JP2007144278A - Deodorizer, and air conditioner equipped with the same - Google Patents

Deodorizer, and air conditioner equipped with the same Download PDF

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JP2007144278A
JP2007144278A JP2005340065A JP2005340065A JP2007144278A JP 2007144278 A JP2007144278 A JP 2007144278A JP 2005340065 A JP2005340065 A JP 2005340065A JP 2005340065 A JP2005340065 A JP 2005340065A JP 2007144278 A JP2007144278 A JP 2007144278A
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deodorizing apparatus
catalyst
discharge electrode
noble metal
supported
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Sota Komae
草太 小前
Takuya Furuhashi
拓也 古橋
Junichiro Hoshizaki
潤一郎 星崎
Shiro Takeuchi
史朗 竹内
Akira Shiga
彰 志賀
Reiji Morioka
怜司 森岡
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Mitsubishi Electric Corp
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Mitsubishi Electric Corp
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  • Air Filters, Heat-Exchange Apparatuses, And Housings Of Air-Conditioning Units (AREA)
  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a deodorizer capable of enhancing decomposition and removal efficiencies of odorous gas components or toxic volatile chemical substances in air by a small amount of a noble metal-based catalyst and charged electric power, and cleaning the air more inexpensively with lower energy. <P>SOLUTION: This device is provided with a discharge electrode 1 applied with a high voltage and a grounding electrode 4 disposed in a flow space of treating object fluid; and a catalyst part 2 disposed between the discharge electrode 1 and grounding electrode 4 and cleaning the odorous gas components and toxic volatile chemical substances. The catalyst part 2 carries a mixture formed by mixing one or more kinds of porous adsorbent having mesopores or micropores, such as zeolite, activated carbon or silica gel; a porous metal oxide having fine pore structure consisting of mainly transit metal, such as manganese oxide or titanium oxide; and noble metals like platinum or palladium. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

この発明は、空気中の臭気ガス成分や有害揮発性化学物質を除去し、空気を清浄化する脱臭装置およびそれを備えた空気調和装置に関するものである。 The present invention relates to a deodorizing device that removes odorous gas components and harmful volatile chemical substances in the air and cleans the air, and an air conditioner equipped with the same.

従来の脱臭装置は、被処理流体の流通空間で放電により低温プラズマを発生させる放電手段と、該放電手段における放電場中または放電場の下流側に配置された触媒手段とを備え、該触媒手段が貴金属系触媒を含むプラズマ触媒反応器からなるものである(例えば、特許文献1参照)。 A conventional deodorizing apparatus includes discharge means for generating low-temperature plasma by discharge in a flow space of a fluid to be treated, and catalyst means disposed in the discharge field of the discharge means or downstream of the discharge field, and the catalyst means Consists of a plasma catalytic reactor containing a noble metal catalyst (see, for example, Patent Document 1).

特開2002−336645号公報(第4−5頁、図1)JP 2002-336645 A (page 4-5, FIG. 1)

従来の脱臭装置では、プラズマ触媒反応器において、触媒手段に含まれる貴金属系触媒を多量に用いなければ臭気ガス成分や有害揮発性化学物質の分解・除去効率が低くなるため、貴金属系触媒を多量に用いることになり、高コストになってしまうという問題点があった。また、プラズマ触媒反応器での放電のために投入する電力に対して臭気ガス成分や有害揮発性化学物質の分解・除去効率が低いという問題点があった。 In conventional deodorization equipment, if the precious metal catalyst contained in the catalyst means is not used in a large amount in the plasma catalyst reactor, the decomposition and removal efficiency of odorous gas components and harmful volatile chemicals will be low. There was a problem that it would be expensive to use. In addition, there is a problem that the efficiency of decomposition / removal of odorous gas components and harmful volatile chemicals is low with respect to the electric power supplied for discharge in the plasma catalytic reactor.

この発明は、上述のような課題を解決するためになされたもので、少量の貴金属系触媒および投入電力で空気中の臭気ガス成分や有害揮発性化学物質の分解・除去効率を向上させることができ、より低コスト、低エネルギーで空気を清浄化することができる脱臭装置およびそれを備えた空気調和装置を得るものである。 The present invention has been made to solve the above-described problems, and can improve the decomposition and removal efficiency of odorous gas components and harmful volatile chemical substances in the air with a small amount of noble metal catalyst and input power. It is possible to obtain a deodorizing apparatus capable of purifying air at a lower cost and with lower energy and an air conditioner equipped with the same.

この発明に係る脱臭装置は、被処理流体の流通空間内に配置され、高電圧が印加される放電電極およびその対向電極と、被処理流体内の臭気ガス成分や有害揮発性化学物質を浄化する触媒部とを備えた脱臭装置において、前記触媒部は前記放電電極と前記対向電極の間に配置され、吸着剤、金属酸化物、貴金属を混合して担持したものである。 A deodorizing apparatus according to the present invention is disposed in a circulation space of a fluid to be treated, and purifies a discharge electrode to which a high voltage is applied and its counter electrode, and an odorous gas component and a harmful volatile chemical substance in the fluid to be treated. In the deodorization apparatus including a catalyst part, the catalyst part is disposed between the discharge electrode and the counter electrode, and carries a mixture of an adsorbent, a metal oxide, and a noble metal.

この発明に係る脱臭装置は、触媒部が放電電極と対向電極の間に配置され、吸着剤、金属酸化物、貴金属を混合して担持したことにより、触媒上での吸着作用、金属酸化物および貴金属による酸化作用や分解作用、放電のラジカル生成による分解作用を組み合わせ、相乗効果を生み出すことで、低コスト、低エネルギーで、臭気ガス成分や有害揮発性化学物質の分解、除去効率を向上させ、室内の空気を清浄化することができる。   In the deodorizing apparatus according to the present invention, the catalyst part is disposed between the discharge electrode and the counter electrode, and adsorbent, metal oxide, and noble metal are mixed and supported, so that the adsorption action on the catalyst, the metal oxide, and By combining the oxidation action and decomposition action by precious metals and the decomposition action by radical generation of discharge, synergistic effect is created, improving the decomposition and removal efficiency of odorous gas components and harmful volatile chemical substances at low cost and low energy, Indoor air can be cleaned.

