JP6290891B2 - Air cleaner - Google Patents
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- JP6290891B2 JP6290891B2 JP2015529324A JP2015529324A JP6290891B2 JP 6290891 B2 JP6290891 B2 JP 6290891B2 JP 2015529324 A JP2015529324 A JP 2015529324A JP 2015529324 A JP2015529324 A JP 2015529324A JP 6290891 B2 JP6290891 B2 JP 6290891B2
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- dust collection
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- collection filter
- fiber structure
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/017—Combinations of electrostatic separation with other processes, not otherwise provided for
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/02—Plant or installations having external electricity supply
- B03C3/04—Plant or installations having external electricity supply dry type
- B03C3/08—Plant or installations having external electricity supply dry type characterised by presence of stationary flat electrodes arranged with their flat surfaces parallel to the gas stream
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/02—Plant or installations having external electricity supply
- B03C3/04—Plant or installations having external electricity supply dry type
- B03C3/09—Plant or installations having external electricity supply dry type characterised by presence of stationary flat electrodes arranged with their flat surfaces at right angles to the gas stream
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/02—Plant or installations having external electricity supply
- B03C3/04—Plant or installations having external electricity supply dry type
- B03C3/12—Plant or installations having external electricity supply dry type characterised by separation of ionising and collecting stations
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/02—Plant or installations having external electricity supply
- B03C3/04—Plant or installations having external electricity supply dry type
- B03C3/14—Plant or installations having external electricity supply dry type characterised by the additional use of mechanical effects, e.g. gravity
- B03C3/155—Filtration
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/34—Constructional details or accessories or operation thereof
- B03C3/38—Particle charging or ionising stations, e.g. using electric discharge, radioactive radiation or flames
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C3/00—Separating dispersed particles from gases or vapour, e.g. air, by electrostatic effect
- B03C3/34—Constructional details or accessories or operation thereof
- B03C3/40—Electrode constructions
- B03C3/41—Ionising-electrodes
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F24—HEATING; RANGES; VENTILATING
- F24F—AIR-CONDITIONING; AIR-HUMIDIFICATION; VENTILATION; USE OF AIR CURRENTS FOR SCREENING
- F24F8/00—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying
- F24F8/10—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by separation, e.g. by filtering
- F24F8/192—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by separation, e.g. by filtering by electrical means, e.g. by applying electrostatic fields or high voltages
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F24—HEATING; RANGES; VENTILATING
- F24F—AIR-CONDITIONING; AIR-HUMIDIFICATION; VENTILATION; USE OF AIR CURRENTS FOR SCREENING
- F24F8/00—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying
- F24F8/20—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by sterilisation
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F24—HEATING; RANGES; VENTILATING
- F24F—AIR-CONDITIONING; AIR-HUMIDIFICATION; VENTILATION; USE OF AIR CURRENTS FOR SCREENING
- F24F8/00—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying
- F24F8/50—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by odorisation
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- A—HUMAN NECESSITIES
- A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
- A61L—METHODS OR APPARATUS FOR STERILISING MATERIALS OR OBJECTS IN GENERAL; DISINFECTION, STERILISATION OR DEODORISATION OF AIR; CHEMICAL ASPECTS OF BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES; MATERIALS FOR BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES
- A61L2209/00—Aspects relating to disinfection, sterilisation or deodorisation of air
- A61L2209/10—Apparatus features
- A61L2209/14—Filtering means
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- A—HUMAN NECESSITIES
- A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
- A61L—METHODS OR APPARATUS FOR STERILISING MATERIALS OR OBJECTS IN GENERAL; DISINFECTION, STERILISATION OR DEODORISATION OF AIR; CHEMICAL ASPECTS OF BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES; MATERIALS FOR BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES
- A61L2209/00—Aspects relating to disinfection, sterilisation or deodorisation of air
- A61L2209/10—Apparatus features
- A61L2209/16—Connections to a HVAC unit
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION 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
- B03C—MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03C2201/00—Details of magnetic or electrostatic separation
- B03C2201/10—Ionising electrode with two or more serrated ends or sides
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- D06M—TREATMENT, NOT PROVIDED FOR ELSEWHERE IN CLASS D06, OF FIBRES, THREADS, YARNS, FABRICS, FEATHERS OR FIBROUS GOODS MADE FROM SUCH MATERIALS
- D06M11/00—Treating fibres, threads, yarns, fabrics or fibrous goods made from such materials, with inorganic substances or complexes thereof; Such treatment combined with mechanical treatment, e.g. mercerising
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- D—TEXTILES; PAPER
- D06—TREATMENT OF TEXTILES OR THE LIKE; LAUNDERING; FLEXIBLE MATERIALS NOT OTHERWISE PROVIDED FOR
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- D06M11/00—Treating fibres, threads, yarns, fabrics or fibrous goods made from such materials, with inorganic substances or complexes thereof; Such treatment combined with mechanical treatment, e.g. mercerising
- D06M11/32—Treating fibres, threads, yarns, fabrics or fibrous goods made from such materials, with inorganic substances or complexes thereof; Such treatment combined with mechanical treatment, e.g. mercerising with oxygen, ozone, ozonides, oxides, hydroxides or percompounds; Salts derived from anions with an amphoteric element-oxygen bond
- D06M11/36—Treating fibres, threads, yarns, fabrics or fibrous goods made from such materials, with inorganic substances or complexes thereof; Such treatment combined with mechanical treatment, e.g. mercerising with oxygen, ozone, ozonides, oxides, hydroxides or percompounds; Salts derived from anions with an amphoteric element-oxygen bond with oxides, hydroxides or mixed oxides; with salts derived from anions with an amphoteric element-oxygen bond
- D06M11/46—Oxides or hydroxides of elements of Groups 4 or 14 of the Periodic Table; Titanates; Zirconates; Stannates; Plumbates
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- D06M11/51—Treating fibres, threads, yarns, fabrics or fibrous goods made from such materials, with inorganic substances or complexes thereof; Such treatment combined with mechanical treatment, e.g. mercerising with sulfur, selenium, tellurium, polonium or compounds thereof
- D06M11/55—Treating fibres, threads, yarns, fabrics or fibrous goods made from such materials, with inorganic substances or complexes thereof; Such treatment combined with mechanical treatment, e.g. mercerising with sulfur, selenium, tellurium, polonium or compounds thereof with sulfur trioxide; with sulfuric acid or thiosulfuric acid or their salts
- D06M11/56—Sulfates or thiosulfates other than of elements of Groups 3 or 13 of the Periodic Table
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- D06M11/58—Treating fibres, threads, yarns, fabrics or fibrous goods made from such materials, with inorganic substances or complexes thereof; Such treatment combined with mechanical treatment, e.g. mercerising with nitrogen or compounds thereof, e.g. with nitrides
- D06M11/64—Treating fibres, threads, yarns, fabrics or fibrous goods made from such materials, with inorganic substances or complexes thereof; Such treatment combined with mechanical treatment, e.g. mercerising with nitrogen or compounds thereof, e.g. with nitrides with nitrogen oxides; with oxyacids of nitrogen or their salts
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- D06M13/005—Compositions containing perfumes; Compositions containing deodorants
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- D06M14/00—Graft polymerisation of monomers containing carbon-to-carbon unsaturated bonds on to fibres, threads, yarns, fabrics, or fibrous goods made from such materials
- D06M14/18—Graft polymerisation of monomers containing carbon-to-carbon unsaturated bonds on to fibres, threads, yarns, fabrics, or fibrous goods made from such materials using wave energy or particle radiation
- D06M14/26—Graft polymerisation of monomers containing carbon-to-carbon unsaturated bonds on to fibres, threads, yarns, fabrics, or fibrous goods made from such materials using wave energy or particle radiation on to materials of synthetic origin
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- 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
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- Engineering & Computer Science (AREA)
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- General Engineering & Computer Science (AREA)
- Electrostatic Separation (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Filtering Materials (AREA)
- Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
Description
本発明は消臭性を有する官能基を繊維表面に導入し、さらに該官能基に、殺菌性、抗ウイルス性を有する金属イオンを結合させた電気集塵フィルタを用いた空気清浄機に関するものである。 The present invention relates to an air purifier using an electric dust collecting filter in which a functional group having deodorizing properties is introduced on the surface of a fiber, and further, metal ions having bactericidal and antiviral properties are bonded to the functional group. is there.
近年、SARS(重症急性呼吸器症候群)やノロウイルス、鳥インフルエンザなどウイルス感染による死者が報告されている。さらにPM2.5のような大気汚染物質による健康被害についても問題になっており、塵埃の除去だけでなく、殺菌・抗ウイルス性や、消臭性などの機能が付与された空気清浄機が求められている。 In recent years, deaths due to viral infections such as SARS (Severe Acute Respiratory Syndrome), Norovirus and avian influenza have been reported. Furthermore, health damage caused by air pollutants such as PM2.5 has become a problem, and there is a need for an air purifier with functions such as sterilization, antiviral properties, and deodorization as well as dust removal. It has been.
このような事態に対応するために、電荷をかけたワイヤの間を通過した塵埃を、光触媒を担持した集塵部にて集塵した後、UVを照射して細菌やウイルスを不活化する空気清浄機や(特許文献1)、繊維表面に放射線グラフト重合によりイオン交換基を導入することによりアンモニアなどのガス成分を吸着除去できる機能性フィルター(特許文献2)などが開発されている。 In order to deal with such a situation, the dust that has passed between the charged wires is collected by the dust collecting unit carrying the photocatalyst and then irradiated with UV to inactivate bacteria and viruses. A cleaner, (Patent Document 1), and a functional filter (Patent Document 2) that can adsorb and remove gas components such as ammonia by introducing ion exchange groups onto the fiber surface by radiation graft polymerization have been developed.
しかし特許文献1のように、光触媒で細菌やウイルスを不活化する場合、紫外線照射ユニットが必要となるため装置が大きくなる上、フィルタや装置などがそれらを構成している材質によっては劣化するという問題がある。さらに光触媒では細菌やウイルスを不活化させるのに時間がかかってしまう。また、特許文献2のように、イオン交換繊維からなるフィルタだけでは特許文献2にも記載があるように比較的粗い粒子しか除去されないため、ウイルスや細菌などの小さな塵埃については後段の高性能フィルタを併用しないと除去が難しい。高性能フィルタを用いると、圧力損失が高くなってしまう。 However, when bacteria and viruses are inactivated with a photocatalyst as in Patent Document 1, an ultraviolet irradiation unit is required, so that the apparatus becomes large, and the filter and the apparatus are deteriorated depending on the material constituting them. There's a problem. Furthermore, it takes time to inactivate bacteria and viruses with photocatalysts. Further, as disclosed in Patent Document 2, only relatively coarse particles can be removed with a filter made of ion-exchange fibers as in Patent Document 2, so that a high-performance filter in the latter stage is used for small dust such as viruses and bacteria. If it is not used together, removal is difficult. When a high performance filter is used, the pressure loss becomes high.
そこで本発明は、上記課題を解決するために、圧力損失が低い構造であっても、捕集効率がより高く、さらに、消臭性と、フィルタで捕集した細菌やウイルスの不活化機能とを兼ね備える、空気清浄機を提供することを目的とする。 Therefore, in order to solve the above problems, the present invention has a higher collection efficiency even with a structure having a low pressure loss, and further has a deodorizing function and an inactivation function of bacteria and viruses collected by a filter. It aims at providing the air cleaner which combines.
すなわち第1の発明は、電圧が印加される放電電極と、前記放電電極に対向して配置される接地電極と、前記放電電極と前記接地電極との間に配置され、通気性を有する繊維構造体で形成される集塵フィルタであって、前記繊維構造体の少なくとも一部の繊維に導入される消臭性を有する官能基と、導入された前記官能基の一部の官能基に結合する金属イオンと、を有する集塵フィルタと、を備え、前記集塵フィルタで捕集した細菌及び/又はウイルスの不活化機能と消臭機能とを兼ね備えることを特徴とする空気清浄機である。 That is, the first invention is a discharge electrode to which a voltage is applied, a ground electrode disposed opposite to the discharge electrode, and a fiber structure disposed between the discharge electrode and the ground electrode and having air permeability. A dust collection filter formed by a body, which binds to a functional group having a deodorizing property introduced into at least a part of fibers of the fiber structure and a part of functional groups of the introduced functional group An air cleaner comprising a dust collection filter having metal ions, and having both an inactivation function and a deodorization function of bacteria and / or viruses collected by the dust collection filter.
また第2の発明は、前記第1の発明において、前記金属イオンが銅、銀、亜鉛、金、白金、コバルト、ニッケル、スズ、アルミニウム、パラジウムから少なくとも1種選択されることを特徴とする空気清浄機である。 According to a second invention, in the first invention, the metal ions are selected from at least one of copper, silver, zinc, gold, platinum, cobalt, nickel, tin, aluminum, and palladium. It is a purifier.
さらにまた第3の発明は、上記第1または第2の発明において、前記集塵フィルタに導入される消臭性を有する官能基が電子線グラフト重合法にて導入されることを特徴とする空気清浄機である。 Still further, a third invention is characterized in that, in the first or second invention, the deodorizing functional group introduced into the dust collecting filter is introduced by an electron beam graft polymerization method. It is a purifier.
