WO2004112941A2 - Air purification system comprising a catalyst and a light source - Google Patents

Air purification system comprising a catalyst and a light source Download PDF

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Publication number
WO2004112941A2
WO2004112941A2 PCT/US2004/018918 US2004018918W WO2004112941A2 WO 2004112941 A2 WO2004112941 A2 WO 2004112941A2 US 2004018918 W US2004018918 W US 2004018918W WO 2004112941 A2 WO2004112941 A2 WO 2004112941A2
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WO
WIPO (PCT)
Prior art keywords
manganese oxide
titanium dioxide
purification system
air purification
coating
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Ceased
Application number
PCT/US2004/018918
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French (fr)
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WO2004112941A3 (en
Inventor
Di Wei
Rakesh Radhakrishnan
Thomas H. Vanderspurt
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Carrier Corp
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Carrier Corp
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Priority to JP2006517264A priority Critical patent/JP2006528055A/en
Priority to EP04755229A priority patent/EP1633459B1/en
Priority to DE602004013002T priority patent/DE602004013002T2/en
Publication of WO2004112941A2 publication Critical patent/WO2004112941A2/en
Publication of WO2004112941A3 publication Critical patent/WO2004112941A3/en
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

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Classifications

    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34—Chemical or biological purification of waste gases
    • B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86—Catalytic processes
    • B01D53/8668—Removing organic compounds not provided for in B01D53/8603 - B01D53/8665
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34—Chemical or biological purification of waste gases
    • B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86—Catalytic processes
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34—Chemical or biological purification of waste gases
    • B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86—Catalytic processes
    • B01D53/8671—Removing components of defined structure not provided for in B01D53/8603 - B01D53/8668
    • B01D53/8675—Ozone
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B82—NANOTECHNOLOGY
    • B82Y—SPECIFIC USES OR APPLICATIONS OF NANOSTRUCTURES; MEASUREMENT OR ANALYSIS OF NANOSTRUCTURES; MANUFACTURE OR TREATMENT OF NANOSTRUCTURES
    • B82Y30/00—Nanotechnology for materials or surface science, e.g. nanocomposites
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Definitions

