WO2010033021A1 - Device and method for disinfection and/or purification of a fluid - Google Patents

Device and method for disinfection and/or purification of a fluid Download PDF

Info

Publication number
WO2010033021A1
WO2010033021A1 PCT/NL2009/050555 NL2009050555W WO2010033021A1 WO 2010033021 A1 WO2010033021 A1 WO 2010033021A1 NL 2009050555 W NL2009050555 W NL 2009050555W WO 2010033021 A1 WO2010033021 A1 WO 2010033021A1
Authority
WO
WIPO (PCT)
Prior art keywords
fluid
particles
reactor
providing
cathode
Prior art date
Application number
PCT/NL2009/050555
Other languages
French (fr)
Inventor
Mateo Jozef Jacques Mayer
Sybrandus Jacob Metz
Gert-Jan Klijn
Original Assignee
Stichting Wetsus Centre Of Excellence For Sustainable Water Technology
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
Application filed by Stichting Wetsus Centre Of Excellence For Sustainable Water Technology filed Critical Stichting Wetsus Centre Of Excellence For Sustainable Water Technology
Priority to EP09748505A priority Critical patent/EP2352704A1/en
Publication of WO2010033021A1 publication Critical patent/WO2010033021A1/en

Links

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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/288Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
    • 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
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/46104Devices therefor; Their operating or servicing
    • 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
    • C02F1/48Treatment of water, waste water, or sewage with magnetic or electric fields

Definitions

  • an electrolyze may occur in the reactor that leads to the presence of radicals on the surface of the particles.
  • These radicals include OH, Cl and O-radicals. These radicals are also capable of killing (micro-) organisms.
  • the direct current component is combined with an alternating current component as both components increase each other's effects for disinfecting and purifying a fluid.
  • the organic contaminations in the fluid adsorb to the charged particles. By the presence of radicals on the surface of these particles such contaminations will be decomposed.
  • Circuit 16 comprises a direct current source 18 and alternating source 20.
  • Direct current source 18 is able to apply a potential difference between cathode 6 and anode 8.
  • One of the primary objectives of providing a direct current is the decomposition of organic contaminations.
  • the alternating current source 20 is able to provide for example a sinusoid, for example with a frequency of 10OkHz, to the electrodes 6,8.
  • the primary objective of the alternating current is disinfection of the fluid.

Abstract

The present invention relates to a device and a method for disinfection and purification of a fluid, like drinking water. The device comprises: - a fluidized bed reactor provided with a suspension of conductive particles that are capable of adsorbing contaminating elements like organisms, organic compounds and/or ions; - an anode and a cathode for providing a substantial number of particles with a charge; - means for generating an electrical and/or electromagnetic field by providing a potential difference between the anode and the cathode; and - an inlet for a fluid, possibly comprising contaminating elements, wherein the fluid is exposed in the device to the electrical and/or electromagnetic field thereby disinfecting and/or purifying the fluid.