さらにまた第4の発明は、上記第1から第3のいずれかの発明において、前記集塵フィルタに導入される消臭性を有する官能基が、スルホン酸基、リン酸基、カルボキシル基から少なくとも1種選択される塩基性ガス吸着能を有する酸性官能基であることを特徴とする空気清浄機である。 Furthermore, in a fourth invention according to any one of the first to third inventions, the deodorizing functional group introduced into the dust collecting filter is at least from a sulfonic acid group, a phosphoric acid group, and a carboxyl group. An air cleaner characterized in that it is an acidic functional group having a basic gas adsorption ability selected from one kind.
さらにまた第5の発明は、上記第1から第3のいずれかの発明において、前記集塵フィルタに導入される消臭性を有する官能基が、アミノ基からなる酸性ガス吸着能を有する塩基性官能基であることを特徴とする空気清浄機である。 Furthermore, a fifth invention is the basic of any one of the first to third inventions, wherein the functional group having a deodorizing property introduced into the dust collecting filter is an amino group and has an acid gas adsorption ability. It is an air cleaner characterized by being a functional group.
さらにまた第6の発明は、上記第1から第3のいずれかの発明において、前記集塵フィルタに導入される消臭性を有する官能基が、スルホン酸基、リン酸基、カルボキシル基から少なくとも1種選択される塩基性ガス吸着能を有する酸性官能基およびアミノ基からなる酸性ガス吸着能を有する塩基性官能基であることを特徴とする空気清浄機である。 Furthermore, a sixth invention is the method according to any one of the first to third inventions, wherein the functional group having a deodorizing property introduced into the dust collecting filter is at least from a sulfonic acid group, a phosphoric acid group, and a carboxyl group. An air cleaner characterized in that it is a basic functional group having an acidic gas adsorption ability comprising an acidic functional group and an amino group having one basic gas adsorption ability.
さらにまた第7の発明は、上記第1から第7のいずれかの発明において、前記集塵フィルタが、酸性ガス吸着特性および/または塩基性ガス吸着特性を有する無機微粒子を含有することを特徴とする空気清浄機である。 Furthermore, a seventh invention is characterized in that, in any one of the first to seventh inventions, the dust collection filter contains inorganic fine particles having acidic gas adsorption characteristics and / or basic gas adsorption characteristics. It is an air purifier.
本発明によれば、圧力損失が低い構造であっても、捕集効率がより高く、さらに、消臭性と、フィルタで捕集した細菌やウイルスを不活化する機能とを兼ね備える空気清浄機を提供することができる。 According to the present invention, there is provided an air purifier having a higher collection efficiency even in a structure with low pressure loss, and further having a deodorizing property and a function of inactivating bacteria and viruses collected by a filter. Can be provided.
以下、本発明の実施形態について図1、2を用いて詳述する。 Hereinafter, embodiments of the present invention will be described in detail with reference to FIGS.
図1、2は本実施形態の空気清浄機100の模式図である。本実施形態の空気清浄機100は、細菌やウイルスを含む塵埃等の微小な物質を帯電させて捕集する電気集塵型の空気清浄機である。本実施形態の空気清浄機100は空気を吸い込む吸引部と、細菌やウイルスを含む塵埃を捕集、不活化する集塵部Aと、送風手段としてのファン50と、排出部から構成されている。集塵部Aは、放電電極20と、接地電極30と、集塵フィルタ10と、電源40とを有しており、集塵フィルタ10は、放電電極20と接地電極30の間に挟持されている。場合によっては、放電電極20と吸引部との間に髪の毛や糸くずなど、比較的大きなゴミを除去するためのプレフィルタを設置してもよい。なお図1において吸引部は入口側と記載されている部分でもよいし、ダクトなどが接続されてさらに上流側に設けられてもよい。また、排出部も同様であり、図1において出口側と記載されている部分でもよいし、さらに下流側に設けられてもよい。また、図1においては放電電極20などが配置され、塵埃を捕集する空間を形成する筐体を、内部の構成が分かるように透明に記載している。また、図1においては、放電電極20と、集塵フィルタ10と、接地電極30と、は互いに離れて配置されているが、実際には集塵フィルタ10は放電電極20と接地電極30とに直接挟まれて(挟持されて)配置されており、集塵フィルタ10が放電電極20と接地電極30とに接触して挟まれている(挟持されている)方が後述で述べる電界が起きやすく、集塵フィルタ10がエレクトレット化されやすいため好ましい。 1 and 2 are schematic views of the air cleaner 100 of the present embodiment. The air cleaner 100 of the present embodiment is an electric dust collection type air cleaner that charges and collects minute substances such as dust containing bacteria and viruses. The air cleaner 100 according to the present embodiment includes a suction unit that sucks air, a dust collection unit A that collects and inactivates dust containing bacteria and viruses, a fan 50 as a blowing unit, and a discharge unit. . The dust collection part A has a discharge electrode 20, a ground electrode 30, a dust collection filter 10, and a power supply 40, and the dust collection filter 10 is sandwiched between the discharge electrode 20 and the ground electrode 30. Yes. In some cases, a prefilter for removing relatively large dust such as hair and lint may be provided between the discharge electrode 20 and the suction portion. In FIG. 1, the suction portion may be a portion described as the inlet side, or may be provided further upstream by connecting a duct or the like. Moreover, the discharge part is the same, and the part described as the exit side in FIG. 1 may be sufficient, and it may be provided further downstream. Further, in FIG. 1, the casing in which the discharge electrode 20 and the like are arranged and forms a space for collecting dust is described transparently so that the internal configuration can be understood. Further, in FIG. 1, the discharge electrode 20, the dust collection filter 10, and the ground electrode 30 are arranged apart from each other, but actually the dust collection filter 10 is connected to the discharge electrode 20 and the ground electrode 30. The electric field described later is more likely to occur when the dust collection filter 10 is sandwiched (clamped) in contact with the discharge electrode 20 and the ground electrode 30 because the dust collection filter 10 is disposed between the discharge electrode 20 and the ground electrode 30. The dust collection filter 10 is preferable because it is easily electretized.
本実施形態の空気清浄機100は、ファン50などの動作により吸引部から空気を取り込み、取り込まれた空気は本体内に送り込まれる。放電電極20、接地電極30は通気流方向と直行する方向に伸び、かつ互いに平行に並んでいる。放電電極20の通気方向下流側には集塵フィルタ10が設置されており、さらにその通気方向下流側に接地電極30が設置されている。 The air cleaner 100 of this embodiment takes in air from a suction part by operation | movement of the fan 50 etc., and the taken-in air is sent in in a main body. The discharge electrode 20 and the ground electrode 30 extend in a direction perpendicular to the air flow direction and are arranged in parallel to each other. A dust collection filter 10 is installed downstream of the discharge electrode 20 in the ventilation direction, and a ground electrode 30 is installed downstream of the ventilation direction.
集塵部Aは、細菌やウイルスや塵埃などの微小な物質(以下、本実施形態において「塵埃」には、ちりやほこり以外に、細菌やウイルスが含まれるものも含むものとする。)を吸着して捕集するとともに、細菌やウイルスを不活化し、さらに、においの原因のガスも吸着して消臭することができる。 The dust collection part A adsorbs minute substances such as bacteria, viruses, and dust (hereinafter, “dust” in this embodiment includes those containing bacteria and viruses in addition to dust and dust). In addition, it can inactivate bacteria and viruses, and can adsorb and deodorize gases that cause odors.
具体的には、まず電源40(高圧電源)によって、放電電極20に電圧を印加することで放電電極20と接地電極30間に電界が生じる。この電界が生じている電極間に集塵フィルタ10を設置することで集塵フィルタ10を構成する繊維が分極しエレクトレット化されるため、通過する塵埃が静電的に吸着捕集される。なお高圧電源40より印加させる直流高電圧の極性はプラスまたはマイナスのどちらでもよい。 Specifically, an electric field is generated between the discharge electrode 20 and the ground electrode 30 by first applying a voltage to the discharge electrode 20 by the power source 40 (high voltage power source). By installing the dust collection filter 10 between the electrodes in which the electric field is generated, the fibers constituting the dust collection filter 10 are polarized and electretized, so that the passing dust is electrostatically adsorbed and collected. Note that the polarity of the DC high voltage applied from the high-voltage power supply 40 may be positive or negative.
また後述のように、集塵フィルタ10の表面には金属イオンが固定されているため、集塵フィルタ10に捕集された細菌やウイルスは該金属イオンの作用により不活化される。また、集塵フィルタ10の表面に消臭性を有する官能基(以下、消臭性官能基とする)が導入されているため、吸引されて集塵部Aに導入される空気中に存在するアンモニアガスなどの悪臭成分は該官能基に吸着され消臭される。 As will be described later, since metal ions are fixed on the surface of the dust collection filter 10, bacteria and viruses collected by the dust collection filter 10 are inactivated by the action of the metal ions. Further, since a functional group having a deodorizing property (hereinafter referred to as a “deodorizing functional group”) is introduced on the surface of the dust collection filter 10, it exists in the air sucked and introduced into the dust collecting part A. Malodorous components such as ammonia gas are adsorbed on the functional group and deodorized.
以上のように、本実施形態の集塵フィルタ10は帯電しているため、HEPAフィルタのように目開きの小さいものでなくても、細菌やウイルスなど、非常に小さいものでも電気的に捕集することができる。なお、上記構成(放電電極20及び接地電極30、集塵フィルタ10)の集塵部Aにおいて、少なくとも集塵フィルタ10がプリーツ加工されたものでもよい。プリーツ加工により、フィルタ面積が増大するため、集塵部の面風速が低下し、集塵性能が向上すると共に、消臭性も向上させることができる。 As described above, since the dust collection filter 10 of the present embodiment is charged, even if it is not a small opening such as a HEPA filter, it is electrically collected even if it is very small such as bacteria or viruses. can do. In addition, in the dust collection part A of the said structure (the discharge electrode 20, the ground electrode 30, and the dust collection filter 10), at least the dust collection filter 10 may be pleated. Since the filter area is increased by the pleating process, the surface wind speed of the dust collecting portion is reduced, the dust collecting performance is improved, and the deodorizing property can be improved.
本実施形態の空気清浄機100に用いた集塵フィルタ10において不活性化できるウイルスについては特に限定されず、ゲノムの種類や、エンベロープの有無等に係ることなく、様々なウイルスを不活化することができる。例えば、ライノウイルス・ポリオウイルス・口蹄疫ウイルス・ロタウイルス・ノロウイルス・エンテロウイルス・ヘパトウイルス・アストロウイルス・サポウイルス・E型肝炎ウイルス・A型、B型、C型インフルエンザウイルス・パラインフルエンザウイルス・ムンプスウイルス(おたふくかぜ)・麻疹ウイルス・ヒトメタニューモウイルス・RSウイルス・ニパウイルス・ヘンドラウイルス・黄熱ウイルス・デングウイルス・日本脳炎ウイルス・ウエストナイルウイルス・B型、C型肝炎ウイルス・東部および西部馬脳炎ウイルス・オニョンニョンウイルス・風疹ウイルス・ラッサウイルス・フニンウイルス・マチュポウイルス・グアナリトウイルス・サビアウイルス・クリミアコンゴ出血熱ウイルス・スナバエ熱・ハンタウイルス・シンノンブレウイルス・狂犬病ウイルス・エボラウイルス・マーブルグウイルス・コウモリリッサウイルス・ヒトT細胞白血病ウイルス・ヒト免疫不全ウイルス・ヒトコロナウイルス・SARSコロナウイルス・ヒトポルボウイルス・ポリオーマウイルス・ヒトパピローマウイルス・アデノウイルス・ヘルペスウイルス・水痘帯状発疹ウイルス・EBウイルス・サイトメガロウイルス・天然痘ウイルス・サル痘ウイルス・牛痘ウイルス・モラシポックスウイルス・パラポックスウイルスなどを挙げることができる。 The virus that can be inactivated in the dust collection filter 10 used in the air cleaner 100 of the present embodiment is not particularly limited, and it is possible to inactivate various viruses regardless of the type of genome or the presence or absence of an envelope. Can do. For example, rhinovirus, poliovirus, foot-and-mouth disease virus, rotavirus, norovirus, enterovirus, hepatovirus, astrovirus, sapovirus, hepatitis E virus, type A, type B, type C influenza virus, parainfluenza virus, mumps virus (mumps) ) · Measles virus · Human metapneumo virus · RS virus · Nipah virus · Hendra virus · Yellow fever virus · Dengue virus · Japanese encephalitis virus · West Nile virus · Type B, hepatitis C virus · Eastern and western equine encephalitis virus · Onion Nyon virus, rubella virus, Lassa virus, Funin virus, Machupo virus, Guanarito virus, Sabia virus, Crimea congo hemorrhagic fever virus, snubber fever, hantavirus, shin Umbre virus, rabies virus, ebola virus, marburg virus, bat lyssa virus, human T cell leukemia virus, human immunodeficiency virus, human coronavirus, SARS coronavirus, human porvovirus, polyomavirus, human papillomavirus, adenovirus Examples include herpes virus, varicella-zoster rash virus, EB virus, cytomegalovirus, smallpox virus, monkeypox virus, cowpox virus, molasipox virus, and parapox virus.
