WO2014102676A1 - An ion absorption/desorption device and a method thereof as well as a ph adjustor - Google Patents
An ion absorption/desorption device and a method thereof as well as a ph adjustor Download PDFInfo
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- WO2014102676A1 WO2014102676A1 PCT/IB2013/061124 IB2013061124W WO2014102676A1 WO 2014102676 A1 WO2014102676 A1 WO 2014102676A1 IB 2013061124 W IB2013061124 W IB 2013061124W WO 2014102676 A1 WO2014102676 A1 WO 2014102676A1
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/288—Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
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- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D15/00—Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
- B01D15/08—Selective adsorption, e.g. chromatography
- B01D15/26—Selective adsorption, e.g. chromatography characterised by the separation mechanism
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- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
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- B01J20/26—Synthetic macromolecular compounds
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- B01J20/28014—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their form
- B01J20/28047—Gels
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- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/32—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
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- B01J20/3206—Organic carriers, supports or substrates
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- B01J20/3206—Organic carriers, supports or substrates
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- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/32—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating
- B01J20/3231—Impregnating or coating ; Solid sorbent compositions obtained from processes involving impregnating or coating characterised by the coating or impregnating layer
- B01J20/3242—Layers with a functional group, e.g. an affinity material, a ligand, a reactant or a complexing group
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- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
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- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/34—Regenerating or reactivating
- B01J20/3425—Regenerating or reactivating of sorbents or filter aids comprising organic materials
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- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/34—Regenerating or reactivating
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- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/285—Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/286—Treatment of water, waste water, or sewage by sorption using natural organic sorbents or derivatives thereof
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- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/46109—Electrodes
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- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/469—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis
- C02F1/4691—Capacitive deionisation
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- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/469—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis
- C02F1/4696—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis electrophoresis
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- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
- C02F1/46104—Devices therefor; Their operating or servicing
- C02F1/46109—Electrodes
- C02F2001/46133—Electrodes characterised by the material
- C02F2001/46138—Electrodes comprising a substrate and a coating
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- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/46—Apparatus for electrochemical processes
Definitions
- the present invention relates to an ion absorption/desorption device and a method thereof as well as a pH adjustor, in particular, relates to performing
- Mineral ions including cations such as sodium, calcium, iron, copper ions and anions such as chloride, bromide, sulphate and carbonate ions, are considered as major solutes dissolved in water.
- unwanted ions in e.g. aqueous solution usually need to be removed.
- the skilled person in the art ever assumes to stuff inorganic oxide gel in the brine chamber to reconstruct the electrodialysis apparatus such as disclosed in US 3847788.
- electrolyte is exuded as overflow from gel, which eliminates the brine stream thereby lowering storage, pumping and piping requirements.
- such device still suffers from shortcomings such as complex construction, scaling problems, simutanelous generation of unwanted brine solution during deionization, which brings trouble in domestic use..
- the object of the present invention lies in solving at least one of said problems.
- the device may comprise: an electrode pair, at least one electrode of the electrode pair is covered by ions-permeable gel with functional groups, the gel absorbs ions in a liquid when a voltage is applied on the electrode pair. Covering the electrode by ions-permeable gel with functional groups facilitates chelation of the cations such as sodium, calcium, iron, copper ions and the anions such as chloride, bromide, sulphate and carbonate ions in the liquid with the functional groups in the gel, thereby immobilizing these ions in the gel so as to improve absorption efficiency.
- ions-permeable gel such an ions-permeable gel with functional groups
- ions-permeable gel is inflatable in the solution, which on the one hand absorbs water in the solution and on the other hand absorbs the unwanted ions in the solution firmly.
- the gel used here will not exude the electrolyte even when a high concentration of salts is absorbed, which inhibits the simultaneous generation of unwanted brine solution.
- the gel used therein may comprise natural polymers or synthetic polymers.
- the natural polymers may comprise: agarose, methylcellulose and hyaluronan;
- the synthetic polymers may comprise: polyacrylamide, polyvinyl alcohol, acrylate polymers and copolymers.
- the ion absorption device may further comprise: conductive materials between at least one electrode of the electrode pair and the gel, the conductive materials include at least one of: titanium, platinum, gold, rhodium, ruthenium; Ti-Ru alloy, graphite, active carbon, porous carbon paper or cloth.
- the conductive materials between at least one electrode and the gel facilitate the gel to cover the electrode better so as to enhance the binding force between them.
- a pH adjustor comprising said ion absorption device.
