1. Field of the Disclosure
The present invention relates to devices and methods for evaporating fluids from an open fluid reservoir, which in some applications may be used to accelerate the rate of concentration of suspended solids therein with or without the feature of promoting or maintaining aerobic conditions within the open fluid reservoir.
2. Background Art
Water and other fluids often accumulate various contaminants, and it is often desirable or necessary to separate the fluid from the contaminant to meet various purity targets or reduce the volume of liquid within an open reservoir, which may be necessary for practical, legal, or other reasons. Such contaminants may include, for example, salts, sulfur, heavy metals, suspended soils, human or animal waste, oils, fertilizers, pharmaceuticals, acid and any other undesirable matter as would be apparent to a person of skill in the art. The sources for contaminated fluids, also called effluent, are many, such as acid mine runoff, petrochemical processing fluids, agricultural runoff, municipal waste water and storm water runoff, and industrial process effluent, to name just a few examples. Frequently, the fluid to be treated is water, although clearly other fluids may need to have contaminants separated therefrom. For the purposes of this application, however, the exact fluid, contaminant, and source of contaminant is not particularly relevant, and so the terms water and contaminant will be used generically to include any fluid and matter, respectively, that one would desire to treat or purify, unless otherwise clearly indicated.
Outdoor open fluid reservoirs, such as retention ponds, aeration reservoirs, dry ponds, open-topped tanks, and the like, are often used to temporarily store effluent that contains undesirable levels of contaminants until the effluent can be treated to separate the contaminant from the water. After separation, the cleaned water can be released to the environment or otherwise used as desired, and the contaminant and/or concentrated effluent can be further processed, recycled, transported to an appropriate landfill, or otherwise disposed of.
When the contaminant is not a volatile substance, one commonly used method of separating the contaminant from the water is to evaporate the water from the effluent, thereby releasing clean water into the atmosphere in the gaseous state in the form of vapor while the contaminant is retained and/or re-captured in the reservoir. Depending on the circulation of effluent into the reservoir, after some period of time the water is either completely evaporated, thereby leaving the contaminants remaining in the reservoir for easy collection and disposal, or the concentration of contaminant is elevated to a point, such as saturation, where it becomes economically advantageous to further process and/or separate the highly concentrated effluent in other ways.
Although the water evaporates naturally at the surface of a pond or other outdoor reservoir, it is often desirable to increase the rate of evaporation to decrease the processing time of the effluent in order to increase economic efficiencies. Thus, it is common to place a reservoir evaporator system directly in the reservoir that effectively accelerates evaporation of the water to the surrounding environment by, for example, increasing the surface area to volume ratio of the effluent to the surrounding air. There are many ways to accomplish this, and of course, the efficacy of this evaporative treatment method is highly dependent on many variables other than the evaporator system, including flow rate of effluent into or through the reservoir, humidity levels of the surrounding environment, the fluid to be evaporated, and temperature, to name a few.
One known type of reservoir evaporator system uses nozzles to spray a fine mist of droplets of the effluent up into the air above the top surface of the reservoir. Under ideal conditions, the water in the droplets evaporates into the surrounding atmosphere more quickly than from the top surface because of the increased surface area to volume ratio, and the contaminants and any un-evaporated droplets fall back into the reservoir. An exemplary reservoir evaporation system generally incorporating this design is disclosed in U.S. Patent Application Publication No. 2010/0139871 to Rasmussen et al. A problem with these misting-types of reservoir evaporation systems, however, is that under non-ideal conditions the contaminates and un-evaporated droplets may be borne by winds away from the reservoir and settle out at nearby areas rather than in the reservoir. This could lead to unwanted deposition of the contaminates in surrounding areas, such as residential or other built-up areas, or uncontrolled release of the contaminates into surrounding environments, all of which are forms of multi-media pollution. Additionally, such systems frequently require a supply of high pressure to force the effluent through a nozzle and adequately aerosolize the effluent into the surrounding air.
Another known type of reservoir evaporator system floats on the top surface of the reservoir and includes a spinning agitator for scooping effluent from the top surface and sprinkling it into the air. The agitator is connected to a source of high pressure air that spins the agitator by means of thrust nozzles, and the exhaust from the thrust nozzles may be directed to further impact the effluent sprinkled into the air to further accelerate evaporation. An exemplary reservoir evaporation generally incorporating this design is disclosed in U.S. Pat. No. 4,001,077 to Kemper. In addition to the potential of causing multi-media pollution, another drawback to these systems is the need to use moving parts, which can frequently break or become jammed through buildup of scale from the contaminants.
Additionally, the inclusion of a high pressure air or liquid supply in each of these reservoir evaporator systems can increase complexity, cost, and maintenance requirements.
A further known type of reservoir evaporator system that dispenses with the use of high pressure air exposes evaporation surfaces that have been wetted with the effluent to the air and wind. One exemplary reservoir evaporation system generally incorporating this design is disclosed in U.S. Pat. No. 7,166,188 to Kadem et al. These designs, while overcoming the problem of drift to surrounding areas, may often require extensive maintenance to keep the evaporation surfaces free of contaminant buildup and often require complex mechanical and/or effluent transfer systems for dispersing the effluent onto the evaporation surfaces.
In view of this existing state of the art, the inventors of the present application have developed a reservoir evaporation system that overcomes in various aspects many of the drawbacks associated with the current systems.
According to one aspect, a fluid evaporator for evaporating fluid from an open fluid reservoir includes a partially enclosed vessel having an upper chamber and a lower chamber. The vessel is arranged to be operatively positioned in the fluid reservoir with the upper chamber disposed above a top surface of the fluid and the lower chamber disposed in the fluid. The vessel has a first opening through a lower portion of the lower chamber, and a gas supply tube extends into the lower chamber and has an air outlet disposed between the opening through the lower portion of the lower chamber and an upper portion of the lower chamber. An exhaust opening through the upper chamber is in fluid communication with the air outlet. The fluid evaporator also has a discharge conduit that has an inlet in fluid communication with the lower chamber and an outlet disposed below the lower chamber, wherein the inlet is separated from the lower portion of the chamber by a weir. When operatively positioned in the fluid reservoir, fluid from the fluid reservoir can enter into the lower chamber through the first opening, the air outlet is positioned to inject air into the fluid underneath the top surface, the air injected from the air outlet can exhaust out of the upper chamber through the exhaust opening, and the inlet is located below the top surface of the fluid.
A fluid evaporator according to another aspect includes a vessel having an upper chamber and a lower chamber, wherein the lower chamber is defined by an annular wall having an open bottom end and an upper end separated from and in fluid communication with the upper chamber, and an exhaust outlet through the upper chamber. A gas supply tube extends into the lower chamber and has an outlet operatively disposed between the bottom end of the annular wall and the upper end, wherein the gas supply tube and the annular wall define an annular space therebetween. The fluid evaporator further includes a fluid outlet pipe having an inlet and a discharge outlet. The inlet is in fluid communication with the lower chamber and disposed between the exhaust outlet and the bottom end of the lower chamber, and the fluid outlet pipe extends away from the inlet along the lower chamber.
According to a further aspect, a fluid evaporator for evaporating fluid from an open fluid reservoir includes a partially enclosed vessel having an upper chamber and a lower chamber, a flotation means with the vessel, a first opening through a lower portion of the lower chamber, a gas supply tube extending into the lower chamber and having an air outlet disposed between the opening through the lower portion of the lower chamber and an upper portion of the lower chamber, and an exhaust opening through the upper chamber and in fluid communication with the air outlet. The flotation means is located to cause the chamber to float operatively positioned on the top surface of the fluid in the fluid reservoir with the upper chamber disposed above the top surface of the fluid and the bottom chamber disposed in the fluid. When operatively positioned in the fluid reservoir, fluid from the fluid reservoir can enter into the lower chamber through the first opening, the air outlet is positioned to inject air into the fluid underneath the top surface, and the air injected from the air outlet can exhaust out of the upper chamber through the exhaust opening.
According to yet another aspect, a fluid evaporator includes a vessel having an upper chamber and a lower chamber, wherein the lower chamber is defined by an annular wall having an open bottom end and an upper end in fluid communication with the upper chamber, an exhaust outlet through the upper chamber. A gas supply tube extends into the lower chamber and has an outlet operatively disposed between the bottom end of the annular wall and the upper end, wherein the gas inlet tube and the annular wall define an annular space therebetween. A flotation device is associated with the vessel. The flotation device is arranged to cause the vessel to float in a pool of liquid with the bottom end of the annular wall disposed beneath a top surface of the pool and the upper chamber projecting upwardly from the top surface of the pool.
