Portable Replenishable Capacitive Deionization Device
20230264989 · 2023-08-24
Inventors
Cpc classification
C02F2201/46165
CHEMISTRY; METALLURGY
C02F2201/46115
CHEMISTRY; METALLURGY
C02F1/4604
CHEMISTRY; METALLURGY
C02F2201/4618
CHEMISTRY; METALLURGY
Y02A20/124
GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
International classification
Abstract
A portable replenishable scalable capacitive deionization device having a plurality of deionization cells, each of the cells having first and second ends, each of the cells including a cell wall, each of the cells having removable end caps covering the cell first and second ends. Each of the cells having first and second conductive members extending the length of each of the deionization cells, the first conductive member electrically connected to a first current source having negative polarity and the second conductive member electrically connected to a second current source having positive polarity. Each of the deionization cells including first, second and third membranes, the first membrane positioned adjacent the first conductive member, the second membrane positioned adjacent the second conductive member, and the third membrane is positioned between the first and second membranes wherein the first, second and third membranes are removable from each of the deionization cells.
Claims
1. A portable replenishable scalable capacitive deionization device comprising: a salt water inlet; a fluid electrode inlet for receiving water comprising conductive material; a plurality of deionization cells, each deionization cell comprising: first and second conductive members extending a length of the deionization cell, with the first conductive member electrically connected to a first current source having negative polarity and the second conductive member electrically connected to a second current source having positive polarity; a first removable membrane positioned adjacent the first conductive member, a second removable membrane positioned adjacent the second conductive member, and a third removable membrane is positioned between the first and second membranes, a first channel lying between the first membrane and the first conductive member, a second channel lying between the second membrane and the second conductive member, the first channel and the second channel operatively coupled to the fluid electrode inlet such that water comprising conductive material is flowed through the first channel and the second channel; and a third channel lying between the first membrane and the third membrane, and a fourth channel lying between the second membrane and the third membrane, the third channel and the fourth channel operatively coupled to the salt water inlet such that salt water is flowed through the third and fourth channels.
2. A portable replenishable scalable capacitive deionization device comprising: a plurality of deionization cells, each of said cells having first and second ends, each of said cells comprising a cell wall, each of said cells comprising removable end caps covering said cell first and second ends, each of said cells having first and second conductive members extending a length of each of said deionization cells, said first conductive member electrically connected to a first current source having negative polarity and said second conductive member electrically connected to a second current source having positive polarity, each of said deionization cells comprising first, second and third membranes, said first membrane positioned adjacent said first conductive member, said second membrane positioned adjacent said second conductive member, said third membrane is positioned between said first and second membranes wherein said first, second and third membranes are removable from each of said deionization cells, each of said cells having first, second, third and fourth channels, said first channel lying between said first membrane and said first conductive member, said second channel lying between said second membrane and said second conductive member, said third channel lying between said first membrane and said third membrane, said fourth channel lying between said second membrane and said third membrane, and wherein said replenishable capacitive deionization device is connected to a source of water to be desalinated and a source of water comprising conductive material, wherein said water comprising said conductive material is flowed through said first channel and said second channel, and said water to be desalinated is flowed through said third and fourth channels.
3. The device of claim 2 additionally comprising first and second reservoirs, said first reservoir for containing the desalinated water and said second reservoir for containing a liquid salt waste.
4. The device of claim 2, wherein said first and second membranes each comprise first and second edges, each of said membrane first and second edges comprise a sealing element.
5. The device of claim 2, wherein said third membrane comprises first and second edges, each of said membrane first and second edges comprise a sealing element.
6. The device of claim 3, additionally comprising a third reservoir for containing the water comprising the conductive material.
7. The device of claim 2, comprising six deionization cells.
8. The device of claim 7, wherein said six deionization cells are interconnected electrically.
9. The device of claim 7, wherein said six deionization cells are interconnected allowing fluid flow from cell to cell.
10. The device of claim 2, wherein the first current source and the second current source are provided by a source of energy selected from the group consisting of: electricity derived from wind based energy, photovoltaic energy, generator derived energy, nuclear energy, coal based energy, natural gas based energy or combinations thereof.
