JP2007105215A - Deodorizer, and deodorizing device and air conditioner using deodorizer - Google Patents

Deodorizer, and deodorizing device and air conditioner using deodorizer Download PDF

Info

Publication number
JP2007105215A
JP2007105215A JP2005298646A JP2005298646A JP2007105215A JP 2007105215 A JP2007105215 A JP 2007105215A JP 2005298646 A JP2005298646 A JP 2005298646A JP 2005298646 A JP2005298646 A JP 2005298646A JP 2007105215 A JP2007105215 A JP 2007105215A
Authority
JP
Japan
Prior art keywords
air
adsorbent
deodorizing
oxide
odor
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP2005298646A
Other languages
Japanese (ja)
Other versions
JP5061448B2 (en
Inventor
Daisuke Kawazoe
大輔 川添
Mitsuhiro Sano
光宏 佐野
Koichi Nakano
幸一 中野
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Panasonic Holdings Corp
Original Assignee
Matsushita Electric Industrial Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Matsushita Electric Industrial Co Ltd filed Critical Matsushita Electric Industrial Co Ltd
Priority to JP2005298646A priority Critical patent/JP5061448B2/en
Priority to MYPI20064320 priority patent/MY150279A/en
Priority to ES06122272T priority patent/ES2387814T3/en
Priority to EP20060122272 priority patent/EP1775013B1/en
Publication of JP2007105215A publication Critical patent/JP2007105215A/en
Application granted granted Critical
Publication of JP5061448B2 publication Critical patent/JP5061448B2/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Abstract

<P>PROBLEM TO BE SOLVED: To transfer harmful acetaldehyde being the main component and being one kind of a VOC to less harmful acetic acid and to adsorb and remove it though a conventional platinum-based catalyst has the problem that its operation temperature is high, so that it cannot be applied to an air conditioner, an air purifier, etc., and a photocatalyst has the problem that its deodorization speed is slower than that of an adsorbent etc., that a light source is required, so that its sizes cannot be reduced and costs are high, and that impact resistance is low. <P>SOLUTION: The deodorizer is composed of the adsorbent 4 having a physical adsorption and and an oxide 5 containing cobalt and having a catalytic action. An odor occurring in a living space can be adsorbed and removed with the adsorbent 4 having the physical adsorption. In particular, the harmful acetaldehyde is transferred to the acetic acid at normal temperature with an oxide catalyst containing cobalt and adsorbed and removed with the adsorbent. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は、部屋や車などの生活空間の気体に含まれる臭気物質を吸着除去でき、特にタバコの主成分で、VOCの一種でもある有害性の高いアセトアルデヒドを有害性の小さい酢酸へ転化し、それを吸着除去することができる脱臭体および脱臭体を用いた脱臭装置および空気調和機に関するものである。   The present invention can adsorb and remove odorous substances contained in the gas of living spaces such as rooms and cars, and in particular converts the highly harmful acetaldehyde, which is a main component of tobacco and also a kind of VOC, into less harmful acetic acid, The present invention relates to a deodorizing body capable of adsorbing and removing it, a deodorizing device using the deodorizing body, and an air conditioner.

従来、白金属を用いた触媒を高温(200℃以上)で作動させ、臭気物質などを水や二酸化炭素などへ分解する白金系の熱触媒が広く知られている。また、特許文献1にはマンガンを主体とする遷移金属による複合酸化物を用いた脱臭用の触媒について開示されている。これによるとマンガンとコバルトの複合酸化物により、50℃でアセトアルデヒドを80%分解されるとしている。さらには、常温での臭気の分解触媒として、比表面積が大きな担体に光触媒を担持した光触媒脱臭フィルターとして特許文献2および特許文献3が開示されている。
特開平10−180108号公報 特開平6−343875号公報 特開2003−53196号公報
Conventionally, a platinum-based thermal catalyst that operates a catalyst using a white metal at a high temperature (200 ° C. or higher) and decomposes odorous substances into water, carbon dioxide, and the like is widely known. Patent Document 1 discloses a deodorizing catalyst using a composite oxide of transition metal mainly composed of manganese. According to this, 80% of acetaldehyde is decomposed at 50 ° C. by the complex oxide of manganese and cobalt. Furthermore, Patent Document 2 and Patent Document 3 are disclosed as photocatalyst deodorizing filters in which a photocatalyst is supported on a carrier having a large specific surface area as an odor decomposition catalyst at room temperature.
Japanese Patent Laid-Open No. 10-180108 JP-A-6-343875 JP 2003-53196 A

しかしながら、従来の白金系の触媒や特許文献1に開示の脱臭体では作動温度が高く、空気調和機や空気清浄機などに応用できないという課題があり、また光触媒は吸着剤などと比較して脱臭速度が遅いことや、光源が必要であるためサイズを小さくできない、コストが高い、耐衝撃性が弱いなどの課題を有していた。   However, the conventional platinum-based catalyst and the deodorizer disclosed in Patent Document 1 have a problem that the operating temperature is high and cannot be applied to an air conditioner or an air cleaner, and the photocatalyst is deodorized as compared with an adsorbent or the like. There are problems such as a low speed, a size that cannot be reduced because a light source is required, a high cost, and a low impact resistance.

本発明は、前記従来の課題を解決するもので、部屋や車などの生活空間で発生する臭気を物理吸着作用を有する吸着剤により吸着除去でき、特に有害なアセトアルデヒドをCo3O4を主成分とする酸化物触媒により常温で酢酸へ転化し、物理吸着作用を有する吸着剤により吸着除去できる脱臭体を提供することを目的とする。   The present invention solves the above-described conventional problems, and can remove odors generated in living spaces such as rooms and cars by an adsorbent having a physical adsorption action, and particularly oxidizes harmful acetaldehyde based on Co3O4 as a main component. An object of the present invention is to provide a deodorizing body which can be converted to acetic acid at room temperature by a physical catalyst and adsorbed and removed by an adsorbent having a physical adsorption action.

本発明は、このような課題を解決するものであり、物理吸着作用を有する吸着剤と、コバルトを含み触媒作用を有する酸化物と、前記吸着剤および前記酸化物とを担持する担体とから構成され、前記酸化物がアルデヒド類をカルボン酸へ転化後、前記吸着剤で吸着除去することを特徴とした脱臭体とするもので、部屋や車などの生活空間で発生する臭気を物理吸着作用を有する吸着剤により吸着除去でき、特に有害なアセトアルデヒドをCo3O4を主成分とする酸化物の触媒作用により常温で酢酸へ転化し、吸着剤により吸着除去できる脱臭体を実現できる。   The present invention solves such a problem, and comprises an adsorbent having a physical adsorption action, an oxide containing cobalt and having a catalytic action, and a carrier carrying the adsorbent and the oxide. The deodorizer is characterized in that the oxide converts aldehydes to carboxylic acids and then adsorbs and removes with the adsorbent, and has a physical adsorption effect on odors generated in living spaces such as rooms and cars. A deodorizing body that can be adsorbed and removed by the adsorbent, and that can convert particularly harmful acetaldehyde to acetic acid at room temperature by the catalytic action of an oxide mainly composed of Co3O4 and can be adsorbed and removed by the adsorbent can be realized.

本発明の脱臭体は、部屋や車などの生活空間で発生する臭気を吸着除去でき、特に有害なアセトアルデヒドを常温で有害性の小さい酢酸へと転化し、吸着除去できる脱臭体を提供することができる。また、本発明の脱臭装置は、人の手を煩わすことなく自動的に吸脱着を制御し、メンテナンスフリーで長期間使用できる脱臭装置を提供することができる。さらに、本発明の空気調和機は、吸着剤を担持した脱臭体に高温の空気を通気することにより、吸着剤から臭気が脱着し、メンテナンスフリーで長期間使用できる脱臭機能を備えた空気調和機を実現できる。   The deodorizing body of the present invention is capable of adsorbing and removing odors generated in living spaces such as rooms and cars, and in particular to provide a deodorizing body that can convert harmful acetaldehyde into less harmful acetic acid at room temperature and can be adsorbed and removed. it can. Moreover, the deodorizing apparatus of this invention can control adsorption / desorption automatically without bothering a person's hand, and can provide the deodorizing apparatus which can be used for a long term without a maintenance. Further, the air conditioner of the present invention is an air conditioner having a deodorizing function that allows deodorization from the adsorbent by allowing high-temperature air to pass through the deodorant carrying the adsorbent, and is maintenance-free and can be used for a long time. Can be realized.