According to yet a further aspect, a reservoir evaporation system for evaporating fluid from an open reservoir of effluent containing a fluid and a contaminant includes a fluid evaporator, an air pump, and an air supply conduit functionally connecting the fluid evaporator with the air pump. The fluid evaporator includes a vessel with an upper chamber and a lower chamber, wherein the vessel is adapted to float in an operative position partially submerged on a top surface of the effluent in the reservoir with the lower chamber submerged in the effluent and the upper chamber extending above the top surface of the effluent. The vessel further includes a first opening into a lower portion of the lower chamber to allow the effluent to enter the chamber, and an exhaust opening into the upper chamber disposed to be above the top surface of the effluent and in communication with the lower chamber. The air supply conduit has an outlet arranged to discharge forced air into the lower portion of the chamber. When the fluid evaporator is in the operative position, air from the air pump can be injected into effluent in the lower chamber and subsequently travel through the upper chamber to be discharged from the vessel through the exhaust opening. By this arrangement fluid from the effluent in the lower chamber can be separated from the contaminant by evaporation.
A method of evaporating fluid from an open reservoir of fluid having a top surface according to an additional aspect includes the step of floating a fluid evaporator comprising a vessel at the top surface of the fluid in a partially submerged state. A bottom end of the vessel is submerged in the fluid and a top end of the vessel is disposed above the top surface of the fluid. A first opening through a lower portion of the vessel allows the fluid to enter the vessel, and an exhaust opening through a covered upper portion of the vessel disposed above the top surface of the fluid is in communication with the lower portion of the vessel. The method further includes the steps of forcing air into the fluid in the lower portion of the vessel through an outlet of an air supply conduit with the outlet disposed below the top surface of the fluid, aerating the fluid inside the lower portion of the vessel with the air, and discharging the air after aerating through the covered upper portion of the chamber to the exhaust opening. In this process fluid in the lower portion of the chamber is evaporated in the discharged air.
In still another aspect, a fluid evaporator includes a vessel arranged to float at the surface of a body of water with an upper chamber disposed above the water and a lower chamber disposed in the water, a gas supply tube having an outlet operatively disposed in the lower chamber, a gas flow path from the lower chamber to the upper chamber, and an exhaust outlet from the upper chamber. A bustle is operatively disposed between the gas flow path and the exhaust outlet and arranged to provide substantially uniform mass flow of gases at all circumferential locations around the bustle from a region inside the bustle radially outwardly to a region outside of the bustle to the exhaust outlet.
These and other aspects of the disclosure will be apparent in view of the following detailed description, claims, and the drawings.
Turning now to the drawings,
The reservoir evaporation system 10 includes a fluid evaporator 14, an air pump 16, and an air supply conduit 18 operatively connecting the fluid evaporator and the air pump. The fluid evaporator 14, which in this example may also be called a pond concentrator, is designed to increase the rate of evaporation of fluid from the effluent 12 by forcing air into effluent within the confines of the fluid evaporator and allowing controlled release of moist exhaust air containing water vapor after mixing with the effluent to reduce, control, and/or eliminate dispersion of entrained effluent with the exhaust air into the surrounding atmosphere. This separates the fluid in the effluent, such as water, from the contaminants by evaporating the fluid to the surrounding environment with the moist exhaust air while leaving contaminants, such as sulfur, salts, and suspended solids, in the effluent. Preferably, air from the air pump 16 is intimately mixed with effluent 12 inside the fluid evaporator, and the moist exhaust air travels through an enclosed exhaust pathway through the fluid evaporator 14 from the surface of the effluent to an exhaust port. As the exhaust air travels along the exhaust pathway, entrained effluent droplets or contaminants are removed from the exhaust air by contacting and collecting on the walls of the exhaust pathway and demister structures, such as baffles, screens, and/or other collection structures. Thus, the exhaust pathway preferably follows a tortuous path through the fluid evaporator between the top surface 20 of the effluent inside the fluid evaporator to the exhaust port to increase contact of the exhaust air with collection surfaces and demister structures before the exhaust air escapes from the fluid evaporator.
To accomplish this controlled evaporation and separation, the fluid evaporator 14 is operatively positioned in the reservoir such that it is partially submerged in the effluent 12. The operative position is preferably such that a top end of the fluid evaporator is disposed above the top surface 20 of the effluent 12 and a bottom end or portion of the fluid evaporator is submerged in the effluent. It should be noted that all directional descriptors, such as up, down, top, bottom, left, right, etc., are used herein for convenience of description in view of the operative positions illustrated in the drawings and are not intended as limitations on the scope of the disclosure. In a preferred arrangement, the fluid evaporator 14 has a body defining a partially enclosed vessel 22 that floats or is otherwise maintained in a position in the reservoir such that the top surface of the effluent is located between an upper chamber 24 of the vessel and a lower chamber 26 of the vessel. An opening 28 through a submerged portion of the fluid evaporator 14 allows effluent to enter into the lower chamber 26, and the lower chamber is separated from and in fluid communication with the upper chamber 24, which projects above the top surface 20 of the effluent 12. The upper chamber 24 at least partly defines the exhaust path from the top surface 20 of the effluent to one or more exhaust ports 30 located above the top surface 20 of the effluent 12 to the surrounding environment. The air supply conduit 18 has a discharge outlet 32 disposed inside the lower chamber arranged to be located below the top surface 20 of the effluent 12. The discharge outlet 32 includes an open end 32a of the conduit 18 at the lower end of the conduit and a plurality of sparge ports 32b, preferably in the form of vertical slots spaced around the conduit, spaced above the open lower end 32a. Thus, in the operative position, the air pump 16 can force air through the air supply conduit 18 and entrain the air in the effluent while contained inside the lower chamber 26, where the air can mix vigorously with the effluent inside the lower chamber 26, thereby allowing fluid from the effluent to evaporate more rapidly with the entrained air. In a preferred arrangement, all of the air enters the lower chamber 26 through the sparge ports 32b and the open end 32a is extended below the level of the sparge ports 32b so that the air does not flow through the open end 32a at the bottom of the air supply conduit 18. However, the open end 32b prevents build up of nuisance debris over time and acts as a pressure relief valve should the slots through which the air enters the lower chamber were to become plugged, such as with scale. Further, the column of water beneath the sparge ports 32b in some arrangements may also serve as a fluid “spring” to suppress possible pulsation of air flow into the lower chamber 26 and thereby promote symmetry of airflow through the fluid evaporator 14, thus promoting smooth operating characteristics. The air then can move naturally to the top surface 20 of the effluent and be released as moist exhaust air. The moist exhaust air then can travel through the exhaust pathway in the upper chamber 24 and out of the fluid evaporator 14 through the exhaust ports 30, while concentrated effluent and contaminants will be trapped within the fluid evaporator. In this manner, the fluid can be evaporated and separated out from the contaminants without allowing uncontrolled dispersion of the effluent into the surrounding environment.
In a further optional arrangement, the fluid evaporator 14 includes a fluid discharge conduit 34 through which aerated effluent from the lower chamber 26 can be discharged downwardly into the reservoir, thereby aerating the reservoir simultaneously while evaporating the fluid. One arrangement includes two discharge tubes 34a, 34b on opposite sides of the fluid evaporator that merge into a single discharge riser 34c below the vessel 22. The discharge riser 34c extends downwardly toward the bottom of the reservoir. This arrangement allows the fluid evaporator 14 to oxygenate the effluent in the reservoir from the bottom up as opposed to from the top down as accomplished by common aeration devices that spray water upwardly into the atmosphere and simply allow the aerated spray to return to the surface of the pond. This also provides a significant advantage over common aerators by providing a better way to promote aerobic digestion and/or provide oxygen to aquatic plants and animals while preventing anaerobic bacterial action from producing undesirable reduced compounds, such as sulfides, ammonia, and methane.
The fluid evaporator 14 may be maintained in the operative position at the top surface of the effluent by any convenient mechanism, such as support legs, a suspension structure, or floatation by, for example, displacement of water by captive air. Preferably, the fluid evaporator 14 floats on the top surface of the effluent 12 by means of a suitable flotation mechanism. This can be particularly advantageous when, for example, the reservoir is not continually replenished and the level of the effluent 12 drops or rises significantly. By floating on the top surface, the fluid evaporator 14 can move up and down with the level of the effluent 12 and thereby remain in the operative position over a large range of depths of the reservoir. In other applications where the level of the reservoir will remain relatively constant, support means such as legs, support brackets, or suspension mechanisms, may be equally sufficient to maintain the fluid evaporator 14 in its operative position.