実施の形態1.
図1は、この発明を実施するための実施の形態1における脱臭装置の分解斜視図である。
図1において、脱臭装置6は、ステンレスや銅等の金属からなり、先端部が鋭角で複数の突起部を有する平板形状の放電電極1と、触媒部2と、プラスチック等の絶縁体からなり、放電電極1および触媒部2を収納し、脱臭装置6の前面を支えるケーシング3と、金属や導電性プラスチック等の導電性材料からなり、メッシュ等の開口を有する接地電極(放電電極1の対向電極)4と、ケーシング3および接地電極4を支持して脱臭装置6全体を支える支持カバー5とから構成される。
なお、脱臭装置6は、ケーシング3、放電電極1、触媒部2、接地電極4、支持カバー5の順に風上側から風下側になるように通風路上に配置される。
Embodiment 1 FIG.
1 is an exploded perspective view of a deodorizing apparatus according to Embodiment 1 for carrying out the present invention.
In FIG. 1, the deodorizing device 6 is made of a metal such as stainless steel or copper, and is made of a flat plate-shaped discharge electrode 1 having a sharp tip and a plurality of protrusions, a catalyst portion 2, and an insulator such as plastic, A casing 3 that houses the discharge electrode 1 and the catalyst unit 2 and supports the front surface of the deodorizing device 6, and a ground electrode (a counter electrode of the discharge electrode 1) made of a conductive material such as metal or conductive plastic and having an opening such as a mesh ) 4 and a support cover 5 that supports the casing 3 and the ground electrode 4 to support the entire deodorizing device 6.
In addition, the deodorizing apparatus 6 is arrange | positioned on a ventilation path so that it may become a leeward side from a windward side in order of the casing 3, the discharge electrode 1, the catalyst part 2, the ground electrode 4, and the support cover 5. FIG.

ここで、触媒部2は、ペーパーセラミックやコージェライト等の基材に、通風路内の風の流れと平行な例えばハニカム状、コルゲート状、四角状の開口部を有するとともに、ゼオライト、活性炭、シリカゲル等のメソ孔あるいはミクロ孔を有する多孔質吸着剤と、酸化マンガン、酸化チタン等の遷移金属を中心とした細孔構造を有する多孔質金属酸化物と、白金、パラジウム等の貴金属とがそれぞれ1種類以上混合されて基材に担持され、さらに接地電極4と接触するように構成される。よって、触媒部2は、基材に多孔質吸着剤、多孔質金属酸化物、貴金属を担持させた絶縁材料と導電材料の混合体であり、導電性を多少有するため、接地電極4と接触することにより接地電極4と同電位になる。 Here, the catalyst part 2 has, for example, a honeycomb-like, corrugated-, or square-shaped opening parallel to the air flow in the ventilation path on a base material such as paper ceramic or cordierite, and zeolite, activated carbon, silica gel 1 each of a porous adsorbent having mesopores or micropores such as a porous metal oxide having a pore structure centered on a transition metal such as manganese oxide or titanium oxide, and a noble metal such as platinum or palladium. More than one kind is mixed and supported on the base material, and is further configured to come into contact with the ground electrode 4. Therefore, the catalyst portion 2 is a mixture of an insulating material and a conductive material in which a porous adsorbent, a porous metal oxide, and a noble metal are supported on a base material. Since the catalyst portion 2 has some conductivity, it is in contact with the ground electrode 4. As a result, it becomes the same potential as the ground electrode 4.

また、接地電極4の開口部は触媒部2の開口部よりも大きくなるように形成される。さらに、放電電極1と接地電極4には高圧電源(図示せず)が接続され、両者の間に3.5kV〜10kVの正または負の直流高電圧が印加される。 Further, the opening of the ground electrode 4 is formed to be larger than the opening of the catalyst unit 2. Further, a high voltage power source (not shown) is connected to the discharge electrode 1 and the ground electrode 4, and a positive or negative DC high voltage of 3.5 kV to 10 kV is applied between them.

次に、動作について説明する。
まず、高圧電源(図示せず)から放電電極1と接地電極4の間に供給される直流電圧により、放電電極1から触媒部2にコロナ放電が発生する。このとき、ケーシング3から吸い込まれた空気中の臭気ガス成分や揮発性有機化合物、例えばアセトアルデヒド、ホルムアルデヒド等は、触媒部2上の疎水性ゼオライト、酸化マンガン等の吸着部で一旦捕捉され、上記コロナ放電により生成された酸素ラジカルや水酸基ラジカルなどの活性種により分解処理され、無害化され、吸着部から解離する。
Next, the operation will be described.
First, corona discharge is generated from the discharge electrode 1 to the catalyst unit 2 by a DC voltage supplied between the discharge electrode 1 and the ground electrode 4 from a high-voltage power supply (not shown). At this time, odorous gas components and volatile organic compounds in the air sucked from the casing 3 such as acetaldehyde and formaldehyde are once captured by the adsorbing portion of the hydrophobic zeolite, manganese oxide and the like on the catalyst portion 2, and the corona It is decomposed and rendered harmless by active species such as oxygen radicals and hydroxyl radicals generated by discharge, and dissociates from the adsorption part.

ここで、上記コロナ放電は触媒部2上の貴金属に対しても優位に働き、貴金属もコロナ放電による分解を助ける働きをする。特に貴金属の中でも白金やパラジウムは酸素との親和性が強く、多くの酸素原子を吸着する性質を有する。すなわち、コロナ放電により貴金属は活性化され、貴金属上の吸着酸素の解離が促され、酸素原子の吸脱着速度は促進される。貴金属から解離した酸素原子は、高濃度時には主に多孔質吸着剤の吸着部で捕捉された臭気ガス成分や揮発性有機化合物へ、低濃度時には主に多孔質金属酸化物の吸着部で捕捉された臭気ガス成分や揮発性有機化合物へと向かい、酸化反応により臭気ガス成分や揮発性有機化合物を分解し、解離させる。このため、吸脱着速度の向上はそのまま分解速度の向上へと繋がる。 Here, the corona discharge works preferentially on the noble metal on the catalyst portion 2, and the noble metal also works to assist decomposition by the corona discharge. In particular, among noble metals, platinum and palladium have a strong affinity for oxygen and have a property of adsorbing many oxygen atoms. That is, the noble metal is activated by corona discharge, the dissociation of the adsorbed oxygen on the noble metal is promoted, and the adsorption / desorption rate of oxygen atoms is promoted. Oxygen atoms dissociated from noble metals are mainly trapped in the odorous gas components and volatile organic compounds trapped in the porous adsorbent adsorbent at high concentrations, and mainly in the porous metal oxide adsorbers at low concentrations. The odor gas components and volatile organic compounds are decomposed and dissociated by an oxidation reaction. For this reason, the improvement in the adsorption / desorption rate directly leads to the improvement in the decomposition rate.

