to oxygenate the water, either air, with an oxygen content of about 21%, or pure oxygen may be used. The production of oxygen and hydrogen by the electrolysis of water is well known. A current is applied across an anode and a cathode which are immersed in an aqueous medium. The current may be a direct current from a battery or an AC/DC converter from a line. Hydrogen gas is produced at the cathode and oxygen gas is produced at the anode. The reactions are:
| AT THE CATHODE: | 4H2O + 4e− → 4OH− + 2H2 | |
| AT THE ANODE: | 2H2O → O2 + 4H+ + 4e− | |
| NET REACTION: | 6H2O → 4OH− + 4H+ ++ 2H2 + O2 | |
286 kilojoules of energy is required to generate one mole of oxygen.
The gasses form bubbles which rise to the surface of the fluid and may be collected. Either the oxygen or the hydrogen may be collected for various uses. The “electrolytic water” surrounding the anode becomes acidic while the electrolytic water surrounding the cathode becomes basic. Therefore, the electrodes tend to foul or pit and have a limited life in these corrosive environments.
Many cathodes and anodes are commercially available. U.S. Pat. No. 5,982,609 discloses cathodes comprising a metal or metallic oxide of at least one metal selected from the group consisting of ruthenium, iridium, nickel, iron, rhodium, rhenium, cobalt, tungsten, manganese, tantalum, molybdenum, lead, titanium, platinum, palladium and osmium. Anodes are formed from the same metallic oxides or metals as cathodes. Electrodes may also be formed from alloys of the above metals or metals and oxides co-deposited on a substrate. The cathode and anodes may be formed on any convenient support in any desired shape or size. It is possible to use the same materials or different materials for both electrodes. The choice is determined according to the uses. Platinum and iron alloys (“stainless steel”) are often preferred materials due to their inherent resistance to the corrosive electrolytic water. An especially preferred anode disclosed in U.S. Pat. No. 4,252,856 comprises vacuum deposited iridium oxide.
Holding vessels for live animals generally have a high population of animals which use up the available oxygen rapidly. Pumps to supply oxygen have high power requirements and the noise and bubbling may further stress the animals. The available electrolytic generators likewise have high power requirements and additionally run at high voltages and produce acidic and basic water which are detrimental to live animals. Many of the uses of oxygenators, such as keeping bait or caught fish alive, would benefit from portable devices that did not require a source of high power. The need remains for quiet, portable, low voltage means to oxygenate water.
It has also been known that plant roots are healthier when oxygenated water is applied. It is thought that oxygen inhibits the growth of deleterious fungi. The water sparged with air as in the '429 patent was shown to increase the biomass of hydroponically grown cucumbers and tomatoes by about 15%.
The need remains for oxygenator models suitable to be placed in-line in water distribution devices so as to be applied to field as well as hydroponic culture.
This invention provides an oxygen emitter which is an electrolytic cell which generates very small microbubbles and nanobubbles of oxygen in an aqueous medium, which bubbles are too small to break the surface tension of the medium, resulting in a medium supersaturated with oxygen.
The electrodes may be a metal or oxide of at least one metal selected from the group consisting of ruthenium, iridium, nickel, iron, rhodium, rhenium, cobalt, tungsten, manganese, tantalum, molybdenum, lead, titanium, platinum, palladium and osmium or oxides thereof. The electrodes may be formed into open grids or may be closed surfaces. The most preferred cathode is a stainless steel mesh. The most preferred mesh is a 1/16 inch grid. The most preferred anode is platinum and iridium oxide on a support. A preferred support is titanium.
In order to form microbubbles and nanobubbles, the anode and cathode are separated by a critical distance. The critical distance ranges from 0.005 inches to 0.140 inches. The preferred critical distance is from 0.045 to 0.060 inches.
Models of different size are provided to be applicable to various volumes of aqueous medium to be oxygenated. The public is directed to choose the applicable model based on volume and power requirements of projected use. Those models with low voltage requirements are especially suited to oxygenating water in which animals are to be held.
Controls are provided to regulate the current and timing of electrolysis.
A flow-through model is provided which may be connected in-line to a watering hose or to a hydroponic circulating system. The flow-through model can be formed into a tube with triangular cross-section. In this model, the anode is placed toward the outside of the tube and the cathode is placed on the inside, contacting the water flow. Alternatively, the anodes and cathodes may be in plates parallel to the long axis of the tube, or may be plates in a wafer stack. Alternately, the electrodes may be placed in a side tube (“T” model) out of the direct flow of water. Protocols are provided to produce superoxygenated water at the desired flow rate and at the desired power usage. Controls are inserted to activate electrolysis when water is flowing and deactivate electrolysis at rest.
This invention includes a method to promote growth and increase yield of plants by application of superoxygenated water. The water treated with the emitter of this invention is one example of superoxygenated water. Plants may be grown in hydroponic culture or in soil. The use of the flow-through model for drip irrigation of crops and waste water treatment is disclosed.
For the purpose of describing the present invention, the following terms have these meanings:
“Critical distance” means the distance separating the anode and cathode at which evolved oxygen forms microbubbles and nanobubbles.
“Critical distance” means the distance separating the anode and cathode at which evolved oxygen forms microbubbles and nanobubbles.
“O2 emitter” means a cell comprised of at least one anode and at least one cathode separated by the critical distance.
“Metal” means a metal or an alloy of one or more metals.
“Microbubble” means a bubble with a diameter less than 50 microns.
“Nanobubble” means a bubble with a diameter less than that necessary to break the surface tension of water. Nanobubbles remain suspended in the water, giving the water an opalescent or milky appearance.
“Supersaturated” means oxygen at a higher concentration than normal calculated oxygen solubility at a particular temperature and pressure.
“Superoxygenated water” means water with an oxygen content at least 120% of that calculated to be saturated at a temperature.
“Water” means any aqueous medium with resistance less than one ohm per square centimeter; that is, a medium that can support the electrolysis of water. In general, the lower limit of resistance for a medium that can support electrolysis is water containing more than 2000 ppm total dissolved solids.
The present invention produces microbubbles and nanobubbles of oxygen via the electrolysis of water. As molecular oxygen radical (atomic weight 8) is produced, it reacts to form molecular oxygen, O2. In the special dimensions of the invention, as explained in more detail in the following examples, O2 forms bubbles which are too small to break the surface tension of the fluid. These bubbles remain suspended indefinitely in the fluid and, when allowed to build up, make the fluid opalescent or milky. Only after several hours do the bubbles begin to coalesce on the sides of the container and the water clears. During that time, the water is supersaturated with oxygen. In contrast, the H2 formed readily coalesces into larger bubbles which are discharged into the atmosphere, as can be seen by bubble formation at the cathode.
The first objective of this invention was to make an oxygen emitter with low power demands, low voltage and low current for use with live animals. For that reason, a small button emitter was devised. The anode and cathode were set at varying distances. It was found that electrolysis took place at very short distances before arcing of the current occurred. Surprisingly, at slightly larger distances, the water became milky and no bubbles formed at the anode, while hydrogen continued to be bubbled off the cathode. At distance of 0.140 inches between the anode and cathode, it was observed that the oxygen formed bubbles at the anode. Therefore, the critical distance for microbubble and nanobubble formation was determined to be between 0.005 inches and 0.140 inches.
As shown in FIG. 1 , the oxygen evolving anode 1 selected as the most efficient is an iridium oxide coated single sided sheet of platinum on a support of titanium (Eltech, Fairport Harbor, Ohio). The cathode 2 is a (fraction ( 1/16)} inch mesh (size 8 mesh) marine stainless steel screen. The anode and cathode are separated by a non-conducting spacer 3 containing a gap 4 for the passage of gas and mixing of anodic and cathodic water and connected to a power source through a connection point 5. FIG. 2 shows a plan view of the assembled device. The O2 emitter 6 with the anode connecting wire 7 and the cathode connecting wire 8 is contained in an enclosure 9, connected to the battery compartment 10. The spacer thickness is critical as it sets the critical distance. It must be of sufficient thickness to prevent arcing of the current, but thin enough to separate the electrodes by no more than 0.140 inches. Above that thickness, the power needs are higher and the oxygen bubbles formed at higher voltage will coalesce and escape the fluid. Preferably, the spacer is from 0.005 to 0.075 inches thick. At the lower limits, the emitter tends to foul more quickly. Most preferably, the spacer is about 0.050 inches thick. The spacer may be any nonconductive material such as nylon, fiberglass, Teflon®, polymer or other plastic. Because of the criticality of the space distance, it is preferable to have a non-compressible spacer. It was found that Buna, with a durometer measure of 60 was not acceptable due to decomposition. Viton, a common fluoroelastomer, has a durometer measure of 90 and was found to hold its shape well.
In operation, a small device with an O2 emitter 1.485 inches in diameter was driven by 4AA batteries. The critical distance was held at 0.050 inches with a Viton spacer. Five gallons of water became saturated in seven minutes. This size is suitable for raising oxygen levels in an aquarium or bait bucket.
It is convenient to attach a control circuit which comprises a timer that is thermostatically controlled by a temperature sensor which determines the off time for the cathode. When the temperature of the solution changes, the resistance of the thermistor changes, which causes an off time of a certain duration. In cool water, the duration is longer so in a given volume, the emitter generates less oxygen. When the water is warmer and therefore hold less oxygen, the duration of off time is shorter. Thus the device is self-controlled to use power most economically. FIG. 3 shows a block diagram of a timer control with anode 1, cathode 2, thermistor temperature sensor 3, timer control circuit 4 and wire from a direct current power source 5.
