This invention relates to a decontamination unit and to a decontamination process.
Decontaminant generating systems, such as those used to generate vaporous hydrogen peroxide (VHP), have been used to decontaminate large enclosures such as rooms and buildings (e.g., hotel rooms, hospital wards, scientific laboratories, etc.) from contaminants such as bacteria, molds, fungi, yeasts, and the like.
A problem with these decontaminant generating systems is that the electric power requirements tend to be relatively high and consequently these systems are not energy efficient. This invention relates to a decontamination unit that is suitable for decontaminating large enclosures that is energy efficient. This decontamination unit is powered by a relatively small electric generator. The electric generator is powered by an internal combustion engine which generates heat. The heat from the internal combustion engine is used to heat process air. The electric generator provides the required electric power to operate a condensing unit which is used to dehumidify process air. The electric generator is also used to power other equipment in the decontamination unit including blowers, electronic controls, and the like.
With the inventive decontamination unit, the requirement for an electric heater to heat process air has been reduced or eliminated. It may be advantageous to employ a relatively small electric heater for start-up when the decontamination unit is used in relatively cold environments. However, with the inventive decontamination unit, the requirements for electric power are significantly reduced as compared to the prior art. For example, in one embodiment, it may be possible to employ a 30 to 150 kilovolt-ampere (kVA) electric generator using the inventive decontamination unit wherein the internal combustion engine generates heat for heating process air, while the same decontamination unit employing an electric heater for heating process air may require a 200 kVA electric generator. The inventive decontamination unit may be fuel efficient as compared to the prior art due to the fact that the electric generator is reduced in size and as a result the power required from the internal combustion engine to drive the electric generator is reduced in size.
This invention relates to a decontamination unit, comprising: an internal combustion engine, the internal combustion engine adapted to be cooled using a coolant; an electric generator, the electric generator adapted to be powered by the internal combustion engine; a heat recovery coil, the heat recovery coil adapted to receive coolant flowing from the internal combustion engine; an evaporator coil, the evaporator coil being part of a condensing unit, the condensing unit adapted to be powered by the electric generator; a blower, the blower adapted to be powered by the electric generator, the blower being suitable for forcing the flow of process air past the evaporator coil and the heat recovery coil, the evaporator coil being adapted for dehumidifying the process air, the heat recovery coil being adapted for heating the process air; and at least one decontaminant dispersing module suitable for mixing decontaminant with the process air and dispersing the resulting decontaminant air mixture in an area to be decontaminated.
This invention relates to a decontamination process, comprising: operating an internal combustion engine, the internal combustion engine providing power to an electric generator, the internal combustion engine generating heat and being cooled using a coolant; flowing process air containing water vapor past an evaporator coil to condense water vapor and separate it from the process air, the evaporator coil being part of a condensing unit, the electric generator providing power to operate the condensing unit; flowing coolant from the internal combustion engine to a heat recovery coil; flowing the process air from the evaporator coil past the heat recovery coil to heat the process air; mixing the process air with a decontaminant to form a decontaminant air mixture; flowing the decontaminant air mixture in an enclosure to be decontaminated.
In the annexed drawings all parts and features have like references. A number of the annexed drawings are schematic illustrations which are not necessarily proportioned accurately or drawn to scale.
All ranges and ratio limits disclosed in the specification and claims may be combined in any manner. It is to be understood that unless specifically stated otherwise, references to “a”, “an”, and/or “the” may include one or more than one, and that reference to an item in the singular may also include the item in the plural. All combinations specified in the claims may be combined in any manner.
The term “ruggedized,” and like terms such as “ruggedization,” are used herein to refer to apparatus that is: (1) hardened to ensure that five exposures to chemical, biological, radiological or nuclear (CBRN) contaminants, decontaminants and decontaminating procedures over a thirty-day period do not cause the apparatus to require corrective maintenance during that thirty-day period; (2) capable of being used at temperatures ranging from about −32° C. to about 49° C.; (3) capable of being used in relative humidities ranging from about 5% to about 100%; and/or (4) capable of operating when exposed to conventional hazards of solar radiation, rain, fungus, salt fog, sand, dust, vibration and/or shock in accordance with Military Standard 810 (MIL-STD-810).
