WO2012059952A1 - Air purification system and method for cleaning air - Google Patents

Air purification system and method for cleaning air Download PDF

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Publication number
WO2012059952A1
WO2012059952A1 PCT/JP2010/006437 JP2010006437W WO2012059952A1 WO 2012059952 A1 WO2012059952 A1 WO 2012059952A1 JP 2010006437 W JP2010006437 W JP 2010006437W WO 2012059952 A1 WO2012059952 A1 WO 2012059952A1
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Prior art keywords
disks
metal substrate
air purification
purification system
charge transfer
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PCT/JP2010/006437
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French (fr)
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Takashi Iwamoto
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Empire Technology Development LLC
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Empire Technology Development LLC
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Priority to PCT/JP2010/006437 priority Critical patent/WO2012059952A1/en
Priority to JP2013516874A priority patent/JP2013542049A/en
Priority to US13/143,715 priority patent/US8252238B2/en
Priority to CN201080069796.6A priority patent/CN103180048B/en
Publication of WO2012059952A1 publication Critical patent/WO2012059952A1/en
Priority to US13/552,325 priority patent/US8354061B2/en
Anticipated expiration legal-status Critical
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03CMAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03C3/00Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
    • B03C3/34Constructional details or accessories or operation thereof
    • B03C3/38Particle charging or ionising stations, e.g. using electric discharge, radioactive radiation or flames
    • B03C3/383Particle charging or ionising stations, e.g. using electric discharge, radioactive radiation or flames using radiation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03CMAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03C3/00Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
    • B03C3/28Plant or installations without electricity supply, e.g. using electrets
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03CMAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03C3/00Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
    • B03C3/34Constructional details or accessories or operation thereof
    • B03C3/40Electrode constructions
    • B03C3/45Collecting-electrodes
    • B03C3/47Collecting-electrodes flat, e.g. plates, discs, gratings
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03CMAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03C3/00Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
    • B03C3/34Constructional details or accessories or operation thereof
    • B03C3/40Electrode constructions
    • B03C3/60Use of special materials other than liquids
    • B03C3/64Use of special materials other than liquids synthetic resins
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03CMAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
    • B03C3/00Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
    • B03C3/34Constructional details or accessories or operation thereof
    • B03C3/74Cleaning the electrodes
    • B03C3/743Cleaning the electrodes by using friction, e.g. by brushes or sliding elements