Attempts were made to measure the diameter of the O2 bubbles emitted by the device of Example 1. In the case of particles other than gasses, measurements can easily be made by scanning electron microscopy, but gasses do not survive electron microscopy. Large bubble may be measured by pore exclusion, for example, which is also not feasible when measuring a gas bubble. A black and white digital, high contrast, backlit photograph of treated water with a millimeter scale reference was shot of water produced by the emitter of Example 1. About 125 bubbles were seen in the area selected for measurement. Seven bubbles ranging from the smallest clearly seen to the largest were measured. The area was enlarged, giving a scale multiplier of 0.029412.
Recorded bubble diameters at scale were 0.16, 0.22, 0.35, 0.51, 0.76, 0.88 and 1.09 millimeters. The last three were considered outliers by reverse analysis of variance and were assumed to be hydrogen bubbles. When multiplied by the scale multiplier, the assumed O2 bubbles were found to range from 4.7 to 15 microns in diameter. This test was limited by the resolution of the camera and smaller bubbles in the nanometer range could not be resolved. It is known that white light cannot resolve features in the nanometer size range, so monochromatic laser light may give resolution sensitive enough to measure smaller bubbles. Efforts continue to increase the sensitivity of measurement so that sub-micron diameter bubbles can be measured.
Depending on the volume of fluid to be oxygenated, the oxygen emitter of this invention may be shaped as a circle, rectangle, cone or other model. One or more may be set in a substrate that may be metal, glass, plastic or other material. The substrate is not critical as long as the current is isolated to the electrodes by the nonconductor spacer material of a thickness from 0.005 to 0.075 inches, preferably 0.050 inches. It has been noticed that the flow of water seems to be at the periphery of the emitter, while the evolved visible bubbles (H2) arise at the center of the emitter. Therefore, a funnel or pyramidal shaped emitter was constructed to treat larger volumes of fluid. FIG. 4 is a cross sectional diagram of such an emitter. The anode 1 is formed as an open grid separated from a marine grade stainless steel screen cathode 2 by the critical distance by spacer 3 around the periphery of the emitter and at the apex. This flow-through embodiment is suitable for treating large volumes of water rapidly.
The size may be varied as required. A round emitter for oxygenating a bait bucket may be about 2 inches in diameter, while a 3-inch diameter emitter is adequate for oxygenating a 10 to 40 gallon tank. The live well of a fishing boat will generally hold 40 to 80 gallons of water and require a 4-inch diameter emitter. It is within the scope of this invention to construct larger emitters or to use several in a series to oxygenate larger volumes. It is also within the scope of this invention to vary the model to provide for low voltage and amperage in cases where the need for oxygen is moderate and long lasting or conversely, to supersaturate water very quickly at higher voltage and amperage. In the special dimensions of the present invention, it has been found that a 6 volt battery supplying a current as low as 40 milliamperes is sufficient to generate oxygen. Such a model is especially useful with live plants or animals, while it is more convenient for industrial use to use a higher voltage and current. Table I shows a number of models suitable to various uses.
| TABLE I | |||||
| Emitter Model | Gallons | Volts | Amps Max. | Ave | |
| Bait keeper |
| 5 | 6 | 0.090 | 0.060 | 0.36 | |
| Livewell | 32 | 12 | 0.180 | 0.120 | 1.44 |
| |
10 | 12 | 0.210 | 0.120 | 1.44 |
| Bait store | 70 | 12 | 0.180 | 0.180 | 2.16 |
| |
2 | 12 | 0.180 | 0.180 | 2.16 |
| |
50 | 12 | 0.500 | 0.265 | 3.48 |
| |
80 | 12 | 0.980 | 0.410 | 4.92 |
| |
2 | 24 | 1.200 | 1.200 | 28.80 |
| Plate | 250 | 12 | 5.000 | 2.500 | 30.00 |
An O2 emitter was made in a multilayer sandwich embodiment. (FIG. 5 ) An iridium oxide coated platinum anode 1 was formed into a grid to allow good water flow and sandwiched between two stainless steel screen cathodes 2. Spacing was held at the critical distance by nylon spacers 3. The embodiment illustrated is held in a cassette 4 which is secured by nylon bolt 5 with a nylon washer 6. The dimensions selected were:
| cathode screen | 0.045 inches thick | |
| nylon spacer | 0.053 inches thick | |
| anode grid | 0.035 inches thick | |
| nylon spacer | 0.053 inches thick | |
| cathode screen | 0.045 inches thick, | |
for an overall emitter thickness of 0.231 inches thick inches.
If a more powerful emitter is desired, it is within the scope of this invention to repeat the sequence of stacking. For example, an embodiment may easily be constructed with this sequence: cathode, spacer, anode, spacer, cathode, spacer, anode, spacer, cathode, spacer, anode, spacer, cathode. The number of layers in the sandwich is limited only by the power requirements acceptable for an application.
It is known that oxygen is important for the growth of plants. Although plants evolve oxygen during photosynthesis, they also have a requirement for oxygen for respiration. Oxygen is evolved in the leaves of the plants, while often the roots are in a hypoxic environment without enough oxygen to support optimum respiration, which can be reflected in less than optimum growth and nutrient utilization. Hydroponically grown plants are particularly susceptible to oxygen deficit in the root system. U.S. Pat. No. 5,887,383 describes a liquid supply pump unit for hydroponic cultures which attain oxygen enrichment by sparging with air. Such a method has high energy requirements and is noisy. Furthermore, while suitable for self-contained hydroponic culture, the apparatus is not usable for field irrigation. In a report available on the web, it was shown that hydroponically grown cucumbers and tomatoes supplied with water oxygenated with a device similar to that described in the '429 patent had increased biomass of about 12% and 17% respectively. It should be noted that when sparged with air, the water may become saturated with oxygen, but it is unlikely that the water is superoxygenated.
A. Superoxygenated Water in Hydroponic Culture.
Two small hydroponic systems were set up to grow two tomato plants. Circulation protocols were identical except that the 2 ½ gallon water reservoir for the Control plant was eroated with and aquarium bubbler and that for the Test plant was oxygenated with a five-inch strip emitter for two minutes prior to pumping. The cycle was set at four minutes of pumping, followed by four minutes of rest. The control water had an oxygen content of about 97% to 103% saturation, that is, it was saturated with oxygen. The test water had an oxygen content of about 153% to 165% saturation, that is, it was supersaturated. The test plant was at least four times the volume of the control plant and began to show what looked like fertilizer burn. At that point the fertilizer for the Test plant was reduced by half Since the plants were not exposed to natural light but to continuous artificial light in an indoor environment without the natural means of fertilization (wind and/or insects), the experiment was discontinued after three months. At that time, the Test plant but not the Control plant had blossomed.
B. Superoxygenated Water in Field Culture.
A pilot study was designed to ascertain that plants outside the hydroponic culture facility would benefit from the application of oxygen. It was decided to use water treated with the emitter of Example 1 as the oxygen carrier. Since water so treated is supersaturated, it is an excellent carrier of oxygen.
Tomato seeds (Burpee “Big Boy”) were planted in one-inch diameter peat and dirt plugs encased in cheese cloth and placed in a tray in a southwest window. Controls were watered once a day with tap water (“Control”) or oxygenated water (“Test”). Both Controls and Test sprouted at one week. After five weeks, the Test plants were an average of 11 inches tall while the Controls were an average of nine inches tall. At this time, May 10, when the threat of frost in Minnesota was minimal, the plants were transplanted to 13 inch diameter pots with drainage holes. Four inches of top soil was added to each pot, topped off with four inches of Scott's Potting Soil. The pots were placed outside in a sunny area with at least eight hours a day of full sun. The plants were watered as needed with either plain tap water (Control) or oxygenated water (Test). The oxygenated water was produced by use of the emitter of Example 1 run for one-half hour in a five-gallon container of water. Previous experiments showed that water thus treated had an oxygen content from 160% to 260% saturation. The Test plants flowered on June 4, while the Controls did not flower until June 18. For both groups, every plant in the group first had flowers on the same day. All plants were fertilized on July 2 and a soaker hose provided because the plants were now so big that watering by hand was difficult. The soaker hose was run for one half to one hour each morning, depending on the weather, to a point at which the soil was saturated with water. One half hour after the soaker hose was turned off, about 750 ml of superoxygenated water was applied to each of the Test plants.
The Test plants were bushier than the Controls although the heights were similar. At this time, there were eight Control plants and seven Test plants because one of the Test plants broke in a storm. On July 2, the control plants averaged about 17 primary branches from the vine stem, while the control plants averaged about 13 primary branches from the vine stem. As the tomatoes matured, each was weighed on a kitchen scale at harvest. The yield history is shown in Table II.
| TABLE II | ||
| Control, grams | Test, grams | |
| tomatoes from | tomatoes from | |
| eight plants/ | seven plants/ | |
| Week of: | cumulative total | cumulative total |
| July 27 | 240 | 400 | ||
| August 3 | 180 | 420 | 2910 | 3310 |
| August 10 | 905 | 1325 | 1830 | 5140 |
| August 17 | 410 | 1735 | 2590 | 7730 |
| August 24 | 3300 | 5035 | 2470 | 10200 |
| August 31 | 4150 | 9175 | 1580 | 11780 |
| September 15 | not weighed | 3710 | 15490 | |
| Final Harvest | 6435 | 15620 | 8895 | 24385 |
| September 24 | ||||
The total yield for the eight Control plants was 15620 grams or 1952 grams of tomatoes per plant.
The total yield for the seven Test plants was 24385 grams or 3484 grams of tomatoes per plant, an increase in yield of about 79% over the Control plants.