In a preferred operative arrangement, one end of the air supply conduit 18 is connected to the air pump 16 and the opposite of the air supply conduit end is connected to the fluid evaporator 14, whereby the air pump can force air through the air supply conduit into the fluid evaporator. The air pump 16 may be any device that is operative to force air or other gasses to the fluid evaporator, such as a fan or other type of air blower. Other possible air pumps could include positive displacement pumps, air compressors, and/or other known gas pumps.
The air pump 16 can be located anywhere capable of being operatively connected with the fluid evaporator 14. As shown in
Power may be supplied to the air pump 16 by any suitable means as would be apparent to a person of skill in the art. For example, the air pump 16 may include an electric motor that is connected with a common alternating current electric supply by appropriate wiring. The electric motor also may be powered by photovoltaic cells. Another contemplated arrangement is to drive the air pump 16 with an internal combustion engine having a power take off, belt, chain, or other drive transfer arrangement known in the art operatively connected for driving the air pump.
Another possible configuration is to place the air pump 16 directly on or to be otherwise carried by the fluid evaporator 14. In this configuration, the air pump 16 may include a power and drive mechanism that is associated directly therewith, such as photovoltaic panels and circuitry and/or a diesel generator or engine unit, to provide power to the air pump. Further, the air supply conduit 18 in such an arrangement may be much shorter and simply extend from a fan, for example, to an outlet disposed in a preferred operative location inside the fluid evaporator 14 without extending across the effluent.
When adapted to float at the surface of the effluent, the fluid evaporator 14 optionally may be maintained in a selected position or area of the reservoir with one or more anchors 38. The anchors 38 may have any form suitable to maintain the fluid evaporator 14 in a selected position. One preferred anchoring system as shown in the drawings includes weights, such as concrete blocks or common boat anchors that are tethered to the fluid evaporator 14 and rest on the bottom of the reservoir. Other anchoring systems, however, could also be used as would be apparent to a person of skill in the art.
One or more solar thermal energy collectors 40 optionally may be connected with the fluid evaporator 14 to provide additional heat for increasing the rate of evaporation of fluid from the effluent 12. The solar thermal energy collectors 40 may be any device suitable for collecting solar thermal energy and concentrating the collected thermal energy to provide increased heat, such as solar hot water or gas panels, parabolic collectors, flat plate collectors, evacuated tube collectors, and/or other solar thermal energy collectors as would be apparent to a person of skill in the art. The solar thermal energy collectors 40 may be used to directly heat the body of the fluid evaporator 14, to directly heat the effluent in the fluid evaporator, and/or to heat the air supply that is forced into the fluid evaporator. In one arrangement, a solar thermal energy collector 40 is carried by and warms the body of the fluid evaporator 14. In this arrangement, the elevated temperature of the fluid evaporator 14 warms the air and effluent in contact therewith and thereby increases the rate of evaporation of fluid from the effluent. In another arrangement, a solar thermal energy collector 40 is located to warm the air supply upstream from the fluid evaporator 14. In this arrangement, the solar thermal energy collector 40 may, for example, include a solar air heat collector connected with the air supply conduit 18 and/or the air pump 16 to heat the air supply.
In addition or alternatively to using a solar thermal energy collector 40, the air supply conduit 18 and/or the fluid evaporator 14 optionally may be coated with an energy absorbent coating that further collects solar energy to warm the system. For example, it may be advantageous to paint portions of the fluid evaporator 14 and the air supply conduit 18 that are exposed to direct sunlight in the operative position with a dark coating, such as black paint, to absorb further solar thermal energy. Other solar energy absorptive coatings may also or alternatively be used as would be apparent to a person of skill in the art.
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Preferably, the vessel 22 is wider at the top than at the bottom. In one arrangement, the lower chamber 26 has a first width, the middle chamber 42 has a second width larger than the first width, and the upper chamber 24 has a third width larger than the second width. When the chambers have circular footprints, as depicted in the drawings, the widths may be equal to the respective diameters of the chambers. In other form factors, however, such as rectangular, polygonal, or elliptical, the widths refer to other width measurements across the footprints of the chambers. Although the successively larger widths of the lower, middle, and upper chambers 26, 42, 24 is not necessary for the fluid evaporator 14 to function, increasing the widths and cross-sectional footprint areas of the chambers from bottom to top along the exhaust path A can improve at least separation of effluent and contaminants from the exhaust air as compared with a vessel having a constant width. The successively larger widths also allow for more stable flotation of the fluid evaporator 14 where captive air within upper chamber 24 and middle chamber 42 is used to provide buoyancy while the pond evaporator 14 is operating.
The lower chamber 26 is formed by a first annular wall 26a that forms a weir with an open bottom end. The first annular wall 26a preferably is in the form of a circular tubular section; however, the annular wall 26a may have any desired shape that will encompass an annular space between the air supply downcomer 44 and an inner annular surface of the first annular wall 26a for defining an aeration mixing chamber. The middle chamber 42 is formed by a second annular wall 42a in the form of a circular tubular section with a larger diameter than the first annular wall 26a. The upper chamber 24 is formed by a third annular wall 24a in the form of a circular tubular section with a larger diameter than the second annular wall 42a. The chambers 24, 26, 42 need not be circular, however, and could take any other shape sufficient to provide the functions of the fluid evaporator 14 discussed herein as would be apparent to a person of skill in the art.
A first horizontal baffle 46 is disposed across the bottom end of the second annular wall 42a and separates the lower chamber 26 from the middle chamber 42. The first horizontal baffle 46 has an opening 48 that preferably matches the size and shape of the top of the first annular wall 26a, which in the present embodiment is circular, to provide for fluid communication between the lower chamber 26 and the middle chamber 42. Thus, the opening 48 acts as an extension of the lower chamber 26 through the horizontal baffle 46 so that aerated effluent 12 passing upwardly within the annular space between the downcomer 44 and the first annular wall 26a overflows radially outwardly over the first horizontal baffle 46 to provide smooth radial flow and allow air and evaporated moisture to separate cleanly from the effluent 12. The first horizontal baffle 46 also forms a first annular shoulder extending between the bottom end of the second annular wall 42a and the top end of the first annular wall 26a.
A second horizontal baffle 50 is disposed across the bottom end of the third annular wall 24a and separates the upper chamber 24 from the middle chamber 42. The second baffle 50 has at least one second opening 52 therethrough to provide for fluid communication from the middle chamber 42 to the upper chamber 24. A preferred arrangement includes a plurality of second openings 52 through the second horizontal baffle 50, each opening arranged to provide fluid communication from the middle chamber 42 to the upper chamber 24. As best seen in
The upper chamber 24 is covered with a top plate 54. The air supply downcomer 44 extends through apertures through the center of the top plate 54 and the first and second horizontal baffles 46, 50. The upper chamber 24 thereby forms a plenum 56 around the downcomer 44 in the upper chamber 24 at the top of the fluid evaporator 14 that can serve both as a part of the exhaust pathway A and as a flotation means to help the fluid evaporator float on the top surface 20 of the reservoir.
At least one exhaust port 30 through an outer wall of the upper chamber 24 allows exhaust air to escape from inside the upper chamber to the surrounding environment. The exhaust port 30 may be directed downwardly, radially outwardly, and/or upwardly from the upper chamber. In one preferred arrangement, as best seen in
Demisting structures preferably are incorporated in and/or across the exhaust path through the upper chamber. In the depicted example, first and second vertical baffles 58, 60, in the form of vertical annular walls, extend partially between the second baffle 50 and the top plate 54 and are spaced apart radially outwardly from the second openings 52. The second vertical baffle 60 effectively forms an upward extension from the top end of the second annular wall 42a and extends part way up from the second horizontal baffle 50 to the top plate 54, thereby forming an opening between the top of the baffle and the top plate. The first vertical baffle 58 extends downwardly from the top plate 54 part way to the second horizontal baffle 50, thereby forming another opening between the bottom of the first vertical baffle 58 and the second horizontal baffle 50. With the two openings vertically displaced from each other, the first and second vertical baffles 58, 60 cause the exhaust path A to have a tortuous route from the second openings 52 to the exhaust ports 30 and thereby act as demister devices. A third baffle 61 in the form a horizontal circular flat plate ring is affixed to the outer diameter of the downcomer tube 44 inside the upper chamber 24. The baffle 61 is spaced beneath the top plate 54 and spaced within several inches above the second horizontal baffle 50. Preferably, the baffle 61 extends radially to the radial extent of the second openings 52 between the middle and upper chambers. The baffle 61 is preferably arranged to provide additional tortuous flow path to help mitigate carryover of liquid droplets into the air exhaust pathway. Of course, any number of arrangements of baffles, tortuous pathways, screens and/or other devices that can act to collect fluids and contaminants carried by the exhaust air can be used as would be apparent to a person of ordinary skill in the art.
