JPH10235154A - Deodorizing filter for deodorizing apparatus or air cleaner - Google Patents
Deodorizing filter for deodorizing apparatus or air cleanerInfo
- Publication number
- JPH10235154A JPH10235154A JP9045615A JP4561597A JPH10235154A JP H10235154 A JPH10235154 A JP H10235154A JP 9045615 A JP9045615 A JP 9045615A JP 4561597 A JP4561597 A JP 4561597A JP H10235154 A JPH10235154 A JP H10235154A
- Authority
- JP
- Japan
- Prior art keywords
- deodorizing
- photocatalyst
- adsorbent
- activated carbon
- deodorizing filter
- 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.)
- Pending
Links
- 230000001877 deodorizing effect Effects 0.000 title claims abstract description 59
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 54
- 239000011941 photocatalyst Substances 0.000 claims abstract description 46
- 239000003463 adsorbent Substances 0.000 claims abstract description 37
- 239000003063 flame retardant Substances 0.000 claims abstract description 18
- 239000000463 material Substances 0.000 claims abstract description 12
- 238000000034 method Methods 0.000 claims abstract description 10
- 238000013032 photocatalytic reaction Methods 0.000 claims abstract description 5
- 239000000843 powder Substances 0.000 claims description 33
- RNFJDJUURJAICM-UHFFFAOYSA-N 2,2,4,4,6,6-hexaphenoxy-1,3,5-triaza-2$l^{5},4$l^{5},6$l^{5}-triphosphacyclohexa-1,3,5-triene Chemical compound N=1P(OC=2C=CC=CC=2)(OC=2C=CC=CC=2)=NP(OC=2C=CC=CC=2)(OC=2C=CC=CC=2)=NP=1(OC=1C=CC=CC=1)OC1=CC=CC=C1 RNFJDJUURJAICM-UHFFFAOYSA-N 0.000 claims description 16
- 239000011230 binding agent Substances 0.000 claims description 12
- WNROFYMDJYEPJX-UHFFFAOYSA-K aluminium hydroxide Chemical compound [OH-].[OH-].[OH-].[Al+3] WNROFYMDJYEPJX-UHFFFAOYSA-K 0.000 claims description 10
- 238000002156 mixing Methods 0.000 claims description 5
- 239000007788 liquid Substances 0.000 claims description 4
- 238000005470 impregnation Methods 0.000 claims description 3
- 238000012423 maintenance Methods 0.000 abstract description 4
- 238000004140 cleaning Methods 0.000 abstract description 2
- 239000012716 precipitator Substances 0.000 abstract description 2
- 230000002708 enhancing effect Effects 0.000 abstract 1
- 229920006395 saturated elastomer Polymers 0.000 abstract 1
- 235000019645 odor Nutrition 0.000 description 22
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 description 21
- IKHGUXGNUITLKF-UHFFFAOYSA-N Acetaldehyde Chemical compound CC=O IKHGUXGNUITLKF-UHFFFAOYSA-N 0.000 description 18
- 239000000835 fiber Substances 0.000 description 18
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 14
- 241000208125 Nicotiana Species 0.000 description 14
- 235000002637 Nicotiana tabacum Nutrition 0.000 description 14
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 9
- 239000000428 dust Substances 0.000 description 8
- 230000001699 photocatalysis Effects 0.000 description 8
- 229910021529 ammonia Inorganic materials 0.000 description 7
- 230000000694 effects Effects 0.000 description 7
- 238000001179 sorption measurement Methods 0.000 description 7
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 description 7
- 239000000126 substance Substances 0.000 description 6
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 5
- -1 aluminum hydroxide Chemical compound 0.000 description 5
- 230000000052 comparative effect Effects 0.000 description 5
- 238000006864 oxidative decomposition reaction Methods 0.000 description 5
- 239000003795 chemical substances by application Substances 0.000 description 4
- 239000000839 emulsion Substances 0.000 description 4
- 230000001953 sensory effect Effects 0.000 description 4
- 239000000779 smoke Substances 0.000 description 4
- 238000009423 ventilation Methods 0.000 description 4
- 239000006096 absorbing agent Substances 0.000 description 3
- 230000002378 acidificating effect Effects 0.000 description 3
- 230000005284 excitation Effects 0.000 description 3
- 238000000465 moulding Methods 0.000 description 3
- 238000011045 prefiltration Methods 0.000 description 3
- 239000004113 Sepiolite Substances 0.000 description 2
- IKHGUXGNUITLKF-XPULMUKRSA-N acetaldehyde Chemical compound [14CH]([14CH3])=O IKHGUXGNUITLKF-XPULMUKRSA-N 0.000 description 2
- NIXOWILDQLNWCW-UHFFFAOYSA-N acrylic acid group Chemical group C(C=C)(=O)O NIXOWILDQLNWCW-UHFFFAOYSA-N 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 230000003197 catalytic effect Effects 0.000 description 2
- 239000000919 ceramic Substances 0.000 description 2
- 239000013078 crystal Substances 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 238000004332 deodorization Methods 0.000 description 2
- 239000002657 fibrous material Substances 0.000 description 2
- 230000004927 fusion Effects 0.000 description 2
- 230000001771 impaired effect Effects 0.000 description 2
- 239000011812 mixed powder Substances 0.000 description 2
- 230000007935 neutral effect Effects 0.000 description 2
- 229910052624 sepiolite Inorganic materials 0.000 description 2
- 235000019355 sepiolite Nutrition 0.000 description 2
- 230000035943 smell Effects 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 229920000049 Carbon (fiber) Polymers 0.000 description 1