In order to apply the findings of example 5 to agricultural uses, an emitter than can oxygenate running water efficiently was developed. In FIG. 7(A) , the oxygenation chamber is comprised of three anodes 1 and cathodes 2, of appropriate size to fit inside a tube or hose and separated by the critical distance are placed within a tube or hose 3 at 120° angles to each other. The anodes and cathodes are positioned with stabilizing hardware 4. The stabilizing hardware, which can be any configuration such as a screw, rod or washer, is preferably formed from stainless steel. FIG. 7(B) shows a plan view of the oxygenation chamber with stabilizing hardware 4 serving as a connector to the power source and stabilizing hardware 5 serving as a connector to the power source. The active area is shown at 6.
This invention is not limited to the design selected for this embodiment. Those skilled in the art can readily fabricate any of the emitters shown in FIG. 4 or 5 , or can design other embodiments that will oxygenate flowing water. One useful embodiment is the “T” model, wherein the emitter unit is set in a side arm. The emitted bubbles are swept into the water flow. The unit is detachable for easy servicing. Table III shows several models of flow through emitters. The voltage and flowrates were held constant and the current varied. The Dissolved oxygen (DO) from the source was 7.1 mg/liter. The starting temperature was 12.2° C. but the flowing water cooled slightly to 11 or 11.5° C. Without undue experimentation, anyone may easily select the embodiment that best suits desired characteristics from Table III or designed with the teachings of Table III.
| TABLE III | |||||
| ACTIVE | DO OF* | ||||
| ELECTRODE | CURRENT, | FLOW RATE | SAMPLE AT | ||
| MODEL | AREA, SQ.IN. | VOLTAGE | AMPS. | GAL/MINUTE | ONE MINUTE |
| 2-Inch “T” | 2 | 28.3 | 0.72 | 12 | N/A |
| 3-inch “T” | 3 | 28.3 | 1.75 | 12 | N/A |
| 2-plate Tube | 20 | 28.3 | 9.1 | 12 | 8.4 |
| 3-Plate tube | 30 | 28.3 | 12.8 | 12 | 9.6 |
| *As the apparatus runs longer, the flowing water becomes milky, indicating supersaturation. The one-minute time point shows the rapid increase in oxygenation. | |||||
The following plants will be tested for response to superoxygenated water: grape vines, lettuce, and radishes in three different climate zones. The operators for these facilities will be supplied with units for drip irrigation. Drip irrigation is a technique wherein water is pumped through a pipe or hose with perforations at the site of each plant to be irrigated. The conduit may be underground or above ground. Since the water is applied directly to the plant rather than wetting the entire field, this technique is especially useful in arid climates or for plants requiring high fertilizer applications.
The superoxygenated water will be applied by drip irrigation per the usual protocol for the respective plants. Growth and yield will be compared to the same plants given only the usual irrigation water. Pest control and fertilization will be the same between test and control plants, except that the operators of the experiments will be cautioned to be aware of the possibility of fertilizer burn in the test plants and to adjust their protocols accordingly.
It is expected that the superoxygenated plants with drip irrigation will show more improved performance with more continuous application of oxygen than did the tomato plants of Example 5, which were given superoxygenated water only once a day.
Waste water, with a high organic content, has a high BOD, due to the bacterial flora. It is desirable to raise the oxygen content of the waste water in order to cause the flora to flocculate. However, it is very difficult to effectively oxygenate such water. Using a 4 inch OEM (see Table I) with a 12 volt battery, four liters of waste water in a five gallon pail were oxygenated. As shown in FIG. 8 , the dissolved oxygen went from 0.5 mg/l to 10.8 mg/l in nine minutes.
Those skilled in the art will readily comprehend that variations, modifications and additions may in the embodiments described herein may be made. Therefore, such variations, modifications and additions are within the scope of the appended claims.
Claims (84)
1. A method for treating waste water comprising;
providing a flow-through oxygenator comprising an emitter for electrolytic generation of microbubbles of oxygen comprising an anode separated at a critical distance from a cathode and a power source all in electrical communication with each other,
placing the emitter within a conduit; and
passing waste water through the conduit.
2. An emitter for electrolytic generation of microbubbles of oxygen in an aqueous medium comprising: an anode separated at a critical distance from a cathode, a nonconductive spacer maintaining the separation of the anode and cathode, the nonconductive spacer having a spacer thickness between 0.005 to 0.050 inches such that the critical distance is less than 0.060 inches and a power source all in electrical communication with each other, wherein the critical distance results in the formation of oxygen bubbles having a bubble diameter less than 0.0006 inches, said oxygen bubbles being incapable of breaking the surface tension of the aqueous medium such that said aqueous medium is supersaturated with oxygen.
3. The emitter of claim 2 , wherein the anode is a metal or a metallic oxide or a combination of a metal and a metallic oxide.
4. The emitter of claim 2 , wherein the anode is platinum and iridium oxide on a support.
5. The emitter of claim 2 , wherein the cathode is a metal or metallic oxide or a combination of a metal and a metallic oxide.
6. The emitter of claim 2 , wherein the critical distance is 0.005 to 0.060 inches.
7. The emitter of claim 2 , comprising a plurality of anodes separated at the critical distance from a plurality of cathodes.
8. A method for oxygenating a non-native habitat for temporarily keeping aquatic animals, comprising:
inserting the emitter of claim 2 into the aqueous medium, the non-native habitat comprising an aquarium, a bait bucket or a live well.
9. A method for lowering the biologic oxygen demand of polluted water comprising:
passing the polluted water through a vessel containing the emitter of claim 2 .
10. A supersaturated aqueous product formed with the emitter of claim 2 , the supersaturated aqueous product having an approximately neutral pH.
11. The emitter of claim 2 , further comprising a timer control.
12. The emitter of claim 2 , wherein the anode and cathode are arranged such that the emitter assumes a funnel or pyramidal shaped emitter.
13. A method for treating water comprising:
providing a flow-through oxygenator comprising an emitter for electrolytic generation of bubbles of oxygen, the emitter including:
a tubular housing having a water inlet, a water outlet, and a longitudinal water flow axis from the inlet to the outlet;
at least two electrodes comprising a first electrode and a second electrode, the first and second electrodes being positioned in the tubular housing, the first electrode opposing and separated from the second electrode by a distance of between 0.005 inches to 0.140 inches within the tubular housing;
each electrode of the emitter is positioned so that substantially all points midway between all opposing electrodes are closer to a surface of the tubular housing than to a center point within the tubular housing and so that at least some water may flow from the water inlet to the water outlet without passing through a space between electrodes of opposite polarity separated by a distance of between 0.005 inches to 0.140 inches;
a power source in electrical communication with the electrodes, the power source configured to deliver a voltage to the electrodes, the voltage being less than or equal to 28.3 volts, the power source being configured to deliver a current to the electrodes, the current being less than or equal to 12.8 amps;
passing water through the tubular housing while electrical current is applied to the electrodes producing oxygen in said water via electrolysis.
14. The method of claim 13 wherein the tubular housing includes an inward-facing surface that runs parallel to the longitudinal axis;
wherein the first and second electrodes extend in a direction that is parallel to the longitudinal axis.
15. The method of claim 13 wherein the tubular housing includes an inward-facing surface that runs parallel to the longitudinal axis;
wherein the first and second electrodes extend in a direction parallel to the longitudinal axis; and
wherein each electrode of the emitter is positioned closer to the inward-facing surface than to the longitudinal axis at the center of the tubular housing.
16. The method of claim 13 wherein at least one of the electrodes is a stainless steel mesh or screen.
17. The method of claim 13 wherein the first and second electrodes are positioned away from a longitudinal center axis of the tubular housing and maintain an unobstructed passageway parallel to the center axis, the passageway running longitudinally for at least the length of the first and second electrodes positioned within the tubular housing.
18. The method of claim 17 wherein the unobstructed passageway includes the center axis and is multiple times wider than the distance separating the opposing first and second electrodes within the tubular housing.
19. The method of claim 17 wherein the first and second electrodes comprise an outside electrode and an inside electrode,
wherein the first and second electrodes extend in a longitudinal direction parallel to the longitudinal axis and an inward-facing surface of the tubular housing, the outside and inside electrodes being outside and inside electrodes respectively in that the first and second electrodes are positioned relative to each other so that the outside electrode is closer to an outer wall of the chamber than the inside electrode is and so that the inside electrode is closer to the longitudinal axis at the center of the tubular housing than the outside electrode is,
wherein the outside electrode defines a cross-sectional area between the outside electrode and the inward facing surface of the tubular housing that is substantially less than a cross-sectional area of the unobstructed passageway.
20. The method of claim 13 wherein the first and second electrodes are positioned away from a longitudinal center axis of the tubular housing and maintain an unobstructed passageway parallel to and including the center axis, the passageway running for at least the length of the first and second electrodes positioned within the housing;
wherein the first and second electrodes comprise an outside electrode and an inside electrode;
wherein the first and second electrodes extend in a longitudinal direction parallel to the longitudinal axis and an inward-facing surface of the tubular housing;
the outside and inside electrodes being outside and inside electrodes respectively in that the first and second electrodes are positioned relative to each other so that the outside electrode is closer to an outer wall of the chamber than the inside electrode is and so that the inside electrode is closer to the longitudinal axis at the center of the tubular housing than the outside electrode is;
wherein the outside electrode defines a cross-sectional area between the outside electrode and the inward facing surface of the tubular housing that is substantially less than a cross-sectional area of the unobstructed passageway; and
wherein the tubular housing of the emitter is round.
