WO2009007691A2 - Électrolyse d'eau salée - Google Patents

Électrolyse d'eau salée Download PDF

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Publication number
WO2009007691A2
WO2009007691A2 PCT/GB2008/002303 GB2008002303W WO2009007691A2 WO 2009007691 A2 WO2009007691 A2 WO 2009007691A2 GB 2008002303 W GB2008002303 W GB 2008002303W WO 2009007691 A2 WO2009007691 A2 WO 2009007691A2
Authority
WO
WIPO (PCT)
Prior art keywords
salt water
water
membrane
electrode
added
Prior art date
Application number
PCT/GB2008/002303
Other languages
English (en)
Other versions
WO2009007691A3 (fr
Inventor
Donald James Highgate
Jennifer Ann Morton
Original Assignee
Itm Power (Research) Ltd.
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Priority claimed from GB0713209A external-priority patent/GB0713209D0/en
Priority claimed from GB0801444A external-priority patent/GB0801444D0/en
Priority claimed from GB0802872A external-priority patent/GB0802872D0/en
Priority claimed from GB0808571A external-priority patent/GB0808571D0/en
Priority claimed from GB0808890A external-priority patent/GB0808890D0/en
Application filed by Itm Power (Research) Ltd. filed Critical Itm Power (Research) Ltd.
Priority to US12/667,441 priority Critical patent/US20100252445A1/en
Priority to AU2008273918A priority patent/AU2008273918B2/en
Priority to GB1000111.3A priority patent/GB2464014B/en
Publication of WO2009007691A2 publication Critical patent/WO2009007691A2/fr
Publication of WO2009007691A3 publication Critical patent/WO2009007691A3/fr

Links

Classifications

    • 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
    • C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/467—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
    • C02F1/4672—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
    • C02F1/4674—Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation with halogen or compound of halogens, e.g. chlorine, bromine
    • 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
    • C02F1/46—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
    • C—CHEMISTRY; METALLURGY
    • C25—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
    • C25B—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES FOR THE PRODUCTION OF COMPOUNDS OR NON-METALS; APPARATUS THEREFOR
    • C25B1/00—Electrolytic production of inorganic compounds or non-metals
    • C25B1/01—Products
    • C25B1/02—Hydrogen or oxygen
    • C25B1/04—Hydrogen or oxygen by electrolysis of water
    • C—CHEMISTRY; METALLURGY
    • C25—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
    • C25B—ELECTROLYTIC OR ELECTROPHORETIC PROCESSES FOR THE PRODUCTION OF COMPOUNDS OR NON-METALS; APPARATUS THEREFOR
    • C25B9/00—Cells or assemblies of cells; Constructional parts of cells; Assemblies of constructional parts, e.g. electrode-diaphragm assemblies; Process-related cell features
    • C25B9/70—Assemblies comprising two or more cells
    • C25B9/73—Assemblies comprising two or more cells of the filter-press type
    • 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
    • C02F1/46—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
    • C02F1/4693—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis electrodialysis
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/08—Seawater, e.g. for desalination
    • C—CHEMISTRY; METALLURGY
    • C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00—Apparatus for treatment of water, waste water or sewage
    • C02F2201/46—Apparatus for electrochemical processes
    • C02F2201/461—Electrolysis apparatus
    • C02F2201/46105—Details relating to the electrolytic devices
    • C02F2201/46115—Electrolytic cell with membranes or diaphragms
    • Y—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
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E60/00—Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
    • Y02E60/30—Hydrogen technology
    • Y02E60/36—Hydrogen production from non-carbon containing sources, e.g. by water electrolysis