また、貴金属から解離した酸素原子は、コロナ放電によって分解された臭気ガス成分や揮発性有機化合物の分解生成物を酸化することで、臭気ガス成分や揮発性有機化合物の分解生成物の再結合を防止することもできるため、臭気ガス成分や揮発性有機化合物の分解がさらに促進されることになる。 In addition, oxygen atoms dissociated from precious metals oxidize odor gas components and volatile organic compound decomposition products decomposed by corona discharge, thereby recombining odor gas components and volatile organic compound decomposition products. Since it can also be prevented, the decomposition of odorous gas components and volatile organic compounds is further promoted.

さらに、触媒部において、触媒部2表面上に対して放電エネルギーを均一に印加させるため、触媒部2に担持(添着)された多孔質吸着剤、多孔質金属酸化物、貴金属の各成分は高分散な状態で混合されていることが望ましく、さらには、多孔質吸着剤と多孔質金属酸化物粒子と貴金属粒子が隣接して接触した状態であることが望ましい。
また、担持させる多孔質吸着剤および多孔質金属酸化物は、臭気ガスや有害揮発性化学物質の触媒部2上への吸着性能を高めるため、メソ孔あるいはミクロ孔を有する多孔体であることが望ましい。
Further, in the catalyst part, each component of the porous adsorbent, the porous metal oxide, and the noble metal supported (attached) on the catalyst part 2 is high so that the discharge energy is uniformly applied to the surface of the catalyst part 2. It is desirable that they are mixed in a dispersed state. Furthermore, it is desirable that the porous adsorbent, the porous metal oxide particles, and the noble metal particles are in contact with each other.
In addition, the porous adsorbent and the porous metal oxide to be supported are porous bodies having mesopores or micropores in order to enhance the adsorption performance of the odor gas and harmful volatile chemical substances onto the catalyst part 2. desirable.

次に、この脱臭装置の実験品による検証実験について説明する。
図2はこの発明の実施の形態1を示す脱臭装置の実験品の分解斜視図、図3はこの脱臭装置の実験品によるアセトアルデヒドの分解・除去性能を示す図である。
図2において、脱臭装置の実験品11は、ステンレスや銅等の金属からなり、2つの針状の突起部を有する放電電極1と、ハニカム状の開口部を有する基材に多孔質吸着剤、多孔質金属酸化物、貴金属を担持させた触媒部2と、放電電極1および触媒部2を覆い、プラスチック等の絶縁体からなり、風路用の穴8aを設けた中央カバー8と、中央カバー8の風路上流側に配置され、放電電極1を保持し、風路用の穴9aを設けた前面カバー9と、金属、貴金属、導電性プラスチック等の導電性材料からなり、メッシュ等の開口を有する接地電極4と、接地電極4を保持し、風路用の穴10aを設けた後部カバー10とから構成される。なお、放電電極1と接地電極4の間には、直流電圧が印加され、コロナ放電が行われる。
Next, a verification experiment using an experimental product of the deodorizing apparatus will be described.
FIG. 2 is an exploded perspective view of an experimental product of the deodorizing apparatus showing Embodiment 1 of the present invention, and FIG. 3 is a diagram showing the acetaldehyde decomposition / removal performance of the experimental product of the deodorizing apparatus.
In FIG. 2, an experimental product 11 of a deodorizing apparatus is made of a metal such as stainless steel or copper, and includes a discharge electrode 1 having two needle-like protrusions, a porous adsorbent on a substrate having a honeycomb-like opening, A catalyst cover 2 supporting a porous metal oxide and a noble metal; a center cover 8 that covers the discharge electrode 1 and the catalyst part 2 and is made of an insulating material such as plastic and provided with a hole 8a for an air passage; The front cover 9 is disposed upstream of the air passage 8 and holds the discharge electrode 1 and is provided with a hole 9a for the air passage. The front cover 9 is made of a conductive material such as metal, precious metal, or conductive plastic, and has an opening such as a mesh. And a rear cover 10 that holds the ground electrode 4 and is provided with an air passage hole 10a. A DC voltage is applied between the discharge electrode 1 and the ground electrode 4 to perform corona discharge.

図3はこの発明の実施の形態1を示す脱臭装置の実験品における投入電力とアセトアルデヒド除去率との関係を示す図であり、触媒部2に添着物としてパラジウム(2g/l)のみ(図3のA)、疎水性ゼオライト+酸化マンガン(同B)、白金(2g/l)のみ(同C)、疎水性ゼオライト+酸化マンガン+白金(0.025g/l)(同D)、疎水性ゼオライト+酸化マンガン+パラジウム(0.5g/l)(同E)をそれぞれ用い、電圧印加した場合のアセトアルデヒド除去状況を示す。 FIG. 3 is a diagram showing the relationship between the input power and the acetaldehyde removal rate in the experimental product of the deodorizing apparatus showing Embodiment 1 of the present invention, and only palladium (2 g / l) as an adduct is attached to the catalyst unit 2 (FIG. 3). A), hydrophobic zeolite + manganese oxide (same B), platinum (2 g / l) only (same C), hydrophobic zeolite + manganese oxide + platinum (0.025 g / l) (same D), hydrophobic zeolite The state of acetaldehyde removal when a voltage is applied using + manganese oxide + palladium (0.5 g / l) (same E) is shown.

図3により、パラジウム(2g/l)のみでは投入電力が増えるにつれてアセトアルデヒド除去率が徐々に大きくなるものの、25%付近で上限に達してしまう。また、白金(2g/l)のみでは投入電力が増えてもアセトアルデヒド除去率が約15%とほぼ一定であり、除去率が低いままである。
そこで、貴金属をより少なくしてゼオライトと酸化マンガンを混合し添着する、例えば疎水性ゼオライト+酸化マンガン+白金(0.025g/l)の場合では、投入電力が増えるにつれてアセトアルデヒド除去率が大きくなり、投入電力0.2Wではアセトアルデヒド除去率が約38%になり、白金(2g/l)のみの場合よりもアセトアルデヒド除去率が向上する。また、疎水性ゼオライト+酸化マンガン+パラジウム(0.5g/l)の場合でも投入電力が増えるにつれてアセトアルデヒド除去率が大きくなり、投入電力0.2Wではアセトアルデヒド除去率が約42%になり、パラジウム(2g/l)のみよりもアセトアルデヒド除去率が向上するとともに、疎水性ゼオライト+酸化マンガンの場合と比較しても少ない投入電力で高いアセトアルデヒドの除去効果が得られる。
According to FIG. 3, with palladium (2 g / l) alone, the acetaldehyde removal rate gradually increases as the input power increases, but reaches the upper limit in the vicinity of 25%. Further, with only platinum (2 g / l), even if the input power is increased, the acetaldehyde removal rate is almost constant at about 15%, and the removal rate remains low.
Therefore, in the case of, for example, hydrophobic zeolite + manganese oxide + platinum (0.025 g / l) mixed with zeolite and manganese oxide with less precious metal, the acetaldehyde removal rate increases as the input power increases. When the input power is 0.2 W, the acetaldehyde removal rate is about 38%, and the acetaldehyde removal rate is improved as compared with the case of only platinum (2 g / l). Further, even in the case of hydrophobic zeolite + manganese oxide + palladium (0.5 g / l), the acetaldehyde removal rate increases as the input power increases, and at an input power of 0.2 W, the acetaldehyde removal rate becomes about 42%. The acetaldehyde removal rate is improved as compared with 2 g / l) alone, and a high acetaldehyde removal effect can be obtained with less input power as compared with the case of hydrophobic zeolite + manganese oxide.

