WO2007085262A1 - System for removal of airborne contaminants - Google Patents
System for removal of airborne contaminants Download PDFInfo
- Publication number
- WO2007085262A1 WO2007085262A1 PCT/DK2007/000038 DK2007000038W WO2007085262A1 WO 2007085262 A1 WO2007085262 A1 WO 2007085262A1 DK 2007000038 W DK2007000038 W DK 2007000038W WO 2007085262 A1 WO2007085262 A1 WO 2007085262A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- ozone
- chamber
- ultraviolet light
- air
- oblong
- Prior art date
Links
- 239000000356 contaminant Substances 0.000 title claims abstract description 20
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 claims abstract description 107
- 238000004519 manufacturing process Methods 0.000 claims abstract description 57
- 230000005855 radiation Effects 0.000 claims abstract description 31
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims abstract description 21
- 238000006243 chemical reaction Methods 0.000 claims abstract description 20
- 239000001301 oxygen Substances 0.000 claims abstract description 19
- 229910052760 oxygen Inorganic materials 0.000 claims abstract description 19
- 244000144972 livestock Species 0.000 claims abstract description 15
- 239000003344 environmental pollutant Substances 0.000 claims abstract description 10
- 239000002245 particle Substances 0.000 claims abstract description 10
- 231100000719 pollutant Toxicity 0.000 claims abstract description 10
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 47
- 239000002253 acid Substances 0.000 claims description 24
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 23
- 239000010453 quartz Substances 0.000 claims description 21
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 21
- 230000002070 germicidal effect Effects 0.000 claims description 18
- 238000010517 secondary reaction Methods 0.000 claims description 15
- 229910021529 ammonia Inorganic materials 0.000 claims description 11
- 238000001228 spectrum Methods 0.000 claims description 11
- 238000005406 washing Methods 0.000 claims description 11
- 230000009467 reduction Effects 0.000 claims description 10
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 7
- 239000001117 sulphuric acid Substances 0.000 claims description 7
- 235000011149 sulphuric acid Nutrition 0.000 claims description 7
- 238000005507 spraying Methods 0.000 claims description 6
- 230000009471 action Effects 0.000 claims description 5
- 238000011010 flushing procedure Methods 0.000 claims description 4
- 230000035515 penetration Effects 0.000 claims description 4
- 238000002211 ultraviolet spectrum Methods 0.000 claims description 4
- 238000001035 drying Methods 0.000 claims description 2
- 230000001404 mediated effect Effects 0.000 claims description 2
- 239000000428 dust Substances 0.000 abstract description 13
- 238000000034 method Methods 0.000 abstract description 11
- 241000894006 Bacteria Species 0.000 abstract description 9
- 241000238631 Hexapoda Species 0.000 abstract description 8
- 239000007789 gas Substances 0.000 abstract description 8
- 241000700605 Viruses Species 0.000 abstract description 7
- 239000002341 toxic gas Substances 0.000 abstract description 3
- 238000009825 accumulation Methods 0.000 abstract description 2
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 abstract description 2
- 230000001473 noxious effect Effects 0.000 abstract description 2
- 239000007788 liquid Substances 0.000 description 10
- 230000000694 effects Effects 0.000 description 7
- 238000004659 sterilization and disinfection Methods 0.000 description 6
- 241000239290 Araneae Species 0.000 description 5
- 241000238421 Arthropoda Species 0.000 description 5
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 5
- 241000255925 Diptera Species 0.000 description 4
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 4
- 230000015572 biosynthetic process Effects 0.000 description 4
- 238000004140 cleaning Methods 0.000 description 4
- 150000001875 compounds Chemical class 0.000 description 4
- 238000001816 cooling Methods 0.000 description 4
- 238000000354 decomposition reaction Methods 0.000 description 4
- 239000012530 fluid Substances 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 3
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 3
- 241001465754 Metazoa Species 0.000 description 3
- 244000052616 bacterial pathogen Species 0.000 description 3
- 230000008901 benefit Effects 0.000 description 3
- 230000002538 fungal effect Effects 0.000 description 3
- 238000009776 industrial production Methods 0.000 description 3
- 230000008569 process Effects 0.000 description 3
- 238000000746 purification Methods 0.000 description 3
- 230000001603 reducing effect Effects 0.000 description 3
- 230000000087 stabilizing effect Effects 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- 150000003863 ammonium salts Chemical class 0.000 description 2
- 150000007514 bases Chemical class 0.000 description 2
- 230000005540 biological transmission Effects 0.000 description 2
- 230000001877 deodorizing effect Effects 0.000 description 2
- 230000000249 desinfective effect Effects 0.000 description 2
- 229910001882 dioxygen Inorganic materials 0.000 description 2
- 239000003337 fertilizer Substances 0.000 description 2
- 230000036541 health Effects 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 229960002163 hydrogen peroxide Drugs 0.000 description 2
- 208000015181 infectious disease Diseases 0.000 description 2
- 230000003993 interaction Effects 0.000 description 2
- 230000014759 maintenance of location Effects 0.000 description 2
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 2
- 229910052753 mercury Inorganic materials 0.000 description 2
- 238000012544 monitoring process Methods 0.000 description 2
- 230000001590 oxidative effect Effects 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- 239000007921 spray Substances 0.000 description 2
- 231100000331 toxic Toxicity 0.000 description 2
- 230000002588 toxic effect Effects 0.000 description 2
- 241000238876 Acari Species 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical class [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 241001414989 Thysanoptera Species 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 239000004063 acid-resistant material Substances 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- 239000003242 anti bacterial agent Substances 0.000 description 1
- 229940088710 antibiotic agent Drugs 0.000 description 1
- 230000000903 blocking effect Effects 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000003054 catalyst Substances 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 230000001276 controlling effect Effects 0.000 description 1
- 238000012864 cross contamination Methods 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 230000001419 dependent effect Effects 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 230000009977 dual effect Effects 0.000 description 1
- 239000000975 dye Substances 0.000 description 1
- 230000008030 elimination Effects 0.000 description 1
- 238000003379 elimination reaction Methods 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 230000001665 lethal effect Effects 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- VUZPPFZMUPKLLV-UHFFFAOYSA-N methane;hydrate Chemical compound C.O VUZPPFZMUPKLLV-UHFFFAOYSA-N 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 229910000069 nitrogen hydride Inorganic materials 0.000 description 1
- 231100000252 nontoxic Toxicity 0.000 description 1
- 230000003000 nontoxic effect Effects 0.000 description 1
- 239000013618 particulate matter Substances 0.000 description 1
- 239000000049 pigment Substances 0.000 description 1
- 230000008092 positive effect Effects 0.000 description 1
- 239000011541 reaction mixture Substances 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 238000005201 scrubbing Methods 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 238000009281 ultraviolet germicidal irradiation Methods 0.000 description 1
- 239000012855 volatile organic compound Substances 0.000 description 1
- 238000009692 water atomization Methods 0.000 description 1
Classifications
-
- 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
- A61L9/00—Disinfection, sterilisation or deodorisation of air
- A61L9/015—Disinfection, sterilisation or deodorisation of air using gaseous or vaporous substances, e.g. ozone
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01K—ANIMAL HUSBANDRY; AVICULTURE; APICULTURE; PISCICULTURE; FISHING; REARING OR BREEDING ANIMALS, NOT OTHERWISE PROVIDED FOR; NEW BREEDS OF ANIMALS
- A01K1/00—Housing animals; Equipment therefor
- A01K1/0047—Air-conditioning, e.g. ventilation, of animal housings
-
- 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
- A61L9/00—Disinfection, sterilisation or deodorisation of air
- A61L9/14—Disinfection, sterilisation or deodorisation of air using sprayed or atomised substances including air-liquid contact processes
-
- 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
- A61L9/00—Disinfection, sterilisation or deodorisation of air
- A61L9/16—Disinfection, sterilisation or deodorisation of air using physical phenomena
- A61L9/18—Radiation
- A61L9/20—Ultraviolet radiation
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B13/00—Oxygen; Ozone; Oxides or hydroxides in general
- C01B13/10—Preparation of ozone
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F24—HEATING; RANGES; VENTILATING
- F24F—AIR-CONDITIONING; AIR-HUMIDIFICATION; VENTILATION; USE OF AIR CURRENTS FOR SCREENING
- F24F8/00—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying
- F24F8/20—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by sterilisation
- F24F8/22—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by sterilisation using UV light
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F24—HEATING; RANGES; VENTILATING
- F24F—AIR-CONDITIONING; AIR-HUMIDIFICATION; VENTILATION; USE OF AIR CURRENTS FOR SCREENING
- F24F8/00—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying
- F24F8/20—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by sterilisation
- F24F8/24—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by sterilisation using sterilising media
- F24F8/26—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by sterilisation using sterilising media using 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
- A61L2209/00—Aspects relating to disinfection, sterilisation or deodorisation of air
- A61L2209/20—Method-related aspects
- A61L2209/21—Use of chemical compounds for treating air or the like
- A61L2209/212—Use of ozone, e.g. generated by UV radiation or electrical discharge
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F24—HEATING; RANGES; VENTILATING
- F24F—AIR-CONDITIONING; AIR-HUMIDIFICATION; VENTILATION; USE OF AIR CURRENTS FOR SCREENING
- F24F8/00—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying
- F24F8/40—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by ozonisation
Definitions
- the present invention relates to a system for removal of airborne contaminants in a confined space comprising a primary reaction chamber which chamber has an inlet for contaminated air connected to the confined space, which chamber has an outlet for treated air connected to the confined space, and which chamber comprises at least one ultraviolet light tube for the generation of ozone, in which chamber air coming from the confined space is treated with a combination of UV radiation and ozone.
