WO2006037282A1 - Method for purifying liquids by using ionized aeration - Google Patents

Method for purifying liquids by using ionized aeration Download PDF

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Publication number
WO2006037282A1
WO2006037282A1 PCT/CZ2005/000042 CZ2005000042W WO2006037282A1 WO 2006037282 A1 WO2006037282 A1 WO 2006037282A1 CZ 2005000042 W CZ2005000042 W CZ 2005000042W WO 2006037282 A1 WO2006037282 A1 WO 2006037282A1
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WO
WIPO (PCT)
Prior art keywords
values
purifying
liquids
liquid
air
Prior art date
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Ceased
Application number
PCT/CZ2005/000042
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French (fr)
Inventor
Oleg Lysytchuk
Jaroslav Hegr
Wladislav Rytschkow
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
RYTSCHKOWA SVETLANA
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RYTSCHKOWA SVETLANA
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Filing date
Publication date
Application filed by RYTSCHKOWA SVETLANA filed Critical RYTSCHKOWA SVETLANA
Priority to US11/576,803 priority Critical patent/US7651617B2/en
Priority to EP05741683A priority patent/EP1797009A1/en
Publication of WO2006037282A1 publication Critical patent/WO2006037282A1/en
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

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Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B13/00Oxygen; Ozone; Oxides or hydroxides in general
    • C01B13/10Preparation of ozone
    • C01B13/11Preparation of ozone by electric discharge
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/4608Treatment of water, waste water, or sewage by electrochemical methods using electrical discharges
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/74Treatment of water, waste water, or sewage by oxidation with air
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/02Specific form of oxidant
    • C02F2305/023Reactive oxygen species, singlet oxygen, OH radical
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage

Definitions

  • the invention falls in area of methods for liquids purifying, especially fluids purifying, from harmful admixtures and microorganisms, and is possible to use for not only water purifying in natural reservoirs but in communal economy at water purifying or to purifying of municipal and industrial sewage water and sediments as well.
  • Method for liquids purifying is also usable in energetic, chemistry and metallurgy at physic-chemical modification of all sorts of liquid media including melts and gases.
  • the electrodes gas bubbles then fetch up solid elements of impurities on surface of liquid.
  • Contemporary electrochemical modification of liquids and electro- floatation is then described for example in patents US 3,893,900 or GB 1411388 and combination of electrochemical modification and ozonization for example in patent CZ 284039.
  • Essence of the invention is that purified liquid is remited to gas-dynamic dispersion by the help of air blasting, which is at first preliminary ionized in non-homogenous electrostatic field of coronary discharges, at voltage between electrodes in values from 3 to 80 kV and more, but not more than 10 millions V, at strength of current of coronae between electrodes in range of values 10 till 1000 mA and at specific load of electrical discharges in range of values from 0,1 to 1OkWh on 1m 3 Of conditioned fluid.
  • gas-dynamic dispersion of liquid is provided in canals sloping down below angles 30-50° to level of purified liquid at flow velocity of blasted air 10 to lOOm/s, at hydraulic resistance of canals in range of values from 1 ,5 to
  • Another essence of the invention is that blasted air is supported before ionization by reagents with high specific resistance exceeding values 10 7 Ohm. cm, whose quantity of dosage varies between 1 to 100 g/m 3 of blasted air.
  • reagents are chosen from groups CaO or SiO 2 or AI 2 O 3 and that air blasting into purified water is realized by high-speed ventilator
  • fig.1 is ground plan view of masked off arrangement whose body is created with hull of the vessel and fig.2 is transverse vertical cut of this device in level A-A.
  • Described device is created with hollow oblong body 1, consisting of side walls 101 , bottom 102 procured with median gullet 103, from arrowy forward panel 104, tail panel 105 and upper removable lid 106, whereby is tank for realization of purifying process created.
  • front panel 104 there are two balanced head openings 107 allowing inflow of polluted water, in tail panel 105 and spouts 108 for outfall of purified water and in upper part of the side walls 101 sets of lateral windows 109.
  • head opennings 107 is in the tank placed ventilator 2, procured partly with incoming neck 21 allowing supply of suctioned air and partly with reservoir 3 of the reagents.
  • ionizer 4 placed, created by set of electrodes 41 , lined up on high voltage generator 5.
  • Ionizer 4 mean his electrodes 41 , are placed in air chamber 6, inclosed in down direction with unpent shell 7, whose lower part is procured with crossway upwards sideway guided canals 71 sloped to horizontal level below angle 30-50° and delimited by upper barriers 72 and lower barriers 73.
  • collectors 8 of drops are set and beside outfall canals 71 are side walls 101 of the body 1 guided lateral chambers 110 created.
  • lateral chambers 110 are by its suction branches 91 lead in pumps 9, by the help of these is purified water brought in into lower part of filters 10, created for example by granular filters with suctable coal of subbase high 0,5-2m and speed of filtration of 1m/min. Pure water is lead away form upper part of the filters 10 through spouts 108 back to water reservoir.
  • moderated pressure ventilator 2 of load 60.000 m 3 /hour at exit pressure 5kPa, whose power consumption vary between values 80-85kW.
  • high voltage generator 5 has been used aggregates with supply voltage 380 V, high voltage to 8OkV, whereas current density for smooth coronary electrodes 41 has been leveled 0,08 - 0,1mA/m.
  • Foam from oxygenated organic compounds and microorganisms is lead away out of upper part of lateral chambers 110 by the help of non- illustrated special pump to cultivation and sediments from inorganic harmful substances settled in median gullet 103 at bottom 102 of the body 1 is regularly removed by the help of as well non- illustrated sludge pump.
  • reagents are coagulants, flocculants and adsorbents lead in ventilator air through reservoir 3, whose implicate increasing of concentration of free electrons in conditioned water pursuant to their adsorption on surface of solid adsorbents particles with high specific electric resistance in values more than 10 7 Ohm.cm.
  • those particles transfer its electric charges for microorganisms and organic compound destruction and settle at the bottom 102, from where are like sediment drainaged.
  • Proposed method has been tested at gas purification from dust coal of steam producing steam boiler in quantity 40t/hour and heated up by glance coal.
  • capacity of out coming gases was 100,000 m 3 /hour, starting gas dustiness 12,29 to 35,8 g/m 3 and hydraulic resistance of device 1 ,4kPa and residual dustiness of out coming gases 0,160 to 0,276 g/m 3 .
  • the level of gas purification is approximately equal to value of 99%.
  • Method for liquids purifying, especially fluids purifying, from harmful admixtures and microorganism according to the invention is possible to use for not only water purifying in natural reservoirs but in communal economy at water purifying or to purifying of municipal and industrial sewage water and sediments as well.
  • Method for liquids purifying is also usable in energetic, chemistry and metallurgy at physic-chemical modification of all sorts of liquid media including melts and gases.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Inorganic Chemistry (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

Method for liquids purifying, especially fluids purifying, from harmful admixtures and microorganisms by using aerating and incidence of electric charges, wherein purified liquid is undergone to gas-dynamic dispersion by the help of blast air, which is at first preliminary ionized in non-homogenous electrostatic field of coronary discharges at voltage between electrodes in values from 3 to 80 kV and more, but not more than 10 millions V, at corona current values between electrodes in value range from 10 to 1000mA and at specific power output of electrical discharges in values range from 0,1 to10kWh on 1m' of conditioned liquid.