Description

DEVICE AND METHOD FOR DISINFECTION AND/OR PURIFICATION OF A
FLUID
The present invention relates to a device for disinfection and/or purification of a fluid, like drinking water .
Providing a sufficient amount of drinking water is important for the growing worldwide population. Existing devices for purification and disinfection of fluids like drinking water use a significant amount of energy and often require dozing additional components like chemicals to the process .
The present invention has for its object to provide a device that requires a limited amount of energy for the purification and/or disinfection. In addition, the invention aims at minimizing the dozing of chemicals to the process.
This objective is achieved with the device according to the invention, comprising: - a fluidized bed reactor provided with a suspension of conductive particles that are capable of adsorbing contaminating elements like organisms, organic compounds and/or ions; an anode and a cathode for providing a substantial number of particles with a charge; means for generating an electrical and/or electromagnetic field by providing a potential difference between the anode and the cathode; and - an inlet for a fluid, possibly comprising contaminating elements, wherein the fluid is exposed in the device to the electrical and/or electro-magnetic field for disinfecting and/or purifying the fluid.
A fluidized bed reactor, according to the invention is provided with a suspension of particles. These particles are conductive and are also capable of adsorbing elements. Such elements comprise living organisms, organic compounds and/or ions. In the reactor a fluid, gas or liquid, is forced through the suspension with the conductive particles. This forcing of the fluid through the solid material is such that the particles are fluidized. In this fluidized state, the force of the fluid acting on the particles balances the weight of these particles. The particles will move around and collide with other particles and other components of the reactor. The reactor, which may have a shape of a pipe or a stirred tank, comprises at least one anode and one cathode. More electrodes may be provided. The number of the electrodes may depend, for example on the dimensions of the reactor, the throughput of fluid and the charge that is applied to the particles. The anode and the cathode are in use connected to a means for generating a potential difference between the anode and the cathode. At an inlet of the reactor, a fluid comprising contaminations is fed to the suspension of conductive particles. The incoming fluid fluidizes the conductive particles that collide with each other, the sidewall of the reactor and the electrodes in the reactor. The potential difference between the anode and the cathode has the effect that particles colliding with an electrode are given a potential. This means that between separate particles a potential difference may be present and that during a collision a transfer of charges will take place .
The electrical field between two particles in a fluidized bed is approximately inversely proportional to the distance between the particles. This electrical field is relatively strong just before two particles collide. The elements or contaminations in the incoming fluid will de adsorbed by the particles. This adsorption may take place by catalyzing the elements or contaminations by the charge on the particles. The effect of this adsorption is that the contaminations are exposed to a relatively high electrical field in case the particle to which it is adsorbed is about to collide with another particle. This electrical field can be so strong that electro-poration occurs and organisms are killed. This disinfects or purifies the fluid, like drinking water, without requiring a significant amount of energy and use of chemicals. The contaminations in the fluid may comprise (micro-) organisms, viruses, protozoa, algae, worm eggs etc. Also the contaminations may comprise organic contaminations like medicine, humus acids etc. Disinfection and/or purification also relate to bromate reduction and capacitive de-ionization .
Besides one inlet to the reactor, it is also possible to provide the reactor according to the invention with a second inlet for the supply of for example a gas to influence the fluidization of the particles and the transfer of charges to and from the particles. Furthermore, it is possible to circulate the contents of the rector, according to the invention, to obtain a type of residence time reactor, using for example an agitator or stirrer. This type of reactor is preferably used in case of relatively small particles with a diameter of below 1 mm. Preferably, electrodes are provided with relatively large specific surface areas. Also preferably, the electrodes are bar- shaped. In a preferred embodiment according to the present invention the conductive particles comprise active carbon or polymer material provided with a metal coating.
For absorbing it is beneficial for the particles to have a relatively large surface area. For this reason, active carbon particles can be used. Other particles can have polymer material or a conductive material as base material. A metal coating, for example comprising silver, can be provided on the particles. The diameter of the particles is preferably in a range of 10 nm to 10 cm, more preferably in the range of 100 nm to 5 cm and most preferably in the range of 100 μm to 1 cm. The density of the particles is preferably larger than 1000 kg/m , although particles with a lower density may also be used. In a preferred embodiment according to the present invention the means for generating a potential difference varies the potential in time with an adjustable amplitude and/or frequency.