Definitions

  • Air cleaning technology an air purification system, and a method for cleaning air are disclosed.
  • VOCs volatile organic compounds
  • the conventional air purification systems use extremely fine grade filters to remove very fine particulates.
  • the extremely fine grade filters are not only expensive but also tend to be clogged easily. Therefore, the conventional air purification systems require new filters every year. Accordingly, the operating costs of the conventional air purification systems are quite high.
  • An aspect of the present disclosure relates to an air purification system comprising a plurality of disks.
  • Each of the plurality of disks comprises a metal substrate, an undercoat layer disposed on the metal substrate, a photosensitive layer disposed on the undercoat layer, and a charge transfer layer disposed on the photosensitive layer.
  • Each of the particulate absorption disks comprises a metal substrate, an undercoat layer disposed on the metal substrate, a photosensitive layer disposed on the undercoat layer, and a charge transfer layer disposed on the photosensitive layer.
  • the particulate absorption disk comprises a metal substrate, an undercoat layer disposed on the metal substrate, a photosensitive layer disposed on the undercoat layer, and a charge transfer layer disposed on the photosensitive layer.
  • Fig. 1 shows a plurality of particulate adsorption disks.
  • Fig. 2 shows a plurality of particulate adsorption disks mounted on a rotating shaft, where the diameter of the disks increases from one end of the shaft to the opposite end.
  • Fig. 3 shows a cross sectional view of the particulate adsorption disk.
  • Fig. 4 shows a diagram of an air purification system.
  • Fig. 5 shows the plurality of particulate adsorption disks.
  • Fig. 6 shows a diagram of the air purification system.
  • an air purification system can include a plurality of planar particulate adsorption disks 10A, 10B and 10C.
  • the system can generally include any number of disks, such as 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 20, 30, 40, 50, 60, 70, 80, 90, 100, and so on.
  • the number of discs may be selected to meet the desired capacity of the system.
  • the discs may generally be any size and shape.
  • the disks are typically flat and round in shape, but other shapes such as squares, triangles, pentagons, hexagons, and so on are equally possible.
  • the individual disks are typically all the same shape and size, but the shape and size may vary.
  • each of the plurality of particulate adsorption disks 10A, 10B and 10C comprises a metal substrate 1, an undercoat layer 2 disposed on the metal substrate 1, a photosensitive layer 3 disposed on the undercoat layer 2, and a charge transfer layer 4 disposed on the photosensitive layer 3, as shown in Fig. 3.
  • a cross-section of the disk would first intersect the metal substrate, then the undercoat layer, then the photosensitive layer, then the charge transfer layer.
  • the air purification system exhibits reduced or eliminated clogging relative to conventional air purification systems.
  • the metal substrate 1 can generally be made of any type of metal. Examples of suitable metals include aluminum, stainless steel, copper, iron, gold, and platinum. A thin resin coating may be deposited on the surface of metal substrate 1 to reduce or prevent corrosion of the surface opposite of undercoat layer 2. Alternatively, a plastic film or plastic sheet on which metal is attached via vapor deposition may be deposited on the surface of metal substrate 1.
  • the undercoat layer 2 is configured to reduce or prevent corrosion of the metal substrate 1.
  • the undercoat layer 2 contains an insulating material or is an insulating material.
  • an insulating aluminum oxide film can be made on the metal substrate 1 by oxidizing the metal substrate.
  • Such insulating oxide film can be used as the undercoat layer 2.
  • the surface of metal substrate 1 may be applied by various methods such as spin-coating or spraying with a polymer such as polyamide or polyimide to form the undercoat layer 2, for example.
  • the photosensitive layer 3 exhibits stable electrostatic properties and an electric charge is induced in the photosensitive layer 3 when the photosensitive layer 3 is exposed to light.
  • the photosensitive layer 3 contains or is an organic photosensitive material or a photo semiconductor material, for example.
  • the photosensitive layer 3 can be formed by various methods such as uniformly coating a solution of organic photosensitive materials on the undercoat layer 2 with a spin coater or sprayer.
  • the photosensitive material can be applied in a pure form, or with other materials such as binders or solvents.
  • the solution of organic photosensitive material is prepared by mixing the photosensitive material such as azo compounds, phthalocyanines or hydrazones with a binder such as polyvinyl alcohol (PVA), vinyl acetate, polyvinyl butyral (PVB) or polycarbonate.