Definitions

  • This invention relates to a method producing hydrogen and oxygen from salt water, and to the production of biologically active salt water.
  • Electrolytic production of hydrogen traditionally uses highly purified water, any contamination risks damaging the membrane, catalyst or electrode structures. Significant efforts have gone into methods of purifying water prior to the electrolysis but these tend to be energy-intensive, have high balance of plant and high space requirements. The ability to electrolyse water without the need for purifying would offer significant advantages. It would be particularly beneficial if the electrolyser system could electrolyse seawater directly.
  • HCAIs health care- associated infections
  • MRSA methicillin-resistant Staphylococcus aureus
  • Traditional methods of decontamination in hospitals include the use of low temperature steam, boiling water, and chemical disinfectants. However, these methods are either ineffective or leave undesirable residues which can cause damage to the component that is being decontaminated.
  • WO03/048421 discloses apparatus for electrolytically producing oxidation reduction potential water from aqueous salt solutions for use in disinfection, sterilisation, decontamination, and wound cleansing.
  • the apparatus includes an electrolysis unit having a three-compartment cell comprising a cathode chamber, an anode chamber, and a saline solution chamber. Water is passed through the anode and cathode compartments.
  • WO2005/094904 also discloses disinfectant solutions comprising electrochemically activated water obtainable from electrolysis of brine. It is indicated as preferred that the aqueous sodium chloride solution is fed into both the anode chamber and cathode chamber of the electrolysis cell. Access to safe drinking water is often difficult.
  • Desalination is used to provide safe drinking water.
  • a common method of desalination is by reverse osmosis. However, this is expensive and requires a high balance of plant.
  • the present invention solves three separate, but related problems. It was initially based on the realisation that salt water can be electrolysed to form hydrogen and oxygen for energy storage, which can then be used to produce potable water and energy in a fuel cell. Further, the process of electrolysis of salt water produces hydrogen in approximately the same quantities as for the electrolysis of purified water, without the need for expensive purification equipment. Hydrophilic membranes as used in the invention are not degraded by the high salt content, unlike conventional membranes. It has also been found that, when salt water is electrolysed, the electrolysed solution is biologically active. A further realisation was that the electrolysis of salt water may also be used to produce potable water directly.
  • the present invention is a method for producing hydrogen and oxygen using an electrolyser having first and second electrode compartments respectively on each side of a hydrophilic ion-exchange membrane, the method comprising adding salt water to one or both of the electrode compartments.
  • this also provides a route to producing potable water.
  • the present invention is a method of producing a biologically active solution using an electrolyser as defined above, the method comprising adding salt water to one or both of the electrode compartments.
  • the present invention is a method for reducing the salt content of salt water using an electrolyser as defined above, the method comprising adding salt water to one or both of the electrode compartments.
  • salt water means water comprising dissolved sodium chloride (NaCI).
  • the term encompasses both "brackish water", which contains approximately 5-35 ppt of dissolved salts, seawater, which contains approximately 35-50 ppt of dissolved salts, and brine, which contains only dissolved sodium chloride (NaCI).
  • seawater varies around the world, but it typically contains dissolved chloride (approximately 15-25 ppt), dissolved sodium ions (approximately 5-15 ppt), dissolved sulphate ions (approximately 1-2 ppt) and dissolved magnesium ions (approximately 1 -2 ppt).
  • Seawater may contain other dissolved substances such as potassium ions, calcium carbonate, bromide and iodide.
  • Brine is water containing dissolved sodium chloride (NaCI) only, i.e. it does not contain a substantial amount of any other dissolved salt.
  • NaCI sodium chloride
  • the term “brine” is interchangeable with “sodium chloride solution” and “saline”.
  • a solution that is described as being “electrochemically active” or “active”, means a solution which has undergone electrochemical activation. Such treatment typically involves exposure of the solution to a substantial electrical potential difference.
  • the method of the present invention involves the electrolysis of brine to produce an electrochemically active solution.
  • the electrochemically active solution may be biologically active.
  • biologically active solution means a solution that has activity against biological organisms.
  • the solution may be bactericidal or yeasticidal, for example.
  • solution encompasses both water and aqueous solutions, such as brine.
  • potable water means water of sufficient quality to serve as drinking water.
  • potable water means water containing less that 1 ppt of dissolved salts.
  • One aspect of the present invention is a method for reducing the salt content of salt water.
  • the present invention is a method for reducing the NaCI content of salt water.
  • the amount of Na + in one of the electrode compartments is reduced.
  • the amount of Na + in the anode compartment is reduced (in a cell having a CE , i.e. cationic exchange, membrane).
  • the reduction in salt content is substantial.
  • the reduction is more than 40%, more than 50%, more than 60%, more than 70%, more than 80%, or more than 90%.
  • Hydrophilic ion-exchange membranes are known to those skilled in the art, see for example WO03/023890, the content of which is incorporated herein by reference.
  • the hydrophilic membrane is preferable a hydrophilic polymer.
  • the hydrophilic membrane is obtainable from the copolymerisation of hydrophilic and hydrophobic monomers that give a hydrophilic polymer on polymerisation.
