The present invention pertains to air filtration systems and specifically to air filtration systems for removing air borne contaminants from the atmosphere. Air borne contaminants are typically removed by use of some type of filter media. Air is passed through the filter media wherein contaminants are trapped by the filter. These types of systems are commonly found in furnaces and air conditioners. Such systems are inefficient and generally do not satisfactorily remove most contaminants from the air. The present invention is an improvement over well known air filtering technology which provides a system for efficiently and effectively removing air borne contaminants from the atmosphere, a room or other defined space.
A known way to remove air borne contaminates utilizes cold plasma ozone oxidation. However, typical cold plasma ozone production is expensive due to current means of producing a high alternating current voltage. This current is in the range of six to sixty thousand volts with low amp draw of two to twenty milliamps. The present invention provides an efficient and low cost solution in producing cold plasma ozone by using luminous gas filled or a combination of metal and gas filled glass tubes that are excited by a low cost electronic power supply.
The present invention relates to systems, apparatus and methods for the reduction or substantial elimination of air born contaminants by way of double oxidation and filtration. The primary oxidation is from a low cost method of producing cold plasma ozone. The secondary oxidation and primary filtration is from a catalyst, such as a manganese activated zeolite (MAZ). Final filtration is accomplished by an air filter, such as a high efficiency particulate air (HEPA) filter.
The present invention includes a substantially enclosed cabinet or housing having two openings, an inlet and an outlet. Within the housing is a fan which is utilized to draw or blow contaminated atmospheric air into the housing. The fan or blower has sufficient force to overcome the pressure drop created by filter media also located within the cabinet. The fan is preferably positioned adjacent the outlet opening and the contaminated air is drawn into the housing through the air intake opening, typically located on an opposite side of the housing. After entering the housing, the contaminated air stream is passed through or by an ozone generator, such as a corona discharge ozone generator. The ozone generator oxidizes air stream in a reaction chamber whereby the oxygen (O2) is converted to ozone (O3). During this process, a substantial amount of the air borne contaminants is precipitated from the air stream. The precipitated contaminants are trapped in a first or pre-filter which is located downstream of the ozone generator.
The ozonated and oxidated air stream next passes through an oxidizing media such as a bed of manganese activated zeolite for filtration by way of adsorption of contaminates. This process also provides a secondary oxidation that converts the ozone or O3 back into oxygen (O2) through a catalytic conversion which again precipitates contaminates from the air stream. The previously generated ozone has now been substantially eliminated from the air stream.
Next, the air stream passes through a second filter. The second filter, like the first removes the remaining precipitated contaminant particulates from the air stream. Finally, the clean air passes through the fan and through the housing outlet where it is returned to the atmosphere.
Referring to
All of the components are housed within an enclosure 20 which defines an interior space having two openings. The openings include an intake opening 22 and an outlet opening 24. Cabinet flow configuration designs include up flow, down flow, side to side flow and/or front to rear flow.
A preferred embodiment of the ozone generator power supply 40 is shown in
As shown in
A simple and exemplary ozone generator 60, as depicted in
An alternative exemplary ozone generator 60a is shown in
Adjacent the ozone generator 60 is a compound filter assembly 80. The first component of the compound filter 80 comprises a pre-filter 82. While any suitable filter would work, the preferred filter 82 is a high efficiency particulate air (HEPA) filter. Beneath the pre-filter 82 is a second filter 86. Again any suitable filter could be used but the preferred filter 86 is again a HEPA filter. Between the HEPA filters 82, 86 is an oxidizing media 84 such as a bed of manganese activated zeolite (MAZ).
Referring back to
One or more additional controls 120 are provided on the housing 20. The controls 120 include one or more switches 122, 124 to control the distribution of electrical power to the power supply 40 and/or the fan 100. In addition, the controls 120 may include a rheostat 126 to regulate the speed at which the fan 100 operates. This, in turn, controls the amount of contaminated air that is drawn into the system 10 for treatment and the rate at which the contaminated air is exposed to the filtering media contained within the compound filter assembly 80. Air flow rate is determined by ozone production rate balanced by catalytic ozone to oxygen conversion and filter limitations. The filters 82, 86 can be flat or radial flow depending upon the surface area required. MAZ may be impregnated or coated on one or both of the filters 82, 86 or may be used as a standalone filter 84 as described above.
The system 10 works as follows. As the contaminated air stream 140 is drawn through the opening 22 and across the ozone generator 60, the contaminated air 140 is oxidized by the infusion of the ozone within a reaction chamber. The oxygen present in the contaminated air is converted from O2 to O3. This also causes a chemical reaction which precipitates contaminants from the air stream 140. These precipitated contaminant particles are trapped in the first or pre-filter 82.
A bed of oxidizing media 84 is located between the filters 82, 86. As the airstream 140 passes through the oxidizing media 84, the O3 is converted back into O2. In a preferred embodiment, the oxidizing media 84 comprises manganese activated zeolite which is basically manganese oxide or MNO2. As the ozone O3 passes through the manganese oxide MNO2, the MNO2 is converted to MNO4 (manganate ion) and the ozone O3 becomes oxygen again, O2. The previously generated ozone is substantially depleted from the air stream as its passes through the bed of oxidizing media 84. This reaction again precipitates additional contaminates from the air stream 140. These additional particles are trapped in the second filter 86. Finally, the cleaned air stream 142 passes across the fan 120 and is expelled through the outlet opening 24.
While manganese activated zeolite has been described as a suitable oxidizing media 84, it is to be understood that other oxidizing medium can be utilized including magnesium treated green sand, as well as others.
After a predetermined period of time or exposure, the filters 82, 86 and oxidizing media 84 must be cleaned or replaced.
It should also be appreciated that there are two distinct variables that can be adjusted to control the effectiveness or efficacy of the filter system 10. The first variable is the size of ozone generator 60. Depending upon the severity of the contaminated air, more or less ozone may be required to sufficiently treat the air. Secondly, the speed of the fan 100 is a variable that controls the amount of time the contaminated air is being oxidized and then converted back into oxygen. Again, a slower fan speed would result in a system having greater efficacy and capable of removing more contaminants from an air stream than a faster fan speed.
The foregoing is considered as illustrative only of the principles of the invention. Furthermore, since numerous modifications and changes will readily occur to those skilled in the art, it is not desired to limit the invention to the exact construction and operation shown and described. While the preferred embodiment has been described, the details may be changed without departing from the inventions claimed herein.
This application claims the benefit of co-pending U.S. Provisional Patent Application Ser. No. 61/343,965, filed 6 May 2010.
Number | Date | Country | |
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61343965 | May 2010 | US |