- Odour and dust removal equipment using ozone and whirling air stream is disclosed in KR2001069629.
- This method and apparatus relates to the production of purified or ozone enriched air to remove contaminants from objects and is accomplished by a system in which air is drawn in as a stream into the system and flows through ozone generating and germicidal chambers.
- An ozone generating ultraviolet radiation source disposed within the ozone chamber emits UV radiation having a wavelength approximately 185 nanometers to irradiate the air and generate ozone.
- the ozonated air enters a germicidal chamber including a germicidal UV radiation source (e.g., emitting radiation having a wavelength of approximately 254 nanometers) that irradiates the ozonated air to destroy contaminants and to catalyse the ozone for enhanced removal of odor causing elements from the air stream.
- a germicidal UV radiation source e.g., emitting radiation having a wavelength of approximately 254 nanometers
- An object of this invention is to remove contaminants from air within a treated space without emitting ozone or ultraviolet radiation into that treated space endangering people and/or animals. However, if the contaminants to be removed comprise particulate matter this will become sticky during ozone treatment and settle on the ultraviolet radiation source with blocking of the emitted radiation as the result. Thus, frequent cleaning of the UV source becomes necessary.
- US2004051056 and corresponding US6809326 both discloses an adjustable ozone delivery system for air disinfection comprising an UV light system for treating the air includes an UV tube lamp having a first section for transmitting UV light in a wavelength range that includes maximum ozone production and maximum germicidal ac- tivity, and a second section for transmitting UV light in a wavelength range that includes maximum germical activity while excluding the production of ozone; and a movable annualar sleeve for controlling the amount of ozone transmitted by the lamp.
- US20040140269A1 discloses an ultraviolet-and-ozone disinfection apparatus provid- ing an improvement on disinfection, which includes a disinfection tank, a mercury UV lamp enclosed by a quartz tube for generating UV light with air trapped between them undergoing UV irradiation to generate ozone, an ozone transmitting tube, a spiral water, transmitting tube wrapping around the quartz tube in a spiral manner to achieve sufficient disinfection by mixing ozone in water, a sleeve barrel enclosing the spiral tube.
- water is exposed to UV radiation to achieve sufficient disinfection and reduce excessive ozone that is harmful to human health.
- EP 1362828 Al and JP 04247294 concerns an ultraviolet lamp used for creating ozone.
- An ultraviolet lamp is enclosed by a container having an inlet at one end and an outlet at the other end.
- An air flow containing molecular oxygen is created between the container and the ultraviolet lamp.
- a portion of the wavelength of the ultraviolet lamp is used for generating ozone.
- Another portion of the wavelength of the ultraviolet lamp is used to kill micro organisms or disinfect a fluid.
- the ozone generated may be released in the fluid, further purifying and deodorizing the fluid.
- the present invention combines the germicidal properties of a ultraviolet lamp with the deodorizing proper- ' ties of ozone in a single device which may be used to purify water or other fluid.
- US4230571 concerns a method and apparatus for the purification of water with ozone and ultraviolet radiation.
- Oxygen-containing gas such as air
- an ultraviolet radiation source such as a mercury vapour lamp.
- the absorption of ultraviolet radiation by oxygen produces ozone which is entrained in the flowing gas.
- the gas is next mixed with the contaminated water and the mixture of water and ozone is then directed past the same ultraviolet source in a path isolated from the confined path of gas alone.
- the ozone in the water acts directly to kill bacteria and viruses and to oxidize undesirable compounds in the water.
- the ultraviolet radiation also acts directly to kill bacteria and viruses in the water. Additionally the ultraviolet radiation acts as a catalyst for the disinfecting and oxidizing action of the ozone, so that water purification occurs much faster than would occur if the ozone were acting alone.
- US4141830 describes an apparatus for purifying liquid such as water, in which an ul- traviolet light source irradiates air passing through a first chamber surrounding the source, and then irradiates the liquid passing through the second chamber surrounding the first chamber.
- the air from the first chamber is ozonated by the U. V. light, and this air is bubbled into the water in the second chamber to maximize the purification through simultaneous ultraviolet and ozone exposure.
- WO04011127Al relates to a method of purifying air, a process for manufacture of fertilizer and an apparatus for purifying air by scrubbing with an acid.
- the apparatus for purifying air contains washing liquid and comprises: at least one air cleaning unit comprising a scrubber in which the air to be purified is washed with the acid containing washing liquid, and from which the purified air and the spent washing liquid is withdrawn; and a washing liquid control unit, arranged in a distance from the air cleaning unit(s), in which the composition of the spent washing liquid withdrawn from the scrubber is readjusted, if desired, by addition of fresh water and fresh acid and withdrawal of a corresponding amount of the spent washing liquid as a product, such as a fertilizer mixture, before the optionally readjusted washing liquid is transferred to and introduced into the scrubber as acid containing washing liquid.
- the invention relates to a building provided with an apparatus for purifying air
- a further object of the invention is to provide a integrated system for the total removal of germs including bacteria, viruses, and fungal spores and flying arthropods present in confined spaces such as livestock production buildings, industrial production buildings, offices, hospitals, schools, etc.
- a further object of the invention is to overcome the problem of dust accumulation on the ultraviolet light emitting lamp and production of nitrogen containing toxic gases.
- the ultraviolet light tube is enclosed in an oblong ozone production chamber, which oblong ozone production chamber can be formed in a quartz tube, which oblong production chamber in one end has a further inlet for an oxygen containing air stream coming exclusively from outside the confined space, which oblong production chamber has an outlet positioned in the opposite end and inside the primary reaction chamber, where the ozone containing air stream can be mixed with contaminated air from the inlet to form a combined air stream, which combined air stream is streaming in reversed direction outside the oblong production chamber, where the combined air stream is subjected to ultraviolet light transmitted through the wall of the oblong production chamber, where said ultraviolet light having its wavelength spectrum restricted to the germicidal range and through the action of ozone.
- the method is useful in a system for odour removal where it may be combined with feed-back control.
- the invention further relates to an ozone production unit useful in the method of the invention.
- the present system has the advantage of being an integrated system for the total removal of germs including bacteria, viruses, and fungal spores and flying insects, such as flies and mosquitoes, and other small arthropods including spiders and mites present in confined spaces such as livestock production buildings, industrial production buildings, offices, hospitals, schools, etc.
