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GB2413320A - Fluid purification device comprising a noble metal matrix in combination with active ceramics - Google Patents

Fluid purification device comprising a noble metal matrix in combination with active ceramics Download PDF

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Publication number
GB2413320A
GB2413320A GB0407805A GB0407805A GB2413320A GB 2413320 A GB2413320 A GB 2413320A GB 0407805 A GB0407805 A GB 0407805A GB 0407805 A GB0407805 A GB 0407805A GB 2413320 A GB2413320 A GB 2413320A
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United Kingdom
Prior art keywords
noble metal
metal matrix
water
fluid
ceramics
Prior art date
Legal status (The legal status 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 status listed.)
Withdrawn
Application number
GB0407805A
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GB0407805D0 (en
Inventor
Melvyn Jones
John William Flowerdew
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STRUCTURE PLAS Ltd
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STRUCTURE PLAS 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
Application filed by STRUCTURE PLAS Ltd filed Critical STRUCTURE PLAS Ltd
Priority to GB0407805A priority Critical patent/GB2413320A/en
Publication of GB0407805D0 publication Critical patent/GB0407805D0/en
Publication of GB2413320A publication Critical patent/GB2413320A/en
Withdrawn legal-status Critical Current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
    • C02F1/50Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
    • C02F1/505Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment by oligodynamic treatment
    • 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
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/02Non-contaminated water, e.g. for industrial water supply
    • C02F2103/023Water in cooling circuits
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/42Nature of the water, waste water, sewage or sludge to be treated from bathing facilities, e.g. swimming pools
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Agricultural Chemicals And Associated Chemicals (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

A fluid treatment device comprising a noble metal matrix 4 in combination with active ceramics 3, to give a disinfecting effect. The noble metal matrix may comprise a mixture of copper and silver, and may be in form of a wire mesh which contains the active ceramics. The matrix may comprise a composite comprising an inner core (30, fig. 7) of noble metal encased in a second material (31, fig. 7) The second material may optionally be non-metallic such as a plastics material or may be a non-noble metal. Fluid communication paths (32, fig. 7) are provided to allow the fluid to be treated access to the surface of the noble metal core. As well as reducing the viable numbers of a wide range of bacteria and other micro-organisms, the device aids flocculation. It may be used in Legionella protection for held water systems, such as in air-conditioning systems, in the disinfection of potable water storage, swimming pools, spa baths or cooling water, de-scaling lime build up, or it may be used to disinfect other fluids such as machine oil, cutting oils and bacterially infected fuel oil or diesel oil.