11. The device of claim 2, wherein said deionization cell comprises a cylindrical tube comprising an interior wall.
12. The device of claim 11, wherein said deionization cell comprises a first half and a second half joined along the length of the deionization cell, said first half comprising an interior wall and said second half comprising an interior wall, said first conductive member affixed to said cell first half interior wall, said first membrane affixed to said cell first half interior wall adjacent said first conductive member forming said first channel, said second conductive member affixed to said cell second half interior wall adjacent said second conductive member forming said second channel, said third membrane affixed between said deionization cell first and second halves in said deionization cell third channel.
13. The device of claim 12, wherein said first and second deionization cell halves are joined together along their lengths to create a cylindrical tube with a contiguous outer surface.
14. The device of claim 4, wherein the sealing element comprises a cured adhesive.
15. The device of claim 4, wherein the sealing element comprises a polymeric rubber.
16. The device of claim 2, wherein the conductive member comprises copper.
17. The device of claim 2, wherein the conductive member comprises conductive graphite.
18. The device of claim 2, additionally comprising first and second membrane supports, said first membrane support positioned adjacent said first conductive member and supporting said first membrane, said second membrane support positioned adjacent said second conductive member and supporting said second conductive member.
19. The device of claim 18, wherein said first and second membranes are friction fit within respective first and second membrane supports.
Description
BRIEF DESCRIPTION OF THE DRAWINGS
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DETAILED DESCRIPTION
[0042] Levels of salinity in water vary across the globe. Across differing bodies of water “salt water” has differing concentrations of salt depending on season, environmental conditions such as temperature, humidity, and geography. Weather conditions such as drought or monsoon, among other factors may also affect the concentration of salt in water. As a result, there does not tend to be a one size shoe fits all feet solution to desalination. At the same time, the disclosed device may be used in any number of environments and adapted to varying levels of salinity by using varying electrical parameters, water feed rate including the dwell time within the device for the water to be treated as well as any number of secondary filters used to address contaminants other than salt.
[0043] Generally, fresh potable water has less than 0.5 ppt of salt while brackish water is considered water with a salinity of about 0.5 to 17 ppt of salt. Seawater may have a salt concentration which ranges radically depending upon ambient conditions. Generally, seawater has a salt concentration ranging from 30 to 40 ppt, on average about 35 ppt. Brine is considered water with a salt concentration over about 50 ppt salt. Here again, the actual salt concentration in water may vary considerably from one body of water to the next given evaporation, freezing, and freshwater runoff among other factors affecting ocean bodies which span miles and project to depths of hundreds of feet.
[0044] Briefly, one disclosed device is a portable replenishable scalable capacitive deionization device that includes a salt water inlet and a fluid electrode inlet for receiving water that contains a conductive material. The disclosed device includes a plurality of deionization cells. Each deionization cell includes first and second conductive members extending a length of the deionization cell, with the first conductive member electrically connected to a first current source having negative polarity and the second conductive member electrically connected to a second current source having positive polarity. A first removable membrane is positioned adjacent the first conductive member, a second removable membrane is positioned adjacent the second conductive member, and a third removable membrane is positioned between the first and second membranes. A first channel is positioned lying between the first membrane and the first conductive member, and a second channel is positioned lying between the second membrane and the second conductive member. The first channel and the second channel are operatively coupled to the fluid electrode inlet such that the water containing the conductive material is flowed through the first channel and the second channel. A third channel is positioned lying between the first membrane and the third membrane, and a fourth channel is positioned lying between the second membrane and the third membrane. The third channel and the fourth channel are operatively coupled to the salt water inlet such that salt water is flowed through the third and fourth channels.
[0045] As used herein “operative coupling” refers to direct or indirect connections in which one or more intervening parts, pieces, devices, etc. may be used to form a connection between two points. In the case of liquid flow operative coupling, examples of such intervening parts, pieces, devices, etc. may include, but are not limited to, pipes, tubing, hoses, valves, pumps, filters, fittings, regulators, restrictors, flow meters, connectors, etc. In the case of electrical operative coupling, examples of such intervening parts, pieces, devices, etc. may include, but are not limited to, circuit breakers, switches, transformers, relays, connections, plugs, receptacles, fuses, capacitors, diodes, transistors, etc.
