CA2298496A1 - Catalytic dental water apparatus - Google Patents
Catalytic dental water apparatus Download PDFInfo
- Publication number
- CA2298496A1 CA2298496A1 CA002298496A CA2298496A CA2298496A1 CA 2298496 A1 CA2298496 A1 CA 2298496A1 CA 002298496 A CA002298496 A CA 002298496A CA 2298496 A CA2298496 A CA 2298496A CA 2298496 A1 CA2298496 A1 CA 2298496A1
- Authority
- CA
- Canada
- Prior art keywords
- water
- silver
- dental
- implements
- oxygen
- 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.)
- Abandoned
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 231
- 230000003197 catalytic effect Effects 0.000 title description 6
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 claims abstract description 91
- 229910052709 silver Inorganic materials 0.000 claims abstract description 82
- 239000004332 silver Substances 0.000 claims abstract description 82
- BQCADISMDOOEFD-UHFFFAOYSA-N Silver Chemical compound [Ag] BQCADISMDOOEFD-UHFFFAOYSA-N 0.000 claims abstract description 81
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 79
- 239000001301 oxygen Substances 0.000 claims abstract description 79
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 76
- 239000003054 catalyst Substances 0.000 claims abstract description 42
- 244000005700 microbiome Species 0.000 claims abstract description 30
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- 238000011144 upstream manufacturing Methods 0.000 claims abstract description 5
- 238000010494 dissociation reaction Methods 0.000 claims abstract 2
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- 230000009286 beneficial effect Effects 0.000 description 6
- 125000004430 oxygen atom Chemical group O* 0.000 description 6
- 239000000126 substance Substances 0.000 description 6
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- 239000011324 bead Substances 0.000 description 5
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- 235000020679 tap water Nutrition 0.000 description 3
- 238000012360 testing method Methods 0.000 description 3
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- RZVAJINKPMORJF-UHFFFAOYSA-N Acetaminophen Chemical compound CC(=O)NC1=CC=C(O)C=C1 RZVAJINKPMORJF-UHFFFAOYSA-N 0.000 description 2
- NOWKCMXCCJGMRR-UHFFFAOYSA-N Aziridine Chemical compound C1CN1 NOWKCMXCCJGMRR-UHFFFAOYSA-N 0.000 description 2
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 2
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- 125000002534 ethynyl group Chemical group [H]C#C* 0.000 description 2
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- OKJPEAGHQZHRQV-UHFFFAOYSA-N iodoform Chemical compound IC(I)I OKJPEAGHQZHRQV-UHFFFAOYSA-N 0.000 description 2
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- 230000019612 pigmentation Effects 0.000 description 2
- 238000009428 plumbing Methods 0.000 description 2
- 230000002035 prolonged effect Effects 0.000 description 2
- 230000001681 protective effect Effects 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 239000008213 purified water Substances 0.000 description 2
- 230000009257 reactivity Effects 0.000 description 2
- 230000002829 reductive effect Effects 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 241000894007 species Species 0.000 description 2
- 239000007921 spray Substances 0.000 description 2
- 239000008223 sterile water Substances 0.000 description 2
- 238000004659 sterilization and disinfection Methods 0.000 description 2
- 238000012546 transfer Methods 0.000 description 2
- 229910052723 transition metal Inorganic materials 0.000 description 2
- 230000035899 viability Effects 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- BLKPFVWYBFDTPX-UHFFFAOYSA-N 2-(6,6-dimethyl-4-bicyclo[3.1.1]hept-3-enyl)acetaldehyde Chemical compound C1C2C(C)(C)C1CC=C2CC=O BLKPFVWYBFDTPX-UHFFFAOYSA-N 0.000 description 1
- 208000002109 Argyria Diseases 0.000 description 1
- 241001554566 Argyria Species 0.000 description 1
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- 238000012935 Averaging Methods 0.000 description 1
- 241000606125 Bacteroides Species 0.000 description 1
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- JPVYNHNXODAKFH-UHFFFAOYSA-N Cu2+ Chemical compound [Cu+2] JPVYNHNXODAKFH-UHFFFAOYSA-N 0.000 description 1
- 208000002064 Dental Plaque Diseases 0.000 description 1
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 1
- 241000588722 Escherichia Species 0.000 description 1
- IAYPIBMASNFSPL-UHFFFAOYSA-N Ethylene oxide Chemical compound C1CO1 IAYPIBMASNFSPL-UHFFFAOYSA-N 0.000 description 1
- 206010015946 Eye irritation Diseases 0.000 description 1
- 241000282326 Felis catus Species 0.000 description 1
- 241000589565 Flavobacterium Species 0.000 description 1
- 241000588748 Klebsiella Species 0.000 description 1
- 241000589248 Legionella Species 0.000 description 1
- 241000589242 Legionella pneumophila Species 0.000 description 1
- 208000007764 Legionnaires' Disease Diseases 0.000 description 1
- 208000019693 Lung disease Diseases 0.000 description 1
- 241000244206 Nematoda Species 0.000 description 1
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- 241000187654 Nocardia Species 0.000 description 1
- 235000002840 Opuntia megacantha Nutrition 0.000 description 1
- 240000008607 Opuntia megacantha Species 0.000 description 1
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- 206010047700 Vomiting Diseases 0.000 description 1
- 238000004378 air conditioning Methods 0.000 description 1
- 239000003619 algicide Substances 0.000 description 1
- HSFWRNGVRCDJHI-UHFFFAOYSA-N alpha-acetylene Natural products C#C HSFWRNGVRCDJHI-UHFFFAOYSA-N 0.000 description 1
- 230000003321 amplification Effects 0.000 description 1
- 230000000844 anti-bacterial effect Effects 0.000 description 1
- 239000004599 antimicrobial Substances 0.000 description 1
- 239000008346 aqueous phase Substances 0.000 description 1
- 125000003118 aryl group Chemical group 0.000 description 1
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- 239000003899 bactericide agent Substances 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000008280 blood Substances 0.000 description 1
- 210000004369 blood Anatomy 0.000 description 1
- 235000012206 bottled water Nutrition 0.000 description 1
- KFCUPNHUPHDVJC-UHFFFAOYSA-N bromine azide Chemical compound BrN=[N+]=[N-] KFCUPNHUPHDVJC-UHFFFAOYSA-N 0.000 description 1
- 230000000711 cancerogenic effect Effects 0.000 description 1
- 150000001735 carboxylic acids Chemical class 0.000 description 1
- 231100000357 carcinogen Toxicity 0.000 description 1
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- 229910001431 copper ion Inorganic materials 0.000 description 1
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- 229910001882 dioxygen Inorganic materials 0.000 description 1
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- 239000003546 flue gas Substances 0.000 description 1
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- 230000037406 food intake Effects 0.000 description 1
- 239000003517 fume Substances 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 239000002920 hazardous waste Substances 0.000 description 1
- 239000002638 heterogeneous catalyst Substances 0.000 description 1
- ILHIHKRJJMKBEE-UHFFFAOYSA-N hydroperoxyethane Chemical compound CCOO ILHIHKRJJMKBEE-UHFFFAOYSA-N 0.000 description 1
- 239000007943 implant Substances 0.000 description 1
- 239000004615 ingredient Substances 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 230000002147 killing effect Effects 0.000 description 1
- 229940115932 legionella pneumophila Drugs 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 235000015250 liver sausages Nutrition 0.000 description 1
- 239000011159 matrix material Substances 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- VKQFCGNPDRICFG-UHFFFAOYSA-N methyl 2-methylpropyl 2,6-dimethyl-4-(2-nitrophenyl)-1,4-dihydropyridine-3,5-dicarboxylate Chemical compound COC(=O)C1=C(C)NC(C)=C(C(=O)OCC(C)C)C1C1=CC=CC=C1[N+]([O-])=O VKQFCGNPDRICFG-UHFFFAOYSA-N 0.000 description 1
- 244000000010 microbial pathogen Species 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 210000002445 nipple Anatomy 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- 238000003199 nucleic acid amplification method Methods 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 239000007800 oxidant agent Substances 0.000 description 1
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 239000011236 particulate material Substances 0.000 description 1
- 238000006116 polymerization reaction Methods 0.000 description 1
- YORCIIVHUBAYBQ-UHFFFAOYSA-N propargyl bromide Chemical compound BrCC#C YORCIIVHUBAYBQ-UHFFFAOYSA-N 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
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- 238000012958 reprocessing Methods 0.000 description 1
- 230000000241 respiratory effect Effects 0.000 description 1
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- 210000003296 saliva Anatomy 0.000 description 1
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- 150000003378 silver Chemical class 0.000 description 1
- 230000036556 skin irritation Effects 0.000 description 1
- 231100000475 skin irritation Toxicity 0.000 description 1
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- 229940035718 sular Drugs 0.000 description 1
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- 230000009182 swimming Effects 0.000 description 1
- 208000024891 symptom Diseases 0.000 description 1
- MLGCXEBRWGEOQX-UHFFFAOYSA-N tetradifon Chemical compound C1=CC(Cl)=CC=C1S(=O)(=O)C1=CC(Cl)=C(Cl)C=C1Cl MLGCXEBRWGEOQX-UHFFFAOYSA-N 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
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- 238000013022 venting Methods 0.000 description 1
- 230000008673 vomiting Effects 0.000 description 1
- 235000020681 well water Nutrition 0.000 description 1
- 239000002349 well water Substances 0.000 description 1
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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/78—Treatment of water, waste water, or sewage by oxidation with ozone
-
- A—HUMAN NECESSITIES
- A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
- A61L—METHODS OR APPARATUS FOR STERILISING MATERIALS OR OBJECTS IN GENERAL; DISINFECTION, STERILISATION OR DEODORISATION OF AIR; CHEMICAL ASPECTS OF BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES; MATERIALS FOR BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES
- A61L2/00—Methods or apparatus for disinfecting or sterilising materials or objects other than foodstuffs or contact lenses; Accessories therefor
- A61L2/16—Methods or apparatus for disinfecting or sterilising materials or objects other than foodstuffs or contact lenses; Accessories therefor using chemical substances
- A61L2/20—Gaseous substances, e.g. vapours
- A61L2/202—Ozone
-
- 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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/725—Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
-
- 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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/74—Treatment of water, waste water, or sewage by oxidation with air
-
- 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
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
- C02F1/32—Treatment of water, waste water, or sewage by irradiation with ultraviolet light
Landscapes
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Organic Chemistry (AREA)
- Water Supply & Treatment (AREA)
- Environmental & Geological Engineering (AREA)
- Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Health & Medical Sciences (AREA)
- Epidemiology (AREA)
- Veterinary Medicine (AREA)
- Public Health (AREA)
- General Health & Medical Sciences (AREA)
- Animal Behavior & Ethology (AREA)
- General Chemical & Material Sciences (AREA)
- Apparatus For Disinfection Or Sterilisation (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
- Dental Tools And Instruments Or Auxiliary Dental Instruments (AREA)
Abstract
The supply of water used in dental operations and other applications in a dental office, or other medical facility, wherein non-contaminated water is necessary to avoid transmission of microorganisms, is enriched with oxygen, whether from ambient air or a source of oxygen. The oxygenated water is passed through a silver containing catalyst cartridge (204). The water borne oxygen is attracted to the silver and forms a weak bond sufficient to permit dissociation to oxidize organic matter, including microorganisms. A small amount of silver dissolves in the water and flows downstream through the attendant conduits (68, 69, 82) to and through dental handpieces and dental implements. A portion of the silver will adhere to the walls of the conduits, handpieces, and implements where it is free to react with the oxygen dissolved in the water flowing therepast. To enhance oxidizing of the organic matter, an ozone generator (48) may be employed to introduce ozone into the water upstream of the silver catalyst cartridge (204).
Description
CATALYTIC DENTAL WATER APPARATUS
BACKGROUND OF THE INVENTION
1. Field of the Invention The present invention relates to purification of dental water lines, to destroying biofilm .that may be present and to preventing biofilm buildup and, more particularly, to having oxygen or ozone enriched water react with a silver catalyst and oxidize organic matter, such as microorganisms and biofilm, that may be present in the water, on surfaces of the dental water lines and on the surfaces of any downstream handpieces, implements or nozzles, to provide uncontaminated water at the point of use.
BACKGROUND OF THE INVENTION
1. Field of the Invention The present invention relates to purification of dental water lines, to destroying biofilm .that may be present and to preventing biofilm buildup and, more particularly, to having oxygen or ozone enriched water react with a silver catalyst and oxidize organic matter, such as microorganisms and biofilm, that may be present in the water, on surfaces of the dental water lines and on the surfaces of any downstream handpieces, implements or nozzles, to provide uncontaminated water at the point of use.
2. Description of Related Art Tap water in dental offices is similar to tap water in most homes and offices.
While this water is generally considered safe to drink, it is never sterile.
Most tap water samples contain fewer than 50 cfu (colony forming units) of bacteria per milliliter (cfu/ml). However, once the water leaves plumbing lines and enters the long plastic tubing that feeds into dental high-speed handpieces and other dental implements, such as air-water syringes and ultrasonic tooth scalars, the environment changes.
Here, the low flow rate, frequent periods of stagnation and large relative surface area of the small bore plastic lines are ideal for microbial contamination.
