The present disclosure or invention relates generally to new, improved, or modified membrane contactors, modules, systems, and/or methods for membrane distillation and/or ammonia removal, and/or methods of manufacture, use, and/or the like. In accordance with at least selected embodiments, the present invention relates to particular possibly preferred membrane contactors, modules, systems, and/or methods for membrane distillation and/or ammonia removal, and/or to particular possibly preferred membrane contactors, cartridges, modules, systems, and/or methods for membrane distillation and/or ammonia removal, involving membrane contactors adapted for membrane distillation, for ammonia removal, or for both membrane distillation and for ammonia removal, as well as other membrane contactor systems, methods or processes such as degassing, gasifying, separation, filtration, and/or the like.
A membrane contactor may be used for many purposes, including, but not limited to, removing entrained gases from liquids, debubbling liquids, filtering liquids, and adding a gas to a liquid. Membrane contactors are known to be used in many different applications; for example, a membrane contactor may be used in membrane distillation and/or ammonia removal. Membrane contactors also may provide a means of accomplishing gas/liquid, and liquid/liquid (which can encompass liquid/dissolved solid) separations. Membrane contactors typically are used to bring two immiscible fluid phases (for example, a first liquid and a second liquid, or a gas and a liquid) into contact with one another to effect separation and/or transfer of one or more components from one fluid to the other.
A hollow fiber membrane contactor typically includes a bundle of microporous hollow fibers and a rigid shell or housing enclosing the fiber bundle. The shell may be provided with four fluid ports: an inlet for introducing the first fluid, an outlet for discharging the first fluid, an inlet for introducing the second fluid, and an outlet for discharging the second fluid. The hollow fibers may be potted, for example, in epoxy or some similar material, on both ends, within the housing, to form polymeric tube sheets with the fiber bores opening on each end into common first and second end cap portions of the shell. In a “tube-side” or “lumen-side” contactor, the first end cap may contain the inlet for the first fluid, which is designated the “tube-side” or “lumen-side” fluid because it is the fluid that passes through the internal lumens of the fibers. The second end cap contains the outlet for discharging the lumen-side fluid. The second fluid, designated the “shell-side” fluid, typically enters and exits the housing through inlet and outlet ports arranged between the tube sheets, whereby the shell-side fluid contacts the external surfaces of the fibers. The shell-side fluid flows through the interstices between fibers of the fiber bundle and may be directed to flow parallel to or perpendicular to the fiber length. As an example, U.S. Pat. No. 5,352,361 to Prasad, et al., incorporated by reference herein in its entirety, may assist in a background understanding of fluid contact across hollow fiber membranes within a shell.
In a “shell-side” contactor, the contactor may include a central core which passes through the end caps and has a first end serving as the inlet for the first fluid, which is designated the “shell-side” fluid because it is the fluid that passes over the exterior or shell of the hollow fibers. The first end cap may contain the inlet for the second fluid, which is designated the “tube-side” or “lumen-side” fluid because it is the fluid that passes through the internal lumens of the fibers. The second end cap contains the outlet for discharging the lumen-side fluid. The first fluid, designated the “shell-side” fluid, typically enters and exits the housing through inlet and outlet ports (open ends) of the perforated core, and typically exits and re-enters the perforations in the core between the tube sheets whereby the shell-side fluid contacts the external surfaces of the fibers. The shell-side fluid flows through the interstices between fibers of the fiber bundle and may be directed to flow parallel to or perpendicular to the fiber length. Because the tube sheets separate the lumen-side fluid from the shell-side fluid, the lumen-side fluid does not mix with the shell-side fluid, and the only transfer between the lumen-side fluid and the shell-side fluid occurs through the walls of the hollow fibers. The fine pores in the fiber wall are normally filled with a stationary layer of one of the two fluids, the other fluid being excluded from the pores due to surface tension and/or pressure differential effects. Mass transfer and separation are usually caused by diffusion, which is typically driven by the difference in concentration of the transferring species between the two phases. Typically, no convective or bulk flow occurs across the membrane. In the case of gas/liquid separations, membrane contactors are typically fabricated with hydrophobic hollow fiber microporous membranes. Since the membranes are hydrophobic and have very small pores, liquid will not easily pass through the pores. As such, the membranes may act as an inert support that brings the liquid and gas phases into direct contact, without dispersion. The mass transfer between the two phases may be governed by the difference in partial pressure of the gas species being transferred. For liquid systems, the liquid/liquid interface at each pore is typically immobilized by the appropriate selection of membrane and liquid phase pressures. In this case, the membrane also may act as an inert support to facilitate direct contacting of two immiscible phases without mixing.
A new or improved liquid degassing membrane contactor or module was disclosed in U.S. Patent Publication No. 2012-0247337-A1 (application Ser. No. 13/247,213, now U.S. Pat. No. 8,449,659), which is incorporated herein by reference in its entirety, that allows for relatively small, modular, degassing modules. The modules disclosed in the 2012-0247337 publication may be used, for example, in industrial processes, at power plants, on offshore oil rigs or drilling platforms, to replace or augment vacuum towers, to provide the benefits of modularity and replaceable cartridges, reduce cost, reduce complexity, eliminate bolts or v-band clamps, and/or the like.
Membrane distillation, or osmotic distillation, is a separation process in which a liquid mixture containing a volatile component is contacted with a microporous, non-liquid-wettable membrane whose opposite surface is exposed to a second liquid phase capable of absorbing that volatile component. Membrane distillation may be used for many purposes, including, but not limited to, desalination, the concentration of beverages and other liquid foodstuffs, the concentration of aqueous solutions of thermally labile pharmaceutical products and biologicals, and/or the like. The primary advantages of membrane distillation may lie in the ability to concentrate solutes to very high levels at low temperature and pressure, with minimal thermal or mechanical damage to or loss of those solutes. The membrane distillation process also may enable the selective removal of a single volatile solute from an aqueous solution (for instance, ethanol from wine and other ferments) using water as the extracting solvent. Low-alcohol-content beverages can be produced in this manner with minimal losses of volatile flavor and fragrance components. Osmotic distillation (OD) may be an attractive complement or alternative to other athermal or low temperature separation techniques such as ultrafiltration (UF), reverse osmosis (RO), pervaporation, and/or vacuum freeze drying.