Description

METHOD FOR PURIFYING LIQUIDS BY USING IONIZED AERATION
Art Domain
The invention falls in area of methods for liquids purifying, especially fluids purifying, from harmful admixtures and microorganisms, and is possible to use for not only water purifying in natural reservoirs but in communal economy at water purifying or to purifying of municipal and industrial sewage water and sediments as well. Method for liquids purifying is also usable in energetic, chemistry and metallurgy at physic-chemical modification of all sorts of liquid media including melts and gases.
Present prior art
There is known a method of water conditioning by complex of electric incidence of electric fields with voltage reaching value of piercing current in sizes 1-100 kV/cm, as described in publication Jakovlev S.V.and colleagues " Technology of electro-chemistry water conditioning" (Leningrad, Strojizdat 1987, page 207). Disadvantage of this way of water purifying method is its low productivity, namely only 4Ol / hour at load 1kW and energy demand depending on quality of conditioned water from 0.1 to δkWhour/ m3
There is also in knowledge method of water conditioning by ozonization according to publication Orlov V.A " Water ozonization" (Moscow, Strojizdat, 1984,page 89) where is mentioned that optimum dose of ozone is from 0,25 to 1 ,25 mg/liter, when his usage and mixing with water allows reducing of dose of used coagulants .In this way is possible to achieve quality of purifying, suitable for sanitary standard in standpoint of bacteria and viruses content. Water purifying is possible to carry out by simultaneously proceeding electro-coagulation and electro-floatation, as mentioned for example in patent US 3,822,204, wherein liquid goes through described arrangement above tabular electrodes in lower part of electro- floater above its bottom. The electrodes gas bubbles then fetch up solid elements of impurities on surface of liquid. Contemporary electrochemical modification of liquids and electro- floatation is then described for example in patents US 3,893,900 or GB 1411388 and combination of electrochemical modification and ozonization for example in patent CZ 284039.
Mutual disadvantage of all featured methods and devices for purifying and water conditioning is their relatively low productivity, backwardness of continuance of purifying process and imperfection of coordination of synchronous continuance of gas-dynamic and electro-physical modification of liquid.
Essence of the invention
Increasing of the quality of purifying of small and big capacities of liquids from harmful pollutants and microorganisms at contemporary decrease of operating costs, solves method for liquids purifying, especially fluids purifying, from harmful admixtures and microorganisms by using aerating and incidence of electrical discharge. Essence of the invention is that purified liquid is remited to gas-dynamic dispersion by the help of air blasting, which is at first preliminary ionized in non-homogenous electrostatic field of coronary discharges, at voltage between electrodes in values from 3 to 80 kV and more, but not more than 10 millions V, at strength of current of coronae between electrodes in range of values 10 till 1000 mA and at specific load of electrical discharges in range of values from 0,1 to 1OkWh on 1m 3Of conditioned fluid. Further essence of the invention is that gas-dynamic dispersion of liquid is provided in canals sloping down below angles 30-50° to level of purified liquid at flow velocity of blasted air 10 to lOOm/s, at hydraulic resistance of canals in range of values from 1 ,5 to
1OkPa and at specific consumption of dispersed water from 0,1 to 30 kg on 1m3 of blasted air.
Another essence of the invention is that blasted air is supported before ionization by reagents with high specific resistance exceeding values 107 Ohm. cm, whose quantity of dosage varies between 1 to 100 g/m3of blasted air.
Finally is essence of the invention that reagents are chosen from groups CaO or SiO2 or AI2O3 and that air blasting into purified water is realized by high-speed ventilator
Connection of gas-dynamic process of dispersion of conditioned water with electro- physic process of ionization of ventilator air, which disperses water, made possible removing of all diffusion speed limitation of process of physic-chemical interactions of the substances in liquid and gaseous phase. Further advantage is successful safe conditions for oxidation of harmful admixtures and destructed structures of microorganisms by highly active free radicals, atoms, and molecules of ozone and oxidized complex of oxygen and nitrogen atoms. Regarding to matter, that basic technical parameters of the process, mean flow speed of gas, regulation of liquid level high in used purifying device, voltage on electrodes and intensity of fluxion of coronary discharges between electrodes, are easily adjustable and controllable in wide scale of technical parameters combinations, method for purifying is possible to use and easily adapt to different capacities and level of liquid contamination. Because used processes of dispersion of conditioned water and processes of ionization of ventilator air by coronary electrical discharges are thermodynamically reliable, there is further increase of reliability of function and decrease of demands on operating and maintenance of used device. Inconsiderable contribution is then minimal consumption of reagents, whereby there is further decrease of expenses on purifying process. - A -
Description of the pictures on enclosed drawings
For illustration of introduced invention applied for purification of free levels of natural waters, such as lakes, ponds, dam reservoirs or rivers, is enclosed basic scheme of device for method application, wherein fig.1 is ground plan view of masked off arrangement whose body is created with hull of the vessel and fig.2 is transverse vertical cut of this device in level A-A.