また本実施形態の空気清浄機100に用いた集塵フィルタ10において不活化できる細菌については、グラム陽性、陰性に関わらず殺菌することができる。例えば、大腸菌、黄色ぶどう球菌、表皮ぶどう球菌、緑膿菌、肺炎桿菌などが挙げられる。 Moreover, about the bacteria which can be inactivated in the dust collection filter 10 used for the air cleaner 100 of this embodiment, it can sterilize irrespective of Gram positive or negative. Examples thereof include Escherichia coli, Staphylococcus aureus, Staphylococcus aureus, Pseudomonas aeruginosa, and Klebsiella pneumoniae.
本実施形態の空気清浄機100で用いる放電電極20は、通気性、導電性があれば特に限定されるものではないが、一例として、金属線や金属の繊維で形成されるメッシュや不織布、ワイヤ、格子状や簾状や突起状の金属製プレート、パンチングされた金属製のプレートやシート、スチールウール、エキスパンドメッシュ、めっきなどで導電性材料を被覆した合繊織編物(不織布も含む)などが挙げられる。また、図2に示すように放電電極20が、針状電極のように鋸刃状の鋭利な先端部を複数有する形態の電極でもよい。針状電極のような形状にすることで、ストリーマ放電が発生し、吸着しきれなかったガスなどを分解してくれるため、より一層の消臭性能が付与できる。 The discharge electrode 20 used in the air cleaner 100 of the present embodiment is not particularly limited as long as it has air permeability and conductivity, but as an example, a mesh or nonwoven fabric formed from a metal wire or metal fiber, a wire , Lattice-like, saddle-like or protruding metal plates, punched metal plates and sheets, steel wool, expanded mesh, synthetic fiber knitted fabrics (including non-woven fabrics) coated with conductive materials such as plating It is done. In addition, as shown in FIG. 2, the discharge electrode 20 may be an electrode having a plurality of sharp edge portions like a saw blade like a needle electrode. By making the shape like a needle-like electrode, streamer discharge is generated and the gas that could not be adsorbed is decomposed, so that further deodorizing performance can be imparted.
接地電極30は、放電電極20と同様、通気性、導電性があれば特に構造や材質等は限定されないが、集塵フィルタ10の全面に均一に電界を発生させる目的のため、金属メッシュやエキスパンドメッシュ、めっきなどで導電性材料を被覆した合繊織編物(不織布も含む)など、平面状のものが好ましい。 As in the case of the discharge electrode 20, the ground electrode 30 is not particularly limited in structure or material as long as it has air permeability and conductivity. However, for the purpose of generating an electric field uniformly on the entire surface of the dust collection filter 10, a metal mesh or an expanded electrode is used. A flat woven or knitted fabric (including non-woven fabric) coated with a conductive material by mesh, plating or the like is preferable.
集塵フィルタ10は、上述のように接地電極30と放電電極20によって形成される電界により帯電し、塵埃を静電気的に吸着させて捕集するフィルタである。本実施形態の空気清浄機100で用いる集塵フィルタ10は、通気性を有する繊維構造体と、繊維構造体表面に存在する消臭性を有する消臭性官能基と、該官能基とイオン結合することにより固定された金属イオンとを有する。 The dust collection filter 10 is a filter that is charged by the electric field formed by the ground electrode 30 and the discharge electrode 20 as described above and electrostatically adsorbs and collects dust. The dust collection filter 10 used in the air cleaner 100 of the present embodiment includes a fiber structure having air permeability, a deodorant functional group having a deodorizing property present on the surface of the fiber structure, and an ion bond with the functional group. And having fixed metal ions.
繊維構造体を構成する材料としては、繊維構造体を形成する繊維は、ポリマーで構成される繊維あるいは表面の少なくとも一部がポリマーである繊維であればよい。具体的には、各種樹脂や、合成繊維や、綿、麻、絹等の天然繊維や、天然繊維から得られた和紙などにより構成されたものが挙げられる。 As a material constituting the fiber structure, the fiber forming the fiber structure may be a fiber composed of a polymer or a fiber in which at least a part of the surface is a polymer. Specific examples include various resins, synthetic fibers, natural fibers such as cotton, hemp, and silk, and Japanese paper obtained from natural fibers.
より具体的には、ポリエチレン樹脂、ポリプロピレン樹脂、ポリスチレン樹脂、ABS樹脂、AS樹脂、EVA樹脂、ポリメチルペンテン樹脂、ポリ塩化ビニル樹脂、ポリ塩化ビニリデン樹脂、ポリアクリル酸メチル樹脂、ポリ酢酸ビニル樹脂、ポリアミド樹脂、ポリイミド樹脂、ポリカーボネート樹脂、ポリエチレンテレフタレート樹脂、ポリブチレンテレフタレート樹脂、ポリアセタール樹脂、ポリアリレート樹脂、ポリスルホン樹脂、ポリフッ化ビニリデン樹脂、ベクトラン(登録商標)、PTFE(polytetrafluoroethylene)などの熱可塑性樹脂、ポリ乳酸樹脂、ポリヒドロキシブチレート樹脂、修飾でんぷん樹脂、ポリカプロラクト樹脂、ポリブチレンサクシネート樹脂、ポリブチレンアジペートテレフタレート樹脂、ポリブチレンサクシネートテレフタレート樹脂、ポリエチレンサクシネート樹脂などの生分解性樹脂、フェノール樹脂、ユリア樹脂、メラミン樹脂、不飽和ポリエステル樹脂、ジアリルフタレート樹脂、エポキシ樹脂、エポキシアクリレート樹脂、ケイ素樹脂、アクリルウレタン樹脂、ウレタン樹脂などの熱硬化性樹脂、シリコーン樹脂、ポリスチレンエラストマー、ポリエチレンエラストマー、ポリプロピレンエラストマー、ポリウレタンエラストマーなどのエラストマーおよび漆などの天然樹脂などが挙げられる。 More specifically, polyethylene resin, polypropylene resin, polystyrene resin, ABS resin, AS resin, EVA resin, polymethylpentene resin, polyvinyl chloride resin, polyvinylidene chloride resin, polymethyl acrylate resin, polyvinyl acetate resin, Polyamide resin, polyimide resin, polycarbonate resin, polyethylene terephthalate resin, polybutylene terephthalate resin, polyacetal resin, polyarylate resin, polysulfone resin, polyvinylidene fluoride resin, Vectran (registered trademark), PTFE (polytetrafluoroethylene) and other thermoplastic resins, poly Lactic acid resin, polyhydroxybutyrate resin, modified starch resin, polycaprolacto resin, polybutylene succinate resin, polybutylene adipate terephthalate resin, polybutylene sac Biodegradable resins such as nitrate terephthalate resin and polyethylene succinate resin, phenol resin, urea resin, melamine resin, unsaturated polyester resin, diallyl phthalate resin, epoxy resin, epoxy acrylate resin, silicon resin, acrylic urethane resin, urethane resin, etc. And thermosetting resins, silicone resins, polystyrene elastomers, polyethylene elastomers, polypropylene elastomers, polyurethane elastomers, and other natural resins such as lacquer.
本実施形態の集塵フィルタ10について、より具体的に説明する。該集塵フィルタ10に係る繊維構造体の一例としては、シート状の織物や編物、不織布などとすることができる。また図1、2で示すようにプリーツ状にすることでより捕集効率を上げることができる。織物、編物、不織布を積層させたものでもよい。 The dust collection filter 10 of this embodiment is demonstrated more concretely. As an example of the fiber structure related to the dust collection filter 10, a sheet-like woven fabric, knitted fabric, non-woven fabric, or the like can be used. Moreover, collection efficiency can be raised more by making it into a pleat shape as shown in FIGS. A laminate of a woven fabric, a knitted fabric, or a nonwoven fabric may be used.
次に、集塵フィルタ10が有する消臭性官能基について説明する。集塵フィルタ10は、繊維構造体を構成する繊維の少なくとも一部に消臭性官能基を備える。より具体的には、繊維構造体の繊維の繊維表面の少なくとも一部に消臭性を有する消臭性官能基を備えている。これらの消臭性官能基についてはイオン交換能を有していれば特に限定されるものではないが、スルホン酸基、アミノ基、リン酸基、カルボキシル基などが好適に用いられる。そして、これらの消臭性官能基は、塩基性ガスを吸着する酸性官能基と、酸性ガスを吸着する塩基性官能基の2種に大別される。塩基性ガスを吸着する酸性官能基としては、スルホン酸基、リン酸基、カルボキシル基などが挙げられ、酸性ガスを吸着する塩基性官能基には、アミノ基などが挙げられる。 Next, the deodorant functional group which the dust collection filter 10 has is demonstrated. The dust collection filter 10 includes a deodorizing functional group on at least a part of the fibers constituting the fiber structure. More specifically, at least a part of the fiber surface of the fiber of the fiber structure is provided with a deodorizing functional group having a deodorizing property. These deodorant functional groups are not particularly limited as long as they have ion exchange ability, but sulfonic acid groups, amino groups, phosphoric acid groups, carboxyl groups and the like are preferably used. These deodorant functional groups are roughly classified into two types: acidic functional groups that adsorb basic gas and basic functional groups that adsorb acidic gas. Examples of acidic functional groups that adsorb basic gas include sulfonic acid groups, phosphoric acid groups, and carboxyl groups. Examples of basic functional groups that adsorb acidic gas include amino groups.
これらの消臭性官能基をポリマーを含む繊維構造体(基材)に導入する方法としては、導入したい消臭性官能基を含む物質を基材と接触させる方法が挙げられる。例えばスルホン酸基を導入する場合を例にすると、無水硫酸、濃硫酸、クロロスルホン酸、発煙硫酸、三酸化硫黄、スルファミン酸、亜硫酸ナトリウム、亜硫酸水素ナトリウムまたはこれらを組み合わせたものに接触させる。特に、発煙硫酸、亜硫酸ナトリウムなどが好適に用いられる。接触させる方法については、水溶液については、浸漬や塗布など公知の方法が用いられるが、無水硫酸など気化しやすいものについては、気化したガスと基材を接触させる方法を用いることもできる。 Examples of a method for introducing these deodorant functional groups into a fiber structure (base material) containing a polymer include a method of bringing a substance containing a deodorant functional group to be introduced into contact with the base material. For example, in the case of introducing a sulfonic acid group, it is brought into contact with sulfuric anhydride, concentrated sulfuric acid, chlorosulfonic acid, fuming sulfuric acid, sulfur trioxide, sulfamic acid, sodium sulfite, sodium bisulfite, or a combination thereof. In particular, fuming sulfuric acid, sodium sulfite and the like are preferably used. As for the contact method, a known method such as dipping or coating is used for the aqueous solution. However, for a material that is easily vaporized such as sulfuric anhydride, a method of bringing the vaporized gas into contact with the substrate can also be used.
また、消臭性官能基を繊維構造体に導入する別の方法として、例えば、消臭性官能基を有するモノマーとして、アクリル酸、メタクリル酸、スチレンスルホン酸ナトリウム、メタリルスルホン酸ナトリウム、アリルスルホン酸ナトリウム、ビニルベンジルトリメチルアンモニウムクロライドなどを用いて放射線グラフト重合を行うことにより、繊維構造体に直接、消臭性官能基を導入することもできる。 Further, as another method for introducing a deodorant functional group into a fiber structure, for example, as a monomer having a deodorant functional group, acrylic acid, methacrylic acid, sodium styrenesulfonate, sodium methallylsulfonate, allylsulfone By performing radiation graft polymerization using sodium acid, vinylbenzyltrimethylammonium chloride or the like, a deodorant functional group can be directly introduced into the fiber structure.
また、放射線グラフト重合法による別の方法としては、放射線グラフト重合によってグラフト鎖を導入後に、更に2次反応を行ってグラフト鎖に消臭性官能基を導入することで、繊維構造体に消臭性官能基を導入してもよい。この場合にグラフト重合に用いられるモノマーとしては、アクリロニトリル、アクロレイン、ビニルピリジン、スチレン、クロロメチルスチレン、メタクリル酸グリシジルなどが挙げられる。例えば、メタクリル酸グリシジルを放射線グラフトによって繊維構造体(たとえば不織布基材)に導入し、次に、亜硫酸ナトリウムなどのスルホン化剤を反応させてスルホン酸基を導入することにより、塩基性ガスの消臭性を有する繊維を得ることができる。また、メタクリル酸グリシジルを介して、ジエタノールアミンなどによって4級アンモニウムや3級アミノ基などの酸性ガスを消臭する塩基性官能基を導入することもできる。 Another method by radiation graft polymerization is to introduce a deodorant functional group into the graft chain by introducing a deodorizing functional group into the graft chain after introducing a graft chain by radiation graft polymerization. A functional group may be introduced. In this case, examples of the monomer used for graft polymerization include acrylonitrile, acrolein, vinylpyridine, styrene, chloromethylstyrene, and glycidyl methacrylate. For example, glycidyl methacrylate is introduced into a fiber structure (for example, a nonwoven fabric substrate) by radiation grafting, and then a sulfonating agent such as sodium sulfite is reacted to introduce a sulfonic acid group, thereby eliminating the basic gas. A fiber having odor properties can be obtained. In addition, a basic functional group capable of deodorizing acidic gases such as quaternary ammonium and tertiary amino groups can be introduced through glycidyl methacrylate with diethanolamine or the like.