- JOYRKODLDBILNP-UHFFFAOYSA-N Ethyl urethane Chemical compound CCOC(N)=O JOYRKODLDBILNP-UHFFFAOYSA-N 0.000 description 1
- 239000004698 Polyethylene Substances 0.000 description 1
- 239000004743 Polypropylene Substances 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- 229910010413 TiO 2 Inorganic materials 0.000 description 1
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- 230000004931 aggregating effect Effects 0.000 description 1
- 239000003610 charcoal Substances 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 235000019504 cigarettes Nutrition 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 239000003365 glass fiber Substances 0.000 description 1
- 239000012784 inorganic fiber Substances 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 229910044991 metal oxide Inorganic materials 0.000 description 1
- 150000004706 metal oxides Chemical class 0.000 description 1
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical class C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 230000009965 odorless effect Effects 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 238000011056 performance test Methods 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 229920003023 plastic Polymers 0.000 description 1
- 229920000728 polyester Polymers 0.000 description 1
- 229920000573 polyethylene Polymers 0.000 description 1
- 229920001155 polypropylene Polymers 0.000 description 1
- 238000012805 post-processing Methods 0.000 description 1
- 230000001376 precipitating effect Effects 0.000 description 1
- 230000003014 reinforcing effect Effects 0.000 description 1
- 238000005070 sampling Methods 0.000 description 1
- 239000000741 silica gel Substances 0.000 description 1
- 229910002027 silica gel Inorganic materials 0.000 description 1
- 238000005245 sintering Methods 0.000 description 1
- 239000010936 titanium Substances 0.000 description 1
- 230000002747 voluntary effect Effects 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
Landscapes
- Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
- Treating Waste Gases (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Catalysts (AREA)
- Filtering Materials (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、主にたばこ臭を除
去するための、光触媒を用いた脱臭装置または空気清浄
機用の脱臭フィルタに関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a deodorizing apparatus using a photocatalyst or a deodorizing filter for an air purifier for mainly removing tobacco odor.
【0002】[0002]
【従来の技術】従来から、部屋の中、あるいは或いは車
室内の空気を清浄化するための空気清浄機が種々提案さ
れており、例えばコロナ放電により塵や埃などを集塵す
るための電気集塵式の空気清浄機があるが、これは塵や
埃などは集塵できるものの、悪臭を除去することができ
ないことから、例えば活性炭などの吸着剤をもって悪臭
成分を吸着する脱臭装置をもって脱臭を行っていた。2. Description of the Related Art Conventionally, various air purifiers for purifying air in a room or in a passenger compartment have been proposed. For example, an electric collector for collecting dust and dirt by corona discharge has been proposed. There is a dust-type air purifier, which can collect dust and dirt, but cannot remove odors.For example, deodorization is performed using a deodorizer that adsorbs odorous components using an adsorbent such as activated carbon. I was
【0003】[0003]
【発明が解決しようとする課題】活性炭等に悪臭成分を
吸着させる方式では悪臭成分を物理吸着または化学吸着
により保持しているのみであり、その保持できる場所が
なくなれば吸着能力が飽和してそれ以上脱臭できなくな
る。良好な脱臭効果を得るためには、比較的短いサイク
ル(例えば3ヶ月程度)で交換しなければならず、その
メンテナンスが厄介であると云う問題があった。これは
極性物質に対して吸着能力の高い添着炭と呼ばれるもの
を用いても交換周期がやや長くなるのみで同様である。In the system in which the malodorous component is adsorbed on activated carbon or the like, the malodorous component is only held by physical adsorption or chemical adsorption. It becomes impossible to deodorize. In order to obtain a good deodorizing effect, replacement must be performed in a relatively short cycle (for example, about three months), and there is a problem that maintenance is troublesome. This is the same even when using what is called impregnated carbon having a high adsorption capacity for polar substances, except that the exchange cycle becomes slightly longer.
【0004】また、オゾンの酸化分解力によって、悪臭
成分を酸化・分解するオゾン脱臭装置を用いることも考
えられるが、オゾンを用いた場合、吸着方式のような飽
和現象は起こらないものの、例えば0.1ppm以上の
オゾン濃度はその有害性から好ましくなく、空気清浄方
法としてあまり有効であるとはいえない。It is also conceivable to use an ozone deodorizer for oxidizing and decomposing malodorous components by the oxidative decomposition power of ozone. However, when ozone is used, a saturation phenomenon unlike the adsorption method does not occur. An ozone concentration of 0.1 ppm or more is not preferable because of its harmfulness, and is not very effective as an air cleaning method.
【0005】一方、脱臭装置として光触媒を用いたもの
がある。この脱臭装置は触媒作用を利用して脱臭するこ
とから脱臭に限れば殆どメンテナンスフリーである。但
し、脱臭能力に優れた光触媒は通常粉状となっている。
粒子径は1μm以下で、比表面積が300g/m2と大
きい。光触媒粉の表面に於て酸化分解反応による脱臭が
行われるので、できるだけその表面活性が失われないよ
うに使われるのことが望ましい。ところが、粉状のまま
で空気清浄機に用いることは困難であることから、例え
ばプレート等の担持体にバインダにより固定すると、光
触媒粉の表面をバインダが覆ってしまい光触媒性が失わ
れ、特開平3−157125号公報に開示されているよ
うに、セラミック等へ焼結させて製造しても、比表面積
が低下し、光触媒性が低下する。On the other hand, there is a device using a photocatalyst as a deodorizing device. Since this deodorizing apparatus deodorizes using a catalytic action, it is almost maintenance-free if deodorizing is limited. However, the photocatalyst excellent in deodorizing ability is usually in a powder form.