21. The method of claim 19 wherein said inward-facing surface is a concave surface.
22. The method of claim 13 further including at least one conductor coupled to one of the first and second electrodes, the at least one conductor exiting a wall of the housing in a radial direction relative to the longitudinal axis of the housing.
23. The method of claim 13 wherein the oxygen produced comprises microbubbles.
24. The method of claim 13 wherein the power source delivers a current to the electrodes at a ratio of 1.75 amps or less per 3 square inches of active electrode.
25. The method of claim 13 wherein the first electrode includes a first anode element and the second electrode includes a first cathode element, and wherein the emitter includes a second anode element non-parallel to the first anode element, and wherein the emitter includes a second cathode element non-parallel to the first cathode element.
26. The method of claim 13 wherein the oxygen produced comprises nanobubbles.
27. An emitter for electrolytic generation of bubbles of oxygen in water, the emitter comprising:
a tubular housing defining an oxygenation chamber and having a water inlet, a water outlet, a longitudinal water flow axis from the inlet to the outlet, and an inward-facing surface that runs parallel to the water flow axis and defines at least in part the oxygenation chamber;
at least two electrodes comprising an outside electrode and an inside electrode, the outside and inside electrodes being positioned in the oxygenation chamber, said outside and inside electrodes extending in a direction that is parallel to the longitudinal axis, the outside electrode opposing and separated from the inside electrode by a distance of between 0.005 inches to 0.140 inches within the chamber,
wherein the position and size of each electrode within the chamber defines a cross-section of the chamber that has a water flow area within the oxygenation chamber through which water may flow without passing between electrodes of opposite polarity that are separated by a distance of between 0.005 inches to 0.140 inches, wherein the water flow area is greater than an area at the cross-section equal to the total area between electrodes of opposite polarity that are separated by a distance of between 0.005 inches to 0.140 inches,
wherein at least a portion of the outside electrode positioned in the chamber is closer to the inward-facing surface of the oxygenation chamber than to a longitudinal center axis of the oxygenation chamber; and
a power source in electrical communication with the outside and inside electrodes, the power source configured to deliver a voltage to the outside and inside electrodes, the voltage being less than or equal to 28.3 volts, the power source being configured to deliver a current to the outside and inside electrodes, the current being less than or equal to 12.8 amps.
28. The emitter of claim 27 wherein each electrode is positioned closer to the inward-facing surface of the chamber than to the longitudinal center axis of the oxygenation chamber.
29. The emitter of claim 27 wherein the outside and inside electrodes are positioned away from the longitudinal center axis of the tubular housing and maintain an unobstructed passageway parallel to the center axis, the passageway running longitudinally for at least the length of the outside and inside electrodes positioned within the chamber.
30. The emitter of claim 29 wherein the unobstructed passageway includes the center axis and is multiple times wider than the distance separating the opposing inner and outer electrodes within the chamber.
31. The emitter of claim 30 wherein the outside electrode defines a cross-sectional area between the outside electrode and the inward-facing surface of the chamber that is substantially less than a cross-sectional area of said unobstructed passageway.
32. The emitter of claim 27 comprising at least one conductor coupled to one of the outside and inside electrodes, the at least one conductor exiting a wall of the housing in a radial direction relative to the longitudinal center axis of the housing.
33. The emitter of claim 27 wherein the power source is configured to deliver a current to the electrodes at a ratio of 1.75 amps or less per 3 square inches of active electrode.
34. The emitter of claim 27 wherein the outer electrode includes a first anode element and the inner electrode includes a first cathode element, and wherein the emitter includes a second anode element non-parallel to the first anode element, and wherein the emitter includes a second cathode element non-parallel to the first cathode element.
35. A method for treating water comprising:
providing a flow-through oxygenator comprising an emitter for electrolytic generation of bubbles of oxygen, the emitter including:
a tubular housing defining an oxygenation chamber and having a water inlet, and a water outlet;
at least two electrodes comprising a first electrode and a second electrode, the first and second electrodes being positioned in the oxygenation chamber, the first electrode opposing and separated from the second electrode by a distance of between 0.005 inches to 0.140 inches, a portion of at least one of the first and second electrodes being in contact with at least one wall of the tubular housing, said wall defining at least in part the oxygenation chamber, wherein each electrode is positioned within the oxygenation chamber so that a cross section of the oxygenation chamber includes a water flow area that allows water to avoid passing between electrodes separated by 0.005 inches to 0.140 inches;
a power source in electrical communication with the first and second electrodes, the power source configured to deliver a voltage to the first and second electrodes, the voltage being less than or equal to 28.3 volts, the power source being configured to deliver a current to the first and second electrodes, the current being less than or equal to 12.8 amps;
passing water through the tubular housing while electrical current is applied to the first and second electrodes to produce oxygen in said water via electrolysis.
36. The method of claim 35 wherein the tubular housing has a longitudinal center axis and an inward-facing surface that runs parallel to the longitudinal center axis; and
wherein each electrode of the emitter is positioned so that substantially all points midway between all opposing electrodes inside the chamber are closer to said inwardly-facing surface than to the longitudinal center axis.
37. The method of claim 35 wherein the chamber has a longitudinal center axis and an inward-facing surface that runs parallel to the longitudinal axis,
wherein the first and second electrodes extend in a direction that is parallel to the longitudinal axis.
38. The method of claim 37 wherein each electrode of the emitter is positioned closer to the inward-facing surface of the chamber than to the longitudinal center axis of the oxygenation chamber.
39. The method of claim 35 wherein the at least one electrode in contact with a wall of the tubular housing is in contact with a curved wall of the tubular housing.
40. The method of claim 35 wherein the outside and inside electrodes are positioned away from a longitudinal center axis of the tubular housing and maintain an unobstructed passageway parallel to the center axis, the passageway running longitudinally for at least the length of the outside and inside electrodes positioned within the chamber.
41. The method of claim 40 wherein the unobstructed passageway includes the center axis and is multiple times wider than the distance separating the opposing first and second electrodes within the chamber.
42. The method of claim 40 wherein the chamber has an inward-facing surface that runs parallel to the longitudinal axis;
wherein the first and second electrodes being outside and inside electrodes respectively in that the first and second electrodes are positioned relative to each other so that the outside electrode is closer to an outer wall of the chamber than the inside electrode is and so that the inside electrode is closer to the longitudinal axis at the center of the tubular housing than the outside electrode is; and
wherein the outside electrode defines a cross-sectional area between the outside electrode and the inward facing surface of the tubular housing that is substantially less than a cross-sectional area of the unobstructed passageway.
43. The method of claim 35 wherein the emitter includes at least one conductor coupled to one of the first and second electrodes, the at least one conductor exiting a wall of the housing in a radial direction relative to a longitudinal axis of the housing.
44. The method of claim 35 wherein the oxygen produced comprises microbubbles.
45. The method of claim 35 wherein the power source delivers a current to the electrodes at a ratio of 1.75 amps or less per 3 square inches of active electrode.
46. The method of claim 35 wherein the first electrode includes a first anode element and the second electrode includes a first cathode element, and wherein the emitter includes a second anode element non-parallel to the first anode element, and wherein the emitter includes a second cathode element non-parallel to the first cathode element.
47. The method of claim 35 wherein the oxygen produced comprises nanobubbles.
48. A method for treating water comprising:
providing a flow-through oxygenator comprising an emitter for electrolytic generation of bubbles of oxygen, the emitter including:
a tubular housing defining an oxygenation chamber, said housing having an inward-facing surface that defines at least in part the oxygenation chamber, the tubular housing having a water inlet, and a water outlet;
at least two electrodes comprising an outside electrode and an inside electrode, the outside and inside electrodes being positioned in the oxygenation chamber, said outside and inside electrodes extending in a direction that runs parallel to the inward-facing surface, the outside and inside electrodes being outside and inside electrodes respectively in that the outside and inside electrodes are positioned relative to each other so that the outside electrode is closer to the inward-facing surface of the chamber than the inside electrode is and so that the inside electrode is closer to the longitudinal center axis than the outside electrode is, the outside electrode opposing and separated from the inside electrode by a distance of between 0.005 inches to 0.140 inches within the chamber;
wherein each electrode of the emitter is positioned closer to the inward-facing surface of the chamber than to a midpoint of the tubular housing and so that at least some water may flow through an unobstructed passageway from the water inlet to the water outlet without passing through a space between electrodes of opposite polarity separated by a distance of between 0.005 inches to 0.140 inches;
passing water through the oxygenation chamber while applying electrical current to the electrodes to produce oxygen in said water via electrolysis.
49. The method of claim 48 wherein the tubular housing defines a longitudinal center axis that lies in the oxygenation chamber and wherein the unobstructed passageway includes the longitudinal center axis.
50. The method of claim 48 wherein at least one of the outside and inside electrodes is in contact with at least one wall of the tubular housing, said wall defining at least in part the oxygenation chamber.
51. The method of claim 50 wherein the at least one electrode in contact with a wall of the tubular housing is in contact with a curved wall of the tubular housing.
52. The method of claim 48 wherein the unobstructed passageway is multiple times wider than the distance separating the opposing inner and outer electrodes within the chamber.
53. The method of claim 52 wherein the outside electrode defines a cross-sectional area between the outside electrode and the inward-facing surface of the chamber that is substantially less than a cross-sectional area of said unobstructed passageway.
54. The method of claim 53 wherein said inward-facing surface is a concave surface.
55. The method of claim 48 wherein the emitter includes at least one conductor coupled to one of the outside and inside electrodes, the at least one conductor exiting a wall of the housing in a radial direction relative to a longitudinal center axis of the housing.