なお、本実施形態の集塵フィルタ10を構成する繊維構造体と、消臭性官能基を含む物質を接触させる前に、つまり、消臭性官能基導入処理の前処理として、α、γ、β線などの放射線や、電子線、紫外線、コロナ放電、プラズマ照射などにより、基材表面のポリマー部にラジカルを発生させてもよい。ラジカルを発生させることにより、消臭性官能基とラジカルが化学結合し、消臭性官能基が導入し難い樹脂の劣化を抑制しつつ容易に消臭性官能基が導入でき、且つ、より強固に消臭性官能基を固定できたり、消臭性官能基を導入したい部分にのみ、導入できるようになるなどのメリットがある。 In addition, before contacting the fiber structure which comprises the dust collection filter 10 of this embodiment, and the substance containing a deodorant functional group, ie, as a pre-process of a deodorant functional group introduction process, (alpha), (gamma), Radicals may be generated in the polymer portion of the substrate surface by radiation such as β rays, electron beam, ultraviolet rays, corona discharge, plasma irradiation, or the like. By generating radicals, the deodorant functional group and the radical are chemically bonded, and the deodorant functional group can be easily introduced while suppressing the deterioration of the resin, which is difficult to introduce the deodorant functional group, and more robust. There are merits such that the deodorant functional group can be fixed to the surface, or the deodorant functional group can be introduced only into the portion where the deodorant functional group is desired to be introduced.
この際、本実施形態の集塵フィルタ10を構成する繊維構造体として用いる事のできる物質は、上述の樹脂であれば限定はされないが、ポリエチレン、ポリプロピレン、ポリスチレン、ポリカーボネート、ポリエステル、ポリアミド、ポリアセタール、ポリ塩化ビニル、ポリ塩化ビニリデン、ポリフッ化ビニリデン、ポリアクリル酸、ポリメチルメタアクリレート、ポリウレタン、ABS、SBC、ラテックスなどが挙げられる。 At this time, the material that can be used as the fiber structure constituting the dust collection filter 10 of the present embodiment is not limited as long as it is the resin described above, but polyethylene, polypropylene, polystyrene, polycarbonate, polyester, polyamide, polyacetal, Examples include polyvinyl chloride, polyvinylidene chloride, polyvinylidene fluoride, polyacrylic acid, polymethyl methacrylate, polyurethane, ABS, SBC, and latex.
以下、繊維構造体にラジカルを生成させる方法について詳述する。 Hereinafter, a method for generating radicals in the fiber structure will be described in detail.
繊維構造体にラジカルを生成させる方法としては、窒素、アルゴン、ヘリウムガスなどの不活性ガス中で、基材へ、α線や、β線や、γ線や、電子線を照射する方法(放射線照射法)や、紫外線を照射する方法(紫外線(UV)法)、または、コロナ放電を照射する方法(コロナ放電法)や、グロー放電により発生するプラズマを照射する方法(プラズマ法)、あるいは、これらを組み合わせた方法などを挙げることができる。本発明では、特に、電子線やコロナ放電を照射する放射線照射法やコロナ放電法が適している。 As a method for generating radicals in the fiber structure, a method of irradiating the substrate with α-rays, β-rays, γ-rays, or electron beams in an inert gas such as nitrogen, argon, or helium (radiation) Irradiation method), ultraviolet irradiation method (ultraviolet (UV) method), corona discharge irradiation method (corona discharge method), plasma discharge generated by glow discharge (plasma method), or The method which combined these etc. can be mentioned. In the present invention, a radiation irradiation method or a corona discharge method for irradiating an electron beam or a corona discharge is particularly suitable.
また、繊維構造体にラジカルを生成させる方法として、基材をイソプロピルアルコール(IPA)などのアルコール類に含浸させた状態で、α線や、β線や、γ線や、電子線や、紫外線を基材へ照射する方法、または、コロナ放電を照射する方法や、グロー放電により発生するプラズマを照射する方法を用いても良い。 As a method of generating radicals in the fiber structure, α-rays, β-rays, γ-rays, electron beams, and ultraviolet rays are used in a state where the base material is impregnated with an alcohol such as isopropyl alcohol (IPA). A method of irradiating the substrate, a method of irradiating corona discharge, or a method of irradiating plasma generated by glow discharge may be used.
また、UV法の光開始剤としてはベンゾフェノン、アントラキノンなどがある。光開始剤が吸収した光のエネルギーが、ポリマーへ移動してラジカルを作る場合と、光開始剤ラジカルがポリマーの水素を引き抜いて、ポリマーにラジカルを作る場合とがある。プラズマ法では、プラズマ中の電子がポリマーにラジカルをつくる場合と、ラジカルを酸素と反応させて過酸化ラジカルとする方法とがある。UV法とプラズマ法とコロナ放電法の特徴は基材の表面近傍のみに限定される。 Examples of UV photoinitiators include benzophenone and anthraquinone. There are a case where the energy of light absorbed by the photoinitiator moves to the polymer to create a radical, and a case where the photoinitiator radical abstracts the hydrogen of the polymer to create a radical in the polymer. In the plasma method, there are a method in which electrons in plasma form radicals in the polymer and a method in which radicals are reacted with oxygen to form peroxide radicals. The characteristics of the UV method, the plasma method, and the corona discharge method are limited to the vicinity of the surface of the substrate.
基材にラジカルを生成させる方法には、上述した放射線照射法や紫外線法(UV法)やコロナ放電法、プラズマ法などに加えて化学開始剤法がある。化学開始剤法には、連鎖移動法、乳化重合法、セリウム塩法などがある。連鎖移動法では、過酸化ベンゾイルのような過酸化物やアゾイソブチロニトリル(AIBN)などが化学開始剤として使用されている。 Methods for generating radicals on the substrate include chemical initiator methods in addition to the radiation irradiation method, ultraviolet method (UV method), corona discharge method, and plasma method described above. Examples of the chemical initiator method include a chain transfer method, an emulsion polymerization method, and a cerium salt method. In the chain transfer method, peroxides such as benzoyl peroxide, azoisobutyronitrile (AIBN), and the like are used as chemical initiators.
本実施形態の放射線照射法には、同時照射法と前照射法がある。同時照射法はポリマーと反応物質の共存下で照射する方法で、前照射法は捕捉ラジカル法ともいわれ、放射線照射してラジカル生成後から反応物質と接触させる方法である。放射線照射法の特徴としては、あらゆる形状のポリマーに活用でき、ポリマー内部までラジカルを生成させることができ、開始剤等の残存がない、大量生産できる等が挙げられる。 The radiation irradiation method of the present embodiment includes a simultaneous irradiation method and a pre-irradiation method. The simultaneous irradiation method is a method of irradiating in the coexistence of a polymer and a reactant, and the pre-irradiation method is also called a trapping radical method, and is a method of contacting a reactant after generating a radical by irradiation with radiation. The characteristics of the radiation irradiation method include that it can be used for polymers of all shapes, radicals can be generated up to the inside of the polymer, no initiator remains, and mass production is possible.
本実施形態では、目的、用途に応じて、ラジカル生成方法として、放射線照射法、UV法、プラズマ法、及び、コロナ放電法を適宜選択すれば良い。 In the present embodiment, a radiation irradiation method, a UV method, a plasma method, and a corona discharge method may be appropriately selected as a radical generation method according to the purpose and application.
本実施形態の空気清浄機100に用いられる集塵フィルタ10を構成する繊維構造体に放射線を照射する方法において、電離放射線の照射線量は、消臭性官能基を導入させるのに十分なラジカルの生成量が得られ、不必要な架橋や部分的な分解が起こらない経済的な照射線量であれば特に制限はないが、ラジカルが均一に生成し、本発明の集塵フィルタを構成する基材の剛性や耐薬品性に及ぼす影響も少ないことから、1kGy〜1000kGyの範囲にあることが好ましく、5kGy〜500kGyの範囲にあることがより好ましく、10kGy〜300kGyの範囲にあることが特に好ましい。 In the method of irradiating the fiber structure constituting the dust collection filter 10 used in the air cleaner 100 of this embodiment, the irradiation dose of ionizing radiation is a radical sufficient to introduce a deodorant functional group. There is no particular limitation as long as it is an economical irradiation dose with which the amount produced is obtained and unnecessary crosslinking or partial decomposition does not occur. However, the radicals are uniformly generated, and the substrate constituting the dust collection filter of the present invention Since it has little influence on the rigidity and chemical resistance, it is preferably in the range of 1 kGy to 1000 kGy, more preferably in the range of 5 kGy to 500 kGy, and particularly preferably in the range of 10 kGy to 300 kGy.
上述のラジカル生成方法により生成されるラジカルについてはポリエチレンでは多くの報告があり、電子線の照射によってアルキル、アリル、ポリエニル、過酸化ラジカルが生成する。ラジカルは結晶部と非晶部に生成するが、分子鎖の運動が激しい非晶部では、ただちに再結合等の反応で消滅する。観察されるのは結晶部内のラジカルである。アルキルラジカルは反応性がきわめて高く、水素を引き抜きながら結晶部を移動し、非晶部で再結合(橋かけ)や酸化反応、グラフト反応で消費される。 There are many reports on radicals generated by the above-described radical generation method in polyethylene, and alkyl, allyl, polyenyl, and peroxide radicals are generated by electron beam irradiation. Radicals are generated in the crystal part and the amorphous part, but in the amorphous part where the movement of the molecular chain is intense, it immediately disappears by a reaction such as recombination. Observed are radicals in the crystal part. Alkyl radicals are extremely reactive, move through the crystal part while extracting hydrogen, and are consumed by recombination (crosslinking), oxidation reaction, and graft reaction in the amorphous part.
ポリマーラジカルは放射線の直接一次作用と、入射した放射線ではじき出された電子による二次作用で生成するので、入射放射線の飛跡に沿ってラジカルが群をなして生成する。一つの群の大きさは数nm程度であり、この群の中でラジカルの再結合が起こる。また、生成したラジカルは水素による付加と引き抜き反応によって、分子間あるいは分子内を移動し結合相手のラジカルを探す。結晶部内ではポリマーの運動が制限されているため反応は起きにくいが、結晶部内に生成したラジカルは分子鎖が自由に運動できる非晶部に移動して反応に参画する。 Since polymer radicals are generated by a direct primary action of radiation and a secondary action by electrons ejected by incident radiation, radicals form in groups along the track of incident radiation. The size of one group is about several nm, and radical recombination occurs in this group. In addition, the generated radicals move between molecules or inside molecules by addition and extraction reactions with hydrogen, and search for radicals as binding partners. The reaction is unlikely to occur in the crystal part because the movement of the polymer is limited, but the radicals generated in the crystal part move to the amorphous part where the molecular chain can move freely and participate in the reaction.
本実施形態において、繊維構造体への放射線照射直後、例えば1〜2分以内に、消臭性官能基を導入するような場合には、放射線を照射する際の温度および、照射後に基材を保存する温度については特に制限はない。しかし、ラジカルを生成した後、時間をおいて消臭性官能基を導入する場合などにはラジカルを保存するために、照射も保存も低温で行うことが望ましい。−5℃程度に低温保存すれば、照射20日経過後でも支障なくポリマーラジカルを用いた反応が可能である。 In this embodiment, immediately after irradiation of radiation to the fiber structure, for example, in the case of introducing the deodorant functional group within 1 to 2 minutes, the temperature at the time of irradiation and the substrate after irradiation There is no particular limitation on the storage temperature. However, when a deodorant functional group is introduced after a period of time after generating radicals, it is desirable to perform irradiation and storage at a low temperature in order to preserve the radicals. If stored at a low temperature of about −5 ° C., a reaction using polymer radicals can be performed without any problem even after 20 days of irradiation.
上述のように、繊維構造体表面にラジカルを発生させた後、消臭性官能基を含む物質を接触させ、再度、α、γ、β線などの放射線や、紫外線、電子線などを照射することで、消臭性官能基が、モノマーを介して繊維構造体を構成する繊維表面に導入されることとなる。 As described above, after generating radicals on the surface of the fiber structure, a substance containing a deodorant functional group is brought into contact, and again irradiated with radiation such as α, γ, β rays, ultraviolet rays, electron beams, etc. By this, a deodorant functional group will be introduce | transduced into the fiber surface which comprises a fiber structure via a monomer.