  • a binder such as polyvinyl alcohol (PVA), vinyl acetate, polyvinyl butyral (PVB) or polycarbonate.
  • PVA polyvinyl alcohol
  • PVB polyvinyl butyral
  • the chemical formulas below show examples of the organic photosensitive materials.
  • the ratio of binder to organic photosensitive material can generally be any ratio. Example ratios include about 0.1, about 0.5, about 1, about 5, and about 10 parts by weight of the binder to one part by weight of the organic photosensitive material.
  • the charge transfer layer 4 is configured to separate the negative charges from the positive charges.
  • the negative charges are transferred to the surface of the charge transfer layer 4.
  • the charge transfer layer 4 contains or is one or more of hydrazone compounds, pyrazoline compounds, polyvinyl ketone compounds, carbazole compounds, oxazole compounds, triazole compounds, aromatic amine compounds, amine compounds, triphenylmethane compounds, or polycyclic aromatic compounds.
  • the chemical formulas below show examples of the materials for the charge transfer layer 4.
  • Example binder resins include silicone, styrene-butadiene copolymer, epoxy, acrylic, saturated or unsaturated polyester, polycarbonate, polyvinyl acetal, phenolic resin, polymethylmethacrylate (PMMA), melamine, polyimide, polyvinyl chloride (PVC), and vinyl acetate.
  • the mix ratio can generally be any ratio.
  • Example ratios include about 0.1, about 0.5, about 1, about 5, and about 10 parts resin binder to one part charge transport material.
  • the resulting mixture is coated over the photosensitive layer 3 with a spin coater or sprayer, for example.
  • the particulate adsorption disks 10A, 10B and 10C can be mounted by a rotating shaft 15 at various intervals depending on the thickness of each of the disks 10A, 10B and 10C and the air flow efficiency between the disks 10A, 10B and 10C.
  • the distance between adjacent disks can generally be any distance, with examples being about 0.01 cm, about 0.02 cm, about 0.03 cm, about 0.04 cm, about 0.05 cm, about 0.1 cm, about 0.2 cm, about 0.3 cm, about 0.4 cm, about 0.5 cm, about 1 cm, about 2 cm, and ranges between any two of these values.
  • the distance between adjacent disks typically will be the same distance between any two adjacent disks, but can alternatively vary.
  • the air purification system can further comprise a light source 20 configured to induce the electric charge in each photosensitive layer 3 of the particulate adsorption disks 10A, 10B and 10C shown in Figures 1-3.
  • the light source 20 can be disposed at any angle, but typically is disposed parallel to the rotating shaft 15. Fluorescent lights, halogen lamps, xenon lamps, Light Emitting Diode (LED), and lasers, for example, can be used as the light source 20. The LED and the lasers are readily available, inexpensive, and long-lasting.
  • a reflector 25 may be disposed near the light source 20 to reflect a light emitted from the light source 20 to the photosensitive layer 3.
  • the electric charge induced by the light emitted from the light source 20 moves through the charge transfer layer 4 and emerges from the surface of the charge transfer layer 4 as a negative charge, while a positive charge emerges from the surface of the opposing metal substrate 1.
  • the rotating shaft 15 mounting the particulate adsorption disks 10A, 10B and 10C is connected to the motor.
  • an air current moves in the direction of rotation of the particulate adsorption disks 10A, 10B and 10C. This rotation draws the air to be purified through the gaps between the particulate adsorption disks 10A, 10B and 10C.
  • the positively charged particulates in the air are drawn to the surface of the charge transfer layer 4 that is negatively charged. Therefore, the positively charged particulates adsorb onto the surface of the charge transfer layer 4 by the electrostatic attractive force.
  • the negatively charged particulates in the air are drawn to the surface of the metal substrate 1 that is positively charged. Therefore, the negatively charged particulates adsorb onto the surface of the metal substrate 1 by the electrostatic attractive force.
  • the disks can be rotated at generally any speed.
  • the particulate adsorption disks 10A, 10B and 10C can be rotated at a rate of about 30 rpm and about 300 rpm.
  • Lower speeds may reduce airflow and lower the rate of air purification.
  • Very high speeds may generate Coriolis forces at the disk surface, also reducing air purification.
  • Various speeds may be desirable depending on the size and shape of the disks, number of disks, degree of air cleaning needed, and so on.
  • At least one protrusion may be provided on each of the metal substrates 1.
  • Each protrusion on the metal substrates 1 induces air flow during the rotation of particulate adsorption disks 10A, 10B and 10C. Induced air flow may reduce or eliminate the use of an external fan in the system, reducing noise and energy usage.