  • the copolymerisation is conducted in the presence of water and a monomer including a strongly ionic group. Examples of suitable monomers are disclosed in WO03/023890.
  • the hydrophilic membrane is an anion exchange solid polymer membrane (AESPE), in which the charge carriers are the OH ' and Cl " ions.
  • AESPE membranes are disclosed in WO2005/060018 and WO2006/032887, the contents of which are incorporated herein by reference. When an AESPE membrane is used, hydrogen is produced at the cathode. AESPE membranes are preferred as they may reduce catalyst degradation. They also allow the optimisation of the catalyst in each chamber. Further, they allow catalysts to be used, which are not compatible with CE materials.
  • a proton exchange solid polymer membrane (more generally termed a cation exchange solid polymer membrane (CESPE)), may be used. Hydrogen is produced at the cathode and oxygen at the anode.
  • CESPE cation exchange solid polymer membrane
  • Such a cell can be operated by supplying seawater either to the oxygen electrode, or to both electrodes.
  • salt water may be added to each of the electrode compartments (the anode and the cathode). If using an electrolyser with a CE membrane, then sodium ions (Na + ) will move from the anode to the cathode, such that the Na + content of the solution on the anode side of the membrane is reduced.
  • the Cl ' present in the anode solution may be electrolysed to form chloride and hypochlorous acid. This may cause the anode water to become chlorinated, but the chlorine compounds may be removed before drinking. Any other positively charged ions present in the anode solution may also migrate through the membrane, to the cathode compartment such as H + , K + , Mg 2+ and Ca 2+ . This embodiment is illustrated in Examples 1 and 2.
  • salt water may be added to one electrode compartment only, and the other electrode compartment may be substantially 'dry'.
  • salt water may be added to the anode side only of a CE membrane, and the cathode side of the membrane may be substantially dry. Since the membrane contains water, a very small amount of water may move from the membrane into the cathode compartment. However, even if this occurs, then the amount of water in the cathode compartment will be negligible. After electrolysis, the salt content of the anode solution may be reduced. This embodiment is illustrated in Example 3.
  • An AE (anionic exchange) electrolyser system is suitable for use in the invention.
  • the membrane is an anionic exchange membrane.
  • Sodium chloride solution may be added to the cathode and HPLC-grade water may be added to the anode.
  • a CE electrolyser system may also be used in the invention.
  • the ion exchange membrane is a cationic exchange membrane.
  • Sodium chloride solution may be added to the anode, and HPLC-grade water may be added to the cathode. In both embodiments, chlorine is produced at the anode, but this may react further once in solution.
  • a list of side reactions that may occur are listed below:
  • hypochlorous acid and the hypochlorite ion (OCI-) are present in equilibrium. It is thought that hypochlorous acid may be a more effective disinfectant than the hypochlorite ion and therefore it may be preferable to alter the reaction conditions to favour the formation of hypochlorous acid.
  • the equilibrium between HOCI and OCI- may be manipulated by controlling the pH of the solution, for example.
  • the present invention is a method of producing a biologically active solution.
  • the electrolysis cell used in that method comprises a CE membrane, and has a first electrode compartment containing brine, but a second electrode compartment that is substantially dry. This produces biologically active brine.
  • an electrolyser suitable for use in the invention comprises an AE membrane.
  • brine is added to the cathode compartment and water is added to the anode compartment.
  • the brine and/or the water may be rendered biologically active. Having water on one side of the membrane may lead to a simplified and therefore lower-cost balance of plant.
  • An electrolyser suitable for use in a method of the invention can be sized to fit the decontamination requirements.
  • the method of the invention is performed using a small electrolyser attached to mop buckets filled with salt water, which activate the cleaning solution during use.
  • An alternative embodiment uses a large electrolyser situated in a sterilisation room, where equipment requiring sterilisation is passed through the activated brine for a predefined period of time.
  • a further embodiment uses a small device positioned in a re-sealable container which, in addition to being an electrolyser, also has the ability to atomise the biologically active solution, for example by having an ultrasonic atomiser nozzle.
  • a container is filled with brine; the brine may then be charged (by powering the electrolyser and activating the brine to a predefined level), atomised, and then used to clean, disinfect or sterilise.
  • the device may be reused by re-filling with brine and then re-charging. This may occur either when the device is empty, or when the brine has become inactive.
  • the device may additionally contain a small fuel cell and gas storage facility, which can store and then use any hydrogen and/or oxygen gas that may be created during activation of the brine.
  • This fuel cell may be used to power a monitoring device (for example, a clock, which resets on re-activation), thus giving a warning when the solution is no longer sufficiently active.
  • the container comprises an electrolyser having an AE membrane.
  • the electrolyser electrolyses both water and brine, so that the water becomes biologically active.
  • the activated material may be used immediately on exit of the electrochemical device as a fluid, a fluid in a gas, or as a microscopic dispersion of droplets in gas.
  • the material may be stored after activation, in controlled conditions, which may extend the activation life.
  • the conditions to be controlled may include pressure, temperature, and UV exposure levels.
  • the present invention may be useful for the decontamination of large areas.