本実施形態の空気清浄機100に用いられる集塵フィルタ10は、さらに殺菌効果と抗ウイルス効果の少なくとも一方を有する成分として少なくとも1種の金属イオンを含むことを特徴とする。本実施形態では、金属イオンは上述の酸性の消臭性官能基(塩基性ガスを消臭する消臭性を有する官能基)の場合は、該酸性の消臭性官能基が持つイオン交換能により金属イオンを結合することができ、繊維構造体に導入された消臭性官能基のうちの一部の消臭性官能基に金属イオンが結合していることが好ましい。また、塩基性の消臭性官能基(酸性ガスを消臭する消臭性を有する官能基)の場合は、塩化金酸のようなアニオン性の金属錯体(錯イオン)を用いる事で金属イオンをイオン結合させることができる。このように繊維構造体に導入された消臭性官能基の一部に細菌とウイルス少なくともいずれかを不活化する金属イオンが導入されることにより、当該繊維構造体によって構成される集塵フィルタ10は、消臭機能と細菌及び/又はウイルスの不活化機能との両方を兼ね備えることができる。従って、本実施形態の空気清浄機100は、集塵フィルタ10で捕集した細菌及び/又はウイルスの不活化機能と消臭機能の両方を効率よく実現することができる。導入方法は、上述の方法にて繊維構造体を構成する繊維表面に、消臭性官能基が導入されているので、目的の金属イオンを含む化合物と繊維構造体とを接触させるだけでよい。具体的には、目的の金属イオンを含む化合物の濃度を調整することで、消臭性官能基と結合する金属イオンの量を自由に制御することができるので、用途に応じたレベルの消臭性と殺菌抗ウイルス性を備えた集塵フィルタ10を提供できる。 The dust collection filter 10 used in the air cleaner 100 of the present embodiment further includes at least one metal ion as a component having at least one of a bactericidal effect and an antiviral effect. In the present embodiment, when the metal ion is the above-described acidic deodorant functional group (functional group having a deodorizing property that deodorizes basic gas), the ion exchange ability of the acidic deodorant functional group It is preferable that the metal ions can be bonded to each other, and the metal ions are bonded to some of the deodorant functional groups introduced into the fiber structure. In the case of a basic deodorant functional group (functional group having a deodorizing property for deodorizing acidic gas), an anionic metal complex (complex ion) such as chloroauric acid is used to form a metal ion. Can be ionically bonded. In this way, by introducing metal ions that inactivate at least one of bacteria and viruses into a part of the deodorant functional group introduced into the fiber structure, the dust collection filter 10 constituted by the fiber structure. Can have both a deodorizing function and a bacteria and / or virus inactivating function. Therefore, the air cleaner 100 of the present embodiment can efficiently realize both the inactivation function and the deodorization function of bacteria and / or viruses collected by the dust collection filter 10. As the introduction method, since the deodorizing functional group is introduced on the surface of the fiber constituting the fiber structure by the above-described method, it is only necessary to bring the compound containing the target metal ion into contact with the fiber structure. Specifically, by adjusting the concentration of the compound containing the target metal ion, the amount of metal ion that binds to the deodorant functional group can be freely controlled. The dust collection filter 10 provided with the property and bactericidal antiviral property can be provided.
一方、金属イオンを基材に固定する方法としては、ゼオライトや活性炭などの無機多孔質体に金属イオンを吸着担持させ、それから基材に固定することで、消臭性と殺菌抗ウイルス性を発揮させる方法や、フタロシアニンなどの金属錯体を基材に塗布し、消臭性を付与する方法が開発されているが、無機多孔質を用いる場合は基材からの脱離が問題となり、フタロシアニンを用いる場合は、着色などの問題や、イオン交換と比較すると消臭スピードが遅いなどの問題が生じる。また殺菌・抗ウイルス効果もないため、消臭と殺菌・抗ウイルス効果の両方の機能を付与したい場合は別の機能性材料を併用する必要がある。さらに、上述のような無機多孔質を用いる方法や金属錯体を用いる方法で金属イオンを結合する方法では、消臭性と殺菌・抗ウイルス性のバランスを用途に応じて制御するのが難しい。しかし本実施形態のように消臭性官能基を繊維構造体に導入し、さらに導入された消臭性官能基の一部に金属イオンを結合した構造とすることによって、消臭性と殺菌・抗ウイルス性の両方を効率良く達成することができるという効果が得られる。さらに、上述のように、繊維構造体に導入された消臭性官能基と金属イオンとを接触させるだけで金属イオンを繊維構造体に結合できるので、接触させる金属イオンの濃度を調整することで消臭性と殺菌・抗ウイルス性のバランスを簡単に制御できるので、用途に応じた設計も容易である。 On the other hand, as a method of fixing metal ions to the base material, the metal ions are adsorbed and supported on an inorganic porous material such as zeolite or activated carbon, and then fixed to the base material, thereby exhibiting deodorant and bactericidal antiviral properties. And a method of applying a metal complex such as phthalocyanine to a substrate and imparting deodorizing properties have been developed. However, when an inorganic porous material is used, detachment from the substrate becomes a problem, and phthalocyanine is used. In such a case, problems such as coloring and problems such as a slow deodorizing speed occur compared to ion exchange. Moreover, since there is no bactericidal / antiviral effect, it is necessary to use another functional material in combination when it is desired to give both functions of deodorizing and bactericidal / antiviral effects. Furthermore, it is difficult to control the balance between the deodorizing property and the bactericidal / antiviral properties according to the application in the method using inorganic porous or the method using metal complex to bind metal ions as described above. However, by introducing a deodorant functional group into the fiber structure as in this embodiment, and further having a structure in which a metal ion is bonded to a part of the introduced deodorant functional group, the deodorization and sterilization The effect that both antiviral properties can be achieved efficiently is obtained. Furthermore, as described above, the metal ion can be bound to the fiber structure simply by bringing the deodorant functional group introduced into the fiber structure into contact with the metal ion, so the concentration of the metal ion to be contacted can be adjusted. Since the balance between deodorant and bactericidal / antiviral properties can be easily controlled, it is easy to design according to the application.
具体的な殺菌効果や抗ウイルス性効果を有する金属イオンとしては、Ag、Zn、Cu、Co、Ni、Al、Pt、Au、Pd、Snなどが挙げられ、それぞれの目的に応じて1種あるいは2種以上を組合せて用いる事ができる。特にZnを用いると、フィルタの変色などが抑えられるため好ましい。 Specific examples of the metal ion having a bactericidal effect or an antiviral effect include Ag, Zn, Cu, Co, Ni, Al, Pt, Au, Pd, and Sn. Two or more types can be used in combination. In particular, use of Zn is preferable because discoloration of the filter can be suppressed.
本実施形態の空気清浄機100に用いられる集塵フィルタ10は、さらに、塩基性ガスを吸着する無機微粒子および/または酸性ガスを吸着する無機微粒子を含んでもよい。この無機微粒子が集塵フィルタ10に固定されることで、さらに消臭効果を向上させることができる。たとえば、フィルタの基材として上述の消臭性官能基が導入し難い材質を用いる場合などでも、必要な消臭性能を有する無機微粒子を固定することで、十分な消臭性能を確保できる。 The dust collection filter 10 used in the air cleaner 100 of the present embodiment may further include inorganic fine particles that adsorb basic gas and / or inorganic fine particles that adsorb acid gas. By fixing the inorganic fine particles to the dust collecting filter 10, the deodorizing effect can be further improved. For example, even when the above-described material that is difficult to introduce the deodorant functional group is used as the base material of the filter, sufficient deodorization performance can be secured by fixing inorganic fine particles having the necessary deodorization performance.
具体的に、塩基性ガスを吸着する無機微粒子として、シリカが挙げられ、酸性ガスを吸着する無機微粒子として、酸化チタン、酸化ジルコニウム、酸化アルミニウム、酸化マグネシウムなどが挙げられる。また上述のように、無機微粒子の表面に塩基性ガスや酸性ガスの吸着能を有する官能基を固定して、塩基性ガスや酸性ガスの吸着能が付与された無機微粒子も使用できる。官能基を有する場合は無機微粒子自体はガス吸着能を有していなくても、有していてもよい。本実施形態における酸性ガス/塩基性ガス吸着特性を有する無機微粒子とは、このような無機微粒子の表面に酸性ガスや塩基性ガスを吸着する官能基を導入したものも含む概念である。 Specifically, the inorganic fine particles that adsorb the basic gas include silica, and the inorganic fine particles that adsorb the acidic gas include titanium oxide, zirconium oxide, aluminum oxide, magnesium oxide, and the like. In addition, as described above, inorganic fine particles provided with a basic gas or acidic gas adsorbing ability by fixing a functional group capable of adsorbing basic gas or acidic gas on the surface of the inorganic fine particles can also be used. In the case of having a functional group, the inorganic fine particles themselves may or may not have a gas adsorbing ability. The inorganic fine particles having acidic gas / basic gas adsorption characteristics in the present embodiment are concepts including those in which a functional group that adsorbs acidic gas or basic gas is introduced on the surface of such inorganic fine particles.
以上に説明した本実施形態の無機微粒子は上述の消臭性官能基を集塵フィルタ10の繊維構造体に導入する前に固定してもよいし、消臭性官能基を繊維構造体に導入した後に導入してもよいが、固定するためのバインダーなどで消臭性官能基が覆われてしまうなどの場合は、消臭性官能基を導入する前に固定するのが好ましい。 The inorganic fine particles of the present embodiment described above may be fixed before the deodorant functional group described above is introduced into the fiber structure of the dust collection filter 10, or the deodorant functional group is introduced into the fiber structure. However, when the deodorant functional group is covered with a binder for fixing, it is preferable to fix before introducing the deodorant functional group.
本実施形態の空気清浄機100に用いられる集塵フィルタ10に用いる塩基性ガスや酸性ガスを吸着する無機微粒子は公知のバインダーを用いて固定することができるが、ガスとの接触効率などを考慮すると、少量でも強固に基材と固定できる不飽和結合部を有するシランモノマーを用いた放射線グラフト重合による固定方法が最も好適である。これらの不飽和結合部を有するシランモノマーは、該シランモノマーが有するシラノール基と無機微粒子表面を還流などの方法により無機微粒子の表面に脱水縮合反応により化学結合(共有結合)を形成して結合させることができ、さらに、該シランモノマーが有する不飽和結合部や反応性官能基とが、グラフト重合により化学結合(共有結合)することにより基材上に固定される。 The inorganic fine particles that adsorb the basic gas and the acid gas used in the dust filter 10 used in the air cleaner 100 of the present embodiment can be fixed using a known binder, but the contact efficiency with the gas is taken into consideration. Then, the fixing method by radiation graft polymerization using the silane monomer which has an unsaturated bond part which can be firmly fixed to a base material even in a small amount is most preferable. These silane monomers having an unsaturated bond portion are bonded by forming a chemical bond (covalent bond) on the surface of the inorganic fine particles by a dehydration condensation reaction between the silanol groups of the silane monomer and the surface of the fine inorganic particles by a method such as reflux. Furthermore, the unsaturated bond part and the reactive functional group of the silane monomer are fixed on the substrate by chemical bonding (covalent bonding) by graft polymerization.
不飽和結合部を有するシランモノマーとしては、ビニル基、エポキシ基、スチリル基、メタクリロ基、アクリロキシ基、イソシアネート基、チオール基などの不飽和結合部や反応性官能基を有するものが挙げられる。具体的には、ビニルトリメトキシシラン、ビニルトリエトキシシラン、ビニルトリアセトキシシラン、N−β−(N−ビニルベンジルアミノエチル)−γ−アミノプロピルトリメトキシシランや、N−(ビニルベンジル)−2−アミノエチル−3−アミノプロピルトリメトキシシランの塩酸塩、2−(3、4エポキシシクロヘキシル)エチルトリメトキシシラン、3−グリシドキシプロピルトリメトキシシラン、3−グリシドキシプロピルメチルジエトキシシラン、3−グリシドキシプロピルトリエトキシシラン、p−スチリルトリメトキシシラン、3−メタクリロキシプロピルメチルジメトキシシラン、3−メタクリロキシプロピルトリメトキシシラン、3−メタクリロキシプロピルメチルジエトキシシラン、3−メタクリロキシプロピルトリエトキシシラン、3−アクリロキシプロピルトリメトキシシラン、3−イソシアネートプロピルトリエトキシシラン、Si(OR1)4(式中、R1は炭素数1〜4のアルキル基を示す)で示されるアルコキシシラン化合物、例えば、テトラメトキシシラン、テトラエトキシシランや、R2XSi(OR3)n(式中、R2は炭素数1〜6の炭化水素基、R3は炭素数1〜4のアルキル基、Xは(4−n)であり、nは1〜3の整数を示す)で示されるアルコキシシラン化合物、例えば、メチルトリメトキシシラン、メチルトリエトキシシラン、ジメチルジエトキシシラン、フェニルトリエトキシシラン、ヘキシルトリメトキシシランや、ヘキサメチルジシラザンなどが挙げられる。Examples of the silane monomer having an unsaturated bond include those having an unsaturated bond or a reactive functional group such as a vinyl group, an epoxy group, a styryl group, a methacrylo group, an acryloxy group, an isocyanate group, and a thiol group. Specifically, vinyltrimethoxysilane, vinyltriethoxysilane, vinyltriacetoxysilane, N-β- (N-vinylbenzylaminoethyl) -γ-aminopropyltrimethoxysilane, N- (vinylbenzyl) -2 -Hydrochloride of aminoethyl-3-aminopropyltrimethoxysilane, 2- (3,4 epoxy cyclohexyl) ethyltrimethoxysilane, 3-glycidoxypropyltrimethoxysilane, 3-glycidoxypropylmethyldiethoxysilane, 3-glycidoxypropyltriethoxysilane, p-styryltrimethoxysilane, 3-methacryloxypropylmethyldimethoxysilane, 3-methacryloxypropyltrimethoxysilane, 3-methacryloxypropylmethyldiethoxysilane, 3-methacryloxypropyl G An alkoxysilane compound represented by reethoxysilane, 3-acryloxypropyltrimethoxysilane, 3-isocyanatopropyltriethoxysilane, Si (OR1) 4 (wherein R1 represents an alkyl group having 1 to 4 carbon atoms), for example, tetramethoxysilane, and tetraethoxysilane, R2 X Si (oR @ 3) n (wherein R2 is a hydrocarbon group having 1 to 6 carbon atoms, R3 is an alkyl group having 1 to 4 carbon atoms, X is (4- n), where n represents an integer of 1 to 3, for example, methyltrimethoxysilane, methyltriethoxysilane, dimethyldiethoxysilane, phenyltriethoxysilane, hexyltrimethoxysilane, And hexamethyldisilazane.