- the invention further relates to a system as described above wherein the chamber comprises at least one nozzle for spraying water into said chamber for the capture and washing out of airborne particles and gaseous ammonia, and flushing of the outer wall of the oblong production chamber, and where the system is further fitted with a drain outlet for water containing trapped pollutants.
- the spray water is cold water having a temperature in the range of about 8 to 10 °. This will ensure that the spray water may act as a cooling means in addition to acting as a flushing means for the quartz tube and a trapping means for dust particles.
- said sprayed water further contains a diluted acid, such as diluted sulphuric acid.
- a diluted acid such as diluted sulphuric acid.
- An acid such as sulphuric acid, which forms water soluble salts with basic com- pounds is preferred.
- the system of the invention has the further advantage of being an integrated system for removal of the full range of air borne contaminants from the air in the above mentioned confined spaces, e.g. closed livestock production units and industrial production buildings where dust and option- ally also gaseous ammonia are present as air contaminants.
- a typical level of ammonia in contaminated air inside a livestock stable may range from about 10 to 40 ppm and up to about 200 ppm.
- a full range of air borne contaminants inckide organic vapours such as volatile odourous compounds, toxic gases such as hydrogen sulphide and other sulphureous compounds, gaseous ammonia and the like; air borne bacteria, viruses and fungal spores; organic and inorganic dust particles, flying arthropods including flies, thrips, mosquitoes and spiders.
- the present invention relates in another aspect to a system as described above which further comprises a secondary reaction chamber for further ozone mediated reduction of airborne contaminants having a final outlet to the confined space, and where the concentration of ozone in the outlet stream is less than about 0.1 - 0.2 ppm, and a secondary reaction zone where further contaminant reduction takes place and where the ozone concentration is reduced to less than about 0.05 - 0.08 ppm when measured in about 1 meter's distance from the outlet.
- said sec- ondary reaction chamber is conveniently made up of appropriate piping that leads the discharged cleaned air from the system back into the confined space.
- An ozone concentration higher than about 0.05 ppm for further odour and germ reduction can safely be allowed inside said secondary reaction chamber.
- the secondary reaction zone con- stitutes the space op to about a distance of about 1 meter from the final outlet where still further contaminant reduction may take place until the discharged treated air has an ozone concentration at the level of about 0.05 ppm considered safe for humans.
- the only slightly elevated ozone concentrations of said secondary reation zone may contribute to reduction or elimination of arthropods in the confined space.
- the invention relates to a system as described above, wherein the radiation emitted from the ultraviolet light tube covers the ultraviolet spectrum from about 280 nm to about 100 nm with at least one spectrum peak in the ozone forming range, preferably at about 184.9 nm and with at least one spectrum peak in the germi- cidal range, preferably at about 253,7 nm.
- the radiation emitted from the ultraviolet light tube covers the ultraviolet spectrum from about 280 nm to about 100 nm with at least one spectrum peak in the ozone forming range, preferably at about 184.9 nm and with at least one spectrum peak in the germi- cidal range, preferably at about 253,7 nm.
- the ultraviolet light tube is mounted inside a protecting tube, hi this way the ozone production chamber is separated from the primary reaction chamber where a higher relative humidity would diminish ozone production.
- the protecting tube is preferably a quartz tube that reflects the ozone forming short wave UV radiation for increasing the radation inside the tube, which leads to an increase in the formation of ozone.
- the quartz tube will permit transmission of the germicidal range UV radiation, thus enabling the full effect of the various peak UV wavelengths generated by the ultraviolet light tube to be utilised in the treatment of contaminated air.
- the invention relates in a further aspect to an ozone production chamber preferably for use in a system according to any one of the preceding claims comprising a tubular quartz cylinder enclosing at least one ultraviolet light tube capable of emitting radia- tion in the ultraviolet spectrum from about 280 nm to about 100 nm with at least one spectrum peak in the ozone forming range, preferably at about 184.9 nm and with at least one spectrum peak in the germicidal range, preferably at about 253,7 nm and where the quartz cylinder permits penetration of radiation having its wavelength peak in the germicidal range but does not permit penetration of radiation having its wavelength peak in the ozone forming range.
- the ozone production chamber is preferably an elongated unit wherein the light tube is firmly fitted and wherein the inlet (22) is integrated and connected to conducting means to secure the exclusive intake of oxygen containing air from outside the chamber.
- the system of the invention utilises inlet air from the outside which has been subjected to a drying process to obtain a relative humidity of less than about 35% in order to minimise unwanted production of hydrogenperoxide in the production chamber.
- the system of the invention is especially useful when the confined space is a livestock stable.
- Fig. 1 is a longitudinal section drawing of one possible embodiment of the invention showing the various components and air streams.
- Fig. 2 shows a longitudinal section drawing of an embodiment of the production chamber (14) and its position in the system of the invention.
- Fig. 1 shows a possible embodiment of a system 2 according to the invention.
- the system is operating inside a confined space 4, where the system 2 comprises a primary action chamber 6, where the reaction chamber 6 has an inlet 8 for contaminated air coming from the confined space 4.
- the system 2 furthermore has an outlet 10 also connected to the confined space 4.
- the chamber 6 comprises an ultraviolet light tube 12 placed inside an oblong ozone production chamber 14.
- the production chamber 14 has in one end 16 an inlet 18 which inlet 18 is supplied by an oxygen containing air stream 20.
- the production chamber 14 has an outlet 22 placed in the opposite end 24 also placed inside the reaction chamber 6.
- ozone containing air stream 26 is generated, which ozone containing air stream 26 is mixed in the primary reaction chamber 6 by contaminated air from the inlet 8 for forming a combined air stream 28.
- the combined air stream 28 flows in reverse direction upwards outside the production chamber 14.
- fig. 1 shows nozzles 30 for spraying water or water containing acids inside the chamber 6.
- a drain outlet 34 is shown for draining the chamber 6.
- a secondary reaction chamber 32 is connected to the chamber 6 where the outlet 10 is connected to the secondary reaction chamber 32.
- a system as shown in fig. 1 is producing ozone-containing air inside the tube 14.
- ozone containing air 26 is mixed with the incoming contaminated air and a combined air stream 28 is formed.
- This air stream 28 is radiated with ultraviolet light so that the air stream 28 is treated both with ozone and ultraviolet light as it is streaming upwards.
- the nozzles 30 are spraying water or water which contains e.g. diluted sulphuric acid into the chamber 6 for letting the acid react with the contents of ammonia.
- a further positive effect by using the drain nozzles 30 inside the chamber 6 is that the tube 14 on its outside will be continuously washed so that any deposition of dust or other contamination outside the tube 14 will be removed.
- Fig. 2 shows a longitudinal section of a system of a second possible embodiment of the primary production chamber 14 and its position in the system 2.
- Fig. 2 shows a system 2, which system could be placed inside a confined space 4 but it could also be placed somewhere else where contaminated air has to be cleaned.
- Fig. 2 shows a reaction chamber 6 which reaction chamber 6 has an inlet 8 and an outlet 10.
- An ultravio- let light tube 12 is shown inside an oblong ozone production chamber 14 which preferably is formed as a quartz tube, the oblong production chamber 14 having in one end 16 an inlet 18 for oxygen containing air stream 20.
- the oblong production chamber 14 has an outlet 22 positioned in the opposite end 24 inside the primary reaction chamber 6.
- the ozone containing air stream 26 is mixed inside the chambers with contaminated air coming from the inlet 8 and forming a combined air stream 28.
- a nozzle 30 for spraying water or water containing diluted sulphuric acid is placed inside the chamber 6 for spraying water or water containing acid for forming a fog which can react with the chemical contents in the chamber 6 and also for cleaning the outside of the oblong production chamber 14 which at the same time is sprayed at the outside.
- a drain outlet 34 is shown for draining the water or the water containing acid into an outlet.