56. The method of claim 48 wherein the oxygen produced comprises microbubbles of oxygen.
57. The method of claim 48 wherein the electrical current is applied to the electrodes at a ratio of 1.75 amps or less per 3 square inches of active electrode.
58. The method of claim 48 wherein the outside electrode includes a first anode element and the inside electrode includes a first cathode element, and wherein the emitter includes a second anode element non-parallel to the first anode element, and wherein the emitter includes a second cathode element non-parallel to the first cathode element.
59. The method of claim 48 wherein the oxygen produced comprises nanobubbles of oxygen.
60. An emitter for electrolytic generation of bubbles of oxygen in water, the emitter comprising:
a tubular oxygenation chamber, said chamber having an outer wall that runs parallel to a longitudinal center axis of the chamber, said chamber having a water inlet and a water outlet,
at least two electrodes comprising an outside electrode and an inside electrode, the outside and inside electrodes being positioned in the oxygenation chamber, the outside and inside electrodes being outside and inside electrodes respectively in that the electrodes are positioned relative to each other so that the outside electrode is closer to the outer wall of the chamber than the inside electrode is and so that the inside electrode is closer to the longitudinal center axis than the outside electrode is, the outside electrode opposing and separated from the inside electrode by a distance of between 0.005 inches to 0.140 inches;
the at least two electrodes being positioned away from the center axis and maintaining a longitudinal, unobstructed passageway parallel to and including the center axis that runs for at least the length of the at least two electrodes positioned within the chamber, the unobstructed passageway having a substantially uniform cross-sectional area along that length, the at least two electrodes being positioned so that water may flow from the water inlet to the water outlet without passing through a space between electrodes of opposite polarity separated by a distance of between 0.005 inches to 0.140 inches;
wherein the outside electrode defines a cross-sectional area between the outside electrode and the outer wall of the chamber that is substantially less than said cross-sectional area of the unobstructed passageway.
61. The emitter of claim 60 wherein at least one of the outside and inside electrodes is in contact with at least one wall of the tubular oxygenation chamber.
62. The emitter of claim 61 wherein the at least one electrode in contact with a wall of the tubular oxygenation chamber is in contact with the outer wall, and wherein the outer wall is a curved wall of the oxygenation chamber.
63. The emitter of claim 60 wherein the unobstructed passageway is multiple times wider than the distance separating the opposing outside and inside electrodes within the chamber.
64. The emitter of claim 60 wherein said outer wall includes an inwardly-facing concave surface.
65. The emitter of claim 60 comprising at least one conductor coupled to one of the outside and inside electrodes, the at least one conductor exiting a wall of the chamber in a radial direction relative to the longitudinal center axis of the chamber.
66. The emitter of claim 60 wherein the outside electrode includes a first anode element and the inside electrode includes a first cathode element, and wherein the emitter includes a second anode element non-parallel to the first anode element, and wherein the emitter includes a second cathode element non-parallel to the first cathode element.
67. A method for treating water comprising:
providing a flow-through oxygenator comprising an emitter for electrolytic generation of bubbles of oxygen, the emitter including:
a tubular housing defining an oxygenation chamber and having a water inlet, a water outlet, a longitudinal water flow axis from the inlet to the outlet, and an inward-facing surface that runs parallel to the water flow axis and defines at least in part the oxygenation chamber;
at least two electrodes comprising an outside electrode and an inside electrode, the outside and inside electrodes being positioned in the oxygenation chamber, said outside and inside electrodes extending in a direction that is parallel to the longitudinal axis, the outside electrode opposing and separated from the inside electrode by a distance of between 0.005 inches to 0.140 inches within the chamber,
wherein the position and size of each electrode within the chamber defines a cross-section of the chamber that has a water flow area within the oxygenation chamber through which water may flow without passing between electrodes of opposite polarity that are separated by a distance of between 0.005 inches to 0.140 inches, wherein the water flow area is greater than an area at the cross-section equal to the total area between electrodes of opposite polarity that are separated by a distance of between 0.005 inches to 0.140 inches; and
a power source in electrical communication with the outside and inside electrodes, the power source configured to deliver a voltage to the outside and inside electrodes, the voltage being less than or equal to 28.3 volts, the power source being configured to deliver a current to the outside and inside electrodes, the current being less than or equal to 12.8 amps;
passing water through the oxygenation chamber while electrical current is applied to the outside and inside electrodes within the chamber to produce oxygen in said water via electrolysis.
68. The method of claim 67 wherein each electrode of the emitter is positioned closer to the inward-facing surface of the chamber than to a longitudinal center axis of the oxygenation chamber.
69. The method of claim 67 wherein the outside and inside electrodes of the emitter is positioned away from a longitudinal center axis of the tubular housing and maintain an unobstructed passageway parallel to the longitudinal center axis, the passageway running longitudinally for at least the length of the outside and inside electrodes within the chamber.
70. The method of claim 69 wherein the unobstructed passageway includes the longitudinal center axis and is multiple times wider than the distance separating the opposing inner and outer electrodes within the chamber.
71. The method of claim 70 wherein the outside electrode defines a cross-sectional area between the outside electrode and the inward-facing surface of the chamber that is substantially less than a cross-sectional area of said unobstructed passageway.
72. The method of claim 67 wherein the emitter includes at least one conductor coupled to one of the outside and inside electrodes, the at least one conductor exiting a wall of the housing in a radial direction relative to a longitudinal center axis of the housing.
73. The method of claim 67 wherein the oxygen produced comprises nanobubbles.
74. The method of claim 67 wherein the power source delivers a current to the outside and inside electrodes at a ratio of 1.75 amps or less per 3 square inches of active electrode.
75. The method of claim 67 wherein the outside electrode includes a first anode element and the inside electrode includes a first cathode element, and wherein the emitter includes a second anode element non-parallel to the first anode element, and wherein the emitter includes a second cathode element non-parallel to the first cathode element.
76. The method of claim 75 wherein the oxygen produced comprises nanobubbles.
77. A method for treating water comprising:
providing a flow-through oxygenator comprising an emitter for electrolytic generation of bubbles of oxygen, the emitter including:
a tubular oxygenation chamber, said chamber having an outer wall that runs parallel to a longitudinal center axis of the chamber, said chamber having a water inlet and a water outlet;
at least two electrodes comprising an outside electrode and an inside electrode, the outside and inside electrodes being positioned in the oxygenation chamber, the outside and inside electrodes being outside and inside electrodes respectively in that the outside and inside electrodes are positioned relative to each other so that the outside electrode is closer to the outer wall of the chamber than the inside electrode is and so that the inside electrode is closer to the longitudinal center axis than the outside electrode is, the outside electrode opposing and separated from the inside electrode by a distance of between 0.005 inches to 0.140 inches;
the at least two electrodes of the emitter being positioned away from the longitudinal center axis and maintaining a longitudinal, unobstructed passageway parallel to and including the longitudinal center axis that runs for at least the length of the at least two electrodes positioned within the chamber, the unobstructed passageway having a substantially uniform cross-sectional area along that length, the at least two electrodes of the emitter being positioned so that water may flow from the water inlet to the water outlet without passing through a space between electrodes of opposite polarity separated by a distance of between 0.005 inches to 0.140 inches;
wherein the outside electrode defines a cross-sectional area between the outside electrode and the outer wall of the chamber that is substantially less than said cross-sectional area of the unobstructed passageway; and
passing water through the oxygenation chamber while applying electrical current to the outside and inside electrodes to produce oxygen in said water via electrolysis.
78. The method of claim 77 wherein at least one of the outside and inside electrodes is in contact with at least one wall of the tubular oxygenation chamber.
79. The method of claim 78 wherein the at least one electrode in contact with a wall of the tubular oxygenation chamber is in contact with the outer wall, and wherein the outer wall is a curved wall of the oxygenation chamber.
80. The method of claim 77 wherein the unobstructed passageway is multiple times wider than the distance separating the opposing outside and inside electrodes within the chamber.
81. The method of claim 77 wherein said outer wall includes an inwardly-facing concave surface.
82. The method of claim 77 wherein the emitter includes at least one conductor coupled to one of the outside and inside electrodes, the at least one conductor exiting a wall of the chamber in a radial direction relative to the longitudinal center axis of the chamber.
83. The method of claim 77 wherein the outside electrode includes a first anode element and the inside electrode includes a first cathode element, and wherein the emitter includes a second anode element non-parallel to the first anode element, and wherein the emitter includes a second cathode element non-parallel to the first cathode element.