The particle diameter is 1 μm or less, and the specific surface area is as large as 300 g / m 2 . Since the surface of the photocatalyst powder is deodorized by an oxidative decomposition reaction, it is desirable that the powder be used so as not to lose its surface activity as much as possible. However, since it is difficult to use the powder as it is in an air purifier, if the powder is fixed to a carrier such as a plate with a binder, the surface of the photocatalyst powder is covered with the binder, and the photocatalytic property is lost. As disclosed in Japanese Unexamined Patent Publication No. 3-157125, even when sintering to ceramic or the like, the specific surface area is reduced and the photocatalytic property is reduced.
【0006】そこで、紙状材に上記光触媒粉を抄き込め
ば、光触媒粉の表面積を確保したまま固定でき、光触媒
性を損なうことがないが、例えば現在の空気清浄機に於
いて一般的に用いられる電気集塵方式のものでは、塵・
埃を電気的に引き寄せるために、高圧を印可したコロナ
放電を利用していることから若干の火花が発生すること
もあることから、特に電気集塵部に隣接するように脱臭
フィルタが配置される場合には難燃性が要求される。従
って、パルプやプラスチック繊維などに光触媒を単に抄
き込んだものは燃え易く、そのままでは使用できない。Therefore, if the photocatalyst powder is formed into a paper-like material, the photocatalyst powder can be fixed while securing the surface area of the photocatalyst powder, without impairing the photocatalytic property. The electric dust collection method used
Since a small spark may be generated due to the use of corona discharge applied with a high voltage to electrically attract dust, the deodorizing filter is particularly arranged adjacent to the electric dust collecting portion. In such cases, flame retardancy is required. Therefore, pulp, plastic fiber, or the like obtained by simply incorporating a photocatalyst is easily burnt and cannot be used as it is.
【0007】一方、除去すべき悪臭成分としてたばこ臭
がある。たばこ臭の成分としては、アンモニア、アセト
アルデヒド、酢酸等が代表的なものとしてあげられる
が、アセトアルデヒドをよく吸着し脱臭除去するものが
総合的に効果が高い。ところが、光触媒ではアンモニ
ア、酢酸については吸着及び脱臭効果に優れているもの
のアセトアルデヒドに関しては速効性は顕著に期待でき
ない。本発明は上記したような従来技術の問題点に鑑み
なされたものであり、その主な目的は、悪臭を含む空気
を、容易に、かつ効率良く清浄化可能であると共に寿命
が長く、メンテナンスも簡便であり、しかもその配置も
容易な脱臭装置または空気清浄機用の脱臭フィルタを提
供することにある。On the other hand, there is a tobacco odor as a malodorous component to be removed. Typical examples of tobacco odor components include ammonia, acetaldehyde, acetic acid and the like, but those which adsorb acetaldehyde well and deodorize and remove it are generally highly effective. However, although the photocatalyst is excellent in the adsorption and deodorization effects of ammonia and acetic acid, the rapid effect of acetaldehyde cannot be remarkably expected. SUMMARY OF THE INVENTION The present invention has been made in view of the above-described problems of the related art, and its main purpose is to easily and efficiently purify air containing a bad smell, to have a long life and to maintain the air. An object of the present invention is to provide a deodorizing device or a deodorizing filter for an air purifier that is simple and easy to arrange.
【0008】[0008]
【課題を解決するための手段】上記した目的は本発明に
よれば、光触媒を励起する光源を有する脱臭装置または
空気清浄機に用いられる脱臭フィルタであって、活性炭
を含む悪臭成分の吸着剤と、前記光源に励起されて悪臭
成分を光触媒反応により分解するための光触媒と、難燃
剤とを混合したものを抄き込んだ紙状材からなる脱臭装
置または空気清浄機用脱臭フィルタを提供することによ
り達成される。According to the present invention, there is provided a deodorizing filter for use in a deodorizing apparatus or an air purifier having a light source for exciting a photocatalyst, comprising an adsorbent for a malodorous component containing activated carbon. A deodorizing device or a deodorizing filter for an air purifier comprising a paper-like material into which a mixture of a photocatalyst excited by the light source to decompose malodorous components by a photocatalytic reaction and a flame retardant is provided. Is achieved by
【0009】フィルタに安価で難燃効果が高い、例えば
水酸化アルミニウムなどの難燃剤をも光触媒及び吸着剤
と共に紙状材に抄き込むことにより、燃え難くなり、例
えば火花の発生する電気集塵機の近傍にも配置でき、そ
の配置自由度が向上すると共にアセトアルデヒドに有効
な活性炭を含む吸着剤と高い活性を維持した光触媒とに
より、例えばたばこ臭に対しても有効な寿命の長い脱臭
フィルタを得ることができる。[0009] By incorporating a flame retardant, such as aluminum hydroxide, into a paper material together with a photocatalyst and an adsorbent into a paper-like material, the filter becomes inflammable. Adsorbent containing activated carbon effective for acetaldehyde and photocatalyst that maintains high activity can be placed near, improve the degree of freedom of placement, and obtain a long-life deodorizing filter effective for tobacco odor, for example Can be.