The term “line” when referring to the drawings may refer to any conduit for conveying a fluid. The conduit may be in any desired form, for example, one or more pipes, tubings, channels, and the like. These may be made of materials sufficient to provide the required properties of strength, flexibility, and resistance to the fluids being conveyed. The lines may be ruggedized to permit use in hostile environments such as those that may be encountered in military applications.
The term “fluid” may refer to a liquid, gas, or mixture thereof.
The inventive decontamination unit, in its illustrated embodiment, will be described with reference to
The decontamination unit 10 may be transported using conventional techniques, for example, the decontamination unit 10 may be transported using an airplane, ship, railroad car, truck, and the like. The power generating unit 100 and the air handling unit 200 may be positioned outside the enclosure to be decontaminated, and one or more of the decontaminant dispersing modules 300 may be placed inside the enclosure to be decontaminated. For a multi-room facility, one or more of the decontaminant dispersing modules may be placed in each room.
The decontamination unit 10 may be used in hostile environments such as those that may be anticipated for military applications or for combating terror. When intended for use in such hostile environments the decontamination unit 10, or at least part thereof, may be ruggedized. The decontamination unit 10 may be constructed using any material that is sufficient to provide the apparatus with the required properties of strength and ruggedization. This may include resistance to anticipated operating conditions and hazards, including hot and cold temperatures, exposure to solar radiation, rain, fungus, salt fog, sand, dust, vibration and/or shock, as well as exposure to CBRN contaminants. The decontamination unit 10 may be constructed of materials capable of withstanding exposure to decontaminants that may be used in the decontamination unit 10 and the contaminants likely to be encountered. The materials of construction may include stainless steel, coated steel, aluminum, anodized aluminum, and the like. Various metal alloys may be used, including the stainless steel alloys SS304 and SS316, and aluminum alloy 6061. Non-reactive materials, such as polytheylene, polyvinyl chloride, fluorinated polymers such as polytetrafluorethylene, and the like, may be used.
The power generating unit 100 may comprise internal combustion engine 110 and electric generator 160. The air handling unit 200 may comprise air dehumidifying and heating unit 210, condensing unit 240, compressor 270, high efficiency particle air (HEPA) filter 280, catalytic converter 285, carbon filter 290, and alkaline gas container 295. Each of the decontaminant dispersing modules 300 may comprise a damper 310, blower 320, heater 330, liquid decontaminant container 340, and vaporization chamber 350.
The decontamination unit 10 may be energy efficient and self-contained. The energy efficiency provided by the decontamination unit 10 may relate to using heat generated by the internal combustion engine 110 for heating process air in the air dehumidifying and heating unit 210. The decontamination unit 10 may be self-contained due to the fact that all of the power required to operate the decontamination unit 10 may be provided by the internal combustion engine 110 and the electric generator 160.
The internal combustion engine 110 may comprise any internal combustion engine that is suitable for providing sufficient power to operate the electric generator 160. The internal combustion engine 110 may be ruggedized to permit use in hostile environments that may be anticipated for military applications. The internal combustion engine 110 may be operated using diesel fuel, gasoline, petroleum gas, propane gas, natural gas, liquefied petroleum gas, hydrogen gas, biofuels (e.g., ethanol, biodiesel fuel, etc.), and the like. The internal combustion engine 110 may comprise a spark ignition engine or a compression ignition engine. The internal combustion engine 210 may comprise a two-cycle engine, four-cycle engine, rotary engine, or gas turbine engine. The internal combustion engine may comprise from 1 to about 12 cylinders, and in one embodiment from about 3 to about 8 cylinders. The internal combustion engine 110 may be turbo-charged. The internal combustion engine 110 may have an engine capacity in the range from about 1 to about 5 liters, and horsepower in the range from about 5 to about 125. The fuel tank 112 may have a capacity in the range from about 20 to about 180 liters, and in one embodiment from about 50 to about 120 liters. The fuel tank 112 may be a base mounted fuel tank, that is, it may be positioned at the base of or under the internal combustion engine 110.