  • the present invention relates generally to a manganese oxide/titanium dioxide photocatalyst/thermocatalyst coating that oxidizes gaseous contaminants, including volatile organic compounds, and decomposes ozone that adsorb onto the surface to form carbon dioxide, water, and other substances.
  • Indoor air can include trace amounts of contaminants, including ozone and volatile organic compounds such as formaldehyde, toluene, propanal, butene, and acetaldehyde.
  • Absorbent air filters such as activated carbon, have been employed to remove these contaminants from the air. As air flows through the filter, the filter blocks the passage of the contaminants, llowing contaminant free air to flow from the filter. A drawback to employing filters is that they simply block the passage of contaminants and do not destroy them. In addition, air filters are not effective to block ozone.
  • Titanium dioxide has been employed as a photocatalyst in an air purifier to destroy contaminants.
  • the titanium dioxide is illuminated with ultraviolet light, photons are absorbed by the titanium dioxide, promoting " an electron from the valence band to the conduction band, thus producing a hole in the valence band and adding an electron in the conduction band.
  • the promoted electron reacts with oxygen, and the hole remaining in the valence band reacts with water, forming reactive hydroxyl radicals.
  • a contaminant adsorbs onto the titanium dioxide catalyst, the hydroxyl radicals attack and oxidize the contaminants to water, carbon dioxide, and other substances.
  • Ozone is a pollutant that is released from equipment commonly found in the workplace, such as copiers, printer, scanners, etc. Ozone can cause nausea and headaches, and prolonged exposure to ozone can damage nasal mucous membranes, causing breathing problems. OSHA has set a permissible exposure limit (PEL) to ozone of 0.08 ppm over an eight hour period.
  • PEL permissible exposure limit
  • Ozone is a thermodynamically unstable molecule and decomposes very slowly up to temperatures of 250°C.
  • manganese oxide is effective in decomposing ozone by facilitating the oxidation of ozone to adsorbed surface oxygen atoms. These adsorbed oxygen atoms then combine with ozone to form an adsorbed peroxide species that desorbs as molecular oxygen.
  • photocatalyst/thermocatalyst coating that oxidizes gaseous contaminants, including volatile organic compounds, and decomposes ozone that adsorb onto the photocatalytic surface to form oxygen, c arbon dioxide, water, and other substances.
  • a manganese oxide/titanium dioxide photocatalytic/thermocatalytic coating on a substrate purifies the air by oxidizing any contaminants that adsorb onto the coating to water, carbon dioxide, and other substances.
  • a fan draws air into an air purification system.
  • the air flows through an open passage or channel o f a honeycomb.
  • T he surface o f the honeycomb is coated with the manganese oxide/titanium coating.
  • An ultraviolet light source positioned between successive honeycombs activates the manganese oxide/titanium dioxide coating.
  • the manganese oxide /titanium dioxide coating decomposes ozone to oxygen simultaneously with oxidation of harmful volatile organic compounds.
  • the manganese oxide lowers the energy barrier required for ozone decomposition, decomposing the ozone to molecular oxygen.
  • the manganese oxide particles on the surface of the titanium dioxide reduce the recombination rate of the electrons and the holes, increasing the photocatalytic activity of the coating.
  • the manganese oxide /titanium dioxide coating acts simultaneously as both a photocatalyst and a thermocatalyst.
  • Figure 1 schematically illustrates an enclosed environment, such as a building, vehicle or other structure, including an interior space and an HVAC system;
  • FIG. 1 schematically illustrates the air purification system of the present invention
  • FIG. 3 schematically illustrates the honeycomb of the air purification system
  • FIG. 4 schematically illustrates a method of preparing the manganese oxide/titanium dioxide photocatalyst/thermocatalyst of the present invention.