次に、脱臭装置の実験品11におけるアセトアルデヒド除去時に発生するオゾン対策について説明する。図4はこの発明の実施の形態1を示す脱臭装置の実験品における投入電力とオゾン発生量の関係を示す図であり、図において、触媒部2に添着物としてパラジウム(2g/l)のみ(図4のA)、疎水性ゼオライト+酸化マンガン(同B)、白金(2g/l)のみ(同C)、疎水性ゼオライト+酸化マンガン+白金(0.025g/l)(同D)、疎水性ゼオライト+酸化マンガン+パラジウム(0.5g/l)(同E)をそれぞれ用いた場合を示す。 Next, a countermeasure for ozone generated when removing acetaldehyde in the experimental product 11 of the deodorizing apparatus will be described. FIG. 4 is a diagram showing the relationship between the input power and the amount of ozone generated in the experimental product of the deodorization apparatus showing Embodiment 1 of the present invention. In the figure, only palladium (2 g / l) is attached to the catalyst unit 2 as an adduct ( 4A), hydrophobic zeolite + manganese oxide (same B), platinum (2 g / l) only (same C), hydrophobic zeolite + manganese oxide + platinum (0.025 g / l) (same D), hydrophobic Shows the case of using the active zeolite + manganese oxide + palladium (0.5 g / l) (same E).

オゾンは人体に影響があり、臭気性も強いため、発生量を1.0mg/h以下に抑制することが望ましく、投入電力あたりのオゾン発生量を少なくする必要がある。そこで、図4により、触媒部2に疎水性ゼオライト+酸化マンガン+白金またはパラジウムを添着した(図4のDおよびE)場合には、投入電力あたりのオゾン発生量が最も少なくなり、さらに、投入電力を約5W以下にすることによりオゾン発生量を1.0mg/h以下に抑制することができることがわかる。 Since ozone affects the human body and has strong odor, it is desirable to suppress the generation amount to 1.0 mg / h or less, and it is necessary to reduce the ozone generation amount per input power. Therefore, according to FIG. 4, when hydrophobic zeolite + manganese oxide + platinum or palladium is attached to the catalyst part 2 (D and E in FIG. 4), the amount of ozone generated per input electric power becomes the smallest, and the input It can be seen that the ozone generation amount can be suppressed to 1.0 mg / h or less by setting the power to about 5 W or less.

よって、触媒部に吸着剤+金属酸化物+貴金属を混合して添着した場合は、貴金属のみを添着する場合や吸着剤+金属酸化物を添着する場合よりも投入電力あたりのオゾン発生量を抑制できるため、投入電力を高く設定することができ、臭気ガスや有害揮発性化学物質の除去率を向上させることができ、さらに、投入電力を約5W以下にすることによりオゾン発生量を1.0mg/h以下に抑制することができる。 Therefore, when adsorbent + metal oxide + noble metal is mixed and attached to the catalyst part, the amount of ozone generated per input power is suppressed compared to the case of adsorbing only precious metal or adsorbent + metal oxide. Therefore, the input power can be set high, the removal rate of odorous gases and harmful volatile chemicals can be improved, and the ozone generation amount can be reduced to 1.0 mg by reducing the input power to about 5 W or less. / h or less.

上記に説明した脱臭装置の構造は、一例として記載したものであり、これに限定されるものではない。例えば突起部を有する放電電極1はこの形状に限定されず、突起部を有さない薄型板状やワイヤー形状であっても同様の効果を奏する。また、触媒部2の構造は、ハニカム状、コルゲート状、四角状に限定されず、ガラスあるいはセラミック、ポリマー材料から成る繊維によって構成された繊維形状、あるいは3次元網目構造を有したセラミック構造体の基材に、多孔質吸着材と、多孔質金属酸化物と、貴金属を担持させた絶縁物と導電材料の混合体とを、担持させた構造であっても同様の効果を奏する。さらに、放電手段として、コロナ放電を一例として記載したが、これに限定されず、例えば、沿面放電、無声放電、などであっても同様の効果を奏する。なお、沿面放電や無声放電を利用する場合は、誘電体が被覆された放電面を有した電極構造を備えることが好ましい。 The structure of the deodorization apparatus demonstrated above is described as an example, and is not limited to this. For example, the discharge electrode 1 having a protrusion is not limited to this shape, and the same effect can be obtained even if it is a thin plate or wire having no protrusion. Further, the structure of the catalyst portion 2 is not limited to a honeycomb shape, a corrugated shape, or a square shape, but is a glass shape made of glass or ceramic, fibers made of a polymer material, or a ceramic structure having a three-dimensional network structure. The same effect can be obtained even in a structure in which a porous adsorbent, a porous metal oxide, and a mixture of an insulator and a conductive material supporting a noble metal are supported on a substrate. Furthermore, although the corona discharge is described as an example of the discharge means, the present invention is not limited to this. For example, the same effect can be obtained even with creeping discharge, silent discharge, and the like. When creeping discharge or silent discharge is used, it is preferable to provide an electrode structure having a discharge surface covered with a dielectric.

以上のように、脱臭装置6は、触媒部2に、ゼオライト、活性炭、シリカゲル等のメソ孔あるいはミクロ孔を有する多孔質吸着剤、酸化マンガン、酸化チタン等の遷移金属を中心とした細孔構造を有する多孔質金属酸化物、白金、パラジウム等の貴金属を混合し担持した材料を配置することにより、触媒部2上での吸着作用、金属酸化物・貴金属による酸化作用や分解作用、放電のラジカル生成による分解作用を組み合わせ、相乗効果を生み出すことにより、低コストで、低エネルギーで臭気ガス成分や有害揮発性化学物質の分解・除去効率を向上でき、室内の空気を清浄化することができる。   As described above, the deodorizing apparatus 6 has a pore structure centered on transition metals such as a porous adsorbent having mesopores or micropores such as zeolite, activated carbon and silica gel, manganese oxide, and titanium oxide in the catalyst portion 2. By disposing a porous metal oxide containing platinum, a material that supports and supports a noble metal such as platinum or palladium, adsorption action on the catalyst part 2, oxidation action or decomposition action by the metal oxide / noble metal, discharge radical By combining the decomposition action by generation and creating a synergistic effect, the decomposition and removal efficiency of odorous gas components and harmful volatile chemical substances can be improved at low cost and with low energy, and the indoor air can be purified.