Examples of carry out of the invention
Examplei :
For purification of surface layers of natural water in water reservoirs, where was detected excessive concentration of microorganisms, for example of anabaena and organic compounds with phosphorus content, phenols, and surface active substances, such as detergents, it is used floating type device, whereby is claimed method realized.
Described device is created with hollow oblong body 1, consisting of side walls 101 , bottom 102 procured with median gullet 103, from arrowy forward panel 104, tail panel 105 and upper removable lid 106, whereby is tank for realization of purifying process created. In front panel 104 there are two balanced head openings 107 allowing inflow of polluted water, in tail panel 105 and spouts 108 for outfall of purified water and in upper part of the side walls 101 sets of lateral windows 109. In the area of head opennings 107 is in the tank placed ventilator 2, procured partly with incoming neck 21 allowing supply of suctioned air and partly with reservoir 3 of the reagents. On air outlet from ventilator 2 is ionizer 4 placed, created by set of electrodes 41 , lined up on high voltage generator 5. Ionizer 4, mean his electrodes 41 , are placed in air chamber 6, inclosed in down direction with unpent shell 7, whose lower part is procured with crossway upwards sideway guided canals 71 sloped to horizontal level below angle 30-50° and delimited by upper barriers 72 and lower barriers 73. Above outfall of the canals 71 , collectors 8 of drops are set and beside outfall canals 71 are side walls 101 of the body 1 guided lateral chambers 110 created. Into lateral chambers 110 are by its suction branches 91 lead in pumps 9, by the help of these is purified water brought in into lower part of filters 10, created for example by granular filters with suctable coal of subbase high 0,5-2m and speed of filtration of 1m/min. Pure water is lead away form upper part of the filters 10 through spouts 108 back to water reservoir.
For realization of described device has been used moderated pressure ventilator 2 of load 60.000 m3 /hour at exit pressure 5kPa, whose power consumption vary between values 80-85kW. As high voltage generator 5 has been used aggregates with supply voltage 380 V, high voltage to 8OkV, whereas current density for smooth coronary electrodes 41 has been leveled 0,08 - 0,1mA/m.
At water purification is air from ventilator 2 lead in between electrodes 41 of ionizer 4, which generate free electrons and free radicals, whose sate air. Then is air lead in canals 71 filled with polluted water in blow through way. At this blowing through at speed 10-100 m/s at specific consumption of dispersive water from 0,1 to 30 kg/m3, which depends on high of level in body 1 tank, water effectively disperses onto a large number of drops and foam with large active surface of liquid and gaseous phase interaction, when hydraulic resistance of canals 71 is 1.5-10 kPa. Used ventilator air goes through, through drops collectors 8 and then is lead away through lateral windows 109 of the body 1. Foam from oxygenated organic compounds and microorganisms is lead away out of upper part of lateral chambers 110 by the help of non- illustrated special pump to cultivation and sediments from inorganic harmful substances settled in median gullet 103 at bottom 102 of the body 1 is regularly removed by the help of as well non- illustrated sludge pump. For the away of water purification processes by the help of reagents are coagulants, flocculants and adsorbents lead in ventilator air through reservoir 3, whose implicate increasing of concentration of free electrons in conditioned water pursuant to their adsorption on surface of solid adsorbents particles with high specific electric resistance in values more than 107 Ohm.cm. Inside of canals 71 those particles transfer its electric charges for microorganisms and organic compound destruction and settle at the bottom 102, from where are like sediment drainaged.
Example 2
Technically modified device has been checked out for gas purification from aluminous electrolyzes of metallurgical factory by the help of solution Na2CO3, where capacity of purified gas was approximately 360m3/hour, temperature of gases incoming into device 42-50° C, temperature of gases coming out of device 18-25°C and hydraulic resistance of gases 0,94-2kPa. According to chemical analysis in the composition of purified gas has been found 32-92g/l Na2CO3, 7-60 g/l NaHCO3 and 18-30g/l NaF.
At analysis of purified gases then measured value of gas dustiness before entering of the device was 0,16 to 0,27g/m3 and after passage through device in values 0,026 to 0,073 g/m3, which presents 85% level of dust and tar purification. At detection of HF content in gas, before entering of the device values were in range from 1 to 7 mg/m3 and after passage through device values were from 0 to 0,88 mg/m3, which presents achievement of level of gas purification from HF 70 to 100%.
Example 3
Proposed method has been tested at gas purification from dust coal of steam producing steam boiler in quantity 40t/hour and heated up by glance coal. At this process, capacity of out coming gases was 100,000 m3/hour, starting gas dustiness 12,29 to 35,8 g/m3 and hydraulic resistance of device 1 ,4kPa and residual dustiness of out coming gases 0,160 to 0,276 g/m3. The level of gas purification is approximately equal to value of 99%.
Industrial application
Method for liquids purifying, especially fluids purifying, from harmful admixtures and microorganism according to the invention is possible to use for not only water purifying in natural reservoirs but in communal economy at water purifying or to purifying of municipal and industrial sewage water and sediments as well. Method for liquids purifying is also usable in energetic, chemistry and metallurgy at physic-chemical modification of all sorts of liquid media including melts and gases.