The air supply downcomer 44, when functionally connected with the air pump 16, defines an end of the portion of the air supply conduit 18. Preferably, the downcomer 44 is disposed within the confines of the lower chamber 26 so that the open end 32a of the discharge outlet 32 is disposed below the top surface 20 of the effluent 12 and spaced vertically between the open bottom end 28 of the first annular wall 26a and the top end of the lower chamber 26 when the fluid evaporator 14 is in the operative position. Preferably, each of the slits forming the sparge ports 32b is identical, positioned above the open end 32a, and symmetrically spaced from each other around the circumference of the wall of downcomer 44 to aid in dispersing air uniformly into the effluent 12 within the annular space 26 when the fluid evaporator 14 is in the operable position.
The fluid evaporator 14 optionally includes means for causing the vessel to float at the top surface of the reservoir. One flotation means may include the plenum 56 in the upper chamber 24 as described previously. Another flotation means includes one or more buoyant flotation devices 62 that are attached to the vessel or other portions of the fluid evaporator. The buoyant flotation devices may be foam structures, enclosed air bladders, hollow fully enclosed air tanks, wood blocks, or other buoyant structures suitable to cause the fluid evaporator to float in the operative position. In a preferred arrangement, the flotation means causes the vessel 22 to float in the operative position with the top level 20 of the effluent extending between the upper and lower chambers 24, 26, and more preferably through a middle elevation of the middle chamber 42. Thus, one possible arrangement of the flotation devices 62 may include foam blocks or rings attached to the exterior of the vessel 22, for example on the outside of the second annular wall 42a. Of course, the exact location of the flotation devices 62 will vary depending on the type of flotation device, weight of the fluid evaporator 14, type of effluent 12, and so on. Preferably the flotation devices 62 are attached to the vessel or other portions of the fluid evaporator so as to be adjustable up and down in the vertical plane to allow adjustment of operable height of the fluid evaporator 14, which is especially desirable to accommodate variances in the specific gravity of effluent 12.
The fluid evaporator 14 optionally also includes the fluid discharge conduit 34 in the form of one or more discharge pipes, shown in
In use, the air pump 16 forces air through the air supply conduit 18 via the downcomer 44 into effluent in the lower chamber 26 of the fluid evaporator 14 when operatively positioned at the top surface 20 of the reservoir. Preferably, the fluid evaporator 14 is operatively positioned by floating on the top surface 20 of the reservoir and anchoring the discharge riser 34c to the bottom of the reservoir with the anchors 38. The air is discharged through the sparge ports 32b creating a region of low density fluid confined within annular space 26 and beneath the top surface 20 of effluent 12 in the reservoir, which causes an upwelling of effluent 12 into the annular space 26 forming a two-phase mixture of air and effluent 12 that is thoroughly mixed as the heavy density liquid effluent 12 phase overruns the highly immiscible low density gaseous phase creating turbulence and resultant shearing forces that break the gas phase into small bubbles. Small bubbles created in this process create greatly expanded interfacial surface area between the continuous liquid effluent 12 phase and the discontinuous gas phase and thereby promote rapid heat and mass transfer between the phases including water vapor transfer to the gas phase and transfer of components of the air stream including oxygen to the effluent 12. The air and effluent mixture then rises rapidly upward through the first opening 48 in the first baffle 46 and rises to a level above the top surface 20 of the effluent in the reservoir due to momentum gained by the upwelling of liquid into, and combined turbulent flow of air and effluent 12 mixture through, chamber 26 and into middle chamber 24. Once released from the confines of chamber 26, shear forces between effluent 12 and air are greatly reduced causing rapid separation of effluent 12 and air under the force of gravity. Under the influence of gravity effluent 12 flows radially outward towards the third annular wall 23a and downwards toward the top surface 20 of the effluent in the reservoir. As the aerated effluent spreads horizontally, moist exhaust air escapes upwardly from the top surface of effluent within chamber 26 that has now been elevated above the top surface 20 of effluent 12 within the reservoir and travels through the second openings 52 and along the exhaust pathway A to the exhaust ports 30. As previously described, effluent droplets and contaminants carried by the exhaust air are separated from the exhaust air by the surfaces of the exhaust pathway A and the various baffles 50, 58, 60, and 61 before the exhaust air is discharged through the exhaust ports 30. Simultaneously, as the level of effluent within the middle chamber 42 rises above the operable condition level of effluent 20, gravity forces effluent to flow from the middle chamber 42 downwardly through the discharge pipes 34a, 34b and the discharge riser 34c back into the reservoir. If the system includes one or more of the solar thermal energy collectors 40, the vessel 22 may be heated and/or the air may be heated upstream from the fluid evaporator 14 by the solar thermal energy collectors to improve the rate of evaporation of fluid in the vessel.
Functionally separating the inlets 64 of the discharge pipes 34a, 34b from the annular space where aeration occurs within the weir formed by the first annular wall 26a provides distinct advantages. This arrangement provides a confined space for high turbulence mixing of the air and effluent within the lower chamber 26, thus increasing the surface-to-volume ratio of air-water interface to increase the rate of evaporation. Simultaneously, this arrangement provides increased surface area at the top of the aerated effluent within chamber 26 that has been elevated above the top surface 20 of the effluent 12 in the reservoir for separation of the exhaust air from the effluent as the aerated effluent travels horizontally over the weir and radially outwardly before the aerated effluent is discharged back into the reservoir through the discharge pipes 34a, 34b.
In one preferred exemplary arrangement, the fluid evaporator 14 is fabricated almost entirely from plastics such as high density polyethylene, polyvinyl chloride and other suitable plastic assemblies and tube sections. The upper chamber 24 is approximately five feet (1.5 m) in diameter and the vessel 22 is approximately six feet (1.8 m) tall. Each of the openings 52 through the second baffle 52 is four inches (10 cm) in diameter, each exhaust port 30 is three inches (7.5 cm) in diameter, and each discharge pipe 34a, 34b is six inches (15 cm) in diameter. Of course, the fluid evaporator 14 may have other dimensions and be formed of any materials suitable for functioning in the manner described herein.