第1の発明は、物理吸着作用を有する吸着剤と、コバルトを含み触媒作用を有する酸化物と、前記吸着剤および前記酸化物とを担持する担体とから構成され、前記酸化物がアルデヒド類をカルボン酸へ転化後、前記吸着剤で吸着除去することを特徴とした脱臭体とするもので、部屋や車などの生活空間で発生する臭気を物理吸着作用を有する吸着剤により吸着除去でき、特に有害なアルデヒド類をCo3O4を主成分とする酸化物の触媒作用により常温でカルボン酸へ転化し、吸着剤により吸着除去できる脱臭体を実現できる。   A first invention is composed of an adsorbent having a physical adsorption action, an oxide containing cobalt and having a catalytic action, and a carrier supporting the adsorbent and the oxide, wherein the oxide contains an aldehyde. It is a deodorant characterized by being adsorbed and removed by the adsorbent after conversion to carboxylic acid, and it can adsorb and remove odors generated in living spaces such as rooms and cars with an adsorbent having a physical adsorption action, especially It is possible to realize a deodorant that can convert harmful aldehydes to carboxylic acid at room temperature by the catalytic action of an oxide containing Co3O4 as a main component, and can be adsorbed and removed by an adsorbent.

第2の発明は、吸着剤が疎水性ゼオライトである請求項1記載の脱臭体とするもので、シリカ分を高めたゼオライトは極性が小さくなるため、非極性の臭気分子を吸着できるようになり、また雰囲気の湿度に依存することなく臭気分子を吸脱着できるようになるため、多様な臭気分子を吸着除去できる脱臭体を実現できる。   According to a second aspect of the present invention, the adsorbent is a hydrophobic zeolite. The deodorizer according to claim 1, wherein the zeolite having an increased silica content has a small polarity, and thus can adsorb non-polar odor molecules. Moreover, since it becomes possible to adsorb and desorb odor molecules without depending on the humidity of the atmosphere, it is possible to realize a deodorizing body capable of adsorbing and removing various odor molecules.

第3の発明は、担体が有機繊維から構成されるハニカム構造体である請求項1記載の脱臭体とするもので、耐衝撃性が高く、通気抵抗が小さく、比表面積が大きいため、圧損を抑え、臭気の吸脱着効率が高く衝撃に強い脱臭体を実現できる。   According to a third aspect of the present invention, there is provided a deodorizing body according to claim 1, wherein the carrier is a honeycomb structure composed of organic fibers. The impact resistance is high, the airflow resistance is small, and the specific surface area is large. Suppressing and deodorizing body with high odor absorption and desorption efficiency and strong impact can be realized.

第4の発明は、酸化物が少なくとも吸着剤表面に担持されている請求項1もしくは請求項2記載の脱臭体とするもので、さらに触媒作用を有する酸化物の分散性を高め、比表面積を大きくすることができ、また吸着剤と近接しているため転化により生成したカルボン酸を速やかに吸着剤へ移動させることで酸化物表面が清浄になるためにカルボン酸への転化率の高い脱臭体を実現できる。
第5の発明は、吸着剤へ吸着したカルボン酸は通気により脱着し、繰り返し使用可能な請求項1もしくは請求項2記載の脱臭体とするもので、吸脱着しやすい吸着剤であるゼオライトを担持した脱臭体に通気することにより、飽和吸着に達したゼオライトが脱着再生され、メンテナンスフリーで長期間使用できる脱臭体を実現できる。
According to a fourth aspect of the present invention, there is provided the deodorizer according to claim 1 or 2, wherein at least the oxide is supported on the surface of the adsorbent. The dispersibility of the oxide having a catalytic action is further increased, and the specific surface area is increased. Deodorant with high conversion rate to carboxylic acid because the oxide surface can be cleaned by quickly moving the carboxylic acid generated by conversion to the adsorbent because it is close to the adsorbent. Can be realized.
According to a fifth aspect of the present invention, the carboxylic acid adsorbed on the adsorbent is desorbed by aeration to form a deodorizing body according to claim 1 or claim 2 that supports zeolite that is easily adsorbed and desorbed. By passing the air through the deodorized body, the zeolite that has reached saturation adsorption is desorbed and regenerated, and a maintenance-free deodorized body that can be used for a long time can be realized.

第6の発明は、酸化物はスピネル型構造である請求項1もしくは請求項4記載の脱臭体とするもので、スピネル型構造の酸化物触媒がアルデヒド類を酸化し岩塩型構造となり、次に岩塩型構造が空気中の酸素により酸化されスピネル型構造に戻り、その繰り返しで触媒作用を発揮するため、スピネル型構造を選択することでアルデヒド類をカルボン酸へ転化する性能が高く、カルボン酸への転化率の高い脱臭体を実現できる。   According to a sixth aspect of the present invention, the oxide has a spinel structure. The deodorizer according to claim 1 or 4, wherein the spinel structure oxide catalyst oxidizes aldehydes to form a rock salt structure. The rock salt type structure is oxidized by oxygen in the air and returns to the spinel type structure, and the catalytic action is exerted by repeating it. Therefore, by selecting the spinel type structure, the ability to convert aldehydes to carboxylic acid is high, and to carboxylic acid A deodorizing body with a high conversion rate can be realized.

第7の発明は、酸化物中のナトリウムおよびカリウム成分は1wt%未満である請求項1、4、6いずれか1項に記載の脱臭体とするもので、ナトリウムやカリウムなどが陽イオンの状態で存在すると、電子の授受を阻害し触媒作用の低下をまねくため、その量を少なくすることでアルデヒド類をカルボン酸へ効率良く転化できる脱臭体を実現できる。   The seventh invention is such that the sodium and potassium components in the oxide are less than 1 wt%, and the deodorizing body according to any one of claims 1, 4, and 6, wherein sodium, potassium, etc. are in a cation state In this case, the deodorizing body capable of efficiently converting aldehydes to carboxylic acids can be realized by reducing the amount thereof because it inhibits electron transfer and lowers the catalytic action.

第8の発明は、アルデヒド類はアセトアルデヒドであり、カルボン酸は酢酸である請求項1記載の脱臭体とするもので、アセトアルデヒドはタバコや建材の接着剤等に多く含まれている発ガン性を有すると言われている有害な物質で、それを有害性が少ない酢酸に転化し、ゼオライトにより除去できる脱臭体を実現できる。   According to an eighth aspect of the present invention, the aldehyde is acetaldehyde and the carboxylic acid is acetic acid. The deodorizing body according to claim 1, wherein the acetaldehyde has a carcinogenicity contained in a large amount of adhesives for tobacco and building materials. It is a harmful substance that is said to have, and it can be converted into acetic acid that is less harmful, and a deodorized body that can be removed by zeolite can be realized.

第9の発明は、少なくとも臭気を含む空気を導入する吸気口と、前記臭気を含む空気を吸気する吸気手段と、前記吸気手段により吸気した空気に含まれる臭気を脱臭するフィルタと、前記フィルタにより脱臭された空気を室内あるいは車内へ導入する導入口と、前記フィルタから脱着した臭気を室外あるいは車外へ排気する排気口とを備え、前記フィルタが請求項1〜8いずれか1項に記載の脱臭体である脱臭装置とするもので、吸着剤を担持した脱臭体に通気することにより、飽和吸着に達した吸着剤から脱着した臭気が室外もし
くは車外に排気されることで、メンテナンスフリーで長期間使用できる脱臭装置を実現できる。
According to a ninth aspect of the present invention, there is provided an intake port for introducing air containing at least odor, an intake means for taking in air containing the odor, a filter for deodorizing odor contained in air taken in by the intake means, and the filter. The deodorizing device according to any one of claims 1 to 8, further comprising an introduction port for introducing the deodorized air into the room or the vehicle and an exhaust port for exhausting the odor desorbed from the filter to the outside or the outside of the vehicle. The deodorizing device is a body, and by ventilating the deodorizing body carrying the adsorbent, the odor desorbed from the adsorbent that has reached the saturated adsorption is exhausted to the outside of the room or outside of the vehicle. A deodorizing device that can be used can be realized.

第10の発明は、吸込部から吹出部に至る通風路に、室内熱交換器と前記室内熱交換器にて温度調整された空気を室内に送り出す室内送風機と、吸入した空気に含まれる臭気を脱臭するフィルターを備え、空気調和機の空調運転停止中に、室内熱交換器を加熱し、前記室内熱交換機により暖められた空気の少なくとも一部が室内機内を循環する、クリーニング運転機能を設け、前記フィルターが請求項1〜8いずれか1項に記載の脱臭体である空気調和機とするものである。吸着剤を担持した脱臭体に高温の空気を通気することにより、吸着剤から臭気が脱着し、メンテナンスフリーで長期間使用できる脱臭機能を備えた空気調和機を実現できる。   In a tenth aspect of the present invention, an indoor heat exchanger, an indoor fan for sending out air whose temperature is adjusted by the indoor heat exchanger, and an odor contained in the sucked air are introduced into a ventilation path extending from the suction portion to the blowout portion. Provided with a cleaning operation function that includes a deodorizing filter, heats the indoor heat exchanger during air conditioning operation stop of the air conditioner, and circulates at least part of the air heated by the indoor heat exchanger in the indoor unit, The filter is an air conditioner that is the deodorizer according to any one of claims 1 to 8. By ventilating high-temperature air through the deodorizer carrying the adsorbent, the odor is desorbed from the adsorbent, and an air conditioner having a deodorizing function that can be used for a long time without maintenance can be realized.