- One electrode of the electrode pair is covered by the gel, and the gel absorbs H + or OH " ions in a liquid when a voltage is applied on the electrode pair.
- Acidic water or alkaline water with different pH values can be generated based on user requirement by using the pH adjustor of the present invention.
- an ion desorption device which may comprise: an electrode pair, at least one electrode of the electrode pair is covered by ions-permeable gel with functional groups, the gel desorbs ions absorbed in the gel into a liquid when a reverse voltage is applied on the electrode pair.
- the repulsive force generated by the ions chelated together with the functional groups under the electric force is greater than the binding force with the functional groups, therefore, those ions bonded together with the functional groups will leave the gel successively and get into the solution.
- the gel used therein may comprise natural polymers or synthetic polymers.
- the natural polymers may comprise: agarose, methylcellulose and hyaluronan;
- the synthetic polymers may comprise: polyacrylamide, polyvinyl alcohol, acrylate polymers and copolymers.
- the ion desorption device may further comprise: conductive materials between at least one electrode of the electrode pair and the gel, the conductive materials include at least one of: titanium, platinum, gold, rhodium, ruthenium; Ti-Ru alloy, graphite, active carbon, porous carbon paper or cloth.
- the conductive materials between at least one electrode and the gel facilitates the gel to cover the electrode better so as to enhance the binding force between them.
- an ion absorption method which may comprising the steps of: applying a voltage on an electrode pair, wherein at least one electrode of the electrode pair is covered by ions-permeable gel with functional groups, such that the gel absorbs ions in the liquid.
- the gel used therein may comprise natural polymers or synthetic polymers.
- it may further comprise: conductive materials between at least one electrode of the electrode pair and the gel, the conductive materials include at least one of: titanium, platinum, gold, rhodium, ruthenium; Ti-Ru alloy, graphite, active carbon, porous carbon paper or cloth.
- an ion desorption method comprising: applying a reverse voltage on an electrode pair, wherein at least one electrode of the electrode pair is covered by ions-permeable gel with functional groups, so as to desorb ions absorbed in the gel into a liquid.
- the gel used therein may comprise natural polymers or synthetic polymers. In a further embodiment of the present invention, it may further comprise: conductive materials between at least one electrode of the electrode pair and the gel, the conductive materials may include at least one of: titanium, platinum, gold, rhodium, ruthenium; Ti-Ru alloy, graphite, active carbon, porous carbon paper or cloth.
- Fig. 1 A schematically shows an ion absorption device according to one aspect of the present invention.
- Fig. IB schematically shows an ion absorption device in an alternative embodiment of the present invention.
- Fig. 1C schematically shows an ion absorption device in another alternative embodiment of the present invention.
- Fig. 2 schematically shows that conductive materials are arranged between the electrode and the gel in an ion absorption device in an alternative embodiment of the present invention.
- Fig. 3 A schematically shows a pH adjustor according to another aspect of the present invention.
- Fig. 3B schematically shows a pH adjustor in an alternative embodiment of the present invention.
- Fig. 4A schematically shows an ion desorption device according to one aspect of the present invention.
- Fig. 4B schematically shows an ion desorption device in an alternative embodiment of the present invention.
- Fig. 4C schematically shows an ion desorption device in another alternative embodiment of the present invention.
- Fig. 1A schematically shows an ion absorption device 10a according to one aspect of the present invention.
- the ion absorption device 10a may comprise an electrode pair 12, 14, at least one electrode of the electrode pair 12, 14 is covered by ions-permeable gel 16a with functional groups, the gel 16a absorbs ions in a liquid 26a when a voltage is applied on the electrode pair 12, 14.
- various materials can be used as the material of the electrode pair 12, 14 of the present invention, for example, metals such as Ti, Pt, Au, Rh and Ru, or alloys as Ti-Ru, or carbon based materials such as graphite and active carbon.
- a first electrode 12 of the electrode pair 12, 14 is covered by an ions-permeable gel 16a with functional groups.
- a second electrode 14 of the electrode pair 12, 14 is covered by an ions-permeable gel 16a with functional groups.
- a modified embodiment of the present invention e.g., Fig. 1B
- both the first electrode 12 and the second electrode 14 of the electrode pair 12, 14 are covered by an ions-permeable gel 16a with functional groups.
- the ions-permeable gel 16a or 16b (which will be mentioned later) with functional groups used in respective embodiments of the present invention is substantially a cross-linked system exhibiting no flow when in the steady-state. These gels are mostly liquid, yet they behave like solids due to a three-dimensional cross-linked network within the liquid.