Water that stagnates in plastic water lines and/or tubing overnight and even during 2 o long periods during the day provide bacteria the opportunity to stick to the wall of the lines/tubing. Water, slowly running through the line, provides a constant flow of bacteria that can adhere to the microbes that are already clinging to the wall. A
cooperating population of several different species, which depend on each other for survival or are otherwise symbiotically related, continue to multiply and form a matrix that provides 2 5 nutrients and mutual protection.
This bacterial population is known as biofilm, a microbial mass that is bathed in liquids. Dental plaque is another example of biofilm. Biofilm can also be found in air conditioning units, artificial implants and many types of equipment, including dental anti-siphon and check valves.
The function of the anti-siphon and check valves is to prevent aspiration of patients' fluids into the dental water lines. Unfortunately, these valves often fail to work properly because of biofilm and other factors.
Microbes can become drawn back into the dental water lines as a result of imperfect hygiene or sterilization practices, a transient negative pressure when the drill stops rotating and/or mechanical failure of anti-siphon valves or other mechanisms. Once this happens, pathogens originating from patients' mouths can enter the lines and adhere to existing biofihn and multiply within them.
These microbes, originating both upstream firm municipal water supplies and downstream from patients' blood and saliva, are not very numerous initially.
Amplification of the microorganisms is nothing less than astounding. Microbial studies of dental water lines reveal bacterial population explosions averaging over 500,000 cfu/ml and often exceeding 1,000,000 cfil/ml.
Thus far, researchers have identified pathogens and opportunists in dental equipment such as Pseudomonas, Legionella, Staphylococci, Streptococci, Nocardia, Serratia, Klebsiella. _Lloraxella, Bacteroides, Flavobacterium, Escherichia, several species of amoebae mown to serve as hosts for Legionella pneumophila and even nematodes (worms).
Various solutions to prevent exposure of dental patients to contaminated water have been proposed. Such proposals include flushing the dental water lines with distilled water or chemicals but little evidence exists that such flushing eliminates the biofihn.
Sterilization of dental instruments between patients has little effect in preventing the 2 5 microbes in the dental water from entering the next patient's mouth. Using new disposable sterile water lines between patients does not solve the problem of biofilm upstream of the replaced lines and the costs are significant. Use of containers having sterile or distilled water is effective only if the water conveying lines are replaced after each patient and if the water does not become contaminated prior to disposal of used water lines. Use of check valves to prevent backflow is essentially ineffective one hundred percent (100%) of the time due to contamination of the valve itself.
Use of electrical current in combination with antimicrobial agents is impractical due to unavailability of inexpensive ready-to-use equipment. Distilling the water received from a municipal water source only addresses the water and not the contaminants present in the lines conveying the water to the patient. To date, devices using 0.2 micron filters or the 1 o like are reasonably effective to prevent transmission therepast of microbes provided that the filters are replaced at least daily and that the process of such replacement does not permit a colony of microbes to be conveyed to a water line downstream of the filter. It is therefore evident that a significant health hazard exists for patients within a dental office and no viable solution is presently commercially available.
While this water is generally considered safe to drink, it is never sterile.
Most tap water samples contain fewer than 50 cfu (colony forming units) of bacteria per milliliter (cfu/ml). However, once the water leaves plumbing lines and enters the long plastic tubing that feeds into dental high-speed handpieces and other dental implements, such as air-water syringes and ultrasonic tooth scalars, the environment changes.
Here, the low flow rate, frequent periods of stagnation and large relative surface area of the small bore plastic lines are ideal for microbial contamination.
Water that stagnates in plastic water lines and/or tubing overnight and even during 2 o long periods during the day provide bacteria the opportunity to stick to the wall of the lines/tubing. Water, slowly running through the line, provides a constant flow of bacteria that can adhere to the microbes that are already clinging to the wall. A
cooperating population of several different species, which depend on each other for survival or are otherwise symbiotically related, continue to multiply and form a matrix that provides 2 5 nutrients and mutual protection.
This bacterial population is known as biofilm, a microbial mass that is bathed in liquids. Dental plaque is another example of biofilm. Biofilm can also be found in air conditioning units, artificial implants and many types of equipment, including dental anti-siphon and check valves.
The function of the anti-siphon and check valves is to prevent aspiration of patients' fluids into the dental water lines. Unfortunately, these valves often fail to work properly because of biofilm and other factors.
Microbes can become drawn back into the dental water lines as a result of imperfect hygiene or sterilization practices, a transient negative pressure when the drill stops rotating and/or mechanical failure of anti-siphon valves or other mechanisms. Once this happens, pathogens originating from patients' mouths can enter the lines and adhere to existing biofihn and multiply within them.
These microbes, originating both upstream firm municipal water supplies and downstream from patients' blood and saliva, are not very numerous initially.
Amplification of the microorganisms is nothing less than astounding. Microbial studies of dental water lines reveal bacterial population explosions averaging over 500,000 cfu/ml and often exceeding 1,000,000 cfil/ml.
Thus far, researchers have identified pathogens and opportunists in dental equipment such as Pseudomonas, Legionella, Staphylococci, Streptococci, Nocardia, Serratia, Klebsiella. _Lloraxella, Bacteroides, Flavobacterium, Escherichia, several species of amoebae mown to serve as hosts for Legionella pneumophila and even nematodes (worms).
Various solutions to prevent exposure of dental patients to contaminated water have been proposed. Such proposals include flushing the dental water lines with distilled water or chemicals but little evidence exists that such flushing eliminates the biofihn.
Sterilization of dental instruments between patients has little effect in preventing the 2 5 microbes in the dental water from entering the next patient's mouth. Using new disposable sterile water lines between patients does not solve the problem of biofilm upstream of the replaced lines and the costs are significant. Use of containers having sterile or distilled water is effective only if the water conveying lines are replaced after each patient and if the water does not become contaminated prior to disposal of used water lines. Use of check valves to prevent backflow is essentially ineffective one hundred percent (100%) of the time due to contamination of the valve itself.
Use of electrical current in combination with antimicrobial agents is impractical due to unavailability of inexpensive ready-to-use equipment. Distilling the water received from a municipal water source only addresses the water and not the contaminants present in the lines conveying the water to the patient. To date, devices using 0.2 micron filters or the 1 o like are reasonably effective to prevent transmission therepast of microbes provided that the filters are replaced at least daily and that the process of such replacement does not permit a colony of microbes to be conveyed to a water line downstream of the filter. It is therefore evident that a significant health hazard exists for patients within a dental office and no viable solution is presently commercially available.
SUMMARY OF THE INVENTION
In the present invention, oxygen, whether from ambient air or a source of oxygen, or ozone from an ozone generator, is introduced to a water source through a sparger or the like to entrain the oxygen or ozone in the water. The water is subsequently conveyed past a silver catalyst cartridge through water lines to each of the various handpieces or water flow dependent implements used by a dentist during the normal course of providing dental services. The oxygen entrained in the water is attracted to the silver in the cartridge and will dissociate from its normal diatomic state to bond with the silver.
However, this bond is weak enough that the oxygen will dissociate to oxidize organic 1 o matter, including microorganisms in the water. A small amount of the silver will dissolve in the water stream flowing therepast and flow downstream. A portion of this silver will adhere to the surfaces of the water lines, handpieces and implements. The adhered silver is free to react with the oxygen dissolved in the water and any attendant biofilm will be destroyed. Any ozone introduced into the water will destroy any microbial pathogens in 15 the water and help to render the water essentially microbe free.
Furthermore, the living organisms in any biofilm attendant the walls of the water lines, handpieces and implements will be destroyed upon contact with the ozone. Thus, the water delivered to a patient's oral cavity during the rendering of dental services will be essentially free of any viable microbial activity.
2 o It is therefore a primary object of the present invention to provide apparatus for delivering water from dental water lines free of any living microbes.
Another object of the present invention is to provide apparatus for destroying any biofilms formed on the walls of water lines, handpieces and nozzles in a dental operatory.
Yet another object of the present invention is to provide apparatus that delivers to 2 5 a dental patient water free of microbial activity whether such water be from a municipal water system or a water container.
Still another object of the present invention is to provide apparatus for destroying any microorganisms present in a dental water line or the water itself whether the water is flowing through the line or is stagnant.
A further object of the present invention is to provide a silver catalyst to enhance 5 oxidization of microorganisms and biofilm attendant dental handpieces and other dental implements.
A yet further object of the present invention is to provide inexpensive apparatus for ensuring that water delivered to a dental patient is free of living microbes.
A still further object of the present invention is to provide a method for 1 o inexpensively and effectively destroying any biofilm and preventing biofilm buildup attendant dental water lines, dental handpieces and related implements.
These and other objects of the present invention will become apparent to those skilled in the art as the description thereof proceeds.
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In the present invention, oxygen, whether from ambient air or a source of oxygen, or ozone from an ozone generator, is introduced to a water source through a sparger or the like to entrain the oxygen or ozone in the water. The water is subsequently conveyed past a silver catalyst cartridge through water lines to each of the various handpieces or water flow dependent implements used by a dentist during the normal course of providing dental services. The oxygen entrained in the water is attracted to the silver in the cartridge and will dissociate from its normal diatomic state to bond with the silver.
However, this bond is weak enough that the oxygen will dissociate to oxidize organic 1 o matter, including microorganisms in the water. A small amount of the silver will dissolve in the water stream flowing therepast and flow downstream. A portion of this silver will adhere to the surfaces of the water lines, handpieces and implements. The adhered silver is free to react with the oxygen dissolved in the water and any attendant biofilm will be destroyed. Any ozone introduced into the water will destroy any microbial pathogens in 15 the water and help to render the water essentially microbe free.
Furthermore, the living organisms in any biofilm attendant the walls of the water lines, handpieces and implements will be destroyed upon contact with the ozone. Thus, the water delivered to a patient's oral cavity during the rendering of dental services will be essentially free of any viable microbial activity.
2 o It is therefore a primary object of the present invention to provide apparatus for delivering water from dental water lines free of any living microbes.
Another object of the present invention is to provide apparatus for destroying any biofilms formed on the walls of water lines, handpieces and nozzles in a dental operatory.
Yet another object of the present invention is to provide apparatus that delivers to 2 5 a dental patient water free of microbial activity whether such water be from a municipal water system or a water container.
Still another object of the present invention is to provide apparatus for destroying any microorganisms present in a dental water line or the water itself whether the water is flowing through the line or is stagnant.
A further object of the present invention is to provide a silver catalyst to enhance 5 oxidization of microorganisms and biofilm attendant dental handpieces and other dental implements.
A yet further object of the present invention is to provide inexpensive apparatus for ensuring that water delivered to a dental patient is free of living microbes.
A still further object of the present invention is to provide a method for 1 o inexpensively and effectively destroying any biofilm and preventing biofilm buildup attendant dental water lines, dental handpieces and related implements.
These and other objects of the present invention will become apparent to those skilled in the art as the description thereof proceeds.
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BRIEF DESCRIPTION OF THE DRAWINGS
The present invention will be described with greater specificity and clarity with reference to the following drawings, in which:
Figure 1 illustrates apparatus for ozonating water delivered to a dental chair; -Figure 2 illustrates details of the ozonating apparatus shown in Figure l;
Figure 3 illustrates apparatus for ozonating water within and delivered from a water container to a dental chair;
Figure 4 illustrates apparatus contained within a water container for delivering ozonated water from the container to a dental chair;
1 o Figure 5 illustrates the apparatus shown in Figure 1 with the addition of a silver catalyst cartridge;
Figure 6 illustrates the apparatus shown in Figure 3 with the addition of a silver catalyst cartridge;
Figure 7 illustrates the apparatus shown in Figure 4 with the addition of a silver catalyst cartridge;
Figure 8 illustrates apparatus for entraining air or oxygen in water and passing the mixture through a silver catalyst cartridge;
Figure 9 illustrates a silver catalyst cartridge;
Figures 10a. l Ob, and l Oc illustrate components of the cartridge shown in Figure 2 0 9; and Figure 11 illustrates test results obtained with the present invention.
The present invention will be described with greater specificity and clarity with reference to the following drawings, in which:
Figure 1 illustrates apparatus for ozonating water delivered to a dental chair; -Figure 2 illustrates details of the ozonating apparatus shown in Figure l;
Figure 3 illustrates apparatus for ozonating water within and delivered from a water container to a dental chair;
Figure 4 illustrates apparatus contained within a water container for delivering ozonated water from the container to a dental chair;
1 o Figure 5 illustrates the apparatus shown in Figure 1 with the addition of a silver catalyst cartridge;
Figure 6 illustrates the apparatus shown in Figure 3 with the addition of a silver catalyst cartridge;
Figure 7 illustrates the apparatus shown in Figure 4 with the addition of a silver catalyst cartridge;
Figure 8 illustrates apparatus for entraining air or oxygen in water and passing the mixture through a silver catalyst cartridge;
Figure 9 illustrates a silver catalyst cartridge;
Figures 10a. l Ob, and l Oc illustrate components of the cartridge shown in Figure 2 0 9; and Figure 11 illustrates test results obtained with the present invention.
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENT
Ozone entrained in water will destroy microbial life forms in the water itself as well as in any biofilm on the containers for the water or upon the walls of channels or lines through which the ozonated water flows because ozone is a viricide, bactericide, and algicide. Referring to Figure 1, there is shown apparatus 10 for ozonating water entering a dental office to provide ozonated water to each dental chair. The ozonated water will destroy any microbes or pathogens within the water and reduce or terminate the motility and viability of microbial activity in any biofilm that may be present on the walls of the water lines and attendant dental implements. Furthermore, the ozonated water will 1 o terminate the motility and viability of any microbes or pathogens aspirated from a patient and entering any water channels in the dental implements and the water lines extending from the dental implements.