【0010】[0010]
【発明の実施の形態】以下に、本発明の好適な実施形態
について添付の図面を参照して詳しく説明する。Preferred embodiments of the present invention will be described below in detail with reference to the accompanying drawings.
【0011】図1は、本発明が適用された空気清浄機に
於ける脱臭装置部の構成を示す断面図である。ケーシン
グ1には空気を浄化すべき室内などから悪臭成分を含む
空気を吸入するための吸気口2が設けられ、該吸気口2
は、ケーシング1の内部に画定された通風路3を介して
排気口4と連通している。吸気口2には、塵などが内部
に入り込むことを防止するためのプレフィルタ5が設け
られている。また、通風路3に於けるプレフィルタ5の
後段には、脱臭部7と、送風ファン8とがこの順番に設
けられている。尚、吸気口2の前段には公知の電気集塵
部が設けられることとなる(図示せず)。FIG. 1 is a sectional view showing the configuration of a deodorizing device in an air purifier to which the present invention is applied. The casing 1 is provided with an intake port 2 for inhaling air containing a malodorous component from a room or the like where air is to be purified.
Communicates with an exhaust port 4 through a ventilation passage 3 defined inside the casing 1. The intake port 2 is provided with a pre-filter 5 for preventing dust and the like from entering the inside. A deodorizing section 7 and a blower fan 8 are provided in this order at a stage subsequent to the pre-filter 5 in the ventilation path 3. It should be noted that a known electric precipitator is provided in front of the intake port 2 (not shown).
【0012】脱臭部7は、中央に左右方向、即ち図の紙
面に対して前後方向に延在する一対の円柱状をなす紫外
線ランプからなる励起光源10と、その前後に設けら
れ、光触媒粉、吸着剤粉及び難燃剤粉の混合粉を抄き込
んでなる後記する一対の脱臭フィルタ11と、各フィル
タ11間の上面、下面及び両側面を覆う紫外光の反射板
12とから構成されている。The deodorizing section 7 is provided at the center with a pair of cylindrical ultraviolet lamps extending in the left-right direction, that is, in the front-rear direction with respect to the plane of the drawing. It is composed of a pair of deodorizing filters 11 described below, which are formed by mixing a mixed powder of an adsorbent powder and a flame retardant powder, and an ultraviolet light reflecting plate 12 covering the upper surface, the lower surface, and both side surfaces between the filters 11. .
【0013】励起光源10の紫外線ランプの波長は20
0nm〜400nmで、光触媒を励起させる能力を有す
るものであり、オゾンの発生等、人体への影響を考慮す
るとブラックライトまたはケミカルライトを用いること
が好ましい。The wavelength of the ultraviolet lamp of the excitation light source 10 is 20
It has the ability to excite the photocatalyst at 0 nm to 400 nm, and it is preferable to use black light or chemical light in consideration of the influence on the human body such as generation of ozone.
【0014】脱臭フィルタ11の光触媒としては、Ti
O2等の金属酸化物を用いると良い(例えば、アモルフ
ァスと結晶とを混在させたTiO2)。この光触媒を粉
状にしたもの、後記する吸着剤粉及び水酸化アルミニウ
ムなどの難燃剤粉を、繊維に抄き込み、プレス、乾燥し
て形成した紙状体を更にコルゲーション成形してフィル
タ状にして脱臭フィルタ11をなしている。各粉を抄き
込んだ繊維の状態を図2に拡大して示す。The photocatalyst of the deodorizing filter 11 is Ti
It is preferable to use a metal oxide such as O 2 (for example, TiO 2 in which amorphous and crystal are mixed). This photocatalyst is powdered, adsorbent powder to be described later, and a flame retardant powder such as aluminum hydroxide are applied to the fiber, pressed and dried, and the formed paper is further corrugated to form a filter. To form a deodorizing filter 11. FIG. 2 is an enlarged view of the state of the fiber into which each powder is formed.
【0015】ここで、上記光触媒粉はエネルギーを与え
ると、電子が励起され、正孔が生じる。この正孔が光触
媒粉表面で悪臭成分分子と接触して酸化分解反応を起こ
す。例えば上記酸化チタンは、紫外線で有効かつ簡便に
エネルギーを与えて酸化分解反応を起こさせることがで
きる。そして、この酸化チタンの結晶構造はアナタース
型のものを用い、できるだけ比表面積の大きなものを使
うと良い。Here, when the photocatalyst powder gives energy, electrons are excited and holes are generated. These holes come into contact with malodorous component molecules on the surface of the photocatalyst powder to cause an oxidative decomposition reaction. For example, the above-mentioned titanium oxide can cause an oxidative decomposition reaction by applying energy effectively and easily with ultraviolet rays. The titanium oxide has a crystal structure of an anatase type and preferably has a specific surface area as large as possible.