  • the particulate adsorption disks 10A, 10B and 10C, the light source 20, and the reflector 25 may be contained in a housing 100.
  • the housing 100 has an air intake 111 and an air outlet 112.
  • a coarse filter configured to remove the large particulates may be attached to the air intake 111.
  • the air to be purified is drawn into the inside of the housing from the air intake 111 and is purified by the rotating particulate adsorption disks 10A, 10B and 10C.
  • the purified air flows from the air outlet 112 of the housing 100.
  • each disk may be arranged in various ways relative to each other, either randomly or in an ordered manner.
  • each disk is disposed in the same orientation within the system. In this orientation, the top of one disk is adjacent to the bottom of the next disk.
  • each disk is disposed in the opposite and alternating orientation to the next disk. In this orientation, the top of one disk is adjacent to the top of the next disk.
  • the particulate adsorption disks 10A, 10B and 10C are arranged so that the charge transfer layers 4 are opposed to each other and the metal substrates 1 are opposed to each other. By this arrangement, surfaces having the same polarity are opposed to each other.
  • This arrangement reduces or eliminates equipotential points from generating between the particulate adsorption disks 10A, 10B and 10C. Therefore, this arrangement effectively reduces the probability of particulates passing through the particulate adsorption disks 10A, 10B and 10C without adhering to the particulate adsorption disks 10A, 10B and 10C.
  • the conventional ion air cleaners generate a particulate ion current by using high-voltage electrodes.
  • the conventional electrostatic precipitators positively charge the particulates in an electrode grid then trapped the particulates in a negatively charged electrode filter.
  • Mechanisms of these conventional air purification systems are complex.
  • the air purification system described herein efficiently uses both positive and negative electrodes. Therefore, the mechanism of the air purification system described herein could be less complex than the conventional air purification systems.
  • the coarse filter attached to the air intake 111 shown in Fig. 4 may be eliminated. Therefore, the air purification system makes it possible to remove the nano particulates without the clogging of filters.
  • the particulate adsorption disks 10A, 10B and 10C may be arranged as an array.
  • a first column 51 including the particulate adsorption disks 10A, 10B and 10C are disposed parallel to a second column 52 including the particulate adsorption disks 10A, 10B and 10C.
  • Two, three, four, five, six, seven, eight, nine, ten, or more columns may be disposed.
  • the particulate adsorption disks 10A, 10B and 10C of the second column 52 can be inserted in the gaps between the particulate adsorption disks 10A, 10B and 10C of the first column 51.
  • the metal substrates 1 of the particulate adsorption disks 10A, 10B and 10C of the first column 51 may be opposed to the charge transfer layers 4 of the particulate adsorption disks 10A, 10B and 10C of the second column 52.
  • the charge transfer layers 4 of the particulate adsorption disks 10A, 10B and 10C of the first column 51 may be opposed to the metal substrates 1 of the particulate adsorption disks 10A, 10B and 10C of the second column 52.
  • the particulates that do not adsorb onto the metal substrates 1 of the first column 51 are attracted by the charge transfer layers 4 of the second column 52.
  • the particulates that do not adsorb onto the charge transfer layers 4 of the first column 51 are attracted by the metal substrates 1 of the second column 52.
  • the air purification system can further include a wiper 60 configured to wipe the surface of the metal substrate 1 or the surface of the charge transfer layer 4.
  • the wiper can generally be made of any material and can be of any shape.
  • a circular polyethylene non-woven fabric pad can be used for the wiper 60.
  • the wiper 60 may be connected to a shaft and a motor for rotating the wiper 60. While the light source 20 emits the light and the particulate adsorption disks 10A, 10B and 10C attract the particulates, the wiper 60 can be separate from the particulate adsorption disks 10A, 10B and 10C.
  • the air purification system may further include a plurality of wipers for wiping the particulate adsorption disks 10A, 10B and 10C respectively.
  • the plurality of wipers may be mounted by the shaft connected to the motor.
  • the air purification system described herein may further include an electrode configured to charge the particulate.
  • the electrode may be disposed near the air intake 111 of the housing 100 shown in Fig. 4.
  • the particulates charged by the electrode are effectively attracted by the particulate adsorption disks 10A, 10B and 10C.