[0046] In accordance with another aspect of the disclosed device, there is provided a capacitive deionization device having a plurality of deionization cells, each of the cells having first and second ends. Each of the cells has a cell wall and removable end caps covering the cell first and second ends. Each of the cells has first and second conductive members extending the length of each of the cells. The first conductive member electrically connected to a first current source having negative polarity and the second conductive member electrically connected to a second current source having positive polarity. Each of the deionization cells has first, second and third membranes The first membrane is positioned adjacent the first conductive member, the second membrane is positioned adjacent the second conductive member, and the third membrane is positioned between the first and second membranes. The first, second and third membranes are removable from each of the cells. Each of the cells has first, second, third and fourth channels. The first channel lies between the first membrane and the first conductive member, the second channel lies between the second membrane and the second conductive member, the third channel lies between the first membrane and the third membrane, and the fourth channel lies between the second membrane and the third membrane. The capacitive deionization device is connected to a source of water to be desalinated and a source of water comprising conductive material. The water comprising the conductive material is flowed through the first channel and the second channel, and the water to be desalinated is flowed through the third and fourth channels.
[0047] Turning to the Figures wherein like parts are designated with like numerals throughout several views, there is disclosed a capacitive deionization device and process for desalinating water containing some concentration of salt in
[0048] Turning to
[0049] Each of the desalinization cells has first, second and third membranes,
[0050] Each of the cells has first, second, third and fourth channels. The first channel 64 lies between the first membrane 58 and the first conductive member 56A. The second channel 66 lies between the second membrane 62 and the second conductive member 56B. The third channel lies between the first membrane 58 and the third membrane 62. The fourth channel 69 lies between the second membrane 62 and the third membrane 60.
[0051] The capacitive deionization device is replenishable and connected to a source of water to be desalinated 22 and a source of water comprising a conductive material 24, the flow electrode,
[0052] A schematic depiction of the process used in the disclosed device is illustrated in
[0053] From the pump 28, the water comprising salt may enter the desalination cells 42. The flow electrode also enters the desalination cells 42. Processing within the desalination cell is explained subsequently. Once processed, the desalinated water may be decanted off into a reservoir 32. Alternatively, the now once processed water may be recycled 36 back through the desalination cells 42. Recycling the water to be processed through the desalination cells 42 repeatedly is within the scope of the various embodiments. Once the desalinated water has been sufficiently desalinated it may be decanted off to the reservoir 32.
[0054] Salt waste resulting from the desalination disclosed device is decanted off into a reservoir 38 for further use or disposal. The flow electrode may either be decanted off into a reservoir 40 or recycled 43 back through the desalination cells 42. As part of the recycle loop 45, a remixer 44 may be used to ensure that the conductive material remains suspended within the flow electrode solution.
[0055] An even more detailed view of the inner workings of one embodiment of the disclosed device may be seen in
[0056] The flow electrode is drawn from reservoir 24 by pump 27 into the desalination cells 42 and recycled within the cell as shown in
[0057] As shown in
[0058] The connection between the individual cells is illustrated in
[0059] Another means of calculating the necessary number of desalination cells is to determine the necessary processing length (inches or centimeters) of cells necessary to fully desalinate the water containing salt feedstock. In order to facilitate portability as well as the ability of the operator to replenish the individual cells, the length of the individual cells may be limited to under 30 inches.