According to another option, the air forced through the air supply conduit 18 is heated with exhaust heat from an internal combustion engine 70, such as a diesel or gas powered engine that either directly drives the air pump 16 or that drives an electrical generator that drives an electric motor that drives the air pump 16. In one contemplated arrangement, the exhaust heat is injected into the air supply conduit 18 immediately downstream of the air pump 16. Preferably, an exhaust duct 72 functionally connects exhaust from the engine 70 to the air supply conduit 18 at a junction fitting 74 adapted to rapidly mix the hot exhaust with the air from the air pump 16 and cool the exhaust to a temperature that will not be harmful to the material of the air supply conduit 18. This is particularly important where the air supply conduit is formed of materials that do not resist high temperatures well, such as PVC or other plastics. A preferred fitting 74 is an eductor as shown in
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Turning now to
Turning now to
The stabilization system 110 is provided on the fluid evaporator 14″ to help stabilize the fluid evaporator 14″ in the upright position, i.e., with the axis Z aligned generally vertically, the lower chamber 26 disposed in the water, and the top plate 54 disposed above the water, on the top surface of the water during operation, i.e., while air is being forced through the air supply downcomer 44 into the lower chamber 26. The stabilization system 110 includes one or more floatation devices 112 operatively secured to the vessel 22 by, for example, one or more outriggers 114. Preferably, the position of the floatation devices 112 may be adjusted axially and/or radially to, for example, cause the vessel 22 to sit higher or lower in the water. In the depicted arrangement, the stabilization system 110 includes two flotation devices 112, each having the form of an elongate enclosed hollow tube, such as a 7′ long by 6″ diameter PVC pipe with enclosed ends, disposed diametrically opposite each other on opposite sides of the vessel 22. Each flotation device 112 is spaced radially from the outer annular periphery of the vessel and sized to provide sufficient buoyancy to hold the upper chamber 24 spaced above the top surface of the water in selected arrangements. In one arrangement, each flotation device 112 has a length that is longer than the diameter of the upper chamber 24, but other size devices may also be adequate. The flotation devices 112 are connected to two outriggers 114, which are shown in the form of two struts 114a and 114b, such as metal tubes, bars, or angle irons, arranged in parallel on opposite sides of the downcomer 44, and connected to the top plate 54 by welds or fasteners, for example. Each strut 114a, 114b extends outwardly from opposite sides of the outer annular periphery of the upper chamber 24, and each flotation device 112 is attached to the struts, for example with fasteners 116 such as bolts or cables near the end of the strut. Each strut 114a, 114b preferably includes a hinge 118a, 118b, 118c, 118d spaced from the outer annular periphery of the upper chamber 24 and arranged to allow the flotation devices 112 to be selectively raised and/or lowered by pivoting the ends of the struts 114a and 114b around the respective hinges. The flotation devices 112 are preferably disposed spaced along an axis X defined by the air supply conduit 18 over the top plate 54 approaching the downcomer 44, such as may defined by a horizontal portion 44a of an elbow connector that connects the air supply conduit 18 to the downcomer 44. Further, each flotation device 112 is preferably axially aligned substantially perpendicular to the axis X in a generally horizontal plane perpendicular to the axis Z. In one arrangement, the axis X is substantially perpendicular to and extends through the axis Z. In this arrangement, the flotation devices 112 may be particularly well arranged to counteract rotational forces that act to tip the vessel 22 off of substantially vertical alignment in response to air being forced through the air supply conduit 118 and into the downcomer 44. Preferably, the ends of the struts 114a, 114b are arranged to be locked in any one of multiple or infinite selected angular orientations by a lock, such as a bolt, pin, and/or clamp, to releasably lock the flotation devices at a selected height along the axis Z. Thus, the height of the flotation devices 112 may be easily adjusted to maintain the fluid evaporator 14″ at a desired vertical position at the top surface of the water, such as to maintain the exhaust ports 30 approximately 1″-2″ (2.5 cm-5 cm) above the top surface of the water, and thereby compensate, for example, for fluids having different densities and/or other variations, such as changes in weight loads. The stabilization system 110 is not limited to the particular arrangement depicted in the drawings, and may take other forms capable of counteracting tipping forces and/or providing for adjustable depth control, for example with a complete or partial ring-shaped flotation device surrounding the vessel 22 that may be moved up and/or down along the axis Z and radially in and/or out from the outer annular periphery of the upper chamber 24. The stabilization system 110 is not limited to use with only the fluid evaporator 14″ and may be used with other fluid evaporators according to the principles of the present disclosure. In some arrangements, the stabilization system 110 is combined with the fluid evaporators 14 and 14′ in a manner consistent with the present disclosure.
The fluid evaporators 14, 14′, and 14″, and the reservoir evaporation systems 10, 100 may be manufactured in any suitable manner apparent to a person of ordinary skill. In preferred arrangements, components of the fluid evaporators are formed of HDPE, PVC and/or metal and connected with fasteners, welds, and/or adhesives, for example. However, the fluid evaporators 14, 14′, and 14″ are not limited to any particular material or construction technique.
The reservoir evaporation systems 10, 100 and the fluid evaporators 14, 14′, and 14″ as disclosed herein are particularly advantageous for use in arid climates, wherein the air injected into the fluid evaporator is very dry and more readily evaporates the fluid from the effluent. Further, the fluid evaporator 14 of the present disclosure provide a nearly maintenance-free design because there are no moving parts in the fluid evaporator that may need to be repaired or regularly cleaned and the turbulent flow paths within the chambers provide scouring and cleaning effects when the pond evaporator is operating. The design is further simplified by having all or most of the moving parts confined to the air pump 16 and any power supply drive means for the air pump, which can be easily accessed when located at the side of the reservoir. Because the fluid evaporator 14 is a single-pass system and high turbulence is maintained within the internal passages of the vessel 22, buildup of scale on the various parts and the frequency at which the parts would need to be cleaned is minimized. By eliminating high pressure pneumatic lines and/or high pressure water lines, a minimum of instrumentation is required as compared to systems that utilize high pressure lines.