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  • Health & Medical Sciences (AREA)
  • General Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Electrostatic Separation (AREA)
  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)

Abstract

Air purification systems comprising a plurality of disks, and methods for their use, are provided. Each of the plurality of disks comprises a metal substrate, an undercoat layer disposed on the metal substrate, a photosensitive layer disposed on the undercoat layer, and a charge transfer layer disposed on the photosensitive layer.

Description

AIR PURIFICATION SYSTEM AND METHOD FOR CLEANING AIR
Air cleaning technology, an air purification system, and a method for cleaning air are disclosed.
Background
Air pollution in sealed spaces such as airplanes, automobiles and private rooms pose significant health risks. Pollutants typically include airborne particulates such as volatile organic compounds (VOCs) from construction materials, house dust and pollen, all of which are known to cause allergic reactions and a range of respiratory disorders.
In recent years, air purification systems featuring filtering systems designed to remove these pollutants have been developed. Global production of the air purification systems was about 12.29 million units in 2008 and is expected to rise to 12.34 million units in 2013. In response to the outbreak of new influenza viruses during 2009, manufacturers are developing expanded product ranges from cheaper entry-level products through to highly functional products. While North America and Europe account for a major share of global sales, demand for air cleaners is rising in China and other Asian markets due to the prevalence of influenza and other infectious diseases.
The conventional air purification systems use extremely fine grade filters to remove very fine particulates. However, the extremely fine grade filters are not only expensive but also tend to be clogged easily. Therefore, the conventional air purification systems require new filters every year. Accordingly, the operating costs of the conventional air purification systems are quite high.
Summary
An aspect of the present disclosure relates to an air purification system comprising a plurality of disks. Each of the plurality of disks comprises a metal substrate, an undercoat layer disposed on the metal substrate, a photosensitive layer disposed on the undercoat layer, and a charge transfer layer disposed on the photosensitive layer.
Another aspect of the present disclosure relates to a method for cleaning air. The method comprises: rotating a plurality of disks, each of the plurality of disks comprising a metal substrate, an undercoat layer disposed on the metal substrate, a photosensitive layer disposed on the undercoat layer, and a charge transfer layer disposed on the photosensitive layer; irradiating the photosensitive layer with a light to induce an electric charge; and contacting air and the plurality of disks.
Yet another aspect of the present disclosure relates to a series of particulate absorption disks. Each of the particulate absorption disks comprises a metal substrate, an undercoat layer disposed on the metal substrate, a photosensitive layer disposed on the undercoat layer, and a charge transfer layer disposed on the photosensitive layer.
Yet another aspect of the present disclosure relates to a particulate absorption disk. The particulate absorption disk comprises a metal substrate, an undercoat layer disposed on the metal substrate, a photosensitive layer disposed on the undercoat layer, and a charge transfer layer disposed on the photosensitive layer.
Fig. 1 shows a plurality of particulate adsorption disks. Fig. 2 shows a plurality of particulate adsorption disks mounted on a rotating shaft, where the diameter of the disks increases from one end of the shaft to the opposite end. Fig. 3 shows a cross sectional view of the particulate adsorption disk. Fig. 4 shows a diagram of an air purification system. Fig. 5 shows the plurality of particulate adsorption disks. Fig. 6 shows a diagram of the air purification system.
Detailed Description
With reference to Fig. 1, an air purification system can include a plurality of planar particulate adsorption disks 10A, 10B and 10C. The system can generally include any number of disks, such as 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 20, 30, 40, 50, 60, 70, 80, 90, 100, and so on. The number of discs may be selected to meet the desired capacity of the system. The discs may generally be any size and shape. The disks are typically flat and round in shape, but other shapes such as squares, triangles, pentagons, hexagons, and so on are equally possible. The individual disks are typically all the same shape and size, but the shape and size may vary. For example, one portion of the system may have smaller disks, while another portion of the system may have larger disks as shown in Fig. 2. Each of the plurality of particulate adsorption disks 10A, 10B and 10C comprises a metal substrate 1, an undercoat layer 2 disposed on the metal substrate 1, a photosensitive layer 3 disposed on the undercoat layer 2, and a charge transfer layer 4 disposed on the photosensitive layer 3, as shown in Fig. 3. A cross-section of the disk would first intersect the metal substrate, then the undercoat layer, then the photosensitive layer, then the charge transfer layer. The air purification system exhibits reduced or eliminated clogging relative to conventional air purification systems.
The metal substrate 1 can generally be made of any type of metal. Examples of suitable metals include aluminum, stainless steel, copper, iron, gold, and platinum. A thin resin coating may be deposited on the surface of metal substrate 1 to reduce or prevent corrosion of the surface opposite of undercoat layer 2. Alternatively, a plastic film or plastic sheet on which metal is attached via vapor deposition may be deposited on the surface of metal substrate 1.