【0016】一方、効率的に上記光触媒による反応を行
わせるためには、できるだけ悪臭成分分子を光触媒に接
触させることが重要である。そのために、本構成ではま
ず悪臭成分分子を吸着剤により吸着しておき、この吸着
剤に捕らえられた悪臭成分分子を酸化チタンにより酸化
・分解するようにした。この吸着剤としては、脱臭対象
となる悪臭の種類と濃度とにもよるが、一般に発生して
いる悪臭は数種類の複合成分が含まれているので、悪臭
を酸性、中性、塩基性に分類したとき、そのすべてに有
効であることが望まれる。このような吸着剤には複合臭
を脱臭するため、添着炭や例えば特開平8−12113
6号公報に記載されているようなシリカゲル、ゼオライ
ト、セピオライト、ミズカナイト及び活性炭等を用いる
と良い。特に、たばこ臭は添着処理のされていない活性
炭を用いると良い。活性炭は粉状のもの以外にも、活性
炭繊維として混合としても良い。この場合、繊維質であ
るので紙強度(フィルタ強度)の向上にも寄与すること
ができる。On the other hand, in order to carry out the reaction by the photocatalyst efficiently, it is important to bring malodorous component molecules into contact with the photocatalyst as much as possible. Therefore, in this configuration, first, the malodor component molecules are adsorbed by the adsorbent, and the malodor component molecules captured by the adsorbent are oxidized and decomposed by titanium oxide. This adsorbent depends on the type and concentration of the odor to be deodorized, but since the odor that is generally generated contains several types of complex components, the odor is classified as acidic, neutral, or basic. When it does, it is desired to be effective for all of them. Such adsorbents may be impregnated with charcoal or, for example, Japanese Patent Application Laid-Open No.
It is preferable to use silica gel, zeolite, sepiolite, mizcanite, activated carbon, and the like as described in JP-A No. 6-No. In particular, for the tobacco odor, it is preferable to use activated carbon that has not been subjected to an impregnation treatment. The activated carbon may be mixed as an activated carbon fiber other than the powdered one. In this case, since it is a fibrous material, it can also contribute to improvement in paper strength (filter strength).
【0017】他方、脱臭フィルタを燃え難くして、即ち
難燃性として前段の電気集塵部に対する配置自由度を高
くするために、水酸化アルミニウムなどの難燃剤をも抄
き込んでいる。ここで、例えば有機系の難燃性処理剤を
使用すると、光触媒の分解性で効果を発揮できないが、
水酸化アルミニウムは粉状無機物なので、上記光触媒や
吸着剤と共に容易に紙のなかに混ぜ込むことができる。On the other hand, a flame retardant such as aluminum hydroxide is also incorporated in order to make the deodorizing filter less flammable, that is, as a flame retardant, so that the degree of freedom in arrangement with respect to the preceding electric precipitating part is increased. Here, for example, when an organic flame retardant is used, the effect cannot be exhibited due to the decomposability of the photocatalyst,
Since aluminum hydroxide is a powdery inorganic substance, it can be easily mixed into paper together with the photocatalyst and the adsorbent.
【0018】紙状体のベースとなる繊維としては、光触
媒の酸化分解力によって紙状体自身が分解、崩壊しない
ように、一般に使われているパルプではなく、無機系の
繊維、例えばガラス繊維、セラミック繊維、金属繊維、
吸着機能を有する活性炭繊維、セピオライト繊維などが
好適である。但し、一般にパルプ繊維以外の繊維を用い
た場合、紙の強度が弱くなるので、後加工される際の必
要最低限の強度が得られない場合には、バルブを使って
も良い。これらの繊維を用いて紙を形成したとき、その
強度が十分に得られないことが考えられるが、5%〜2
0%の熱融着繊維(例えばポリエチレン、ポリプロピレ
ン、ポリエステル等)と液状のエマルジョンバインダ
(例えばアクリル系、ウレタン系等)を5%〜10%添
加することにより、強度が向上し、そのような問題がな
くなる。The fiber serving as the base of the paper is not a commonly used pulp but inorganic fibers, such as glass fiber, so that the paper itself does not decompose or collapse due to the oxidative decomposition power of the photocatalyst. Ceramic fiber, metal fiber,
Activated carbon fibers and sepiolite fibers having an adsorption function are suitable. However, in general, when fibers other than pulp fibers are used, the strength of the paper becomes weak. Therefore, if the minimum strength required for post-processing cannot be obtained, a valve may be used. When paper is formed using these fibers, it is considered that the strength is not sufficiently obtained.
By adding 5% to 10% of 0% heat-fused fiber (for example, polyethylene, polypropylene, polyester, etc.) and a liquid emulsion binder (for example, acrylic, urethane, etc.), the strength is improved, and such a problem is caused. Disappears.
【0019】紙状体の繊維同士の間、または交絡点に光
触媒粉を抄き込み、担持させる方法としては、一般の紙
を作る場合と同様に湿式抄紙法を用いると良い。実際に
は抄紙機にて、紙のベースとなる繊維と光触媒粉、吸着
剤粉及び難燃剤粉の混合粉とを混合し、更に紙の強度の
向上のための熱融着繊維及びエマルジョンバインダを投
入したものを抄く。ここで、液状のエマルジョンバイン
ダは、光触媒及び吸着剤の表面を覆い、触媒性や吸着性
を損なうので、極力その使用量は少なくした方が良い。
また、光触媒粉、吸着剤粉及びエマルジョンバインダは
そのままでは抄紙時に網の目から大部分が抜け落ち、十
分に担持できず歩留まりが悪くなることから、粉と繊維
とを結合させて抜け落ちを防ぐための定着剤を用いると
良い。この定着剤によって粉同士が凝集し網の目から抜
け落ちなくなる。その後、プレスし、熱融着繊維の融着
温度以上の温度で乾燥させて紙状体を得る。この紙状体
を脱臭装置に組み込んで使う場合、コルゲーション成形
してフィルタ状にすることで圧損が低くなり利用し易く
なる。As a method for introducing and supporting the photocatalyst powder between the fibers of the paper-like body or at the point of entanglement, it is preferable to use a wet papermaking method as in the case of making ordinary paper. Actually, the fiber as the base of the paper and the mixed powder of the photocatalyst powder, the adsorbent powder and the flame retardant powder are mixed in a paper machine, and the heat-bonded fibers and the emulsion binder for improving the strength of the paper are further mixed. Grab the input. Here, the liquid emulsion binder covers the surfaces of the photocatalyst and the adsorbent, and impairs the catalytic property and the adsorptivity. Therefore, it is better to reduce the amount of use as much as possible.