Ammonia is a prevalent problem in the wastewater of many industries. Because ammonia is widely used as a cleaning agent in many processes (by way of example only, the production of semiconductors or components to be used in the electronics industry), it may end up in plant wastewater and must be treated or removed from water prior to the water being discharged back into the environment. In various emerging markets around the globe, new environmental controls and/or regulations may come into being, which increases the need for effective and affordable systems for ammonia removal from fluids used in industrial processes. Membrane contactors may offer a desirable alternative for removing ammonia from wastewater in many industries, and some membrane contactors can remove up to 90%, even 95%, or more of the incoming ammonia. In addition, membrane contactors may extract ammonia from wastewater and convert it into a harmless ammonium salt, which may have some commercial value as a fertilizer. Ammonia removal systems may vary based on process parameters, and a given ammonia removal system may be sized based on the parameters of the desired application. Desirable process parameters for ammonia removal with membrane contactors may include, but are not limited to: NH3 inlet concentration >about 500 ppm; pre-filtration (filtering out materials before the ammonia removal process begins) of filtering out materials greater than about 10 μm, or greater than about 5 μm, in diameter; temperature of about 40-55° C.; feed stream pH>about 10; acid stream pH<about 2; and sulfuric acid as stripping media (about 96% by weight), as well as other like parameters, and combinations thereof.
Therefore, a need exists to develop new, improved, or modified contactors, modules, systems, and/or methods for membrane distillation and/or ammonia removal.
In accordance with at least certain embodiments, aspects or objects, the present invention addresses the above needs and provides such new, improved, or modified contactors, modules, systems, and/or methods for membrane distillation and/or ammonia removal.
The instant invention is directed toward various membrane contactors, modules, and/or systems, and their methods of manufacture and use. In at least selected embodiments, the present invention is directed to one or more membrane contactors, and/or a system, module or array of membrane contactors useful in the removal of ammonia from a fluid and/or in membrane distillation or osmotic distillation of a fluid. In accordance with at least selected embodiments, examples, or aspects, the present invention is directed to membrane distillation or osmotic distillation with the use of a particular possibly preferred membrane contactor or array of membrane contactor. In accordance with at least selected embodiments, examples, or aspects, the present invention is directed to ammonia removal with the use of a particular possibly preferred membrane contactor or array of membrane contactor.
In accordance with at least certain embodiments, the present disclosure or invention is directed to new, improved, or modified membrane contactors, modules, systems, and/or methods for membrane distillation and/or ammonia removal, and/or methods of manufacture, use, and/or the like. In accordance with at least selected embodiments, the present invention relates to particular possibly preferred membrane contactors, modules, systems, and/or methods for membrane distillation and/or ammonia removal, and/or to particular possibly preferred membrane contactors, cartridges, modules, systems, and/or methods for membrane distillation and/or ammonia removal, involving membrane contactors adapted for membrane distillation, for ammonia removal, or for both membrane distillation and ammonia removal, as well as to other membrane contactor systems, methods or processes such as degassing, gasifying, separation, filtration, and/or the like. In accordance with at least one particular embodiment, the same particular membrane contactor may be used for membrane distillation and for ammonia removal, and is adapted to operate in both membrane distillation and ammonia removal arrays, systems, methods or processes.
For the purpose of illustrating the embodiments, examples or aspects of the invention, there is shown in the drawings a form that is presently possibly preferred; it being understood, however, that the present invention is not limited to the precise embodiments, aspects, arrangements, and/or instrumentalities shown.
In accordance with at least selected embodiments, aspects or objects of the present invention, a possibly preferred membrane contactor for membrane distillation and/or ammonia removal may include at least one integrally potted hollow fiber membrane structure in a cylindrical housing with the ends of the membrane structure recessed in the housing a certain distance, by way of example only, a recess of at least 1″ from each end. The membrane contactor for membrane distillation and/or ammonia removal may also have respective disc, domed and/or other molded shaped end caps adapted to be received in each open end of the housing. In other embodiments, the membrane structure may be recessed in the housing a recess of, for example, at least 2″ from each end. The end caps each may have at least one of liquid and gas ports therein, and the end caps may be adapted to be held in place in the cylindrical housing by at least one retaining element. Such a retaining element may include, for example, a retaining or locking ring received in a groove in the interior of the cylindrical housing. The end caps each may have a central opening therein adapted to receive a liquid end port or nozzle, and another opening therein adapted to receive a gas (or a second liquid) end port or pipe. The integrally potted membrane structure may include a perforated core, a plurality of hollow fiber membranes, and a tube sheet or potting affixing each end of the hollow fibers and adhering to the interior of the housing. The integrally potted membrane structure may be potted in place in the housing by an inverted potting process involving the use of a removable plunger or plug and trimming the ends of the potting and opening the ends of the hollow fibers using a cutting means to produce recessed tube sheets. The length of pipe of the cylindrical housing may be formed of a modified section of pipe including in each end a larger diameter section for receiving an end cap, a groove for receiving a retaining ring, and a flared entrance for facilitating the insertion of the end cap and retaining ring. The length of pipe may be selected from standard PVC, ABS, polypropylene, steel, stainless steel, or other pipe material that will bond with epoxy to facilitate integral potting. Although integral potting may be preferred, one or more cartridges in a shell or housing may be used in a less preferred embodiment.
The above embodiment of a membrane contactor for membrane distillation and/or ammonia removal, or multiple membrane contactors, contactor array or system, may be used for membrane distillation. The above embodiment of a membrane contactor for membrane distillation and/or ammonia removal, or multiple membrane contactors, contactor array or system, may also be used for ammonia removal.
The instant invention of utilizing one or more membrane contactors for ammonia removal and/or membrane distillation may offer several advantages over other designs. Such advantages may include but are not limited to:
In other embodiments, one or more end caps of the membrane contactor (or any part of the membrane contactor that may be wetted, for example, with an acid-containing solution in an ammonia removal process) may be made from a fluoropolymer resin such as PTFE, to impart chemical resistance to the part(s). One example of a PTFE resin may be Teflon®, which is commercially available from DuPont. In other embodiments, one or more end caps (or other parts of the membrane contactor that may be wetted) may be made from silicone. In ammonia removal applications, such materials may be chosen to ensure, for example, chemical resistance or acid resistance for the part(s). This means that the membrane contactors, systems, and methods disclosed herein may overcome certain material limitations that may have existed for prior contactors, systems, or methods.
Referring to the drawings wherein like numerals indicate like elements, there is shown, in
Although it may be less preferred than the above, the module 100 may be adapted for adding one or more gases to the liquid, and the central end ports or nozzles 112, 114 may respectively be liquid ports to receive liquid to be treated or modified or to discharge the treated liquid, and ports or openings 124, 126 may be gas ports (or liquid ports) to respectively receive or remove carbon dioxide, nitrogen, and/or the like, to be connected to a gas source or pump, or the like, to facilitate the control or addition of a gas or gases.