塩基性ガスや酸性ガスを吸着する無機微粒子は、基材である繊維構造体の表面に固定するだけではなく、繊維構造体の内部に固定されてもよい。たとえば、基材となる繊維構造体に不織布を用いる場合、不織布の製造工程中に無機微粒子を噴霧することで、糸と共に交絡させて固定されていてもよい。このような塩基性ガスや酸性ガスを吸着する無機微粒子を内部に固定した不織布を用いることで、不織布の表面部分に無機微粒子を固定しなくてもよいため、消臭性官能基を導入する面積を不織布の表面部分においてより多く確保できるため好ましい。 The inorganic fine particles that adsorb basic gas or acidic gas may be fixed not only on the surface of the fiber structure as a base material but also inside the fiber structure. For example, when using a nonwoven fabric for the fiber structure used as a base material, it may be entangled and fixed together with the yarn by spraying inorganic fine particles during the manufacturing process of the nonwoven fabric. By using a non-woven fabric in which inorganic fine particles that adsorb such basic gas or acid gas are fixed, it is not necessary to fix the inorganic fine particles on the surface portion of the non-woven fabric. Is more preferable in the surface portion of the nonwoven fabric.
以上の本実施形態の空気清浄機100に用いる消臭性、殺菌・抗ウイルス性を有する集塵フィルタ10は、単層で用いるほか、目的にあわせて複数(2層以上)の積層体として用いる事もできる。 The dust collection filter 10 having deodorizing properties and sterilization / antiviral properties used in the air cleaner 100 of the present embodiment described above is used as a single layer or a plurality of (two or more layers) laminated bodies according to the purpose. You can also do things.
本実施形態の集塵フィルタ10を単層で用いる場合、集塵フィルタ10に塩基性ガスを吸着する酸性の消臭性官能基と、酸性ガスを吸着する塩基性の消臭性官能基の両方を導入してもよい。酸性ガスと塩基性ガスの両方の消臭性官能基を導入すれば、フィルタが単層であっても両方のガスについて消臭できる。当該両方の消臭性官能基を導入する場合には、たとえばフィルタの片面側に塩基性ガスを吸着する酸性の消臭性官能基を導入し、もう片面側に酸性ガスを吸着する塩基性の消臭性官能基を導入することができる。あるいは表面や裏面の一部の領域又は複数の領域に対して、それぞれの消臭性官能基を導入することもできる。例えば線状、海島状、ストライプ状などの非連続な状態で酸性と塩基性の消臭性官能基をそれぞれ導入すればよい。、 When the dust collection filter 10 of this embodiment is used in a single layer, both the acidic deodorant functional group that adsorbs the basic gas to the dust collection filter 10 and the basic deodorant functional group that adsorbs the acidic gas. May be introduced. If deodorant functional groups of both acidic gas and basic gas are introduced, deodorization can be performed for both gases even if the filter is a single layer. When introducing both of the deodorizing functional groups, for example, an acidic deodorizing functional group that adsorbs a basic gas is introduced on one side of the filter, and a basic adsorbing acidic gas is adsorbed on the other side. Deodorant functional groups can be introduced. Or each deodorant functional group can also be introduce | transduced with respect to the one part area | region or several area | region of the surface and the back surface. For example, an acidic and basic deodorizing functional group may be introduced in a discontinuous state such as a linear shape, a sea island shape, or a stripe shape. ,
上述のように酸性ガス・塩基性ガスの両方の消臭性官能基を導入する場合には、殺菌・抗ウイルス性を有する金属イオンは、塩基性ガスを吸着する官能基と酸性ガスを吸着する官能基の両方の消臭性官能基に固定されてよい。また、塩基性ガスをより多く消臭したい場合は塩基性の消臭性官能基に金属イオンを固定してもよい。酸性ガスをより多く消臭したい場合は酸性の消臭性官能基に金属イオンを固定してもよい。必要な消臭性能等に応じて金属イオンを結合させる官能基を適宜選択すればよい。またこの時、塩基性ガスや酸性ガスを吸着する無機微粒子を、消臭機能向上のために使用環境に合わせてさらに固定してもよい。 As described above, when deodorizing functional groups of both acidic gas and basic gas are introduced, the metal ions having bactericidal and antiviral properties adsorb the functional group that adsorbs basic gas and acidic gas. It may be fixed to both deodorant functional groups of the functional group. When it is desired to deodorize more basic gas, metal ions may be fixed to the basic deodorant functional group. In order to deodorize more acidic gas, metal ions may be fixed to the acidic deodorant functional group. What is necessary is just to select suitably the functional group which couple | bonds a metal ion according to required deodorizing performance. At this time, the inorganic fine particles that adsorb basic gas or acid gas may be further fixed in accordance with the use environment in order to improve the deodorizing function.
本実施形態の集塵フィルタ10を2層以上の積層体として用いる場合、塩基性ガスを吸着する酸性の消臭性官能基を導入したフィルタと、酸性ガスを吸着する塩基性の消臭性官能基を導入したフィルタを積層することができる。酸性ガスと塩基性ガスの消臭に対応したそれぞれのフィルタを積層させることで、集塵フィルタ10は両方のガスを消臭できる。 When the dust collection filter 10 of this embodiment is used as a laminate of two or more layers, a filter having an acidic deodorizing functional group that adsorbs a basic gas and a basic deodorizing functional group that adsorbs an acidic gas. Filters into which groups are introduced can be stacked. By stacking the filters corresponding to the deodorization of the acid gas and the basic gas, the dust collection filter 10 can deodorize both gases.
また芯材となる不織布やハニカムなどの通気性を有する繊維構造体と、上述の消臭性官能基が導入された単層構造あるいは積層構造のフィルタと、を積層させてもよい。芯材と積層することで強度が向上するので、集塵フィルタ10の表面積を増加させるためのプリーツ形状などの加工がしやすくなる。またこの時、塩基性ガスや酸性ガスを吸着する無機微粒子を、消臭機能向上のために使用環境に合わせてさらに固定してもよい。 Further, a fiber structure having air permeability such as a nonwoven fabric or a honeycomb as a core material and a filter having a single layer structure or a multilayer structure in which the above-described deodorant functional group is introduced may be laminated. Since the strength is improved by laminating with the core material, processing such as a pleated shape for increasing the surface area of the dust collecting filter 10 is facilitated. At this time, the inorganic fine particles that adsorb basic gas or acid gas may be further fixed in accordance with the use environment in order to improve the deodorizing function.
(空気清浄機の他の実施形態)
図3は、本実施形態の空気清浄機100のさらに別の実施形態を示す。図3の空気清浄機100は、集塵フィルタ10と放電電極20、接地電極30、電源40とを含む集塵部Aと、放電線60と接地電極70と電源80とを含むイオン化部Bを備えた空気清浄機100である。この空気清浄機100は、集塵部Aの風上に空気をイオン化して塵埃を帯電させるイオン化部Bを設けることを特徴とした空気清浄機の一例である。イオン化部Bを通過する際に、イオン化された空気の作用(イオン化部Bの周囲の気体を電離させて発生するイオンの作用)により、塵埃や細菌、ウイルスなどの微生物が帯電し、その帯電した塵埃等を集塵部Aに送り込み捕集させるため、集塵性能を高めることができる。(Another embodiment of the air purifier)
FIG. 3 shows still another embodiment of the air cleaner 100 of the present embodiment. The air cleaner 100 of FIG. 3 includes a dust collection part A including a dust collection filter 10, a discharge electrode 20, a ground electrode 30, and a power supply 40, and an ionization part B including a discharge line 60, a ground electrode 70, and a power supply 80. It is the air cleaner 100 provided. This air cleaner 100 is an example of an air cleaner characterized in that an ionization unit B that ionizes air and charges dust on the wind of the dust collection unit A is provided. When passing through the ionization part B, microorganisms such as dust, bacteria, and viruses are charged by the action of ionized air (the action of ions generated by ionizing the gas around the ionization part B). Since dust or the like is sent to and collected in the dust collecting part A, dust collection performance can be improved.
次に、実施例を挙げて本発明をより具体的に説明する。ただし、本発明はこれらの実施例のみに限定されるものではない。 Next, the present invention will be described more specifically with reference to examples. However, the present invention is not limited to only these examples.
<集塵フィルタの作製>
以下、実施例の電子線照射には、エレクトロカーテン型電子線照射装置(岩崎電気(株)製 CB250/15/180L)を用いた。集塵フィルタの実施例および比較例は以下の通り作製した。<Preparation of dust collection filter>
Hereinafter, an electron curtain type electron beam irradiation apparatus (CB250 / 15 / 180L manufactured by Iwasaki Electric Co., Ltd.) was used for the electron beam irradiation in the examples. Examples and comparative examples of the dust collection filter were produced as follows.
(サンプル1)
集塵フィルタの基材として、エレクトレット性能を有するPP(ポリプロピレン)基材のメルトブロー不織布(東レ・ファインケミカル(株)製 EM05010)を、窒素雰囲気下にて、電子線を200kVの加速電圧で5Mrad照射した。ついでこの不織布を、窒素雰囲気下にて、30%発煙硫酸に1時間さらし、水洗、中和して、スルホン化を行った。得られたスルホン化PP不織布を、1%硫酸亜鉛水溶液に20分間浸漬し、水洗及び乾燥し、亜鉛イオン担持スルホン化不織布を得た。(Sample 1)
As a base material of the dust collection filter, a PP (polypropylene) base material melt blown nonwoven fabric (EM05010 manufactured by Toray Fine Chemical Co., Ltd.) having an electret performance was irradiated with an electron beam at an acceleration voltage of 200 kV for 5 Mrad in a nitrogen atmosphere. . The nonwoven fabric was then exposed to 30% fuming sulfuric acid for 1 hour under a nitrogen atmosphere, washed with water and neutralized to effect sulfonation. The obtained sulfonated PP nonwoven fabric was immersed in a 1% zinc sulfate aqueous solution for 20 minutes, washed with water and dried to obtain a sulfonated nonwoven fabric carrying zinc ions.
(サンプル2)
サンプル1と同じPP不織布に、窒素雰囲気下にて、電子線を200kVの加速電圧で20Mrad照射した。ついでこの不織布を10%のメタクリル酸グリシジル溶液に浸漬し、グラフト重合反応を行い、さらに、亜硫酸水素ナトリウム水溶液でスルホン化を行った。得られたスルホン化PP不織布を1%硫酸銅水溶液に20分間浸漬し、水洗及び乾燥し、銅イオン担持スルホン化不織布を得た。(Sample 2)
The same PP nonwoven fabric as Sample 1 was irradiated with an electron beam at an acceleration voltage of 200 kV for 20 Mrad in a nitrogen atmosphere. Subsequently, this nonwoven fabric was immersed in a 10% glycidyl methacrylate solution to carry out a graft polymerization reaction, and further sulfonated with an aqueous sodium hydrogen sulfite solution. The obtained sulfonated PP nonwoven fabric was immersed in a 1% aqueous copper sulfate solution for 20 minutes, washed with water and dried to obtain a sulfonated nonwoven fabric carrying copper ions.
(サンプル3)
サンプル1と同じPP不織布に、実施例2と同様にグラフト重合反応を行い、さらに、ジエチルアミン溶液にグラフト重合反応を行った不織布を浸漬しアミノ化を行った。得られたアミノ化PP不織布を1%塩化金酸水溶液に20分間浸漬し、水洗及び乾燥し、金錯体担持アミノ化不織布を得た。(Sample 3)
A graft polymerization reaction was performed on the same PP nonwoven fabric as Sample 1 in the same manner as in Example 2. Further, the nonwoven fabric subjected to the graft polymerization reaction was immersed in a diethylamine solution for amination. The obtained aminated PP nonwoven fabric was immersed in a 1% chloroauric acid aqueous solution for 20 minutes, washed with water and dried to obtain a gold complex-carrying aminated nonwoven fabric.