In addition, most of the photocatalyst powder, adsorbent powder and emulsion binder fall off from the mesh during papermaking as they are, and cannot be sufficiently supported, resulting in poor yield. A fixing agent is preferably used. This fixing agent prevents the powders from aggregating and falling off the mesh. Then, it presses and is dried at the temperature more than the fusion temperature of a heat fusion fiber, and a paper-like object is obtained. When this paper is used by incorporating it into a deodorizing device, by forming it into a filter by corrugation molding, the pressure loss is reduced and it is easy to use.
【0020】[0020]
【実施例】上記光触媒粉として酸化チタン(ST−0
1:石原産業社製)、吸着剤粉として酸化チタン系吸着
剤(ST−01:石原産業社製)及び添着処理していな
い活性炭、難燃剤として水酸化アルミニウムを抄き込ん
だ紙状体からなる脱臭フィルタの脱臭性能及び比較例と
してとして酸化チタン(ST−01:石原産業社製)、
吸着剤粉として酸化チタン系吸着剤(ST−01:石原
産業社製)を抄き込み、かつ難燃剤を抄き込んでいない
紙状体からなる脱臭フィルタの脱臭性能の測定を図3に
示す装置を用いて行った。これら紙状体に含まれる成分
の重量部を表1に示す。EXAMPLES Titanium oxide (ST-0) was used as the photocatalyst powder.
1: Ishihara Sangyo Co., Ltd.), a titanium oxide-based adsorbent (ST-01: Ishihara Sangyo Co., Ltd.) as adsorbent powder, activated carbon not subjected to impregnation treatment, and a paper-like material into which aluminum hydroxide was added as a flame retardant. Performance of the deodorizing filter and titanium oxide (ST-01: manufactured by Ishihara Sangyo Co., Ltd.) as a comparative example,
FIG. 3 shows the measurement of the deodorizing performance of a deodorizing filter made of a paper-like body into which a titanium oxide-based adsorbent (ST-01: manufactured by Ishihara Sangyo Co., Ltd.) is incorporated as the adsorbent powder and the flame retardant is not incorporated. This was performed using an apparatus. Table 1 shows parts by weight of the components contained in these paper-like bodies.
【0021】[0021]
【表1】 [Table 1]
【0022】測定装置は、1m3のアクリル製ボックス
に、図1の構成の空気清浄機(電気集塵部のないもの)
と、たばこ吸煙機と、内部攪拌用のファンを配置したも
のである。脱臭性能の測定は、上記脱臭フィルタを空気
清浄機に配置し、日本電機工業会の「空気清浄機脱臭性
能試験に関する自主基準」に準拠して以下のような操作
で行った。 (1)たばこをたばこ吸煙機で燃やしている間は、空気
清浄機の運転を停止させておく。 (2)たばこは吸煙機でマイルドセブン5本を燃焼さ
せ、最も燃焼の速いたばこがフィルタに達したところで
吸煙機の運転を止め、残りを自然燃焼させる。 (3)最後まで燃焼していたたばこが燃焼し終わってか
ら3分後に、検知管でアンモニア濃度とアセトアルデヒ
ド濃度とを同時に測定し、次いで酢酸濃度を測定する。 (4)攪拌用ファンを止め、空気清浄機を運転させる。 (5)所定時間後、(3)と同様にして、各濃度の測定
をする。 (6)所定時間に官能値も測定する。この際、ボックス
の開閉をせず、内部の空気を採取できるようにあらかじ
め採取口を設け、ここからポンプで内部の空気を採取
し、6段階評価による臭気強度、及び9段階評価による
快・不快度を評価する。The measuring device is an air purifier having the configuration shown in FIG. 1 (without an electric dust collecting unit) in an acrylic box of 1 m 3 .
, A cigarette smoke evacuator and a fan for internal stirring. The deodorizing performance was measured by placing the above deodorizing filter in an air purifier and performing the following operation in accordance with the Japan Electrical Manufacturers'Association's"Voluntary Standard for Air Purifier Deodorizing Performance Test". (1) While the tobacco is being burned by the tobacco smoke absorber, the operation of the air purifier is stopped. (2) The smoker burns five mild sevens with a smoke absorber, and when the fastest burning tobacco reaches the filter, stops operation of the smoke absorber and burns the rest naturally. (3) Three minutes after the burning of the tobacco that has been burned to the end, the ammonia concentration and the acetaldehyde concentration are simultaneously measured with a detector tube, and then the acetic acid concentration is measured. (4) Stop the stirring fan and operate the air purifier. (5) After a predetermined time, each concentration is measured in the same manner as in (3). (6) The sensory value is also measured at a predetermined time. At this time, a sampling port is provided in advance so that the inside air can be sampled without opening and closing the box, and the inside air is sampled from this through a pump. Evaluate the degree.