実施の形態2.
この実施の形態2では、実施の形態1で示した脱臭装置6を備えた空気調和装置について説明する。
図5はこの発明を実施するための実施の形態2における脱臭装置を備えた空気調和装置の正面図であり、便宜上、前面パネルを外したものを示す。図6はこの脱臭装置を備えた空気調和装置の側面断面図である。図6において、脱臭装置6は空気調和装置12の通風路入口、例えば正面に向かって右側上方の熱交換器13の前面に取り付けられる。これにより、空気調和装置12の運転時には、ファン14を稼動させ、室内空気を空気調和装置12正面上方から脱臭装置6へ取り込み、脱臭装置6で清浄化した後、熱交換器13で加熱または冷却し、空気調和装置12正面下方から室内へ送出する。
Embodiment 2. FIG.
In the second embodiment, an air conditioner including the deodorizing device 6 shown in the first embodiment will be described.
FIG. 5 is a front view of an air-conditioning apparatus provided with a deodorizing apparatus according to Embodiment 2 for carrying out the present invention, and shows a state in which a front panel is removed for convenience. FIG. 6 is a side cross-sectional view of an air conditioner equipped with this deodorizing device. In FIG. 6, the deodorizing apparatus 6 is attached to the ventilation path inlet of the air conditioning apparatus 12, for example, the front surface of the heat exchanger 13 on the upper right side toward the front. As a result, when the air conditioner 12 is in operation, the fan 14 is operated, the indoor air is taken into the deodorizer 6 from above the front of the air conditioner 12, cleaned by the deodorizer 6, and then heated or cooled by the heat exchanger 13. Then, the air conditioner 12 is sent into the room from the front lower side.

図7はこの発明を実施するための実施形態2における脱臭装置の触媒部の斜視図であり、この脱臭装置の触媒部以外の構成は実施の形態1と同様であるため、図示を省略する。図8はこの脱臭装置の触媒部における平方インチあたりのセル数と圧力損失との関係を示す図、図9はこの脱臭装置の触媒部におけるセル数とアセトアルデヒド除去率との関係を示す図である。
ここで、脱臭装置6の触媒部2において、平方インチあたり200〜500セルのコルゲート状開口部を有するセラミックペーパー基材を用い、この基材に吸着剤、金属酸化物、貴金属を添着している。これにより、空気中の臭気ガス成分や揮発性有機化合物の除去率の向上が見込める。
FIG. 7 is a perspective view of the catalyst unit of the deodorizing apparatus according to the second embodiment for carrying out the present invention. Since the configuration other than the catalyst unit of the deodorizing apparatus is the same as that of the first embodiment, the illustration is omitted. FIG. 8 is a diagram showing the relationship between the number of cells per square inch and the pressure loss in the catalyst portion of this deodorizing apparatus, and FIG. 9 is a diagram showing the relationship between the number of cells in the catalyst portion of this deodorizing apparatus and the acetaldehyde removal rate. .
Here, in the catalyst part 2 of the deodorizing apparatus 6, a ceramic paper base material having corrugated openings of 200 to 500 cells per square inch is used, and adsorbent, metal oxide, and noble metal are attached to this base material. . Thereby, the improvement of the removal rate of the odorous gas component and volatile organic compound in the air can be expected.

次に、空気調和装置の脱臭装置の動作について説明する。
まず、脱臭装置6を空気調和装置12の通風路入口に備え、臭気成分を除去する場合に、触媒部2におけるより効果的な構造としては、ハニカム状、コルゲート状、四角状の開口部を有する構造、または繊維形状が挙げられる。特に、図7に示すようなコルゲート状の触媒を用いた場合には、通風時の圧損が低く、流通が良いため、臭気成分の触媒への衝突確率が高く、優れた吸着性能を有する。
Next, operation | movement of the deodorizing apparatus of an air conditioning apparatus is demonstrated.
First, when the deodorizing device 6 is provided at the inlet of the air passage of the air conditioner 12 and odor components are removed, the catalyst portion 2 has a honeycomb, corrugated or square opening as a more effective structure. Examples include structure or fiber shape. In particular, when a corrugated catalyst as shown in FIG. 7 is used, since the pressure loss during ventilation is low and the circulation is good, the collision probability of the odor component to the catalyst is high and the adsorption performance is excellent.

また、図8は通風方向に厚さ10mmの触媒部2を用いた場合の流速1m/sにおける圧力損失のセル数依存性を示し、セル数の増加に伴い圧力損失は二次関数的に上昇することがわかる。そのため、空気調和装置12はより少ないセル数のコルゲート状触媒を用いる必要がある。特に、500セル以下の圧力損失は、空気調和装置12において外気吸引に大きな影響を与える15Paよりも低い値であるため、500セル以下のコルゲート状の構造を有する触媒を用いることが、外気吸引に大きな影響が少なく、望ましい。 FIG. 8 shows the cell number dependence of the pressure loss at a flow rate of 1 m / s when the catalyst part 2 having a thickness of 10 mm is used in the ventilation direction. The pressure loss increases in a quadratic function as the number of cells increases. I understand that Therefore, the air conditioner 12 needs to use a corrugated catalyst having a smaller number of cells. In particular, since the pressure loss of 500 cells or less is a value lower than 15 Pa, which has a great influence on the outside air suction in the air conditioner 12, it is necessary to use a catalyst having a corrugated structure of 500 cells or less for the outside air suction. Less significant and desirable.

さらに、図9は空気調和装置12に備えたコルゲート状の構造を有する触媒部2において、アセトアルデヒド除去効率のセル数依存性を示し、200〜500セル間ではセトアルデヒド除去率が高く、触媒の効果を十分に発揮でき、吸着・分解効果が最も高いことを示している。
なお、コルゲート状の開口部を有する触媒部2を中心に説明したが、ハニカム状、四角状の開口部を有する構造や繊維形状であっても同様の効果が得られる。
Furthermore, FIG. 9 shows the cell number dependence of the acetaldehyde removal efficiency in the catalyst part 2 having a corrugated structure provided in the air conditioner 12, and the effect of the catalyst is high between 200 and 500 cells. Can be fully demonstrated, and the adsorption / decomposition effect is the highest.
In addition, although it demonstrated centering on the catalyst part 2 which has a corrugated opening part, the same effect is acquired even if it is a structure and fiber shape which have a honeycomb-shaped and square-shaped opening part.