- Such ions-permeable gels 16a with functional groups can be used for ion absorption for the following reasons: 1) Over 90% of the total weight of gel is water, which has high permeability, and ions can get into the gel by free diffusion or under electric force. 2) The three-dimensional cross-linked network limits the mobility of the absorbed ions, preventing them from leaking out. 3) The active groups contained in gel such as hydroxyl groups, amino groups and carboxyl groups, which depend on the gel ingredients, can bind with ions by hydrogen bonding interaction or electrostatic interaction. Therefore, ions absorbed by gel can be further stabilized.
- the gel 16a used in respective embodiments of the present invention may comprise natural polymers or synthetic polymers.
- the natural polymers comprise: agarose, methylcellulose and hyaluronan;
- the synthetic polymers comprise: polyacrylamide, polyvinyl alcohol, acrylate polymers and copolymers.
- the ion absorption device comprises conductive materials 24 between at least one electrode of the electrode pair 12, 14 and the gel 16a
- the conductive materials 24 include at least one of: titanium, platinum, gold, rhodium, ruthenium; Ti-Ru alloy, graphite, active carbon, porous carbon paper or cloth, as schematically shown in Fig. 2.
- the first electrode 12 of the electrode pair 12, 14 in Fig. 1 A serves as a cathode
- the second electrode 14 serves as an anode
- the liquid 26a used therein can be e.g. water containing Ca 2+
- the surface of the first electrode 12 is covered by agarose gel.
- the chemical formula of the agarose gel is:
- hydroxyl groups are contained in the chemical formula of the agarose gel.
- the OH " ion as an ion with opposite polarity from Ca 2+ generates closely bond Ca(OH) 2 by maintaining neutral electricity, i.e., the OH " ion reacting with Ca , so as to stabilize the Ca ions in the gel further.
- the Ca 2+ ions in the water are removed through said absorption of Ca 2+ ions.
- a corresponding ions-permeable gel 16a with functional groups can be used for a different ion absorption.
- the methylcellulose, the methyl methacrylate, the methacrylic acid, the polyacrylamide and the methyl allyl sulfonate gel, acrylate polymers, copolymers have carboxyl functional groups
- the hyaluronan and the polyvinyl alcohol have hydroxyl functional groups
- the polyurethane has amino functional groups, etc.
- the various natural polymer gels or synthetic polymer gels listed here are only demonstrative, which does not mean that the gels used in the respective embodiments of the present invention are limited to these.
- the hydrogel for absorbing heavy metal ions generally comprises various chelated functional groups, such as carboxyl (-COOH), amido (-NH 2 ), hydroxyl (-OH), sulfonic group (-SO3) etc., so, if the hydrogel in general does not comprise functional groups for chelating heavy metal, chemical reaction should occur to itself to introduce such functional groups, or to introduce other substances to form copolymers so as to obtain such functional groups.
- the skilled person in the art can make modification to the gel based on actual needs such that the gel covering the electrode can have one functional group such as amido, two functional groups such as amido and carboxyl, or three functional groups at the same time such as amido, carboxyl, and hydroxyl, or more other functional groups. This is not difficult for the skilled person in the art to realize, which will not be elaborated here.
- the above embodiment 1 only schematically explains the process of absorbing the Ca 2+ ions in water. During the process of carrying out the present invention, it may also need to absorb other ions e.g. cations such as sodium ions, iron ions, copper ions, or e.g. anions such as chloride ions, bromine ions, sulfate ions and carbonate ions.
- ions e.g. cations
- anions such as chloride ions, bromine ions, sulfate ions and carbonate ions.
- the surface of the first electrode 12 as the cathode should be covered by gel 16a.
- the surface of the second electrode 14 as the anode should be covered by gel 16a, i.e., using the ion absorption device as shown in Fig. IB.
- both the surface of the first electrode 12 as the cathode and the surface of the second electrode 14 as the anode should be covered by gel 16a, i.e., using the ion absorption device as shown in Fig. 1C.
- the gels covering the first electrode 12 and the second electrode 14 may differ from each other based on needs. This is not difficult for the skilled person in the art to understand.
- the ion absorption device as shown in Figs. 1A-1C and Fig. 2 may comprise an input 18 for inputting the liquid 26a, e.g. water containing Ca 2+ ions etc.
- the ion absorption device as shown in Figs. 1A-1C may further comprise an output 22 for outputting water after removal of the Ca 2+ ions etc.