The undercoat layer 2 is configured to reduce or prevent corrosion of the metal substrate 1. The undercoat layer 2 contains an insulating material or is an insulating material. In the case where the metal substrate 1 is composed of aluminum, an insulating aluminum oxide film can be made on the metal substrate 1 by oxidizing the metal substrate. Such insulating oxide film can be used as the undercoat layer 2. Alternatively, the surface of metal substrate 1 may be applied by various methods such as spin-coating or spraying with a polymer such as polyamide or polyimide to form the undercoat layer 2, for example.
The photosensitive layer 3 exhibits stable electrostatic properties and an electric charge is induced in the photosensitive layer 3 when the photosensitive layer 3 is exposed to light. The photosensitive layer 3 contains or is an organic photosensitive material or a photo semiconductor material, for example. The photosensitive layer 3 can be formed by various methods such as uniformly coating a solution of organic photosensitive materials on the undercoat layer 2 with a spin coater or sprayer. The photosensitive material can be applied in a pure form, or with other materials such as binders or solvents. The solution of organic photosensitive material is prepared by mixing the photosensitive material such as azo compounds, phthalocyanines or hydrazones with a binder such as polyvinyl alcohol (PVA), vinyl acetate, polyvinyl butyral (PVB) or polycarbonate. The chemical formulas below show examples of the organic photosensitive materials. The ratio of binder to organic photosensitive material can generally be any ratio. Example ratios include about 0.1, about 0.5, about 1, about 5, and about 10 parts by weight of the binder to one part by weight of the organic photosensitive material.
Figure JPOXMLDOC01-appb-C000001
The charge transfer layer 4 is configured to separate the negative charges from the positive charges. The negative charges are transferred to the surface of the charge transfer layer 4. The charge transfer layer 4 contains or is one or more of hydrazone compounds, pyrazoline compounds, polyvinyl ketone compounds, carbazole compounds, oxazole compounds, triazole compounds, aromatic amine compounds, amine compounds, triphenylmethane compounds, or polycyclic aromatic compounds. The chemical formulas below show examples of the materials for the charge transfer layer 4.
Figure JPOXMLDOC01-appb-C000002
The materials described above can be mixed, melted, or dissolved with a resin binder. Generally any resin binder can be used. Example binder resins include silicone, styrene-butadiene copolymer, epoxy, acrylic, saturated or unsaturated polyester, polycarbonate, polyvinyl acetal, phenolic resin, polymethylmethacrylate (PMMA), melamine, polyimide, polyvinyl chloride (PVC), and vinyl acetate. The mix ratio can generally be any ratio. Example ratios include about 0.1, about 0.5, about 1, about 5, and about 10 parts resin binder to one part charge transport material. The resulting mixture is coated over the photosensitive layer 3 with a spin coater or sprayer, for example.
With reference again to Fig. 1, the particulate adsorption disks 10A, 10B and 10C can be mounted by a rotating shaft 15 at various intervals depending on the thickness of each of the disks 10A, 10B and 10C and the air flow efficiency between the disks 10A, 10B and 10C. The distance between adjacent disks can generally be any distance, with examples being about 0.01 cm, about 0.02 cm, about 0.03 cm, about 0.04 cm, about 0.05 cm, about 0.1 cm, about 0.2 cm, about 0.3 cm, about 0.4 cm, about 0.5 cm, about 1 cm, about 2 cm, and ranges between any two of these values. The distance between adjacent disks typically will be the same distance between any two adjacent disks, but can alternatively vary. The rotating shaft 15 penetrates through each of the centers of the circular disks 10A, 10B and 10C. The rotating shaft will typically be axially perpendicular to the surface of the disks, but can be oriented at any angle. The rotating shaft 15 can be connected to a motor to rotate the particulate adsorption disks 10A, 10B and 10C.
With reference next to Fig. 4, the air purification system can further comprise a light source 20 configured to induce the electric charge in each photosensitive layer 3 of the particulate adsorption disks 10A, 10B and 10C shown in Figures 1-3. The light source 20 can be disposed at any angle, but typically is disposed parallel to the rotating shaft 15. Fluorescent lights, halogen lamps, xenon lamps, Light Emitting Diode (LED), and lasers, for example, can be used as the light source 20. The LED and the lasers are readily available, inexpensive, and long-lasting. A reflector 25 may be disposed near the light source 20 to reflect a light emitted from the light source 20 to the photosensitive layer 3.
The electric charge induced by the light emitted from the light source 20 moves through the charge transfer layer 4 and emerges from the surface of the charge transfer layer 4 as a negative charge, while a positive charge emerges from the surface of the opposing metal substrate 1. As described above, the rotating shaft 15 mounting the particulate adsorption disks 10A, 10B and 10C is connected to the motor. When the particulate adsorption disks 10A, 10B and 10C are rotated by the motor, an air current moves in the direction of rotation of the particulate adsorption disks 10A, 10B and 10C. This rotation draws the air to be purified through the gaps between the particulate adsorption disks 10A, 10B and 10C.
The positively charged particulates in the air are drawn to the surface of the charge transfer layer 4 that is negatively charged. Therefore, the positively charged particulates adsorb onto the surface of the charge transfer layer 4 by the electrostatic attractive force. The negatively charged particulates in the air are drawn to the surface of the metal substrate 1 that is positively charged. Therefore, the negatively charged particulates adsorb onto the surface of the metal substrate 1 by the electrostatic attractive force.
The disks can be rotated at generally any speed. For example, the particulate adsorption disks 10A, 10B and 10C can be rotated at a rate of about 30 rpm and about 300 rpm. Lower speeds may reduce airflow and lower the rate of air purification. Very high speeds may generate Coriolis forces at the disk surface, also reducing air purification. Various speeds may be desirable depending on the size and shape of the disks, number of disks, degree of air cleaning needed, and so on.