Description

t C C e #e e 24 1 3320 Fl.,UID PURIFICATION DEVICE
Field of the Invention
The invention relates to netllods and apparatus for the purification of fluids, particularly with respect to the use ol a combination of noble metals and activated ceramics for the reductions or elimination of nicroorganisms. The methods and apparatus are also useful to aid flocculation of suspended solids, including micro-orgallisms.
Review of the Ale known to the Applicant Many infectious diseases of mall are caused by water-borne organisms. These organisms may gain access to lumalls by ingestion of water, by deposition of organisms from water to food, eating and drlnlhlg vessels, or by inhalation of water droplets containing the pathogenic organisms. The presence of water bome pathogens is particularly problematic in situations where a body of water is maintained at temperatures that may allow the organisms to survive or grow. Situations such as this are often found in air cooling systems, swimming pools, spa balLs and other aquatic recreational situations.
Furl.]lenllore, such water-home organisms are commonly fowld in other fluids such as aqueous suspensions and solutions as well as non-aqueous fluids Sucl t]uids would include machine oil and cutting oils; cooling fluids used for example on oil drilling platfonns; fuel oils.
., 2,.. "',2, '. ", Established tecl1ology for the disinfection of swimming pools and spas is predominantly concon1ed with dosing the system with chemicals that generate a concentration of disinfecting agent in the water, such as ch]oine. Systems such as this pose a number of problems for both users and operators alike.
It is important to maintain the concentration of the disinfecting agents at an appropriate level with regard to loath safety and efficacy. However, dosage control is often inaccurate, and operators, who often dislike handling chemicals, may not be trained to the con ect standards. These factors may lead to pool and spa waters not being treated adequately or safely.
Inappropriate use of disinfection agents may also lead to the formation of dangerous gasses such as phosgene. In order to maintain safe and efficacious conditions, the control of pH Is often required, requiring the addition of alkalis or acids. This poses additional self-evident problems for operators.
Furthen1lore, the unstable nature of the disinfection systems often necessitates constant manual monitoring, which is inaccurate.
The shortcomings of manual monitoring could, in principle, be overcome by the use of auto-nol1iLonng systems. However, due to the inherent tinge lags in systems such as these, such auto-n1onitoing does not cope well with high load periods, leading operators to resort to inte1l1ittent manual dosing of disinfection agents. This often leads lo occasional high levels of disinfection agents which is at best perceived as unpleasant, and at worst unhealthy.
Where chlorine is used as the disinfection agent, it can pose particular problems. It may leave users' skin dry, and produces an unpleasant atmosphere. Furthermore, chloramines fonned through the reaction of organic amides in body fluids with cl1lorDle, produce odours, sting eyes and dry out the skin of users. They are also known to cause eczema. Filially, disinfecting media such as these are, oJ course, products of the clerical industry. In this respect, reduction in their use would contribute to overall environmental goals c.: :e :. ë 's:: of reduction of the generation of greenhouse gasses, and the release of other contaminants into the atmosphere.
The prior ale contains descriptions of many devices for purifying water and other fluids. The development of technology in this field may be illustrated by a number of typical examples. U1( patent application GB2227998A describes a water purifying device comprising three coaxially mounted cylinders, and containing activated charcoal as a purifying material. Intenahonal application PCT/GB99/00965 describes a water purification and filtration device that uses a fine mesh of silver wire to eradicate bacteria and other contaminants from water. Likewise, lJK patent application GB2375105A discloses water disinfection/fltration ncda connpising a lalitted mesh of silver and copper wire.
We have developed a novel combination of active ceramic and noble metals that has unexpectedly improved performance over the use of tile materials alone, or what would be expected from their mere collocation. Furthermore, use of the technology aids flocculation. As well as having an effect on inert suspended solids, llocculatio' is advantageous for the removal of parasites such as CrJptosporidun', Garda oocysts, and certain viruses.
this new system is effective against contamination prevailing in swinging pools and spas, (for example the contamination introduced by body fluids such as urine and perspiration) and thus provides the basis for a more economical pool and spa bath E,uifcaLion system. The system is also more ecologically acceptable than the curl ent chemical fomls of disinfection.
Fluid treatment devices according to this invention 1lave wide implication.
IJses of the device include the following: Water: L,egonella protection for held water systems, air conditioning systems, occasional usage water equipment (such as safety showers, leisure centre facilities, sports clubs etc); disinfection of potable wale'- storage; disinfection of high volume held water supplies; disinfection of swimming pools, spa baths :: . ::4::' C 1 . . c e.