The electric generator 160 may comprise any electric generator that can be powered by the internal combustion engine 110 and provide sufficient power to operate the various electrically powered components of the decontamination unit 10. These may include blowers 212 and 320, condensing unit 240, compressor 270, heater 330, as well as any lighting, electrically operated valves, computers, monitors, controllers, recorders, and the like, that may be required. The electric generator 160 may be ruggedized to permit use in hostile environments such as those that may be anticipated for military applications. The electric generator 160 may have a power rating in the range from about 30 to about 150 kVA, and in one embodiment in the range from about 60 to about 90 kVA, and in one embodiment in the range from about 70 to about 80 kVA. The power rating is significantly less than that of an electrical generator of about 200 kVA that might be required for a comparably sized decontamination unit wherein the process air is heated using an electric heater powered by the electric generator rather than by heat generated by the internal combustion engine as with the inventive decontamination unit 10.
The internal combustion engine 110 and the electric generator 160 may be combined as a single piece of equipment. This combination may be referred to as a power generator. An example of a power generator that may be used is a 75 kW packaged diesel generator set available from John Deere under the trade designation SKU 553465, Model MJ75UL-2SAE. The engine is a diesel engine. The electric generator may have an output of 75 kVA at 50 Hz. This power generator may be skid mounted and have the dimensions of 80 inches (203 cm) by 40 inches (102 cm) by 52 inches (132 cm), and a weight of 2337 pounds (1060 kg). Additional information concerning this power generator may be found at http://www.gopower.com/products/2097//75-kW-John-Deere-Open-Fully-Packaged-Diesel-Generator-Set-*UL*-(75-KVA-at-50-hz).
The internal combustion engine 110 may include fuel tank 112, radiator 115 and exhaust gas system 120. The exhaust gas system 120 may include exhaust gas heat exchanger 122 and exhaust gas diverter valve 124. Exhaust gas produced by the internal combustion engine 110 may flow through line 126 and exhaust gas diverter valve 124. From exhaust gas diverter valve 124, the exhaust gas may flow through line 128 to and through exhaust gas heat exchanger 122, and from the exhaust gas heat exchanger 122 to the atmosphere. Alternatively, the exhaust gas may bypass exhaust gas heat exchanger 122 and flow from exhaust gas diverter valve 124 through line 130 to the atmosphere. Alternatively, part of the exhaust gas may flow through the exhaust gas heat exchanger 122 and part of the exhaust gas may bypass the exhaust gas heat exchanger 122. The exhaust gas heat exchanger 122 may be used to heat engine coolant flowing from the internal combustion engine 110 to the heat recovery coil 214.
Engine coolant may circulate in the internal combustion engine 110 during its operation in order to control the internal temperature of the internal combustion engine. Any coolant known for use with internal combustion engines may be used. For example, the coolant may comprise a mixture of water and an antifreeze such as ethylene glycol, diethylene glycol, propylene glycol, or a mixture of two or more thereof. The engine coolant may flow from internal combustion engine 110 through line 132 to and through exhaust gas heat exchanger 122. In exhaust gas heat exchanger 122, the coolant may be heated by the exhaust gas. The coolant may flow from exhaust gas heat exchanger 122 through line 134 to three-way valve 136. The coolant may flow through three-way valve 136 to line 138, through line 138 to heat recovery coil 214, through the heat recovery coil 214, and then back to the internal combustion engine 110 through lines 140, 142 and 144. Alternatively, the engine coolant may bypass the heat recovery coil 214 and flow through three-way valve 136 to line 148, through line 148 to radiator 115, through radiator 115 to line 144, and through line 144 back to the internal combustion engine 110. Alternatively, part of the engine coolant may flow through the heat recovery coil 214 and part of the coolant may bypass the heat recovery coil 214. The amount of coolant that flows from the internal combustion engine 110 to the heat recovery coil 214 may depend upon the heating requirements for the heat recovery coil 214. During start up, it may be advantageous to bypass the heat recovery coil 214 and circulate the coolant through the radiator 115 until heat for the process air using the heat recovery coil 214 is needed.
The condensing unit 240, which includes evaporator coil 242 may be used to dehumidify process air flowing through the air dehumidifying and heating unit 210. The condensing unit 240 may comprise any condenser that employs a vapor compression refrigeration system suitable for providing sufficient cooling to the evaporator coil 242 to dehumidify the process air. The condensing unit 240 includes compressors 244 and 246, condensing coil 248, fans 250 and 252, and expansion valve 254. The compressors 244 and 246, and the fans 250 and 252 may be powered using the electric generator 160. The compressors 244 and 246 may be compressors of any suitable design. These may include reciprocating compressors, rotary screw compressors, centrifugal compressors, scroll compressors, and the like. The condensing unit 240 may have a weight in the range from about 1500 to about 4000 pounds (680 to 1814 Kg), and in one embodiment in the range from about 2000 to about 3000 pounds (907 to 1361 Kg), and in one embodiment about 2400 pounds (1089 Kg). The condensing unit 240 may be ruggedized to permit use in hostile environments such as those that may be anticipated for military applications.