Although it may be still less preferred than above, the module 100 may be adapted for controlling or adding humidity to a gas or air stream, and the end ports or nozzles 112, 114 may be liquid ports to receive water, and end ports or openings 124, 126 may be gas ports to respectively receive and remove sweep gas, strip gas, air, or the like, and/or for one or both to be connected to vacuum (to be connected to a vacuum source or pump) to facilitate the creation, addition, removal, and/or control of water vapor, humidity, or the like.
Although it may be yet less preferred than above, the end ports or nozzles 112, 114 may be gas ports, and end ports or openings 124, 126 may be liquid ports or gas ports.
The end ports 112, 114 may be liquid ports, and end ports 124, 126 may be liquid ports, or the end ports 112, 114 may be gas ports, and end ports 124, 126 may also be gas ports.
For at least certain applications, the arrangement may be a countercurrent flow of liquid and/or gas (possibly preferably countercurrent flow liquid 1 and liquid 2). For example, liquid may flow from port 112 to port 114 while gas (or a second liquid) flows from port 126 to port 124, or liquid may flow from port 114 to port 112 while gas (or a second liquid) flows from port 124 to port 126. For at least certain other applications, the preferred arrangement may be a common direction (co-current) flow of liquid and gas (or liquid 1 and liquid 2). For example, liquid may flow from port 112 to port 114 while gas (or a second liquid) flows from port 124 to port 126, or liquid may flow from port 114 to port 112 while gas (or a second liquid) flows from port 126 to port 124. For at least certain still other applications, the preferred arrangement may be flow of liquid from one liquid port to the other while gas is drawn out of both gas ports. For example, both gas ports 124 and 126 may be connected to vacuum (such as to a vacuum pump). For at least certain yet other applications, the preferred arrangement may be flow of liquid from one liquid port to the other while gas is forced into both gas ports. For example, both gas ports 124 and 126 may be connected to a source or supply of gas to be introduced into the liquid (such as for carbonation, nitrogenation, or the like).
Many industries have the need to remove, add or control dissolved gasses in liquids. Module or contactor 100 and similar membrane contactors as shown and described herein can be used in such industries where gasses need to be removed, controlled or added. In other words, there are many membrane degassing and gas transfer applications where the present liquid degasifiers could be used. Furthermore, many industries have the need to remove ammonia from various liquids, and many industries have the need to effect membrane distillation or osmotic distillation.
With reference to
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Preferably, housing or shell 110 of module 100 has an elongated constant diameter central opening portion 132 and enlarged diameter end portions 162, 164 (see
Further, nozzles 112, 114 are locked in position in the openings 136 in end caps 116, 118 by retaining or locking rings or clips 186, 188 received in respective grooves 187 in nozzles 112, 114.
As described above, the preferred module 100 has a very simple yet very effective construction. The shell side fluid or liquid is separated from the lumen side fluid or gas (except at the membrane interface). Preferably, standard materials and parts are used where possible. For example, standard o-rings and locking rings are used together with custom or modified parts such as the housing, end caps, nozzles, and center tubes. Depending on the module end use or application, different end ports, nozzles, side ports, and/or openings may need to be used.
In certain embodiments, one or more o-rings may be made from an elastomer or a rubber. For example, one or more o-rings may be made from EPDM rubber (ethylene propylene diene monomer rubber). In other embodiments, one or more o-rings may be made from a fluoroelastomer, such as a Viton® fluoroelastomer resin commercially available from DuPont. Such a fluoroelastomer may be used, for example, in applications for ammonia removal where chemical resistance is needed.
Although the center tube 154 may be a single piece perforated pipe (with or without a center plug or flow restrictor), as shown in
Membrane mat 156 is preferably separated into two membrane portions 196 and 198 by baffle 155. For example, if liquid to be degassed (or a first liquid) is flowing through module 100 from end port 112 to end port 114, the liquid flows through the opening 113 in end port 112, through opening 142 in tube 190, out through perforations or openings 200 in tube 190, around, for example, the hollow fibers in membrane mat portion 196, over baffle 155 (between baffle 155 and casing interior 134), around, for example, the hollow fibers in membrane mat portion 198, through perforations or openings 200 in tube 192, through opening 144 in tube 192, and out through the opening 115 in nozzle 114. In this example, tube 190 is a liquid distribution tube and tube 192 is a liquid collection tube.
In another example, the liquid to be degassed (or some first liquid) is flowing through module 100 from end port 114 to end port 112, the liquid flows through opening 115 in end port 114, through opening 144 in tube 192, out through perforations or openings 200 in tube 192, around, for example, the hollow fibers in membrane mat portion 198, over baffle 155 (between baffle 155 and casing interior 134), around, for example, the hollow fibers in membrane mat portion 196, through perforations or openings 200 in tube 190, through opening 142 in tube 190, and out through opening 113 in end port 112. In this example, tube 192 is a liquid distribution tube and tube 190 is a liquid collection tube.
Although
Although it is preferred to use one membrane unit having baffled membrane mats therein, it is understood that non-baffled or multiple baffle configurations could be used. For example, membrane mats of short modules may be non-baffled, while those of long modules may include two or more baffles.
With reference to
With reference to
It is contemplated that press type processes 300 and 400 can be combined to simultaneously place rings 122 and 188 in position. Such can be accomplished by using adapter 404 and combining plunger 402 with plunger 302. The same combined process can be used for rings 120 and 186 and may be accomplished with an Arbor Press.
With reference to
With reference to
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In
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Although the particular gas (or liquid) port or port seal design is not limited, the preferred is a gas (or liquid) port seal design that will work with both positive and negative pressures.
Some of the polymer components may be selected from, for example, polyvinyl chloride (PVC), chlorinated polyvinyl chloride (CPVC), high impact polystyrene (HIPS), polyacrylonitrile-butadi-ene-styrene (ABS), polyacrylate-styrene-acrlonitrile (ASA), and polycarbonate (PC).