- a secondary reaction chamber 32 is shown, to which a tube 36 is connected. Also a ventilator 38 is shown. The ventilator 38 pulls contaminated air 26 through the inlet 8 and through the reaction chamber 6, from where the ventilator pulls the air into the secondary reaction chamber 32 and further through the outlet 10 into piping 36.
- the secondary reaction chamber 32 has the effect that an ozone reaction continuous so that the content of ozone is reduced to near a safety level before the air stream leaves the outlet 10.
- the oxygen containing air stream is cooled to a temperature well below about 40 0 C in order to prevent the quartz tube from heating to a temperature above 40 °C which could result in reduced ozone production. Further it is preferred that the humidity of the oxygen containing air stream is reduced, hi a second possible embodiment of the invention cooling means are used for both reducing the content of humidity and for cooling the oxygen containing air stream.
- Ozone is a toxic and powerful oxidizing gas having a strong disinfecting and odour reducing effect.
- ozone can be produced from oxygen containing gas or air, such as atmospheric air, at the desired site of action, and it decomposes naturally within relatively short time to molecular oxygen leaving non-toxic residual products, depending on temperature, relative humidity, pH and presence of other organic or inorganic matter.
- Ozone is useful for reduction of air borne pollutants, hi the present invention ozone is produced when an oxygen containing air stream, such as an uncon- taminated atmospheric air stream, is brought into contact with ultraviolet light.
- the oxygen containing air stream has a relative humidity of less than about 35 %.
- the oxygen containing air is preferably generated from compressed air using a conventional oxygen generator with means for nitrogen removal and cooling means. In this way the oxygen content of the air stream may be elevated in comparison to normal atmospheric air. It is preferred to use clean air with a low content of particles because these will become ionized through contact with ozone and settle on the light tube resulting in loss of effect.
- NO x atmospheric air nitrogen oxides
- Ozone interaction with water and acid hi the present system water and diluted acid, preferably diluted sulphuric acid, is sprayed directly into the chamber (6) through the nozzle (30) for the capture and washing out of airborne particles and gaseous ammonia. Dust particles, insects and organic molecules tend to stick to an ultraviolet light source during decomposition. Therefore it is preferred, that the outer wall of the oblong ozone production chamber (14) housing the ultraviolet light tube is continually flushed with the sprayed water and diluted acid. Decomposing ozone in the primary reaction chamber (6) generates atomic oxygen that reacts with water droplets or water vapour from the nozzle (30) to form hy- droxyl radicals which contributes to pollutant reduction.
- the diluted acid sprayed into the chamber (6) will react with gaseous ammonia to produce water soluble ammonium salts.
- the system is fitted with a drain outlet (32) for condensed water from chamber (6), and the water containing trapped pollutants, including odour substances, bacteria, dust, and possibly small insects and spiders and ammonium salts, may be removed through piping to a slurry tank. Due to the use of ozone and sprayed diluted acid, the reaction chamber (6) and its components are made of non-corroding and acid resistant materials.
- ultraviolet light in the wavelength range of about 100 nm to about 200 nm In addition to the ozone generating effect of ultraviolet light in the wavelength range of about 100 nm to about 200 nm, ultraviolet light in the wavelength range from about 200 nm to about 280 nm, and preferably with a spectrum peak at approximately 254 nm, has a general germicidal effect including lethal effect on insects and spiders.
- the production chamber (14) comprises at least one ultraviolet light source (12) capable of emitting radiation in both the ozone generating range and in the germicidal range inside a hollow quartz tube, where said tube permits clean atmospheric air to enter through the inlet (18) and become ozonized through the action of ozone forming ultraviolet radiation, and after exiting the production chamber (14) through the outlet (22) to be mixed with contaminated air and sprayed water and diluted acid inside the reaction chamber (6), and where said quartz tube further permits transmission of the germicidal range only of the ultraviolet radia- tion generated from the light tube (12).
- the mixture of contaminated air, ozone, sprayed water and sprayed diluted acid comprises a primary reaction mixture where in addition germicidal ultraviolet radiation transmitted through the quartz tube contributes to desinfection.
- the atmospheric air stream following the exit from the passage between ultraviolet light tube (12) and quartz tube (14) is reversed and mixed with contaminated air under simultaneous supply of sprayed water droplets containing diluted acid and then subjected to a passage along the outside of the quartz tube where it is irradiated with ultraviolet light of. 253,7 nm (UV-C) resulting in the formation of atomic oxygen and hydroxyl radicals.
- UV-C ultraviolet light of. 253,7 nm
- This formation takes place with decomposition of a part of the previously formed ozone resulting in a particularly reactive environment.
- the presence of water and acid, preferably sulphuric acid will have the effect that a part of the air borne dust particles are washed out while at the same time flushing the quartz tube and prevent it from becoming clogged.
- the decomposition of pollutants started in the primary reaction chamber will continue when the air stream exits through outlet (10) during the passage through convenient piping to a final discharge to the confined space.
- the air desinfecting and pollutant reducing effect of the system of the invention is dependent on dosage of ultraviolet light and acid as well as air retention time in the system, e.g. retention time in the production chamber (14), the primary reaction chamber (6) and the discharge piping.
- the ultraviolet dosage can be regulated through con- trol of the number of ultraviolet light tubes in operation and through interaction between the percentage of clean air and recirculated contaminated air from the confined space.
- the treatment time is controlled through the size of the secondary reaction chambers, e.g. the discharge piping.
- a feed-back system comprising an electronic nose capable of detecting critical ozone levels and having proper monitoring equipment that can shut down full or partly the ozone generation until the concentration in the stable has returned to acceptable levels.
- concentration of gaseous ammonia may be monitored to regulate the amount of sprayed diluted acid.
- the system is useful in all types of closed livestock stables where the density of production animals leads to air borne pollution resulting in elevated risk of diseases and decreased production economy.
- the advantages of using the system of the invention include reduced pressure of infection from air borne germs and cross contamination reduced pressure of infection from the external environment reduced amount of insects, spiders and other arthropods in the confined space • reduced use of antibiotics increased fodder utilisation and growth rate recirculation of a greater proportion of the total air volume is possible • reduced costs of heating during the winter season economic gain for the farmer reduced odour discharge to the environment
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Abstract
The present invention relates to a system for removal of airborne contaminants in a confined space comprising a primary reaction chamber which chamber comprises at least one ultraviolet light tube for the generation of ozone, in which chamber air coming from the confined space is treated with a combination of UV radiation and ozone. It is an object of the invention to provide a system for removal of airborne pollutants in confined spaces, such as a livestock stable. A further object of the invention is to overcome the problem of dust accumulation on the ultraviolet light emitting lamp and production of nitrogen containing toxic gases. This can be achieved if the ultraviolet light tube is enclosed in an oblong ozone production chamber, which oblong production chamber in one end has a further inlet for an oxygen containing air stream coming exclusively from outside the confined space, where the ozone containing air stream can be mixed with contaminated air from the inlet to form a combined air stream, where the combined air stream is subjected to ultraviolet light transmitted through the wall of the oblong production chamber. Hereby is achieved an effective system for the removal of airborne contaminants including bacteria, virus, insects, malodour, dust particles, and noxious gases such as NH3 and H2S in production buildings such as livestock tables or barns. The method is useful in a system for odour removal where it maybe combined with feed-back control.
Description
SYSTEM FOR REMOVAL OF AIRBORNE CONTAMINANTS
The present invention relates to a system for removal of airborne contaminants in a confined space comprising a primary reaction chamber which chamber has an inlet for contaminated air connected to the confined space, which chamber has an outlet for treated air connected to the confined space, and which chamber comprises at least one ultraviolet light tube for the generation of ozone, in which chamber air coming from the confined space is treated with a combination of UV radiation and ozone.
FIELD OF THE INVENTION
It is generally recognised that airborne pollutants, such as ammonia, bacteria and dust as well as insects and volatile organic compounds having an unpleasant odour inside livestock stables alone and in combination may have a considerable negative impact on the health of production animals and farm workers leading to reduced economy in the livestock production.