At least one protrusion may be provided on each of the metal substrates 1. Each protrusion on the metal substrates 1 induces air flow during the rotation of particulate adsorption disks 10A, 10B and 10C. Induced air flow may reduce or eliminate the use of an external fan in the system, reducing noise and energy usage.
As shown in Fig. 4, the particulate adsorption disks 10A, 10B and 10C, the light source 20, and the reflector 25 may be contained in a housing 100. The housing 100 has an air intake 111 and an air outlet 112. A coarse filter configured to remove the large particulates may be attached to the air intake 111. The air to be purified is drawn into the inside of the housing from the air intake 111 and is purified by the rotating particulate adsorption disks 10A, 10B and 10C. The purified air flows from the air outlet 112 of the housing 100.
Individual disks may be arranged in various ways relative to each other, either randomly or in an ordered manner. In one example, each disk is disposed in the same orientation within the system. In this orientation, the top of one disk is adjacent to the bottom of the next disk. In alternative example, each disk is disposed in the opposite and alternating orientation to the next disk. In this orientation, the top of one disk is adjacent to the top of the next disk. With reference again to Fig. 1, the particulate adsorption disks 10A, 10B and 10C are arranged so that the charge transfer layers 4 are opposed to each other and the metal substrates 1 are opposed to each other. By this arrangement, surfaces having the same polarity are opposed to each other. This arrangement reduces or eliminates equipotential points from generating between the particulate adsorption disks 10A, 10B and 10C. Therefore, this arrangement effectively reduces the probability of particulates passing through the particulate adsorption disks 10A, 10B and 10C without adhering to the particulate adsorption disks 10A, 10B and 10C.
Since the particulate adsorption disks 10A, 10B and 10C are charged to different polarities on each side, both positively and negatively charged particulates are attracted to the particulate adsorption disks 10A, 10B and 10C simultaneously. The conventional ion air cleaners generate a particulate ion current by using high-voltage electrodes. The conventional electrostatic precipitators positively charge the particulates in an electrode grid then trapped the particulates in a negatively charged electrode filter. Mechanisms of these conventional air purification systems are complex. On the contrary, the air purification system described herein efficiently uses both positive and negative electrodes. Therefore, the mechanism of the air purification system described herein could be less complex than the conventional air purification systems. Depending on the size of particles in the air, the coarse filter attached to the air intake 111 shown in Fig. 4 may be eliminated. Therefore, the air purification system makes it possible to remove the nano particulates without the clogging of filters.
With reference to Fig. 5, the particulate adsorption disks 10A, 10B and 10C may be arranged as an array. A first column 51 including the particulate adsorption disks 10A, 10B and 10C are disposed parallel to a second column 52 including the particulate adsorption disks 10A, 10B and 10C. Two, three, four, five, six, seven, eight, nine, ten, or more columns may be disposed.
The particulate adsorption disks 10A, 10B and 10C of the second column 52 can be inserted in the gaps between the particulate adsorption disks 10A, 10B and 10C of the first column 51. The metal substrates 1 of the particulate adsorption disks 10A, 10B and 10C of the first column 51 may be opposed to the charge transfer layers 4 of the particulate adsorption disks 10A, 10B and 10C of the second column 52. Also, the charge transfer layers 4 of the particulate adsorption disks 10A, 10B and 10C of the first column 51 may be opposed to the metal substrates 1 of the particulate adsorption disks 10A, 10B and 10C of the second column 52.
The particulates that do not adsorb onto the metal substrates 1 of the first column 51 are attracted by the charge transfer layers 4 of the second column 52. The particulates that do not adsorb onto the charge transfer layers 4 of the first column 51 are attracted by the metal substrates 1 of the second column 52.
With reference to Fig. 6, the air purification system can further include a wiper 60 configured to wipe the surface of the metal substrate 1 or the surface of the charge transfer layer 4. The wiper can generally be made of any material and can be of any shape. For example, a circular polyethylene non-woven fabric pad can be used for the wiper 60. The wiper 60 may be connected to a shaft and a motor for rotating the wiper 60. While the light source 20 emits the light and the particulate adsorption disks 10A, 10B and 10C attract the particulates, the wiper 60 can be separate from the particulate adsorption disks 10A, 10B and 10C. When the light source 20 is turned off, the wiper 60 can be moved to one or all of the particulate adsorption disks 10A, 10B and 10C and wipes off the particulates adsorbing onto the surfaces of the particulate adsorption disks 10A, 10B and 10C. The air purification system may further include a plurality of wipers for wiping the particulate adsorption disks 10A, 10B and 10C respectively. The plurality of wipers may be mounted by the shaft connected to the motor.
Modifications and variations of the embodiments described above will occur to those skilled in the art, in the light of the above teachings. For example, the air purification system described herein may further include an electrode configured to charge the particulate. The electrode may be disposed near the air intake 111 of the housing 100 shown in Fig. 4. The particulates charged by the electrode are effectively attracted by the particulate adsorption disks 10A, 10B and 10C. The scope of this disclosure is defined with reference to the following claims.