By providing a potential difference that varies in time, the charge that is given to the particles that collide with the electrodes depend on the time of the collision. This realizes more potential differences between the particles in the suspension and improves transfer of charge from these particles to each other, the reactor wall, and/or an electrode. The varying potential differences are preferably generated by providing an alternating current component to the anode and/or cathode. This alternating current component preferably comprises a frequency in the range of IHz-IOOGHz, more preferably IkHz-IMHz, even more preferably 10kHz-500kHz, and most preferably 30kHz-200kHz .
The cell membranes of the (micro-) organisms are irreversibly damaged and the organisms may be killed, using a frequency in a range of IHz-IOOGHz. Experiments have shown that smaller frequency ranges between IkHz-IMHz and 10kHz-500 kHz have a large influence on damaging the cell membranes. In fact, experiments have shown that a frequency in the range of 30kHz-200kHz has the most impact on the cells. The amplitude of the alternating current component preferably comprises an amplitude in the range of lOmV-lOOkV. The alternating current can have a sinusoid, a saw tooth, a block signal etc. or combinations thereof. In a preferred embodiment the alternating current is generated in a resonance circuit comprising at least a coil and a condensator that is connected to the electrodes of the reactor .
In a further preferred embodiment according to the present invention the potential differences between the electrodes comprise a direct current component.
By providing a direct current component between the electrodes an electrolyze may occur in the reactor that leads to the presence of radicals on the surface of the particles. These radicals include OH, Cl and O-radicals. These radicals are also capable of killing (micro-) organisms. As the charged particles collide at a relatively high frequency to the electrodes the (micro-) organisms are exposed to a relatively strong electrical field that may damage for example cell membranes of the organisms. Preferably, the direct current component is combined with an alternating current component as both components increase each other's effects for disinfecting and purifying a fluid. Also, the organic contaminations in the fluid adsorb to the charged particles. By the presence of radicals on the surface of these particles such contaminations will be decomposed. As the organic components decompose they are removed from the surface area of the particles. This has the effect that a driving force is maintained for adsorption of new organic contaminations to the surface. This is especially relevant in case of extremely low concentrations of these contaminations, for example on ppb-level, to be removed in a sustainable way from the fluid, without using chemicals or requiring regeneration of the particles.
The invention further relates to a method for disinfecting or purifying a fluid, like drinking water, comprising the steps of: providing a device according to any of claims 1- 11; providing the reactor at an inlet with fluid possibly comprising contaminations; disinfecting and/or purifying the fluid in the reactor; and - outputting the disinfected and/or purified fluid to an outlet of the reactor.
Such method provides the same effects and advantages as those stated with reference to the device. Further advantages, features and details of the invention are elucidated on the basis of preferred embodiments thereof, wherein reference is made to the accompanying drawings in which : figure 1 shows a schematic overview of a device according to the invention; - figure 2 shows an alternative embodiment used in an experiment; and figure 3 shows a schematic overview of a further alternative embodiment according to the present invention . A device 2 (figure 1) for disinfection and/or purification of a fluid like drinking water comprises a fluid bed reactor 4. Reactor 4 is provided with a cathode 6 and an anode 8. Furthermore, reactor 4 comprises particles 10 of activated carbon. At the bottom of reactor 4 is provided an inlet 12 for supply of water to reactor 4. On top of reactor 4 is provided an outlet 14 for the output of purified water. Electrodes 6,8 are connected in circuit 16. Circuit 16 comprises a direct current source 18 and alternating source 20. Direct current source 18 is able to apply a potential difference between cathode 6 and anode 8. One of the primary objectives of providing a direct current is the decomposition of organic contaminations. The alternating current source 20 is able to provide for example a sinusoid, for example with a frequency of 10OkHz, to the electrodes 6,8. The primary objective of the alternating current is disinfection of the fluid. By combining the direct current source 18 and alternating current source 20 a synergetic effect is realized in that both sources 18, 20 enhance each others effect. Contaminated water is supplied by inlet 12 to reactor 4. Particles 10, present in reactor 4 are charged by the electrodes 6,8. Organic components in the incoming water flow decompose and (micro-) organisms are damaged and possibly killed. This disinfects and purifies the water flow. Purified water is let to output 14 of reactor 4. To improve the fluidized bed behavior of the particles 10, an additional gas flow (not shown) may be provided to the reactor. Also, the content of reactor 4 may be circulated to improve its performance. Also, it is possible to supply and remove particles 10 to and from reactor 4 in a more or less continuous manner.
In an alternative embodiment of device 22 for disinfection and purification of a fluid (figure 2), a vessel 24 is filled with a fluid 26, like water. Fluid 26 comprises conductive particles. Fluid 26 is forced to move along the electrodes 36,38 and collide to these electrodes 36,38 and sidewall of vessel 24 by stirrer 28. Fluid is provided by a first input 30. A second input 32 may supply clean water to the vessel 24. Fluid 26 can be removed from vessel 24 by output 34. In vessel 24 there are provided two substantially vertically placed parallel stainless steal electrodes 36,38 with a length of about 15 cm and a diameter of about 12 mm. The electrodes 36,38 are hollow and the thickness of the steal layer is about 2 mm. The distance between the centers of the electrodes 36,38 is about 6 cm. The electrodes 36, 38 are connected in circuit 40. Also, circuit 40 comprises a source 42 for providing an alternating current to the electrodes 36,38.