Fluid evaporators, aerators, and mixers in accordance with any one or more of the principles disclosed herein in some arrangements may be applied to any combination of these unit operations within, for example, ponds or tanks, for purposes such as reducing the volume of water or wastewater through evaporation, humidifying gases and gas mixtures such as air, dissolving air in water to prevent water or wastewater from turning septic, providing air and oxygen to support aquaculture or to reduce chemical oxygen demand, and/or mixing desirable materials with water or wastewater. For example, fluid evaporators and systems of the present disclosure are in some arrangements useful for simple aeration of ponds to prevent anaerobic effects, oxygenation of fish and shell fish farm ponds, aeration and evaporation of livestock wastewater ponds, evaporation of ponds used for oil and gas field waters, aeration of ponds at golf courses, and aeration and/or evaporation of many other types of fluid reservoirs.
Number | Name | Date | Kind |
---|---|---|---|
2372846 | Frederick et al. | Apr 1945 | A |
2387818 | Wethly | Oct 1945 | A |
2468455 | Metziger | Apr 1949 | A |
2560226 | Joos et al. | Jul 1951 | A |
2619421 | Greenfield | Nov 1952 | A |
2651647 | Greenfield | Sep 1953 | A |
2658349 | Keller | Nov 1953 | A |
2658735 | Ybarrondo | Nov 1953 | A |
2721065 | Ingram | Oct 1955 | A |
2790506 | Vactor | Apr 1957 | A |
2867972 | Hokderreed et al. | Jan 1959 | A |
2879838 | Flynt et al. | Mar 1959 | A |
2890166 | Heinze | Jun 1959 | A |
2911421 | Greenfield | Nov 1959 | A |
2911423 | Greenfield | Nov 1959 | A |
2979408 | Greenfield | Apr 1961 | A |
2981250 | Steward | Apr 1961 | A |
3060921 | Luring et al. | Oct 1962 | A |
3076715 | Greenfield | Feb 1963 | A |
3203875 | Harris | Aug 1965 | A |
3204861 | Brown | Sep 1965 | A |
3211538 | Gross et al. | Oct 1965 | A |
3212235 | Markant | Oct 1965 | A |
3212559 | Williamson | Oct 1965 | A |
3251398 | Greenfield | May 1966 | A |
3268443 | Cann | Aug 1966 | A |
3284064 | Kolm et al. | Nov 1966 | A |
3299651 | McGrath | Jan 1967 | A |
3304991 | Greenfield | Feb 1967 | A |
3306039 | Peterson | Feb 1967 | A |
3323575 | Greenfield | Jun 1967 | A |
3405918 | Calaceto et al. | Oct 1968 | A |
3432399 | Schutt | Mar 1969 | A |
3539549 | Greenfield | Nov 1970 | A |
3578892 | Wilkinson | May 1971 | A |
3601374 | Wheeler | Aug 1971 | A |
3638924 | Calaceto et al. | Feb 1972 | A |
3704570 | Gardenier | Dec 1972 | A |
3713786 | Umstead | Jan 1973 | A |
3716458 | Greenfield et al. | Feb 1973 | A |
3730673 | Straitz, III | May 1973 | A |
3743483 | Shah | Jul 1973 | A |
3754869 | Van Raden | Aug 1973 | A |
3756580 | Dunn | Sep 1973 | A |
3756893 | Smith | Sep 1973 | A |
3762893 | Larsen | Oct 1973 | A |
3782300 | White et al. | Jan 1974 | A |
3789902 | Shah et al. | Feb 1974 | A |
3826096 | Hrusch | Jul 1974 | A |
3838974 | Hemsath et al. | Oct 1974 | A |
3838975 | Tabak | Oct 1974 | A |
3840002 | Douglas et al. | Oct 1974 | A |
3855079 | Greenfield et al. | Dec 1974 | A |
3870585 | Kearns et al. | Mar 1975 | A |
3876490 | Tsuruta | Apr 1975 | A |
3880756 | Raineri et al. | Apr 1975 | A |
3898134 | Greenfield et al. | Aug 1975 | A |
3901643 | Reed et al. | Aug 1975 | A |
3915620 | Reed | Oct 1975 | A |
3917508 | Greenfield et al. | Nov 1975 | A |
3925148 | Erwin | Dec 1975 | A |
3944215 | Beck | Mar 1976 | A |
3945331 | Drake et al. | Mar 1976 | A |
3947215 | Peterson et al. | Mar 1976 | A |
3947327 | Greenfield et al. | Mar 1976 | A |
3950230 | Greenfield et al. | Apr 1976 | A |
3994671 | Straitz, III | Nov 1976 | A |
4001077 | Kemper | Jan 1977 | A |
4007094 | Greenfield et al. | Feb 1977 | A |
4012191 | Lisankie et al. | Mar 1977 | A |
4013516 | Greenfield et al. | Mar 1977 | A |
4026682 | Pausch | May 1977 | A |
4036576 | McCracken | Jul 1977 | A |
4070423 | Pierce | Jan 1978 | A |
4079585 | Helleur | Mar 1978 | A |
4080883 | Zink et al. | Mar 1978 | A |
4092908 | Straitz, III | Jun 1978 | A |
4118173 | Shakiba | Oct 1978 | A |
4119538 | Yamauchi et al. | Oct 1978 | A |
4140471 | Straitz, III et al. | Feb 1979 | A |
4154570 | Schwartz | May 1979 | A |
4157239 | Reed | Jun 1979 | A |
4181173 | Pringle | Jan 1980 | A |
4185685 | Giberson | Jan 1980 | A |
4198198 | Straitz, III | Apr 1980 | A |
4227897 | Reed | Oct 1980 | A |
4230536 | Sech | Oct 1980 | A |
4257746 | Wells | Mar 1981 | A |
4259185 | Mixon | Mar 1981 | A |
4264826 | Ullmann | Apr 1981 | A |
4270974 | Greenfield et al. | Jun 1981 | A |
4276115 | Greenfield et al. | Jun 1981 | A |
4285578 | Yamashita et al. | Aug 1981 | A |
4300924 | Coyle | Nov 1981 | A |
4306858 | Simon | Dec 1981 | A |
4336101 | Greenfield et al. | Jun 1982 | A |
4346660 | McGill | Aug 1982 | A |
RE31185 | Greenfield et al. | Mar 1983 | E |
4430046 | Cirrito | Feb 1984 | A |
4432914 | Schifftner | Feb 1984 | A |
4440098 | Adams | Apr 1984 | A |
4445464 | Gerstmann et al. | May 1984 | A |
4445842 | Syska | May 1984 | A |
4450901 | Janssen | May 1984 | A |
4485746 | Erlandsson | Dec 1984 | A |
4496314 | Clarke | Jan 1985 | A |
4518458 | Greenfield et al. | May 1985 | A |
4538982 | McGill et al. | Sep 1985 | A |
4583936 | Krieger | Apr 1986 | A |
4608120 | Greenfield et al. | Aug 1986 | A |
4613409 | Volland | Sep 1986 | A |
4648973 | Hultholm et al. | Mar 1987 | A |
4652233 | Hamazaki et al. | Mar 1987 | A |
4658736 | Walter | Apr 1987 | A |
4683062 | Krovak et al. | Jul 1987 | A |
4689156 | Zibrida | Aug 1987 | A |
4693304 | Volland | Sep 1987 | A |
4771708 | Douglass, Jr. | Sep 1988 | A |
4863644 | Harrington et al. | Sep 1989 | A |
4882009 | Santoleri et al. | Nov 1989 | A |
4890672 | Hall | Jan 1990 | A |
4909730 | Roussakis et al. | Mar 1990 | A |
4913065 | Hemsath | Apr 1990 | A |
4938899 | Oros et al. | Jul 1990 | A |
4952137 | Schwartz et al. | Aug 1990 | A |
4961703 | Morgan | Oct 1990 | A |
5009511 | Sarko et al. | Apr 1991 | A |
5028298 | Baba et al. | Jul 1991 | A |
5030428 | Dorr et al. | Jul 1991 | A |
5032230 | Shepherd | Jul 1991 | A |
5068092 | Aschauer | Nov 1991 | A |
5076895 | Greenfield et al. | Dec 1991 | A |
5132090 | Volland | Jul 1992 | A |
5154898 | Ajinkya et al. | Oct 1992 | A |
5176798 | Rodden | Jan 1993 | A |
5183563 | Rodden | Feb 1993 | A |
5227017 | Tanaka et al. | Jul 1993 | A |
5238580 | Singhvi | Aug 1993 | A |
5279356 | Bruhn | Jan 1994 | A |
5279646 | Schwab | Jan 1994 | A |
5336284 | Schifftner | Aug 1994 | A |
5342482 | Duesel, Jr. | Aug 1994 | A |
D350838 | Johnson | Sep 1994 | S |
5347958 | Gordon, Jr. | Sep 1994 | A |
5423979 | Allen | Jun 1995 | A |
5460511 | Grahn | Oct 1995 | A |
5484471 | Schwab | Jan 1996 | A |
5512085 | Schwab | Apr 1996 | A |
5527984 | Stultz et al. | Jun 1996 | A |
5585005 | Smith et al. | Dec 1996 | A |
5630913 | Tajer-Ardebili | May 1997 | A |
5632864 | Enneper | May 1997 | A |
5636623 | Panz et al. | Jun 1997 | A |
5648048 | Kuroda et al. | Jul 1997 | A |
5656155 | Norcross et al. | Aug 1997 | A |
5662802 | Heins et al. | Sep 1997 | A |
5695614 | Hording et al. | Dec 1997 | A |
5695643 | Brandt et al. | Dec 1997 | A |
5735680 | Henkelmann | Apr 1998 | A |
5749719 | Rajewski | May 1998 | A |
5759233 | Schwab | Jun 1998 | A |
5810578 | Hystad et al. | Sep 1998 | A |
5865618 | Hiebert | Feb 1999 | A |
5879563 | Garbutt | Mar 1999 | A |
5925223 | Simpson et al. | Jul 1999 | A |
5934207 | Echols et al. | Aug 1999 | A |
5951743 | Hsieh et al. | Sep 1999 | A |
5958110 | Harris et al. | Sep 1999 | A |
5968320 | Sprague | Oct 1999 | A |
5968352 | Ditzler | Oct 1999 | A |
6007055 | Schifftner | Dec 1999 | A |
6119458 | Harris et al. | Sep 2000 | A |
6149137 | Johnson et al. | Nov 2000 | A |
6250916 | Philippe et al. | Jun 2001 | B1 |
6276872 | Schmitt | Aug 2001 | B1 |
6293277 | Panz et al. | Sep 2001 | B1 |
6332949 | Beckhaus et al. | Dec 2001 | B1 |
6345495 | Cummings | Feb 2002 | B1 |
6383260 | Schwab | May 2002 | B1 |
6391100 | Hogan | May 2002 | B1 |
6391149 | Calfee et al. | May 2002 | B1 |
6394428 | Hinada et al. | May 2002 | B2 |