The vapor compression refrigeration system used in the condensing unit 240 may involve the use of a refrigerant, which, in the form of a saturated vapor, enters the compressors 242 and 244 from lines 241 and 243, respectively. The refrigerant is compressed in the compressors 242 and 244 to form a high-temperature, high-pressure vapor. The high-temperature, high-pressure vapor flows from the compressors 242 and 244 through lines 245 and 247, and lines 246 and 247, respectively, to the condensing coil 248. In the condensing coil 248, heat is removed from the refrigerant and the refrigerant is condensed to form a saturated liquid. Air that is cooler than the condensing coil 248 is forced across the condensing coil 248 by fans 250 and 252. The refrigerant flows from the condensing coil 248 through line 253 to and through expansion valve 254 where it undergoes a reduction in pressure. This results in an evaporation of part of the liquid refrigerant and a cooling of the refrigerant. A liquid-vapor refrigerant mixture is formed. The liquid-vapor refrigerant mixture flows from the expansion valve 254 through the evaporator coil 255. In the evaporator coil 255, the refrigerant absorbs heat energy from process air flowing across the evaporator coil 255, as indicated by arrow 261. This results in the liquid part of the liquid-vapor refrigerant mixture evaporating and the formation of a saturated vapor in the evaporator coil 255. Moisture from the process air condenses on the exterior of the evaporator coil 255. The resulting condensate flows from the exterior of the evaporator coil 255 out of the air dehumidifying and heating unit 210 as indicated by arrow 258. To complete the refrigeration cycle, the saturated refrigerant vapor flows from the evaporator coil 255 through line 256 to and through lines 241 and 243 back to the compressors 242 and 244. Valve 259 is provided in lines 256 to permit a partial or complete bypass of the compressors 242 and 244. This may be useful during start up or shut down.
The cooling capacity of the refrigeration system used in the condensing unit 240 may be in the range from about 5 to about 25 tons of refrigeration, and in one embodiment in the range from about 15 to about 25 tons of refrigeration, and in one embodiment about 21 tons of refrigeration. The term “ton of refrigeration” refers to the rate of heat removal required to freeze 1 ton (2000 pounds) of water at 32° F. (0° C.) in 24 hours. One ton of refrigeration=12,000 Btu/hr=12,660 kJ/h=3.517 kW.
The refrigerant may comprise any refrigerant suitable for use in a vapor compression refrigeration system. The refrigerant may comprise nitrogen, ammonia, carbon dioxide, one or more organic compounds containing 1 to about 5 carbon atoms (e.g., methylenechloride), one or more hydrocarbons containing 1 to about 5 carbon atoms (e.g., methane, ethane, ethylene, propane, butane, pentane, etc.), or a mixture of two or more thereof. The refrigerant may comprise one or more chlorofluorocarbons or hydrochlorofluorcarbons available from DuPont under the tradename Freon. Examples may include Freon-11 (trichlorofluoromethane), Freon-12 (dichlorodiflouromethane), or a mixture thereof.
Process air flows from the enclosure being decontaminated and enters the air handling unit 200 from gas return line 296 and flows through the HEPA filter 280, catalytic converter 285 and carbon filter 290 prior to entering the air dehumidifying and heating unit 210. The catalytic converter 285 may be used to destroy residual amounts of the decontaminant that may be in the gaseous air stream. For example, the catalytic converter 285 may be use to convert residual hydrogen peroxide to water vapor and oxygen. The catalyst may comprise any transition metal, transition metal oxide, or combination thereof, having the desired catalytic properties. The catalyst may comprise Ag, Mn, Pd, Pt, Rh, an oxide of one or more of the foregoing metals, or a mixture of two or more of the foregoing metals and/or oxides. The catalyst may be supported by a suitable support such as an alumina support. The catalyst may comprise silver in the form of a screen or screen plating. The catalyst may comprise a silver based alloy. The catalyst may comprise manganese dioxide. The catalyst may be in the form of a bed of particulate solids. The process air may flow through a dehumidifying section 267 of the air dehumidifying and heating unit 210 in contact with evaporator coil 255 where it may be dehumidified. Water vapor in the process air may condense out when the air contacts the evaporator coil 255 as discussed above. The dehumidified process air may flow through channel 262 to air heating section 263 of the air dehumidifying and heating unit 210 where it may contact heat recovery coil 214 and be heated. The heated process air may flow through line 297 to the one or more decontaminant dispersing modules 300 where it may be mixed with one or more decontaminants to form a decontaminant air mixture. Optionally, an alkaline gas such as ammonia may flow from alkaline gas container 295, which may be a pressurized cartridge, to line 297 where it may be combined with the process air.