(サンプル4)
エレクトレット性能を持たない基材として、PP基材のスパンボンド不織布(旭化成せんい(株)製 P01100)にサンプル1と同様の方法にてスルホン化まで行った。得られたスルホン化PP不織布を1%硝酸銀水溶液に20分間浸漬し、水洗及び乾燥し、銀イオン担持スルホン化不織布を得た。(Sample 4)
As a base material having no electret performance, a PP base spunbond nonwoven fabric (P01100 manufactured by Asahi Kasei Fibers Co., Ltd.) was subjected to sulfonation in the same manner as in Sample 1. The obtained sulfonated PP nonwoven fabric was immersed in a 1% silver nitrate aqueous solution for 20 minutes, washed with water and dried to obtain a sulfonated nonwoven fabric carrying silver ions.
(サンプル5)
エレクトレット性能を持たない別の基材として、PE(ポリエチレン)基材のスパンボンド不織布(ユニチカ(株)製 S1003WDO)にサンプル1と同様の方法にてスルホン化まで行った。得られたスルホン化PE不織布を1%硝酸銀水溶液に20分間浸漬し、水洗及び乾燥し、銀イオン担持スルホン化不織布を得た。(Sample 5)
As another base material having no electret performance, a PE (polyethylene) base material spunbonded nonwoven fabric (S1003WDO manufactured by Unitika Ltd.) was subjected to sulfonation in the same manner as in Sample 1. The obtained sulfonated PE nonwoven fabric was immersed in a 1% aqueous silver nitrate solution for 20 minutes, washed with water and dried to obtain a sulfonated nonwoven fabric carrying silver ions.
(サンプル6)
市販の酸化ジルコニウム微粒子(日本電工株式会社製、PCS-60)をメタノールに対して10.0質量%、シランモノマーとして3−メタクリロキシプロピルトリメトキシシラン(信越化学工業株式会社製、KBM−503)を酸化ジルコニウム微粒子に対して5.0質量%加えてpHを5.0に塩酸で調整した後、ビーズミルにより平均粒子径18nmに粉砕分散した。その後、凍結乾燥機により固液分離して120℃で加熱してシランモノマーを酸化ジルコニウム微粒子の表面に脱水縮合反応により化学結合させて薄膜を形成した。得られたシランモノマー被覆酸化ジルコニウム微粒子をメタノールに10.0質量%分散してビーズミルにより平均粒子径18nmに再度粉砕分散した後、メタノールを加えて固形分を5.0質量%に調整しスラリーを得た。その後、得られたスラリーをサンプル1の亜鉛イオン担持スルホン化不織布の片面にスプレーにて塗布し、80℃、1分間乾燥した後、電子線を200kVの加速電圧で5Mrad照射することで、シランモノマーで被覆された酸化ジルコニウム微粒子からなる薄膜を不織布に結合させてサンプル6の不織布を得た。(Sample 6)
Commercially available zirconium oxide fine particles (Nippon Denko Corporation, PCS-60) are 10.0% by mass with respect to methanol, and 3-methacryloxypropyltrimethoxysilane (Shin-Etsu Chemical Co., Ltd., KBM-503) is oxidized as a silane monomer. After adding 5.0% by mass to the zirconium fine particles and adjusting the pH to 5.0 with hydrochloric acid, it was pulverized and dispersed to an average particle size of 18 nm by a bead mill. Thereafter, solid-liquid separation was performed using a freeze dryer, and the film was heated at 120 ° C. to chemically bond the silane monomer to the surface of the zirconium oxide fine particles by a dehydration condensation reaction to form a thin film. The obtained silane monomer-coated zirconium oxide fine particles were dispersed in 10.0% by mass in methanol and pulverized and dispersed again to an average particle size of 18 nm by a bead mill, and then methanol was added to adjust the solid content to 5.0% by mass to obtain a slurry. After that, the obtained slurry was applied to one side of the sulfonated nonwoven fabric carrying zinc ions of sample 1 by spraying, dried at 80 ° C. for 1 minute, and then irradiated with an electron beam at an acceleration voltage of 200 kV for 5 Mrad, whereby a silane monomer A thin film made of zirconium oxide fine particles coated with was bonded to a nonwoven fabric to obtain a nonwoven fabric of Sample 6.
(サンプル7)
サンプル6の酸化ジルコニウム微粒子をシリカ微粒子に変えた以外は同じ方法で作成したスラリーを、サンプル3の金錯体担持アミノ化不織布の片面にスプレーにて塗布し、80℃、1分間乾燥した後、電子線を200kVの加速電圧で5Mrad照射することで、シランモノマーで被覆されたシリカ微粒子からなる薄膜を結合させてサンプル7の不織布を得た。(Sample 7)
A slurry prepared in the same manner except that the zirconium oxide fine particles in sample 6 were changed to silica fine particles was applied to one side of the gold complex-carrying aminated nonwoven fabric of sample 3 by spraying, dried at 80 ° C. for 1 minute, By irradiating the wire with 5 Mrad at an acceleration voltage of 200 kV, a thin film made of silica fine particles coated with a silane monomer was bonded to obtain a nonwoven fabric of Sample 7.
(サンプル8)
サンプル1の亜鉛イオン担持スルホン化不織布と、サンプル3の金錯体担持アミノ化不織布とを、ホットメルト接着剤としてヘンケルジャパン株式会社製MP843を、ノードソン株式会社製ALTA400シグレチャースプレーガンより糸状に吐出させ、貼り合せえることでサンプル8の不織布を得た。(Sample 8)
The sample 1 zinc ion-supported sulfonated non-woven fabric and the sample 3 gold complex-supported aminated non-woven fabric are discharged as a hot melt adhesive from Henkel Japan Co., Ltd. MP843 in a thread form from the Nordson Co., Ltd. ALTA 400 sigleture spray gun. The nonwoven fabric of Sample 8 was obtained by pasting together.
(サンプル9)
サンプル1と同じPP不織布の未加工品をサンプル9とした。(Sample 9)
An unprocessed product of the same PP nonwoven fabric as Sample 1 was designated as Sample 9.
(サンプル10)
サンプル1と同じPP不織布に、サンプル1と同様の方法にてスルホン化まで行ったスルホン化PP不織布をサンプル10とした。(Sample 10)
A sulfonated PP nonwoven fabric obtained by subjecting the same PP nonwoven fabric as Sample 1 to sulfonation by the same method as Sample 1 was designated as Sample 10.
(サンプル11)
サンプル1と同じPP不織布に、サンプル3と同様の方法にてアミノ化まで行ったアミノ化PP不織布をサンプル11とした。(Sample 11)
Sample 11 was an aminated PP nonwoven fabric obtained by subjecting the same PP nonwoven fabric as Sample 1 to amination by the same method as Sample 3.
(サンプル12)
サンプル1と同じPP不織布の未加工品の片面に、サンプル6と同様の方法にて酸化ジルコニウムを固定しサンプル12とした。(Sample 12)
Zirconium oxide was fixed on one side of the same non-woven PP nonwoven fabric as sample 1 by the same method as sample 6 to obtain sample 12.
(サンプル13)
サンプル1と同じPP不織布の未加工品の片面に、サンプル7と同様の方法にてシリカ微粒子を固定しサンプル13とした。(Sample 13)
Sample 13 was prepared by fixing silica fine particles on one side of the same non-woven PP nonwoven fabric as sample 1 by the same method as sample 7.
(サンプル14)
未加工のガラス繊維紙(北越紀州製紙(株)製H−510A)をサンプル14とした。各サンプルの構成を表1に示す。(Sample 14)
Unprocessed glass fiber paper (H-510A, Hokuetsu Kishu Paper Co., Ltd.) was used as sample 14. Table 1 shows the configuration of each sample.
<集塵効率測定>
次に、集塵効率について測定した。図2のように、表1に記載のサンプル1〜8をそれぞれ電極間に設置し、電位差5kVの電圧を印加させた。放電電極として金属板を針状に打ち抜いたものを用い、接地電極としては金属メッシュを用いた。0.1μmのNaCl粒子を試験粒子として、捕集効率試験機(柴田科学(株)製、AP−632F型)にて、20L/minの流量時の集塵効率を測定し、実施例1〜8とした。また実施例1、4、5に印加を加えず集塵効率を測定したものを比較例1〜3とし、サンプル9、10、12のうち、電圧を印加せずに集塵効率を測定したものを比較例5、7、9とし、電圧を印加して、集塵効率を測定したものを比較例4、6、8とした。その結果を表2に示す。<Dust collection efficiency measurement>
Next, the dust collection efficiency was measured. As shown in FIG. 2, Samples 1 to 8 shown in Table 1 were respectively installed between the electrodes, and a voltage with a potential difference of 5 kV was applied. A metal plate punched out as a discharge electrode was used, and a metal mesh was used as the ground electrode. Examples 1 to 8 were measured for dust collection efficiency at a flow rate of 20 L / min with a collection efficiency tester (manufactured by Shibata Kagaku Co., Ltd., AP-632F type) using 0.1 μm NaCl particles as test particles. It was. Moreover, what measured dust collection efficiency without applying an application to Example 1, 4, 5 was set as Comparative Examples 1-3, and measured the dust collection efficiency without applying a voltage among samples 9, 10, and 12. Are Comparative Examples 5, 7, and 9, and those in which the dust collection efficiency was measured by applying a voltage were referred to as Comparative Examples 4, 6, and 8. The results are shown in Table 2.
<通気抵抗測定>
直径36mmの大きさの各サンプルフィルタを試験体とし、捕集効率試験機(柴田科学(株)製 AP−632F型)を用いて、20L/minの流量時の各サンプルにおける通気抵抗を測定した。その結果を表2に示す。表2に示す通気抵抗は、各実施例、比較例に用いたフィルタのサンプルのみの測定値である。<Measurement of ventilation resistance>
Each sample filter having a diameter of 36 mm was used as a test specimen, and the airflow resistance in each sample at a flow rate of 20 L / min was measured using a collection efficiency tester (AP-632F type manufactured by Shibata Kagaku Co., Ltd.). . The results are shown in Table 2. The ventilation resistance shown in Table 2 is a measured value of only the sample of the filter used in each example and comparative example.
上記の結果より、電圧を印加した実施例1〜3、6〜8、比較例4、6、8において通気抵抗が比較例10のHEPAフィルタの1/10程度にも関わらず、同等の集塵効果が得られる事が確認できた。実施例4、5、比較例2、3はエレクトレット能をもたない通常の不織布ではあるが、実施例4、5と比較例2、3を比較することで、電圧を印加することにより、印加しない時の4倍程度、集塵効率が向上することが確認できた。また比較例5、7の結果よりエレクトレット不織布は官能基を導入すると集塵効率が低下するが、比較例6の結果のように、電圧を印加することで再び集塵効率が向上できることも確認できた。以上のことより、放電電極と接地電極間に集塵フィルタを設置することで高い集塵能を持った空気清浄機が提供できることが確認できた。 From the above results, in Examples 1 to 3, 6 to 8 and Comparative Examples 4, 6, and 8 to which a voltage was applied, the air resistance was about 1/10 that of the HEPA filter of Comparative Example 10, but the same dust collection It was confirmed that the effect was obtained. Examples 4 and 5 and Comparative Examples 2 and 3 are ordinary nonwoven fabrics that do not have electret capability, but by comparing Examples 4 and 5 with Comparative Examples 2 and 3, applying voltage is applied. It was confirmed that the dust collection efficiency was improved by about 4 times compared to when not. In addition, from the results of Comparative Examples 5 and 7, the dust collection efficiency of the electret nonwoven fabric decreases when a functional group is introduced, but it can also be confirmed that the dust collection efficiency can be improved again by applying a voltage as in the result of Comparative Example 6. It was. From the above, it was confirmed that an air cleaner having a high dust collecting ability can be provided by installing a dust collecting filter between the discharge electrode and the ground electrode.
<消臭性の評価>
サンプル1、3、6〜14の各サンプルを10cm×10cmの大きさに切り取り、サンプリングバッグに入れた後、塩基性ガスとしてアンモニアを60ppm含む空気を、酸性ガスとして酢酸を60ppm含む空気を同サンプリングバッグ内に5L封入し、サンプリングバッグ内の各ガスの残存濃度を所定の時間毎に検知管により測定した。測定時間は、ガス含有空気を封入してから、それぞれ5、15、30分後とし、結果を表3に示した。<Evaluation of deodorizing properties>
Samples 1, 3, and 6-14 were cut to a size of 10cm x 10cm, placed in a sampling bag, and then air containing 60ppm of ammonia as basic gas and air containing 60ppm of acetic acid as acidic gas were sampled. 5 L was sealed in the bag, and the residual concentration of each gas in the sampling bag was measured with a detector tube every predetermined time. The measurement times were 5, 15, and 30 minutes after the gas-containing air was sealed. The results are shown in Table 3.