Experiment An experiment is performed using the device 22. In the experiment about 150 ml cylindrical shaped active carbon particles with a length of about 5-8 mm and a diameter of about 2.5 mm are put in a vessel with a volume of about 80 ml. An amount of 300 ml de-mineralized water is supplied to the particles after which it is stirred for 30 minutes to remove air from the pores of the particles. After 30 minutes almost all air was removed as particles did not float on the water, but sank to the bottom of the container. In a next step the particles were removed from the water and washed to remove suspended carbon particles. This resulted in about 150 ml washed active carbon, with pores filled with water. The washed active carbon is put in a container with a volume of 800 ml, containing a mixture of 150 ml tap water and 150 ml so-called grey water, i.e. domestic waste water, comprising protozoa. From a microscopic analysis a droplet of water from the containers comprised about 5 protozoa. With a droplet volume of about 0.05 ml the container would contain a concentration of protozoa of about 100 protozoa per ml. Then the electrodes are provided with an alternating current with a frequency of 100 kHz and an amplitude of 10 Volt. After 60 minutes, while the contents of the container are stirred, four samples are taken and analyzed using a microscope. The number of living protozoa significantly decreased. After 80-100 minutes of treatment in the device, analyses of samples showed that all protozoa are killed. Additionally, the experiment was repeated without providing an alternating current between the electrodes. After 100 minutes of stirring the contents of the container a large amount of the protozoa was still alive.
In another embodiment of a device 44 (figure 3) according to the invention, a fluidized bed reactor 46, comprises an anode compartment 48, wherein an anode 50 is placed. Anode 48 is filled with particles 52. Anode compartment 48 is separated by grid 54 from cathode compartment 56. Cathode compartment 56 is provided with a cathode 58 that is filled with particles 60. The pores of grid 54 have dimensions such that the conductive particles can not flow through these pores, while the fluid contaminations may flow through these openings. This tube- like reactor 46 may be used for disinfection, bromate reduction and capacitive de-ionization . Fluid is fed to reactor 46 by inlet 62. The fluid moves through the anode compartment 48, passes grid 52 and flows through cathode compartment 56. Finally the fluid leaves reactor 46 via outlet 64.
Anode 50 and cathode 58 are connected in a circuit 66. Circuit 66 comprises a voltage supply 68 and a NPN transistor 70. Reactor 46 is connected to the collector side of transistor 70. Resistance 72 maintains a direct current from collector to emitter. The resistance and voltage supply are selected such that electrolysis occurs in reactor 46. Between the basis of transistor 70 and the minus side of voltage supply 68, a function generator 74 is provided. With function generator 74, for example the amplitude of the alternating current can be selected.
Additionally to the circuit 66 shown in the illustrated embodiment, a coupling condensator and additional resistances between the basis and the minus of the voltage source 68 may be provided. By using function generator 74 it is possible to vary the direct current in a similar frequency as compared to the alternating current.
For bromate reduction, using device 44, the incoming fluid comprises bromate and bromide ions. In the anode compartment 48 the bromide can be transferred to bromine and/or bromate. As soon as the fluid leaves the compartment 48 and enters compartment 56 a reduction reaction can take place on cathode 58. Bromate and bromine are transferred to bromide. This causes the removal of bromate from the fluid. Although particles in the cathode compartment 56 of the fluidized bed may have a different charge, the absorption of bromide and bromated will be limited by the nett negative charge of the cathode. Of course this depends on the selected values of source 68 and function generator 64. In addition, the specific surface of the conducted particles is relatively large so that only a limited amount of bromate needs to be adsorbed to the electrode surface to enable transfer of the bromate in the reactor almost entirely to bromide. Furthermore, a restricted transport of anode particles 52 through openings in grid 54 into cathode compartment 56 and transfer of cathode particles 60 through grid 54 into anode compartment 48 may increase transfer of bromate to bromide. According to the inventors an explanation may be that positively charged particles in the cathode compartment 56 comprise a significant amount of bromate ions that are adsorbed to the surface and that after collision with the cathodes 58 almost instantaneous is transferred into bromide. The present invention is by no means limited to the above described preferred embodiments thereof. The rights sought are defines by the following claims within the scope of which many modifications can be envisaged. One of the possible applications of the device and/or method according to the invention is the irrigation or spraying of water in horticulture and agriculture. The device and/or method according to the invention will prevent or minimize the distribution of bacteria, viruses and/or fungi. An example is in the cultivation of potatoes where irrigation or spraying of water is not always possible due to the presence of the Ralstonia solanacearum bacteria ("bruinrot") in the water. The device and/or method according to the invention will disinfect and/or purify the water thereby killing the bacteria. This enables the irrigation or spraying of water.