[0060] Enough tubing is inserted through holes 46 (
[0061] As can be seen in
[0062] The desalination cell of the disclosed device also includes first 64, second 66, third 68 and fourth 69 channels. The first 64 and second 66 channels are for transport of the flow electrode adjacent the current collectors 56A and 56B,
[0063] The third 68 and fourth 69 channels are divided by the third membrane 60. The feedstock water containing the salt enters the desalination cell 42 through the two inlets 70 and then is processed within the cell. The concentrated salt water and recovered desalinated water exits the cell through outlets to channels 72 and 74,
[0064] Any number of alternative arrangements are possible. Using a plurality (two or more) of desalination cells 42, the water containing the salt (feedstock) may be processed by cells arranged in series
[0065] A further embodiment of the desalination cell 42 of the disclosed device is illustrated in
[0066] As can be seen in
[0067] Referring back to
[0068] In this embodiment, the lower interconnections between the desalination cells are housed in the bottom portion 13 of the outer casing in the base 17 beneath the seats 15,
[0069] As the disclosed device is modular it may be built out through any number of cells and devices. Given the potential need for added pumping capacity, the pumps may be housed separately. The disclosed device may be provided with increased recovery capacity by adding further cells. A remixer may also be used between any two desalination cells. This allows for the desalination cells of the disclosed device to be used in series to further recover and purify the water to be recovered.
[0070] The water to be purified by the disclosed device may be delivered through any number of means including gravity flow, electrical pump, etc. The longer the resident time for the feedstock (water to be recovered) in the cells of the disclosed device, the more efficient the recovery process. A mechanical or electromechanical pump is preferred as allowing the stepped or adjustable means of flowing water to the device given varying levels of salinity. Any number of pumping devices may be used to pump the various fluids through the disclosed device. One family of pumps that have been found useful include those made by Stenner of Jacksonville Fla. Of particular use are the peristaltic metering pumps such as ECON FX and VX.
[0071] The power source for the device may take the form of alternating current, direct current or a combination of the two. Preferably, electrical power is used to charge the conductive elements of the disclosed device and any further electrical appliance used with the device such as a pump. The source of electricity may comprise any available resource including solar energy, wind energy, as well as conventional industrial or residential sources of electricity alternating and/or direct current. For example, photovoltaic energy, generator derived energy, nuclear energy, coal based energy, natural gas based energy, etc. may be used.
[0072] The cell 42 may be comprised of any material which does not interfere with the intended recovery of water. Plastic polymers such as PVC, ceramics including glass, as well as nonconductive composites and metal alloys, among other materials, are all useful. In cross section the cells may be circular (cylindrical), square, oblong, rectangular, or any other shape which facilitates operation of the device. One source for cell materials is Harrington Industrial Plastics of Jacksonville, Fla. This design of the device facilitates use in domestic/residential environments as well as field use in any number of institutional or governmental applications. The length of the cells may range from about 6 inches to about 30 inches. The width of the cell may range from 1 inch to 5 inches. The cells may be comprised of ceramics such as glass, polymeric plastics such as PVC, or nonconductive metals which will not interfere with the recovery process. End caps may also be obtained commercially through any number of sources such as Harrington Industrial Plastics of Jacksonville Fla. In embodiments formed as cylindrical tubes, the cells may have a contiguous outer surface.
[0073] In the production of a system of cells the individual cells may be joined through adhesives or mechanical fixtures, among other means. If the intention is to build a system which is modular, the cells may be affixed to one another in a manner which allows the addition of further cells (or devices) to the original device. Further the disclosed device can be configured to accept membranes which may be replaced if worn over time or if the system is applied to a different environment of use.
[0074] Each cell has end caps at either end, each having holes for the introduction of a feed line and two lines for recovered water and saline, respectively. Conductive elements are placed on the interior of either side of the cell adjacent and running the length of the cell. Contacts for the electrodes are placed adjacent the end caps. The contacts allow for electrical connection of the device electrodes to a power source and interconnection of the cells from cell to cell or individually.
[0075] Suitable conductive element materials include any conductive material such as copper, and conductive graphite, among other materials. Commercially available materials include conductive graphite available from HP Material Solutions of California and conductive copper tape available made by Tapes Master and available through Amazon or directly from Tapes Master at tapesmaster.com. In one embodiment, a conductive copper foil is placed in the cell running the entire length of the cell and a graphite foil is place over the top of the copper.