The process air flows from line 297 to each of the decontaminant dispersing modules 300. In each of the modules 300, the process air flows through damper 310 to and through blower 320, then from blower 320 through heater 330 to vaporization chamber 350. The decontaminant (e.g., hydrogen peroxide), which is in liquid form, is stored in liquid decontaminant container 340. The liquid decontaminant flows into vaporizer 350 where it is combined with the process air and vaporized. Compressed air from compressor 270 flows through line 271 to vaporization chamber 350 where it is used to disperse the liquid decontaminant in the process air to form the decontaminant air mixture. The resulting decontaminant air mixture flows out of the vaporization chamber 350, as indicated by arrow 360, into the enclosure to be decontaminated. The damper 310 may be used to control the flow of process air into the decontaminant dispensing module 300. When more than one module is being used, process air may flow to some of the modules but be cut off from other modules as required. Each of the modules 300 may be controlled from a central location.
The decontaminant may comprise one or more oxidants such as peracids (e.g., peracetic acid) and/or peroxides (e.g., hydrogen peroxide), and the like. Oxidants such as hypochlorites, ozone, and the like, may be used. Mixtures of two or more of these may be used. Aqueous solutions of these oxidants may be used. The decontaminant may be combined with a solvent. The solvent may be miscible with water. When the decontaminant comprises hydrogen peroxide, the solvent may be used to enhance the solubility of the hydrogen peroxide and its associated decomposition products in the contaminant and thereby enhance the rate of destruction of the contaminant. The solvent may comprise a mixture of water and tert-butyl alcohol; water and acetonitrile; or water, acetronitrile and isopropyl alcohol. Other suitable solvents may include tetrahydrofuran, dimethylsulfoxide, acetone, acetaldehyde, propylene oxide, acetamide, diethylamine, dimethoxyethane, or a mixture of two or more thereof. The solvent concentration in the combined mixture of decontaminant and solvent may be in the range up to about 60% by weight solvent, and in one embodiment in the range from about 20 to about 60% by weight solvent. The decontaminant may be combined with an alkaline gas such as ammonia in applications wherein an increase in the pH of the decontaminant may be desired.
Vaporous hydrogen peroxide (VHP), which may be generated from an aqueous solution of hydrogen peroxide, may be used as the decontaminant. The aqueous solution may comprise from about 30% to about 40% by weight hydrogen peroxide, and from about 60% to about 70% by weight water. By adding an alkaline gas that is soluble in the hydrogen peroxide (ammonia, for example), the pH of the decontaminant may be controlled. The presence of hydrogen peroxide in the decontaminant may serve to lower the pH (35% aqueous hydrogen peroxide solution has a pH of about 3 to about 4) and the ammonia may be added to raise the pH to a value of about 8 to about 9. The volumetric ratio of VHP to ammonia gas may be in the range from about 1:1 to about 1:0.0001.
VHP, when used in combination with ammonia gas, may be referred to as modified VHP or mVHP. VHP and/or mVHP may be effective microbial and chemical decontaminants because they may provide a broad spectrum of activity against a wide variety of pathogenic microorganisms and chemical pathogenic agents, such as hard to destroy spores of Bacillus stearothermophilus, Bacillus anthracis, smallpox virus, and the like. They may be also effective at or close to room temperature (e.g., about 15 to about 30° C.), making them suitable for use in the enclosure to be decontaminated with little or no heating. VHP and/or mVHP may have good material compatibility, rendering them safe for use with a variety of equipment and materials, including electronic equipment, soft furnishings, brass and chrome fixtures, and the like. VHP may degrade to water and oxygen over time, which may not be harmful to a person subsequently entering the decontaminated enclosure. Low levels of hydrogen peroxide (for example, about 1 ppm, or less) that may remain in the decontaminated enclosure may not be considered to pose a risk to a person entering the enclosure.