  • FIG. 1 schematically illustrates a building, vehicle, or other structure 10 including an interior space 12, such as a room, an office or a vehicle cabin, such as a car, train, bus or aircraft.
  • An HVAC system 14 heats or cools the interior space 12. Air in the interior space 12 is drawn by a path 16 into the HVAC system 14. The HVAC system 14 changes the temperature of the air drawn 16 from the interior space 12. If the HVAC system 14 is operating in a cooling mode, the air is cooled. Alternately, if the HVAC system 14 is operating in a heating mode, the air is heated. The air is then returned back by a path 18 to the interior space 12, changing the temperature of the air in the interior space 12.
  • FIG. 2 schematically illustrates an air purification system 20 employed to purify the air in the building or vehicle 10 by oxidizing contaminants, such as volatile organic compounds and semi-volatile organic compounds, to water, carbon dioxide, and other substances.
  • the contaminants can be aldehydes, ketones, alcohols, aromatics, alkenes, or alkanes.
  • the air purification system 20 also decomposes ozone to oxygen.
  • the air purification system 20 can purify air before it is drawn along path 16 into the HVAC system 14 or it can purify air leaving the HVAC system 14 before it is blown along path 18 into the interior space 12 of the building or vehicle 10.
  • the air purification system 20 can also be a stand alone unit that is not employed with a HVAC system 14.
  • a fan 34 draws air into the air purification system 20 through an inlet 22.
  • the air flows through a particle filter 24 that filters out dust or any other large particles by blocking the flow of these particles.
  • the air then flows through a substrate 28, such as a honeycomb.
  • the honeycomb 28 is made of aluminum or an aluminum alloy.
  • Figure 3 schematically illustrates a front view of the honeycomb 28 having a plurality of hexagonal open passages or channels 30. The surfaces of the plurality of open passages 30 are coated with a manganese oxide/titanium dioxide (MnO x /TiO 2 ) photocatalytic/thermocatalytic coating 40.
  • MnO x /TiO 2 manganese oxide/titanium dioxide
  • the coating 40 When activated by ultraviolet light, the coating 40 oxidizes volatile organic compounds that adsorb onto the manganese oxide/titanium dioxide coating 40. As explained below, as air flows through the open passages 30 of the honeycomb 28, contaminants that are adsorbed on the surface of the manganese oxide/titanium dioxide coating 40 are oxidized into carbon dioxide, water and other substances.
  • a light source 32 positioned between successive honeycombs 28 activates the photocatalytic coating 40 on the surface of the open passages 30.
  • the honeycombs 28 and the light source 32 alternate in the air purification system 20. That is, there is a light source 32 located between each of the honeycombs 28.
  • the light source 32 is an ultraviolet light source which generates light having a wavelength in the range of 180 nanometers to 400 nanometers.
  • the light source 32 is illuminated to activate the manganese oxide/titanium dioxide coating 40 on the surface of the honeycomb 28.
  • the photons of the ultraviolet light are absorbed by the manganese oxide/titanium dioxide coating 40, an electron is promoted from the valence band to the conduction band, producing a hole in the valence band.
  • the manganese oxide/titanium dioxide coating 40 must be in the presence of oxygen and water to oxidize the contaminants into carbon dioxide, water, and other substances.
  • the electrons that are promoted to the conduction band are captured by the oxygen.
  • the holes in the valence band react with water molecules adsorbed on the manganese oxide/titanium dioxide coating 40 to form reactive hydroxyl radicals.
  • the hydroxyl radical attacks the contaminant, abstracting a hydrogen atom from the contaminant.
  • the hydroxyl radical oxidizes the contaminants and produces water, carbon dioxide, and other substances.
  • Manganese oxide supported on titanium dioxide facilitates the decomposition of ozone to adsorbed surface oxygen atoms. These oxygen atoms then combine with ozone to form an adsorbed peroxide species that desorbs as molecular oxygen.