第11の発明は、請求項10において、室内機通風路内の空気を室外に排気する排気機能を備え、クリーニング運転の実施中乃至は実施後に、前記排気手段を動作させる空気調和機とするものである。吸着剤を担持した脱臭体に高温の空気を通気させ、吸着剤から脱着した臭気を室外に排気することで、脱着した臭気成分により室内環境を著しく損ねることを更に緩和、あるいは防ぐことができる。   An eleventh aspect of the invention is the air conditioner according to claim 10, which has an exhaust function for exhausting the air in the indoor unit ventilation path to the outside, and operates the exhaust means during or after the cleaning operation. It is. By allowing high-temperature air to pass through the deodorizer carrying the adsorbent and exhausting the odor desorbed from the adsorbent to the outside of the room, it is possible to further alleviate or prevent the indoor environment from being significantly impaired by the desorbed odor component.

以下、本発明の実施の形態について、図面を参照しながら説明する。なお、この実施の形態によって本発明が限定されるものではない。   Hereinafter, embodiments of the present invention will be described with reference to the drawings. Note that the present invention is not limited to the embodiments.

(実施の形態1)
図1(a)は本発明の第1の実施の形態における脱臭体を示す外観模式図であり、(b)は脱臭体表面の拡大模式図である。脱臭体1は、担体3としてポリエチレンテレフタレートを代表とするポリエステル繊維やセルロース繊維などの有機繊維から構成される平板および波形板を交互に積層されたハニカム構造体であり、通気方向2へ低い通気抵抗で通気することができる。
(Embodiment 1)
Fig.1 (a) is an external appearance schematic diagram which shows the deodorizing body in the 1st Embodiment of this invention, (b) is an enlarged schematic diagram of the deodorizing body surface. The deodorizing body 1 is a honeycomb structure in which flat plates and corrugated plates made of organic fibers such as polyester fibers and cellulose fibers typified by polyethylene terephthalate are used as the carrier 3 and has a low ventilation resistance in the ventilation direction 2. Can ventilate.

担体3は、物理吸着作用を有する吸着剤4(以下、本実施の形態では物理吸着剤4という)および触媒作用を有する酸化物5(以下、本実施の形態では触媒酸化物5という)を表面に担持する。物理吸着剤4や触媒酸化物5を担体3にアンカー効果もしくは物理的な結合もしくは化学的な結合などの作用により結合させ、担持されている。このときバインダを添加し、前記効果を高めると良いが、添加量が多い場合、吸着効果や触媒活性を低下させる原因となり、少ない場合、担体3との密着力が低下し、剥がれ落ちやすくなる。望ましくは、物理吸着剤4とバインダとの固形分が重量比で1:1〜20:1程度である。また、バインダは無機系としてはナトリウムやカリウム成分を極力除去したコロイダルシリカ、リン酸アルミニウムなどが適しており、有機系としては水に酢酸ビニル、アクリル、エチレン、ビニルアルコール、変性ウレタンなどの樹脂粒子や、これらの樹脂からなる共重合樹脂粒子を分散させた水系エマルジョン型接着剤を用いるのが望ましい。この有機系バインダは、水を蒸発させることにより、樹脂粒子や共重合樹脂粒子の濃度が高くなり、そしてこれら粒子の表面同士がくっつき始め、粒子表面が互いに溶け合い、被膜を形成することで接着作用が発揮される。このように樹脂皮膜となるため、有機繊維に担持後も加工性に優れる一方で、無機系バインダより触媒性能は劣るという短所もある。   The support 3 has an adsorbent 4 having a physical adsorption action (hereinafter referred to as a physical adsorbent 4 in the present embodiment) and an oxide 5 having a catalytic action (hereinafter referred to as a catalyst oxide 5 in the present embodiment) on the surface. To carry. The physical adsorbent 4 and the catalyst oxide 5 are supported by being bonded to the support 3 by an action such as an anchor effect or a physical bond or a chemical bond. At this time, it is preferable to add a binder to enhance the effect. However, if the addition amount is large, it may cause a decrease in the adsorption effect and catalytic activity, and if it is small, the adhesion with the carrier 3 is lowered and the film is easily peeled off. Desirably, the solid content of the physical adsorbent 4 and the binder is about 1: 1 to 20: 1 by weight ratio. In addition, as inorganic binders, colloidal silica and aluminum phosphate from which sodium and potassium components are removed as much as possible are suitable. As organic binders, resin particles such as vinyl acetate, acrylic, ethylene, vinyl alcohol, and modified urethane are used in water. Alternatively, it is desirable to use an aqueous emulsion adhesive in which copolymer resin particles made of these resins are dispersed. This organic binder increases the concentration of resin particles and copolymer resin particles by evaporating water, and the surfaces of these particles start to stick to each other, and the particle surfaces melt together to form a coating. Is demonstrated. Thus, since it becomes a resin film, it is excellent in processability even after being supported on the organic fiber, but also has a disadvantage that the catalyst performance is inferior to that of the inorganic binder.

物理吸着剤4は、ゼオライト、シリカゲル、セピオライト、アルミナ、活性炭等の物理吸着作用を有する物質が用いられるが、臭気物質の吸脱着速度が速いゼオライトが最も望ましく、特にシリカ/アルミナ比が大きいため極性が小さい疎水性ゼオライトを用いるとよい。これにより、非極性の臭気分子も吸着するようになり、また雰囲気の湿度に依存することなく臭気分子を吸脱着できるため、多様な臭気分子を吸脱着できる脱臭体を実現できる。また、ゼオライトやセピオライト等にはナトリウムやカリウム成分を極力除去した
ものを用いることが望ましい。これによりアルデヒド類からカルボン酸への転化率が向上する。
As the physical adsorbent 4, a substance having a physical adsorption action such as zeolite, silica gel, sepiolite, alumina, activated carbon or the like is used. However, a zeolite having a fast adsorption / desorption rate of an odorous substance is most desirable. It is preferable to use a hydrophobic zeolite having a small particle size. As a result, non-polar odor molecules can be adsorbed, and the odor molecules can be adsorbed and desorbed without depending on the humidity of the atmosphere, so that a deodorant capable of adsorbing and desorbing various odor molecules can be realized. In addition, it is desirable to use zeolite or sepiolite from which sodium and potassium components are removed as much as possible. This improves the conversion rate of aldehydes to carboxylic acids.

本実施の形態で用いた疎水性ゼオライトは0.1〜10μm程度の径であるが、この大きさに限定されるものではない。しかしながら、大きさを小さくした方が、同体積での表面積を大きくとることができるので好ましい。さらに、物理吸着剤4の形は図中にあるような球状に限定されるものではなく、また実際は物理吸着剤4の一次粒子が集まり、二次粒子を形成したり、さらには三次粒子を形成したりした粒子が担体3へ担持されていると考えられる。脱臭体の表面に凹凸を設けることにより、単位体積あたりの表面積を増やすことができるようになり、より効果的である。   The hydrophobic zeolite used in the present embodiment has a diameter of about 0.1 to 10 μm, but is not limited to this size. However, it is preferable to reduce the size because the surface area can be increased with the same volume. Furthermore, the shape of the physical adsorbent 4 is not limited to the spherical shape as shown in the figure, and actually, the primary particles of the physical adsorbent 4 gather to form secondary particles or even tertiary particles. It is considered that the damaged particles are supported on the carrier 3. By providing irregularities on the surface of the deodorizing body, the surface area per unit volume can be increased, which is more effective.

本実施の形態では、脱臭体1に有機繊維で構成される平板および波形板を交互に積層されたハニカム構造体を用いたが、物理吸着剤4と触媒酸化物5との混合物を格子状に押出成型を行ったハニカム構造体を用いても良い。これにより、バインダを用いることがなくハニカム構造体全体を物理吸着剤4と触媒酸化物5とにすることができるので、吸着効果およびカルボン酸への転化率が高い脱臭体を実現できる。   In the present embodiment, a honeycomb structure in which flat plates and corrugated plates made of organic fibers are alternately stacked on the deodorizing body 1 is used, but the mixture of the physical adsorbent 4 and the catalyst oxide 5 is formed in a lattice shape. An extruded honeycomb structure may be used. Thereby, since the whole honeycomb structure can be made into the physical adsorbent 4 and the catalyst oxide 5 without using a binder, the deodorizing body with a high adsorption effect and the conversion rate to carboxylic acid is realizable.