- the liquid 26a input from the input 18 is hard water containing Ca 2+ ions, Mg 2+ ions etc.
- the ion absorption device 10a, 20a or 30a it is soft water output from the output 22 with the Ca 2+ ions, Mg 2+ ions, etc. removed.
- what are inputted and outputted from the input 18 and the output 22 should be respectively water containing heavy metal ions and the corresponding deionized water. This is not difficult to understand.
- agarose of 2g can be dissolved in deionized water of 100ml.
- the agarose solution is poured into an electrode module containing electrodes, e.g. the electrode module containing the first electrode 12 and/or the electrode module containing the second electrode 14.
- conductive material 24, such as carbon cloth is applied between the electrode module and the agarose solution.
- the purpose of applying the carbon cloth lies in enhancing the bonding force between the agarose gel formed by the agarose solution and the electrode due to the concavo-convex shape of the surface of the carbon cloth.
- the agarose gel is formed on the surface of the first electrode 12 or the surface of the second electrode 14 or the surfaces of both. Subsequently, the electrode covered by the gel 16a is used for ion absorption.
- the embodiment 2 takes the agarose gel formed on the surface of the electrode as example. According to the teaching of the present invention, the skilled person in the art needs to select different gel materials for absorbing different ions in the liquid 26a. After the corresponding gel materials are selected, it is not difficult to fabricate the corresponding gel on the corresponding electrode surface. It will not be elaborated in the present invention.
- the agarose gel fabricated in embodiment 2 will be used to cover the surfaces of the first electrode 12 and the second electrode 14 to perform the following experiment.
- the liquid 26a used in embodiment 3 is water containing Ca 2+ , C0 3 2 ⁇ , K + and CI " ions.
- the liquid 26a is input from the input 18 to a reaction chamber constituted by the first electrode 12 and the second electrode 14, and the agarose gel covering the first electrode 12 and the second electrode 14.
- DC voltage of 30V is applied on the first electrode 12 and the second electrode 14, standard titration is used to detect the content of ions in the liquid 26a.
- Table 1 The detected data is shown in Table 1 below.
- Table 1 Absorption of different cations and anions under a voltage of 30 V.
- the initial concentrations of the Ca 2+ , C0 3 2 ⁇ , K + and CI " ions are respectively 4.8mM, 5.0mM, 5mM, 5mM.
- the detected concentrations of the Ca 2+ , C0 3 2 ⁇ , K + and CI " ions are respectively 3.2mM, 3.6mM, 2.67mM, 3.28mM.
- the detected concentrations of the Ca 2+ , C0 3 2" , K + and CI " ions are respectively 1.8mM, 3.0mM, 0.7 ImM, 1.09mM.
- the detected concentrations of the Ca 2+ , C0 3 2" , K + and CI " ions are respectively 0.54mM, 1.2mM, 0.36mM, 0.55mM. It can be seen from the above experimental data that the longer time the voltage is applied, the lower the concentrations of the residual ions in the liquid 26a are, which means that more and more ions are absorbed on the agarose gel.
- the above embodiments 1-3 of the present invention only take the agarose gel as example. It is not difficult for the skilled person in the art to understand that natural polymers or synthetic polymers may be used in the process of carrying out the present invention.
- the natural polymers may comprise: agarose, methylcellulose and hyaluronan etc.
- the synthetic polymers may comprise: polyacrylamide, polyvinyl alcohol, acrylate polymers and copolymers etc.
- the gels listed above are all ions-permeable gels with functional groups. In the case of applying a voltage, the ions e.g. cations such as sodium ions, iron ions, copper ions, or e.g.
- anions such as chloride ions, bromine ions, sulfate ions and carbonate ions in the liquid can be chelated together with the functional groups in the gel by covering the surface of the electrode with such gels. Thereby, these ions are quickly immobilized in the gel, and the absorption efficiency is improved.
- Fig. 3 A schematically shows a pH adjustor 40.
- Fig. 3B schematically shows a pH adjustor 50 in an alternative embodiment of the present invention.
- One electrode of the electrode pair 12, 14 is covered by a gel 16a, the gel 16a absorbs H + or OH " ions in a liquid 26a when a voltage is applied on the electrode pair 12, 14.
- the second electrode 14 as shown in Fig. 3B is covered by e.g. hyaluronic acid gel, which gel has hydroxyl functional groups.
- conductive material 24 e.g.
- Figs. 4A-4C of the present invention will be described below.