Claims

1. Device for disinfection or purification of a fluid, like drinking water, comprising: - a fluidized bed reactor provided with a suspension of conductive particles that are capable of adsorbing contaminating elements like organisms, organic compounds and/or ions; an anode and a cathode for providing a substantial number of particles with a charge; means for generating an electrical and/or electromagnetic field by providing a potential difference between the anode and the cathode; and - an inlet for a fluid, possibly comprising contaminating elements, wherein the fluid is exposed in the device to the electrical and/or electro-magnetic field for disinfecting and/or purifying the fluid.
2. Device according to claim 1, wherein the conductive particles comprise active carbon and/or polymer material provided with a metal coating.
3. Device according to claim 1 or 2, wherein the means for generating a potential difference varies the potential in time with an adjustable amplitude and/or frequency.
4. Device according to claim 3, wherein the potential difference comprising an alternating current component.
5. Device according to claim 4, wherein the alternating current component comprises a frequency in the range of IHz-IOOGHz, preferably IkHz-IMHz, more preferably 10kHz-500 kHz, and most preferably 30kHz-200kHz .
6. Device according to claim 4 or 5, wherein the amplitude of the alternating current component comprises an amplitude in the range of lOmV-lOOkV.
7. Device according to any of claims 1-6, wherein the potential differences comprising a direct current component .
8. Device according to any of claims 1-7, wherein the particles having a diameter in the range of 10 nm-10 cm, preferably 100 nm-5 cm, and more preferably 100 μm- 1 cm.
9. Device according to any of claims 1-8, wherein the particles having an average density of above 1000 kg/ m3.
10. Device according to any of claims 1-9, the device further comprising supply means for supplying gas to the reactor to manipulate the fluidized bed behavior of the particles and/or the transfer of potential from and to the particles.
11. Device according to any of claims 1-10, wherein the reactor comprising circulating means for circulating the particles.
12. Method for disinfecting and/or purifying a fluid, like drinking water, comprising the steps of:
providing a device according to any of claims 1- 11; providing the reactor at an inlet with fluid possibly comprising contaminations; disinfecting and/or purifying the fluid in the reactor; and - outputting the disinfected and/or purified fluid to an outlet of the reactor.
PCT/NL2009/050555 2008-09-18 2009-09-17 Device and method for disinfection and/or purification of a fluid WO2010033021A1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
EP09748505A EP2352704A1 (en) 2008-09-18 2009-09-17 Device and method for disinfection and/or purification of a fluid

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
NL1035953A NL1035953C (en) 2008-09-18 2008-09-18 Device and method for disinfection and/or purification of a fluid.
NL1035953 2008-09-18

Publications (1)

Publication Number Publication Date
WO2010033021A1 true WO2010033021A1 (en) 2010-03-25

Family

ID=40567567

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/NL2009/050555 WO2010033021A1 (en) 2008-09-18 2009-09-17 Device and method for disinfection and/or purification of a fluid

Country Status (3)

Country Link
EP (1) EP2352704A1 (en)
NL (1) NL1035953C (en)
WO (1) WO2010033021A1 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US9896918B2 (en) 2012-07-27 2018-02-20 Mbl Water Partners, Llc Use of ionized water in hydraulic fracturing

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB1367318A (en) * 1970-09-15 1974-09-18 Battelle Memorial Institute Method and apparatus for puryfying ionically conducting solutions by electroadsorption
NL7604579A (en) * 1975-04-30 1976-11-02 Westinghouse Electric Corp METHOD AND DEVICE FOR THE REMOVAL OF POLLUTANTS FROM WATER.
NL7607843A (en) * 1975-07-16 1977-01-18 Einhell Hans Gmbh ELECTROLYSIS CELL FOR TREATING WATER.
JPH09253652A (en) 1996-03-19 1997-09-30 Konica Corp Fluidized bed type electrolytic cell and water treatment method
JPH11158681A (en) 1997-11-20 1999-06-15 Mitsui Mining & Smelting Co Ltd Treatment of selenium-containing water to be treated
DE19835592A1 (en) * 1998-05-01 1999-11-11 Ind Tech Res Inst Waste liquor treatment with Fenton reagent, useful for highly concentrated waste liquor purification