  • the manganese oxide acts as a site for dissociative ozone adsorption by lowering the energy barrier required for ozone decomposition. Therefore, in the presence of ozone alone, the manganese oxide produces oxygen.
  • the peroxide species are highly reactive and assist in the oxidation of volatile organic compounds to carbon dioxide and water. Therefore, the manganese oxide can be highly effective in oxidizing volatile organic compounds as well. In the presence of volatile organic compounds alone, the manganese oxide of the coating 40 produces carbon dioxide, water, and other substances.
  • the manganese oxide/titanium dioxide coating 40 decomposes ozone to oxygen simultaneously with oxidation of harmful volatile organic compounds to carbon dioxide, water, and other substances. Therefore, the manganese oxide/titanium dioxide photocatalytic/thermocatalytic coating acts simultaneously as both a photocatalyst and a thermocatalyst.
  • the highly dispersed manganese oxide particles on the surface of the titanium dioxide reduce the recombination rate of the electrons and the holes, increasing the photocatalytic activity of the coating.
  • the manganese oxide particles are nano- sized.
  • the support for the bifunctional catalyst is titanium dioxide.
  • the titanium dioxide is Millennium titania, Degussa P-25, or an equivalent titanium dioxide.
  • other photocatalytic materials or a combination of titanium dioxide with other metal oxides can be employed, as long as they are active supports for thermo-catalytic function.
  • the photocatalytic materials can be Fe 2 0 3 , ZnO, V 2 Os, Sn0 2 , or FeTiO 3 .
  • metal oxides can be mixed with titanium dioxide, such as Fe 2 0 3 , ZnO, V 2 0 5 , Sn0 2 , CuO, MnO x , W0 3 , Co 3 O 4 , CeO 2 , Zr0 2 , Si0 2 , A1 2 0 3 , Cr 2 0 3 , orNiO.
  • the manganese oxide/titanium dioxide can also be loaded with a metal oxide.
  • the metal oxide is WO 3 , ZnO, Fe 2 0 3 , V 2 Os, Sn0 2 , PbO, MgO, Co 3 O 4 , NiO, Ce0 2 , CuO, Si0 2 , A1 2 0 3 , Cr 2 0 3 , or ZrO 2 .
  • the purified air After passing through the honeycombs 28, the purified air then exits the air purifier through an outlet 36.
  • the walls 38 of the air purification system 20 are preferably lined with a reflective material 42.
  • the reflective material 42 reflects the ultraviolet light onto the surface of the open passages 30 of the honeycomb 28.
  • the catalytic performance of the manganese oxide/titanium dioxide coating is influenced by the preparation method.
  • the nano-particles of manganese oxide can be generated by deposition-precipitation, co-precipitation, impregnation, or chemical vapor deposition. By employing these methods, nano-particles of manganese oxide can be generated, improving the catalytic activity.
  • FIG. 4 schematically illustrates a flowchart of the method of preparing the manganese oxide/titanium dioxide photocatalyst/thermocatalyst of the present invention.
  • Water is added drop-wise to powder titanium dioxide to determine the point at which the pores in the titanium dioxide are filled with water, or the point of incipient wetness (step 44).
  • This amount of water is then used to dissolve a manganese salt (manganese nitrate or preferably manganese acetate), shown in step 46.
  • the amount of manganese salt needed is determined by the mole percentage of manganese targeted for the surface, usually 0.1 to 6 mol%.
  • the manganese salt solution is then added drop-wise (step 48) to the titanium dioxide.
  • the resulting powder is then dried (step 50) at 120°C for six hours.
  • the powder is then calcined (step 52) at 500°C for six hours to remove the acetate and nitrate. During calcination, the manganese is oxidized to form manganese oxide. After calcination, a titanium dioxide powder layered with manganese oxide nano-particles is created.
  • honeycomb 28 has been illustrated and described, it is to be understood that the manganese oxide/titanium dioxide coating 40 can be applied on any structure.
  • the voids in a honeycomb 28 are typically hexagonal in shape, but it is to be understood that other void shapes can be employed.
  • contaminants adsorb onto the manganese oxide/titanium dioxide coating 40 of the structure in the presence of a light source, the contaminants are oxidized into water, carbon dioxide and other substances.