触媒酸化物5は、コバルトを主成分とする酸化物でスピネル型の結晶構造のCo3O4とすることが望ましい。その他、Mn、Fe、Ni、Cu、Znなどの遷移金属を加え、スピネル型構造の複合酸化物としても良い。これは、スピネル型構造の酸化物触媒がアルデヒド類を酸化し岩塩型構造となり、次に岩塩型構造が空気中の酸素により酸化されスピネル型構造に戻り、その繰り返しで触媒作用を発揮するため、スピネル型構造を選択することでアルデヒド類をカルボン酸へ転化する性能が高く、カルボン酸への転化率の高い脱臭体を実現できる。また、本実施の形態で用いた触媒酸化物5も0.1〜10μm程度の径であるが、この大きさに限定されるものではない。しかしながら、大きさを小さくした方が、同体積での表面積を大きくとることができるので好ましい。さらに、触媒酸化物5の形も図中にあるような球状に限定されるものではなく、また実際は触媒酸化物5の一次粒子が集まり、二次粒子を形成したり、さらには三次粒子を形成したりした粒子が担体3へ担持されていると考えられる。触媒酸化物5もアンカー効果もしくは物理的な結合もしくは化学的な結合などの作用により、担体3あるいは物理吸着剤4に担持されている。   The catalyst oxide 5 is preferably an oxide containing cobalt as a main component and Co3O4 having a spinel crystal structure. In addition, transition metals such as Mn, Fe, Ni, Cu, and Zn may be added to form a composite oxide having a spinel structure. This is because the spinel type oxide catalyst oxidizes aldehydes to form a rock salt type structure, and then the rock salt type structure is oxidized by oxygen in the air to return to the spinel type structure, and the catalytic action is exhibited by repetition of that, By selecting a spinel structure, it is possible to realize a deodorant having a high performance for converting aldehydes to carboxylic acids and a high conversion rate to carboxylic acids. The catalyst oxide 5 used in the present embodiment also has a diameter of about 0.1 to 10 μm, but is not limited to this size. However, it is preferable to reduce the size because the surface area can be increased with the same volume. Further, the shape of the catalyst oxide 5 is not limited to the spherical shape as shown in the figure, and the primary particles of the catalyst oxide 5 are actually gathered to form secondary particles or even tertiary particles. It is considered that the damaged particles are supported on the carrier 3. The catalyst oxide 5 is also supported on the support 3 or the physical adsorbent 4 by an action such as an anchor effect or a physical bond or a chemical bond.

次に担持方法について説明する。物理吸着剤4と触媒酸化物5との担体3への担持方法については、スプレーなどを用いた噴霧法、ディップ法などあるが、担体3が無機繊維の場合、物理吸着剤4と触媒酸化物5と必要に応じてバインダを水や溶剤などに分散させ、ハニカム構造体をそのスラリーに浸漬することで担持するディップ法が望ましい。また担体3が有機繊維の場合、抄紙工程中に有機繊維に加えて物理吸着剤4と触媒酸化物5とを混合しておくことで抄紙を行い、これらを担持させることができる。ディップ法の場合、粉末状の物理吸着剤4と触媒酸化物5とを分散させスラリーを作製するが、物理吸着剤4および触媒酸化物5の平均径は小さい方が望ましく、一次粒子の平均径で1μm以下程度が望ましい。さらには、なるべく凝集が起こらないように水や溶媒に分散させることが望ましく、必要に応じて分散剤を添加すると良い。   Next, the carrying method will be described. The method for supporting the physical adsorbent 4 and the catalyst oxide 5 on the carrier 3 includes a spraying method using a spray or the like, a dip method, and the like. When the carrier 3 is an inorganic fiber, the physical adsorbent 4 and the catalyst oxide are used. 5 and a dip method in which a binder is dispersed in water or a solvent as required, and the honeycomb structure is immersed in the slurry to carry the dip method. In the case where the carrier 3 is an organic fiber, paper can be made and supported by mixing the physical adsorbent 4 and the catalyst oxide 5 in addition to the organic fiber during the paper making process. In the case of the dip method, a powdery physical adsorbent 4 and the catalyst oxide 5 are dispersed to produce a slurry. The average diameter of the physical adsorbent 4 and the catalyst oxide 5 is preferably small, and the average diameter of the primary particles Is preferably about 1 μm or less. Furthermore, it is desirable to disperse in water or a solvent so that aggregation does not occur as much as possible, and a dispersant may be added as necessary.

以下、脱臭体に対する実験例を示す。
(実験1)
疎水性ゼオライトと、四三酸化コバルトCo3O4(以下、本実施の形態ではコバルト触媒Aという)を水に分散させ、バインダとして固形分濃度20wt%のナトリウムフリーのコロイダルシリカ(以下、本実施の形態ではバインダAという)を加え、水と疎水性ゼオライトとコバルト触媒AとバインダAとの比が8:1:1:1のスラリー(以下、本実施の形態ではスラリーAという)を作製した。
Hereafter, the experiment example with respect to a deodorizing body is shown.
(Experiment 1)
Hydrophobic zeolite and tribasic cobalt tetraoxide Co3O4 (hereinafter referred to as cobalt catalyst A in the present embodiment) are dispersed in water, and a sodium-free colloidal silica (hereinafter referred to in the present embodiment) having a solid concentration of 20 wt% as a binder. Binder A) was added, and a slurry having a ratio of water, hydrophobic zeolite, cobalt catalyst A, and binder A of 8: 1: 1: 1 (hereinafter referred to as slurry A in the present embodiment) was produced.

また、疎水性ゼオライトと、コバルト触媒Aを水に分散させ、バインダとしてナトリウム安定型コロイダルシリカ(以下、本実施の形態ではバインダBという)を加え、水と疎水性ゼオライトとコバルト触媒AとバインダBとの比が8:1:1:1のスラリー(以下、本実施の形態ではスラリーBという)を作製した。   Further, hydrophobic zeolite and cobalt catalyst A are dispersed in water, sodium stable colloidal silica (hereinafter referred to as binder B in this embodiment) is added as a binder, and water, hydrophobic zeolite, cobalt catalyst A and binder B are added. And a ratio of 8: 1: 1: 1 (hereinafter referred to as slurry B in this embodiment).

また、コバルト触媒Aを水に分散させ、バインダAを加え、水とコバルト触媒AとバインダAとの比が4:1:1のスラリー(以下、本実施の形態ではスラリーCという)を作製した。   Further, cobalt catalyst A was dispersed in water, binder A was added, and a slurry having a ratio of water, cobalt catalyst A, and binder A of 4: 1: 1 (hereinafter referred to as slurry C in the present embodiment) was produced. .

次に、セルロース繊維からなるハニカム構造体(120×36×t10、160セル/inch2)を3つ用意した(以下、本実施の形態ではそれぞれ、ハニカムA、ハニカムB、ハニカムCという)。ハニカムAをスラリーAへ、ハニカムBをスラリーBへ、ハニカムCをスラリーCへ各々浸漬し、130℃での乾燥を2回繰り返し、各々に0.1g/ccで担持した。なおハニカムBは、重量が9.8gで計算上ナトリウム分が約1wt%含有しているものである。 Next, three honeycomb structures (120 × 36 × t10, 160 cells / inch 2 ) made of cellulose fibers were prepared (hereinafter referred to as honeycomb A, honeycomb B, and honeycomb C in this embodiment). The honeycomb A was immersed in the slurry A, the honeycomb B was immersed in the slurry B, and the honeycomb C was immersed in the slurry C. The drying at 130 ° C. was repeated twice, and each was supported at 0.1 g / cc. The honeycomb B has a weight of 9.8 g and a calculated sodium content of about 1 wt%.

また、白金を30mg担持したセルロース繊維からなるハニカム構造体と、マンガン:コバルトが3:1の複合酸化物を0.05g/cc担持したハニカム構造体(120×36×t10、160セル/inch2)を用意した(以下、本実施例ではそれぞれハニカムD、Eという)。 Further, a honeycomb structure made of cellulose fibers carrying 30 mg of platinum and a honeycomb structure carrying 0.05 g / cc of a composite oxide of 3: 1 manganese: cobalt (120 × 36 × t10, 160 cells / inch 2 (Hereinafter referred to as honeycombs D and E in this example).

作製した3種類および用意した2種類のハニカムサンプルそれぞれにアセトアルデヒドを空間速度(以下、SVという)1200、濃度100ppmで連続通気を行い、入口側と出口側のアセトアルデヒド濃度をガスクロマトグラフ(検出器FID)により測定した。また、出口側の酢酸濃度を検知管により測定した。結果を(表1)に示す。なお、ハニカムAを用いた実験が実施例1、ハニカムBを用いた実験が実施例2、ハニカムCを用いた実験が実施例3、ハニカムDを用いた実験が比較例1、ハニカムEを用いた実験が比較例2である。   Acetaldehyde was continuously aerated at a space velocity (hereinafter referred to as SV) of 1200 and a concentration of 100 ppm to each of the three types of prepared honeycomb samples and the prepared two types of honeycomb samples, and the concentration of acetaldehyde on the inlet side and the outlet side was measured with a gas chromatograph (detector FID). It was measured by. Further, the acetic acid concentration on the outlet side was measured with a detector tube. The results are shown in (Table 1). The experiment using the honeycomb A was Example 1, the experiment using the honeycomb B was Example 2, the experiment using the honeycomb C was Example 3, the experiment using the honeycomb D was Comparative Example 1, and the honeycomb E was used. This experiment was Comparative Example 2.