In accordance with at least one example, the preferred materials for each of the major components may be as follows:
Module Housing: PVC, ABS, polyethylene, steel, stainless steel (SS), or any material that will bond with epoxy;
Center Tube: ABS, PVC, or the like;
Center Tube Connector: ABS, PVC, or the like;
Shell-Side End Port or Nozzle: Noryl™, ABS, Delrin (Acetal), steel, SS, or the like;
Lumen-Side End Port or Nozzle: 1″ threaded pipe (PVC, ABS, steel, SS, or the like);
End Cap: Delrin, PVC, ABS, CPVC, FRP, SS, Noryl™, steel, or the like;
Thread for hollow fiber array: PP or other polyolefin;
Hollow Fiber Polypropylene fiber (for example, Celgard® X-40 PP fiber or X-50 PP fiber) or some other fiber material that is inert to acids or other chemicals used during a process such as ammonia removal; hollow fiber material may also be selected based on having the appropriate/desired fiber strength, porosity and fiber wall thickness; and
Potting: Epoxy, thermoplastic, or the like.
In accordance with at least one possibly preferred example, the preferred materials for at least each of the major components are selected, optimized, constructed, connected, and/or adapted to operate in or for use in membrane distillation and/or ammonia removal methods, processes, systems, and/or arrays, and possibly more preferably for both membrane distillation and ammonia removal as well as other applications.
According to at least one inverted potting embodiment, the hollow fiber mats are embedded/potted in a resin by the following method: A staple of hollow fiber mats is introduced into a housing. In a first step, a plunger or plug is placed in one end of the housing and then fugitive or removable liquid or gel is introduced into the housing via the openings while the housing is spinning around its central axis. As a result, the fugitive or removable liquid or gel forms a layer into which the ends of the hollow fibers are embedded. In a second step a liquid hardenable resin is introduced into the housing and by the centrifugal effect forms a resin layer over the first layer of the fugitive or removable liquid or gel, such that the hollow fibers are embedded in the resin layer in a segment along the fiber length nearby the fiber ends. After hardening of the resin, the fugitive or removable liquid or gel and the plug are removed and the hollow fibers are embedded in the hardened resin such that the fibers extend with their ends beyond the resin layer. Then, the fiber ends are trimmed to form the recessed tube sheet with open ends of the fibers on the outer surface. This process is repeated for the other recessed tube sheet.
Potting or thermosetting materials may include, but are not limited to, epoxy, polyurethane, and thermoplastics. Epoxies are preferred. Thermoplastics, as used herein, refers to a high polymer that softens when exposed to heat and returns to its original condition when cooled to room temperature; the term is usually applied to synthetics such as polyvinyl chloride, nylons, fluorocarbon polymers, linear polyethylene, polyurethane prepolymer, polystyrene, polypropylene, and cellulosic and acrylic resins. Exemplary thermoplastics include polyolefins, such as polypropylene and polyethylene.
Different potting methods may be employed to form the potting or tube sheets. Such different potting methods include, but are not limited to, mold potting, centrifugal potting, and gravity potting.
In at least certain other embodiments, the present invention is directed to contactors, modules, systems, and/or methods of degassing liquids.
In at least particular possibly preferred embodiments, the contactor or module is integrally potted, has planar, disc shaped end caps, and a cylindrical housing or shell receiving and supporting a membrane structure. In at least particular possibly preferred embodiments, each of the planar disc shaped end caps has a central opening therein adapted to receive a liquid end port or nozzle, another opening therein adapted to receive a gas, or second liquid, end port or threaded pipe, and is held in place in the housing or shell by at least one retaining element such as a retaining or locking ring. In at least particular possibly preferred embodiments, the integrally potted membrane structure is potted in place in the housing or shell by an inverted potting process involving the use of a removable plunger or plug to recess the potting.
The instant application relates to membrane contactors or modules and their methods of manufacture and use. In at least selected embodiments, the present invention is directed to membrane contactors or modules and/or their methods of manufacture and/or use. In at least certain embodiments, the present invention is directed to contactors, modules, systems, and/or methods of effecting ammonia removal or membrane distillation with one or more hollow fiber membrane contactors or modules. In at least particular possibly preferred embodiments, the contactor or module is integrally potted, has planar, disc shaped end caps, and a high pressure cylindrical housing or shell receiving and supporting a membrane element or structure including a perforated core, a plurality of hollow fiber membranes, a tube sheet or potting affixing each end of the hollow fibers and adhering to the interior of the housing or shell. In at least particular possibly preferred embodiments, each of the planar disc shaped end caps has a central opening therein adapted to receive a liquid end port or nozzle, another opening therein adapted to receive a gas, or second liquid, end port or nozzle, and is adapted to be held in place in the cylindrical housing or shell by at least one retaining element such as a retaining or locking ring received in a groove in the interior of the cylindrical housing or shell. In at least particular possibly preferred embodiments, the integrally potted membrane structure is potted in place in the housing or shell by an inverted potting process involving the use of a removable plunger or plug to provide recessed potting and by trimming the end of the potting and opening the ends of the hollow fibers preferably using an internal lathe means (which can preferably reach into the housing to trim the recessed potting or tube sheet), and may also include machining or forming a larger diameter section for receiving the end cap, a groove for receiving the retaining ring, and a flared entrance for facilitating the insertion of the end cap and retaining ring preferably using an internal lathe means.
In at least particular possibly preferred embodiments, the contactor housing, shell, casing, or body is selected from standard PVC, CPVC, ABS, polypropylene, steel, or stainless steel pipe (preferably a pipe material that will bond with epoxy to facilitate integral potting), such as 1″ to 24″ (nominal pipe size)(nominal diameter) standard PVC, ABS, steel, or stainless steel pipe, preferably 2″ to 24″ (nominal pipe size) Schedule 80 PVC pipe or 2″ to 24″ (nominal pipe size) Schedule 40 PVC pipe, more preferably 4″ to 20″ (nominal pipe size) Schedule 80 gray PVC pipe, and most preferably 6″ to 18″ (nominal pipe size) Schedule 80 gray PVC pipe.
At least certain prior membrane cartridges were formed or machined to have tube sheets or hollow fibers which ended flush with the end of the cartridge. In contrast, at least selected possibly preferred embodiments of the present invention have potting, tube sheets and/or hollow fibers which end deeply recessed in the module housing (for example, a recess of at least 1″, preferably at least 2″, and more preferably 3″ or more in for example an 8″ nominal diameter Schedule 80 PVC pipe or housing). In accordance with at least selected possibly preferred embodiments, the deeply recessed potting, tube sheets and/or hollow fibers are trimmed or cut using an internal trimming or cutting means such as an internal lathe that can reach up into the housing (for example, a recess of at least 1″, preferably at least 2″, and more preferably 3″ or more in for example an 8″ nominal diameter Schedule 80 PVC pipe as the housing). In accordance with at least one possibly preferred embodiment of the present invention, the potting, tube sheets, and/or hollow fibers are deeply recessed in the housing by numerically controlled (NC) lathe machining such as lathe finish cutting with tapered blades.