[0076] The conductive elements may be charged by a DC power source on either side of the cell. Here again, the conductive elements may be charged in series or individually. As the purity and volume of recovered water may vary, use of a step or adjustable or steppable DC power source is preferred. One power source which has been found useful is a Daedalon AC/DC Power Supply available from Science First in Jacksonville Fla., (www.sciencefirst.com).
[0077] The relative thickness of the conductive element ranges from about 0.5 mm to about 2 mm. The width of the current collectors generally ranges from about 0.1 mm to about 3 cm. This allows for the necessary dimensions to provide for the necessary voltage and current density to draw the respective contaminant ions through the respective ion selective membranes and out of the fluid stream to be recovered.
[0078] Membrane
[0079] Water purification using this technology is based on solubility of ions (anions and cations) in water. Unlike poles attract and like poles repel, thus the ions migrate toward the poles of opposite charge. Suitable membranes allow the selective passage of either anions or cations towards the pole of opposite charge.
[0080] Suitable membranes may depend on the ionic species to be selected for separation from the fluid to be recovered. In water desalination, generally useful membranes may be classified as cationic or anionic. Membranes may comprise any number of materials. Polymeric materials such as thermoplastic or thermosetting polymers are useful in forming selective membranes in accordance with various embodiments.
[0081] Thermoplastic polymers useful in making membranes in accordance with various embodiments include vinyl polymers such as polyethylene, polypropylene, as well as polyesters, polyamides, polyimides, polyamide-imides, polyethers, block polyamides-polyethers, block polyester polyethers, polycarbonates, polysulfones, polybisimidazoles, polybisoxazoles, polybisthiazoles, and polyphenyl polymers. Other thermoplastic polymers which may be useful as membrane material include nylons, polyacetals, poly acetals, polyurethanes, polyphenyl-aniline sulfides, polypropylenes, and poly ether ether ketones among others.
[0082] Generally thermoplastic polymers and copolymers comprising monomers including ethylene, propylene, styrene, acrylonitrile, butadiene, isoprene, acrylic acid, methacrylic acid, methylacrylate, methylmethacrylate, vinyl acetate, hydroxy methacrylate, hydroxyl ethyl acrylate as well as other known vinyl monomers.
[0083] Membranes useful in the disclosed device may also be fabricated from thermosetting polymers. Useful thermosetting polymer systems in accordance with various embodiments include epoxies, polyurethanes, polyesters, acrylics, bismaleimides such as the reaction product of bismaleimide and methyl dianiline. Other thermosetting polymers that may be used in fabricating membranes useful in the disclosed device include silicones, phenolics, polyamides, polysulfides, curable polyesters, maleate resins that are the reaction product of polyols and maleic anhydride. Maleic anhydride may also be reacted with various acids such as fumaric acid and isophthalic acid among others.
[0084] Suitable cationic membranes may comprise monomers of styrene, aniline, vinylchloride, styrene, butadiene, propylene, and ethylene, among other monomers. Representative polymers which may be used as a cationic exchange membrane include polystyrene and polyanaline blends, heterogeneous polyvinylchloride/styrene-butadiene-rubber blends, and monovalent selective membranes made of blends of sulfonated poly(ether sulfone) with sulfonated poly (ether ether ketone. Ceramic cation exchange membranes may also be used such as those synthesized by impregnating ceramic supports with zirconium phosphate or phosphotungstic acid based membranes deposited on graphite supports.
[0085] Useful anionic exchange membranes may include, for example, poly(vinyltrimethoxysilane-co-2-(dimethylamine)ethylmethacrlylate)copolymer, membranes composed of 4-vinylbenzyl chloride, styrene, and ethylmethacrylate, cross-linked polystyrene, acrylonitrile/butadiene/styrene with activated carbon and silver fillers, and aliphatic-hydrocarbon based anion exchange membranes prepared from glycidyl methacrylate and divinylbenzene, among others.
[0086] Commercially available anionic and cationic ion selective membranes which are useful in the disclosed device include those available from the Fuji Film Membrane Technology Group such as the Type 10 and Type 12 anionic and cationic ion exchange membrane. Preferable are those membranes available from Resin-Tech Inc. such as anionic AMB-SS and cationic CMB-SS both presented as single sheets. The Resin Tech membrane has been found preferable as it provides properties of stability and allows for removability from the cell.