Figure 2007105215
Figure 2007105215

(表1)より、コバルト触媒Aはアセトアルデヒドを酢酸に変える触媒として働き、また白金などと比較して高い活性を有している。また、アセトアルデヒドから変わった酢酸はゼオライトに吸着保持されることが可能である。さらには、ナトリウムを含む実施例2は一度活性が落ち、また元に戻っている。これは、ナトリウムがイオン状態となり、コバルト触媒A、酸素、アセトアルデヒド間の電子の授受を阻害するためであると考えられ、酢酸ナトリウムなどの化合物を形成することでカチオンが少なくなり、電子授受の影響をなくすことができると考えられる。
(実験2)
疎水性ゼオライトとコバルト触媒Aを水に分散させ、バインダAを加え、水と疎水性ゼオライトとコバルト触媒AとバインダAとの比が8:1:1:1のスラリー(以下、本実施の形態ではスラリーDという)と、活性炭とコバルト触媒Aとを水に分散させ、バインダAを加え、水と活性炭とコバルト触媒AとバインダAとの比が8:1:1:1のスラリー(以下、本実施の形態ではスラリーEという)を作製した。
From Table 1, the cobalt catalyst A functions as a catalyst for converting acetaldehyde into acetic acid, and has higher activity than platinum. In addition, acetic acid changed from acetaldehyde can be adsorbed and held on the zeolite. In addition, Example 2 containing sodium once lost activity and was back. This is thought to be because sodium is in an ionic state and inhibits the transfer of electrons between cobalt catalyst A, oxygen, and acetaldehyde. The formation of a compound such as sodium acetate reduces the number of cations, and the effects of electron transfer Can be eliminated.
(Experiment 2)
Hydrophobic zeolite and cobalt catalyst A are dispersed in water, binder A is added, and a slurry in which the ratio of water, hydrophobic zeolite, cobalt catalyst A, and binder A is 8: 1: 1: 1 (hereinafter, this embodiment) Then, the slurry D), the activated carbon and the cobalt catalyst A are dispersed in water, the binder A is added, and a slurry having a ratio of water, activated carbon, cobalt catalyst A, and binder A of 8: 1: 1: 1 (hereinafter, In this embodiment, the slurry E is prepared.

次に、セルロース繊維からなるハニカム構造体(120×36×t10、160セル/inch2)を2つ用意した(以下、本実施の形態ではそれぞれ、ハニカムD、ハニカムEという)。ハニカムDをスラリーDへ、ハニカムEをスラリーEへ各々浸漬し、130℃での乾燥を2回繰り返し、各々に0.1g/ccで担持した。 Next, two honeycomb structures (120 × 36 × t10, 160 cells / inch 2 ) made of cellulose fibers were prepared (hereinafter referred to as honeycomb D and honeycomb E, respectively in the present embodiment). The honeycomb D was immersed in the slurry D and the honeycomb E was immersed in the slurry E, respectively, and drying at 130 ° C. was repeated twice, and each was supported at 0.1 g / cc.

作製した2種類のハニカムサンプルにファンを取り付け、各サンプルをそれぞれ10ppmのアセトアルデヒド濃度に調整した40L容器の中へ入れた。容器内の温度は約20℃であった。270L/minの流量でサンプルを通過するようにファンを調整し、実験開始から60分後の酢酸濃度を検知管により測定した。   A fan was attached to the two types of honeycomb samples produced, and each sample was placed in a 40 L container adjusted to a 10% acetaldehyde concentration. The temperature in the container was about 20 ° C. The fan was adjusted to pass through the sample at a flow rate of 270 L / min, and the acetic acid concentration 60 minutes after the start of the experiment was measured with a detector tube.

実験後、それぞれのサンプルを容器から取り出し、臭気のない場所でファンを作動させ、約20℃で40分間通気を行った。その後、上記実験を行った。これら一連の実験、通気を10回繰り返した。(表2)に実験結果を示す。なお、ハニカムDを用いた実験が実施例4、ハニカムEを用いた実験が比較例3である。なお「N.D」は検出限界(0.05ppm)以下を示す。   After the experiment, each sample was taken out of the container, the fan was operated in a place where there was no odor, and aeration was performed at about 20 ° C. for 40 minutes. Thereafter, the above experiment was performed. These series of experiments and aeration were repeated 10 times. (Table 2) shows the experimental results. The experiment using the honeycomb D is Example 4, and the experiment using the honeycomb E is Comparative Example 3. “ND” indicates a detection limit (0.05 ppm) or less.

Figure 2007105215
Figure 2007105215

(表2)より、実施例4については10回目の酢酸濃度が0.1ppmと小さく、比較例3は1.0ppmと大きい。これは、ゼオライトは活性炭と比較して、通気により酢酸が脱着され再生率が高いことを示している。   From Table 2, the tenth acetic acid concentration in Example 4 is as small as 0.1 ppm, and Comparative Example 3 is as large as 1.0 ppm. This indicates that the zeolite has a higher regeneration rate due to the desorption of acetic acid by aeration than the activated carbon.

これらより、酸化コバルト触媒とゼオライトによりアセトアルデヒドを常温で酢酸へと転化し、吸着除去できる脱臭体を実現でき、また通気による脱着で物理吸着作用を有する吸着剤を再生させることができるので、メンテナンスフリーで長期間使用できる脱臭体を提供することができる。   From these, it is possible to realize a deodorant that can be adsorbed and removed by converting acetaldehyde to acetic acid at room temperature with a cobalt oxide catalyst and zeolite, and it is possible to regenerate the adsorbent with physical adsorption action by desorption by aeration, so maintenance is free The deodorizing body which can be used for a long time can be provided.

(実施の形態2)
図2は本発明の第2の実施例における脱臭体の模式図である。部屋あるいは車10内部に脱臭装置11が設置されている。脱臭装置11は吸気手段13と、吸気口14と、脱臭用のフィルタ15と、脱臭された空気を部屋に戻す導入口17と、臭気を含む空気20を部屋あるいは車内から排気する排気口19からなる。また、導入口17と排気口19との間には、これらを切り替える切替弁18がある。なお、本発明の脱臭装置は空気調和機や換気扇等に取り付けて、あるいは組み込んで用いることもできる。
(Embodiment 2)
FIG. 2 is a schematic view of a deodorizing body in the second embodiment of the present invention. A deodorizing device 11 is installed in the room or the vehicle 10. The deodorizing device 11 includes an intake means 13, an intake port 14, a filter 15 for deodorization, an introduction port 17 for returning the deodorized air to the room, and an exhaust port 19 for exhausting air 20 containing odor from the room or the interior of the vehicle. Become. Further, a switching valve 18 for switching between these is provided between the introduction port 17 and the exhaust port 19. In addition, the deodorizing apparatus of this invention can also be attached to an air conditioner, a ventilation fan, etc., or can also be incorporated and used.

吸気手段13はシロッコファン、ターボファン、プロペラファン、クロスフローファン、貫流ファン等が一般の吸気手段として使用され、特に限定するものではない。本実施の形態ではプロペラファンを用いた。また、吸気手段13はフィルター15への送風手段としても用いることができる。   As the intake means 13, a sirocco fan, a turbo fan, a propeller fan, a cross flow fan, a cross-flow fan or the like is used as a general intake means, and is not particularly limited. In this embodiment, a propeller fan is used. The intake means 13 can also be used as a blowing means for the filter 15.

次に動作方法について説明する。部屋あるいは車10内で臭気が発生した場合、脱臭装置11は臭気を含む空気12を吸気手段13により吸気口14を通して吸い込み、フィルタ15を通り脱臭され、脱臭された空気16は導入口17を通り、部屋10へ戻される。フィルタ15が飽和吸着に達し、部屋あるいは車10内に臭気がない場合、切替弁18によって通気方向を室外へ排出する排気口19側へ切り替え、吸気手段13を作動させ通気させることにより、臭気が飽和吸着した物理吸着作用を有する吸着剤から臭気を脱着させ、脱着させた臭気を含む空気20を室外あるいは車外へ排出することができる。
したがって、この動作を繰り返すことにより、メンテナンスフリーで長期間使用できる脱臭装置を実現できる。
Next, an operation method will be described. When odor is generated in the room or the car 10, the deodorizing device 11 sucks the odorous air 12 through the intake port 14 by the intake means 13, passes through the filter 15 and is deodorized, and the deodorized air 16 passes through the inlet port 17. Returned to the room 10. When the filter 15 reaches saturation adsorption and there is no odor in the room or the car 10, the switching valve 18 switches the ventilation direction to the exhaust port 19 side that discharges to the outside, and the intake means 13 is operated to ventilate the odor. Odor is desorbed from the adsorbent having a physical adsorption action that is saturated and adsorbed, and the air 20 containing the desorbed odor can be discharged to the outside or outside the vehicle.
Therefore, by repeating this operation, a deodorizing apparatus that can be used for a long time without maintenance can be realized.