84. The method of claim 83 wherein the oxygen produced comprises nanobubbles of oxygen.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US15/085,741 USRE47092E1 (en) | 2002-02-22 | 2016-03-30 | Flow-through oxygenator |
Applications Claiming Priority (7)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US35853402P | 2002-02-22 | 2002-02-22 | |
| US10/372,017 US6689262B2 (en) | 2002-02-22 | 2003-02-21 | Microbubbles of oxygen |
| US10/732,326 US7396441B2 (en) | 2002-02-22 | 2003-12-10 | Flow-through oxygenator |
| US12/023,431 US7670495B2 (en) | 2002-02-22 | 2008-01-31 | Flow-through oxygenator |
| US13/247,241 USRE45415E1 (en) | 2002-02-22 | 2011-09-28 | Flow-through oxygenator |
| US14/601,340 USRE47665E1 (en) | 2002-02-22 | 2015-01-21 | Flow-through oxygenator |
| US15/085,741 USRE47092E1 (en) | 2002-02-22 | 2016-03-30 | Flow-through oxygenator |
Related Parent Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| US12/023,431 Reissue US7670495B2 (en) | 2002-02-22 | 2008-01-31 | Flow-through oxygenator |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| USRE47092E1 true USRE47092E1 (en) | 2018-10-23 |
Family
ID=63833033
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| US15/085,741 Expired - Lifetime USRE47092E1 (en) | 2002-02-22 | 2016-03-30 | Flow-through oxygenator |
Country Status (1)
| Country | Link |
|---|---|
| US (1) | USRE47092E1 (en) |
Citations (60)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US788557A (en) | 1904-06-21 | 1905-05-02 | Carl Adolph Sahlstroem | Electrical ozonizer. |
| US3775182A (en) | 1972-02-25 | 1973-11-27 | Du Pont | Tubular electrochemical cell with coiled electrodes and compressed central spindle |
| US3990962A (en) | 1973-10-01 | 1976-11-09 | Goetz Friedrich | Electrolytic cell device |
| US4005014A (en) | 1974-05-17 | 1977-01-25 | Arnold Wikey | Water treatment system with prolonged aeration |
| US4048030A (en) | 1975-07-16 | 1977-09-13 | Jorge Miller | Electrolytic cell for treatment of water |
| US4071447A (en) | 1975-04-16 | 1978-01-31 | Swift & Company | Dewatering of wastewater treatment wastes |
| GB1522188A (en) | 1974-10-17 | 1978-08-23 | Swift & Co | Apparatus and method for removing pollutants from wastewater |
| US4179347A (en) | 1978-02-28 | 1979-12-18 | Omnipure, Inc. | System for electrocatalytic treatment of waste water streams |
| US4219417A (en) | 1976-12-21 | 1980-08-26 | Dravo Corporation | Wastewater flotation utilizing streaming potential adjustment |
| US4225401A (en) | 1978-12-22 | 1980-09-30 | Kernforschungsanlage Julich Gesellschaft Mit Beschrankter Haftung | Method for generating hydrogen and oxygen |
| US4252856A (en) | 1973-03-12 | 1981-02-24 | Union Carbide Corporation | Chemically bonded aluminum coated carbon via monocarbides |
| US4257352A (en) | 1979-04-12 | 1981-03-24 | Ronald J. Randazza | Protozoan marine life inhibitor |
| US4587001A (en) | 1983-06-21 | 1986-05-06 | Imperial Chemical Industries Plc | Cathode for use in electrolytic cell |
| US4761208A (en) | 1986-09-29 | 1988-08-02 | Los Alamos Technical Associates, Inc. | Electrolytic method and cell for sterilizing water |
| US5015354A (en) | 1988-05-11 | 1991-05-14 | Permelec Electrode Ltd. | Bipolar-electrode electrolytic cell |
| US5049252A (en) | 1986-01-21 | 1991-09-17 | Murrell Wilfred A | Water cleaning system |
| US5148772A (en) | 1991-01-07 | 1992-09-22 | Kirschbaum Robert N | Method and apparatus for electrically inhibiting bacteria growth in aquariums |
| US5239158A (en) | 1992-04-15 | 1993-08-24 | Eaton Corporation | Laser marking of molded hand grips |
| KR940003935B1 (en) | 1991-12-09 | 1994-05-09 | 문재덕 | Apparatus for supplying air of in the aquarium |
| US5336399A (en) | 1991-12-27 | 1994-08-09 | Takekazu Kajisono | Apparatus for purifying and activating water |
| US5389214A (en) | 1992-06-19 | 1995-02-14 | Water Regeneration Systems, Inc. | Fluid treatment system employing electrically reconfigurable electrode arrangement |
| US5427667A (en) | 1992-04-03 | 1995-06-27 | Bakhir; Vitold M. | Apparatus for electrochemical treatment of water |
| WO1995021795A1 (en) | 1994-02-10 | 1995-08-17 | Bruce Davies | Electrocatalytic dissolved oxygen generator for water processing |
| US5500131A (en) | 1994-04-05 | 1996-03-19 | Metz; Jean-Paul | Compositions and methods for water treatment |
| US5534143A (en) | 1990-09-18 | 1996-07-09 | Louisiana State University Board Of Supervisors, A Governing Body Of Louisiana State University Agricultural And Mechanical College | Microbubble generator for the transfer of oxygen to microbial inocula, and microbubble generator immobilized cell reactor |
| EP0723936A2 (en) | 1995-01-30 | 1996-07-31 | First Ocean Co., Ltd. | A composite electrode construction for electrolysis of water |
| US5653900A (en) | 1991-01-17 | 1997-08-05 | United Distillers Plc | Dynamic laser marking |
| US5728287A (en) | 1996-10-31 | 1998-03-17 | H2 O Technologies, Ltd. | Method and apparatus for generating oxygenated water |
| US5767483A (en) | 1993-08-19 | 1998-06-16 | United Distillers Plc | Method of laser marking a body of material having a thermal conductivity approximately equal to that of glass |
| WO1999039561A1 (en) | 1998-02-10 | 1999-08-12 | Mazzei Angelo L | Beneficiation of soil with dissolved oxygen for growing crops |
| US5982609A (en) | 1993-03-22 | 1999-11-09 | Evans Capacitor Co., Inc. | Capacitor |
| US6033539A (en) | 1998-08-21 | 2000-03-07 | Gablenko; Viacheslav G. | Units for electro-chemical synthesis of water solution |
| US6110353A (en) | 1997-04-11 | 2000-08-29 | H20 Technologies, Ltd. | Housing and method that provide extended resident time for dissolving generated oxygen into water |
| US6171469B1 (en) | 1996-10-31 | 2001-01-09 | H2O Technologies, Ltd. | Method and apparatus for increasing the oxygen content of water |
| US6296756B1 (en) | 1999-09-09 | 2001-10-02 | H20 Technologies, Ltd. | Hand portable water purification system |
| US6315886B1 (en) | 1998-12-07 | 2001-11-13 | The Electrosynthesis Company, Inc. | Electrolytic apparatus and methods for purification of aqueous solutions |
| WO2001089997A2 (en) | 2000-05-11 | 2001-11-29 | Megaton Systems As | Means for electrochemical treatment of water |
| US6332972B1 (en) | 1999-12-17 | 2001-12-25 | H20 Technologies, Ltd. | Decontamination method and system, such as an in-situ groundwater decontamination system, producing dissolved oxygen and reactive initiators |
| US6337008B1 (en) | 2000-06-12 | 2002-01-08 | Alcan International Limited | Electrolysis cells |
| US6394429B2 (en) | 1996-05-13 | 2002-05-28 | Universidad De Sevilla | Device and method for fluid aeration via gas forced through a liquid within an orifice of a pressure chamber |
| US20020074237A1 (en) | 2000-12-19 | 2002-06-20 | Tominaga Mfg. Co. | Method of producing electrolyzed water |
| US6419815B1 (en) | 1998-06-26 | 2002-07-16 | Xogen Power Inc. | Method for producing orthohydrogen and/or parahydrogen |
| US6462303B2 (en) | 2000-01-27 | 2002-10-08 | Acushnet Company | Laser marking of golf balls |
| US6524475B1 (en) | 1999-05-25 | 2003-02-25 | Miox Corporation | Portable water disinfection system |
| US20030091469A1 (en) | 2001-10-31 | 2003-05-15 | Yasuhito Kondo | Water treating method and water treating system |
| US20030155297A1 (en) | 2002-02-12 | 2003-08-21 | Jerry Kellgren | Method and apparatus for oxygenating ground water |
| WO2003072507A1 (en) | 2002-02-22 | 2003-09-04 | Aqua Innovations, Inc. | Microbubbles of oxygen |
| US20040004007A1 (en) | 2001-07-26 | 2004-01-08 | Orolin John J. | Apparatus, methods, and systems for cleaning and controlling bacteria growth, such as in fluid supply lines |
| US20040060910A1 (en) | 2002-05-17 | 2004-04-01 | Rainer Schramm | High speed, laser-based marking method and system for producing machine readable marks on workpieces and semiconductor devices with reduced subsurface damage produced thereby |
| US20040118701A1 (en) * | 2002-02-22 | 2004-06-24 | Senkiw James Andrew | Flow-through oxygenator |
| US6811757B2 (en) | 2001-04-04 | 2004-11-02 | Ecozone Technologies Ltd. | Dielectric barrier discharge fluid purification system |
| US6846536B1 (en) | 1998-03-20 | 2005-01-25 | Ccs Technology, Inc. | Laser-markable sheathing |
| US20060054205A1 (en) | 2002-10-01 | 2006-03-16 | Akira Yabe | Nanobubble utilization method and device |
| US20070187262A1 (en) | 2006-02-10 | 2007-08-16 | Tennant Company | Electrochemically activated anolyte and catholyte liquid |