With joint reference to Figures 1 and 2, apparatus 10 includes a container 12 for receiving water from a water line 14. An ozone generator 16 is disposed within container 12 and includes a lamp or tube 18 for emitting ultraviolet light within a watertight steel cylinder 17. A compressor 20 provides a source of air under pressure through pipe 22 into ozone generator 16. Outlet 24 of pipe 22 may be at the upper end of the ozone generator, as illustrated. A pipe 26 extends from within the ozone generator and includes an inlet 28 located at the lower end of ozone generator 16. Thereby, air flowing into the 2 o generator through outlet 24 is forced to pass around and along tube 18 to inlet 28 to increase the exposure of the air to the ultraviolet radiation from the tube.
It is well known that the oxygen in the air subjected to ultraviolet light will result in conversion of the oxygen molecules into ozone molecules as a function of the intensity of and exposure time to ultraviolet radiation. Thus, ozone enriched air flows into pipe 26 through inlet 28.
2 5 A check valve 30 in pipe 26 prevents reverse flow therethrough. Pipe 26 is terminated by a sparger 32. The sparger emits the ozone enriched air in the form of tiny bubbles which become readily entrained and/or dissolved in the water in and flowing through container 12.
Ozone entrained in water will destroy microbial life forms in the water itself as well as in any biofilm on the containers for the water or upon the walls of channels or lines through which the ozonated water flows because ozone is a viricide, bactericide, and algicide. Referring to Figure 1, there is shown apparatus 10 for ozonating water entering a dental office to provide ozonated water to each dental chair. The ozonated water will destroy any microbes or pathogens within the water and reduce or terminate the motility and viability of microbial activity in any biofilm that may be present on the walls of the water lines and attendant dental implements. Furthermore, the ozonated water will 1 o terminate the motility and viability of any microbes or pathogens aspirated from a patient and entering any water channels in the dental implements and the water lines extending from the dental implements.
With joint reference to Figures 1 and 2, apparatus 10 includes a container 12 for receiving water from a water line 14. An ozone generator 16 is disposed within container 12 and includes a lamp or tube 18 for emitting ultraviolet light within a watertight steel cylinder 17. A compressor 20 provides a source of air under pressure through pipe 22 into ozone generator 16. Outlet 24 of pipe 22 may be at the upper end of the ozone generator, as illustrated. A pipe 26 extends from within the ozone generator and includes an inlet 28 located at the lower end of ozone generator 16. Thereby, air flowing into the 2 o generator through outlet 24 is forced to pass around and along tube 18 to inlet 28 to increase the exposure of the air to the ultraviolet radiation from the tube.
It is well known that the oxygen in the air subjected to ultraviolet light will result in conversion of the oxygen molecules into ozone molecules as a function of the intensity of and exposure time to ultraviolet radiation. Thus, ozone enriched air flows into pipe 26 through inlet 28.
2 5 A check valve 30 in pipe 26 prevents reverse flow therethrough. Pipe 26 is terminated by a sparger 32. The sparger emits the ozone enriched air in the form of tiny bubbles which become readily entrained and/or dissolved in the water in and flowing through container 12.
An electronics assembly 34, connected to a suitable power source, provides the requisite electrical power through conductor 36 to tube 18 to bring about energization of the tube and emission of ultraviolet radiation. To prevent an accumulation of ozone enriched air within container 12, any such gaseous compound is evacuated through an outlet 40 leading to a gas separator 42 through a pipe 44. Outflow from the gas separator is through a pipe 46 to an ozone destructor 48. The remaining air is discharged through a pipe 50 to a drain or the like to accommodate drainage of any moisture that may accumulate downstream of container 12.
As an alternative to air injection, oxygen may be injected into ozone generator 16 1 o to provide a higher concentration of ozone in the gas discharged from sparger 32. A
source of oxygen and an injector for propelling oxygen into the ozone generator is represented by numeral 52 identifying an oxygen injector. The oxygen is injected through pipe 54 into the ozone generator. It is to be understood that injection of air or oxygen is primarily in the alternative although oxygen enriched air could also be injected.
15 The ozonated water produced within container 12 is discharged through outlet 60 into conduit 62. The conduit serves as a water line to provide ozonated water at each of chairs 64,66, etc. in a dental office. In particular, branch lines 68,69 may extend from conduit 62 to a manifold or the like attendant each dental chair and in fluid communication with dental implements and other devices that normally discharge the 2 0 water received. Waste water generated at chair 64 is conveyed to a drain 70 through drain line 72. Similarly, waste water generated at chair 66 is conveyed to drain 70 through drain line 74. Such drain lines would be present for each chair.
Ozone entrained in water is somewhat unstable and will revert to the molecular form of oxygen at a higher or lower rate depending upon a number of variables.
To 2 5 ensure a fresh supply of ozonated water within conduit 62 after periods of inactivity or non-flow of ozonated water through one or more of branches 68,69, a flow restrictor 80 may be employed. Such flow restrictor accommodates a low flow rate of ozonated water continuously through conduit 62 into discharge pipe 82 and drain 70.
Alternatively, a return line 90 is in fluid communication with conduit 62 downstream of the last branch leading to a dental chair. Ozonated water from conduit 62 is drawn into the return line by a pump 92. The pump conveys the ozonated water through return line 94 into water line 14 upstream of inlet i 5 in container 12. Thus, the ozonated water flowing through the return line, which water may have a lowered concentration of entrained ozone, is reintroduced to the ozone generator. Such reintroduction, rather than simply having the ozonated water recirculate through conduit 62 and the return line, ensures that water having at least a minimal level of entrained ozone is always present at each of the branch lines (such as branch lines 68,69).
1 o For reasons set forth above, a number of dental offices have begun to use bottles of distilled or purified water instead of relying upon the municipal water system to satisfy the water needs. Referring to Figure 3, there is illustrated a variant apparatus 100 for use in conjunction with such bottled water. An ozone generator 102 includes a lamp or tube 104 disposed within a closed steel cylinder 105 and connected to an electronics assembly 106 through a conductor 108. Upon energizing the electronics assembly, electrical power is provided to tube 104 causing it to emit ultraviolet radiation. The air within cylinder 1 OS of ozone generator 102 will be irradiated to cause a molecular change of the oxygen into ozone. An inflow of air is provided from outlet 112 of pipe 114 connected to an air source 116 under pressure. A regulator 118 may be disposed in pipe 114 to regulate the 2 o pressure of the air flowing into the ozone generator. As suggested by the dashed box identified as an oxygen injector 120, oxygen may be discharged through outlet 112 into cylinder 105 or a mixture of air and oxygen may be discharged into the cylinder. The ozone enriched air within cylinder 1 OS flows out through inlet 122 of pipe 124. As illustrated, outlet 112 and inlet 122 are at opposite ends of tube 104 to maximize 2 5 exposure of the air to the ultraviolet radiation emitted from tube 104 and thereby enhance the ozone enriched air.
Bottle 130 containing distilled or otherwise purified water 132 includes a stopper 134 for sealing the bottle against contact between the ambient air and water 132. Pipe 124 extends through stopper 134, as illustrated, and is terminated by a sparger 136 located in proximity to the bottom of bottle 130. The purpose of the sparger is that of discharging the ozone enriched air into the water in the form of tiny bubbles to enhance entrainment within the water. A discharge conduit 138 includes an inlet 140 proximate the bottom of bottle 130. The ozone enriched water {ozonated water) within bottle 130 is 5 conveyed via discharge conduit 138 through stopper 134 to the various dental handpieces or other water related dental implements. Thereby, these handpieces and implements are supplied with ozonated waxer which will have the effect of destroying the motility and killing any bacteria, microbes or microorganisms present in either the water or in any biofilm on the wall of the discharge conduit or the walls of channels in the handpieces or 1 o dental implements. Under certain circumstances, it may be beneficial to treat chemically the water flowing to the dental handpieces and other implements. This may be accomplished by incorporating a chemical injector 142 in fluid communication via conduit 143 with discharge conduit 138 downstream of bottle 130.
A certain amount of ozone enriched air will separate from water 132 and collect at the top of bottle 130. This ozone is discharged through discharge line 14S
extending through stopper 134 from within the bottle. The impetus for such discharge results from the pressure within the bottle generated by the inflowing ozone enriched air through sparger 136. The rate of ozone discharge through line 14S is controlled by flow restrictor 146. To prevent damage to the ambient environment, an ozone destructor 147 eliminates 2 o the ozone molecules such that the resulting venting through outlet 148 is a gas essentially ozone free.
Referring to Figure 4, there is illustrated a further variant apparatus 1 SO
similar to variant apparatus 100 shown in Figure 3 except that ozone generator 1S2 is disposed within bottle 1 S4. The ozone generator may be suspended from or otherwise attached to 2 5 a cap 1 S 6 in threaded engagement with neck 1 S 8 of bottle 1 S 4. A lamp or tube 160 for emitting ultraviolet radiation is disposed within a closed steel cylinder 162 of ozone generator 1 S2. It is electrically connected to an electronics assembly via a conductor i 61.
Air, oxygen, or a mixture of air and oxygen is pumped into the ozone generator through a pipe 163 having an outlet 164 proximate one end of tube 160. The ozone enriched air produced by radiation from tube 160 is discharged into inlet 166 of pipe 168.
The pipe, which may extend through a wall of cylinder 162, as illustrated, discharges the ozone enriched air through a sparger 170 located in proximity to the bottom of bottle 154 to enhance entrainment of the ozone enriched air in water 172 as the minute bubbles from the sparger migrate upwardly. The ozone enriched water or ozonated water is discharged from within bottle 154 through inlet 174 of conduit 176. As indicated, conduit conveys the ozonated water to the dental handpieces and other dental implements using water as part of their function. As noted in the drawing, the air flow from outlet 164 to inlet 166 within cylinder 162 is essentially along the full length of tube 160 to enhance 1 o exposure of the air to ultraviolet radiation and thereby promote transformation of the oxygen molecules into ozone molecules.
Referring to Figure 5 there is shown an apparatus 200 similar to a great extent with apparatus 10 shown in Figure i. For identification purposes, the same reference numerals for common elements will be used. By operation of ozone generator 16, a 15 combination of air and ozone is introduced into water 202 within container 12 by sparger 32. Accordingly, the water outflowing from container 12 through conduit 62 will have a mixture of entrained andlor dissolved oxygen and ozone. Prior to flow of this mixture into branch lines 68,69, etc. it is passed through a silver catalyst cartridge 204. Within the cartridge, the oxygen entrained/dissolved in the water makes contact with the silver 2 o and will dissociate fi~om its normal diatomic state to bond with the silver. However, this bond is weak enough that the oxygen will dissociate to oxidize organic matter (such as microorganisms) in contact therewith. Through such oxidation, the microorganisms, which are the major dangerous constituents of biofilm and present potential health hazards, will be destroyed. Thereby colonization of such microorganisms will not and 2 5 cannot occur. Additionally, a small amount of silver dissolves into the water flowing therepast and conveyed downstream through branch lines 68,69, etc. to the various handpieces and dental implements attendant each of chairs 64,66, etc. A
portion of the silver dissolved into the water will adhere to the interior surfaces of the branch lines, the handpieces and the implements. Upon such adherence, the silver is free to react with the oxygen conveyed therepast by the flowing water. Typically, the concentration of silver is only order of about three parts per million (3 mg/L).
The apparatus shown in Figure 5 provides numerous beneficial features for a dental operatory or other medical facility using water from a municipal water source. The introduction of ozone into the water has the beneficial effect of sterilizing the water received. By using a sparger, to introduce the ozone and attendant air from the ozone generator establishes elevated levels of oxygen and ozone in the water. The solubility of the ozone in the water is essentially proportional to the pressure. The ozone assists in biofihn reduction by dissociating to form oxygen containing radicals which will react 1 o (oxidize) organic matter and microorganisms. Additionally, the presence of ozone within the silver catalyst cartridge increases the activity of the silver catalyst and thereby increases the reaction rate between the silver and oxygen. It is believed that an interaction between the silver and the ozone may cause some reaction with the water itself to convert a small amount of the water to hydrogen peroxide; it is well known that hydrogen peroxide is a strong oxidizer and functions as a disinfecting agent.
Accordingly, the presence of hydrogen peroxide may have a further beneficial effect in destroying existing biofilm and preventing the formation of biofilin. As the ozone is carried downstream, it will spontaneously decompose to oxygen and its effectiveness for biofilm destruction will be reduced. However, the silver present in the water and adhered 2 o to the walls of the conduits, pipes, handpieces and implements will react with the dissolved oxygen decomposed from the ozone and provide fiuther destruction of organic matter and the microorganisms. As a result of the combination of ozone and oxygen entrainment in the water and the silver catalyst, the water flowing into the dental handpieces and dental implements will be sterile and a residual disinfecting agent will 2 5 exist throughout the plumbing network of a dental operatory.
For the above and below described configurations employing ozone, it may be prudent from time to time to purge the water conduits and related water conveying equipment with ozone. Such purging, after evacuation of all water, would expose and tend to destroy any residual biofilm that may be present on the exposed surfaces.