When the decontaminant air stream flows into the enclosure to be decontaminated and contacts contaminated surfaces to be decontaminated, the process may be regarded as a dry process characterized by the absence of condensate formation on the surfaces being decontaminated. Alternatively, the process may be regarded as a wet process characterized by the formation of a condensate in the form of a liquid film on the surfaces being decontaminated. The liquid film may have a film layer thickness in the range up to about 20 microns, and in one embodiment up to about 10 microns, and in one embodiment up to about 5 microns, and in one embodiment up to about 1 micron. The film layer may be referred to as a microcondensate layer of hydrogen peroxide.
The progress of the decontamination process may be monitored using one or more decontamination or sterilization indicators. These indicators may contain a biological indicator. The biological indicator may comprise one or more test organisms which may be more resistant to the decontamination process than the organisms to be destroyed by the decontamination process. The test organism may be placed in contact with an incubation medium to determine whether the decontamination process was effective.
The temperature of the decontaminant air stream entering the enclosure to be decontaminated may be in the range from about 10° C. to about 50° C., and in one embodiment in the range from about 15° C. to about 50° C., and in one embodiment in the range from about 15° C. to about 30° C. The relative humidity of the decontaminant air stream entering the enclosure to be decontaminated may be in the range from about 0 to about 50%, and in one embodiment in the range from about 20 to about 40% by volume. The term “relative humidity” is used herein to refer to the ratio of the partial pressure of water vapor in the decontaminant air stream to the saturated vapor pressure of water at the temperature of the decontaminant air stream expressed in terms of percentage. The concentration of decontaminant in the decontaminant air mixture entering the enclosure to be decontaminated may be in the range from about 0.01 to about 2% by volume, and in one embodiment in the range from about 0.01 to about 1.5% by volume, and in one embodiment in the range from about 0.01 to about 1% by volume, and in one embodiment in the range from about 0.01 to about 0.5% by volume, and in one embodiment in the range from about 0.02 to about 0.2% by volume, and in one embodiment in the range from about 0.02 to about 0.05% by volume. When the decontaminant comprises solvent, the concentration of decontaminant plus solvent in the decontaminant air mixture entering the enclosure to be decontaminated may be in the range from about 0.01 to about 0.2% by volume, and in one embodiment in the range from about 0.02 to about 0.08% by volume. When the decontaminant comprises an alkaline gas, the concentration of alkaline gas in the decontaminant air mixture entering the enclosure to be decontaminated may be in the range from about 0.001 to about 0.01% by volume, and in one embodiment in the range from about 0.003 to about 0.005% by volume. The gas flow rate through the enclosure being decontaminated may be in the range from about 5 to about 40 cubic feet per minute (CFM) (0.14 to 1.13 cubic meters per minute (CMM)), and in one embodiment in the range from about 10 to about 20 CFM (0.28 to 0.57 CMM). The temperature within the enclosure being decontaminated may be in the range from about 10° C. to about 50° C., and in one embodiment in the range from about 15° C. to about 50° C., and in one embodiment in the range from about 15° C. to about 30° C. The operating pressure within the enclosure being decontaminated may be slightly negative to prevent the leakage of contaminants and decontaminants from the enclosure. The internal pressure may be in the range of up to about 10 inches of water below atmospheric pressure, and in one embodiment in the range from about 0.01 to about 5 inches of water, and in one embodiment in the range from about 0.01 to about 2 inches of water, and in one embodiment in the range from about 0.01 to about 1 inch of water, and in one embodiment in the range from about 0.01 to about 0.5 inch of water, and in one embodiment in the range from about 0.01 to about 0.3 inch of water below atmospheric pressure.