以上のことから、コルゲート状、ハニカム状、四角状の開口部を有する触媒部2を200〜500セル間で用いる、または繊維形状の触媒部2を用いることにより、空気調和装置12内での脱臭装置6は最適動作を実現することができ、貴金属による分解・酸化反応、触媒上の吸着成分における放電による分解が活性化され、脱臭装置6の分解、除去効果を最大限に生かすことが可能である。
また、脱臭装置を空気調和装置の通風路入口に備えたことにより、臭気ガス成分や有害揮発性化学物質の分解、除去して清浄化した空気を加熱または冷却でき、快適な冷暖房を行うことができる。
From the above, deodorization in the air conditioner 12 is achieved by using the catalyst part 2 having corrugated, honeycomb, or square openings between 200 to 500 cells or using the fiber-shaped catalyst part 2. The device 6 can realize the optimum operation, and the decomposition / oxidation reaction by the noble metal and the decomposition by the discharge of the adsorbed component on the catalyst are activated, and the decomposition / removal effect of the deodorizing device 6 can be maximized. is there.
In addition, by providing a deodorizing device at the air passage inlet of the air conditioner, it is possible to heat or cool the air that has been purified by decomposing and removing odorous gas components and harmful volatile chemical substances, and performing comfortable air conditioning. it can.

実施の形態3.
この実施の形態3では、実施の形態1で示した脱臭装置6の放電電極の材質をステンレスや銅等の金属から貴金属に変更したものについて説明する。
図10はこの発明を実施するための実施の形態3における脱臭装置の放電電極の材質とアセトアルデヒド残存率との関係を示す図である。なお、脱臭装置6の構成は図1や図2と同様であり、放電電極1の材質が異なるだけであるため、図示を省略し、図1や図2を流用する。
Embodiment 3 FIG.
In the third embodiment, a description will be given of a case where the material of the discharge electrode of the deodorizing apparatus 6 shown in the first embodiment is changed from a metal such as stainless steel or copper to a noble metal.
FIG. 10 is a diagram showing the relationship between the material of the discharge electrode of the deodorizing apparatus and the acetaldehyde residual rate in Embodiment 3 for carrying out the present invention. In addition, since the structure of the deodorizing apparatus 6 is the same as that of FIG.1 and FIG.2, and only the materials of the discharge electrode 1 differ, illustration is abbreviate | omitted and FIG.1 and FIG.2 are diverted.

次に、動作について、図1を用いて説明する。
脱臭装置6において、白金、パラジウム、ロジウム、ルテニウム、イリジウム、金、銀等の貴金属を一種類以上用いて形成された放電電極1、あるいは上記貴金属成分をコーティング(被膜)した放電電極1を用いる。これにより、脱臭装置6中の通風路の前半部分において、高圧電源(図示せず)による放電電極1への高電圧印加により活性化された放電電極1上の貴金属成分による臭気成分の吸着除去・酸化分解が行われ、かつ、貴金属からの酸素原子の解離によりオゾン生成が促進される。さらに、コロナ放電により生成された放電ラジカル(酸素ラジカルや水酸基ラジカル等)により臭気成分や有害揮発性化学物質が分解され、その後の再結合が貴金属から解離した酸素原子により抑制されることで、放電電極1および放電内部での臭気成分の分解除去率が向上する。よって、通風路を流れる臭気成分の濃度が低下し、触媒部2の吸着量が低減されるとともに、臭気成分の吸着除去・分解反応も効率的に行われ、脱臭装置6全体の除去率が大きく向上する。
Next, the operation will be described with reference to FIG.
In the deodorizing device 6, a discharge electrode 1 formed using one or more kinds of noble metals such as platinum, palladium, rhodium, ruthenium, iridium, gold, silver, or the discharge electrode 1 coated (coated) with the noble metal component is used. As a result, in the first half of the ventilation path in the deodorizing device 6, adsorption / removal of odor components by the noble metal component on the discharge electrode 1 activated by applying a high voltage to the discharge electrode 1 by a high voltage power source (not shown). Oxidation decomposition is performed, and ozone generation is promoted by dissociation of oxygen atoms from the noble metal. Furthermore, discharge radicals (oxygen radicals, hydroxyl radicals, etc.) generated by corona discharge decompose odor components and harmful volatile chemical substances, and subsequent recombination is suppressed by oxygen atoms dissociated from noble metals. The decomposition removal rate of the odor components in the electrode 1 and the discharge is improved. Therefore, the concentration of the odorous component flowing through the ventilation path is reduced, the adsorption amount of the catalyst unit 2 is reduced, and the adsorption removal / decomposition reaction of the odorous component is also efficiently performed, so that the removal rate of the deodorizing apparatus 6 as a whole is large. improves.

次に、この脱臭装置の実験品11による検証実験について、図2、図10を用いて説明する。
図10は、脱臭装置の実験品11に一定濃度のアセトアルデヒドを流し続けた場合に、放電電極1の素材の違いによるアセトアルデヒド残存率の経時変化を示すものである。そこで、図2の脱臭装置の実験品11において、放電電極1をステンレスおよび白金により形成し、通風路に一定濃度の臭気成分を流通させると、開始直後はアセトアルデヒド吸着除去・分解率が高く残存率が低くなるが、常に一定濃度のアセトアルデヒドを流入しているため、時間の経過に伴い徐々に吸着量が減衰し、アセトアルデヒド残存率が増加していく。そして、所定の時間が経過すると、触媒部2上へのアセトアルデヒドの吸着速度とコロナ放電による触媒部2上での分解速度が平衡に達し、残存率の変化が少なくなる。
Next, a verification experiment using the experimental product 11 of the deodorizing apparatus will be described with reference to FIGS.
FIG. 10 shows the change over time in the residual acetaldehyde ratio due to the difference in the material of the discharge electrode 1 when a constant concentration of acetaldehyde is allowed to flow through the experimental product 11 of the deodorization apparatus. Therefore, in the experimental product 11 of the deodorizing apparatus of FIG. 2, when the discharge electrode 1 is made of stainless steel and platinum and a certain concentration of odor components is circulated through the ventilation path, the acetaldehyde adsorption removal / decomposition rate is high immediately after the start and the residual rate However, since a constant concentration of acetaldehyde always flows in, the amount of adsorption gradually decreases with the passage of time, and the residual ratio of acetaldehyde increases. When a predetermined time elapses, the acetaldehyde adsorption rate on the catalyst unit 2 and the decomposition rate on the catalyst unit 2 due to corona discharge reach an equilibrium, and the change in the remaining rate is reduced.