The use of ozonated water, with or without purging with ozone, will help keep the water conduits and associated equipment clean. Thus, the maintenance (cleaning) is reduced and the performance and life of dental drills, irngation faucets and all water using dental tools will be enhanced.
Referring to Figure 6 there is shown an apparatus 210, which apparatus is similar to that shown in Figure 3. With respect to common elements, the same reference numerals will be applied. The major difference between the apparatus 100 (Figure 3) and apparatus 210 is the introduction of a silver catalyst cartridge 212 in series with discharge conduit 138. As set forth in further detail with reference to Figure 3, sparger 136 1 o introduces ozone and oxygen to water 122 within container 130. This ozone and oxygen is entrained and to some extent dissolved in the water outflow through discharge conduit 138 and enters silver catalyst cartridge 212. The beneficial effects of the water outflowing finm the cartridge through discharge conduit 138 will be essentially the same as discussed above with respect to Figure 5.
15 Figure 7 illustrates apparatus 220, which is essentially the same as apparatus 150 shown in Figure 4. Accordingly, common elements have been given the same reference numerals. Apparatus 220 includes a silver catalyst cartridge 222 disposed in series in conduit 176 conveying water to the various handpieces and implements, as discussed above. The ozone and oxygen discharged by sparger 170 into water 172 contained in 2 o container 154 is transmitted to and through silver catalyst cartridge 222.
The reactions within the cartridge and beneficial effects of the water flowing therefrom discussed above with respect to Figures ~ and 6 will also be true for the water flowing from cartridge 222 of apparatus 220.
Figure 8 illustrates an apparatus 230 similar in many respects to the apparatus 2 5 shown in each of Figures 5, 6 and 7 except that an ozone generator is not formed a part thereof. The deletion of the ozone generator constitutes a significant cost reduction and avoids maintenance efforts and expenses associated therewith. Apparatus 230 includes a container 232, which may be referred to a saturation chamber (a term which could also be applied to the containers associated with each of apparatus 200, 210 and 220).
A source 234 of air, which could be air from a dental operatory supply, is conveyed through a conduit 236 into container 232. A regulator 238 may be disposed in conduit 236 to maintain the pressure therein at a predetermined pressure, such as 45 psig. To prevent outflow from container 232 through conduit 236 a check valve 230 may be employed in the conduit. A sparger 242 is disposed at the terminal end of conduit 236 to introduce fine bubbles of air into water 244 to entrain/dissolve these bubbles in the water. To prevent a buildup of an air space 246 within container 232, a vent conduit 248 may be employed. Such conduit would include a flow restrictor 250 to prevent discharge of 1 o water therethrough. The air (gas) flow past the restrictor may be vented to the atmosphere through an outlet 252.
To increase the amount of oxygen to be entrained in water 244, a source 254 of oxygen may be employed, as depicted in dashed lines. The oxygen is conveyed through conduit 256 from the source of oxygen into conduit 236. A valve 258 may be used to 15 select inflow from either source 234 of air or source 254 of oxygen;
alternatively, a valve capable of metering a flow from each of the sources of air and oxygen may be used.
Because each of the source of air and the source of oxygen must be under pressure to cause gas to flow therefrom into conduit 236, water 244 in container 232 becomes pressurized. Such pressure environment also assists in expelling gas through vent conduit 2 0 248 to prevent existence of a significant air space 246. The pressure environment present within container 232 causes the water to be discharged into inlet 260 of discharge conduit 262. The discharge conduit conveys the water with entrained air/oxygen to silver catalyst cartridge 264. The chemical reactions resulting within the cartridge are the same as those described above with respect to Figures 5, 6 and 7. The outflow from the 2 5 cartridge is conveyed via conduit 266 to the branch lines associated with each dental chair and the related handpieces and implements, as described above. To further assist in destroying microorganisrris within the water discharged from container 232, a W source 268 may be used in conjunction with discharge conduit 262 to irradiate the water flowing therepast and thereby kill irradiated microorganisms. As UV source 268 is an alternate embodiment, it is shown in dashed lines.
Referring jointly to Figures 9, 10a, l Ob and l Oc, a representative silver catalyst -cartridge will be described in detail. A cartridge of this type may be used as each of the silver catalyst cartridges discussed above. The cartridge is formed of a tube or sleeve 282 having an interior diameter of .0875 inches and of a 2 inch length. A plug 284 is disposed at each end. The plug includes a cylinder 286 for insertion into an end of sleeve 282 and an annular protrusion 288 to limit insertion of the plug. A centrally located threaded aperture 290 is formed in the plug to threadedly receive a fitting 292 having a 1 o barbed nipple 294 extending therefrom for penetrable engagement with an attached conduit. A downstream fitting engaging downstream plug 284 may be similar to fitting 292; alternatively, it may be a fitting 296 threaded engaging plug 284 and configured to receive and engage the end of tubing or a conduit extending therefrom. A
twenty micron (20~c) filter 298 may be attached to the downstream plug, which filter prevents outflow of 15 particulate material largex than twenty microns. Silver catalyst 298 comprises beads of silver packed between the end plugs within sleeve 282. These beads comprise silver deposited on a mineral substrate (alumina) and are available from Fountainhead Technologies, Inc. of Providence, RI. They are described in further detail in an article entitled "Fountainhead Technologies talks about their unique approach to catalytical 2 o water purification" published in the November, 1994 issue of the Catalyst Review Newsletter, which article is incorporated herein by reference and attached as Exhibit "A".
As set forth in a Material Safety Data Sheet prepared by Fountainhead Technologies, Inc.;
incorporated herein by reference and attached as Exhibit "B", the ratio of alumina (Ah03) to silver (Ag) is in the range of about 97.9% to about 98.3% and in the range of about 2 5 2.1 % to about 1.7%, respectively.
As described above, the silver catalyst cartridge works essentially in the following manner. Dissolved oxygen in the water flowing through the cartridge contacts the beads of silver. The bond of diatomic oxygen molecule is ruptured upon contact to create individual oxygen atoms which then become loosely bound to the silver surface.
The WO 99!65533 PCT/US99/13591 unique ability of silver to enter into oxidative reactions is due to the very weak bond it forms with oxygen (approximately 7 to 8 kcaUmol; most other transition metals bond with oxygen at strengths of more than 100 kcal/mol).. These weak bonds allow silver to readily transfer the loosely held oxygen atoms to any oxidizable substrate, such as organic matter and microorganisms. When other organic matter and microorganisms make contact with the loosely bound oxygen atoms, oxidation occurs and the bonds in the organic matter and microorganisms are ruptured. The oxidized fragments will depart from the surface of the silver beads to expose the beads and the process is repeated. Silver ions are slowly released into the water by a combination of erosion and galvanic action. The silver ions so produced provide a residual oxidation activity downstream to affect any organic matter or microorganisms coming in to contact therewith.
To test the efficacy of the present invention, a number of experiments were conducted in different dental office locations. The results of these experiments are tabulated in Figure 11. During these tests, the number of colony forming units (cfu) per millimeter at each Noted sampling cite were recorded. In office No. 1 prior to use of the present invention, the water at handpiece A had 220,000 cfus and a water irrigation implement had 450 cfus. During the succeeding three weeks, the number of cfus dropped to 1, 3 and 0 and 1, 4, and 0, respectively. In office No. 2, a handpiece A
and a water irrigation implement prior to installation of the invention had 34,000 cfus and 355,000 2 0 cfus, respectively. After one week, the sample at handpiece A contained less than 100 cfus and there were none in the irrigation implement. For the following three weeks, there were no cfus measured at either the handpiece A or the irngation implement. In the office No. 3, prior to use of the invention, handpiece A had 9,400 cfus and water irrigation implement had 12,150 cfus. After installation of the invention, the cfus at 2 5 handpiece A dropped to 80 and the cfus at the irrigation implement dropped to 13. After a week, the cfus at handpiece A dropped to 5 and the cfus at the irrigation implement increased to 23 (the reason for the increase is unknown and may have been poor data or due to an intervening activity). In office No. 4, the number of cfus at handpiece A was 40,000 and at water irrigation implement was 41,000 prior to installation of the invention.
3 0 Thereafter, the cfus dropped to zero after installation and for the ensuing four weeks. In WO 99/65533 PC'f/US99/13591 office No. 5, the number of cfus prior to installation were 212 at the handpiece A and 89,500 at the water irrigation implement. Thereafter and for the next five weeks, the number of cfus at each of the handpiece and the water irrigation implement was essentially zero. In office No. 6, handpiece A contained 4,100 cfus and the water irrigation implement contained 350 cfus prior to the installation of the present invention.
After installation and one week thereafter, the cfus at both locations dropped to zero.
Accordingly, one must come to the inescapable conclusion that the present invention is highly effective in destroying microorganisms in the environment of a dental operatory. Furthermore, it will destroy any existing biofilm and will prevent the buildup of biofilm in the attendant water conduits and water conveying and pieces and implements used in the dental practice.
While the invention has been described with reference to several particular embodiments thereof, those skilled in the art will be able to make the various modifications to the described embodiments of the invention without departing from the true spirit and scope of the invention. It is intended that all combinations of elements and steps which perform substantially the same function in substantially the same way to achieve the same result are within the scope of the invention.
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EXHIBIT " A'"
CATALYST REVIEW N~SL
November 1994 Reprint of the Special Fountainhead Interview:
UCC Fdes Appeal .........................1 Dow Sues Fxxoa .......................2 "Fountainhead Degassa/Hindustan 3 Agreement.
n~pands ......................4 Technologies Engelhard Introduces Talks About Their New FCC Catalyst .............................5 Smciallnieroinv: Unique Approach to Fountainhead's Unique , ~a~l~Wa~.P~~tion......~ Catalytic Water '"~yt'~~~a'~'~ Purif i c ati o n"
Awarded Grant ............................10 N-arylamides from Aromatic ds 12 C
u ..................................
ompo n Smcial Feahm:
Catalysis RdzD at the National Laboratories13 ................ Conducted by: The Catalyst Review Stauffei s New Flue Gas Process . 15 ' Industry Rumors.......................... 16 ;.
n~ocESs Spiocial bsteraietv with Forartaixshcad Technologies Fountainhead Technologies Tallcs About Their Unique Approach to Catalytic Water P ' 'canon..
Fosssdtd iu 1983, ForasbaiaHtad T'eaiiaologies, htt (FHT7 is a rrlai~iat utrocomerirs tlu aqueous saaitaNon bias, Ray Deoktwic~. Daedor of Rtseanale & Drcelopnreat for F81. rra~y spoke ud~k The CatalystReaiuo aboutt&t ar>~s proprietmy ca~Iy~c ~x p~rio~e systaa and lroto it is diJ~r~xiiattd jrom other aaailable tedmologits. Ray also ap<rke abord du futraie potasdal for tlds fi~da~al tedoiology for water sauitatiox CR: How did Fonat:iahezd become iavolved is the development of ~alytic water pu:sfication systems?
~HT: the company started out in 1983 as a group of three ent:eprmasus exploring the use of silver as a ante tecimology Ior water pari<>mtion. Several yearn prior, studies of potable waoer systems by NASA in the Apollo program showed that ~lv~er ions were effective for drinlang water disirfedion.
But no one had looked at the role of silver in bs~al diainfectiocs, whirls led our founders to the discovery of a catalytic system.
Cst: Could yon explaia your catalyst techuoio6y?
FHT: The catalyst the syatem, which is core of the tectmology.
is what differentiates it from other water pnri~ot~
syabems on the avasket.
We employ a catalyst bed wbaceby Oxidative Catalysis silver is for Aqueous Systems deposed on a mineral subatsatp (alumina). As dissolved oxygen, which sxitssrally exists in water.
mi~E'S ODntaCt With ~ ~~A: aatdYSd the 511VQ' "~
~
catalyst bed (see , Figure i-A~ the , ~, "~;d, bond of the diatomic n~ waryst and oxygen o~ sires molecule is ruptured to erects individual oxygen atoms which then become loosely bound to the silver surface (see Figure I-B). The unique ability of silver to enter into oxidative reactiom iR due to the very weak bond it ~ f~: n" moisaesr forays with oxygen (approximatelybard tisn~r~ar 7 to 8 oxnpsn scans lcral/mol; most other transition metals bond with oxygen' at strengths of more ~,~ y than 100 lccsl jmol). These adcsry dynsmc weak bonds allow silver to readily spa. ~s usarysr transfer the loaselv esd held oxygen atom to "s amam~rnrd'widr any oxidizable~
substrate. As passing~' n'~ arome bactetis or oxyprn.