The contaminants may comprise one or more chemical, biological, radiological and/or nuclear (CBRN) warfare agents. Different levels of decontamination may be accomplished within the enclosure to be decontaminated. As used herein, the term “decontamination,” is intended to encompass both microbial decontamination as well as chemical decontamination—the destruction of chemical agents, or their conversion to harmless or odorless compounds. Decontamination may also encompass the neutralizing of unpleasant odors, such as tobacco smoke, perfume, or body odor residues, and odors and dampness due to molds. “Microbial decontamination” may be used herein to encompass the destruction of biological contaminants, specifically, living microorganisms, and also the destruction or inactivation of pathogenic forms of proteinaceous-infectious agents (prions). The term microbial decontamination encompasses sterilization, the highest level of biological contamination control, which connotes the destruction of all living microorganisms. The term also includes disinfection, the destruction of harmful microorganisms, and sanitizing, which connotes being free from germs. “Chemical decontamination” is intended to encompass the destruction of pathogenic chemical agents or their conversion to less harmful or odiferous species.
Exemplary biological contaminants which may be destroyed in the decontamination process include bacterial spores, vegetative bacteria, viruses, molds, and fungi. Some of these may be capable of killing or causing severe injury to mammals, particularly humans. Included among these are viruses, such as equine encephalomyelitis and smallpox, the coronavirus responsible for Severe Acute Respiratory Syndrome (SARS); bacteria, such as those which cause plague (Yersina pestis), anthrax (Bacillus anthracis), and tularemia (Francisella tularensis); and fungi, such as coccidioidomycosis; as well as toxic products expressed by such microorganisms; for example, the botulism toxin expressed by the common Clostridium botulinium bacterium.
Also included are the less harmful microorganisms, such as those responsible for the common cold (rhinoviruses), influenza (orthomyxoviruses), skin abscesses, toxic shock syndrome (Staphylococcus aureus), bacterial pneumonia (Streptococcus pneumoniae), stomach upsets (Escherichia coli, Salmonella), and the like.
Exemplary pathogenic chemical agents may include substances which are often referred to as chemical warfare agents, such as poison gases and liquids, particularly those which are volatile, such as nerve gases, blistering agents (also known as vesicants), and other extremely harmful or toxic chemicals. As used herein, the term “chemical pathogenic agent” is intended to include only those agents which are effective in relatively small dosages to substantially disable or kill mammals and which can be degraded or otherwise rendered harmless by a process which includes oxidation.
Exemplary chemical pathogenic agents may include choking agents, such as phosgene; blood agents, which act on the enzyme cytochrome oxidase, such as cyanogen chloride and hydrogen cyanide; incapacitating agents, such as 3-quinuclidinyl benzilate (“BZ”), which blocks the action of acetylcholine; vesicants, such as di(2-chloroethyl) sulfide (mustard gas or “HD”) and dichloro(2-chlorovinyl)arsine (Lewisite); nerve agents, such as ethyl-N, N dimethyl phosphoramino cyanidate (Tabun or agent GA), o-ethyl-S-(2-diisopropyl aminoethyl) methyl phosphono-thiolate (agent VX), isopropyl methyl phosphonofluoridate (Sarin or Agent GB), methylphosphonofluoridic acid 1,2,2-trimethylpropyl ester (Soman or Agent GD).
While the disclosed invention has been explained in relation to various detailed embodiments, it is to be understood that various modifications thereof may become apparent to those skilled in the art upon reading the specification. Therefore, it is to be understood that the invention specified herein is intended to include such modifications as may fall within the scope of the appended claims.
This application claims benefit under 35 U.S.C. §119(e) to U.S. Provisional Application Ser. No. 60/893,134, filed Mar. 6, 2007, and U.S. Provisional Application Ser. No. 60/962,876, filed Aug. 1, 2007. These applications are incorporated herein by reference in their entireties.