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Abstract

A manganese oxide/titanium dioxide photocatalytic/thermocatalytic coating simultaneously oxidizes volatile organic compounds and decomposes ozone that adsorb onto the coating into water, carbon dioxide, and other substances. The manganese oxide is nano-sized. When photons of the ultraviolet light are absorbed by the manganese oxide/titanium dioxide coating, reactive hydroxyl radicals are formed. When a contaminant is adsorbed onto the manganese oxide/titanium dioxide coating, the hydroxyl radical oxidizes the contaminant to produce water, carbon dioxide, and other substances. Manganese oxide lowers the energy barrier required for ozone decomposition, decomposing the ozone to molecular oxygen. Therefore, the m anganese oxide/titanium dioxide coating can also simultaneously decompose ozone to oxygen.

Description

BIFUNCTIONAL MANGANESE OXIDE/TITANIUM DIOXIDE PHOTOCATALYST/THERMOCATALYST
BACKGROUND OF THE INVENTION
[1] The present invention relates generally to a manganese oxide/titanium dioxide photocatalyst/thermocatalyst coating that oxidizes gaseous contaminants, including volatile organic compounds, and decomposes ozone that adsorb onto the surface to form carbon dioxide, water, and other substances.
[2] Indoor air can include trace amounts of contaminants, including ozone and volatile organic compounds such as formaldehyde, toluene, propanal, butene, and acetaldehyde. Absorbent air filters, such as activated carbon, have been employed to remove these contaminants from the air. As air flows through the filter, the filter blocks the passage of the contaminants, llowing contaminant free air to flow from the filter. A drawback to employing filters is that they simply block the passage of contaminants and do not destroy them. In addition, air filters are not effective to block ozone.
[3] Titanium dioxide has been employed as a photocatalyst in an air purifier to destroy contaminants. When the titanium dioxide is illuminated with ultraviolet light, photons are absorbed by the titanium dioxide, promoting" an electron from the valence band to the conduction band, thus producing a hole in the valence band and adding an electron in the conduction band. The promoted electron reacts with oxygen, and the hole remaining in the valence band reacts with water, forming reactive hydroxyl radicals. When a contaminant adsorbs onto the titanium dioxide catalyst, the hydroxyl radicals attack and oxidize the contaminants to water, carbon dioxide, and other substances.
[4] Photocatalytically, titanium dioxide alone is less effective in decomposing ozone.
Ozone (O3) is a pollutant that is released from equipment commonly found in the workplace, such as copiers, printer, scanners, etc. Ozone can cause nausea and headaches, and prolonged exposure to ozone can damage nasal mucous membranes, causing breathing problems. OSHA has set a permissible exposure limit (PEL) to ozone of 0.08 ppm over an eight hour period.
[5] Ozone is a thermodynamically unstable molecule and decomposes very slowly up to temperatures of 250°C. At ambient temperatures, manganese oxide is effective in decomposing ozone by facilitating the oxidation of ozone to adsorbed surface oxygen atoms. These adsorbed oxygen atoms then combine with ozone to form an adsorbed peroxide species that desorbs as molecular oxygen. [6] Hence, there is a need for photocatalyst/thermocatalyst coating that oxidizes gaseous contaminants, including volatile organic compounds, and decomposes ozone that adsorb onto the photocatalytic surface to form oxygen, c arbon dioxide, water, and other substances.
SUMMARY OF THE INVENTION
[7] A manganese oxide/titanium dioxide photocatalytic/thermocatalytic coating on a substrate purifies the air by oxidizing any contaminants that adsorb onto the coating to water, carbon dioxide, and other substances.
[8] A fan draws air into an air purification system. The air flows through an open passage or channel o f a honeycomb. T he surface o f the honeycomb is coated with the manganese oxide/titanium coating. An ultraviolet light source positioned between successive honeycombs activates the manganese oxide/titanium dioxide coating.
[9] When photons of the ultraviolet light are absorbed by the manganese oxide/titanium dioxide c oating, reactive hydroxyl radicals are formed. W hen a contaminant, such as a volatile organic compound, is adsorbed onto the manganese oxide/titanium dioxide coating, the hydroxyl radical attacks the contaminant, abstracting a hydrogen atom from the contaminant and oxidizing the volatile organic compounds to water, carbon dioxide, and other substances.
[10] At room temperature, the manganese oxide /titanium dioxide coating decomposes ozone to oxygen simultaneously with oxidation of harmful volatile organic compounds. When ozone adsorbs on the coating, the manganese oxide lowers the energy barrier required for ozone decomposition, decomposing the ozone to molecular oxygen. Additionally, the manganese oxide particles on the surface of the titanium dioxide reduce the recombination rate of the electrons and the holes, increasing the photocatalytic activity of the coating. The manganese oxide /titanium dioxide coating acts simultaneously as both a photocatalyst and a thermocatalyst.
[11] These and other features of the present invention will be best understood from the following specification and drawings.