Claims

PATENT CLAIMS
1. Method for liquids purifying, especially fluids purifying, from harmful admixtures and microorganisms by using aerating and incidence of electric charges, wherein purified liquid is undergone to gas-dynamic dispersion by the help of blast air, which is at first preliminary ionized in non-homogenous electrostatic field of coronary discharges at voltage between electrodes in values from 3 to 80 kV and more, but not more than 10 millions V, at corona current values between electrodes in value range from 10 to 1000mA and at specific power output of electrical discharges in values range from 0,1 to 10 kWh on 1m3 of conditioned liquid.
2. Method for liquids purifying according to claim 1, wherein gas-dynamic dispersion of liquid is provided in canals sloping below angle 30-50° according to level of purified liquid at flow velocity of blasting air 10 to 100m/s, at canal hydraulic resistance varying between values from 1,5 to 1OkPa and at specific consumption of dispersed water from 0,1 to 30kg on 1m3 of blast air.
3. Method for liquids purifying according to claims 1 and 2, wherein blast air is before ionization enriched of reagents with high specific resistance exceeding values 107 Ohm.cm, whose quantity dosage varies between values 1 to 100g/m3 of blast air.
4.Method for liquids purifying according to claim 3, wherein reagents are chosen from groups CaO or SiOa or AI2O3.
δ.Method for liquids purifying according to claims 1 to 4, wherein air blasting into purified water is realized by high-speed ventilator.
PCT/CZ2005/000042 2004-10-06 2005-05-25 Method for purifying liquids by using ionized aeration Ceased WO2006037282A1 (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
US11/576,803 US7651617B2 (en) 2004-10-06 2005-05-25 Method for purifying liquids by using ionized aeration
EP05741683A EP1797009A1 (en) 2004-10-06 2005-05-25 Method for purifying liquids by using ionized aeration