In accordance with at least selected particular possibly preferred embodiments of the present invention, the housing is a machined or modified 1″ to 24″ (nominal pipe size)(nominal diameter) standard PVC, ABS, steel, or stainless steel pipe, preferably 2″ to 24″ (nominal pipe size) Schedule 80 PVC pipe or 2″ to 24″ (nominal pipe size) Schedule 40 PVC pipe, more preferably 4″ to 20″ (nominal pipe size) Schedule 80 gray PVC pipe, still more preferably 6″ to 18″ (nominal pipe size) Schedule 80 gray PVC pipe, and most preferably an about 8″ nominal pipe size Schedule 80 PVC pipe, the membrane is preferably integrally potted in the housing an inverted potting technique so the potting is recessed in the housing, the potting is preferably machined deeply recessed in the housing by, for example, numerically controlled (NC) lathe machining (preferably with no initial rough cut or additional finish cut operation), the contactor or module length is preferably easily shortened or extended by selecting shorter or longer housing lengths (for example with an 8″ nominal diameter Schedule 80 PVC pipe as the housing, the housing length may be selected to be about 10″ to 60″, preferably about 20″ to 50″, more preferably about 24″ to 36″), the end caps are preferably planar, disc shaped end caps or plates that fit inside the housing, and/or the end caps are preferably pressed into place and held in position with retaining rings (no bolts or v-band clamps needed) and may be press installed with an Arbor Press.
In accordance with at least selected embodiments of the present invention, it is preferred that the contactor operate, for example, at shell-side liquid pressures of about 5 to 200 psig, preferably 10 to 100 psig, more preferably 10 to 90 psig, and most preferably 10 to 60 psig, and at lumen-side gas vacuum or pressures of minus 14.7 psig to about positive 60 psig, preferably minus 14.7 psig to positive 30 psig, more preferably minus 10 psig to positive 15 psig, most preferably at about a minus 5 psig (to clarify terminology: psi=pounds per square inch, psig=pounds per square inch gauge, psia=pounds per square inch absolute, psig=psia+14.7 psi, 14.7 psia=normal atmospheric pressure, −14.7 psig=0 psia=lowest possible negative pressure or absolute vacuum).
In at least selected embodiments, the present invention is directed to high pressure membrane contactors and/or their methods of manufacture and/or use. In at least certain embodiments, the present invention is directed to effecting ammonia removal or membrane distillation with a hollow fiber membrane contactor. Preferably, the contactor has a high pressure housing, casing or shell enclosing at least one membrane element or structure, preferably an integrally potted shell side liquid, baffled membrane element, including a perforated core, a plurality of hollow fiber membranes, a tube sheet affixing each end of the hollow fibers to the cylindrical housing, shell or casing. More preferably, lumens of the hollow fibers are in fluid communication with a liquid, a sweep gas (a strip gas), a vacuum, or both, and the liquid from which ammonia is to be removed, for example, enters the contactor via an open end of the perforated core and radially exits through the core perforations, crosses over the exterior of the hollow fibers (the shell side or shell-side), optionally passes over at least one baffle and crosses over the exterior of another portion of the hollow fibers, returns to the core through the perforations, and exits the contactor with less dissolved or entrained gas, or less ammonia. The entrained or dissolved gas diffuses or passes from the liquid across the hollow fiber membrane and into the lumen Similarly, the ammonia in the shell-side liquid diffuses or passes from the liquid across the hollow fiber membrane and into the lumen, through which a solution of an acid (for example, sulfuric acid) has been flowing to effect the ammonia removal.
In at least selected embodiments, the present invention is directed to high pressure membrane contactors having high pressure housings or shells that are preferably selected from desired lengths of standard PVC, ABS, polypropylene, steel, or stainless steel pipe (preferably a pipe material that will bond with epoxy to facilitate integral potting), such as 1″ to 24″ (nominal pipe size)(nominal diameter) standard PVC, ABS, steel, or stainless steel pipe, preferably 2″ to 24″ (nominal pipe size) Schedule 80 PVC pipe or 2″ to 24″ (nominal pipe size) Schedule 40 PVC pipe, more preferably 4″ to 20″ (nominal pipe size) Schedule 80 gray PVC pipe, and most preferably 6″ to 18″ (nominal pipe size) Schedule 80 gray PVC pipe. Such pipe section housings are preferably machined or modified to receive end caps and retaining rings. The end caps may include both liquid and gas (or permeate) end ports or nozzles with the liquid ports or nozzles preferably adapted to operate under pressure and the permeate or gas ports preferably adapted to function under vacuum or reduced pressure conditions. In certain preferred embodiments, the end caps may include multiple liquid end ports or nozzles.
In at least selected embodiments, the present invention is directed to improved, unique and/or low cost ammonia removal and/or membrane distillation membrane contactors, modules or systems, their methods of manufacture, and/or methods of use thereof. In at least certain embodiments, the present invention is directed to membrane treatment of fluids such as ammonia removal or membrane distillation, using a membrane contactor or module. Preferably, the contactor has a pressure housing enclosing at least one membrane structure, element, cartridge, or unit preferably including a perforated core, a plurality of hollow fiber membranes, a tube sheet affixing each end of said hollow fibers, and an optional baffle. The membrane structure may be a shell side structure in which the hollow fiber lumens are in fluid communication with a an acid solution (in the case of ammonia removal), and the liquid from which ammonia is to be removed enters the contactor via an open end of the perforated core, radially exits the core perforations, crosses over the exterior (lumen-side) of the membranes within the housing, and exits the contactor with less ammonia. The ammonia preferably diffuses from the liquid across the microporous membrane into the lumen.
In at least one embodiment, a possibly preferred membrane structure is integrally potted and includes a perforated center tube, a membrane mat comprising a plurality of one or more types of hollow fiber membranes each having a first end and a second end both being open, an optional baffle separating the hollow fiber mat into two areas, and potting at each end. The first and second membrane ends are open, for example, to allow a lumen-side fluid to pass therethrough. It may be preferred that the baffle is formed of a center tube plug of a one piece center tube or of at least one connector joining at least first and second sections of a multi-piece center tube and by epoxy that is applied over the center tube connector in the mat or bundle, preferably the center of the mat or bundle, while winding thereby forming a dam or block through at least a portion, preferably substantially the entire thickness, of the hollow fiber mat. It may also be preferred that the potting be made of epoxy and that the ends of the potting be cut off to form the open first and second ends (tube sheets) following potting.