BRIEF DESCRIPTION OF THE DRAWINGS
[12] The various features and advantages of the invention will become apparent to those skilled in the art from the following detailed description of the currently preferred embodiment. The drawings that accompany the detailed description can be briefly described as follows: [13] Figure 1 schematically illustrates an enclosed environment, such as a building, vehicle or other structure, including an interior space and an HVAC system;
[14] Figure 2 schematically illustrates the air purification system of the present invention;
[15] Figure 3 schematically illustrates the honeycomb of the air purification system; and
[16] Figure 4 schematically illustrates a method of preparing the manganese oxide/titanium dioxide photocatalyst/thermocatalyst of the present invention.
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENT
[17] Figure 1 schematically illustrates a building, vehicle, or other structure 10 including an interior space 12, such as a room, an office or a vehicle cabin, such as a car, train, bus or aircraft. An HVAC system 14 heats or cools the interior space 12. Air in the interior space 12 is drawn by a path 16 into the HVAC system 14. The HVAC system 14 changes the temperature of the air drawn 16 from the interior space 12. If the HVAC system 14 is operating in a cooling mode, the air is cooled. Alternately, if the HVAC system 14 is operating in a heating mode, the air is heated. The air is then returned back by a path 18 to the interior space 12, changing the temperature of the air in the interior space 12.
[18] Figure 2 schematically illustrates an air purification system 20 employed to purify the air in the building or vehicle 10 by oxidizing contaminants, such as volatile organic compounds and semi-volatile organic compounds, to water, carbon dioxide, and other substances. The contaminants can be aldehydes, ketones, alcohols, aromatics, alkenes, or alkanes. The air purification system 20 also decomposes ozone to oxygen. The air purification system 20 can purify air before it is drawn along path 16 into the HVAC system 14 or it can purify air leaving the HVAC system 14 before it is blown along path 18 into the interior space 12 of the building or vehicle 10. The air purification system 20 can also be a stand alone unit that is not employed with a HVAC system 14.
[19] A fan 34 draws air into the air purification system 20 through an inlet 22. The air flows through a particle filter 24 that filters out dust or any other large particles by blocking the flow of these particles. The air then flows through a substrate 28, such as a honeycomb. In one example, the honeycomb 28 is made of aluminum or an aluminum alloy. Figure 3 schematically illustrates a front view of the honeycomb 28 having a plurality of hexagonal open passages or channels 30. The surfaces of the plurality of open passages 30 are coated with a manganese oxide/titanium dioxide (MnOx/TiO2) photocatalytic/thermocatalytic coating 40. When activated by ultraviolet light, the coating 40 oxidizes volatile organic compounds that adsorb onto the manganese oxide/titanium dioxide coating 40. As explained below, as air flows through the open passages 30 of the honeycomb 28, contaminants that are adsorbed on the surface of the manganese oxide/titanium dioxide coating 40 are oxidized into carbon dioxide, water and other substances.
[20] A light source 32 positioned between successive honeycombs 28 activates the photocatalytic coating 40 on the surface of the open passages 30. As shown, the honeycombs 28 and the light source 32 alternate in the air purification system 20. That is, there is a light source 32 located between each of the honeycombs 28. Preferably, the light source 32 is an ultraviolet light source which generates light having a wavelength in the range of 180 nanometers to 400 nanometers.
[21] The light source 32 is illuminated to activate the manganese oxide/titanium dioxide coating 40 on the surface of the honeycomb 28. When the photons of the ultraviolet light are absorbed by the manganese oxide/titanium dioxide coating 40, an electron is promoted from the valence band to the conduction band, producing a hole in the valence band. The manganese oxide/titanium dioxide coating 40 must be in the presence of oxygen and water to oxidize the contaminants into carbon dioxide, water, and other substances. The electrons that are promoted to the conduction band are captured by the oxygen. The holes in the valence band react with water molecules adsorbed on the manganese oxide/titanium dioxide coating 40 to form reactive hydroxyl radicals.
[22] When a contaminant is adsorbed onto the coating 40, the hydroxyl radical attacks the contaminant, abstracting a hydrogen atom from the contaminant. In this method, the hydroxyl radical oxidizes the contaminants and produces water, carbon dioxide, and other substances.
[23] At ambient temperatures, manganese oxide is effective in decomposing ozone.
Manganese oxide supported on titanium dioxide facilitates the decomposition of ozone to adsorbed surface oxygen atoms. These oxygen atoms then combine with ozone to form an adsorbed peroxide species that desorbs as molecular oxygen. When ozone adsorbs on the manganese oxide, the manganese oxide acts as a site for dissociative ozone adsorption by lowering the energy barrier required for ozone decomposition. Therefore, in the presence of ozone alone, the manganese oxide produces oxygen.