(実施の形態3)
図3は、本発明の第10および11の実施の形体における空気調和機の冷凍サイクル構成図、図4は、同空気調和機の室内機の構成を示す概略断面図、図5は、同空気調和機の制御内容を示すブロック図である。
(Embodiment 3)
FIG. 3 is a configuration diagram of the refrigeration cycle of the air conditioner according to the tenth and eleventh embodiments of the present invention, FIG. 4 is a schematic sectional view showing the configuration of the indoor unit of the air conditioner, and FIG. It is a block diagram which shows the control content of a harmony machine.

図3において、301は圧縮機、302は四方弁、303は室外熱交換器、304は減圧機、305は室内熱交換器であり、順次冷媒を通す冷媒配管で接続してヒートポンプ式の冷凍サイクルを形成している。また、306は室内熱交換器305に通風する送風手段となる室内ファン、307は室内熱交換器305を構成する配管(図示せず)の温度を検知する配管温センサ、308は室外熱交換器303に通風する室外ファンである。309は、室内と室外とを連通するダクト(図示せず)を介して、室内機313の通風路中の空気を室外に排出するための排気ファンである。圧縮機301と、四方弁302と、室外熱交換器303と、室外ファン308は、本実施の形態における空気調和機の室外機(図示せず)に内蔵されている。   In FIG. 3, 301 is a compressor, 302 is a four-way valve, 303 is an outdoor heat exchanger, 304 is a pressure reducer, 305 is an indoor heat exchanger, and is connected by a refrigerant pipe through which refrigerant is passed in order, and a heat pump type refrigeration cycle Is forming. Reference numeral 306 denotes an indoor fan serving as a blowing means for ventilating the indoor heat exchanger 305, reference numeral 307 denotes a pipe temperature sensor for detecting the temperature of a pipe (not shown) constituting the indoor heat exchanger 305, and reference numeral 308 denotes an outdoor heat exchanger. This is an outdoor fan that ventilates 303. Reference numeral 309 denotes an exhaust fan for discharging the air in the ventilation path of the indoor unit 313 to the outside through a duct (not shown) that connects the room and the outside. The compressor 301, the four-way valve 302, the outdoor heat exchanger 303, and the outdoor fan 308 are built in the outdoor unit (not shown) of the air conditioner in the present embodiment.

室内機313は、図4に示すように、室内熱交換器305と、室内ファン306と、排気ファン309と、通風路を形成するケーシング310と、室内熱交換器305で熱交換された空気を吹き出す吹出部314に設けられ吹き出される風の向きを変える風向偏向羽根311と、通風路を通過する空気の臭気を除去する脱臭体のフィルタ312から構成されている。また、315は、空気調和機の運転をリモートコントロールするためのリモコンであり、ユーザがリモコン315上で様々な操作をおこなうことが可能となっている。   As shown in FIG. 4, the indoor unit 313 includes an indoor heat exchanger 305, an indoor fan 306, an exhaust fan 309, a casing 310 that forms a ventilation path, and air that has been heat-exchanged by the indoor heat exchanger 305. It is composed of a wind direction deflecting blade 311 that is provided in the blowing unit 314 and changes the direction of the blown wind, and a deodorizing body filter 312 that removes the odor of the air passing through the ventilation path. Reference numeral 315 denotes a remote controller for remotely controlling the operation of the air conditioner. The user can perform various operations on the remote controller 315.

次に、上記構成による空気調和機の空調作用について説明する。   Next, the air conditioning operation of the air conditioner configured as described above will be described.

暖房運転時においては、圧縮機301で吸入し圧縮された冷媒は、四方弁302を経て室内熱交換器305に送られ、ここで凝縮液化する。室内熱交換器305を出た冷媒は減
圧機304で減圧され室外熱交換器303に導かれ、ここで冷媒が蒸発して室外空気(外気)から蒸発潜熱を奪い気化する。そして室外熱交換器303を経た冷媒は、再び四方弁302を経て圧縮機301に吸入される。
During the heating operation, the refrigerant sucked and compressed by the compressor 301 is sent to the indoor heat exchanger 305 through the four-way valve 302, where it is condensed and liquefied. The refrigerant exiting the indoor heat exchanger 305 is depressurized by the decompressor 304 and guided to the outdoor heat exchanger 303, where the refrigerant evaporates and takes the latent heat of evaporation from the outdoor air (outside air) and vaporizes it. The refrigerant that has passed through the outdoor heat exchanger 303 is again sucked into the compressor 301 through the four-way valve 302.

以上のように構成された空気調和機において、以下にその実施の形態について詳述する。   The embodiment of the air conditioner configured as described above will be described in detail below.

図4(a)は空気調和機の室内機313が空調運転をしている様子を概略断面図に示したものである。   FIG. 4A is a schematic cross-sectional view of the air conditioner indoor unit 313 performing air conditioning operation.

ユーザがリモコン315を操作し、空気調和機の空調運転を指示すると、該指令を受け図5の320に示す室内機313に内蔵された制御装置により、配管温センサ307で室内熱交換器305の温度を検知しながら圧縮機301や四方弁302、室内ファン306、風向偏向羽根311などに必要に応じて制御信号が送られ空調運転を開始する。   When the user operates the remote controller 315 to instruct the air conditioning operation of the air conditioner, the control unit built in the indoor unit 313 shown in 320 of FIG. 5 receives the command, and the pipe temperature sensor 307 controls the indoor heat exchanger 305. While detecting the temperature, a control signal is sent to the compressor 301, the four-way valve 302, the indoor fan 306, the wind direction deflecting blade 311 and the like as necessary to start the air conditioning operation.

このとき室内機313の据え付けられた室内に各種の臭気が存在している場合、吸込部から吹出部314に至る通風路中に配置されているフィルタ312によって室内の臭気成分を吸着除去することができる。   At this time, when various odors exist in the room where the indoor unit 313 is installed, the odor components in the room can be adsorbed and removed by the filter 312 disposed in the ventilation path from the suction portion to the blowout portion 314. it can.

なお、空気調和機においては冷房運転中は室内機内部が多湿環境となるため、フィルタ312を構成する吸着剤は疎水性ゼオライトがもっとも望ましいが、吸着剤の種類はこれに限定するものではない。   In the air conditioner, since the interior of the indoor unit becomes a humid environment during the cooling operation, the adsorbent constituting the filter 312 is most preferably a hydrophobic zeolite, but the type of the adsorbent is not limited thereto.

次に、本実施の形態の空気調和機に設けられている、クリーニング運転機能について詳述する。   Next, the cleaning operation function provided in the air conditioner of the present embodiment will be described in detail.

図5において、室内機313に内蔵された制御装置320は、室内熱交換器305を加熱する暖房運転をおこなうことにより、前記室内熱交換機305に付着した臭気の脱着乃至は室内機313の内部の乾燥もしくはヒートショックによりカビ類の繁殖を抑制するクリーニング運転をおこなわせる、クリーニング運転指示手段321を備えている。制御装置320からは、圧縮機301、室内ファン306、排気ファン309、風向偏向羽根311に必要に応じて制御信号が送られる。   In FIG. 5, the control device 320 built in the indoor unit 313 performs a heating operation for heating the indoor heat exchanger 305, so that the odor attached to the indoor heat exchanger 305 is removed or the inside of the indoor unit 313 is installed. A cleaning operation instructing unit 321 is provided for performing a cleaning operation for suppressing the growth of molds by drying or heat shock. A control signal is sent from the control device 320 to the compressor 301, the indoor fan 306, the exhaust fan 309, and the wind direction deflecting blade 311 as necessary.

空気調和機の運転中にリモコン315から停止指令が出されたとき、該指令を受けクリーニング運転指示手段321により、所定の温度T[℃](例えば40℃)を、クリーニング運転における室内熱交換器305の目標温度に設定し、クリーニング運転指示手段321により、配管温センサ307で室内熱交換器305の温度を検知しながら圧縮機301や室内ファン306を制御し、室内熱交換器305の温度を目標温度T[℃]に調節し、クリーニング運転を所定の時間M[分](例えば60分)おこなう。   When a stop command is issued from the remote controller 315 during the operation of the air conditioner, a predetermined temperature T [° C.] (for example, 40 ° C.) is received by the cleaning operation instruction means 321 in response to the command and the indoor heat exchanger in the cleaning operation. The compressor 301 and the indoor fan 306 are controlled by the cleaning operation instruction means 321 while detecting the temperature of the indoor heat exchanger 305 by the pipe temperature sensor 307 by the cleaning operation instruction means 321, and the temperature of the indoor heat exchanger 305 is set. The temperature is adjusted to the target temperature T [° C.], and the cleaning operation is performed for a predetermined time M [minutes] (for example, 60 minutes).