  • decontamination of large spaces or surfaces is useful in a variety of applications, for example in hospitals and other care facilities, cruise ships, aircraft, ventilation systems, swimming pools, schools, interior and exterior of buildings, underground tunnels and stations, cooling towers, water storage facilities, restaurants and hotels. Decontamination may be required on a routine basis to prevent infections such as MRSA or Legionella. Alternatively, it may be required on a one-off basis following an infection outbreak or a terrorist attack.
  • One aspect of the present invention effectively combines the production of potable water (e.g. from sea water) with the production and transmission of energy.
  • potable water e.g. from sea water
  • the output from solar photovoltaic electricity generation or wind power is used to power the seawater electrolysis process, the resulting hydrogen transmitted to areas where power is required, and the hydrogen combined with atmospheric oxygen in a fuel cell, the result is clean (low carbon footprint) energy and potable water as the outputs. This effectively removes the need for a separate desalination stage, thus reducing operating costs and environmental pollution.
  • An electrolyser cell with an active area of 8 cm 2 was set up using a cationic (OR) membrane and platinum-coated titanium catalyst.
  • OR cationic
  • the composition of an OR membrane is disclosed in WO03/013890. The cell was run at 0.555 A/cm 2 (4.4 A in total) at a flow rate of 70 ml/min.
  • the salt content of the circulating solution was measured pre and post- electrolysis at both the anode and the cathode, so that any changes in salt content due to electrolysis could be calculated.
  • Example 2 The same cell as used in Example 1 was run with the sodium chloride solution re-circulated around both the anode and cathode for 1 hour with 3.5 wt % solution. The results are shown in Table 2. Table 2
  • test cell was run using a one-pass CE system with a dry cathode. The experiments were carried out using a range of sea salt concentrations from 0.5- 3.65 wt %. The electrolysed solutions were tested for chlorine concentration and for salinity. The test cell was a small evaluation cell ( ⁇ 4.5 cm 2 active area). The test results are shown in Table 3. Table 3
  • Example 4 the NaOCI that is produced in the anode has been shown to offer a decontamination effect.
  • the NaOCI may be filtered prior to drinking, if this is necessary. Filtering methods are known to those of ordinary skill in the art.
  • Example 4
  • sea salts were purchased from Sigma Aldrich.
  • the average salinity of seawater was chosen as a base test (3.5%), which was prepared using the following components: chloride 19290 mg/L sodium 10780 mg/L sulfate 2660 mg/L magnesium 1320 mg/L potassium 420 mg/L calcium 400 mg/L carbonate/bicarbonate 200 mg/L strontium 8.8 mg/L boron 5.6 mg/L bromide 56 mg/L iodide 0.24 mg/L lithium 0.3 mg/L fluoride 1.0 mg/L
  • the seawater was circulated at the anode and cathode of a PEM cell at a rate of 50 ml/min. The water did a single pass only. No re-circulation occurred.
  • the cell was a simple test cell comprising a Perspex cell housing/manifold with titanium electrodes and a titanium electrode mesh. Each cell had an active area of -6.6 cm 2 .
  • the membrane was an acidic membrane which was cured via UV polymerisation.
  • the electrolyser test was run at 1 Amp (150 mA/cm 2 ) for 20 minutes, without significant voltage rise. After 20 mins the voltage began to increase, possibly due to a contamination of catalysts from salt deposits or reactions occurring at the oxygen producing side. The voltage was approximately 4 V, significantly higher than would be expected for pure water electrolysis.
  • the seawater test was repeated for an alkaline membrane; the same test cell was used. Seawater made from the same components was used, and again flowed with a single pass at a rate of 50 ml/min.
  • the membrane was an alkaline membrane which was cured by UV polymerisation.
  • the electrolyser test was run at 1 Amp ((150 mA/cm 2 ) for a period of 5 hours. After an initially high voltage (5 V), the voltage dropped (within approximately 30 minutes) to 4.4 V and remained steady for the remainder of the test period. Oxygen production was approximately half that expected for pure water electrolysis, indicating that side-reactions were occurring, potentially creating alternative commercially valuable products.
  • Example 6
  • a negative control (bacteria + 4 M brine solution) and a positive control (bacteria) were also tested.
  • the solutions were tested against E. coli K12 at three different contact times; 1 , 5 and 30 minutes.
  • the method followed was the standard method for the first phase of testing of any liquid chemical disinfectant or antiseptic.
  • Each of the four test solutions showed bacterial survival in comparison to the controls of less than 0.0001%.
  • the positive and negative controls showed approximately 80 million E.coli per ml.
  • brine was circulated around the cathode and HPLC water was circulated around the anode, using a one-pass system.
  • the cell was run at 0.5 A (approximately 70 mA/cm 2 ) at a flow rate of 10 ml/min.
  • a sample of electrolysed water was extracted from the anode side of the cell, and tested against MRSA at three different contact times; 1 , 5 and 30 minutes. At all three contact times, the test solution showed bacterial survival in comparison to the controls of less than 0.01%.
  • the method of testing followed was the standard method for the first phase of testing of any liquid chemical disinfectant or antiseptic.
  • Example 10 A sample was also extracted from the cathode (brine) side of the cell, and tested against MRSA at three contact times; 1 , 5 and 30 minutes. At all three contact times, the test solution showed bacterial survival in comparison to the controls of less than 0.01%.
  • brine was circulated around the cathode and HPLC water was circulated around the anode, using a one-pass system.
  • the cell was run at 1 A (approximately 140 mA/cm2) at a flow rate of 50 ml/min.
  • a sample of electrolysed water was extracted from the anode and the brine from cathode of the cell for testing.
  • brine was circulated around the anode and HPLC water was circulated around the cathode, using a one-pass system.
  • the cell was run at 1 A (approximately 140 mA/cm2) at a flow rate of 50 ml/min.
  • a sample of electrolysed water was extracted from the cathode and the brine from anode of the cell for testing.