A wide range of solutions to these problems has been described including ozone injection to livestock buildings disclosed in US Patent No. 5983834.
Utilisation of ozone and water atomisation to control odour is disclosed in US Patent No. 6076748.
Odour and dust removal equipment using ozone and whirling air stream is disclosed in KR2001069629.
A method and apparatus for producing purified or ozone enriched air to remove contaminants from objects disclosed in WO 00/06209. This method and apparatus relates to the production of purified or ozone enriched air to remove contaminants from objects and is accomplished by a system in which air is drawn in as a stream into the system and flows through ozone generating and germicidal chambers. An ozone generating ultraviolet radiation source disposed within the ozone chamber emits UV radiation having a wavelength approximately 185 nanometers to irradiate the air and generate ozone. The ozonated air enters a germicidal chamber including a germicidal
UV radiation source (e.g., emitting radiation having a wavelength of approximately 254 nanometers) that irradiates the ozonated air to destroy contaminants and to catalyse the ozone for enhanced removal of odor causing elements from the air stream. An object of this invention is to remove contaminants from air within a treated space without emitting ozone or ultraviolet radiation into that treated space endangering people and/or animals. However, if the contaminants to be removed comprise particulate matter this will become sticky during ozone treatment and settle on the ultraviolet radiation source with blocking of the emitted radiation as the result. Thus, frequent cleaning of the UV source becomes necessary.
US2004051056 and corresponding US6809326 both discloses an adjustable ozone delivery system for air disinfection comprising an UV light system for treating the air includes an UV tube lamp having a first section for transmitting UV light in a wavelength range that includes maximum ozone production and maximum germicidal ac- tivity, and a second section for transmitting UV light in a wavelength range that includes maximum germical activity while excluding the production of ozone; and a movable annualar sleeve for controlling the amount of ozone transmitted by the lamp.
US20040140269A1 discloses an ultraviolet-and-ozone disinfection apparatus provid- ing an improvement on disinfection, which includes a disinfection tank, a mercury UV lamp enclosed by a quartz tube for generating UV light with air trapped between them undergoing UV irradiation to generate ozone, an ozone transmitting tube, a spiral water, transmitting tube wrapping around the quartz tube in a spiral manner to achieve sufficient disinfection by mixing ozone in water, a sleeve barrel enclosing the spiral tube. Along the entire flow path, water is exposed to UV radiation to achieve sufficient disinfection and reduce excessive ozone that is harmful to human health.
EP 1362828 Al and JP 04247294 concerns an ultraviolet lamp used for creating ozone. An ultraviolet lamp is enclosed by a container having an inlet at one end and an outlet at the other end. An air flow containing molecular oxygen is created between the container and the ultraviolet lamp. A portion of the wavelength of the ultraviolet lamp is used for generating ozone. Another portion of the wavelength of the ultraviolet lamp is used to kill micro organisms or disinfect a fluid. The ozone generated may be
released in the fluid, further purifying and deodorizing the fluid. The present invention combines the germicidal properties of a ultraviolet lamp with the deodorizing proper- ' ties of ozone in a single device which may be used to purify water or other fluid.
US4230571 concerns a method and apparatus for the purification of water with ozone and ultraviolet radiation. Oxygen-containing gas, such as air, is directed to flow in a confined path past an ultraviolet radiation source, such as a mercury vapour lamp. The absorption of ultraviolet radiation by oxygen produces ozone which is entrained in the flowing gas. The gas is next mixed with the contaminated water and the mixture of water and ozone is then directed past the same ultraviolet source in a path isolated from the confined path of gas alone. The ozone in the water acts directly to kill bacteria and viruses and to oxidize undesirable compounds in the water. The ultraviolet radiation also acts directly to kill bacteria and viruses in the water. Additionally the ultraviolet radiation acts as a catalyst for the disinfecting and oxidizing action of the ozone, so that water purification occurs much faster than would occur if the ozone were acting alone.
US4141830 describes an apparatus for purifying liquid such as water, in which an ul- traviolet light source irradiates air passing through a first chamber surrounding the source, and then irradiates the liquid passing through the second chamber surrounding the first chamber. The air from the first chamber is ozonated by the U. V. light, and this air is bubbled into the water in the second chamber to maximize the purification through simultaneous ultraviolet and ozone exposure.
WO04011127Al relates to a method of purifying air, a process for manufacture of fertilizer and an apparatus for purifying air by scrubbing with an acid. The apparatus for purifying air contains washing liquid and comprises: at least one air cleaning unit comprising a scrubber in which the air to be purified is washed with the acid containing washing liquid, and from which the purified air and the spent washing liquid is withdrawn; and a washing liquid control unit, arranged in a distance from the air cleaning unit(s), in which the composition of the spent washing liquid withdrawn from the scrubber is readjusted, if desired, by addition of fresh water and fresh acid and withdrawal of a corresponding amount of the spent washing liquid as a product, such
as a fertilizer mixture, before the optionally readjusted washing liquid is transferred to and introduced into the scrubber as acid containing washing liquid. Furthermore the invention relates to a building provided with an apparatus for purifying air
It is an object of the invention to provide a system for removal of airborne pollutants in confined spaces, such as a livestock stable. A further object of the invention is to provide a integrated system for the total removal of germs including bacteria, viruses, and fungal spores and flying arthropods present in confined spaces such as livestock production buildings, industrial production buildings, offices, hospitals, schools, etc. A further object of the invention is to overcome the problem of dust accumulation on the ultraviolet light emitting lamp and production of nitrogen containing toxic gases. This can be achieved if the ultraviolet light tube is enclosed in an oblong ozone production chamber, which oblong ozone production chamber can be formed in a quartz tube, which oblong production chamber in one end has a further inlet for an oxygen containing air stream coming exclusively from outside the confined space, which oblong production chamber has an outlet positioned in the opposite end and inside the primary reaction chamber, where the ozone containing air stream can be mixed with contaminated air from the inlet to form a combined air stream, which combined air stream is streaming in reversed direction outside the oblong production chamber, where the combined air stream is subjected to ultraviolet light transmitted through the wall of the oblong production chamber, where said ultraviolet light having its wavelength spectrum restricted to the germicidal range and through the action of ozone.
Hereby is achieved an effective system for the removal of airborne contaminants in- eluding bacteria, virus, insects, malodour, dust particles, and noxious gases such as NH3 and H2S in production buildings such as livestock stables. or barns. The method is useful in a system for odour removal where it may be combined with feed-back control. The invention further relates to an ozone production unit useful in the method of the invention. The present system has the advantage of being an integrated system for the total removal of germs including bacteria, viruses, and fungal spores and flying insects, such as flies and mosquitoes, and other small arthropods including spiders and mites present in confined spaces such as livestock production buildings, industrial production buildings, offices, hospitals, schools, etc.
The invention further relates to a system as described above wherein the chamber comprises at least one nozzle for spraying water into said chamber for the capture and washing out of airborne particles and gaseous ammonia, and flushing of the outer wall of the oblong production chamber, and where the system is further fitted with a drain outlet for water containing trapped pollutants. It is preferred that the spray water is cold water having a temperature in the range of about 8 to 10 °. This will ensure that the spray water may act as a cooling means in addition to acting as a flushing means for the quartz tube and a trapping means for dust particles.
It is preferred that in the system of the invention said sprayed water further contains a diluted acid, such as diluted sulphuric acid. The presence of acid in the sprayed water enables basic compounds such as ammonia to be bound due to salt formation with the acid. An acid, such as sulphuric acid, which forms water soluble salts with basic com- pounds is preferred. In this preferred embodiment the system of the invention has the further advantage of being an integrated system for removal of the full range of air borne contaminants from the air in the above mentioned confined spaces, e.g. closed livestock production units and industrial production buildings where dust and option- ally also gaseous ammonia are present as air contaminants. A typical level of ammonia in contaminated air inside a livestock stable may range from about 10 to 40 ppm and up to about 200 ppm. In the context of the present invention a full range of air borne contaminants inckide organic vapours, such as volatile odourous compounds, toxic gases such as hydrogen sulphide and other sulphureous compounds, gaseous ammonia and the like; air borne bacteria, viruses and fungal spores; organic and inorganic dust particles, flying arthropods including flies, thrips, mosquitoes and spiders.