このとき同時に、図4(b)に示すように、臭気除去運転指示手段321により、吹出部314から吹き出される空気をショートサーキットさせる位置へ風向偏向羽根311の位置の制御をおこなう
この結果、室内機313の通風路を室内熱交換機305により加熱された空気が循環し、フィルタ312を高温の空気が通気することとなり、フィルタ312を構成する飽和吸着した物理吸着作用を有する吸着剤から臭気を脱着させることができる。
At the same time, as shown in FIG. 4B, the position of the wind direction deflecting blade 311 is controlled by the odor removal operation instruction means 321 to a position where the air blown out from the blowing portion 314 is short-circuited. The air heated by the indoor heat exchanger 305 circulates in the ventilation path of the machine 313 and high-temperature air is ventilated through the filter 312, so that the odor is desorbed from the adsorbent having a physical adsorption action that constitutes the filter 312 and is saturated. Can be made.

したがって、運転終了毎にクリーニング運転として暖房運転を実施することにより、空気調和機においてメンテナンスフリーで長期間使用できる脱臭機能を実現できる。   Therefore, a deodorizing function that can be used for a long time without maintenance in the air conditioner can be realized by performing the heating operation as the cleaning operation at the end of the operation.

ここで示したのは、リモコン315から発せられた空気調和機の空調運転停止指令を受けて自動的にクリーニング運転としての暖房運転を実施する形態であるが、クリーニング運転の開始をユーザが手動で指示する形態や空調運転開始前にクリーニング運転を自動的に実施する形態など、クリーニング運転を実施するタイミングを任意に定めても同様の効果が期待できるのはいうまでもない。   In this embodiment, an air conditioner operation stop command issued from the remote controller 315 is received to automatically perform a heating operation as a cleaning operation. However, the user manually starts the cleaning operation. Needless to say, the same effect can be expected even if the timing for performing the cleaning operation is arbitrarily determined, such as a mode for instructing or a mode for automatically performing the cleaning operation before the start of the air conditioning operation.

こうしてクリーニング運転により、フィルタ312から臭気成分発生量が徐々に増加してくるが、このとき同時に臭気除去運転指示手段321により排気ファン309に運転指令を出し、室内機313の通風路内の空気を空気をダクトを介して室外に排気するようにすると、吹出部314から吹き出される空気は、風向偏向羽根311によりショートサーキットしており、また排気ファン309の動作により臭気成分が室外に放出され、臭気成分の室内放出を低下させることができるため、室内環境の快適性を損なうことなく、メンテナンスフリーで長期間使用できる脱臭機能を空気調和機に付加することができる。   As a result of the cleaning operation, the amount of odorous components generated from the filter 312 gradually increases. At this time, the odor removal operation instruction means 321 issues an operation command to the exhaust fan 309, and the air in the ventilation path of the indoor unit 313 is removed. When the air is exhausted to the outside through the duct, the air blown out from the blowing portion 314 is short-circuited by the wind direction deflecting blade 311 and the odor component is released to the outside by the operation of the exhaust fan 309. Since indoor release of odor components can be reduced, a deodorizing function that can be used for a long period of time without maintenance can be added to the air conditioner without impairing the comfort of the indoor environment.

以上のように、本発明にかかる脱臭体および脱臭体を用いた脱臭装置は、上述したように生活空間で発生する臭気を吸着除去でき、特に有害なアセトアルデヒドを常温で有害性の小さい酢酸へと転化し、吸着除去できる脱臭体を提供することができ、また人の手を煩わすことなく自動的に吸脱着を制御し、メンテナンスフリーで長期間使用できる脱臭装置を提供することができる。   As described above, the deodorizing body and the deodorizing apparatus using the deodorizing body according to the present invention can adsorb and remove the odor generated in the living space as described above, and convert particularly harmful acetaldehyde into acetic acid that is less harmful at room temperature. It is possible to provide a deodorizing body that can be converted and adsorbed and removed, and to provide a deodorizing apparatus that can automatically control adsorption and desorption without bothering humans and can be used for a long time without maintenance.

さらに、脱臭体は空気調和機、生ごみ処理機、VOC分解機、介護用脱臭機などへ搭載することにより、メンテナンスフリーで長期間利用できる脱臭機能、有害物質分解機能を付加することができるものである。また、脱臭装置は部屋に設置された空気調和機や換気扇、車のカーエアコン等と連動させることができるものである。   Furthermore, the deodorizing body can be added to a maintenance-free long-term deodorizing function and a toxic substance decomposing function by installing it in an air conditioner, garbage disposal machine, VOC decomposer, nursing care deodorizer, etc. It is. The deodorizing device can be linked to an air conditioner, a ventilation fan, a car air conditioner, etc. installed in the room.

(a)本発明の第1の実施の形態における脱臭体を示す外観模式図(b)本発明の第1の実施の形態における脱臭体表面の拡大模式図(A) Schematic external view showing the deodorizing body in the first embodiment of the present invention (b) Enlarged schematic view of the surface of the deodorizing body in the first embodiment of the present invention 本発明の第2の実施の形態における脱臭装置を示す模式図The schematic diagram which shows the deodorizing apparatus in the 2nd Embodiment of this invention. 本発明の第3の実施の形態における空気調和機の冷凍サイクル構成図The refrigeration cycle block diagram of the air conditioner in the 3rd Embodiment of this invention 本発明の第3の実施の形態における空気調和機の室内機の構成を示す概略断面図Schematic sectional drawing which shows the structure of the indoor unit of the air conditioner in the 3rd Embodiment of this invention 本発明の第3の実施の形態における空気調和機の制御内容を示すブロック図The block diagram which shows the control content of the air conditioner in the 3rd Embodiment of this invention.

符号の説明Explanation of symbols

1 脱臭体
2 通気方向
3 担体
4 物理吸着作用を有する吸着剤
5 触媒作用を有する酸化物
10 部屋あるいは車
11 脱臭装置
12 臭気を含む空気
13 吸気手段
14 吸気口
15 フィルター
16 脱臭された空気
17 導入口
18 切替弁
19 排気口
20 臭気を含む空気
301 圧縮機
302 四方弁
303 室外熱交換機
304 減圧機
305 室内熱交換機
306 室内ファン
307 配管温センサ
308 室外ファン
309 排気ファン
310 ケーシング
311 風向偏向羽根
312 フィルタ
313 室内機
314 吹出部
315 リモコン
DESCRIPTION OF SYMBOLS 1 Deodorizing body 2 Air flow direction 3 Support | carrier 4 Adsorbent which has a physical adsorption action 5 Oxide which has a catalytic action 10 Room or vehicle 11 Deodorizing device 12 Air containing odor 13 Intake means 14 Inlet 15 Filter 16 Deodorized air 17 Introduction Port 18 Switching valve 19 Exhaust port 20 Odor containing air 301 Compressor 302 Four-way valve 303 Outdoor heat exchanger 304 Decompressor 305 Indoor heat exchanger 306 Indoor fan 307 Piping temperature sensor 308 Outdoor fan 309 Exhaust fan 310 Casing 311 Wind direction deflecting blade 312 Filter 313 Indoor unit 314 Air outlet 315 Remote control

Claims (11)