''viruses make contact with these Spiacial Ir~erviem urith Fora~tai~read Tec3mologits (GOr~ia~re~
loosely bonmd oxygen atoms (see Q~dative Catatwis for Aqaeon S~te~ teow~awdl Figure 1-C~, the bonds in the bao~ia or views are ruptured. The oxidized bsdeia fragments leave ~
the anlyst snrbae (see Fisure 1-D), ~ a prdnp wol~um V
ptovyding a fresh surface receptive "~A lfai . _ . ,_ ~ i to additto~l oxygeen. ~, ~"d ~", i ;~ ..l . _ s,~ ..,,~ ~,~.ty-_ ' In addition to the catalytic action ~ ~' ~ ~ ~~~ ~~
provided by the silver cetalvst bed.
oar sysDems are oleo designed such that both silver end copper ion are sbwlyel~sedioto the water Ian t-0: b~.f~rlt ~an~po.
dsndng op~on by a a ~ banal, wA~d~
combination of a~oaion and galvanic~ ~ a action. The silver ions so prodnad__ provide a reddwlbadeaddal activi and wilN IAa ~poad tY sulAr. AMr the aoppa ion ad as npsad ooh ~
a residual p/~r Ir dl~lp~d h C& >xaotly how eiffective is yoar techaoloay is purifying wated FAT: A nnasber of a" o"' e~cpenments have been pa~smed on the system's efli~acy.~ Most noteworthy is one study performed at the Univeesity of Arizona~'~ s,inereby a 99.96 percent reduction in E. toll (fmm an initial oonoentration of Z4 x 10' CFU/ml) was obwnred in a single pass over the analyst wherein the contact time between the water and catalyst was on the order of just a few seconas. This study, as well as others conducted is pause and at independenk labs, demonstrates that the catalyst system produces water that is pose enough to meet US. Environmental P~tedion Agenry dr3nicarg water standards (see Table 1 ).
Table 1 EPA Stu~dands for Miaeals ~c Bacber;a in Dr>akina Water EPA Mmo~aaa~m Level Fount;iabead Glalyst Pte' ae: Compaason BadetialLevel(Coliform) <1/100mL lI/100mL' meets standard 5vlver O.l,ppm 0.01- 0.035 ppm b6X below maximum Copper ~ 1.0 ppm 0.02 - 0.06 ppm 95 x below maximum 99%% of 6~ia Idled wnsin 5 seconds of ca~ct Special Itrha~ai~w with Forartai~ad Ta3rnologus (cortarared) CR: What diffeteati~s FFIT"s system f~ ~6 ~°~'at f~I': 'f tire ace a nnaibar of ws~ pms6oation ted~nofogiss ai Mme ~y ~ t~
world. Cbior~ne is tl~e mwt aorrvenoonai and most widely nssd water disarfatxion system. Omcte ga~tatoes.
elecaode iosu:ms. rev~ss osarasrs. and distil>ation errs slso wrH aaaepted methods for pa~iYi~ war Utililrs these otl~ systmu, ma ~iyst-based system is lees costly to operate. no ~'~Y ~ v'aY ~ ~PP~ . 'tee 1~~
of eonsse. is the catalyst sysemt which makes otrs psvduds s>m~e ltd e~odlve. Our catahst the a~islli of the baaena and the virsss sad. because of the sbw sdede of copper and srlva ions. it promdes reaidual:aaitatioa No other water pn:i~ott systeat cur do an ~.
We c~urently hold four U5. pates and thtae are several snare U5. and forttigst patatls pending.
Cats W6ids madceb are crest tailed forFFICI"a waterpsa~a~ea per?
FHI': Our oorrstrltants at Ardms D. I~tle have helped us idadify nasrsrotrs marltats for which this tsr~no~r is appsarpnate. 'They a>dttde: ~tiaetal wamr. pole water. o~olictg towea. and a variety of irdustzial appi~otrs.
pity prsasary market right sow is steeatiosral water. We've been is that market for the last two years. To date, soars 20.000 onus have been arta0ed is swimming pools and spas at as SO US. states.
The series potettial for this mseiret alone ~s wound fight million mots. in 1994, in this masker ak~tte.
Founvitrltead Tedmologies expavenoed approxiatatrly 700 paoent ssies gsowttt.
We heiieve our tedamlogy is ideally suited for the dsiriang water market- ~e ~
m~ Ameriaut i~ouseholds me well water and about 50 pesoetst of the gtouadwatei reserns is ~ U.S.
°s'e y polluted. In additiam. last year alone, these weee 250,000 violations of the Sate Dratl~sg Waoer Ad by mu:nopal water suppliers.
These facts reprnent a substaatisl market opportunity for our tedatdogy.
Referrrrcrs:
Ges~a. C°.. Naranjo. J., Hvaluation of Catalvtically Active Media for Miavvisl Reduction. Teclut>cal Report.
:~pnl n.1993.
~ATAL1'IIC fVata Purifier Cadge Disiniec~on F.lfmatcy. Researdt ltspo~
1t13826, Herbert V. Shtrifa inc..
Octooer 20.1993.
C=. Heisug Jr.. O~ or O~ and Ag: A New:atalyst Technology for Aqueous Phase ~arutation. Ozone Soartae and cogtr~eertng, VoL I5. p. 333.1993.
Source: : ne Cacalvrx Review EXHIBIT "B"'' Witrrrr Furs'fi~arion Technolop~
forttttsiaAs~d Ttieweolo,ios, lac.
30t v~ll~r Strect Preridlnw. AI ti~Jt TH.140tf 725~!!!0 fu 1101175~9993 nttlntlt Aeonc::
rt~tvn?.ndvo~~.can -MATERIAL SAFETY DATA SHEET
S~tion I Product Information Trade Name f~rld Synonyms:Natures , VISION~
Chemical Family: Heterogeneous Catalyst Formula: AIzOa +. Ag Chemical Names: Aluminum Oxide, Sihrer Common Names: Aiumina. Silver Metal Section 11 Hazardous InBredierlts Components in the Solid Mixture:
Component: Alumina CAS 1344-28-1 Pen~r~t: 97.9 . 98.3%
OSHA PEL: 15 mglm3 Total dust; 5 mglms Respirabie fraction TWA
ACGtH TLV: 10 mgim3 TWA
Component: Silver metal CAS 7440-22-4 Percent: 1.7 - 2.1 OSHA PEL: 0.01 mglm3 TWA
ACGIH TLV: 0.1 mg/m3 TWA
EXHIBIT "B"
Section 111 Physical Data Appearance and Odor. Dark gray granules. No odor.
Solubility in Water: Insoluble Sulk Density: .65 ~0 g / crn~
Percent Votatife (wt) (~7 1 ~0~°F: Less than 1 Section IV Fire Explosion Data Fire and Explosion Hazard: Material will not bum or explode. See Section Vt for incompatible materials.
Flash Point: Non flammable Firef~ghting Media: Dry chemical, water spray or foam. For larger fires, use water spray, fog, or foam.
Stability: Stable Conditions to Avoid: None Known Section V Health Hazard Data Health hazards may arise from aye contact, prolonged or repeated skin contact, repeated inhalation, or repeated ingestion.
Contains silver which can cause argyria, gray pigmentation of the eyes, skin, and mucous membranes if it is repeatedly inhaled or ingested. May cause eye and skin irritation. No ingredient of this product is listed by NTP; /ARC, or OSHA as a carcinogen.
Signs and symptoms of exposure: Redness and tearing of the eyes, gray pigmentation of eyes, skin, or mucous membranes.
Medical conditions aggravated by exposure: Pns-existing skin and eye condi~ons.
Asthma or lung disease.
Vortex Water Technologies s.ss.rpd 2 DWM-300 Dental Water Catalyst Section V (coot.) Health Hazard Data First Aid: In case of contact, immediately flush eyes or skin with plenty of water for at least 15 minutes. Remove contact lenses, if worn. Remove contaminated clothing and shoes. If inhaled, remove to fresh air. If not breathing, give artificial respiration. If breathing is difficult, give oxygen. If Large quantities are swallowed, call a physician immediately. Do NOT induce vomiting unless directed to do so by a physician.
Never give anything by mouth to an unconscious person.
Section VI Reactivity Data Reactivity: Stable under normal temperature and pressures in sealed containers. Hazardous polymerization will not oxur.
Incompatibility (materials to avoid): Acetylene, acetylene compounds. aziridine, bromine azide, 3-bromopropyne, carboxylic acids, ethylene oxide. ethyl hydroperoxide, ethyleneimine, iodoform, nitric acid, ozonides, peroxomonosuifuric acid, and peroxyforrnic acid.
Hazardous Decomposition Products: None Section Vli Spill or Leak Procedures l Diapoaal Spill or Leak Procedures:
Notify safety personnel of spills or teaks. Clean-up personnel need protection against inhalation of dusts or fumes. Eye protection is recommended. Vacuuming or wet methods of clean-up are preferred. Place in appropriate containers for disposal keeping airborne particles at a minimum.
Disposal:
Consult applicable local, state, or federal regulations to select method of disposal.
Recover metal components by reprocessing whenever possible.
Contains silver which is reported to be toxic to both terrestrial and aquatic organisms.
Sihrer is a CERCLA hazardous substance with a reportable quantity of 1000 Ibs.
(454 kg). Silver is a toxic chemical subject to the reporting requirements of SARA
Title 111 ~313 and 40 CFR Part 372. Contains silver, RCRA hazardous waste number D011.
Vortex Water Technologies g.sits.rpd 3 OWM-300 Dental Water Catalyst Section VIII Special Protoctfon Information Respiratory Protection: Provide a NiOSHIMSHA approved respirator in the absence of proper environment control. Contact your safety equipment supplier for proper mask type.
Ventilation: Provide general andlor local exhaust ventilation to keep exposures below the TL.V. Ventilation used must be designed to prevent spots of dust accumulation or recycling of dusts.
Protective Clothing: Wear protective clothing, including long sleeves and gloves, to prevent repeated or prolonged skin corEtact.
Eye Protection: Chemical splash goggles in compliance with OSHA
regulations are recommended.
Personal Hygiene: Avoid breathing dust. Avoid contact with eyes, skin, and clothing. Do not taste or swallow. Keep skin breaks covered. Wash thoroughly after handling.
Keep container closed.
Vortex Water Technologies DWM-300 Dental Water Catalyst *rB
As an alternative to air injection, oxygen may be injected into ozone generator 16 1 o to provide a higher concentration of ozone in the gas discharged from sparger 32. A
source of oxygen and an injector for propelling oxygen into the ozone generator is represented by numeral 52 identifying an oxygen injector. The oxygen is injected through pipe 54 into the ozone generator. It is to be understood that injection of air or oxygen is primarily in the alternative although oxygen enriched air could also be injected.
15 The ozonated water produced within container 12 is discharged through outlet 60 into conduit 62. The conduit serves as a water line to provide ozonated water at each of chairs 64,66, etc. in a dental office. In particular, branch lines 68,69 may extend from conduit 62 to a manifold or the like attendant each dental chair and in fluid communication with dental implements and other devices that normally discharge the 2 0 water received. Waste water generated at chair 64 is conveyed to a drain 70 through drain line 72. Similarly, waste water generated at chair 66 is conveyed to drain 70 through drain line 74. Such drain lines would be present for each chair.
Ozone entrained in water is somewhat unstable and will revert to the molecular form of oxygen at a higher or lower rate depending upon a number of variables.
To 2 5 ensure a fresh supply of ozonated water within conduit 62 after periods of inactivity or non-flow of ozonated water through one or more of branches 68,69, a flow restrictor 80 may be employed. Such flow restrictor accommodates a low flow rate of ozonated water continuously through conduit 62 into discharge pipe 82 and drain 70.
Alternatively, a return line 90 is in fluid communication with conduit 62 downstream of the last branch leading to a dental chair. Ozonated water from conduit 62 is drawn into the return line by a pump 92. The pump conveys the ozonated water through return line 94 into water line 14 upstream of inlet i 5 in container 12. Thus, the ozonated water flowing through the return line, which water may have a lowered concentration of entrained ozone, is reintroduced to the ozone generator. Such reintroduction, rather than simply having the ozonated water recirculate through conduit 62 and the return line, ensures that water having at least a minimal level of entrained ozone is always present at each of the branch lines (such as branch lines 68,69).
1 o For reasons set forth above, a number of dental offices have begun to use bottles of distilled or purified water instead of relying upon the municipal water system to satisfy the water needs. Referring to Figure 3, there is illustrated a variant apparatus 100 for use in conjunction with such bottled water. An ozone generator 102 includes a lamp or tube 104 disposed within a closed steel cylinder 105 and connected to an electronics assembly 106 through a conductor 108. Upon energizing the electronics assembly, electrical power is provided to tube 104 causing it to emit ultraviolet radiation. The air within cylinder 1 OS of ozone generator 102 will be irradiated to cause a molecular change of the oxygen into ozone. An inflow of air is provided from outlet 112 of pipe 114 connected to an air source 116 under pressure. A regulator 118 may be disposed in pipe 114 to regulate the 2 o pressure of the air flowing into the ozone generator. As suggested by the dashed box identified as an oxygen injector 120, oxygen may be discharged through outlet 112 into cylinder 105 or a mixture of air and oxygen may be discharged into the cylinder. The ozone enriched air within cylinder 1 OS flows out through inlet 122 of pipe 124. As illustrated, outlet 112 and inlet 122 are at opposite ends of tube 104 to maximize 2 5 exposure of the air to the ultraviolet radiation emitted from tube 104 and thereby enhance the ozone enriched air.
Bottle 130 containing distilled or otherwise purified water 132 includes a stopper 134 for sealing the bottle against contact between the ambient air and water 132. Pipe 124 extends through stopper 134, as illustrated, and is terminated by a sparger 136 located in proximity to the bottom of bottle 130. The purpose of the sparger is that of discharging the ozone enriched air into the water in the form of tiny bubbles to enhance entrainment within the water. A discharge conduit 138 includes an inlet 140 proximate the bottom of bottle 130. The ozone enriched water {ozonated water) within bottle 130 is 5 conveyed via discharge conduit 138 through stopper 134 to the various dental handpieces or other water related dental implements. Thereby, these handpieces and implements are supplied with ozonated waxer which will have the effect of destroying the motility and killing any bacteria, microbes or microorganisms present in either the water or in any biofilm on the wall of the discharge conduit or the walls of channels in the handpieces or 1 o dental implements. Under certain circumstances, it may be beneficial to treat chemically the water flowing to the dental handpieces and other implements. This may be accomplished by incorporating a chemical injector 142 in fluid communication via conduit 143 with discharge conduit 138 downstream of bottle 130.