そこで、放電電極1にステンレスを用いた場合と白金を用いた場合のアセトアルデヒド残存率を比較すると、ステンレスよりも白金を用いた方がアセトアルデヒド残存率が常に低い状態を維持していることから、放電電極1での臭気成分除去が白金によって行われ、臭気成分の分解・除去効率および触媒部2の寿命が向上していることがわかる。
なお、放電電極1を白金を用いて形成したものについて説明したが、白金、パラジウム、ロジウム、ルテニウム、イリジウム、金、銀等の貴金属を一種類以上用いて形成する、あるいは上記貴金属成分をコーティングして形成すればよく、同様の効果が得られる。
また、本実施形態の放電電極1を有する脱臭装置6を空気調和装置の通風路入口に設けてもよいことは言うまでも無い。
Therefore, when the residual rate of acetaldehyde is compared between the case where stainless steel is used for the discharge electrode 1 and the case where platinum is used, the residual rate of acetaldehyde is always lower when using platinum than stainless steel. It can be seen that the odor component removal at the electrode 1 is performed by platinum, and the decomposition / removal efficiency of the odor component and the life of the catalyst unit 2 are improved.
In addition, although what formed the discharge electrode 1 using platinum was demonstrated, it formed using 1 or more types of noble metals, such as platinum, palladium, rhodium, ruthenium, iridium, gold | metal | money, silver, or the said noble metal component was coated. The same effect can be obtained.
Moreover, it cannot be overemphasized that the deodorizing apparatus 6 which has the discharge electrode 1 of this embodiment may be provided in the ventilation path entrance of an air conditioning apparatus.

以上のことから、放電電極1を白金、パラジウム、ロジウム、ルテニウム、イリジウム、金、銀等の貴金属を一種類以上用いて形成する、あるいは上記貴金属成分をコーティングして形成することにより、放電電極1および放電内部での臭気成分の分解除去率が向上し、通風路を流れる臭気成分の濃度が低下し、触媒部2の吸着量が低減されるとともに、臭気成分の吸着除去・分解反応も効率的に行われ、脱臭装置6全体の除去率が大きく向上することができる。 From the above, the discharge electrode 1 is formed by using one or more kinds of noble metals such as platinum, palladium, rhodium, ruthenium, iridium, gold and silver, or by coating the noble metal component. In addition, the decomposition and removal rate of odorous components inside the discharge is improved, the concentration of odorous components flowing through the ventilation path is reduced, the amount of adsorption of the catalyst unit 2 is reduced, and the odorous component removal and decomposition reaction is also efficient. The removal rate of the entire deodorizing device 6 can be greatly improved.

この発明の実施の形態1を示す脱臭装置の分解斜視図である。It is a disassembled perspective view of the deodorizing apparatus which shows Embodiment 1 of this invention. この発明の実施の形態1を示す脱臭装置の実験品の分解斜視図である。It is a disassembled perspective view of the experimental product of the deodorizing apparatus which shows Embodiment 1 of this invention. この発明の実施の形態1を示す脱臭装置の実験品における投入電力とアセトアルデヒド除去率との関係を示す図である。It is a figure which shows the relationship between the input electric power and the acetaldehyde removal rate in the experimental product of the deodorizing apparatus which shows Embodiment 1 of this invention. この発明の実施の形態1を示す脱臭装置の実験品における投入電力とオゾン発生量の関係を示す図であるIt is a figure which shows the relationship between the input electric power and ozone generation amount in the experimental product of the deodorizing apparatus which shows Embodiment 1 of this invention. この発明の実施の形態2を示す脱臭装置を備えた空気調和装置の正面図である。It is a front view of the air conditioning apparatus provided with the deodorizing apparatus which shows Embodiment 2 of this invention. この発明の実施の形態2を示す脱臭装置を備えた空気調和装置の側面断面図である。It is side surface sectional drawing of the air conditioning apparatus provided with the deodorizing apparatus which shows Embodiment 2 of this invention. この発明の実施の形態2を示す脱臭装置の触媒部の斜視図である。It is a perspective view of the catalyst part of the deodorizing apparatus which shows Embodiment 2 of this invention. この発明の実施の形態2を示す脱臭装置の触媒部における平方インチあたりのセル数と圧力損失との関係を示す図である。It is a figure which shows the relationship between the cell number per square inch in the catalyst part of the deodorizing apparatus which shows Embodiment 2 of this invention, and a pressure loss. この発明の実施の形態2を示す脱臭装置の触媒部におけるセル数とアセトアルデヒド除去効率との関係を示す図である。It is a figure which shows the relationship between the number of cells in the catalyst part of the deodorizing apparatus which shows Embodiment 2 of this invention, and acetaldehyde removal efficiency. この発明の実施の形態3を示す脱臭装置の放電電極の材質とアセトアルデヒド残存率との関係を示す図である。It is a figure which shows the relationship between the material of the discharge electrode of the deodorizing apparatus which shows Embodiment 3 of this invention, and an acetaldehyde residual rate.

符号の説明Explanation of symbols

1 放電電極、 2 触媒部、 3 ケーシング、 4 接地電極、 5 支持カバー、 6 脱臭装置、 8 中央カバー、9 前面カバー、 10 後部カバー、 11 脱臭装置の実験品、 12 空気調和装置、 13 熱交換器、 14 ファン。   DESCRIPTION OF SYMBOLS 1 Discharge electrode, 2 Catalyst part, 3 Casing, 4 Ground electrode, 5 Support cover, 6 Deodorizer, 8 Center cover, 9 Front cover, 10 Rear cover, 11 Deodorizer experimental product, 12 Air conditioner, 13 Heat exchange 14 fans.