| US7388889B2 (en) | 2005-04-27 | 2008-06-17 | Vitro Laser Gmbh | Method and device for producing subsurface markings in a transparent material body |
| US7486705B2 (en) | 2004-03-31 | 2009-02-03 | Imra America, Inc. | Femtosecond laser processing system with process parameters, controls and feedback |
| US7626138B2 (en) | 2005-09-08 | 2009-12-01 | Imra America, Inc. | Transparent material processing with an ultrashort pulse laser |
| US7628912B2 (en) | 2006-09-25 | 2009-12-08 | Sharp Kabushiki Kaisha | Manufacturing device and application device for liquid containing micro-nano bubbles |
| US20100276294A1 (en) | 2003-03-28 | 2010-11-04 | Lambie John M | Electrolytic sanitization of water |
| US7922607B2 (en) | 2007-02-16 | 2011-04-12 | Acushnet Company | Noncontact printing on subsurface layers of translucent cover golf balls |
-
2016
- 2016-03-30 US US15/085,741 patent/USRE47092E1/en not_active Expired - Lifetime
Patent Citations (73)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US788557A (en) | 1904-06-21 | 1905-05-02 | Carl Adolph Sahlstroem | Electrical ozonizer. |
| US3775182A (en) | 1972-02-25 | 1973-11-27 | Du Pont | Tubular electrochemical cell with coiled electrodes and compressed central spindle |
| US4252856A (en) | 1973-03-12 | 1981-02-24 | Union Carbide Corporation | Chemically bonded aluminum coated carbon via monocarbides |
| US3990962A (en) | 1973-10-01 | 1976-11-09 | Goetz Friedrich | Electrolytic cell device |
| US4005014A (en) | 1974-05-17 | 1977-01-25 | Arnold Wikey | Water treatment system with prolonged aeration |
| GB1522188A (en) | 1974-10-17 | 1978-08-23 | Swift & Co | Apparatus and method for removing pollutants from wastewater |
| US4071447A (en) | 1975-04-16 | 1978-01-31 | Swift & Company | Dewatering of wastewater treatment wastes |
| US4048030A (en) | 1975-07-16 | 1977-09-13 | Jorge Miller | Electrolytic cell for treatment of water |
| US4219417A (en) | 1976-12-21 | 1980-08-26 | Dravo Corporation | Wastewater flotation utilizing streaming potential adjustment |
| US4179347A (en) | 1978-02-28 | 1979-12-18 | Omnipure, Inc. | System for electrocatalytic treatment of waste water streams |
| US4225401A (en) | 1978-12-22 | 1980-09-30 | Kernforschungsanlage Julich Gesellschaft Mit Beschrankter Haftung | Method for generating hydrogen and oxygen |
| US4257352A (en) | 1979-04-12 | 1981-03-24 | Ronald J. Randazza | Protozoan marine life inhibitor |
| US4587001A (en) | 1983-06-21 | 1986-05-06 | Imperial Chemical Industries Plc | Cathode for use in electrolytic cell |
| US5049252A (en) | 1986-01-21 | 1991-09-17 | Murrell Wilfred A | Water cleaning system |
| US4761208A (en) | 1986-09-29 | 1988-08-02 | Los Alamos Technical Associates, Inc. | Electrolytic method and cell for sterilizing water |
| US5015354A (en) | 1988-05-11 | 1991-05-14 | Permelec Electrode Ltd. | Bipolar-electrode electrolytic cell |
| US5534143A (en) | 1990-09-18 | 1996-07-09 | Louisiana State University Board Of Supervisors, A Governing Body Of Louisiana State University Agricultural And Mechanical College | Microbubble generator for the transfer of oxygen to microbial inocula, and microbubble generator immobilized cell reactor |
| US5148772A (en) | 1991-01-07 | 1992-09-22 | Kirschbaum Robert N | Method and apparatus for electrically inhibiting bacteria growth in aquariums |
| US5653900A (en) | 1991-01-17 | 1997-08-05 | United Distillers Plc | Dynamic laser marking |
| KR940003935B1 (en) | 1991-12-09 | 1994-05-09 | 문재덕 | Apparatus for supplying air of in the aquarium |
| US5336399A (en) | 1991-12-27 | 1994-08-09 | Takekazu Kajisono | Apparatus for purifying and activating water |
| US5427667A (en) | 1992-04-03 | 1995-06-27 | Bakhir; Vitold M. | Apparatus for electrochemical treatment of water |
| US5373138A (en) | 1992-04-15 | 1994-12-13 | Eaton Corporation | Laser marking of molded hand grips |
| US5239158A (en) | 1992-04-15 | 1993-08-24 | Eaton Corporation | Laser marking of molded hand grips |
| US5389214A (en) | 1992-06-19 | 1995-02-14 | Water Regeneration Systems, Inc. | Fluid treatment system employing electrically reconfigurable electrode arrangement |
| US5982609A (en) | 1993-03-22 | 1999-11-09 | Evans Capacitor Co., Inc. | Capacitor |
| US5767483A (en) | 1993-08-19 | 1998-06-16 | United Distillers Plc | Method of laser marking a body of material having a thermal conductivity approximately equal to that of glass |
| WO1995021795A1 (en) | 1994-02-10 | 1995-08-17 | Bruce Davies | Electrocatalytic dissolved oxygen generator for water processing |
| US5500131A (en) | 1994-04-05 | 1996-03-19 | Metz; Jean-Paul | Compositions and methods for water treatment |
| EP0723936A2 (en) | 1995-01-30 | 1996-07-31 | First Ocean Co., Ltd. | A composite electrode construction for electrolysis of water |
| US6394429B2 (en) | 1996-05-13 | 2002-05-28 | Universidad De Sevilla | Device and method for fluid aeration via gas forced through a liquid within an orifice of a pressure chamber |
| US5728287A (en) | 1996-10-31 | 1998-03-17 | H2 O Technologies, Ltd. | Method and apparatus for generating oxygenated water |
| US6478949B1 (en) | 1996-10-31 | 2002-11-12 | H2O Technologies, Ltd. | Method and apparatus for increasing the oxygen content of water |
| US6171469B1 (en) | 1996-10-31 | 2001-01-09 | H2O Technologies, Ltd. | Method and apparatus for increasing the oxygen content of water |
| US6110353A (en) | 1997-04-11 | 2000-08-29 | H20 Technologies, Ltd. | Housing and method that provide extended resident time for dissolving generated oxygen into water |
| WO1999039561A1 (en) | 1998-02-10 | 1999-08-12 | Mazzei Angelo L | Beneficiation of soil with dissolved oxygen for growing crops |
| US6846536B1 (en) | 1998-03-20 | 2005-01-25 | Ccs Technology, Inc. | Laser-markable sheathing |
| US6419815B1 (en) | 1998-06-26 | 2002-07-16 | Xogen Power Inc. | Method for producing orthohydrogen and/or parahydrogen |
| US6033539A (en) | 1998-08-21 | 2000-03-07 | Gablenko; Viacheslav G. | Units for electro-chemical synthesis of water solution |
| US6315886B1 (en) | 1998-12-07 | 2001-11-13 | The Electrosynthesis Company, Inc. | Electrolytic apparatus and methods for purification of aqueous solutions |
| US6328875B1 (en) | 1998-12-07 | 2001-12-11 | Zappi Water Purification System, Inc., | Electrolytic apparatus, methods for purification of aqueous solutions and synthesis of chemicals |
| US6524475B1 (en) | 1999-05-25 | 2003-02-25 | Miox Corporation | Portable water disinfection system |
| US6296756B1 (en) | 1999-09-09 | 2001-10-02 | H20 Technologies, Ltd. | Hand portable water purification system |
| US20020046957A1 (en) | 1999-09-09 | 2002-04-25 | H2O Technologies, Limited | Hand portable water purification system |
| US6332972B1 (en) | 1999-12-17 | 2001-12-25 | H20 Technologies, Ltd. | Decontamination method and system, such as an in-situ groundwater decontamination system, producing dissolved oxygen and reactive initiators |
| US6462303B2 (en) | 2000-01-27 | 2002-10-08 | Acushnet Company | Laser marking of golf balls |
| WO2001089997A2 (en) | 2000-05-11 | 2001-11-29 | Megaton Systems As | Means for electrochemical treatment of water |
| US6337008B1 (en) | 2000-06-12 | 2002-01-08 | Alcan International Limited | Electrolysis cells |
| US20020074237A1 (en) | 2000-12-19 | 2002-06-20 | Tominaga Mfg. Co. | Method of producing electrolyzed water |
| US6811757B2 (en) | 2001-04-04 | 2004-11-02 | Ecozone Technologies Ltd. | Dielectric barrier discharge fluid purification system |
| US20040004007A1 (en) | 2001-07-26 | 2004-01-08 | Orolin John J. | Apparatus, methods, and systems for cleaning and controlling bacteria growth, such as in fluid supply lines |
| US20030091469A1 (en) | 2001-10-31 | 2003-05-15 | Yasuhito Kondo | Water treating method and water treating system |
| US20030155297A1 (en) | 2002-02-12 | 2003-08-21 | Jerry Kellgren | Method and apparatus for oxygenating ground water |
| WO2003072507A1 (en) | 2002-02-22 | 2003-09-04 | Aqua Innovations, Inc. | Microbubbles of oxygen |
| US20060150491A1 (en) | 2002-02-22 | 2006-07-13 | Senkiw James A | Flow-through oxygenator |
| US20040118701A1 (en) * | 2002-02-22 | 2004-06-24 | Senkiw James Andrew | Flow-through oxygenator |
| US6689262B2 (en) * | 2002-02-22 | 2004-02-10 | Aqua Innovation, Inc. | Microbubbles of oxygen |
| US20030164306A1 (en) | 2002-02-22 | 2003-09-04 | Senkiw James Andrew | Microbubbles of oxygen |
| US20080202995A1 (en) | 2002-02-22 | 2008-08-28 | Aqua Innovations, Inc. | Flow-through oxygenator |