A certain amount of ozone enriched air will separate from water 132 and collect at the top of bottle 130. This ozone is discharged through discharge line 14S
extending through stopper 134 from within the bottle. The impetus for such discharge results from the pressure within the bottle generated by the inflowing ozone enriched air through sparger 136. The rate of ozone discharge through line 14S is controlled by flow restrictor 146. To prevent damage to the ambient environment, an ozone destructor 147 eliminates 2 o the ozone molecules such that the resulting venting through outlet 148 is a gas essentially ozone free.
Referring to Figure 4, there is illustrated a further variant apparatus 1 SO
similar to variant apparatus 100 shown in Figure 3 except that ozone generator 1S2 is disposed within bottle 1 S4. The ozone generator may be suspended from or otherwise attached to 2 5 a cap 1 S 6 in threaded engagement with neck 1 S 8 of bottle 1 S 4. A lamp or tube 160 for emitting ultraviolet radiation is disposed within a closed steel cylinder 162 of ozone generator 1 S2. It is electrically connected to an electronics assembly via a conductor i 61.
Air, oxygen, or a mixture of air and oxygen is pumped into the ozone generator through a pipe 163 having an outlet 164 proximate one end of tube 160. The ozone enriched air produced by radiation from tube 160 is discharged into inlet 166 of pipe 168.
The pipe, which may extend through a wall of cylinder 162, as illustrated, discharges the ozone enriched air through a sparger 170 located in proximity to the bottom of bottle 154 to enhance entrainment of the ozone enriched air in water 172 as the minute bubbles from the sparger migrate upwardly. The ozone enriched water or ozonated water is discharged from within bottle 154 through inlet 174 of conduit 176. As indicated, conduit conveys the ozonated water to the dental handpieces and other dental implements using water as part of their function. As noted in the drawing, the air flow from outlet 164 to inlet 166 within cylinder 162 is essentially along the full length of tube 160 to enhance 1 o exposure of the air to ultraviolet radiation and thereby promote transformation of the oxygen molecules into ozone molecules.
Referring to Figure 5 there is shown an apparatus 200 similar to a great extent with apparatus 10 shown in Figure i. For identification purposes, the same reference numerals for common elements will be used. By operation of ozone generator 16, a 15 combination of air and ozone is introduced into water 202 within container 12 by sparger 32. Accordingly, the water outflowing from container 12 through conduit 62 will have a mixture of entrained andlor dissolved oxygen and ozone. Prior to flow of this mixture into branch lines 68,69, etc. it is passed through a silver catalyst cartridge 204. Within the cartridge, the oxygen entrained/dissolved in the water makes contact with the silver 2 o and will dissociate fi~om its normal diatomic state to bond with the silver. However, this bond is weak enough that the oxygen will dissociate to oxidize organic matter (such as microorganisms) in contact therewith. Through such oxidation, the microorganisms, which are the major dangerous constituents of biofilm and present potential health hazards, will be destroyed. Thereby colonization of such microorganisms will not and 2 5 cannot occur. Additionally, a small amount of silver dissolves into the water flowing therepast and conveyed downstream through branch lines 68,69, etc. to the various handpieces and dental implements attendant each of chairs 64,66, etc. A
portion of the silver dissolved into the water will adhere to the interior surfaces of the branch lines, the handpieces and the implements. Upon such adherence, the silver is free to react with the oxygen conveyed therepast by the flowing water. Typically, the concentration of silver is only order of about three parts per million (3 mg/L).
The apparatus shown in Figure 5 provides numerous beneficial features for a dental operatory or other medical facility using water from a municipal water source. The introduction of ozone into the water has the beneficial effect of sterilizing the water received. By using a sparger, to introduce the ozone and attendant air from the ozone generator establishes elevated levels of oxygen and ozone in the water. The solubility of the ozone in the water is essentially proportional to the pressure. The ozone assists in biofihn reduction by dissociating to form oxygen containing radicals which will react 1 o (oxidize) organic matter and microorganisms. Additionally, the presence of ozone within the silver catalyst cartridge increases the activity of the silver catalyst and thereby increases the reaction rate between the silver and oxygen. It is believed that an interaction between the silver and the ozone may cause some reaction with the water itself to convert a small amount of the water to hydrogen peroxide; it is well known that hydrogen peroxide is a strong oxidizer and functions as a disinfecting agent.
Accordingly, the presence of hydrogen peroxide may have a further beneficial effect in destroying existing biofilm and preventing the formation of biofilin. As the ozone is carried downstream, it will spontaneously decompose to oxygen and its effectiveness for biofilm destruction will be reduced. However, the silver present in the water and adhered 2 o to the walls of the conduits, pipes, handpieces and implements will react with the dissolved oxygen decomposed from the ozone and provide fiuther destruction of organic matter and the microorganisms. As a result of the combination of ozone and oxygen entrainment in the water and the silver catalyst, the water flowing into the dental handpieces and dental implements will be sterile and a residual disinfecting agent will 2 5 exist throughout the plumbing network of a dental operatory.
For the above and below described configurations employing ozone, it may be prudent from time to time to purge the water conduits and related water conveying equipment with ozone. Such purging, after evacuation of all water, would expose and tend to destroy any residual biofilm that may be present on the exposed surfaces.
The use of ozonated water, with or without purging with ozone, will help keep the water conduits and associated equipment clean. Thus, the maintenance (cleaning) is reduced and the performance and life of dental drills, irngation faucets and all water using dental tools will be enhanced.
Referring to Figure 6 there is shown an apparatus 210, which apparatus is similar to that shown in Figure 3. With respect to common elements, the same reference numerals will be applied. The major difference between the apparatus 100 (Figure 3) and apparatus 210 is the introduction of a silver catalyst cartridge 212 in series with discharge conduit 138. As set forth in further detail with reference to Figure 3, sparger 136 1 o introduces ozone and oxygen to water 122 within container 130. This ozone and oxygen is entrained and to some extent dissolved in the water outflow through discharge conduit 138 and enters silver catalyst cartridge 212. The beneficial effects of the water outflowing finm the cartridge through discharge conduit 138 will be essentially the same as discussed above with respect to Figure 5.
15 Figure 7 illustrates apparatus 220, which is essentially the same as apparatus 150 shown in Figure 4. Accordingly, common elements have been given the same reference numerals. Apparatus 220 includes a silver catalyst cartridge 222 disposed in series in conduit 176 conveying water to the various handpieces and implements, as discussed above. The ozone and oxygen discharged by sparger 170 into water 172 contained in 2 o container 154 is transmitted to and through silver catalyst cartridge 222.
The reactions within the cartridge and beneficial effects of the water flowing therefrom discussed above with respect to Figures ~ and 6 will also be true for the water flowing from cartridge 222 of apparatus 220.
Figure 8 illustrates an apparatus 230 similar in many respects to the apparatus 2 5 shown in each of Figures 5, 6 and 7 except that an ozone generator is not formed a part thereof. The deletion of the ozone generator constitutes a significant cost reduction and avoids maintenance efforts and expenses associated therewith. Apparatus 230 includes a container 232, which may be referred to a saturation chamber (a term which could also be applied to the containers associated with each of apparatus 200, 210 and 220).
A source 234 of air, which could be air from a dental operatory supply, is conveyed through a conduit 236 into container 232. A regulator 238 may be disposed in conduit 236 to maintain the pressure therein at a predetermined pressure, such as 45 psig. To prevent outflow from container 232 through conduit 236 a check valve 230 may be employed in the conduit. A sparger 242 is disposed at the terminal end of conduit 236 to introduce fine bubbles of air into water 244 to entrain/dissolve these bubbles in the water. To prevent a buildup of an air space 246 within container 232, a vent conduit 248 may be employed. Such conduit would include a flow restrictor 250 to prevent discharge of 1 o water therethrough. The air (gas) flow past the restrictor may be vented to the atmosphere through an outlet 252.
To increase the amount of oxygen to be entrained in water 244, a source 254 of oxygen may be employed, as depicted in dashed lines. The oxygen is conveyed through conduit 256 from the source of oxygen into conduit 236. A valve 258 may be used to 15 select inflow from either source 234 of air or source 254 of oxygen;
alternatively, a valve capable of metering a flow from each of the sources of air and oxygen may be used.
Because each of the source of air and the source of oxygen must be under pressure to cause gas to flow therefrom into conduit 236, water 244 in container 232 becomes pressurized. Such pressure environment also assists in expelling gas through vent conduit 2 0 248 to prevent existence of a significant air space 246. The pressure environment present within container 232 causes the water to be discharged into inlet 260 of discharge conduit 262. The discharge conduit conveys the water with entrained air/oxygen to silver catalyst cartridge 264. The chemical reactions resulting within the cartridge are the same as those described above with respect to Figures 5, 6 and 7. The outflow from the 2 5 cartridge is conveyed via conduit 266 to the branch lines associated with each dental chair and the related handpieces and implements, as described above. To further assist in destroying microorganisrris within the water discharged from container 232, a W source 268 may be used in conjunction with discharge conduit 262 to irradiate the water flowing therepast and thereby kill irradiated microorganisms. As UV source 268 is an alternate embodiment, it is shown in dashed lines.
Referring jointly to Figures 9, 10a, l Ob and l Oc, a representative silver catalyst -cartridge will be described in detail. A cartridge of this type may be used as each of the silver catalyst cartridges discussed above. The cartridge is formed of a tube or sleeve 282 having an interior diameter of .0875 inches and of a 2 inch length. A plug 284 is disposed at each end. The plug includes a cylinder 286 for insertion into an end of sleeve 282 and an annular protrusion 288 to limit insertion of the plug. A centrally located threaded aperture 290 is formed in the plug to threadedly receive a fitting 292 having a 1 o barbed nipple 294 extending therefrom for penetrable engagement with an attached conduit. A downstream fitting engaging downstream plug 284 may be similar to fitting 292; alternatively, it may be a fitting 296 threaded engaging plug 284 and configured to receive and engage the end of tubing or a conduit extending therefrom. A
twenty micron (20~c) filter 298 may be attached to the downstream plug, which filter prevents outflow of 15 particulate material largex than twenty microns. Silver catalyst 298 comprises beads of silver packed between the end plugs within sleeve 282. These beads comprise silver deposited on a mineral substrate (alumina) and are available from Fountainhead Technologies, Inc. of Providence, RI. They are described in further detail in an article entitled "Fountainhead Technologies talks about their unique approach to catalytical 2 o water purification" published in the November, 1994 issue of the Catalyst Review Newsletter, which article is incorporated herein by reference and attached as Exhibit "A".
As set forth in a Material Safety Data Sheet prepared by Fountainhead Technologies, Inc.;
incorporated herein by reference and attached as Exhibit "B", the ratio of alumina (Ah03) to silver (Ag) is in the range of about 97.9% to about 98.3% and in the range of about 2 5 2.1 % to about 1.7%, respectively.
As described above, the silver catalyst cartridge works essentially in the following manner. Dissolved oxygen in the water flowing through the cartridge contacts the beads of silver. The bond of diatomic oxygen molecule is ruptured upon contact to create individual oxygen atoms which then become loosely bound to the silver surface.
The WO 99!65533 PCT/US99/13591 unique ability of silver to enter into oxidative reactions is due to the very weak bond it forms with oxygen (approximately 7 to 8 kcaUmol; most other transition metals bond with oxygen at strengths of more than 100 kcal/mol).. These weak bonds allow silver to readily transfer the loosely held oxygen atoms to any oxidizable substrate, such as organic matter and microorganisms. When other organic matter and microorganisms make contact with the loosely bound oxygen atoms, oxidation occurs and the bonds in the organic matter and microorganisms are ruptured. The oxidized fragments will depart from the surface of the silver beads to expose the beads and the process is repeated. Silver ions are slowly released into the water by a combination of erosion and galvanic action. The silver ions so produced provide a residual oxidation activity downstream to affect any organic matter or microorganisms coming in to contact therewith.
To test the efficacy of the present invention, a number of experiments were conducted in different dental office locations. The results of these experiments are tabulated in Figure 11. During these tests, the number of colony forming units (cfu) per millimeter at each Noted sampling cite were recorded. In office No. 1 prior to use of the present invention, the water at handpiece A had 220,000 cfus and a water irrigation implement had 450 cfus. During the succeeding three weeks, the number of cfus dropped to 1, 3 and 0 and 1, 4, and 0, respectively. In office No. 2, a handpiece A
and a water irrigation implement prior to installation of the invention had 34,000 cfus and 355,000 2 0 cfus, respectively. After one week, the sample at handpiece A contained less than 100 cfus and there were none in the irrigation implement. For the following three weeks, there were no cfus measured at either the handpiece A or the irngation implement. In the office No. 3, prior to use of the invention, handpiece A had 9,400 cfus and water irrigation implement had 12,150 cfus. After installation of the invention, the cfus at 2 5 handpiece A dropped to 80 and the cfus at the irrigation implement dropped to 13. After a week, the cfus at handpiece A dropped to 5 and the cfus at the irrigation implement increased to 23 (the reason for the increase is unknown and may have been poor data or due to an intervening activity). In office No. 4, the number of cfus at handpiece A was 40,000 and at water irrigation implement was 41,000 prior to installation of the invention.