[24] Additionally, the peroxide species are highly reactive and assist in the oxidation of volatile organic compounds to carbon dioxide and water. Therefore, the manganese oxide can be highly effective in oxidizing volatile organic compounds as well. In the presence of volatile organic compounds alone, the manganese oxide of the coating 40 produces carbon dioxide, water, and other substances. [25] At room temperature, the manganese oxide/titanium dioxide coating 40 decomposes ozone to oxygen simultaneously with oxidation of harmful volatile organic compounds to carbon dioxide, water, and other substances. Therefore, the manganese oxide/titanium dioxide photocatalytic/thermocatalytic coating acts simultaneously as both a photocatalyst and a thermocatalyst.
[26] The highly dispersed manganese oxide particles on the surface of the titanium dioxide reduce the recombination rate of the electrons and the holes, increasing the photocatalytic activity of the coating. Preferably, the manganese oxide particles are nano- sized.
[27] Preferably, the support for the bifunctional catalyst is titanium dioxide. In one example, the titanium dioxide is Millennium titania, Degussa P-25, or an equivalent titanium dioxide. However, it is to be understood that other photocatalytic materials or a combination of titanium dioxide with other metal oxides can be employed, as long as they are active supports for thermo-catalytic function. For example, the photocatalytic materials can be Fe203, ZnO, V2Os, Sn02, or FeTiO3. Additionally, other metal oxides can be mixed with titanium dioxide, such as Fe203, ZnO, V205, Sn02, CuO, MnOx, W03, Co3O4, CeO2, Zr02, Si02, A1203, Cr203, orNiO.
[28] The manganese oxide/titanium dioxide can also be loaded with a metal oxide. In one example, the metal oxide is WO3, ZnO, Fe203, V2Os, Sn02, PbO, MgO, Co3O4, NiO, Ce02, CuO, Si02, A1203, Cr203, or ZrO2.
[29] After passing through the honeycombs 28, the purified air then exits the air purifier through an outlet 36. The walls 38 of the air purification system 20 are preferably lined with a reflective material 42. The reflective material 42 reflects the ultraviolet light onto the surface of the open passages 30 of the honeycomb 28.
[30] The catalytic performance of the manganese oxide/titanium dioxide coating is influenced by the preparation method. The nano-particles of manganese oxide can be generated by deposition-precipitation, co-precipitation, impregnation, or chemical vapor deposition. By employing these methods, nano-particles of manganese oxide can be generated, improving the catalytic activity.
[31] Figure 4 schematically illustrates a flowchart of the method of preparing the manganese oxide/titanium dioxide photocatalyst/thermocatalyst of the present invention. Water is added drop-wise to powder titanium dioxide to determine the point at which the pores in the titanium dioxide are filled with water, or the point of incipient wetness (step 44). This amount of water is then used to dissolve a manganese salt (manganese nitrate or preferably manganese acetate), shown in step 46. The amount of manganese salt needed is determined by the mole percentage of manganese targeted for the surface, usually 0.1 to 6 mol%.
[32] The manganese salt solution is then added drop-wise (step 48) to the titanium dioxide. The resulting powder is then dried (step 50) at 120°C for six hours. The powder is then calcined (step 52) at 500°C for six hours to remove the acetate and nitrate. During calcination, the manganese is oxidized to form manganese oxide. After calcination, a titanium dioxide powder layered with manganese oxide nano-particles is created.
[33] To coat manganese oxide/titanium dioxide bifunctional catalyst to a substrate, water is added to the dried manganese oxide/titanium dioxide photocatalyst/thermocatalyst to form a suspension. The suspension is applied to the surface of the honeycomb 28 by spraying, electrophoresis, or dip coating to form the manganese oxide/titanium dioxide coating 40. After the suspension is applied, the suspension is allowed to dry, forming a uniform manganese oxide/titanium dioxide coating 40 on the honeycomb 28. Preferably, the suspension has weight 1% of manganese oxide on titanium dioxide.
[34] Although a honeycomb 28 has been illustrated and described, it is to be understood that the manganese oxide/titanium dioxide coating 40 can be applied on any structure. The voids in a honeycomb 28 are typically hexagonal in shape, but it is to be understood that other void shapes can be employed. As contaminants adsorb onto the manganese oxide/titanium dioxide coating 40 of the structure in the presence of a light source, the contaminants are oxidized into water, carbon dioxide and other substances.
[35] The foregoing description is only exemplary of the principles of the invention.
Many modifications and variations of the present invention are possible in light of the above teachings. The preferred embodiments of this invention have been disclosed, however, so that one of ordinary skill in the art would recognize that certain modifications would come within the scope of this invention. It is, therefore, to be understood that within the scope of the appended claims, the invention may be practiced otherwise than as specifically described. For that reason the following claims should be studied to determine the true scope and content of this invention.