Number | Name | Date | Kind |
---|---|---|---|
2348574 | Ross | May 1944 | A |
2404778 | Allison | Jul 1946 | A |
2823863 | Moyes | Feb 1958 | A |
3858645 | Egger | Jan 1975 | A |
3994684 | Tomasulo | Nov 1976 | A |
4342200 | Lowi, Jr. | Aug 1982 | A |
4675923 | Ashley | Jun 1987 | A |
4743430 | Spielholz | May 1988 | A |
4808377 | Childers et al. | Feb 1989 | A |
4858256 | Shankman | Aug 1989 | A |
4861560 | Nakajima | Aug 1989 | A |
4909988 | Childers et al. | Mar 1990 | A |
4987735 | DeLong | Jan 1991 | A |
4993199 | Hughes | Feb 1991 | A |
5114670 | Duffey | May 1992 | A |
5258162 | Andersson et al. | Nov 1993 | A |
5277875 | Albright et al. | Jan 1994 | A |
5286447 | Fannin et al. | Feb 1994 | A |
5323061 | Immler et al. | Jun 1994 | A |
5401589 | Palmer et al. | Mar 1995 | A |
5405587 | Fernandez et al. | Apr 1995 | A |
5472004 | Gilliard | Dec 1995 | A |
5502975 | Brickley et al. | Apr 1996 | A |
5520893 | Kasting, Jr. et al. | May 1996 | A |
5535944 | Knowles | Jul 1996 | A |
5634880 | Feldman et al. | Jun 1997 | A |
5665316 | Salonia et al. | Sep 1997 | A |
5706846 | Sutton | Jan 1998 | A |
5868667 | Lin et al. | Feb 1999 | A |
5882590 | Stewart et al. | Mar 1999 | A |
5916096 | Wiesmann et al. | Jun 1999 | A |
5941672 | Lapointe et al. | Aug 1999 | A |
5958336 | Duarte | Sep 1999 | A |
6077480 | Edwards et al. | Jun 2000 | A |
6120739 | Thomas et al. | Sep 2000 | A |
6199388 | Fischer, Jr. | Mar 2001 | B1 |
6279589 | Goodley | Aug 2001 | B1 |
6488902 | DeCato et al. | Dec 2002 | B1 |
6517639 | Toepfer et al. | Feb 2003 | B2 |
6557365 | Dinnage et al. | May 2003 | B2 |
6645450 | Stoltz et al. | Nov 2003 | B2 |
6711907 | Dinnage et al. | Mar 2004 | B2 |
6734405 | Centanni et al. | May 2004 | B2 |
6751964 | Fischer | Jun 2004 | B2 |
6852279 | Williams et al. | Feb 2005 | B2 |
6867393 | Lewis | Mar 2005 | B1 |
6906296 | Centanni et al. | Jun 2005 | B2 |
6923716 | Koeger | Aug 2005 | B2 |
6928143 | Menear et al. | Aug 2005 | B2 |
6936434 | McDonnell et al. | Aug 2005 | B2 |
6953549 | Hill et al. | Oct 2005 | B2 |
6986386 | Sekhar et al. | Jan 2006 | B2 |
7040544 | Guyer | May 2006 | B2 |
7047751 | Dinnage et al. | May 2006 | B2 |
7102052 | McVey et al. | Sep 2006 | B2 |
7144550 | Devine et al. | Dec 2006 | B2 |
7160566 | Fink et al. | Jan 2007 | B2 |
7203979 | O'Brien | Apr 2007 | B2 |
7308798 | Caggiano | Dec 2007 | B2 |
20020015672 | Saint-Martin et al. | Feb 2002 | A1 |
20030129111 | Miller et al. | Jul 2003 | A1 |
20030132100 | Crowe et al. | Jul 2003 | A1 |
20030138347 | Lin | Jul 2003 | A1 |
20030164091 | Hill et al. | Sep 2003 | A1 |
20040184950 | McVey et al. | Sep 2004 | A1 |
20040197252 | Parrish | Oct 2004 | A1 |
20050005533 | Stewart et al. | Jan 2005 | A1 |
20050175500 | Adams et al. | Aug 2005 | A1 |
20050217710 | Kaipaninen | Oct 2005 | A1 |
20050220666 | Foster | Oct 2005 | A1 |
20060008379 | Mielnik et al. | Jan 2006 | A1 |
20060018788 | Monico et al. | Jan 2006 | A1 |
20060088441 | Hill | Apr 2006 | A1 |
20060099121 | Doona et al. | May 2006 | A1 |
20060252974 | McVey et al. | Nov 2006 | A1 |
20060270887 | Watkins | Nov 2006 | A1 |
20060289490 | Mielnik | Dec 2006 | A1 |
20070098592 | Buczynski et al. | May 2007 | A1 |
20070274858 | Childers et al. | Nov 2007 | A1 |
Number | Date | Country |
---|---|---|
0057929 | Oct 2000 | WO |
02066082 | Aug 2002 | WO |
02090747 | Nov 2002 | WO |
2004110504 | Dec 2004 | WO |
Number | Date | Country | |
---|---|---|---|
20080279721 A1 | Nov 2008 | US |
Number | Date | Country | |
---|---|---|---|
60893134 | Mar 2007 | US | |
60962876 | Aug 2007 | US |