The present invention relates in another aspect to a system as described above which further comprises a secondary reaction chamber for further ozone mediated reduction of airborne contaminants having a final outlet to the confined space, and where the concentration of ozone in the outlet stream is less than about 0.1 - 0.2 ppm, and a secondary reaction zone where further contaminant reduction takes place and where the ozone concentration is reduced to less than about 0.05 - 0.08 ppm when measured in about 1 meter's distance from the outlet. In this embodiment of the invention said sec-
ondary reaction chamber is conveniently made up of appropriate piping that leads the discharged cleaned air from the system back into the confined space. An ozone concentration higher than about 0.05 ppm for further odour and germ reduction can safely be allowed inside said secondary reaction chamber. The secondary reaction zone con- stitutes the space op to about a distance of about 1 meter from the final outlet where still further contaminant reduction may take place until the discharged treated air has an ozone concentration at the level of about 0.05 ppm considered safe for humans. The only slightly elevated ozone concentrations of said secondary reation zone may contribute to reduction or elimination of arthropods in the confined space.
In a further aspect the invention relates to a system as described above, wherein the radiation emitted from the ultraviolet light tube covers the ultraviolet spectrum from about 280 nm to about 100 nm with at least one spectrum peak in the ozone forming range, preferably at about 184.9 nm and with at least one spectrum peak in the germi- cidal range, preferably at about 253,7 nm. These radiation ranges enables the dual purpose of ozone generation and germ reduction of the UV light tube.
The ultraviolet light tube is mounted inside a protecting tube, hi this way the ozone production chamber is separated from the primary reaction chamber where a higher relative humidity would diminish ozone production. The protecting tube is preferably a quartz tube that reflects the ozone forming short wave UV radiation for increasing the radation inside the tube, which leads to an increase in the formation of ozone. The quartz tube will permit transmission of the germicidal range UV radiation, thus enabling the full effect of the various peak UV wavelengths generated by the ultraviolet light tube to be utilised in the treatment of contaminated air.
The invention relates in a further aspect to an ozone production chamber preferably for use in a system according to any one of the preceding claims comprising a tubular quartz cylinder enclosing at least one ultraviolet light tube capable of emitting radia- tion in the ultraviolet spectrum from about 280 nm to about 100 nm with at least one spectrum peak in the ozone forming range, preferably at about 184.9 nm and with at least one spectrum peak in the germicidal range, preferably at about 253,7 nm and where the quartz cylinder permits penetration of radiation having its wavelength peak
in the germicidal range but does not permit penetration of radiation having its wavelength peak in the ozone forming range. The ozone production chamber is preferably an elongated unit wherein the light tube is firmly fitted and wherein the inlet (22) is integrated and connected to conducting means to secure the exclusive intake of oxygen containing air from outside the chamber.
During cold and humid seasons it is preferred that the system of the invention utilises inlet air from the outside which has been subjected to a drying process to obtain a relative humidity of less than about 35% in order to minimise unwanted production of hydrogenperoxide in the production chamber.
The system of the invention is especially useful when the confined space is a livestock stable.
DESCRIPTION OF THE DRAWINGS
Fig. 1 is a longitudinal section drawing of one possible embodiment of the invention showing the various components and air streams.
Fig. 2 shows a longitudinal section drawing of an embodiment of the production chamber (14) and its position in the system of the invention.
Detailed description of the drawings
Fig. 1 shows a possible embodiment of a system 2 according to the invention. The system is operating inside a confined space 4, where the system 2 comprises a primary action chamber 6, where the reaction chamber 6 has an inlet 8 for contaminated air coming from the confined space 4. The system 2 furthermore has an outlet 10 also connected to the confined space 4. The chamber 6 comprises an ultraviolet light tube 12 placed inside an oblong ozone production chamber 14. The production chamber 14 has in one end 16 an inlet 18 which inlet 18 is supplied by an oxygen containing air stream 20. The production chamber 14 has an outlet 22 placed in the opposite end 24 also placed inside the reaction chamber 6. Inside the production chamber 14 an ozone containing air stream 26 is generated, which ozone containing air stream 26 is mixed
in the primary reaction chamber 6 by contaminated air from the inlet 8 for forming a combined air stream 28. The combined air stream 28 flows in reverse direction upwards outside the production chamber 14. Furthermore, fig. 1 shows nozzles 30 for spraying water or water containing acids inside the chamber 6. A drain outlet 34 is shown for draining the chamber 6. A secondary reaction chamber 32 is connected to the chamber 6 where the outlet 10 is connected to the secondary reaction chamber 32.
In operation a system as shown in fig. 1 is producing ozone-containing air inside the tube 14. At the outlet 22 at the second end 24 of the quartz tube 14 ozone containing air 26 is mixed with the incoming contaminated air and a combined air stream 28 is formed. This air stream 28 is radiated with ultraviolet light so that the air stream 28 is treated both with ozone and ultraviolet light as it is streaming upwards. At the same time the nozzles 30 are spraying water or water which contains e.g. diluted sulphuric acid into the chamber 6 for letting the acid react with the contents of ammonia.
A further positive effect by using the drain nozzles 30 inside the chamber 6 is that the tube 14 on its outside will be continuously washed so that any deposition of dust or other contamination outside the tube 14 will be removed.
Fig. 2 shows a longitudinal section of a system of a second possible embodiment of the primary production chamber 14 and its position in the system 2. Fig. 2 shows a system 2, which system could be placed inside a confined space 4 but it could also be placed somewhere else where contaminated air has to be cleaned. Fig. 2 shows a reaction chamber 6 which reaction chamber 6 has an inlet 8 and an outlet 10. An ultravio- let light tube 12 is shown inside an oblong ozone production chamber 14 which preferably is formed as a quartz tube, the oblong production chamber 14 having in one end 16 an inlet 18 for oxygen containing air stream 20. The oblong production chamber 14 has an outlet 22 positioned in the opposite end 24 inside the primary reaction chamber 6. The ozone containing air stream 26 is mixed inside the chambers with contaminated air coming from the inlet 8 and forming a combined air stream 28. A nozzle 30 for spraying water or water containing diluted sulphuric acid is placed inside the chamber 6 for spraying water or water containing acid for forming a fog which can react with the chemical contents in the chamber 6 and also for cleaning the outside of the oblong
production chamber 14 which at the same time is sprayed at the outside. A drain outlet 34 is shown for draining the water or the water containing acid into an outlet. A secondary reaction chamber 32 is shown, to which a tube 36 is connected. Also a ventilator 38 is shown. The ventilator 38 pulls contaminated air 26 through the inlet 8 and through the reaction chamber 6, from where the ventilator pulls the air into the secondary reaction chamber 32 and further through the outlet 10 into piping 36.
The secondary reaction chamber 32 has the effect that an ozone reaction continuous so that the content of ozone is reduced to near a safety level before the air stream leaves the outlet 10.
In a preferred embodiment of the invention the oxygen containing air stream is cooled to a temperature well below about 40 0C in order to prevent the quartz tube from heating to a temperature above 40 °C which could result in reduced ozone production. Further it is preferred that the humidity of the oxygen containing air stream is reduced, hi a second possible embodiment of the invention cooling means are used for both reducing the content of humidity and for cooling the oxygen containing air stream.
It is possible to use a very high concentration of oxygen for the production of ozone. Even liquid oxygen could be used after an evaporating process; which process could produce low temperature gaseous oxygen.