6402816 | Trivett et al. | Jun 2002 | B1 |
6435860 | Brookshire et al. | Aug 2002 | B1 |
6468389 | Harris et al. | Oct 2002 | B1 |
6485548 | Hogan | Nov 2002 | B1 |
6500216 | Takayasu | Dec 2002 | B1 |
6616733 | Pellegrin | Sep 2003 | B1 |
6632083 | Bussman et al. | Oct 2003 | B1 |
6719829 | Schwab | Apr 2004 | B1 |
6733636 | Heins | May 2004 | B1 |
6742337 | Hays et al. | Jun 2004 | B1 |
6752920 | Harris et al. | Jun 2004 | B2 |
6913671 | Bolton et al. | Jul 2005 | B2 |
6919000 | Klausner et al. | Jul 2005 | B2 |
6926757 | Kalliokoski et al. | Aug 2005 | B2 |
6936140 | Paxton et al. | Aug 2005 | B2 |
7037434 | Myers et al. | May 2006 | B2 |
7069991 | Gudmestad et al. | Jul 2006 | B2 |
7073337 | Mangin | Jul 2006 | B2 |
7074339 | Mims | Jul 2006 | B1 |
7077201 | Heins | Jul 2006 | B2 |
7111673 | Hugill | Sep 2006 | B2 |
7142298 | Nuspliger | Nov 2006 | B2 |
7144555 | Squires et al. | Dec 2006 | B1 |
7150320 | Heins | Dec 2006 | B2 |
7156985 | Frisch | Jan 2007 | B1 |
7166188 | Kedem et al. | Jan 2007 | B2 |
7225620 | Klausner et al. | Jun 2007 | B2 |
7288186 | Harris | Oct 2007 | B2 |
7332010 | Steiner | Feb 2008 | B2 |
7402247 | Sutton | Jul 2008 | B2 |
7416172 | Duesel et al. | Aug 2008 | B2 |
7416177 | Suzuki et al. | Aug 2008 | B2 |
7424999 | Xu et al. | Sep 2008 | B2 |
7428926 | Heins | Sep 2008 | B2 |
7438129 | Heins | Oct 2008 | B2 |
7442035 | Duesel, Jr. et al. | Oct 2008 | B2 |
7459135 | Pieterse et al. | Dec 2008 | B2 |
7572626 | Frisch et al. | Aug 2009 | B2 |
7591309 | Minnich et al. | Sep 2009 | B2 |
7614367 | Frick | Nov 2009 | B1 |
7661662 | Forstmanis | Feb 2010 | B2 |
7681643 | Heins | Mar 2010 | B2 |
7717174 | Heins | May 2010 | B2 |
7758819 | Nagelhout | Jul 2010 | B2 |
7832714 | Duesel, Jr. et al. | Nov 2010 | B2 |
7955419 | Casella | Jun 2011 | B2 |
8066845 | Duesel, Jr. et al. | Nov 2011 | B2 |
8114287 | Harris | Feb 2012 | B2 |
8136797 | Duesel et al. | Mar 2012 | B2 |
8585869 | Duesel et al. | Nov 2013 | B1 |
20010013666 | Nomura et al. | Aug 2001 | A1 |
20020069838 | Rautenbach et al. | Jun 2002 | A1 |
20030104778 | Liu | Jun 2003 | A1 |
20030127226 | Heins | Jul 2003 | A1 |
20040000515 | Harris et al. | Jan 2004 | A1 |
20040031424 | Pope | Feb 2004 | A1 |
20040040671 | Duesel et al. | Mar 2004 | A1 |
20040045681 | Bolton et al. | Mar 2004 | A1 |
20040045682 | Liprie | Mar 2004 | A1 |
20040079491 | Harris et al. | Apr 2004 | A1 |
20050022989 | Heins | Feb 2005 | A1 |
20050074712 | Brookshire et al. | Apr 2005 | A1 |
20050230238 | Klausner et al. | Oct 2005 | A1 |
20050242036 | Harris | Nov 2005 | A1 |
20050279500 | Heins | Dec 2005 | A1 |
20060000355 | Ogura et al. | Jan 2006 | A1 |
20060032630 | Heins | Feb 2006 | A1 |
20070051513 | Heins | Mar 2007 | A1 |
20070114683 | Duesel et al. | May 2007 | A1 |
20070175189 | Gomiciaga-Pereda et al. | Aug 2007 | A1 |
20070251650 | Duesel et al. | Nov 2007 | A1 |
20080110417 | Smith | May 2008 | A1 |
20080115361 | Santini et al. | May 2008 | A1 |
20080173176 | Duesel et al. | Jul 2008 | A1 |
20080173590 | Duesel et al. | Jul 2008 | A1 |
20080174033 | Duesel et al. | Jul 2008 | A1 |
20080213137 | Frisch et al. | Sep 2008 | A1 |
20080265446 | Duesel et al. | Oct 2008 | A1 |
20080272506 | Duesel et al. | Nov 2008 | A1 |
20080277262 | Harris | Nov 2008 | A1 |
20090078416 | Heins | Mar 2009 | A1 |
20090127091 | Heins | May 2009 | A1 |
20090294074 | Forstmanis | Dec 2009 | A1 |
20100095763 | Harris | Apr 2010 | A1 |
20100126931 | Capeau et al. | May 2010 | A1 |
20100139871 | Rasmussen et al. | Jun 2010 | A1 |
20100176042 | Duesel, Jr. et al. | Jul 2010 | A1 |
20100224364 | Heins | Sep 2010 | A1 |
20100236724 | Duesel, Jr. et al. | Sep 2010 | A1 |
20110147195 | Shapiro et al. | Jun 2011 | A1 |
20110168646 | Tafoya | Jul 2011 | A1 |
20110180470 | Harris | Jul 2011 | A1 |
20110240540 | Harris | Oct 2011 | A1 |
20110303367 | Panz et al. | Dec 2011 | A1 |
20120211441 | Harris | Aug 2012 | A1 |
20130233697 | Bryant | Sep 2013 | A1 |
Number | Date | Country |
---|---|---|
757-2004 | May 2007 | CL |
556 455 | Aug 1932 | DE |
1 173 429 | Jul 1964 | DE |
0 047 044 | Mar 1982 | EP |
2 441 817 | Jun 1980 | FR |
383570 | Nov 1932 | GB |
463770 | Apr 1937 | GB |
60257801 | Dec 1985 | JP |
62121687 | Jun 1987 | JP |
2003021471 | Jan 2003 | JP |
WO-9610544 | Apr 1996 | WO |
WO-2004022487 | Mar 2004 | WO |
WO-2005110608 | Nov 2005 | WO |
WO-2008112793 | Sep 2008 | WO |
WO-2009071763 | Jun 2009 | WO |
WO-2010092265 | Aug 2010 | WO |
WO-2011042693 | Apr 2011 | WO |
WO-2011050317 | Apr 2011 | WO |
WO-2012100074 | Jul 2012 | WO |
Entry |
---|
“Gas Atomized Venturi Scrubbers,” Bionomic Industries, copyright 2008, printed from www.bionomicind.com <http://www.bionomicind.com> on May 25, 2011. |
“Waste Heat Recovery Systems,” Bionomic Industries, copyright 2008, printed from www.bionomicind.com <http://www.bionomicind.com> on May 25, 2011. |
Alabovskij et al., “Concentration of Boiler Washing Water in Submerged-Combustion Devices,” Promyshl. Energet, 4:38-39 (1975). English-language abstract only. |
Bachand et al., “Denitrification In Constructed Free-Water Surface Wetlands: II. Effects of Vegetation and Temperature,” Ecological Engineering, 14:17-32 (2000). |
Barrett et al., “The Industrial Potential and Economic Viability of Spouted Bed Processes,” Chemeca 85, paper D4c, The Thirteenth Australasian Conference on Chemical Engineering, Perth, Australia, pp. 401-405 (1985). |
Bennett et al., “Design of A Software Application for the Simulation and Control of Continuous and Batch Crystallizer Circuits,” Advances in Engineering Software, 33:365-374 (2002). |
Berg, “The Development of the Controlled Buoyancy System for Installation of Submerged Pipelines,” Journal AWWA, Water Technology/Quality, pp. 214-218 (1977). |
Brandt et al., “Treatment Process for Waste Water Disposal of the “Morcinek” Mine Using Coalbed Methane,” Conference on Coalbed Methane Utilization, Oct. 5-7 (1994). |
Cherednichenko et al., “Disposal of Saline Wastes From Petroleum Refineries, All-Union Scientific-Research and Planning-Design Institute of the Petroleum Refining and Petrochemical Industry,” Khimiya I Tekhnologiya Topliv I Masel, 9:37-39 (1974). Translated. |
Claflin et al., “The Use of Spouted Beds for the Heat Treatment of Grains,” Chemeca 81, The 9th Australasian Conference on Chemical Engineering, Christchurch, New Zealand, 4:65-72 (1981). |
Claflin, “Intraparticle Conduction Effects on the Temperature Profiles in Spouted Beds,” Chemeca 85, paper D9b, The Thirteenth Australasian Conference on Chemical Engineering, Perth, Australia, pp. 471-475 (1985). |
Cross et al., “Leachate Evaporation by Using Landfill Gas,” Proceedings Sardinia 97, Sixth Landfill Symposium, S. Margherita di Pula, Cagliari, Italy, pp. 413-422 (1997). |
Dunn, “Incineration's Role in Ultimate Disposal of Process Wastes,” Chemical Engineering, Deskbook Issue, pp. 141-150 (1975). |
Durkee et al., “Field Tests of Salt Recovery System for Spent Pickle Brine,” Journal of Food Service, 38:507-511 (1973). |
English translation of Chinese First Office Action for Application No. 201080012067.7, dated Oct. 12, 2012. |
English translation of Chinese Search Report for Application No. 201080012067.7, dated Sep. 12, 2012. |
English-language translation of Hage, H., “The MeMon Experiment: A Step towards Large-Scale Processing of Manure,” Applied Science, 4 (1988). |
Etzensperger et al., “Phenol Degradation In A Three-Phase Biofilm Fluidized Sand Bed Reactor,” Bioprocess Engineering, 4:175-181 (1989). |
EVRAS—Evaporative Reduction and Solidification Systems; Brochure for Web. Believed to be publically available as early as Mar. 5, 2010. |