3 0 Thereafter, the cfus dropped to zero after installation and for the ensuing four weeks. In WO 99/65533 PC'f/US99/13591 office No. 5, the number of cfus prior to installation were 212 at the handpiece A and 89,500 at the water irrigation implement. Thereafter and for the next five weeks, the number of cfus at each of the handpiece and the water irrigation implement was essentially zero. In office No. 6, handpiece A contained 4,100 cfus and the water irrigation implement contained 350 cfus prior to the installation of the present invention.
After installation and one week thereafter, the cfus at both locations dropped to zero.
Accordingly, one must come to the inescapable conclusion that the present invention is highly effective in destroying microorganisms in the environment of a dental operatory. Furthermore, it will destroy any existing biofilm and will prevent the buildup of biofilm in the attendant water conduits and water conveying and pieces and implements used in the dental practice.
While the invention has been described with reference to several particular embodiments thereof, those skilled in the art will be able to make the various modifications to the described embodiments of the invention without departing from the true spirit and scope of the invention. It is intended that all combinations of elements and steps which perform substantially the same function in substantially the same way to achieve the same result are within the scope of the invention.
///
EXHIBIT " A'"
CATALYST REVIEW N~SL
November 1994 Reprint of the Special Fountainhead Interview:
UCC Fdes Appeal .........................1 Dow Sues Fxxoa .......................2 "Fountainhead Degassa/Hindustan 3 Agreement.
n~pands ......................4 Technologies Engelhard Introduces Talks About Their New FCC Catalyst .............................5 Smciallnieroinv: Unique Approach to Fountainhead's Unique , ~a~l~Wa~.P~~tion......~ Catalytic Water '"~yt'~~~a'~'~ Purif i c ati o n"
Awarded Grant ............................10 N-arylamides from Aromatic ds 12 C
u ..................................
ompo n Smcial Feahm:
Catalysis RdzD at the National Laboratories13 ................ Conducted by: The Catalyst Review Stauffei s New Flue Gas Process . 15 ' Industry Rumors.......................... 16 ;.
n~ocESs Spiocial bsteraietv with Forartaixshcad Technologies Fountainhead Technologies Tallcs About Their Unique Approach to Catalytic Water P ' 'canon..
Fosssdtd iu 1983, ForasbaiaHtad T'eaiiaologies, htt (FHT7 is a rrlai~iat utrocomerirs tlu aqueous saaitaNon bias, Ray Deoktwic~. Daedor of Rtseanale & Drcelopnreat for F81. rra~y spoke ud~k The CatalystReaiuo aboutt&t ar>~s proprietmy ca~Iy~c ~x p~rio~e systaa and lroto it is diJ~r~xiiattd jrom other aaailable tedmologits. Ray also ap<rke abord du futraie potasdal for tlds fi~da~al tedoiology for water sauitatiox CR: How did Fonat:iahezd become iavolved is the development of ~alytic water pu:sfication systems?
~HT: the company started out in 1983 as a group of three ent:eprmasus exploring the use of silver as a ante tecimology Ior water pari<>mtion. Several yearn prior, studies of potable waoer systems by NASA in the Apollo program showed that ~lv~er ions were effective for drinlang water disirfedion.
But no one had looked at the role of silver in bs~al diainfectiocs, whirls led our founders to the discovery of a catalytic system.
Cst: Could yon explaia your catalyst techuoio6y?
FHT: The catalyst the syatem, which is core of the tectmology.
is what differentiates it from other water pnri~ot~
syabems on the avasket.
We employ a catalyst bed wbaceby Oxidative Catalysis silver is for Aqueous Systems deposed on a mineral subatsatp (alumina). As dissolved oxygen, which sxitssrally exists in water.
mi~E'S ODntaCt With ~ ~~A: aatdYSd the 511VQ' "~
~
catalyst bed (see , Figure i-A~ the , ~, "~;d, bond of the diatomic n~ waryst and oxygen o~ sires molecule is ruptured to erects individual oxygen atoms which then become loosely bound to the silver surface (see Figure I-B). The unique ability of silver to enter into oxidative reactiom iR due to the very weak bond it ~ f~: n" moisaesr forays with oxygen (approximatelybard tisn~r~ar 7 to 8 oxnpsn scans lcral/mol; most other transition metals bond with oxygen' at strengths of more ~,~ y than 100 lccsl jmol). These adcsry dynsmc weak bonds allow silver to readily spa. ~s usarysr transfer the loaselv esd held oxygen atom to "s amam~rnrd'widr any oxidizable~
substrate. As passing~' n'~ arome bactetis or oxyprn.
''viruses make contact with these Spiacial Ir~erviem urith Fora~tai~read Tec3mologits (GOr~ia~re~
loosely bonmd oxygen atoms (see Q~dative Catatwis for Aqaeon S~te~ teow~awdl Figure 1-C~, the bonds in the bao~ia or views are ruptured. The oxidized bsdeia fragments leave ~
the anlyst snrbae (see Fisure 1-D), ~ a prdnp wol~um V
ptovyding a fresh surface receptive "~A lfai . _ . ,_ ~ i to additto~l oxygeen. ~, ~"d ~", i ;~ ..l . _ s,~ ..,,~ ~,~.ty-_ ' In addition to the catalytic action ~ ~' ~ ~ ~~~ ~~
provided by the silver cetalvst bed.
oar sysDems are oleo designed such that both silver end copper ion are sbwlyel~sedioto the water Ian t-0: b~.f~rlt ~an~po.
dsndng op~on by a a ~ banal, wA~d~
combination of a~oaion and galvanic~ ~ a action. The silver ions so prodnad__ provide a reddwlbadeaddal activi and wilN IAa ~poad tY sulAr. AMr the aoppa ion ad as npsad ooh ~
a residual p/~r Ir dl~lp~d h C& >xaotly how eiffective is yoar techaoloay is purifying wated FAT: A nnasber of a" o"' e~cpenments have been pa~smed on the system's efli~acy.~ Most noteworthy is one study performed at the Univeesity of Arizona~'~ s,inereby a 99.96 percent reduction in E. toll (fmm an initial oonoentration of Z4 x 10' CFU/ml) was obwnred in a single pass over the analyst wherein the contact time between the water and catalyst was on the order of just a few seconas. This study, as well as others conducted is pause and at independenk labs, demonstrates that the catalyst system produces water that is pose enough to meet US. Environmental P~tedion Agenry dr3nicarg water standards (see Table 1 ).
Table 1 EPA Stu~dands for Miaeals ~c Bacber;a in Dr>akina Water EPA Mmo~aaa~m Level Fount;iabead Glalyst Pte' ae: Compaason BadetialLevel(Coliform) <1/100mL lI/100mL' meets standard 5vlver O.l,ppm 0.01- 0.035 ppm b6X below maximum Copper ~ 1.0 ppm 0.02 - 0.06 ppm 95 x below maximum 99%% of 6~ia Idled wnsin 5 seconds of ca~ct Special Itrha~ai~w with Forartai~ad Ta3rnologus (cortarared) CR: What diffeteati~s FFIT"s system f~ ~6 ~°~'at f~I': 'f tire ace a nnaibar of ws~ pms6oation ted~nofogiss ai Mme ~y ~ t~
world. Cbior~ne is tl~e mwt aorrvenoonai and most widely nssd water disarfatxion system. Omcte ga~tatoes.
elecaode iosu:ms. rev~ss osarasrs. and distil>ation errs slso wrH aaaepted methods for pa~iYi~ war Utililrs these otl~ systmu, ma ~iyst-based system is lees costly to operate. no ~'~Y ~ v'aY ~ ~PP~ . 'tee 1~~
of eonsse. is the catalyst sysemt which makes otrs psvduds s>m~e ltd e~odlve. Our catahst the a~islli of the baaena and the virsss sad. because of the sbw sdede of copper and srlva ions. it promdes reaidual:aaitatioa No other water pn:i~ott systeat cur do an ~.
We c~urently hold four U5. pates and thtae are several snare U5. and forttigst patatls pending.
Cats W6ids madceb are crest tailed forFFICI"a waterpsa~a~ea per?
FHI': Our oorrstrltants at Ardms D. I~tle have helped us idadify nasrsrotrs marltats for which this tsr~no~r is appsarpnate. 'They a>dttde: ~tiaetal wamr. pole water. o~olictg towea. and a variety of irdustzial appi~otrs.
pity prsasary market right sow is steeatiosral water. We've been is that market for the last two years. To date, soars 20.000 onus have been arta0ed is swimming pools and spas at as SO US. states.
The series potettial for this mseiret alone ~s wound fight million mots. in 1994, in this masker ak~tte.
Founvitrltead Tedmologies expavenoed approxiatatrly 700 paoent ssies gsowttt.
We heiieve our tedamlogy is ideally suited for the dsiriang water market- ~e ~
m~ Ameriaut i~ouseholds me well water and about 50 pesoetst of the gtouadwatei reserns is ~ U.S.
°s'e y polluted. In additiam. last year alone, these weee 250,000 violations of the Sate Dratl~sg Waoer Ad by mu:nopal water suppliers.
These facts reprnent a substaatisl market opportunity for our tedatdogy.
Referrrrcrs:
Ges~a. C°.. Naranjo. J., Hvaluation of Catalvtically Active Media for Miavvisl Reduction. Teclut>cal Report.
:~pnl n.1993.
~ATAL1'IIC fVata Purifier Cadge Disiniec~on F.lfmatcy. Researdt ltspo~
1t13826, Herbert V. Shtrifa inc..
Octooer 20.1993.
C=. Heisug Jr.. O~ or O~ and Ag: A New:atalyst Technology for Aqueous Phase ~arutation. Ozone Soartae and cogtr~eertng, VoL I5. p. 333.1993.
Source: : ne Cacalvrx Review EXHIBIT "B"'' Witrrrr Furs'fi~arion Technolop~
forttttsiaAs~d Ttieweolo,ios, lac.
30t v~ll~r Strect Preridlnw. AI ti~Jt TH.140tf 725~!!!0 fu 1101175~9993 nttlntlt Aeonc::
rt~tvn?.ndvo~~.can -MATERIAL SAFETY DATA SHEET
S~tion I Product Information Trade Name f~rld Synonyms:Natures , VISION~
Chemical Family: Heterogeneous Catalyst Formula: AIzOa +. Ag Chemical Names: Aluminum Oxide, Sihrer Common Names: Aiumina. Silver Metal Section 11 Hazardous InBredierlts Components in the Solid Mixture:
Component: Alumina CAS 1344-28-1 Pen~r~t: 97.9 . 98.3%
OSHA PEL: 15 mglm3 Total dust; 5 mglms Respirabie fraction TWA
ACGtH TLV: 10 mgim3 TWA
Component: Silver metal CAS 7440-22-4 Percent: 1.7 - 2.1 OSHA PEL: 0.01 mglm3 TWA
ACGIH TLV: 0.1 mg/m3 TWA
EXHIBIT "B"
Section 111 Physical Data Appearance and Odor. Dark gray granules. No odor.
Solubility in Water: Insoluble Sulk Density: .65 ~0 g / crn~
Percent Votatife (wt) (~7 1 ~0~°F: Less than 1 Section IV Fire Explosion Data Fire and Explosion Hazard: Material will not bum or explode. See Section Vt for incompatible materials.
Flash Point: Non flammable Firef~ghting Media: Dry chemical, water spray or foam. For larger fires, use water spray, fog, or foam.
Stability: Stable Conditions to Avoid: None Known Section V Health Hazard Data Health hazards may arise from aye contact, prolonged or repeated skin contact, repeated inhalation, or repeated ingestion.
Contains silver which can cause argyria, gray pigmentation of the eyes, skin, and mucous membranes if it is repeatedly inhaled or ingested. May cause eye and skin irritation. No ingredient of this product is listed by NTP; /ARC, or OSHA as a carcinogen.
Signs and symptoms of exposure: Redness and tearing of the eyes, gray pigmentation of eyes, skin, or mucous membranes.
Medical conditions aggravated by exposure: Pns-existing skin and eye condi~ons.
Asthma or lung disease.
Vortex Water Technologies s.ss.rpd 2 DWM-300 Dental Water Catalyst Section V (coot.) Health Hazard Data First Aid: In case of contact, immediately flush eyes or skin with plenty of water for at least 15 minutes. Remove contact lenses, if worn. Remove contaminated clothing and shoes. If inhaled, remove to fresh air. If not breathing, give artificial respiration. If breathing is difficult, give oxygen. If Large quantities are swallowed, call a physician immediately. Do NOT induce vomiting unless directed to do so by a physician.
Never give anything by mouth to an unconscious person.
Section VI Reactivity Data Reactivity: Stable under normal temperature and pressures in sealed containers. Hazardous polymerization will not oxur.
Incompatibility (materials to avoid): Acetylene, acetylene compounds. aziridine, bromine azide, 3-bromopropyne, carboxylic acids, ethylene oxide. ethyl hydroperoxide, ethyleneimine, iodoform, nitric acid, ozonides, peroxomonosuifuric acid, and peroxyforrnic acid.