【0023】実施例及び比較例のたばこ臭の除去の様子
(濃度変化、官能値)を図4(a)、図4(b)、図4
(c)及び図5に示す。FIGS. 4 (a), 4 (b), 4 (a), 4 (b), and 4 (b) show how tobacco odor is removed (concentration change, sensory value) in Examples and Comparative Examples.
This is shown in (c) and FIG.
【0024】図4(a)、図4(c)に示されるよう
に、本実施例の脱臭フィルタにあってはアンモニア、酢
酸ともに1時間以内に50%除去していることがわか
る。また、アセトアルデヒドはアンモニアや酢酸ほど吸
着性がないため、急激に減少しないが、24時間後には
明らかに減少していることがわかる。As shown in FIGS. 4 (a) and 4 (c), in the deodorizing filter of this embodiment, both ammonia and acetic acid are removed by 50% within one hour. Further, it can be seen that acetaldehyde does not rapidly decrease because it has less adsorptivity than ammonia and acetic acid, but clearly decreases after 24 hours.
【0025】一方、比較例のものはアンモニア、酢酸に
ついては初期に除去されているもののアセトアルデヒド
は24時間後でもほとんど減少していないことがわか
る。これにより、たばこ臭に脱臭効果の高い添着処理の
されていない活性炭を混ぜると、混ぜていなかったもの
が速効性を期待できないのに比べて、より素早くたばこ
臭を除去できることがわかる。On the other hand, in the comparative example, ammonia and acetic acid were removed at the initial stage, but acetaldehyde hardly decreased even after 24 hours. This shows that when activated carbon not impregnated with a high deodorizing effect is mixed with tobacco odor, tobacco odor can be removed more quickly than non-impregnated carbon that cannot be expected to have immediate effect.
【0026】また、官能値では濃度変化以上の違いがみ
られ、比較例ではかろうじて臭気強度が3になる程度で
あるが、本実施例では1〜4時間後に臭気強度3、更に
24時間後では臭気強度2以下にまで下げることができ
た。In addition, the sensory value shows a difference larger than the change in concentration, and the odor intensity is barely 3 in the comparative example. However, in this example, the odor intensity is 3 after 1 to 4 hours, and the odor intensity is 3 after 24 hours. The odor intensity could be reduced to 2 or less.
【0027】尚、たばこ臭以外の悪臭については、例え
ば本願出願人による特願平8−303636号明細書の
記載により明らかなように、本実施例、比較例とも酸
性、中性、塩基性の悪臭について効率的に脱臭すること
が可能である。As to the malodor other than the tobacco odor, as is clear from the description of Japanese Patent Application No. 8-303636 by the applicant of the present invention, both of the Examples and Comparative Examples are acidic, neutral and basic. It is possible to deodorize odors efficiently.
【0028】ここで、光触媒と吸着剤との合計部は多い
ほど脱臭能力に優れるが、紙に抄き込んだときに合計部
が50を越えると、粉を保持し難くなり、また光触媒と
吸着剤との合計部が多くなる程紙の強度が弱くなり、コ
ルゲーション成形してフィルタ状にすることが困難にな
ると云う問題が生じる。逆に光触媒と吸着剤との合計部
が少ないと十分な脱臭能力が得られない。例えば光触媒
と吸着剤との合計部が10程度であれば紙強度的にはフ
ィルタ成形に耐えられる強度を確保することができる
が、脱臭能力は十分ではない。Here, the larger the total part of the photocatalyst and the adsorbent, the better the deodorizing ability. However, if the total part exceeds 50 when it is incorporated into paper, it becomes difficult to hold the powder, As the total amount of the agent and the agent increases, the strength of the paper becomes weaker, which causes a problem that it becomes difficult to form a filter by corrugation molding. Conversely, if the total amount of the photocatalyst and the adsorbent is small, sufficient deodorizing ability cannot be obtained. For example, if the total amount of the photocatalyst and the adsorbent is about 10, paper strength can be secured enough to withstand filter molding, but the deodorizing ability is not sufficient.
【0029】そこで、脱臭能力を最大限に生かすように
光触媒と吸着剤との合計部は多くし、バインダ等で補強
して紙強度を得るようにすると良い。但し、バインダが
多すぎると光触媒性及び吸着性を損ねるので、5重量%
〜10重量%程度とするのが良い。上記光触媒と吸着剤
との合計部45はこれらの点から決定した。また、合計
部45のうち、活性炭量は多くなれば、アセトアルデヒ
ドの吸着性も向上するが、20部以上では顕著な効果が
認められない。更に、活性炭の部数が22.5、即ち光
触媒量との比が1:1を越えると、光触媒粉に励起光の
紫外線が届き難くなり、光触媒性が損なわれる。Therefore, it is preferable to increase the total amount of the photocatalyst and the adsorbent so as to maximize the deodorizing ability, and to obtain paper strength by reinforcing with a binder or the like. However, if the amount of the binder is too large, the photocatalytic property and the adsorptivity are impaired.
The content is preferably about 10 to 10% by weight. The total part 45 of the photocatalyst and the adsorbent was determined from these points. In addition, when the amount of activated carbon in the total part 45 is large, the acetaldehyde adsorptivity is also improved. However, a remarkable effect is not recognized in 20 parts or more. Further, if the number of activated carbons is 22.5, that is, the ratio to the amount of the photocatalyst exceeds 1: 1, it becomes difficult for the ultraviolet light of the excitation light to reach the photocatalyst powder, and the photocatalytic property is impaired.