Abstract

L'invention concerne un procédé pour produire de l'hydrogène et de l'oxygène à partir d'eau salée au moyen d'un dispositif d'électrolyse comprenant un premier et un second compartiment d'électrode disposés respectivement sur chaque côté d'une membrane hydrophile échangeuse d'ions. Ledit procédé consiste : à ajouter de l'eau salée dans un ou les deux compartiments de l'électrode et à électrolyser l'eau salée. L'invention concerne également un procédé pour produire une solution biologiquement active au moyen du dispositif d'électrolyse précité, ledit procédé consistant : à ajouter de l'eau salée dans un ou les deux compartiments de l'électrode et à électrolyser l'eau salée. L'invention concerne enfin un procédé pour réduire la teneur en sel de l'eau salée au moyen du dispositif d'électrolyse précité, ledit procédé consistant : à ajouter de l'eau salée dans un ou les deux compartiments de l'électrode et à électrolyser l'eau salée.
PCT/GB2008/002303 2007-07-07 2008-07-07 Électrolyse d'eau salée WO2009007691A2 (fr)

Priority Applications (3)

Application Number Priority Date Filing Date Title
US12/667,441 US20100252445A1 (en) 2007-07-07 2008-07-07 Electrolysis of Salt Water
AU2008273918A AU2008273918B2 (en) 2007-07-07 2008-07-07 Electrolysis of salt water
GB1000111.3A GB2464014B (en) 2007-07-07 2008-07-07 Electrolysis of salt water

Applications Claiming Priority (10)

Application Number Priority Date Filing Date Title
GB0713209.5 2007-07-07
GB0713209A GB0713209D0 (en) 2007-07-07 2007-07-07 Electrolysis of seawater
GB0801444A GB0801444D0 (en) 2008-01-25 2008-01-25 Method of performing chemical reactions
GB0801444.1 2008-01-25
GB0802872.2 2008-02-15
GB0802872A GB0802872D0 (en) 2008-02-15 2008-02-15 Electrolysis
GB0808571.4 2008-05-10
GB0808571A GB0808571D0 (en) 2008-05-10 2008-05-10 Electrolysis
GB0808890.8 2008-05-15
GB0808890A GB0808890D0 (en) 2008-05-15 2008-05-15 Electrolysis

Publications (2)

Publication Number Publication Date
WO2009007691A2 true WO2009007691A2 (fr) 2009-01-15
WO2009007691A3 WO2009007691A3 (fr) 2009-04-16

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PCT/GB2008/002303 WO2009007691A2 (fr) 2007-07-07 2008-07-07 Électrolyse d'eau salée

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US (1) US20100252445A1 (fr)
AU (1) AU2008273918B2 (fr)
GB (1) GB2464014B (fr)
WO (1) WO2009007691A2 (fr)

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