Fan et al., “Some Remarks on Hydrodynamic Behavior of a Draft Tube Gas-Liquid-Solid Fluidized Bed,” AlChE Symposium Series, No. 234(80):91-97 (1985). |
Final Office Action for U.S. Appl. No. 11/625,002, dated May 26, 2010. |
Final Office Action for U.S. Appl. No. 11/625,022, dated Jan. 24, 2011. |
Final Office Action for U.S. Appl. No. 11/625,024, dated Dec. 8, 2010. |
Fox et al., “Control Mechanisms of Flulidized Solids Circulation Between Adjacent Vessels,” AlChE Journal, 35(12):1933-1941 (1989). |
Genck, “Guidelines for Crystallizer Selection and Operation,” CEP, pp. 26-32 (2004). www.cepmagazine.org. |
German Kurz, “Immersion Heater,” OI U. Gasfeuerung, 18(3):171-180 (1973). English-language abstract only. |
Hattori et al., “Fluid and Solids Flow Affecting the Solids Circulation Rate in Spouted Beds with a Draft Tube,” Journal of Chemical Engineering of Japan, 37(9):1085-1091 (2004). |
Hill et al., “Produced Water and Process heat Combined Provide Opportunities for Shell CO2”; EVRAS; Facilities 2000: Facilities Engineering in the Next Millennium. |
Hocevar et al., “The Influence of Draft-Tube Pressure Pulsations on the Cavitation-Vortex Dynamics in a Francis Turbine,” Journal of Mechanical Engineering, 49:484-498 (2003). |
International Preliminary Report on Patentability and Written Opinion issued for International Patent application No. PCT/US2011/021811, dated Aug. 14, 2012. |
International Preliminary Report on Patentability for Application No. PCT/US2006/015803, dated Nov. 13, 2007. |
International Preliminary Report on Patentability for Application No. PCT/US2006/028515, dated Jan. 22, 2008. |
International Preliminary Report on Patentability for Application No. PCT/US2007/001487, dated Jul. 21, 2009. |
International Preliminary Report on Patentability for Application No. PCT/US2007/001632, dated Jul. 21, 2009. |
International Preliminary Report on Patentability for Application No. PCT/US2007/001633, dated Jul. 21, 2009. |
International Preliminary Report on Patentability for Application No. PCT/US2007/001634, dated Jul. 21, 2009. |
International Preliminary Report on Patentability for Application No. PCT/US2008/056702, dated Sep. 15, 2009. |
International Preliminary Report on Patentability for Application No. PCT/US2010/043647, dated Feb. 9, 2012. |
International Preliminary Report on Patentability for Application No. PCT/US2010/043648, dated Feb. 9, 2012. |
International Search Report and Written Opinion for Application No. PCT/US08/56702, dated Jun. 10, 2008. |
International Search Report and Written Opinion for Application No. PCT/US10/043647, dated Apr. 27, 2011. |
International Search Report and Written Opinion for Application No. PCT/US10/043648, dated Apr. 27, 2011. |
International Search Report and Written Opinion for Application No. PCT/US2006/015803, dated Oct. 30, 2007. |
International Search Report and Written Opinion for Application No. PCT/US2010/024143, dated Oct. 12, 2010. |
International Search Report and Written Opinion for Application PCT/US2011/021811, dated Mar. 21, 2011. |
International Search Report for Application No. PCT/US2006/028515, dated Nov. 14, 2006. |
International Search Report for Application No. PCT/US2012/021897, dated Oct. 8, 2012. |
Intevras Technologies, LLC—Innovative solutions for water purification, remediation and process improvement; Power Point Presentation, Oct. 2009. |
Jones, “Liquid Circulation in a Draft-Tube Bubble Column,” Chemical Engineering Science, 40(3):449-462 (1985). |
Layne Evaporative Reduction and Solidification System Brochure (2010). |
MikroPul, “Wet Scrubbers,” (2009). www.mikropul.com. |
Miyake et al., “Performance Characteristics of High Speed-Type Cross Flow Turbine,” 83-0047:2575-2583 (1993). |
Mueller et al., “Rotating Disk Looks Promising for Plant Wastes,” (2007). |
Mussatti, Daniel, Section 6, Particulate Matter Controls. Chapter 2 Wet Scrubbers for Particulate Matter. Innovative Strategies and Economics Group. United States Environmental Protection Agency. Jul. 2002. |
Notice of Allowance for U.S. Appl. No. 11/625,159, dated Jul. 9, 2010. |
Office Action for U.S. Appl. No. 11/625,002, dated Jan. 6, 2010. |
Office Action for U.S. Appl. No. 11/625,022, dated Jun. 22, 2010. |
Office Action for U.S. Appl. No. 11/625,024, dated Jun. 18, 2010. |
Office Action for U.S. Appl. No. 11/625,024, dated Nov. 27, 2009. |
Office Action issued for U.S. Appl. No. 12/705,462, dated Nov. 6, 2012. |
Office Action issued for U.S. Appl. No. 12/846,257, dated Nov. 16, 2012. |
Padial et al., “Three-Dimensional Simulation of a Three-Phase Draft-Tube Bubble Column,” Chemical Engineering Science, 55:3261-3273 (2000). |
Rule 62 EPC Communication issued from the European Patent Office for Application No. 10741828.7, dated Jan. 31, 2013. |
Rule 62 EPC Communication issued from the European Patent Office for Application No. 10805026.1, dated Feb. 27, 2013. |
Rule 62 EPC Communication issued from the European Patent Office for Application No. 10805027.9, dated Feb. 5, 2013. |
Sathyanarayana et al., Circular C.W. Intake System—A Research Opinion, Seventh Technical Conference of the British Pump Manufacturer's Association, paper 21, pp. 293-313, 1981. |
Schone, “Oil Removal from Exhaust Steam and Condensate of Piston-Powered Steam Engines,” Braunkohle, 31:82-92 (1932). English-language abstract only. |
Screen shots from video on LFG website taken Jan. 18, 2011 (http://www.shawgrp.com/markets/envservices/envsolidwaste/swlfg). |
Shaw LFG Specialties, LCC “Waste Heat Leachate Evaporator System” (2011). |
Shaw LFG Specialties, LLC, 2006 Product Catalog. |
Shimizu et al., “Filtration Characteristics of Hollow Fiber Microfiltration Membranes Used in Membrane Bioreactor for Domestic Wastewater Treatment,” Wat. Res., 30(10):2385-2392 (1996). |
Smith, “Sludge-U-Like, As the Ban on Sea Disposal of Sewage Waste Looms, Technologies That Can Deliver Cleaner, Thicker and More Farmer-Friendly Sludges Are Gaining Popularity,” Water Bulletin, 708 (1996). |
St. Onge et al., “Start-Up, Testing, and Performance of the First Bulb-Type Hydroelectric Project in the U.S.A.,” IEEE Transactions on Power Apparatus Systems, PAS-101(6):1313-1321 (1982). |
Swaminathan et al., “Some Aerodynamic Aspects of Spouted Beds of Grains,” Department of Chemical Engineering, McGill University, Montreal, Quebec, Canada, pp. 197-204 (2007). |
Talbert et al., “The Elecrospouted Bed,” IEEE Transactions on Industry Applications, vol. 1 A-20, No. 5, pp. 1220-1223 (1984). |
U.S. Office Action for U.S. Appl. No. 12/530,484, dated Apr. 16, 2013. |
U.S. Office Action for U.S. Appl. No. 12/846,337, dated Apr. 17, 2013. |
Williams et al., “Aspects of Submerged Combustion As a Heat Exchange Method,” Trans IChemE, 71(A):308-309 (1993). |
Written Opinion for Application No. PCT/US2010/024143, dated Oct. 12, 2010. |
Written Opinion for Application No. PCT/US2012/021897, dated Sep. 28, 2012. |
Ye et al., “Removal and Distribution of Iron, Manganese, Cobalt, and Nickel Within A Pennsylvania Constructed Wetland Treating Coal Combustion By-Product Leachate,” J. Environ. Qual., 30:1464-1473 (2001). |
Yeh et al., “Double-Pass Heat or Mass Transfer Through A Parallel-Plate Channel with Recycle,” International Journal of Hat and Mass Transfer, 43:487-491 (2000). |
Yoshino et al., “Removal and Recovery of Phosphate and Ammonium as Struvite from Supernatant in Anaerobic Digestion,” Water Science and Technology, 48(1):171-178 (2003). |
U.S. Appl. No. 13/849,274, filed Mar. 22, 2013. |
Number | Date | Country | |
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20130248122 A1 | Sep 2013 | US |
Number | Date | Country | |
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61614601 | Mar 2012 | US |