Claims (24)

  1. An air purification system comprising a plurality of disks, each of the plurality of disks comprising a metal substrate, an undercoat layer disposed on the metal substrate, a photosensitive layer disposed on the undercoat layer, and a charge transfer layer disposed on the photosensitive layer.
  2. The air purification system of claim 1, wherein the plurality of disks are arranged so that the charge transfer layers of adjacent disks are opposed to each other.
  3. The air purification system of claim 1 or claim 2, wherein the plurality of disks are arranged so that the metal substrates of adjacent disks are opposed to each other.
  4. The air purification system of any one of claims 1-3, wherein the plurality of disks are arranged as an array.
  5. The air purification system of any one of claims 1-4, further comprising a light source configured to induce an electric charge in the photosensitive layer.
  6. The air purification system of any one of claims 1-5, further comprising a rotating shaft mounting the plurality of disks.
  7. The air purification system of claim 6, further comprising a motor connected to the rotating shaft to rotate the plurality of disks.
  8. The air purification system of any one of claims 1-7, wherein a protrusion is provided on the metal substrate.
  9. The air purification system of any one of claims 1-8, further comprising a wiper configured to wipe a surface of the metal substrate.
  10. The air purification system of any one of claims 1-8, further comprising a wiper configured to wipe a surface of the charge transfer layer.
  11. A method for cleaning air comprising:
    rotating a plurality of disks, each of the plurality of disks comprising a metal substrate, an undercoat layer disposed on the metal substrate, a photosensitive layer disposed on the undercoat layer, and a charge transfer layer disposed on the photosensitive layer;
    irradiating the photosensitive layer with a light to induce an electric charge; and
    contacting air and the plurality of disks.
  12. The method of claim 11, wherein the plurality of disks are arranged so that the charge transfer layers of adjacent disks are opposed to each other.
  13. The method of claim 11 or claim 12, wherein the plurality of disks are arranged so that the metal substrates of adjacent disks are opposed to each other.
  14. The method of any one of claims 11-13, wherein the plurality of disks are arranged as an array.
  15. The method of any one of claims 11-14, wherein the plurality of disks are mounted by a rotating shaft.
  16. The method of claim 15, wherein the plurality of disks are rotated by a motor connected to the rotating shaft.
  17. The method of any one of claims 11-16, wherein a protrusion is provided on the metal substrate.
  18. The method of any one of claims 11-17, further comprising wiping a surface of the metal substrate.
  19. The method of any one of claims 11-17, further comprising wiping a surface of the charge transfer layer.
  20. A series of particulate absorption disks, each of the particulate absorption disks comprising a metal substrate, an undercoat layer disposed on the metal substrate, a photosensitive layer disposed on the undercoat layer, and a charge transfer layer disposed on the photosensitive layer.
  21. The series of particulate absorption disks of claim 20, wherein the plurality of disks are arranged so that the charge transfer layers of adjacent disks are opposed to each other.
  22. The series of particulate absorption disks of claim 20 or claim 21, wherein the plurality of disks are arranged so that the metal substrates of adjacent disks are opposed to each other.
  23. The series of particulate absorption disks of any one of claims 20-22, wherein the particulate absorption disks are mounted by a shaft.
  24. A particulate absorption disk comprising a metal substrate, an undercoat layer disposed on the metal substrate, a photosensitive layer disposed on the undercoat layer, and a charge transfer layer disposed on the photosensitive layer.

PCT/JP2010/006437 2010-11-01 2010-11-01 Air purification system and method for cleaning air Ceased WO2012059952A1 (en)

Priority Applications (5)

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PCT/JP2010/006437 WO2012059952A1 (en) 2010-11-01 2010-11-01 Air purification system and method for cleaning air
JP2013516874A JP2013542049A (en) 2010-11-01 2010-11-01 Air cleaning system and method for cleaning air
US13/143,715 US8252238B2 (en) 2010-11-01 2010-11-01 Air purification system and method for cleaning air
CN201080069796.6A CN103180048B (en) 2010-11-01 2010-11-01 Air cleaning system and the method for clean air
US13/552,325 US8354061B2 (en) 2010-11-01 2012-07-18 Air purification system and method for cleaning air

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US13/552,325 Division US8354061B2 (en) 2010-11-01 2012-07-18 Air purification system and method for cleaning air

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US8354061B2 (en) 2013-01-15
US20120279392A1 (en) 2012-11-08
US8252238B2 (en) 2012-08-28
US20120103191A1 (en) 2012-05-03
JP2013542049A (en) 2013-11-21
CN103180048B (en) 2015-07-29
CN103180048A (en) 2013-06-26

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