[0087] Optionally, the sides of the membrane may be fixed in a membrane support. Membrane supports which have been found useful may be seen in
[0088] A further example of a membrane support may be found in
[0089] The membrane may also comprise a bead of polymer on both longitudinal sides of the membrane. Specifically, by placing a small bead of polymer (for example, rubber or cured thermoset adhesive) that portion of the membrane which rests within the membrane support has a structural element which precludes the membrane from pulling away from the membrane support while allowing slidable removal of the membrane from the membrane support.
[0090] Assembly
[0091] In one embodiment, fabrication of the desalination cells 42 comprises a number of steps. To one section of a cell wall 70, a conductive element 72 is affixed using mechanical means or adhesive,
[0092] One useful embodiment of the membrane support is shown in
[0093] An alternative means of affixing the membranes within the desalination cell is seen in
[0094] To make the membranes resistant to leakage, the membranes may be grommeted 96 along their entire length on either side of the membrane 94 so that fluid (e.g., water) will not leak around the edges of the membrane that are seated in the clips 90 in the sidewalls of the cell 42,
[0095]
[0096] In order to facilitate replacement of component parts the desalination cell may be hinged on one side in a clam shell design,
WORKING EXAMPLES
[0097] The following examples illustrate certain attributes and properties of the disclosed device.
Example 1
[0098] From a ten-foot length of clear PVC pipe (1.0 inches OD, schedule 40 Harrington Industrial Plastics, Jacksonville Fla.) six twelve-inch sections were cut. Each of the twelve-inch sections were then cut lengthwise in half over their twelve-inch length. One ½ inch strip of conductive copper (Tapes Master Inc., Amazon) tape with adhesive on one side was then laid into each of the twelve sections. The conductive tape was allowed to run past the twelve-inch length on both sides of the section to enable connection from cell to cell as well as connection to a DC power source.
[0099] Membrane supports were then fashioned from edge molding commercially available at Ace Hardware, Jacksonville Fla. The molding was cut to 12-inch lengths and the side flanges were trimmed leaving only enough edge to fix the membrane in the support. Holes were punched into the base (base width 0.5 inches at the outer width of the base) of the membrane support to allow the flow of ions within the flow electrode channel. The membrane was then glued into each of the twelve 12-inch half section of PVC pipe adjacent the conductive copper tape using a hot glue (Gorilla Glue Company).
[0100] Ion selective membranes (anionic and cationic) were obtained from Resin Tech of New Jersey. Anionic resin (AMB-SS) stock was obtained in single sheets. Cationic resin (CMB-SS) was also obtained in single sheet stock. The respective anionic and cationic membranes were cut to size and mounted on each membrane support. The length of each section membrane was cut at twelve inches. The width of each section of membrane was fashioned so that it is wide enough when fixed in the membrane support to project up from the membrane support but not so far as to make contact with any other membranes. Membrane sections were cut in widths of 0.5 inches×12 inch lengths. Before insertion into the membrane support the outer edges of each membrane was coated with one sixteenth of an inch of epoxy to create an adherent bead. As explained earlier, the epoxy bead was intended to fix the membrane in the support during recovery of the salt water while allowing removal of the membrane when the membrane is in need of replacement. The epoxy was allowed to cure. The membranes were then inserted into their respective membrane supports. The first and second membranes were anionic exchange membranes. The third membrane was a cationic exchange membrane.