and Jacuzzs); cleaning water and other water uses in the food industry where storage/low usage nnay cause a bacterial contamination problem; held water used for cooling any application where the water becomes bacterially contaminated.
Other Fluids: Machine oil/cutting oils where held in reservoirs for usage; cooling fluids when stored between use, such as oil drilling platfonns, well drilling rigs etc.; general production process protection where fluids and/or aqueous solutions are held in line or in storage; replacement disinfection system where it is necessary to purge and disinfect production equipment after production run and prior to next run; disinfection of bacterially infected fuel oil/diesel oil in motor, marine, aeronautical industries, reduction of viscosity and/or surface tension, improving cost factor in pumping of fluids.
Other [Jses: De-scaling of lime build up in domestic and commercial uses, such as calorifiers, water heating equipment and such similar equipment; improvements to electrical efficiency when used in conjunction with water heating equipment; inhibition of biofiln growth.
The system is effective against a wide range of water-borne pathogens Including bacteria such as Legionella pneumoph71a, Salmonella t'phinzurium, Fuzterobacter aerogenes, Staphylococcus aureus, Pseudomonas spp. and Escherchia colt, protozoa such as Cryptosporidum and Gardza, viruses and algae.
Summary of the 1lvelltion
I:n its broadest aspect, the invention provides a fluid treatment device in whicl1 a noble metal matrix is combined with active ceramics to give a disinfecting effect. Preferably, the noble metal matrix conpises a mixture of copper and silver. More preferably, the noble metal matrix contains no snore than approximately 10% silver. Most preferably, the noble natal matrix contains of the order of l t!/0 silver.
:: :e : :s:: t: I t Preferably also, in any device embodying the invention, the noble metal matrix is in the foml of a wire mesh which contains tile ceramics.
Most preferably also, a device according to any of the previous descriptions comprises a noble metal having a covering, said covering characterized by (i) slot being comprised of a noble metal and (ii) the provision of one or more perforations allowing fluid communication between said noble metal and a surrounding fluid.
According to ally embodiment of the invention, the noble metal matrix and active ceramics are preferably arranged so that the fluid is brought into contact with said noble metal matrix before contacting the said active ceramics. In such instances, continuing experimentation and research indicates that the flow/connection of' fluid between these two components may also he an important practical factor.
By 'noble metal matrix' we mean any appropriate combination which would, when put into practice, give a measurable disinfecting effect on the fluid flow being treated.
Tllus the so-called 'noble' metal could for example be zinc which is lolown to fulfil the requirement just stated.
The noble metal could be a solid metal wire, or a surface coating carried by either a non-noble metal or a non-tnetallic cattier (such as a polymer) . Both these are known In themselves. What has not previously been disclosed, however, is the concept of the noble metal fonnilg the core (net the Her portion) of' a mixed-component wire if' suitable provision ('eg. perforation) is made for the noble metal to be exposed to, arid to react with, the fluid flow being treated. Such a presetatiol of the noble metal matrix can improve filter life without long term loss of effectiveness. c #
1 e v I .e . #
Brief Description of the Drawings
The invention will be described with reference to the accompanying drawings In which: Figure I shows a schematic diagram of a water purification cartridge containing a noble metal matrix and a bed of active ceramic beads.
Figure 2 shows a schematic diagram of an experimental system for testing and demonstrating the efficacy of the disclosed method and apparatus.
Figure 3 is a graph showing tile effect of water on the viability of two test organisms.
Figure 4 shows tile effect of water, treated for nine days according to the present invention, on the viability of two test organisms.
Figure 5 shows the effect of water, treated for twenty days according to the present invention, on the viability of two test organisms.
Figure 6 shows a cross-section of a composite comprising a noble metal and a perforated encasing material.
Figure 7 shows a perspective view of a composite comprising a noble metal and a perforated encasing, immaterial.
l:)escription of Preferred Embodllllellt In order to demonstrate the efficacy of tile current invention, a fluid treatment cartridge was constructed. '['his is illustrated in Figure], in Which there is a cartridge housing 1 provided with an Inlet pol16 and an outlet port 7. Within talc cartridge there are two support plates 2 and 5. Between the support plates 2 and 5 there Is a bung 4 of noble metal matrix which supports a bed of active : : . . : : 7: : : . 8 . . ceramic beads 3. The positional relationship, and containment of these two components is stir] uldergonlg r esearch, but initial results indicate that presence of both components in the right quantities/weights and the ability for the fluid to move freely between both components either though forced or conductive novenent are important practical factors.
In the enbodimert to be described below, the cartridge housing I was constructed of a plastics material. T he cartridge housing 1 took the forth of a plastics tube of length 2()cn with an internal diameter of 5. 4cn. The noble Dletal bung 4 also had a diameter of 5.4cn1 and a weight of 15hg. In this enbodinent the active ceramic bead bed 3 had a depth of 4cm and a weight of l OOg.