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
CZPV2004-1014 2004-10-06
CZ20041014A CZ297103B6 (en) 2004-10-06 2004-10-06 Method for purifying fluids by making use of ionized aeration

Publications (1)

Publication Number Publication Date
WO2006037282A1 true WO2006037282A1 (en) 2006-04-13

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US (1) US7651617B2 (en)
EP (1) EP1797009A1 (en)
CZ (1) CZ297103B6 (en)
RU (1) RU2355644C2 (en)
WO (1) WO2006037282A1 (en)

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3822204A (en) 1966-10-06 1974-07-02 Fmc Corp Method and apparatus for separation of sludge
US3893900A (en) 1972-05-24 1975-07-08 Stanley Electric Co Ltd Apparatus for treating wastewater using an electrolytic cell
GB1411388A (en) 1972-09-19 1975-10-22 Hartley Simon Ltd Electrolytic flotation apparatus
US5766447A (en) * 1995-12-21 1998-06-16 U.S. Philips Corporation Method and device for treating an aqueous solution
CZ284039B6 (en) 1992-06-04 1998-07-15 Eco Purification Systems B.V. Purification process of liquids
DE10014833A1 (en) 2000-03-24 2001-10-04 Luwatec Gmbh Luft Und Wasserte Intensive purification of mechanically, organically and/or biologically contaminated water, employs filtration and sintered distributors of pressurized, ionized air
US20020040875A1 (en) 2000-06-16 2002-04-11 Fantom Technologies Inc. Ozonation process
WO2002048053A1 (en) 2000-12-16 2002-06-20 University Of Strathclyde Decontaminated fluids and biocidal liquids
DE20122005U1 (en) 2000-03-24 2003-12-18 Luwatec Gmbh Luft- Und Wassertechnik Intensive purification of mechanically, organically and/or biologically contaminated water, employs filtration and sintered distributors of pressurized, ionized air

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4386055A (en) * 1980-12-19 1983-05-31 Joan McBride Ozonator with air actuated rotor

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3822204A (en) 1966-10-06 1974-07-02 Fmc Corp Method and apparatus for separation of sludge
US3893900A (en) 1972-05-24 1975-07-08 Stanley Electric Co Ltd Apparatus for treating wastewater using an electrolytic cell
GB1411388A (en) 1972-09-19 1975-10-22 Hartley Simon Ltd Electrolytic flotation apparatus
CZ284039B6 (en) 1992-06-04 1998-07-15 Eco Purification Systems B.V. Purification process of liquids
US5766447A (en) * 1995-12-21 1998-06-16 U.S. Philips Corporation Method and device for treating an aqueous solution
DE10014833A1 (en) 2000-03-24 2001-10-04 Luwatec Gmbh Luft Und Wasserte Intensive purification of mechanically, organically and/or biologically contaminated water, employs filtration and sintered distributors of pressurized, ionized air
DE20122005U1 (en) 2000-03-24 2003-12-18 Luwatec Gmbh Luft- Und Wassertechnik Intensive purification of mechanically, organically and/or biologically contaminated water, employs filtration and sintered distributors of pressurized, ionized air
US20020040875A1 (en) 2000-06-16 2002-04-11 Fantom Technologies Inc. Ozonation process
WO2002048053A1 (en) 2000-12-16 2002-06-20 University Of Strathclyde Decontaminated fluids and biocidal liquids

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
JAKOVLEV S.V., TECHNOLOGY OF ELECTROCHEMISTRY WATER CONDITIONING, 1987, pages 207

Also Published As

Publication number Publication date
US20090084729A1 (en) 2009-04-02
RU2355644C2 (en) 2009-05-20
CZ297103B6 (en) 2006-09-13
US7651617B2 (en) 2010-01-26
RU2007116983A (en) 2008-11-20
EP1797009A1 (en) 2007-06-20
CZ20041014A3 (en) 2006-07-12

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