Claims

CLAIMSWhat is claimed is:
1. An air purification system comprising: a substrate; a manganese oxide/titanium dioxide coating applied on said substrate, and said manganese oxide/titanium dioxide coating includes manganese oxide on titanium dioxide; and a light source to activate said manganese oxide/titanium dioxide coating, and said manganese oxide/titanium dioxide c oating oxidizes contaminants that are adsorbed onto said manganese oxide/titanium dioxide coating when activated by said light source -
2. The air purification system as recited in claim 1 wherein said manganese oxide is nano-sized.
3. The air p urification system as recited in claim 1 wherein said 1 ight s ource is an ultraviolet light source.
4. The air purification system as recited in claim 1 wherein photons from said light source are absorbed by said manganese oxide/titanium dioxide coating to form a reactive hydroxyl radical that oxidizes contaminants in the presence of oxygen and water to carbon dioxide and water.
5. The air purification system as recited in claim 1 wherein said contaminants are one of a volatile organic compound and a semi-volatile organic compound including at least one of aldehyde, ketone, alcohol, aromatic, alkene, and alkane.
6. The air purification system as recited in claim 1 wherein said manganese oxide/titanium dioxide coating decomposes ozone.
7. The air purification system as recited in claim 6 wherein said manganese oxide lowers an energy barrier of decomposition of said ozone to decompose said ozone to molecular oxygen.
8. The air purification system as recited in claim 6 wherein said manganese oxide facilitates decomposition of said ozone into adsorbed atomic oxygen and adsorbed peroxide species, and said adsorbed atomic oxygen and said adsorbed peroxide species oxidize volatile organic compounds to carbon dioxide, water and other substances.
9. The air purification system as recited in claim 1 further including a metal oxide on a surface of said titanium dioxide.
10. The air purification system as recited in claim 9 wherein said metal oxide is at least one of W03, ZnO, Fe203, V205, Sn02, PbO, MgO, Co304, NiO, Ce02, CuO, SiO2, Al2O3, Cr203, and Zr02.
11. The a ir p urification s ystem as recited i n c laim 1 further including a m etal o xide mixed with said titanium dioxide.
12. The air purification system as recited in claim 11 wherein said metal oxide is at least one of W03, ZnO, CdS, SrTi03, Fe203, V205, Sn02, FeTi03, PbO, Mg03, Co304, NiO, Ce02, CuO, Si02, A1203, Cr203, and Zr02.
13. The air purification system as recited in claim 1 wherein said substrate is an array of voids separated by a solid wall.
14. The air purification system as recited in claim 1 further including a housing, the air purification system is in said housing, and walls of said housing are lined with a reflective material.
15. The air purification system as recited in claim 1 wherein the air purification system is at room temperature.
16. An air purification system comprising: a container having an inlet and an outlet; a porous substrate inside said container; a device for drawing a fluid into said container through said inlet, flowing said fluid through said porous substrate, and expelling said fluid out of said container through said outlet; a manganese oxide/titanium dioxide catalytic coating applied on said substrate, said manganese oxide/titanium dioxide coating including manganese oxide on titanium dioxide, and said manganese oxide lowers an energy barrier for decomposition of ozone to oxygen; and an ultraviolet light source to activate said catalytic coating, and photons from said ultraviolet 1 ight source are a bsorbed by said manganese oxide/titanium dioxide catalytic coating to form a reactive hydroxyl radical, and said reactive hydroxyl radical oxidizes contaminants jin said fluid that are adsorbed onto said manganese oxide/titanium dioxide catalytic coating when activated by said light ultraviolet light source to water and carbon dioxide in the presence of water and oxygen.
17. A method of purifying air comprising the steps of: applying a manganese oxide/titanium dioxide catalytic coating applied on a substrate, s aid m anganese o xide/titanium dioxide coating including m anganese oxide on titanium dioxide; activating said manganese oxide/titanium dioxide catalytic coating; forming a reactive hydroxyl radical; adsorbing contaminants onto said manganese oxide/titanium dioxide catalytic coating; oxidizing said contaminants with said hydroxyl radical; lowering an energy barrier of decomposition of ozone with said manganese oxide of said manganese oxide/titanium dioxide catalytic coating; and then decomposing said ozone to oxygen.
PCT/US2004/018918 2003-06-19 2004-06-14 Air purification system comprising a catalyst and a light source Ceased WO2004112941A2 (en)

Priority Applications (3)

Application Number Priority Date Filing Date Title
JP2006517264A JP2006528055A (en) 2003-06-19 2004-06-14 Bifunctional manganese oxide / titanium dioxide photocatalyst / thermal catalyst
EP04755229A EP1633459B1 (en) 2003-06-19 2004-06-14 Air purification system comprising a catalyst and a light source
DE602004013002T DE602004013002T2 (en) 2003-06-19 2004-06-14 A CATALYST AND A LIGHT SOURCE COMPRISING AIR CLEANING SYSTEM

Applications Claiming Priority (2)

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US10/464,942 2003-06-19
US10/464,942 US20040258581A1 (en) 2003-06-19 2003-06-19 Bifunctional manganese oxide/titanium dioxide photocatalyst/thermocatalyst for improving indoor air quality

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WO2004112941A2 true WO2004112941A2 (en) 2004-12-29
WO2004112941A3 WO2004112941A3 (en) 2005-01-27

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EP (1) EP1633459B1 (en)
JP (1) JP2006528055A (en)
KR (1) KR100808343B1 (en)
CN (1) CN1805780A (en)
AT (1) ATE391547T1 (en)
DE (1) DE602004013002T2 (en)
ES (1) ES2300802T3 (en)
WO (1) WO2004112941A2 (en)

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JP2006528055A (en) 2006-12-14
WO2004112941A3 (en) 2005-01-27
US20040258581A1 (en) 2004-12-23
ATE391547T1 (en) 2008-04-15
EP1633459A2 (en) 2006-03-15
KR20060026428A (en) 2006-03-23
KR100808343B1 (en) 2008-02-27
ES2300802T3 (en) 2008-06-16
DE602004013002D1 (en) 2008-05-21
EP1633459B1 (en) 2008-04-09
DE602004013002T2 (en) 2009-06-18

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