[0101] The third or central membrane is cut in the same manner as the first two membranes—although larger—and mounted to the sections of each cell as the sections is assembled to form the six cells. Specifically, membrane sections were cut in twelve-inch lengths and—given the width of 12 half sections of pipe −0.75 inches in width. The membrane sections were treated similarly with epoxy creating a bead of epoxy on either side of each membrane section over the length of each membrane. Each membrane was then inserted into two fixing elements on either side of the membrane sections (
[0102] Four holes were drilled in each of the twelve end caps (Harrington Industrial Plastics, Jacksonville Fla.) and a twelve-inch length of clear vinyl tubing ( 5/32 inch OD) was inserted through each of the holes in each of the end caps. The tubing extended about an inch into the interior of each end cap. Once four sections of tubing were inserted into each end cap, the interior of each end cap was lined with silicone putty (E/FUSING 900 Moldable Silicone Putty) at the surface that the tubing was inserted through. The putty served two purposes; fixing the tubing in place in the end cap and sealing the membranes against leakage and cross contamination.
[0103] The two half sections of the cell were combined to form each of the six cells and the end caps were attached at either end of each of the cells feeding each of the four sections of tubing into the four channels. The two conductive members were wrapped around the sides of each respective cell half to enable further connection between cells and to the power source. Connectors (Harrington Industrial Plastics, Jacksonville Fla.) to make the tubing connections between the cells as well as to connect the cells to the source of salt water (preprocessing) and the discharge reservoirs (postprocessing). The tubing in the six cells was then connected together using connecters (Harrington Industrial Plastics, Jacksonville Fla.). The six cells were connected in series as well as to the pumps used to create flow to the six cells which were attached in series.
[0104] Water flow was facilitated using three Model ECON FX Pumps (85MPH5) made by Stenner of Jacksonville Fla. The flow rates ranged from 0.2 gpm to 15.1 gpm for the water needing purification and the flow electrode. From the reservoirs (flow electrode and feedstock water for recovery) these respective fluids passed through a prefilter and then to the pump. From the pump, the water to be recovered was flowed into the cells. Once through the cells the water was decanted off, recovered water in one vessel and concentrated saline in another. At the same time water is flowed through an immediately adjacent channel which through the flow electrode drew and concentrated saline ions into the channel and flushed from the system.
[0105] From a further reservoir, the fluid electrode was dispensed. This fluid was a mixture of conductive carbon particles suspended in water. The fluid electrode was flowed between the conductive copper member and the membrane in a continuous loop through the anionic and cationic sides of the cell through which they are connected. After coming through both sides of the cell the fluid electrode was subjected to a remixer. A 2500 ml Erlenmeyer flask having an input for receiving the water/carbon particle mixture and an output allowing the fluid electrode to be pumped back into the cells was used as a remixer. The addition of further volumes of flow electrode was controlled by a stop cock. This mixing vessel was used to enhance the homogeneity of the carbon particles in the flow electrode. The concentration of the conductive particles in the water conductive particle mixture ranged from 1% to 5% w/v. The system used was a vessel or flask with a double-hose barbs to allow the flow electrode in for mixing/remixing and out for introduction back into the flow electrode channel. Mixing in the flask was undertaken using Intllab Magnetic Stirrer. The recovered water was tested for salinity and recycled through the system.
[0106] Because concentration polarization becomes more important as the solution becomes more dilute, the solution velocity increases in the stacks processing the most dilute solution. The velocity of the solution was controlled using the pump which is stoppable and can be adjusted to provide a slower or faster rate of fluid flow. Typically, large recovery systems have 6-10 cells in series to achieve the recovered water. This will depend on salinity, weather, and other environmental conditions. For applications requiring high purity water, the disclosed device may be run in series with the flow electrode, recovered water, and concentrated saline flowing from one device to the next. The fluid and electrical connections were discrete to each set of cells. Electrical connections may also be configured in series across the entire system.
Example 2
[0107] Six further cells were assembled in a manner which was identical to Example 1 with one exception. Instead of using conductive copper foil as the conductive member, conductive graphite (GOONSDS Graphite Sheets Foil 0.1 mm) strips were cut from graphite sheets. The graphite sheets were cut in twelve-inch lengths and 0.5-inch widths. The cells were connected in series and the salt water was processed as described in Example 1.
[0108] While various embodiments have been illustrated and described, it is to be understood that the invention is not so limited. Numerous modifications, changes, variations, substitutions and equivalents will occur to those skilled in the art without departing from the scope of the present invention as defined by the appended claims.