In accordance with at least one embodiment, the center tube forms an axial opening in each end of the membrane structure and is perforated along its length to provide radial openings for liquid to flow out through the perforations and over the hollow fibers. The axial opening in each end of the membrane structure is adapted to be in fluid communication with the liquid ports or nozzles in the end caps of the module. For example, a respective elongate nozzle may be used to connect the corresponding axial opening with the liquid supply.
In accordance with one possibly preferred aspect of the present invention, there is provided a commercially viable ammonia removal or membrane distillation contactor having a cylindrical housing or shell and at least one integrally potted membrane structure therein.
In accordance with another possibly preferred aspect of the present invention, there is provided a commercially viable contactor having a housing made of a length or section of modified standard pipe adapted to receive an end cap in each end thereof.
In accordance with yet another possibly preferred aspect of the present invention, there is provided a commercially viable membrane contactor for ammonia removal and/or membrane distillation having an integrally potted membrane structure with deeply recessed tube sheets in a cylindrical housing or shell.
In accordance with still yet another possibly preferred aspect of the present invention, it was discovered that a commercially viable, high pressure membrane contactor for ammonia removal and/or membrane distillation could be constructed using a desired length of standard PVC, ABS, steel, or stainless steel pipe modified to receive and retain end caps therein.
Membrane contactors of the present invention may make it possible to transfer gas to or from an aqueous stream (or remove ammonia from a liquid stream) without dispersion. Such membrane contactors may contain thousands of Celgard® microporous polyolefin, for example, hydrophobic polypropylene, hollow fibers knitted into an array using polypropylene thread (see
The possibly preferred membrane contactors of the present invention may include a bundle of microporous hollow fibers, a rigid shell or housing enclosing the fiber bundle, and an end cap at each end of the housing. The end caps may be provided with four fluid ports: an inlet for introducing the first fluid, an outlet for discharging the first fluid, an inlet for introducing the second fluid, and an outlet for discharging the second fluid. The hollow fibers may be potted on both ends, recessed within the housing, to form polymeric tube sheets with the fiber bores opening on each end into common first and second end cap portions of the contactor. Although not preferred, in a “tube-side” or “lumen-side” type contactor, the first end cap may contain the inlet for the first fluid, which is designated the “tube-side” or “lumen-side” fluid because it is the fluid that passes through the internal lumens of the fibers. The second end cap contains the outlet for discharging the lumen-side fluid. The second fluid, designated the “shell-side” fluid, typically enters and exits the housing through inlet and outlet ports arranged between the tube sheets, whereby the shell-side fluid contacts the external surfaces of the fibers. The shell-side fluid flows through the interstices between fibers of the fiber bundle, and may be directed to flow parallel or perpendicular to the fiber length.
In the preferred “shell-side” contactor, the contactor may include a central core which passes through the membrane structure and has a first end serving as the inlet for the first fluid, which is designated the “shell-side” fluid because it is the fluid that passes over the exterior or shell of the hollow fibers. The first end cap may contain the inlet or port for the second fluid, which is designated the “tube-side” or “lumen-side” fluid because it is the fluid that passes through the internal lumens of the fibers. The second end cap contains the outlet for discharging the lumen-side fluid. The first fluid, designated the “shell-side” fluid, may enter and exit the end caps via respective inlet and outlet ports or nozzles operatively connected to the open ends of the perforated core, and typically exits and re-enters the perforations in the core between the tube sheets whereby the shell-side fluid contacts the external surfaces of the fibers. The shell-side fluid flows through the interstices between fibers of the fiber bundle, and may be directed to flow parallel and/or perpendicular to the fiber length.
Because the tube sheets separate the lumen-side fluid from the shell-side fluid, the lumen-side fluid does not mix with the shell-side fluid, and typically the only transfer between the lumen-side fluid and the shell-side fluid occurs through the walls of the hollow fibers. The fine pores in the fiber wall are normally filled with a stationary layer of one of the two fluids, the other fluid being excluded from the pores due to surface tension and/or pressure differential effects. Mass transfer and separation are usually caused by diffusion, which is driven by the difference in concentration of the transferring species between the two phases. Typically, no convective or bulk flow occurs across the membrane.
The hollow fibers are preferably made of polyolefin materials such as polypropylene and may also be made of polymethyl pentene (PMP, or poly(4-methyl-1-pentene)), polyvinylidene fluoride (PVDF), microporous hydrophobic PVDF, copolymers of polyvinylidene fluoride, such as a copolymer of polyvinylidene fluoride and hexafluoropropylene (PVDF:HFP), other polyolefins (e.g., polyethylene, polybutene), polysulfones (e.g., polysulfone, polyethersulfone, polyarylsulfone), cellulose and its derivations, poly phenyl oxide (PPO), PFAA, PTFE, other fluorinated polymers, polyamides, polyether imides (PEI), polyimides, polyamideimides (PAI), combinations, blends or copolymers thereof, and/or the like.
Although the possibly preferred present membrane contactors utilize a microporous membrane, the separation principle differs substantially from other membrane separations such as filtration and gas separation. With such preferred hollow fiber membrane contactors, there is no convective flow through the pores as occurs in other membrane separations. Instead, the preferred membrane acts as an inert support that brings the liquid and gas phases in direct contact without dispersion. The mass transfer between the two phases is governed entirely by the pressure of the gas phase. Because of the preferred Celgard® hollow fibers and the contactor geometry, the surface area per unit volume is an order of magnitude higher than traditional technologies such as packed columns, forced draft deaerators and vacuum towers. This high level of surface area to volume leads to a dramatic reduction in contactor/system size for a given level of performance.
It is noted that although the baffled membrane design appears to be preferred, there appear to be three design variants for the presently described membrane contactors. The baffled membrane design uses a radial liquid flow path around a central baffle. Liquid flows on the outside (shell side or shell-side) of the hollow fibers. The NB, or No Baffle design, does not utilize a central baffle, but it is still a radial flow device. The liquid outlet port on the no baffle design is located in the middle of the device rather than at the contactor ends as in the baffled design. One end of the NB contactor is capped and allows liquid to flow outward or radially across the fibers from a central distribution tube. This variant appears best suited for vacuum operation. The third variant or design allows for liquid flow inside of the hollow fiber (lumen side or lumen-side). These devices are not radial flow devices and appear best suited for small flow applications.