Significance of ozone in the system of the invention
Ozone is a toxic and powerful oxidizing gas having a strong disinfecting and odour reducing effect. In addition, ozone can be produced from oxygen containing gas or air, such as atmospheric air, at the desired site of action, and it decomposes naturally within relatively short time to molecular oxygen leaving non-toxic residual products, depending on temperature, relative humidity, pH and presence of other organic or inorganic matter. Ozone is useful for reduction of air borne pollutants, hi the present invention ozone is produced when an oxygen containing air stream, such as an uncon- taminated atmospheric air stream, is brought into contact with ultraviolet light. At elevated air humidity there is a risk of generation of hydrogenperoxide instead of ozone, and it is therefore preferred to monitor the atmospheric air humidity and establish a
pre-desiccations step before bringing the air in contact with the ultraviolet light tube. Preferably, the oxygen containing air stream has a relative humidity of less than about 35 %. The oxygen containing air is preferably generated from compressed air using a conventional oxygen generator with means for nitrogen removal and cooling means. In this way the oxygen content of the air stream may be elevated in comparison to normal atmospheric air. It is preferred to use clean air with a low content of particles because these will become ionized through contact with ozone and settle on the light tube resulting in loss of effect.
Due to the toxic nature of ozone it is important to minimize its release into the confined space or building to be treated, especially when livestock and humans are present in the building. In this method relatively low concentrations of ozone are produced resulting in a maximum concentration of about 0.1 ppm at a distance of about 1 meter from the outlet. Ozone reacts primarily with C=C and C-H bonds resulting in decom- position of almost all organic substances to carbon dioxide and water. Ozone decomposes pigments and dyes and the majority of odour producing compounds including sulphur compounds and hydrogen sulphide. Ozone oxidizes metal ions, hi the system of the invention using ultraviolet light tubes to generate ozone from atmospheric air nitrogen oxides (NOx) are not produced or produced only in insignificant amounts.
Ozone interaction with water and acid hi the present system water and diluted acid, preferably diluted sulphuric acid, is sprayed directly into the chamber (6) through the nozzle (30) for the capture and washing out of airborne particles and gaseous ammonia. Dust particles, insects and organic molecules tend to stick to an ultraviolet light source during decomposition. Therefore it is preferred, that the outer wall of the oblong ozone production chamber (14) housing the ultraviolet light tube is continually flushed with the sprayed water and diluted acid. Decomposing ozone in the primary reaction chamber (6) generates atomic oxygen that reacts with water droplets or water vapour from the nozzle (30) to form hy- droxyl radicals which contributes to pollutant reduction. The diluted acid sprayed into the chamber (6) will react with gaseous ammonia to produce water soluble ammonium salts. The system is fitted with a drain outlet (32) for condensed water from chamber (6), and the water containing trapped pollutants, including odour substances, bacteria,
dust, and possibly small insects and spiders and ammonium salts, may be removed through piping to a slurry tank. Due to the use of ozone and sprayed diluted acid, the reaction chamber (6) and its components are made of non-corroding and acid resistant materials.
Effect of ultraviolet light
In addition to the ozone generating effect of ultraviolet light in the wavelength range of about 100 nm to about 200 nm, ultraviolet light in the wavelength range from about 200 nm to about 280 nm, and preferably with a spectrum peak at approximately 254 nm, has a general germicidal effect including lethal effect on insects and spiders. This is utilized in the present invention where the production chamber (14) comprises at least one ultraviolet light source (12) capable of emitting radiation in both the ozone generating range and in the germicidal range inside a hollow quartz tube, where said tube permits clean atmospheric air to enter through the inlet (18) and become ozonized through the action of ozone forming ultraviolet radiation, and after exiting the production chamber (14) through the outlet (22) to be mixed with contaminated air and sprayed water and diluted acid inside the reaction chamber (6), and where said quartz tube further permits transmission of the germicidal range only of the ultraviolet radia- tion generated from the light tube (12). The mixture of contaminated air, ozone, sprayed water and sprayed diluted acid comprises a primary reaction mixture where in addition germicidal ultraviolet radiation transmitted through the quartz tube contributes to desinfection.
In a preferred embodiment of the invention the atmospheric air stream following the exit from the passage between ultraviolet light tube (12) and quartz tube (14) is reversed and mixed with contaminated air under simultaneous supply of sprayed water droplets containing diluted acid and then subjected to a passage along the outside of the quartz tube where it is irradiated with ultraviolet light of. 253,7 nm (UV-C) resulting in the formation of atomic oxygen and hydroxyl radicals. This formation takes place with decomposition of a part of the previously formed ozone resulting in a particularly reactive environment. The presence of water and acid, preferably sulphuric acid, will have the effect that a part of the air borne dust particles are washed out while at the same time flushing the quartz tube and prevent it from becoming clogged. The
decomposition of pollutants started in the primary reaction chamber will continue when the air stream exits through outlet (10) during the passage through convenient piping to a final discharge to the confined space.
Monitoring of the system
The air desinfecting and pollutant reducing effect of the system of the invention is dependent on dosage of ultraviolet light and acid as well as air retention time in the system, e.g. retention time in the production chamber (14), the primary reaction chamber (6) and the discharge piping. The ultraviolet dosage can be regulated through con- trol of the number of ultraviolet light tubes in operation and through interaction between the percentage of clean air and recirculated contaminated air from the confined space. The treatment time is controlled through the size of the secondary reaction chambers, e.g. the discharge piping.
In a preferred embodiment of the invention, e.g. when the system is installed in a stable, it is further connected to a feed-back system comprising an electronic nose capable of detecting critical ozone levels and having proper monitoring equipment that can shut down full or partly the ozone generation until the concentration in the stable has returned to acceptable levels. In the same way the concentration of gaseous ammonia may be monitored to regulate the amount of sprayed diluted acid.
Applicability of the system of the invention
The system is useful in all types of closed livestock stables where the density of production animals leads to air borne pollution resulting in elevated risk of diseases and decreased production economy. The advantages of using the system of the invention include reduced pressure of infection from air borne germs and cross contamination reduced pressure of infection from the external environment reduced amount of insects, spiders and other arthropods in the confined space • reduced use of antibiotics increased fodder utilisation and growth rate recirculation of a greater proportion of the total air volume is possible • reduced costs of heating during the winter season
economic gain for the farmer reduced odour discharge to the environment
Claims
1. A system (2) for removal of airborne contaminants in a confined space (4) comprising a primary reaction chamber (6) which chamber (6) has an inlet (8) for contaminated air connected to the confined space (4), which chamber (6) has an outlet (10) for treated air connected to the confined space (4), and which chamber (6) comprises at least one ultraviolet light tube (12) for the generation of ozone, in which chamber (6) air coming from the confined space (4) is treated with a combination of UV radiation and ozone, characterized in that the ultraviolet light tube (12) is enclosed in an oblong ozone production chamber (14) which oblong ozone production chamber (14) is formed in a quartz tube, which oblong production chamber (14) in one end (16) has a further inlet (18) for an oxygen containing air stream (20) coming exclusively from outside the confined space (4), and which oblong production chamber (14) has an outlet (22) positioned in the opposite end (24) and inside the primary reaction chamber (6) where the ozone containing air stream (26) is mixed with contaminated air from the inlet (8) to form a combined air stream (28), which combined air stream (28) is streaming in reversed direction outside the oblong production chamber (14), where the combined air stream (28) is subjected to ultraviolet light transmitted through the wall of the oblong production chamber (14), and where said ultraviolet light having its wavelength spectrum restricted to the germicidal range and through the action of ozone.
2. A system according to claim 1 where the chamber (6) comprises at least one nozzle (30) for spraying water into said chamber for the capture and washing out of airborne particles and gaseous ammonia, and flushing of the outer wall of the oblong produc- tion chamber (14), and where the system is further fitted with a drain outlet (34) for water containing trapped pollutants.
3. A system according to claim 1 or 2 wherein said water further contains diluted acid, such as diluted sulphuric acid.
4. A system according to any one of the preceding claims further comprising a secondary reaction chamber (32) for further ozone mediated reduction of airborne contaminants having an outlet to the confined space (4), and where the concentration of ozone in the outlet stream is less than about 0.1 - 0.2 ppm, and a secondary reaction zone where further contaminant reduction takes place and where the ozone concentration is reduced to less than about 0.05 - 0.08 ppm when measured in about 1 meter's distance from the outlet.
