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:
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
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.
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.
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.
An O2 emitter was made in a multilayer sandwich embodiment. (
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.
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
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
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
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.
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.
Number | Name | Date | Kind |
---|---|---|---|
788557 | Sahlstroem | May 1905 | A |
3775182 | Patton et al. | Nov 1973 | A |
3990962 | Gotz | Nov 1976 | A |
4005014 | Wikey | Jan 1977 | A |
4048030 | Miller | Sep 1977 | A |
4071447 | Ramirez | Jan 1978 | A |
4179347 | Krause et al. | Dec 1979 | A |
4219417 | Ramirez | Aug 1980 | A |
4225401 | Divisek et al. | Sep 1980 | A |
4252856 | Sara | Feb 1981 | A |
4257352 | Habegger | Mar 1981 | A |
4587001 | Cairns et al. | May 1986 | A |
4761208 | Gram et al. | Aug 1988 | A |
5015354 | Nishiki et al. | May 1991 | A |
5049252 | Murrell | Sep 1991 | A |
5148772 | Kirschbaum | Sep 1992 | A |
5239158 | Locklear et al. | Aug 1993 | A |
5336399 | Kajisono | Aug 1994 | A |
5373138 | Locklear et al. | Dec 1994 | A |
5389214 | Erickson et al. | Feb 1995 | A |
5427667 | Bakhir et al. | Jun 1995 | A |
5500131 | Metz | Mar 1996 | A |
5534143 | Portier et al. | Jul 1996 | A |
5653900 | Clement et al. | Aug 1997 | A |
5728287 | Hough et al. | Mar 1998 | A |
5767483 | Allan et al. | Jun 1998 | A |
5982609 | Evans | Nov 1999 | A |
6033539 | Gablenko | Mar 2000 | A |
6110353 | Hough | Aug 2000 | A |
6171469 | Hough et al. | Jan 2001 | B1 |
6296756 | Hough et al. | Oct 2001 | B1 |
6315886 | Zappi | Nov 2001 | B1 |
6328875 | Zappi et al. | Dec 2001 | B1 |
6332972 | Orollin | Dec 2001 | B1 |
6337008 | Christensen et al. | Jan 2002 | B1 |
6394429 | Gañan-Cálvo | May 2002 | B2 |
6419815 | Chambers | Jul 2002 | B1 |
6462303 | Brown | Oct 2002 | B1 |
6478949 | Hough et al. | Nov 2002 | B1 |
6524475 | Herrington et al. | Feb 2003 | B1 |
6689262 | Senkiw | Feb 2004 | B2 |
6811757 | Niv et al. | Nov 2004 | B2 |
6846536 | Priesnitz et al. | Jan 2005 | B1 |
7067763 | Clement et al. | Jun 2006 | B2 |
7388889 | Remy | Jun 2008 | B2 |
7396441 | Senkiw | Jul 2008 | B2 |
7486705 | Shah et al. | Feb 2009 | B2 |
7626138 | Bovatsek et al. | Dec 2009 | B2 |
7628912 | Yamasaki et al. | Dec 2009 | B2 |
7912100 | Shah et al. | Mar 2011 | B2 |
7922607 | Morgan et al. | Apr 2011 | B2 |
8279903 | Shah et al. | Oct 2012 | B2 |
8389891 | Bovatsek et al. | Mar 2013 | B2 |
20020046957 | Hough et al. | Apr 2002 | A1 |
20020074237 | Takesako et al. | Jun 2002 | A1 |
20030091469 | Kondo et al. | May 2003 | A1 |
20030155297 | Kellgren | Aug 2003 | A1 |
20030164306 | Senkiw | Sep 2003 | A1 |
20040004007 | Orolin et al. | Jan 2004 | A1 |
20040060910 | Schramm | Apr 2004 | A1 |
20040118701 | Senkiw | Jun 2004 | A1 |
20060054205 | Yabe et al. | Mar 2006 | A1 |
20060150491 | Senkiw | Jul 2006 | A1 |
20070187262 | Field et al. | Aug 2007 | A1 |
20080202995 | Senkiw | Aug 2008 | A1 |
20100276294 | Lambie | Nov 2010 | A1 |
Number | Date | Country |
---|---|---|
0 723 936 | Jul 1996 | EP |
0723936 | Jul 1996 | EP |
1 522 188 | Aug 1978 | GB |
1522188 | Aug 1978 | GB |
940003935 | May 1994 | KR |
WO-1995021795 | Aug 1995 | WO |
WO 9939561 | Aug 1999 | WO |
WO-9939561 | Aug 1999 | WO |
WO-0189997 | Nov 2001 | WO |
WO-03072507 | Sep 2003 | WO |
Entry |
---|
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. 6, 2013, 14 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, 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 May 13, 2014 to Non Final Office Action dated Mar. 25, 2014, 6 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, Supplemental Preliminary Amendment dated Jul. 18, 2014, 5 pgs. |
U.S. Appl. No. 13/247,241, Supplemental Preliminary Amendment dated Sep. 17, 2014, 7 pgs. |
U.S. Appl. No. 13/247,241, Supplemental Preliminary Amendment dated Oct. 20, 2014, 6 pgs. |
U.S. Appl. No. 14/601,340, Preliminary Amendment dated Jan. 21, 2015. |
U.S. Appl. No. 14/601,340, Supplemental Preliminary Amendment, filed Jan. 21, 2015. |
U.S. Appl. No. 14/601,340, Office Action, dated May 13, 2015. |
U.S. Appl. No. 14/601,340, Amendment, dated Jul. 6, 2015. |
U.S. Appl. No. 14/601,340, Office Action, dated Oct. 27, 2015. |
U.S. Appl. No. 14/601,340, Response to Final Action, dated Nov. 15, 2015. |
U.S. Appl. No. 14/601,340, Advisory Action, dated Nov. 21, 2015. |
U.S. Appl. No. 14/601,340, Interview Request, dated Jan. 21, 2015. |
U.S. Appl. No. 14/601,340, Amendment with RCE, dated Jan. 26, 2016. |
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. |
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. |
Foller, P.C., et al., “The Anodic Evolution of Ozone”, Journal of the Electrochemical Society, 129(3), (1982), 506-515. |
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. 14/601,340, Applicant's Appeal Brief, filed Nov. 21, 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, Office Action, dated Oct. 5, 2017. |
U.S. Appl. No. 14/601,340, Amendment and Response, filed Feb. 6, 2017. |
U.S. Appl. No. 14/601,340, Applicant's Interview Summary, filed May 17, 2017. |
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. |
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. |
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