The present possibly preferred membrane contactors may utilize one of several fiber types, such as PP, PMP, or PVDF, which may be well suited for absorption/stripping techniques for water. PVDF fibers may better handle sanitizers added to seawater. The Celgard® X-40 membrane has a thicker wall with a smaller inside diameter than the X-50 and is recommended for oxygen removal. The Celgard® X-50 membrane has a slightly thinner wall with a larger inside diameter. (see
Below is a comparison of the Celgard® X-40 and X-50 hollow fibers.
A possible third fiber variant, a microporous polyolefin, was introduced in smaller contactors for gas transfer of low surface tension fluids and the fluid always flows on the shell side in these devices. Furthermore, a microporous PVDF fiber has been introduced for better tolerance of oxidizing species in water. Additionally, an XIND fiber was introduced in larger industrial contactors, and is geared to non-FDA degassing applications.
When using the Baffled or No-Baffle Membrane Contactors in gas absorption applications such as aeration or carbonation, etc., a gas is introduced into the inside (lumen side) of the hollow fiber membrane and the liquid phase is introduced to the outside (shell side) of the hollow fiber. The partial pressure of the gas and the water temperature controls the amount of gas dissolved in the liquid phase. When using Lumen Side Liquid membrane contactors (non radial flow devices) in this application, the liquid is introduced to the lumen side while the gas is introduced to the shell side.
When using the Baffled or No Baffle Membrane Contactors in gas stripping applications such as decarbonation or deoxygenation, a vacuum or stripping gas or combination of those is applied to the lumen side of the hollow fiber. The liquid stream is introduced to the outside of the fiber. The partial pressure of the gas is decreased to remove dissolved gases from the liquid phase. When using Lumen Side Liquid membrane contactors (non radial flow devices) in this application, the liquid is introduced to the lumen side while the gas/vacuum is applied to the shell side.
In another embodiment, a spiral-type hollow fiber membrane fabric-containing module or contactor for membrane distillation or ammonia removal may have an 8×20 configuration (or other sized similar configurations) with a module housing made of a modified section of pipe having an 8 inch diameter and a 20 inch length. This embodiment of a spiral-type hollow fiber membrane fabric-containing module may include a pair of end caps that may be adapted to fit in the ends of the module housing. Liquid end ports may be in each of the end caps. At least one gas port may be in at least one of the end caps or in the side of the module housing near one end thereof. At least one membrane structure may be adapted to fit in the module housing. Each membrane structure may include:
The above embodiment of a spiral-type hollow fiber membrane fabric-containing module or contactor may be used for membrane distillation and/or ammonia removal, or multiple membrane contactors, may be used for membrane distillation and/or ammonia removal. The above embodiment of a spiral-type hollow fiber membrane fabric-containing module or contactor may be preferred for membrane distillation and/or ammonia removal, or multiple membrane contactors, may also be preferred for membrane distillation and/or ammonia removal.
In another embodiment, an integrally potted hollow fiber membrane contactor for membrane distillation or ammonia removal may have an 8×20 configuration (or other sized similar configurations) with a high pressure cylindrical housing having an 8 inch diameter and a 20 inch length. This embodiment of an integrally potted membrane contactor may include planar, disc shaped end caps, domed shaped end caps and/or other molded shaped end caps. The high pressure cylindrical housing may receiving and support a membrane element including a perforated core, a plurality of hollow fiber membranes, a tube sheet affixing each end of the hollow fibers and adhering to the interior of the housing. Each of the end caps may have a central opening therein that may be adapted to receive a liquid end port, another opening therein that may be adapted to receive a gas end port, and may be adapted to be held in place in the cylindrical housing by at least one retaining element which may be a retaining ring received in a groove in the interior of the cylindrical housing. The integrally potted membrane structure may be potted in place in the housing by an inverted potting process involving the use of a removable plunger to provide recessed potting and by trimming the end of the potting and opening the ends of the hollow fibers using an internal lathe means. Opening the ends of the hollow fibers means exposing the fiber lumens and thereby providing access to the insides of the hollow fibers for the lumen-side fluid. The housing may include a larger diameter section for receiving the end cap, the groove for receiving the retaining ring, and a flared entrance for facilitating the insertion of the end cap and retaining ring.
In an ammonia removal system, for example, the fluid comprising ammonia may be the shell-side fluid, which may be inserted into a port or inlet in an end cap of a membrane contactor. Such a shell-side fluid may flow, for example, through the inlet into the core of the membrane contactor, which core may be perforated with a plurality of holes. The holes or perforations in the core allow the fluid to flow out of the core into the membrane structure comprising hollow fibers and allow the fluid to encounter the shell-sides of the hollow fibers in the membrane structure. In some embodiments, the inlet for the shell-side fluid may be substantially in the center of an end cap of the membrane contactor.
In certain embodiments, a counter-flow of a fluid containing one or more acids may be used to effect ammonia removal from a shell-side fluid containing ammonia. For example, the counter-flow fluid may be a solution of sulfuric acid. Further, this counter-flow fluid may be the lumen-side fluid. Such a lumen-side fluid may be inserted into an inlet port in an end cap of a membrane contactor. In certain embodiments, the inlet port for the lumen-side fluid, for example, a fluid containing one or more acids, may be located offset from the center of the end cap. In certain embodiments, the lumen-side fluid (for example, a fluid comprising acid) encounters the lumens of the hollow fibers by flowing through the inlet port in an end cap of the contactor and by moving inside the lumens of the hollow fibers, which lumens were exposed when the potted hollow fibers were cut open during manufacture of the membrane contactor.
While not wishing to be bound by theory, it is believed that the respective surface tensions of the two fluids (the shell-side fluid and the lumen-side fluid) come into play and allow for ammonia removal to take place in an ammonia removal application (or a chemisorption application). The pores, for example, micropores, in the walls of the hollow fibers in the membrane structure allow for the chemical reaction of the ammonia removal process to take place.
The above embodiment of an integrally potted hollow fiber membrane contactor, or multiple membrane contactors, may be used for membrane distillation. The above embodiment of an integrally potted hollow fiber membrane contactor, or multiple membrane contactors, may also be used for ammonia removal.
In one embodiment of the instant invention, a system for membrane (or osmotic) distillation or ammonia removal may be provided. The system may include at least one hollow fiber membrane module or contactor for membrane distillation or ammonia removal, according to any one of the embodiments described above. In one embodiment of the system, at least two hollow fiber membrane modules or contactors for membrane distillation or ammonia removal according to any one of the embodiments described above may be included.
The instant invention also contemplates a method of membrane distillation comprising the step of using the membrane contactor for membrane distillation or ammonia removal according to any one of the embodiments described above.