Flthe noble metal nlatix consisted of a wire mesh comprising 99.1% (w/w) copper and 0.9 /0 (w/w) silver.
The active ceramic leads had the following composition: % molecular wt Si 86.03 Al 22.54 Ma 1.59 K 6.83 Fe 1.37 Tl 0.53 Ca 1.27 To denolstrate the efficacy of the cartridge, a test system was constructed as depicted in the schematic diagram of Figure 2 in Chicle was provided a tank 21 of capacity 172 litres. 50 litres of water 22 were added lo the tank. Pipe world 23 rc-circulated the water 22 by meals of a peristaltic pump 24 tl-ough the cartridge 25 described above. After passing through the cartridge 25 the water was returned to the tank 21. in Ifs enbodinent, flee tank 21 was constructed of tom thick glass, and was provided with a lid made of erspex. The water e c I 22 was agitated by Pearls of ten 25mm long magnetic followers spaced at equal intervals along the centre of the base of the tank. The pH of tile water 22 was measured by rise of a pH meter 26 and was controlled by the addition of a phosphate buffer.
To demonstrate the bacteriocidal action of the system water was circulated around the system at a flow rate of 25 litres per flour. The water temperature was held at 28 C and the pH at 7.. Samples were taken frown the tank at iltevals and divided into lS x 1 00ml aliquots placed illtO sterile plastic pots and maintained at 28"C in a water bath. Two genera of bacteria were used in the experiment described below: Pcoli (ARCH 25922) and Staphylococcus aureus (ATCC 25923). I m] of the bacteria suspension were added to each pot which was then resumed to the water bath. At intervals of 1 5 10 20 and 30 minutes a pot frown each test series was removed from the water bath and either EDTA (ethylenediaminetetracetic acid) or sodium thioglycollate were added to sequester ally metal ions in the solution to prevent any further reaction. The remaining viable bacteria of each species were then enumerated.
To provide a time zero control three x 1 00nl aliquots of one quarter strength Ringer s SO]UtiO'I were prepared and lml of bacteria were added to each aliquot. Quenching agents (EDTA and thioglyco]late as above) were also added to these pots. file table below give details of the results obtained at Day 0 Day 9 and Day 20.
Day O (O hours) At B C exposure tune (mild (ciu/ml) (cAu/rrl/) (cpu/ml) (ciu/rrl) 0 3.48E+06 4.82E-06 5 55E+06 6.12E+06 1 4.58E1-06 4.37E1-06 3.57E-06 6.95E1-06 3.97E t-06 4.52Ei-()6 3.75E-FO6 5.82E1-06 3.38E-06 4 25E+()6 2.52E1-06 5 13E1-06 3 95E 06 3.75E t06 3.80E+06 5.72E+06 4.37E1-06 3.96E106 5.05E106 510E+06 log removal ( log NtlNo) 0.01 -0.08 -0.04 -0.08 :: :: .:: 9: I: : . . c Day 9 (215 hours) Exposure tweeze (rIZllZ) 0 3.47E+06 4.28E+06 8 45E+06 5.05E+OS 1 1.82E+06 3 OSE+06 8.07E-tO6 3.506+05 4.80E+05 1.73+06 7.83E+06 3.15E+OS 1.65E+05 8.43E+05 7.52E+06 3.40E+OS 2.30E+04 2.97E+OS 7.47E+()6 1.87E+OS S.95E+03 8.93E4-04 6.92E+06 2.95E4- OS log r emoval ( log Nt/NO) -2.77 -1.68 -0.09 -0.23 Day 20 Exposure time (nZz/z) 5.52E-- OS 8.52E-OS 1.53E+06 8 SOE+06 0 2 42E+OS 2.00Et06 1.43E+06 1.02E+07 1 I.51E+05 3.58E405 1.40E+06 6.21E+06 5.77E+04 1.52E+05 3.05E+06 9.03E4-06 1 58E+04 6.07E1-04 3.47Et06 8.65E+06 2() 3.25E+03 2 88Ed-04 2.78E+06 8.27E+06 -2.23 -1.47 0.26 -0.01 log removal ( log Nt/NO) tA = E. coil EDTA quenched B = E CO/I sodium thloglycollate quench C= Staph. aureus EDNA quench D - Staph aureus sodium thloglycollate quench Cal= colony forming units The data obtained from water before treatment tl-ough the cartridge is shown In Figure 3. It can be seen that water from the re-circulation system prior to treatment through the cartridge embodying tile invention has effectively no bacteriocidal activity either against E.coli or against Staph. aureus.
By contrast Figure 4 shows the bacteiocidal effect of water recycled through the cartridge of the present invention for a period of nine days. The water has considerable bacteriocidal effect against E coli. After 30 minutes exposure a log reduction hi viable organisms of between 1.5 and 3 is seen equivalent to the destruction of between 99% and 99.9% of the viable organisms. It can be noted in Figure 4 that the curves depicting the viable numbers of Scold have also not reached a plateau and so further eradication of the organisms would be expected.
: ' 1', ' ::e c:e I: : Figure 5 shows the bacteriocidal effect of water, recycled through the cartridge of the present invention for a period of 20 days. As before, the water has considerable bacteriocidal effects against E. coli. The rate and extent of destruction of this orgamsn1 follows a similar pattern to that shown in Figure 4.
The table above, and also Figures 4 and 5 shows that the water has little or no effect on staph. aureus.
A further enbodinent of the noble metal matrix is illustrated in Figures 6 and 7. Fi gure 6 depicts a cross-section of a composite comprising an Inner core 30 of noble metal encased in a second material 31. This second material may optionally be non-metallic such as a plastics material or a non-noble metal.
Fluid communication paths 32 are provided to allow the fluid to be treated to access a portion of the surface of the noble natal core 30. Figure 7 depicts a perspective view of such a composite material in which the fluid communication paths 32 are provided as a series of perforations in the outer encasing material. Such an arrangement of the noble metal matrix can improve filter life without long term loss of effectiveness.