物理吸着作用を有する吸着剤と、コバルトを含み触媒作用を有する酸化物と、前記吸着剤および前記酸化物とを担持する担体とから構成され、前記酸化物がアルデヒド類をカルボン酸へ転化後、前記吸着剤で吸着除去することを特徴とした脱臭体。 It is composed of an adsorbent having a physical adsorption action, an oxide containing cobalt and having a catalytic action, and a carrier supporting the adsorbent and the oxide, and the oxide converts an aldehyde into a carboxylic acid, A deodorizing body characterized by being adsorbed and removed by the adsorbent. 吸着剤が疎水性ゼオライトである請求項1記載の脱臭体。 The deodorizing body according to claim 1, wherein the adsorbent is a hydrophobic zeolite. 担体が有機繊維から構成されるハニカム構造体である請求項1記載の脱臭体。 The deodorizing body according to claim 1, wherein the carrier is a honeycomb structure composed of organic fibers. 酸化物が少なくとも吸着剤表面に担持されている請求項1もしくは請求項2記載の脱臭体。 The deodorizing body according to claim 1 or 2, wherein an oxide is supported on at least the adsorbent surface. 吸着剤へ吸着したカルボン酸は通気により脱着し、繰り返し使用可能な請求項1もしくは請求項2記載の脱臭体。 The deodorizing body according to claim 1 or 2, wherein the carboxylic acid adsorbed on the adsorbent is desorbed by aeration and can be used repeatedly. 酸化物はスピネル型構造である請求項1もしくは請求項4記載の脱臭体。 The deodorizer according to claim 1 or 4, wherein the oxide has a spinel structure. 酸化物中のナトリウムおよびカリウム成分は1wt%未満である請求項1、4、6いずれか1項に記載の脱臭体。 The deodorizing body according to any one of claims 1, 4, and 6, wherein a sodium and potassium component in the oxide is less than 1 wt%. アルデヒド類はアセトアルデヒドであり、カルボン酸は酢酸である請求項1記載の脱臭体。 The deodorizer according to claim 1, wherein the aldehyde is acetaldehyde and the carboxylic acid is acetic acid. 少なくとも臭気を含む空気を導入する吸気口と、前記臭気を含む空気を吸気する吸気手段と、前記吸気手段により吸気した空気に含まれる臭気を脱臭するフィルタと、前記フィルタにより脱臭された空気を室内あるいは車内へ導入する導入口と、前記フィルタから脱着した臭気を室外あるいは車外へ排気する排気口とを備え、前記フィルタが請求項1〜8いずれか1項に記載の脱臭体である脱臭装置。 An air inlet for introducing air containing at least odor, an air intake means for taking in air containing the odor, a filter for deodorizing odor contained in air sucked by the air intake means, and air deodorized by the filter Or the deodorizing apparatus which is provided with the introduction port introduce | transduced into a vehicle, and the exhaust port which exhausts the odor remove | desorbed from the said filter to the exterior or the exterior of a vehicle, and the said filter is a deodorizing body of any one of Claims 1-8. 吸込部から吹出部に至る通風路に、室内熱交換器と前記室内熱交換器にて温度調整された空気を室内に送り出す室内送風機と、吸入した空気に含まれる臭気を脱臭するフィルタを備え、空気調和機の空調運転停止中に、室内熱交換器を加熱し、前記室内熱交換機により暖められた空気の少なくとも一部が室内機内を循環する、クリーニング運転機能を設け、前記フィルタが請求項1〜8いずれか1項に記載の脱臭体であることを特徴とする空気調和機。 In the ventilation path from the suction part to the blowing part, an indoor heat exchanger and an indoor fan for sending out the air whose temperature is adjusted by the indoor heat exchanger to the room, and a filter for deodorizing the odor contained in the sucked air, The filter is provided with a cleaning operation function in which an indoor heat exchanger is heated while air conditioning operation of the air conditioner is stopped, and at least a part of the air heated by the indoor heat exchanger circulates in the indoor unit. The air conditioner characterized by being a deodorizing body of any one of -8. 室内機通風路内の空気を室外に排気する排気機能を備え、クリーニング運転の実施中乃至は実施後に、前記排気手段を動作させることを特徴とする請求項10に記載の空気調和機。 The air conditioner according to claim 10, further comprising an exhaust function for exhausting air in the indoor unit ventilation path to the outside and operating the exhaust unit during or after the cleaning operation.
JP2005298646A 2005-10-13 2005-10-13 Air conditioner Active JP5061448B2 (en)

Priority Applications (4)

Application Number Priority Date Filing Date Title
JP2005298646A JP5061448B2 (en) 2005-10-13 2005-10-13 Air conditioner
MYPI20064320 MY150279A (en) 2005-10-13 2006-10-12 Deodorizer, and deodorizing device and air conditioner using same
ES06122272T ES2387814T3 (en) 2005-10-13 2006-10-13 Air conditioner using cobalt oxide deodorant composition
EP20060122272 EP1775013B1 (en) 2005-10-13 2006-10-13 Air conditioner using deodorising composition with cobalt oxide

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2005298646A JP5061448B2 (en) 2005-10-13 2005-10-13 Air conditioner

Publications (2)

Publication Number Publication Date
JP2007105215A true JP2007105215A (en) 2007-04-26
JP5061448B2 JP5061448B2 (en) 2012-10-31

Family

ID=38031546

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2005298646A Active JP5061448B2 (en) 2005-10-13 2005-10-13 Air conditioner

Country Status (1)

Country Link
JP (1) JP5061448B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012241646A (en) * 2011-05-20 2012-12-10 Mitsubishi Motors Corp System and method for recovering and utilizing steam in exhaust
CN105561749A (en) * 2015-12-21 2016-05-11 天津欧盼科技开发有限公司 Method for comprehensively treating indoor environmental pollution

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4838291A (en) * 1971-09-20 1973-06-05
JPH04371228A (en) * 1991-06-17 1992-12-24 Agency Of Ind Science & Technol Gold catalyst for removal of malodorous substance
JPH05115748A (en) * 1991-10-25 1993-05-14 Matsushita Electric Ind Co Ltd Removal of malodor
JPH0631128A (en) * 1992-07-15 1994-02-08 Babcock Hitachi Kk Deodorizing method
JPH10272365A (en) * 1997-03-28 1998-10-13 Nichias Corp Dedorization catalyst and element for deodorization
JPH10318550A (en) * 1997-05-20 1998-12-04 Daikin Ind Ltd Air conditioner with deodorizer
JP2000217897A (en) * 1999-02-01 2000-08-08 Matsushita Electric Ind Co Ltd Air purifying material and air purifying device using same
JP2001179032A (en) * 1999-12-27 2001-07-03 Daikin Ind Ltd Air cleaning equipment, air cleaner and air conditioner
JP2003320002A (en) * 2002-05-07 2003-11-11 Matsushita Electric Ind Co Ltd Deodorant body

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4838291A (en) * 1971-09-20 1973-06-05
JPH04371228A (en) * 1991-06-17 1992-12-24 Agency Of Ind Science & Technol Gold catalyst for removal of malodorous substance
JPH05115748A (en) * 1991-10-25 1993-05-14 Matsushita Electric Ind Co Ltd Removal of malodor
JPH0631128A (en) * 1992-07-15 1994-02-08 Babcock Hitachi Kk Deodorizing method
JPH10272365A (en) * 1997-03-28 1998-10-13 Nichias Corp Dedorization catalyst and element for deodorization
JPH10318550A (en) * 1997-05-20 1998-12-04 Daikin Ind Ltd Air conditioner with deodorizer
JP2000217897A (en) * 1999-02-01 2000-08-08 Matsushita Electric Ind Co Ltd Air purifying material and air purifying device using same
JP2001179032A (en) * 1999-12-27 2001-07-03 Daikin Ind Ltd Air cleaning equipment, air cleaner and air conditioner
JP2003320002A (en) * 2002-05-07 2003-11-11 Matsushita Electric Ind Co Ltd Deodorant body

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2012241646A (en) * 2011-05-20 2012-12-10 Mitsubishi Motors Corp System and method for recovering and utilizing steam in exhaust
CN105561749A (en) * 2015-12-21 2016-05-11 天津欧盼科技开发有限公司 Method for comprehensively treating indoor environmental pollution

Also Published As

Publication number Publication date
JP5061448B2 (en) 2012-10-31

Similar Documents

Publication Publication Date Title
CN204478340U (en) A kind of regenerative air cleaning system
JP4948817B2 (en) Deodorant with active oxygen scavenging ability and air purifier using the same
WO2010100739A1 (en) Air conditioner
JP4904695B2 (en) Deodorizing body, method for producing deodorizing body, and deodorizing apparatus using the same
JP5061448B2 (en) Air conditioner
JP2006255251A (en) Deodorizer, and deodorizing equipment using the deodorizer
JP2006280906A (en) Deodorization filter for suction and exhaust port of air-conditioning equipment, and its manufacturing method
JPH11221442A (en) Composite deodorizing and dust collecting filter
JP2007037670A (en) Deodorizer and deodorizing device
JP4058210B2 (en) Photocatalyst member
JP2001314491A (en) Air purifying filter
JP5172087B2 (en) Deodorizing body and deodorizing apparatus using the deodorizing body
JP4926446B2 (en) Deodorizing body and deodorizing apparatus using the same
JP2000254452A (en) Air purifier
EP1775013B1 (en) Air conditioner using deodorising composition with cobalt oxide
JP2000217897A (en) Air purifying material and air purifying device using same
CN100528246C (en) Air conditioner
JP4887756B2 (en) Deodorizing body and deodorizing apparatus using the same
JPH05237342A (en) Purifier of gas
JP5103750B2 (en) Adsorption element and humidity control air conditioner
JP2009052753A (en) Ventilation fan
JP2007285563A (en) Air-conditioner
JPH11347334A (en) Deodorizing unit and deodorizing device
JP2004209433A (en) Deodorization filter and blowing device
JPH10296043A (en) Gad adsorption filter for air conditioning device

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20081003

RD01 Notification of change of attorney

Free format text: JAPANESE INTERMEDIATE CODE: A7421

Effective date: 20091126

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20100729

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20111129

A521 Request for written amendment filed

Free format text: JAPANESE INTERMEDIATE CODE: A523

Effective date: 20120126

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20120710

A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20120723

R151 Written notification of patent or utility model registration

Ref document number: 5061448

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R151

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20150817

Year of fee payment: 3