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB1367318A (en) * 1970-09-15 1974-09-18 Battelle Memorial Institute Method and apparatus for puryfying ionically conducting solutions by electroadsorption
NL7604579A (en) * 1975-04-30 1976-11-02 Westinghouse Electric Corp METHOD AND DEVICE FOR THE REMOVAL OF POLLUTANTS FROM WATER.
NL7607843A (en) * 1975-07-16 1977-01-18 Einhell Hans Gmbh ELECTROLYSIS CELL FOR TREATING WATER.
JPH09253652A (en) 1996-03-19 1997-09-30 Konica Corp Fluidized bed type electrolytic cell and water treatment method
JPH11158681A (en) 1997-11-20 1999-06-15 Mitsui Mining & Smelting Co Ltd Treatment of selenium-containing water to be treated
DE19835592A1 (en) * 1998-05-01 1999-11-11 Ind Tech Res Inst Waste liquor treatment with Fenton reagent, useful for highly concentrated waste liquor purification

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US9896918B2 (en) 2012-07-27 2018-02-20 Mbl Water Partners, Llc Use of ionized water in hydraulic fracturing

Also Published As

Publication number Publication date
EP2352704A1 (en) 2011-08-10
NL1035953C (en) 2010-03-19

Similar Documents

Publication Publication Date Title
US6740245B2 (en) Non-chemical water treatment method and apparatus employing ionized air purification technologies
Mesones et al. Synergistic and antagonistic effects in the photoelectrocatalytic disinfection of water with TiO2 supported on activated carbon as a bipolar electrode in a novel 3D photoelectrochemical reactor
JP2000093967A (en) Method and apparatus for liquid treatment
CN104058480B (en) Low pressure discharge plasma body water treatment device and method
KR101210558B1 (en) Plasma water treatmant processing device
WO2009108045A1 (en) Device and method for disinfecting a fluid
CN111573933A (en) Graphene nano purification system and technology for treating medical sewage containing new coronavirus
Cui et al. The types of plasma reactors in wastewater treatment
US20100326926A1 (en) Systems and methods for generation of low zeta potential mineral crystals to enhance quality of liquid solutions
Ghernaout Electric field (EF) in the Core of the Electrochemical (EC) Disinfection
EP0766647B1 (en) Photoelectrochemical reactor
Govindan et al. Critical evaluation of mechanism responsible for biomass abatement during electrochemical coagulation (EC) process: A critical review
Loganathan et al. Bisphenols in water: Occurrence, effects, and mitigation strategies
CN203200062U (en) Low air pressure discharge plasma water treatment device
Li et al. Eutrophic water purification efficiency using a combination of hydrodynamic cavitation and ozonation on a pilot scale
NL1035953C (en) Device and method for disinfection and/or purification of a fluid.
JP2001340847A (en) Aeration/separation apparatus for removing/separating algae, green algae, and red tide plankton
CN212127868U (en) Electromagnetic strong oxidation coking wastewater advanced treatment system
Kiran et al. Remediation of textile effluents via physical and chemical methods for a safe environment
CN105271604A (en) Method for removing PPCPs in water body
KR20050049437A (en) A high pollution waste water disposal plant
CN202116407U (en) Device for treating catering wastewater
Sharma et al. Adsorption of textile dyes by plant biomass—a review
KR101862325B1 (en) Agriculture and livestock groundwater and seawater purification device for purifying friendly
JP2015029968A (en) Method and apparatus for removing microorganism and organic matter in water

Legal Events

Date Code Title Description
121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 09748505

Country of ref document: EP

Kind code of ref document: A1

NENP Non-entry into the national phase

Ref country code: DE

WWE Wipo information: entry into national phase

Ref document number: 2009748505

Country of ref document: EP