Claims (8)

: . ...11 it; CLAIMS
1. A fluid treatment device in which a noble metal matrix is combined with active eeranies to give a disinfecting effect.
2. A device according to Claim 1 wherein tile noble metal matrix comprises a mixture of copper and silver.
3. A device according to Claim 2 wherein the noble metal natix contains no more than approximately 10% silver.
4. A device according to Claim 2 wherein the noble metal matrix contains of the order of 1% silver.
5. A devotee according to any previous claim wherein the noble metal matrix Is in the forth of a wire mesh whicl1 contains the ceramics.
6. A device according to any previous claims wherein the noble metal has a covering, said covering characterized by (i) not being comprised of a noble metal and (ii) the provision of one or snore perforations allowing fluid eomn1unieation between said noble metal and a surrounding fluid.
7. A device aeeordng to any previous elain1 wherein tile noble metal matrix and active ceramics are arranged so float fluid is brought into contact with said noble metal matrix before contacting the said active ceramics.
8. A fluid treatment device substantially as described herein, with reference to any appropriate combination of the drawings.
GB0407805A 2004-04-06 2004-04-06 Fluid purification device comprising a noble metal matrix in combination with active ceramics Withdrawn GB2413320A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
GB0407805A GB2413320A (en) 2004-04-06 2004-04-06 Fluid purification device comprising a noble metal matrix in combination with active ceramics

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
GB0407805A GB2413320A (en) 2004-04-06 2004-04-06 Fluid purification device comprising a noble metal matrix in combination with active ceramics

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GB2413320A true GB2413320A (en) 2005-10-26

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2008152120A3 (en) * 2007-06-12 2009-04-09 Detlef Militz Use of a three-dimensional yarn system
ES2394566A1 (en) * 2010-03-02 2013-02-01 Asociación De Investigación De La Industria Textil Water treatment system for the elimination of legionella in water transfer equipment in air current and procedure of operation of such treatment system (Machine-translation by Google Translate, not legally binding)
EP2594532A1 (en) * 2011-11-21 2013-05-22 Martin Bergmann Umwelttechnik Method and arrangement for hygienisation of water in a swimming pool system or swimming or bathing area

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH01162563A (en) * 1987-12-17 1989-06-27 Kobe Steel Ltd Sprue part filter for light alloy casting
JPH06335687A (en) * 1993-05-28 1994-12-06 Suzuki Seisakusho:Yugen Water purifying method and water purifier using the method
EP0870862A2 (en) * 1997-04-05 1998-10-14 Daikyo Co., Ltd. Auxiliary device for activating cleaning water
JPH115082A (en) * 1997-06-17 1999-01-12 Technos Kk Active water apparatus
GB2395945A (en) * 2002-10-18 2004-06-09 Graham Colin Brebner Water disinfection knitted matrix with active ceramics and a descaling device
GB2395944A (en) * 2002-09-09 2004-06-09 Graham Colin Brebner Water disinfection knitted matrix with active ceramics

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH01162563A (en) * 1987-12-17 1989-06-27 Kobe Steel Ltd Sprue part filter for light alloy casting
JPH06335687A (en) * 1993-05-28 1994-12-06 Suzuki Seisakusho:Yugen Water purifying method and water purifier using the method
EP0870862A2 (en) * 1997-04-05 1998-10-14 Daikyo Co., Ltd. Auxiliary device for activating cleaning water
JPH115082A (en) * 1997-06-17 1999-01-12 Technos Kk Active water apparatus
GB2395944A (en) * 2002-09-09 2004-06-09 Graham Colin Brebner Water disinfection knitted matrix with active ceramics
GB2395945A (en) * 2002-10-18 2004-06-09 Graham Colin Brebner Water disinfection knitted matrix with active ceramics and a descaling device

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
EPODOC abstract of KR 009513318 B1 (HONG) 02.11.1995 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2008152120A3 (en) * 2007-06-12 2009-04-09 Detlef Militz Use of a three-dimensional yarn system
ES2394566A1 (en) * 2010-03-02 2013-02-01 Asociación De Investigación De La Industria Textil Water treatment system for the elimination of legionella in water transfer equipment in air current and procedure of operation of such treatment system (Machine-translation by Google Translate, not legally binding)
EP2594532A1 (en) * 2011-11-21 2013-05-22 Martin Bergmann Umwelttechnik Method and arrangement for hygienisation of water in a swimming pool system or swimming or bathing area

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