Claims (13)

被処理流体の流通空間内に配置され、高電圧が印加される放電電極およびその対向電極と、被処理流体内の臭気ガス成分や有害揮発性化学物質を浄化する触媒部とを備えた脱臭装置において、前記触媒部は前記放電電極と前記対向電極の間に配置され、吸着剤、金属酸化物、貴金属を混合して担持したことを特徴とする脱臭装置。 A deodorizing apparatus including a discharge electrode and a counter electrode to which a high voltage is applied and a catalyst unit for purifying odorous gas components and harmful volatile chemical substances in the fluid to be treated, which are disposed in the flow space of the fluid to be treated. The deodorizing apparatus according to claim 1, wherein the catalyst unit is disposed between the discharge electrode and the counter electrode, and adsorbent, metal oxide, and noble metal are mixed and supported. 前記触媒部に担持される貴金属は、白金または/およびパラジウムであることを特徴とする請求項1記載の脱臭装置。 The deodorizing apparatus according to claim 1, wherein the noble metal supported on the catalyst portion is platinum and / or palladium. 前記触媒部に担持される吸着剤は、細孔構造を有する多孔体材料であることを特徴とする請求項1記載の脱臭装置。 The deodorizing apparatus according to claim 1, wherein the adsorbent supported on the catalyst part is a porous material having a pore structure. 前記触媒部に担持される吸着剤は、メソ孔あるいはミクロ孔構造を有することを特徴とする請求項1または3記載の脱臭装置。 The deodorizing apparatus according to claim 1 or 3, wherein the adsorbent supported on the catalyst part has a mesopore or micropore structure. 前記触媒部に担持される吸着剤は、ゼオライト、活性炭、シリカのいずれかの1種類以上からなることを特徴とする請求項1、3、4のいずれかに記載の脱臭装置。 The deodorizing apparatus according to any one of claims 1, 3, and 4, wherein the adsorbent supported on the catalyst part is made of at least one of zeolite, activated carbon, and silica. 前記触媒に担持される金属酸化物は、細孔構造を有する多孔体材料であることを特徴とする請求項1記載の脱臭装置。 The deodorizing apparatus according to claim 1, wherein the metal oxide supported on the catalyst is a porous material having a pore structure. 前記触媒に担持される金属酸化物は、遷移金属酸化物であることを特徴とする請求項1または6記載の脱臭装置。 The deodorizing apparatus according to claim 1 or 6, wherein the metal oxide supported on the catalyst is a transition metal oxide. 前記放電電極とその対向電極への投入電力が5W以下であることを特徴とする請求項1記載の脱臭装置。 The deodorizing apparatus according to claim 1, wherein an electric power applied to the discharge electrode and the counter electrode is 5 W or less. 前記触媒部は、ハニカム状、コルゲート状、四角状の開口部を有する形状、あるいは繊維形状であることを特徴とする請求項1記載の脱臭装置。 The deodorizing apparatus according to claim 1, wherein the catalyst portion has a honeycomb shape, a corrugated shape, a shape having a square opening, or a fiber shape. 前記触媒部は、平方インチあたり200〜500セルの開口部を有することを特徴とする請求項1または9記載の脱臭装置。 The deodorizing apparatus according to claim 1 or 9, wherein the catalyst unit has an opening of 200 to 500 cells per square inch. 前記放電電極は、貴金属より形成される、または貴金属で被覆されることを特徴とする請求項1記載の脱臭装置。 The deodorizing apparatus according to claim 1, wherein the discharge electrode is formed of a noble metal or is covered with a noble metal. 前記放電電極が形成される貴金属または被覆される貴金属は、白金、パラジウム、ロジウム、ルテニウム、イリジウム、金、銀のうち1種類以上であることを特徴とする請求項1または11記載の脱臭装置。 The deodorizing apparatus according to claim 1 or 11, wherein the noble metal on which the discharge electrode is formed or the noble metal to be coated is at least one of platinum, palladium, rhodium, ruthenium, iridium, gold, and silver. 前記請求項1〜12のいずれかに記載の脱臭装置を通風路入口に備えたことを特徴とする空気調和装置。 An air-conditioning apparatus comprising the deodorizing apparatus according to any one of claims 1 to 12 at an inlet of a ventilation path.
JP2005340065A 2005-11-25 2005-11-25 Deodorizer, and air conditioner equipped with the same Pending JP2007144278A (en)

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Cited By (6)

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JP2009192130A (en) * 2008-02-14 2009-08-27 Mitsubishi Heavy Ind Ltd Air conditioner
JP2009202137A (en) * 2008-02-29 2009-09-10 Mitsubishi Electric Corp Air treatment apparatus
JP2012517343A (en) * 2009-02-25 2012-08-02 エルジー・ハウシス・リミテッド Catalyst body and method for removing formaldehyde using the same
WO2013042328A1 (en) * 2011-09-21 2013-03-28 株式会社Nbcメッシュテック Device and method for gas treatment using low-temperature plasma and catalyst medium
JP2015511170A (en) * 2012-01-20 2015-04-16 ユニヴァーシティー オブ ニューキャッスル アポン タイン Integrated enhanced biorefinery for gas-liquid conversion
EP3698865A1 (en) * 2019-02-20 2020-08-26 Umicore Ag & Co. Kg Platinum and manganese-containing zeolite

Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009192130A (en) * 2008-02-14 2009-08-27 Mitsubishi Heavy Ind Ltd Air conditioner
JP2009202137A (en) * 2008-02-29 2009-09-10 Mitsubishi Electric Corp Air treatment apparatus
JP2012517343A (en) * 2009-02-25 2012-08-02 エルジー・ハウシス・リミテッド Catalyst body and method for removing formaldehyde using the same
JPWO2013042328A1 (en) * 2011-09-21 2015-03-26 株式会社Nbcメッシュテック Gas processing apparatus and method using low temperature plasma and catalyst body
KR20140079413A (en) * 2011-09-21 2014-06-26 가부시키가이샤 엔비씨 메슈테크 Device and method for gas treatment using low-temperature plasma and catalyst medium
CN103974758A (en) * 2011-09-21 2014-08-06 株式会社Nbc纱纲技术 Device and method for gas treatment using low-temperature plasma and catalyst medium
WO2013042328A1 (en) * 2011-09-21 2013-03-28 株式会社Nbcメッシュテック Device and method for gas treatment using low-temperature plasma and catalyst medium
EP2759330A4 (en) * 2011-09-21 2016-05-04 Nbc Meshtec Inc Device and method for gas treatment using low-temperature plasma and catalyst medium
US9962651B2 (en) 2011-09-21 2018-05-08 Nbc Meshtec, Inc. Device and method for gas treatment using non-thermal plasma and catalyst medium
KR101952354B1 (en) 2011-09-21 2019-05-22 가부시키가이샤 엔비씨 메슈테크 Device and method for gas treatment using non-thermal plasma and catalyst medium
JP2015511170A (en) * 2012-01-20 2015-04-16 ユニヴァーシティー オブ ニューキャッスル アポン タイン Integrated enhanced biorefinery for gas-liquid conversion
EP3698865A1 (en) * 2019-02-20 2020-08-26 Umicore Ag & Co. Kg Platinum and manganese-containing zeolite
WO2020169697A1 (en) * 2019-02-20 2020-08-27 Umicore Ag & Co. Kg Platinum- and manganese-containing zeolite

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