- Fig.4A schematically shows an ion desorption device according to one aspect of the present invention.
- Fig. 4B schematically shows an ion desorption device in an alternative embodiment of the present invention.
- Fig. 4C schematically shows an ion desorption device in another alternative embodiment of the present invention.
- All of the ion desorption devices 10b, 20b, 30b as schematically shown in Figs. 4A-4C comprise an electrode pair 12, 14, at least one electrode of the electrode pair 12, 14 is covered by an ions-permeable gel 16b with functional groups, the ions absorbed in the gel 16b is desorbed into a liquid 26b when a reverse voltage is applied on the electrode pair 12, 14.
- FIG. 4A-4C only lies in that the gel 16b is applied at different positions.
- Fig. 4A only the first electrode 12 is covered by the gel 16b
- Fig. 4B only the second electrode 14 is covered by the gel 16b
- Fig. 4C both the first electrode 12 and the second electrode 14 are covered by the gel 16b.
- Figs. 4A-4C is equivalent to a reverse operation of the ion absorption process as shown in Figs. 1 A-1C.
- the ions captured in the gel need to be released, thus it is benefit for recycle use of the gel on the one hand, and acquisition of solution with desired ion content on the other hand.
- a reverse voltage is applied on the electrode pairl2, 14, wherein at least one electrode of the electrode pair 12, 14 is covered by an ions-permeable gel 16b with functional groups in order to desorb the ions absorbed in the gel 16b into the liquid 26b.
- the absorbed cations are released from the gel 16b and get into the liquid 26b.
- a positive voltage can be applied to the electrode covered by the gel, in this way, since the polarity of the electrode and that of the cations absorbed in the gel are same, a repulsive effect is generated, thereby the cations absorbed in the gel are desorbed into the liquid 26b.
- the similar operation can be performed to the absorbed anions, i.e., applying a negative voltage to the electrode covered by the gel, so as to desorb the anions absorbed in the gel into the liquid 26b. This is easy for the skilled person in the art to understand.
- both the first electrode 12 and the second electrode 14 are covered by agarose gel.
- the first electrode 12 is covered by agarose gel with calcium ions absorbed therein
- the second electrode 14 is covered by agarose gel with chloride ions absorbed therein.
- the calcium ions and the chloride ions absorbed in the agarose gel are respectively released from the corresponding gels, and get into the liquid 26b.
- the water is oxidized to generate hydrogen ions, the hydrogen ions neutralize the hydroxyl ions in the gel.
- the second electrode 14 as the cathode the water is deoxidized to generate hydroxyl ions, the hydroxyl ions neutralize the hydrogen ions in the gel.
- the gel 16b used in the ion desorption device in the respective embodiments of the present invention may comprise natural polymers or synthetic polymers, wherein the natural polymers may comprise: agarose, methylcellulose and hyaluronan; the synthetic polymers may comprise: polyacrylamide, polyvinyl alcohol, acrylate polymers and copolymers.
- the ion desorption device in the respective embodiments of the present invention may comprise conductive materials 24 between at least one electrode of the electrode pair 12, 14 and the gel 16b, the conductive materials 24 include at least one of: titanium, platinum, gold, rhodium, ruthenium; Ti-Ru alloy, graphite, active carbon, porous carbon paper or cloth.
- the present invention may further provide an ion absorption method.
- the method may comprise the steps of: applying a voltage on an electrode pair 12, 14, wherein at least one electrode of the electrode pair 12, 14 is covered by ions-permeable gel 16a with functional groups, such that the gel 16a absorbs ions in the liquid 26a.
- the present invention may further provide an ion desorption method.
- the method may comprise the steps of: applying a reverse voltage on an electrode pair 12, 14, wherein at least one electrode of the electrode pair 12, 14 is covered by ions-permeable gel 16b with functional groups, so as to desorb ions absorbed in the gel 16b into a liquid 26b.
- the gel used therein may comprise natural polymers or synthetic polymers, wherein the natural polymers may comprise: agarose, methylcellulose and hyaluronan; the synthetic polymers may comprise: polyacrylamide, polyvinyl alcohol, acrylate polymers and copolymers.
- the conductive materials 24 include at least one of: titanium, platinum, gold, rhodium, ruthenium; Ti-Ru alloy, graphite, active carbon, porous carbon paper or cloth.