The instant invention also contemplates a method of ammonia removal comprising the step of using the membrane contactor for membrane distillation or ammonia removal according to any one of the embodiments described above.
Background information for at least certain TMCS (Trans-Membrane Chemi-Sorption) for the ammonia removal process in accordance with at least selected particular embodiments:
In general, in accordance with at least certain embodiments, the ammonia removal or TMCS process has two chemical reactions going on: On feed side, any ammonium ion converts to gas form by adding NaOH (source of OH−)
NH4++OH−→NH3(gas)+H2O
On lumen side, the NH3 gas reacts with Sulfuric Acid and converts to Ammonium Sulfate form
2NH3(gas)+H2SO4→(NH4)2SO4
Membrane technology is an alternative for ammonia removal and recovery from wastewater compared to many other water treatment processes, such as strippers, scrubbers, and deaeration systems. Among the available alternatives, the TransMembraneChemiSorption (TMCS) may be preferred under under certain operating conditions.
The TransMembraneChemiSorption (TMCS) separation technique preferably uses a membrane device to strip a gas species from a liquid feed phase and captures it using a liquid receiving phase that chemically reacts with the gas species. The hydrophobic hollow fiber membrane can be used as a medium to separate aqueous phases because it is not inherently selective between permeating species. The driving force for mass transfer of the species through the microporous hollow fiber membrane is the difference in concentrations between the two phases. Mass transfer stops when chemical equilibrium is reached. In the TMCS process, the driving force remains high because the transferred component chemically reacts in the receiving phase, allowing concentration levels in the receiving phase to remain at or near zero. In order to remove ammonia from a wastewater stream by TMCS, the dissolved ammonium ions (NH4+) are converted to free ammonia gas (NH3). At normal water temperatures, this is accomplished by dosing the water with an alkali to raise the pH to a sufficiently high level. The wastewater, containing a high concentration of free ammonia gas, is led into a Liqui-Cel® extra-flow membrane contactor and introduced to the outside (shellside) of the hollow fibers. A counter-current flow of an acid solution is introduced to the inside of the hollow fibers (lumenside). Due to the difference in ammonia gas concentration between the wastewater stream and acid solution, the NH3 gas transfers across the microporous membrane. In the receiving phase, the NH3 instantly reacts with the acid. This reaction forms an ammonium salt and is virtually irreversible. In theory, all free ammonia can be removed from a wastewater stream in a single step provided there are enough H+ ions available in the receiving phase and there is sufficient contact time for the chemisorption process to occur. In reality, the rate of ammonia transfer is limited by the maximum flow rate the membrane module can handle and the concentration gradient from inlet to outlet of the module. Connecting the membrane contactors in parallel or in series is essential for optimal system performance, size and cost. Water vapor transport between the feed phase and the receiving phase may also be considered because it can reduce the driving force and decrease system performance.
The applicability of a TMCS system may depend on the operating conditions and the goal of the separation process. The standard water quality requirements for at least certain contactors or modules are 5-10 lm pre-filtration and a low fouling index. The membrane contactor materials may show good resistivity against high or low pH. For operating temperatures up to 50° C., the pressure on the shellside and lumenside of the hollow fiber may be limited to about 3 bar.
The objective of a TMCS process is to remove as much NH3 from the wastewater as possible at minimal cost and risk while recovering some value to generate a quicker return. The cost-benefit analysis may involve capital expenses, operating expenses, cost savings, and the value of the resulting end products.
In accordance with at least selected Membrane (or Osmotic) Distillation embodiments:
The inventive membrane contactors are preferably used in a type of Membrane Distillation (MD) called Direct Contact Membrane Distillation (DCMD). There are other types of MD including Air Gap MD (AGMD), Vacuum MD (VMD), and others. Generally, for DCMD we flow a hot water (usually salt water) stream on one side of the membrane and a cold water directly on the other side of the membrane. The porosity of the membrane acts as an air gap between the two streams. Water does not enter the pore structure due to the hydrophobic behavior of the membrane. The hot (salt) water will have a higher vapor pressure than the cold (distilled) water. This vapor pressure differential is the driving force that causes the hot water source to evaporate across the membrane and condense on the cold water side.
The process of evaporation and condensation will cause a temperature change from the hot to the cold due to the heat of vaporization or the latent heat. There is also a temperature change between the hot and the cold due to convection between the two streams. The latter temperature change should be minimized as much as possible, since this temperature change may not do any useful work as far as the MD process is concerned and may lower the driving force between the two streams. This effect can be minimized by selecting membranes that have low coefficients of conduction. In other words they have insulating properties between the hot and cold streams.
In accordance with at least particular embodiments, it is important to select a membrane that offers good vapor transport properties (no restrictions) and that is somewhat insulating between the hot and cold water streams. The fiber is preferably also hydrophobic and has a pore size distribution that prevents any water breakthrough across the membrane. The MD process may be operating pressure independent, but the pore size should be small enough to prevent water pressure from breaking through the fiber wall. As an example a fiber with good properties would be PP or PVDF, having an inside diameter of 315 micron, an outside diameter of 600 micron, a porosity of 70%, and a nominal pore size of <0.2 micron.
In accordance with at least selected embodiments, aspects or objects, the present disclosure or invention relates generally to new, improved, or modified membrane contactors, modules, systems, and/or methods for membrane distillation and/or ammonia removal, and/or methods of manufacture, use, and/or the like. In accordance with at least certain selected embodiments, the present invention relates to particular possibly preferred membrane contactors, modules, systems, and/or methods for membrane distillation and/or ammonia removal, and/or to particular possibly preferred membrane contactors, modules, systems, and/or methods for membrane distillation and/or ammonia removal, involving membrane contactors adapted for membrane distillation, for ammonia removal, or for both membrane distillation and for ammonia removal, as well as other membrane contactor systems, methods or processes such as degassing, gasifying, separation, filtration, and/or the like. In accordance with at least one particular embodiment, the same particular membrane contactor may be used for membrane distillation and for ammonia removal, and is adapted to operate in both membrane distillation and ammonia removal arrays, systems, methods or processes.
The present invention may be embodied in other forms without departing from the spirit and the essential attributes thereof, and, accordingly, reference should be made to the appended claims, rather than to the foregoing specification, as indicated in the scope of the invention.
This application claims priority to and the benefit of co-pending U.S. Provisional Patent Application No. 61/791,034, filed Mar. 15, 2013, which is hereby incorporated by reference herein in its entirety.
Number | Date | Country | |
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61791034 | Mar 2013 | US |