以上の結果より、アンモニアガスにおいては、スルホン酸基を導入したサンプル1、6、8、10で非常に高い消臭効果が認められ、塩基性ガスにおいては、アミノ基を導入したサンプル3、7、8、11で非常に高い消臭効果が認められた。特にサンプル8では両消臭性官能基を導入しているため、酸性、塩基性、両方のガスの消臭性が確認できた。また酸性ガス吸着性無機微粒子を固定したサンプル12、塩基性ガス吸着性無機微粒子を固定したサンプル13でも、それぞれのガスの消臭性が確認できた。さらに消臭性官能基と消臭性無機微粒子を組み合わせたサンプル6、7でも、酸性、塩基性の両方のガスの吸着特性が確認できた。官能基も消臭性無機微粒子も導入していないサンプル9、14には消臭効果がないことが確認できた。 From the above results, in ammonia gas, a very high deodorizing effect was observed in samples 1, 6, 8, and 10 in which sulfonic acid groups were introduced, and in basic gas, samples 3 and 7 in which amino groups were introduced. 8 and 11, very high deodorizing effect was recognized. In particular, since both deodorizing functional groups were introduced in Sample 8, the deodorizing properties of both acidic and basic gases could be confirmed. Moreover, the deodorizing property of each gas was confirmed also in the sample 12 which fixed the acidic gas adsorbing inorganic fine particle, and the sample 13 which fixed the basic gas adsorbing inorganic fine particle. Furthermore, the adsorption characteristics of both acidic and basic gases could be confirmed in Samples 6 and 7 in which the deodorant functional group and the deodorant inorganic fine particles were combined. It was confirmed that Samples 9 and 14 into which neither functional groups nor deodorant inorganic fine particles were introduced had no deodorizing effect.
<殺菌性の評価>
サンプル1〜14の各サンプルの殺菌性評価は、大腸菌(Escherichia coli)を用いた。大腸菌の懸濁液 100μLをプラスチックシャーレ上に滴下し、その上から、2cm×2cmに切り取った各フィルタサンプルを載せて、懸濁液をサンプル全面に延ばした後、室温で60分間作用させた。60分後、20mg/mLのブイヨンタンパク質液(SCDLP培地)1900μLを添加し、ピペッティングにより細菌を洗い出し、上清液を回収した。その後、SCDLP培地を用いて、回収した上清液の10倍段階希釈系列を作製し、回収した上清液と各希釈段階液をそれぞれ1mLずつシャーレにとり、溶解したNB寒天培地を加えて、混和した。寒天培地が固化した後、37℃にて培養を行った。形成されたコロニー数をカウントし、生菌数(CFU/0.1mL, Log10);(CFU:colony-forming unit)を算出することで、それぞれの大腸菌に対する殺菌性を評価した。結果を表4に示す。<Evaluation of bactericidal properties>
Escherichia coli was used for the bactericidal evaluation of the samples 1 to 14. 100 μL of the Escherichia coli suspension was dropped onto a plastic petri dish, and each filter sample cut into 2 cm × 2 cm was placed thereon. The suspension was spread over the entire surface of the sample, and then allowed to act at room temperature for 60 minutes. After 60 minutes, 1900 μL of a 20 mg / mL bouillon protein solution (SCDLP medium) was added, the bacteria were washed out by pipetting, and the supernatant was collected. Then, a 10-fold serial dilution series of the collected supernatant was prepared using SCDLP medium, and 1 mL each of the collected supernatant and each diluted liquid was placed in a petri dish, and dissolved NB agar medium was added and mixed. did. After the agar medium solidified, it was cultured at 37 ° C. The number of colonies formed was counted and the number of viable bacteria (CFU / 0.1 mL, Log10); (CFU: colony-forming unit) was calculated to evaluate the bactericidal properties against each Escherichia coli. The results are shown in Table 4.
<抗ウイルス性の評価>
サンプル1〜14の各サンプルの抗ウイルス性評価は、MDCK細胞を用いて培養したインフルエンザウイルス(influenza A/北九州/159/93(H3N2))を用いた。ウイルスの懸濁液100μLをプラスチックシャーレ上に滴下し、その上から2cm×2cmに切り取った各フィルタサンプルを載せて、懸濁液をサンプル全面に延ばした後、室温で60分間作用させた。60分後、SCDLP培地1900μLを添加し、ピペッティングによりウイルスを洗い出し、上清液を回収した。その後、細胞培養培地(MEM)を用いて、回収した上清液の10倍段階希釈系列を作製した。回収した上清液と各希釈段階液0.1mLをMDCK細胞を培養した6穴細胞培養プレートに接種した。60分間静置しウイルスを細胞へ吸着させた後、0.7%寒天培地を重層し、48時間、34℃、5%CO2インキュベータにて培養後、ホルマリン固定、メチレンブルー染色を行い、形成されたプラーク数をカウントして、ウイルスの感染価(PFU/0.1mL,Log10);(PFU:plaque-forming units)を算出した。その試験結果を表4に示す。<Evaluation of antiviral properties>
For the antiviral evaluation of each sample 1-14, influenza virus (influenza A / Kitakyushu / 159/93 (H3N2)) cultured using MDCK cells was used. 100 μL of the virus suspension was dropped onto a plastic petri dish, each filter sample cut out 2 cm × 2 cm from the top was placed, the suspension was spread over the entire surface of the sample, and then allowed to act at room temperature for 60 minutes. After 60 minutes, 1900 μL of SCDLP medium was added, the virus was washed out by pipetting, and the supernatant was collected. Thereafter, a 10-fold serial dilution series of the collected supernatant was prepared using cell culture medium (MEM). The recovered supernatant and 0.1 mL of each diluted solution were inoculated into a 6-well cell culture plate in which MDCK cells were cultured. Plaque formed by adsorbing virus to cells by standing for 60 minutes, overlaying 0.7% agar medium, culturing in 34 ° C, 5% CO 2 incubator for 48 hours, fixing with formalin and staining with methylene blue The number was counted, and the virus infectivity titer (PFU / 0.1 mL, Log 10); (PFU: plaque-forming units) was calculated. The test results are shown in Table 4.
以上の結果より、金属イオンを結合させたサンプル1〜8の不織布では殺菌、抗ウイルス性能が確認できたのに対し、金属イオンを結合していないサンプル9〜14については殺菌、抗ウイルス性能が確認できなかった。 From the above results, sterilization and antiviral performance were confirmed in the nonwoven fabrics of samples 1 to 8 to which metal ions were bonded, whereas samples 9 to 14 that were not bonded to metal ions had sterilization and antiviral performance. I could not confirm.
<浮遊ウイルス除去評価>
次に、サンプル1、9、10を用いて、実機での浮遊ウイルス除去試験を行った。まず各サンプルを図2に示すようなフィルタユニットに搭載した電機集塵機を1m3のBOX内に設置し、集塵手段に電位差5kVの電圧を印加させた。ネブライザを用いてインフルエンザウイルス(influenza A/北九州/159/93(H3N2)、約1×1010個)を含む懸濁液をBOX内に噴霧し、ウイルスを浮遊させた。その後、電気集塵機を作動させ、0.2m3/minの流量でBOX内の空気を循環させた。循環してから15分後のBOX内の浮遊ウイルスをゼラチンフィルタで捕集した。捕集後のゼラチンフィルタをシャーレに取り、MEMを加えて37℃に置く事でゼラチンフィルタを溶解させた。その後、MEMを用いて、ゼラチンフィルタ溶解液の10倍段階希釈系列を作製した。ゼラチンフィルタ溶解液と各希釈段階液0.1mLを、MDCK細胞を培養した6穴細胞培養プレートに接種した。60分間静置しウイルスを細胞へ吸着させた後、0.7%寒天培地を重層し、48時間、34℃、5%CO2インキュベータにて培養後、ホルマリン固定、メチレンブルー染色を行い、形成されたプラーク数をカウントして、ウイルスの感染価(PFU/0.1mL,Log10)を算出した。電気集塵機がない場合のウイルス感染価(自然減衰)(P0)と循環後のウイルス感染価(Pm)から、各サンプルのBOX内の浮遊ウイルス除去率P(%)を次式(1)より求めた。
P(%)=(1−Pm/P0)×100 (1)
その結果とそれぞれの実施例、比較例の構成を表5に示す。<Evaluation of floating virus removal>
Next, using the samples 1, 9, and 10, a floating virus removal test was performed with an actual machine. First, an electric dust collector in which each sample was mounted on a filter unit as shown in FIG. 2 was installed in a 1 m 3 BOX, and a voltage with a potential difference of 5 kV was applied to the dust collecting means. Using a nebulizer, a suspension containing influenza virus (influenza A / Kitakyushu / 159/93 (H3N2), approximately 1 × 10 10 cells) was sprayed into the BOX to float the virus. After that, the electrostatic precipitator was activated and the air in the BOX was circulated at a flow rate of 0.2 m 3 / min. Floating virus in the BOX 15 minutes after circulation was collected with a gelatin filter. The collected gelatin filter was taken in a petri dish, MEM was added and placed at 37 ° C. to dissolve the gelatin filter. Thereafter, a 10-fold serial dilution series of gelatin filter solution was prepared using MEM. Gelatin filter lysate and 0.1 mL of each dilution step solution were inoculated into a 6-well cell culture plate in which MDCK cells were cultured. Plaque formed by adsorbing virus to cells by standing for 60 minutes, overlaying 0.7% agar medium, culturing in 34 ° C, 5% CO 2 incubator for 48 hours, fixing with formalin and staining with methylene blue The number was counted and the virus infectivity titer (PFU / 0.1 mL, Log10) was calculated. From the virus infection titer (natural decay) without a dust collector (P0) and the virus infection titer after circulation (Pm), calculate the floating virus removal rate P (%) in the BOX of each sample from the following equation (1). It was.
P (%) = (1-Pm / P0) x 100 (1)
Table 5 shows the results and the configurations of the examples and comparative examples.
続いて実際に捕集したウイルスが不活化しているかどうかの確認をするために、浮遊ウイルス試験後の各サンプルを、前述と同様の抗ウイルス性評価の方法にて抗ウイルス性を評価した。その結果を表5に示す。 Subsequently, in order to confirm whether or not the virus actually collected was inactivated, the antiviral properties of each sample after the floating virus test were evaluated by the same antiviral evaluation method as described above. The results are shown in Table 5.
以上の結果より、電圧を印加した実施例9と比較例11、12において比較例13〜15よりもウイルスの捕集効率が向上することが確認できた。また、金属イオンを担持した実施例9、比較例13で、高い抗ウイルス性が確認できた。これらのことから、本発明より、圧力損失が低くても高い集塵能力を持ち、かつ、捕集した細菌やウイルスを不活化する能力をもつ空気清浄機が提供できることが確認できた。 From the above results, it was confirmed that in Example 9 and Comparative Examples 11 and 12 to which a voltage was applied, the virus collection efficiency was improved as compared with Comparative Examples 13 to 15. In Example 9 and Comparative Example 13 carrying metal ions, high antiviral properties could be confirmed. From these facts, it was confirmed that the present invention can provide an air purifier having a high dust collecting ability even when the pressure loss is low and having the ability to inactivate collected bacteria and viruses.
Claims (4)
前記放電電極に対向して配置される接地電極と、
前記放電電極と前記接地電極との間に配置され、通気性を有する繊維構造体で形成される集塵フィルタであって、前記繊維構造体の少なくとも一部の繊維に導入されるスルホン酸基と、導入された前記スルホン酸基の一部のスルホン酸基に結合する、銅イオン、銀イオン、亜鉛イオン、金イオンから少なくとも一種選択される金属イオンと、を有する集塵フィルタと、
を備えることを特徴とする空気清浄機。 A discharge electrode to which a voltage is applied;
A ground electrode disposed opposite the discharge electrode;
A dust collection filter disposed between the discharge electrode and the ground electrode and formed of a fiber structure having air permeability, and a sulfonic acid group introduced into at least some of the fibers of the fiber structure; A dust collection filter having a metal ion selected from at least one of copper ion, silver ion, zinc ion, and gold ion that binds to a part of the sulfonic acid group of the introduced sulfonic acid group ,
Air purifier, wherein the obtaining Bei a.
前記放電電極に対向して配置される接地電極と、A ground electrode disposed opposite the discharge electrode;
前記放電電極と前記接地電極との間に配置され、通気性を有する繊維構造体で形成される集塵フィルタであって、前記繊維構造体の少なくとも一部の繊維に導入されるアミノ基と、導入された前記アミノ基の一部のアミノ基に結合する金イオンと、を有する集塵フィルタと、A dust collection filter disposed between the discharge electrode and the ground electrode and formed of a fiber structure having air permeability, an amino group introduced into at least some of the fibers of the fiber structure; A dust collection filter having a gold ion bonded to a part of the amino groups of the introduced amino group,
を備えることを特徴とする空気清浄機。An air purifier characterized by comprising:
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| JP2013160824 | 2013-08-01 | ||
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| PCT/JP2014/001117 WO2015015671A1 (en) | 2013-08-01 | 2014-02-28 | Air purification device |
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