Hazardous Decomposition Products: None Section Vli Spill or Leak Procedures l Diapoaal Spill or Leak Procedures:
Notify safety personnel of spills or teaks. Clean-up personnel need protection against inhalation of dusts or fumes. Eye protection is recommended. Vacuuming or wet methods of clean-up are preferred. Place in appropriate containers for disposal keeping airborne particles at a minimum.
Disposal:
Consult applicable local, state, or federal regulations to select method of disposal.
Recover metal components by reprocessing whenever possible.
Contains silver which is reported to be toxic to both terrestrial and aquatic organisms.
Sihrer is a CERCLA hazardous substance with a reportable quantity of 1000 Ibs.
(454 kg). Silver is a toxic chemical subject to the reporting requirements of SARA
Title 111 ~313 and 40 CFR Part 372. Contains silver, RCRA hazardous waste number D011.
Vortex Water Technologies g.sits.rpd 3 OWM-300 Dental Water Catalyst Section VIII Special Protoctfon Information Respiratory Protection: Provide a NiOSHIMSHA approved respirator in the absence of proper environment control. Contact your safety equipment supplier for proper mask type.
Ventilation: Provide general andlor local exhaust ventilation to keep exposures below the TL.V. Ventilation used must be designed to prevent spots of dust accumulation or recycling of dusts.
Protective Clothing: Wear protective clothing, including long sleeves and gloves, to prevent repeated or prolonged skin corEtact.
Eye Protection: Chemical splash goggles in compliance with OSHA
regulations are recommended.
Personal Hygiene: Avoid breathing dust. Avoid contact with eyes, skin, and clothing. Do not taste or swallow. Keep skin breaks covered. Wash thoroughly after handling.
Keep container closed.
Vortex Water Technologies DWM-300 Dental Water Catalyst *rB
Claims (8)
1. A method for destroying microorganisms and biofilm within conduits conveying water from a container to dental handpieces and water discharging implements and within any of the channels of the handpieces and the implements by oxidizing the microorganisms, said method comprising the steps of:
(a) providing a source of oxygen containing gas under a pressure greater than ambient pressure;
(b) generating ozone from the gas under pressure within a UV opaque member to produce ozone enriched gas;
(c) conveying the ozone enriched gas into the water within a container, which water is to be directed to the handpieces and implements and to pressurize the water at a pressure above ambient pressure;
(d) entraining the ozone enriched gas in the water in the container to produce ozone enriched water;
(e) further conveying the ozone enriched water through the water lines to a silver catalyst cartridge to attract the oxygen to the silver and cause the oxygen to dissociate from its normal diatomic state to bond with the silver;
(f) oxidizing the microorganisms with oxygen dissociated from the silver;
and (g) dissolving silver into the water flowing downstream to permit adherence of the silver to the water conveying surfaces of the conduits, handpieces and implements and subsequent reaction with oxygen in the water to oxidize any attendant microorganisms.
(a) providing a source of oxygen containing gas under a pressure greater than ambient pressure;
(b) generating ozone from the gas under pressure within a UV opaque member to produce ozone enriched gas;
(c) conveying the ozone enriched gas into the water within a container, which water is to be directed to the handpieces and implements and to pressurize the water at a pressure above ambient pressure;
(d) entraining the ozone enriched gas in the water in the container to produce ozone enriched water;
(e) further conveying the ozone enriched water through the water lines to a silver catalyst cartridge to attract the oxygen to the silver and cause the oxygen to dissociate from its normal diatomic state to bond with the silver;
(f) oxidizing the microorganisms with oxygen dissociated from the silver;
and (g) dissolving silver into the water flowing downstream to permit adherence of the silver to the water conveying surfaces of the conduits, handpieces and implements and subsequent reaction with oxygen in the water to oxidize any attendant microorganisms.
2. The method as set forth in Claim 1 wherein said step of generating comprises the step of urging flow of the oxygen containing gas past a source of ultraviolet radiation.
3. The method as set forth in Claim 1 including the step of enriching with oxygen the gas to be ozone enriched.
4. Apparatus for entraining ozone in a fluid to be delivered to a water manifold and associated conduits in fluid communication with dental implements to oxidize organic matter and microorganisms that may be present in the fluid, and to destroy biofilm present on the surfaces of the conduits and on the surfaces of the dental implements, said apparatus comprising in combination:
(a) an ozone generator for generating ozone comprising a source of UV
radiation, a member for housing said UV radiation source, said member being opaque to UV radiation and able to withstand above ambient atmospheric pressure;
(b) a source in fluid communication with said member for conveying an oxygen containing gas at pressure above ambient pressure into said member to accommodate ozone generation under pressure in said ozone generator;
(c) a pressurizable container of fluid to be ozonated to provide a source of ozonated fluid to the manifold, the conduits and the dental implements;
(d) a device disposed in said container and in fluid communication with said ozone generator for entraining the ozone and the gas from said ozone generator under pressure in the fluid within said container to enhance the level of ozone concentration in the fluid and to provide the source of ozonated fluid;
(e) a silver catalyst cartridge in fluid communication with said container for receiving the ozonated fluid to weakly bond oxygen radicals with the silver and result in subsequent dissociation of the oxygen radicals from the silver to oxidize organic matter and microorganisms in contact therewith and for dissolving silver into the ozonated water to permit adherence of the silver to the interior walls of the manifold, the conduits and the dental implements to react with oxygen in the water and further oxidize organic matter and microorganisms; and (f) an outlet of said silver catalyst cartridge in fluid communication with the manifold, the conduits and the dental implements to interconnect said outlet with the manifold, the conduits and the dental implements to convey the ozonated fluid and silver to the manifold, the conduits and the dental implements.
(a) an ozone generator for generating ozone comprising a source of UV
radiation, a member for housing said UV radiation source, said member being opaque to UV radiation and able to withstand above ambient atmospheric pressure;
(b) a source in fluid communication with said member for conveying an oxygen containing gas at pressure above ambient pressure into said member to accommodate ozone generation under pressure in said ozone generator;
(c) a pressurizable container of fluid to be ozonated to provide a source of ozonated fluid to the manifold, the conduits and the dental implements;
(d) a device disposed in said container and in fluid communication with said ozone generator for entraining the ozone and the gas from said ozone generator under pressure in the fluid within said container to enhance the level of ozone concentration in the fluid and to provide the source of ozonated fluid;
(e) a silver catalyst cartridge in fluid communication with said container for receiving the ozonated fluid to weakly bond oxygen radicals with the silver and result in subsequent dissociation of the oxygen radicals from the silver to oxidize organic matter and microorganisms in contact therewith and for dissolving silver into the ozonated water to permit adherence of the silver to the interior walls of the manifold, the conduits and the dental implements to react with oxygen in the water and further oxidize organic matter and microorganisms; and (f) an outlet of said silver catalyst cartridge in fluid communication with the manifold, the conduits and the dental implements to interconnect said outlet with the manifold, the conduits and the dental implements to convey the ozonated fluid and silver to the manifold, the conduits and the dental implements.
5. The apparatus as set forth in Claim 4 wherein the pressure within said member is from about 30 to about 40 psig.
6. The apparatus as set forth in Claim 4 wherein said entraining device is a sparger.
7. Apparatus for destroying microorganisms present in a source of water supplying water to a manifold attendant each dental chair of a dental office, which manifold is in fluid communication through conduits with dental implements that normally discharge water as part of their operation and for destroying biofilm on the surfaces of the manifold of the conduits interconnecting the manifold with the dental implements and on the surfaces of the dental implements, said apparatus comprising in combination:
(a) a container for having water to be delivered to the dental implements;
(b) a source of oxygen containing gas under pressure for providing oxygen containing gas under pressure to the water in said container;
(c) a sparger for introducing the oxygen containing gas into the water in said container;
(d) a conduit for conveying the oxygen containing gas from said source to said sparger;
(e) a silver catalyst cartridge in fluid communication with the water in said container through a conduit for catalyzing oxidation of organic matter and microorganisms present in the water flowing into said cartridge and for releasing silver to adhere to the interior walls of the manifold, the interconnecting conduits and the dental implements and cause oxidation of any biofilm upon such walls; and (f) a gas separator for removing from said container gas not entrained within the water in said container.
(a) a container for having water to be delivered to the dental implements;
(b) a source of oxygen containing gas under pressure for providing oxygen containing gas under pressure to the water in said container;
(c) a sparger for introducing the oxygen containing gas into the water in said container;
(d) a conduit for conveying the oxygen containing gas from said source to said sparger;
(e) a silver catalyst cartridge in fluid communication with the water in said container through a conduit for catalyzing oxidation of organic matter and microorganisms present in the water flowing into said cartridge and for releasing silver to adhere to the interior walls of the manifold, the interconnecting conduits and the dental implements and cause oxidation of any biofilm upon such walls; and (f) a gas separator for removing from said container gas not entrained within the water in said container.
8. Apparatus for destroying microorganisms present in water channeled to dental handpieces and implements and for destroying biofilm attendant the handpieces and implements and the conduits extending upstream from the handpieces and implements, said apparatus comprising in combination:
(a) a source of water disposed in a container;
(b) a source of oxygen containing gas under pressure;
(c) a regulator for maintaining the gas at a pressure above ambient pressure;
(d) a pipe for conveying the oxygen containing gas from said source to a sparger disposed within the water in said container to entrain the oxygen containing gas in the water;
(e) a silver catalyst cartridge in fluid communication with said container for receiving the oxygen containing gas entrained water and for catalyzing oxidation of microorganisms coming in contact with oxygen radicals bonded to silver in said cartridge during flow through said cartridge and for releasing silver; and (f) a conduit for conveying the oxygen containing gas entrained water from said cartridge to the dental handpieces and implements and to deposit silver released from said cartridge on the interior surfaces of the conduits and of the dental handpieces and implements and destroy by oxidization any biofilm present on the interior surfaces of the conduits and the dental handpieces and implements.
(a) a source of water disposed in a container;
(b) a source of oxygen containing gas under pressure;
(c) a regulator for maintaining the gas at a pressure above ambient pressure;
(d) a pipe for conveying the oxygen containing gas from said source to a sparger disposed within the water in said container to entrain the oxygen containing gas in the water;
(e) a silver catalyst cartridge in fluid communication with said container for receiving the oxygen containing gas entrained water and for catalyzing oxidation of microorganisms coming in contact with oxygen radicals bonded to silver in said cartridge during flow through said cartridge and for releasing silver; and (f) a conduit for conveying the oxygen containing gas entrained water from said cartridge to the dental handpieces and implements and to deposit silver released from said cartridge on the interior surfaces of the conduits and of the dental handpieces and implements and destroy by oxidization any biofilm present on the interior surfaces of the conduits and the dental handpieces and implements.
Applications Claiming Priority (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US8954198P | 1998-06-17 | 1998-06-17 | |
US60/089,541 | 1998-06-17 | ||
PCT/US1999/013591 WO1999065533A1 (en) | 1998-06-17 | 1999-06-16 | Catalytic dental water apparatus |
Publications (1)
Publication Number | Publication Date |
---|---|
CA2298496A1 true CA2298496A1 (en) | 1999-12-23 |
Family
ID=22218226
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CA002298496A Abandoned CA2298496A1 (en) | 1998-06-17 | 1999-06-16 | Catalytic dental water apparatus |
Country Status (3)
Country | Link |
---|---|
AU (1) | AU4571799A (en) |
CA (1) | CA2298496A1 (en) |
WO (1) | WO1999065533A1 (en) |
Families Citing this family (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US6464868B1 (en) * | 1999-09-14 | 2002-10-15 | Amos Korin | Method and system for controlling biofilm |
WO2002081378A1 (en) * | 2001-04-09 | 2002-10-17 | Downs Bradley J | Structure and process for continuously treating dental unit water |
US7794608B2 (en) | 2006-06-30 | 2010-09-14 | Zuvo Water, Llc | Apparatus and method for treating water with ozone |
US7818822B2 (en) | 2006-07-13 | 2010-10-26 | Zuvo Water, Llc | Toilet tank water purifier |
US11046602B2 (en) | 2015-09-17 | 2021-06-29 | Charles E. C. Harris | Fluid purification apparatus and method |
WO2017175028A1 (en) * | 2016-04-04 | 2017-10-12 | PHILIPPI, Eduardo Frederico Borsarini | System and method for deodorization, sterilization, and increase resistance to maturation in food |
Family Cites Families (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4422450A (en) * | 1982-07-28 | 1983-12-27 | Panlmatic Company | Actinic ozone periodontal irrigating apparatus and method |
US5352369A (en) * | 1993-04-01 | 1994-10-04 | Fountainhead Technologies, Inc. | Method of treating water |
US5709799A (en) * | 1996-06-03 | 1998-01-20 | Vortex Corporation | Super ozonating water purifier |
US5935431A (en) * | 1997-01-15 | 1999-08-10 | Korin; Amos | Ultraviolet ozone water purifier for water disinfection |
-
1999
- 1999-06-16 AU AU45717/99A patent/AU4571799A/en not_active Abandoned
- 1999-06-16 WO PCT/US1999/013591 patent/WO1999065533A1/en active Application Filing
- 1999-06-16 CA CA002298496A patent/CA2298496A1/en not_active Abandoned
Also Published As
Publication number | Publication date |
---|---|
WO1999065533A1 (en) | 1999-12-23 |
AU4571799A (en) | 2000-01-05 |
WO1999065533A9 (en) | 2000-10-19 |
WO1999065533B1 (en) | 2000-03-02 |
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