5. A system according to any one of the' preceding claims, wherein said secondary reaction chamber comprises an outlet (36) leading treated air from the primary reaction chamber to a secondary reaction zone within the confined space.
6. A system according to any one of the preceding claims, wherein the radiation emitted from the ultraviolet light tube covers the ultraviolet spectrum from about 280 nm to about 100 nm with at least one spectrum peak in the ozone forming range, preferably at about 184.9 nm and with at least one spectrum peak in the germicidal range, preferably at about 253,7 nm.
7. The system according to claim 6, wherein the ultraviolet light tube is mounted inside a quartz tube.
8. An ozone production chamber preferably for use in a system according to any one of the preceding claims comprising a tubular quartz cylinder enclosing at least one ultraviolet light tube capable of emitting radiation in the ultraviolet spectrum from about 280 nm to about 100 nm with at least one spectrum peak in the ozone forming range, preferably at about 184.9 nm and with at least one spectrum peak in the germicidal range, preferably at about 253,7 nm and where the quartz cylinder permits pene- tration of radiation having its wavelength peak in the germicidal range but does not permit penetration of radiation having its wavelength peak in the ozone forming range.
9. The system according to any one of the preceding claims wherein the inlet air from the outside has been subjected to a drying process to obtain a relative humidity of less than 35%.
10. The system according to any one of the preceding claims wherein the confined space is a livestock stable.
Priority Applications (5)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
EP07702457A EP1986703B1 (en) | 2006-01-27 | 2007-01-26 | System for removal of airborne contaminants |
DK07702457.8T DK1986703T3 (en) | 2006-01-27 | 2007-01-26 | Airborne Pollution Removal System |
DE602007004195T DE602007004195D1 (en) | 2006-01-27 | 2007-01-26 | SYSTEM FOR REMOVING AIR POLLUTANTS |
US12/162,230 US20090020016A1 (en) | 2006-01-27 | 2007-01-26 | System for removal of airborne contaminants |
AT07702457T ATE454172T1 (en) | 2006-01-27 | 2007-01-26 | SYSTEM FOR REMOVAL OF AIR POLLUTANTS |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DKPA200600128 | 2006-01-27 | ||
DKPA200600128 | 2006-01-27 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO2007085262A1 true WO2007085262A1 (en) | 2007-08-02 |
Family
ID=37943803
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/DK2007/000038 WO2007085262A1 (en) | 2006-01-27 | 2007-01-26 | System for removal of airborne contaminants |
Country Status (6)
Country | Link |
---|---|
US (1) | US20090020016A1 (en) |
EP (1) | EP1986703B1 (en) |
AT (1) | ATE454172T1 (en) |
DE (1) | DE602007004195D1 (en) |
DK (1) | DK1986703T3 (en) |
WO (1) | WO2007085262A1 (en) |
Cited By (5)
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NL1037676C2 (en) * | 2010-02-02 | 2011-08-03 | Ozontech B V | TREATMENT, IN PARTICULAR DISINFECTION OF STABLES. |
CN101761998B (en) * | 2010-01-22 | 2012-02-29 | 华中科技大学 | Embedded pipeline air-conditioning system of envelop enclosure and control method thereof |
CN107158910A (en) * | 2017-06-28 | 2017-09-15 | 青岛国林环保科技股份有限公司 | A kind of denitrating flue gas ozone reaction device |
GB2601529A (en) * | 2020-12-03 | 2022-06-08 | Rocco Tulino Rosario | Electrostatic device with high hourly capacity for indoor air sanitization |
EP4023256A2 (en) | 2021-01-04 | 2022-07-06 | Luminalia Ingenieria y Fabricación, S.L | Disinfection device for fluids circulating through ducts by means of uv radiation |
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CA2856196C (en) | 2011-12-06 | 2020-09-01 | Masco Corporation Of Indiana | Ozone distribution in a faucet |
US9415131B2 (en) * | 2012-10-12 | 2016-08-16 | Evoqua Water Technologies Pte. Ltd | Enhanced photooxidation reactor and process |
US9095115B1 (en) * | 2013-08-12 | 2015-08-04 | Jones-Hamilton Co. | Animal house having ammonia control apparatus |
RU2542504C1 (en) * | 2014-03-06 | 2015-02-20 | Федеральное государственное бюджетное образовательное учреждение высшего профессионального образования "Кубанский государственный аграрный университет" | Method of sanation of livestock premises in presence of animals |
JP6489685B2 (en) * | 2015-03-13 | 2019-03-27 | 株式会社 リブレックス | Ozone generator |
WO2017013653A1 (en) * | 2015-07-21 | 2017-01-26 | Alex Keinan | System and method for detection of particles in liquid or in air |
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CN108704465B (en) * | 2018-05-30 | 2020-05-19 | 华中科技大学 | Method and device for simultaneously desulfurizing and denitrifying flue gas by using vacuum ultraviolet and effective chlorine |
CN111921358A (en) * | 2020-08-27 | 2020-11-13 | 南京茂泽新能源设备有限公司 | Livestock and poultry manure fermentation tail gas treatment device |
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DE10040566A1 (en) * | 2000-08-15 | 2002-03-07 | Pichler Kunststofftechnik Gmbh | Disinfecting water by ultra violet light and ozone converted from oxygen by ultra violet light in twin chamber concentric tubular assembly |
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2007
- 2007-01-26 AT AT07702457T patent/ATE454172T1/en not_active IP Right Cessation
- 2007-01-26 US US12/162,230 patent/US20090020016A1/en not_active Abandoned
- 2007-01-26 DE DE602007004195T patent/DE602007004195D1/en active Active
- 2007-01-26 WO PCT/DK2007/000038 patent/WO2007085262A1/en active Application Filing
- 2007-01-26 EP EP07702457A patent/EP1986703B1/en not_active Not-in-force
- 2007-01-26 DK DK07702457.8T patent/DK1986703T3/en active
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DE1246977B (en) * | 1964-11-18 | 1967-08-10 | Claus Hellmann | Ventilation device, especially for cattle stalls |
US4141830A (en) * | 1977-02-02 | 1979-02-27 | Ontario Research Foundation | Ozone/ultraviolet water purifier |
DE10040566A1 (en) * | 2000-08-15 | 2002-03-07 | Pichler Kunststofftechnik Gmbh | Disinfecting water by ultra violet light and ozone converted from oxygen by ultra violet light in twin chamber concentric tubular assembly |
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WO2006136167A1 (en) * | 2005-06-22 | 2006-12-28 | Oz Clean Aps | System and apparatus for air cleaning |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101761998B (en) * | 2010-01-22 | 2012-02-29 | 华中科技大学 | Embedded pipeline air-conditioning system of envelop enclosure and control method thereof |
NL1037676C2 (en) * | 2010-02-02 | 2011-08-03 | Ozontech B V | TREATMENT, IN PARTICULAR DISINFECTION OF STABLES. |
CN107158910A (en) * | 2017-06-28 | 2017-09-15 | 青岛国林环保科技股份有限公司 | A kind of denitrating flue gas ozone reaction device |
CN107158910B (en) * | 2017-06-28 | 2023-11-21 | 青岛国林科技集团股份有限公司 | Ozone reaction device for flue gas denitration |
GB2601529A (en) * | 2020-12-03 | 2022-06-08 | Rocco Tulino Rosario | Electrostatic device with high hourly capacity for indoor air sanitization |
EP4023256A2 (en) | 2021-01-04 | 2022-07-06 | Luminalia Ingenieria y Fabricación, S.L | Disinfection device for fluids circulating through ducts by means of uv radiation |
Also Published As
Publication number | Publication date |
---|---|
ATE454172T1 (en) | 2010-01-15 |
EP1986703A1 (en) | 2008-11-05 |
DK1986703T3 (en) | 2010-05-10 |
EP1986703B1 (en) | 2010-01-06 |
US20090020016A1 (en) | 2009-01-22 |
DE602007004195D1 (en) | 2010-02-25 |
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