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- Organic Chemistry (AREA)
- Analytical Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Health & Medical Sciences (AREA)
- Molecular Biology (AREA)
- Electrochemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Dispersion Chemistry (AREA)
- Physics & Mathematics (AREA)
- Electromagnetism (AREA)
- General Health & Medical Sciences (AREA)
- Toxicology (AREA)
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Abstract
Description
Claims
Priority Applications (6)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
BR112015014933A BR112015014933A2 (en) | 2012-12-24 | 2013-12-19 | ph adjuster, ion desorption device, ph adjustment method and ion desorption method |
RU2015130652A RU2015130652A (en) | 2012-12-24 | 2013-12-19 | DEVICE AND METHOD FOR ABSORPTION / DESORPTION OF IONS, AND ALSO THE PH REGULATOR |
JP2015548849A JP2016505370A (en) | 2012-12-24 | 2013-12-19 | Ion absorption / desorption device and method, and pH controller |
US14/654,857 US20150336819A1 (en) | 2012-12-24 | 2013-12-19 | Ion absorption/desorption device and a method thereof as well as a ph adjustor |
CN201380067565.5A CN104870372A (en) | 2012-12-24 | 2013-12-19 | An ion absorption/desorption device and a method thereof as well as a ph adjustor |
EP13830111.4A EP2935121A1 (en) | 2012-12-24 | 2013-12-19 | An ion absorption/desorption device and a method thereof as well as a ph adjustor |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
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CNPCT/CN2012/001724 | 2012-12-24 | ||
CN2012001724 | 2012-12-24 |
Publications (1)
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WO2014102676A1 true WO2014102676A1 (en) | 2014-07-03 |
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Application Number | Title | Priority Date | Filing Date |
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PCT/IB2013/061124 WO2014102676A1 (en) | 2012-12-24 | 2013-12-19 | An ion absorption/desorption device and a method thereof as well as a ph adjustor |
Country Status (6)
Country | Link |
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US (1) | US20150336819A1 (en) |
EP (1) | EP2935121A1 (en) |
JP (1) | JP2016505370A (en) |
BR (1) | BR112015014933A2 (en) |
RU (1) | RU2015130652A (en) |
WO (1) | WO2014102676A1 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113322105A (en) * | 2021-07-02 | 2021-08-31 | 上海电气集团国控环球工程有限公司 | High-efficiency debenzolization and purification process for coke oven gas |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US3847788A (en) | 1970-03-27 | 1974-11-12 | R Wallace | Electrogel apparatus for removing electrolytes and concentrating the same from an aqueous solution |
US20110272292A1 (en) * | 2009-06-18 | 2011-11-10 | Hitachi Chemical Company, Ltd. | Metal collection method and metal collection device |
KR101136816B1 (en) * | 2011-07-26 | 2012-04-13 | 한국지질자원연구원 | Manufacturing method of electrode module for recovering metal ion, electrode module for recovering metal ion and device for recovering metal ion having the same |
-
2013
- 2013-12-19 EP EP13830111.4A patent/EP2935121A1/en not_active Withdrawn
- 2013-12-19 WO PCT/IB2013/061124 patent/WO2014102676A1/en active Application Filing
- 2013-12-19 RU RU2015130652A patent/RU2015130652A/en unknown
- 2013-12-19 US US14/654,857 patent/US20150336819A1/en not_active Abandoned
- 2013-12-19 JP JP2015548849A patent/JP2016505370A/en active Pending
- 2013-12-19 BR BR112015014933A patent/BR112015014933A2/en not_active IP Right Cessation
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US3847788A (en) | 1970-03-27 | 1974-11-12 | R Wallace | Electrogel apparatus for removing electrolytes and concentrating the same from an aqueous solution |
US20110272292A1 (en) * | 2009-06-18 | 2011-11-10 | Hitachi Chemical Company, Ltd. | Metal collection method and metal collection device |
KR101136816B1 (en) * | 2011-07-26 | 2012-04-13 | 한국지질자원연구원 | Manufacturing method of electrode module for recovering metal ion, electrode module for recovering metal ion and device for recovering metal ion having the same |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113322105A (en) * | 2021-07-02 | 2021-08-31 | 上海电气集团国控环球工程有限公司 | High-efficiency debenzolization and purification process for coke oven gas |
Also Published As
Publication number | Publication date |
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JP2016505370A (en) | 2016-02-25 |
RU2015130652A (en) | 2017-02-02 |
BR112015014933A2 (en) | 2017-07-11 |
US20150336819A1 (en) | 2015-11-26 |
EP2935121A1 (en) | 2015-10-28 |
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