| US7396441B2 (en) * | 2002-02-22 | 2008-07-08 | Aqua Innovations, Inc. | Flow-through oxygenator |
| US20040060910A1 (en) | 2002-05-17 | 2004-04-01 | Rainer Schramm | High speed, laser-based marking method and system for producing machine readable marks on workpieces and semiconductor devices with reduced subsurface damage produced thereby |
| US7067763B2 (en) | 2002-05-17 | 2006-06-27 | Gsi Group Corporation | High speed, laser-based marking method and system for producing machine readable marks on workpieces and semiconductor devices with reduced subsurface damage produced thereby |
| US20060054205A1 (en) | 2002-10-01 | 2006-03-16 | Akira Yabe | Nanobubble utilization method and device |
| US20100276294A1 (en) | 2003-03-28 | 2010-11-04 | Lambie John M | Electrolytic sanitization of water |
| US8279903B2 (en) | 2004-03-31 | 2012-10-02 | Imra America, Inc. | Femtosecond laser processing system with process parameters, controls and feedback |
| US7486705B2 (en) | 2004-03-31 | 2009-02-03 | Imra America, Inc. | Femtosecond laser processing system with process parameters, controls and feedback |
| US7912100B2 (en) | 2004-03-31 | 2011-03-22 | Imra America, Inc. | Femtosecond laser processing system with process parameters, controls and feedback |
| US7388889B2 (en) | 2005-04-27 | 2008-06-17 | Vitro Laser Gmbh | Method and device for producing subsurface markings in a transparent material body |
| US7626138B2 (en) | 2005-09-08 | 2009-12-01 | Imra America, Inc. | Transparent material processing with an ultrashort pulse laser |
| US8389891B2 (en) | 2005-09-08 | 2013-03-05 | Imra America, Inc. | Transparent material processing with an ultrashort pulse laser |
| US20070187262A1 (en) | 2006-02-10 | 2007-08-16 | Tennant Company | Electrochemically activated anolyte and catholyte liquid |
| US7628912B2 (en) | 2006-09-25 | 2009-12-08 | Sharp Kabushiki Kaisha | Manufacturing device and application device for liquid containing micro-nano bubbles |
| US7922607B2 (en) | 2007-02-16 | 2011-04-12 | Acushnet Company | Noncontact printing on subsurface layers of translucent cover golf balls |
Non-Patent Citations (39)
| Title |
|---|
| Da Silva, Leonardo M, et al., "Electrochemical ozone production: influence of the supporting electrolyte on kinetics and current efficiency", Electrochimica Acta, 48(6), (Feb. 5, 2003), 699-709. |
| Da Silva, Leonardo M, et al., "electrochemistry and green chemical processes: electrochemical ozone production", Quim. Nova, 26(6), (2003), 880-888. |
| Effect of Oxgenated Water on the Growth & Biomass Development of Seedless Cucumbers and Tomato Seedlings under Greenhouse Conditions, Project Report: Seair Diffusion Systems, [Online]. Retrieved from the Internet: URL:http://www.seair.ca/Pages/pdfs/DrMirzaReport.pdf, (2003), 5 pgs. |
| Foller, P.C., et al., "The Anodic Evolution of Ozone", Journal of the Electrochemical Society, 129(3), (1982), 506-515. |
| Mohyuddin Mirza et al., "Effect of Oxygenated Water on the Growth & Biomass Development of Seedless Cucumbers and Tomato Seedlings under Greenhouse Conditions," Seair Diffusion Systems, 2003, 5 pages, www.seair.ca. |
| Stucki, S., et al, "Ozone micro-bubble disinfection method for wastewater reuse system", Water Science & Technology, 56(5), (2007), 53-61. |
| U.S. Appl. No. 12/023,431, Non Final Office Action dated Mar. 27, 2009, 5 pgs. |
| U.S. Appl. No. 12/023,431, Notice of Allowance dated Sep. 23, 2009, 6 pgs. |
| U.S. Appl. No. 12/023,431, Preliminary Amendment dated Dec. 16, 2008, 7 pgs. |
| U.S. Appl. No. 12/023,431, Response dated Aug. 20, 2009 to Non Final Office Action dated Feb. 27, 2009, 7 pgs. |
| U.S. Appl. No. 13/247,241, Examiner Interview Summary dated May 23, 2013, 3 pgs. |
| U.S. Appl. No. 13/247,241, Final Office Action dated Nov. 5, 2013, 16 pgs. |
| U.S. Appl. No. 13/247,241, Non Final Office Action dated Mar. 25, 2014, 12 pgs. |
| U.S. Appl. No. 13/247,241, Non Final Office Action dated Mar. 6, 2013, 14 pgs. |
| U.S. Appl. No. 13/247,241, Notice of Allowance dated Nov. 18, 2014, 7 pgs. |
| U.S. Appl. No. 13/247,241, Preliminary Amendment dated Sep. 28, 2011, 17 pgs. |
| U.S. Appl. No. 13/247,241, Response dated Jan. 21, 2014 to Final Office Action dated Nov. 5, 2013, 18 pgs. |
| U.S. Appl. No. 13/247,241, Response dated Jul. 8, 2013 to Non Final Office Action dated Mar. 6, 2013, 15 pgs. |
| U.S. Appl. No. 13/247,241, Response dated May 13, 2014 to Non Final Office Action dated Mar. 25, 2014, 6 pgs. |
| U.S. Appl. No. 13/247,241, Supplemental Preliminary Amendment dated Jul. 18, 2014, 5 pgs. |
| U.S. Appl. No. 13/247,241, Supplemental Preliminary Amendment dated Oct. 20, 2014, 6 pgs. |
| U.S. Appl. No. 13/247,241, Supplemental Preliminary Amendment dated Sep. 17, 2014, 7 pgs. |
| U.S. Appl. No. 14/601,340, Advisory Action, dated Nov. 21, 2015. |
| U.S. Appl. No. 14/601,340, Amendment and Response, filed Feb. 6, 2017. |
| U.S. Appl. No. 14/601,340, Amendment with RCE, dated Jan. 26, 2016. |
| U.S. Appl. No. 14/601,340, Amendment, dated Jul. 6, 2015. |
| U.S. Appl. No. 14/601,340, Applicant's Appeal Brief, filed Nov. 21, 2017. |
| U.S. Appl. No. 14/601,340, Applicant's Interview Summary, filed May 17, 2017. |
| U.S. Appl. No. 14/601,340, Applicant's Reply Brief, filed Feb. 26, 2018, pp. 1-15. |
| U.S. Appl. No. 14/601,340, Examiner's Answer, dated Feb. 13, 2018, pp. 1-35. |
| U.S. Appl. No. 14/601,340, Examiner's Interview Summary, dated May 22, 2017. |
| U.S. Appl. No. 14/601,340, Final Office Action, dated Jun. 5, 2017. |
| U.S. Appl. No. 14/601,340, Interview Request, dated Jan. 21, 2015. |
| U.S. Appl. No. 14/601,340, Office Action, dated May 13, 2015. |
| U.S. Appl. No. 14/601,340, Office Action, dated Oct. 27, 2015. |
| U.S. Appl. No. 14/601,340, Office Action, dated Oct. 5, 2017. |
| U.S. Appl. No. 14/601,340, Preliminary Amendment dated Jan. 21, 2015. |
| U.S. Appl. No. 14/601,340, Response to Final Action, dated Nov. 15, 2015. |
| U.S. Appl. No. 14/601,340, Supplemental Preliminary Amendment, filed Jan. 21, 2015. |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| USRE47665E1 (en) | Flow-through oxygenator | |
| US6689262B2 (en) | Microbubbles of oxygen | |
| EP0942645A1 (en) | Method of raising fish by use of algal turf | |
| US5951839A (en) | Method of producing a water-based fluid having magnetic resonance of a selected material | |
| WO2024010797A1 (en) | Electrolytic cells, treatment of water, and methods of use | |
| WO2019069734A1 (en) | Hydrogen water generation device | |
| US20190373828A1 (en) | Flow through Oxygen Infuser | |
| USRE47092E1 (en) | Flow-through oxygenator | |
| JP4200455B2 (en) | Electrolyzed reduced water generation device for crop cultivation, foliar spray water, soil irrigation water or soil irrigation water, and crop cultivation method | |
| WO2022061209A1 (en) | Electrochemical plant treatment apparatus and method | |
| KR980007951A (en) | Environment-friendly farming method using anion and ozone and its device | |
| US12404191B2 (en) | Surface water biosource augmentation production and distribution system | |
| US6361715B1 (en) | Method for reducing the redox potential of substances | |
| MXPA06006276A (en) | Flow-through oxygenator | |
| KR100332921B1 (en) | A method for eliminating red tide and an apparatus for eliminating red tide | |
| JPH07285817A (en) | Method for using special active water for plant | |
| CN217184241U (en) | Water planting device | |
| WO2022180430A1 (en) | Agroponics system | |
| JP6994780B2 (en) | Hydrogen water generator | |
| WO2024211604A3 (en) | Method and system for enhancing and retaining growth and health of biomatter | |
| KR101206008B1 (en) | Device and Method of disinfecting nutrient solution for plant factory | |
| JP2000024667A (en) | Manufacturing device for water obtained by immersing charcoal in filled water and by high voltage application/ discharge and utilizing application thereof | |
| JP2003018929A (en) | Method and apparatus for hydroponics | |
| JPS5898188A (en) | Biomass multi-purpose pumping-up power plant | |
| JP2000024668A (en) | Manufacturing device for water obtained by immersing deposit- and weather-produced reef coral particles in filled water and by high voltage application/discharge and utilizing application thereof |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| MAFP | Maintenance fee payment |
Free format text: PAYMENT OF MAINTENANCE FEE, 12TH YR, SMALL ENTITY (ORIGINAL EVENT CODE: M2553); ENTITY STATUS OF PATENT OWNER: SMALL ENTITY Year of fee payment: 12 |