【0030】本実施形態の主たる除去対象のたばこ臭の
除去過程としては、まずアセトアルデヒドを活性炭が効
率良く吸着し、吸着したアセトアルデヒドをこれに近接
する光触媒によって効率的に分解することとなる。ま
た、その他の悪臭に対しても、例えば塩基性物質はST
−01及び繊維質に速やかに吸着される。ST−01に
吸着されたにおい分子はST−01自身の光触媒性によ
って酸化分解され、におわない分子となって放出され
る。繊維質に吸着したにおい分子は、ST−01に吸着
したにおい分子が分解されるに従い、ST−01に拡散
していき、酸化分解される。In the process of removing the tobacco odor to be mainly removed according to this embodiment, first, activated carbon is efficiently adsorbed by acetaldehyde, and the adsorbed acetaldehyde is efficiently decomposed by a photocatalyst adjacent thereto. Also, for other bad smells, for example, the basic substance is ST
-01 and quickly adsorbed on fiber. The odor molecules adsorbed on ST-01 are oxidatively decomposed by the photocatalytic property of ST-01 itself, and are released as odorless molecules. The odor molecules adsorbed on the fibrous material are diffused into ST-01 and oxidatively decomposed as the odor molecules adsorbed on ST-01 are decomposed.
【0031】酸性物質も同様に、吸着作用によってST
−31に速やかに吸着された後、ST−01で酸化分解
される。ここでST−31は光触媒性も有しているの
で、或程度吸着剤自身に吸着されたまま酸化分解するこ
ともある。Similarly, the acidic substance is caused by the adsorption action to cause ST.
After being quickly adsorbed on -31, it is oxidatively decomposed in ST-01. Since ST-31 also has photocatalytic properties, it may be oxidatively decomposed while being adsorbed to some extent by the adsorbent itself.
【0032】一方、難燃性についてUL−94Vに従っ
て測定した。実際には燃焼させる試験片を幅12.5m
m、長さ130mmに裁断し、ブンゼンバーナにより炎
を近づけ、燃焼状態を観察した。その結果を表2に示
す。On the other hand, the flame retardancy was measured according to UL-94V. Actually, the specimen to be burned is 12.5m wide.
m, the length was cut to 130 mm, the flame was brought close by a Bunsen burner, and the combustion state was observed. Table 2 shows the results.
【0033】[0033]
【表2】 [Table 2]
【0034】水酸化アルミニウムを難燃剤として混合す
ると、表2のようにその配合比率に応じて難燃性が向上
する。このうちNo.5は、難燃比が小さくなって燃え
易くなるはずだが、活性炭を混合しているためにNo.
1〜No.4と傾向が異なっており、この難燃比でもU
L規格94V−0に適合している。When aluminum hydroxide is mixed as a flame retardant, the flame retardancy is improved according to the mixing ratio as shown in Table 2. No. In No. 5, the flame retardancy ratio should be small and it should be easy to burn. However, No. 5 was mixed with activated carbon.
1 to No. 4 and the tendency is different.
It conforms to L standard 94V-0.
【0035】尚、水酸化アルミニウムは紙の抄紙工程に
問題なく導入することができ、更に有機系の難燃剤のよ
うに光触媒性によって分解されない。It should be noted that aluminum hydroxide can be introduced into a papermaking process without any problem, and is not decomposed due to photocatalytic properties unlike organic flame retardants.
【0036】[0036]
【発明の効果】上記した説明により明らかなように、本
発明によれば、光触媒反応を利用する脱臭装置または空
気清浄機に於いて、活性炭を含む悪臭成分の吸着剤と、
悪臭成分を光触媒反応により分解するための光触媒と、
難燃剤とを混合したものを抄き込んだ紙状材を脱臭フィ
ルタとして用いることにより、まず悪臭成分を活性炭を
含む吸着剤が吸着することにより悪臭成分の光触媒への
接触効率が向上し、また吸着した悪臭成分が効率的に順
次分解・除去されることから、悪臭を含む空気を、容易
に、かつ効率良く清浄化可能となる。また、単に吸着剤
を用いる場合のように飽和しないことから、寿命が長く
なり、そのメンテナンスも容易になる。しかも水酸化ア
ルミニウムなどの難燃剤を抄き込んで難燃性を向上する
ことにより、火花が発生するような電気集塵機の近傍に
も配置でき、その配置自由度が向上する。As is apparent from the above description, according to the present invention, in a deodorizer or an air purifier utilizing a photocatalytic reaction, an adsorbent for a malodorous component containing activated carbon,
A photocatalyst for decomposing malodorous components by a photocatalytic reaction,
By using a paper-like material made by mixing a flame retardant and a paper material as a deodorizing filter, the adsorbent containing activated carbon first adsorbs the malodorous component, thereby improving the contact efficiency of the malodorous component with the photocatalyst, and Since the adsorbed malodor components are sequentially decomposed and removed efficiently, the air containing the malodor can be easily and efficiently cleaned. In addition, since it does not saturate as in the case of simply using an adsorbent, its life is extended and its maintenance is facilitated. In addition, by incorporating a flame retardant such as aluminum hydroxide to improve the flame retardancy, it can be disposed near an electric dust collector where sparks are generated, and the degree of freedom of the arrangement is improved.
【図1】本発明が適用された第1の実施形態に於ける脱
臭装置の構成を示す断面図。FIG. 1 is a cross-sectional view showing a configuration of a deodorizing device according to a first embodiment to which the present invention is applied.
【図2】光触媒粉及び吸着剤粉を繊維に抄き込んだ紙状
材の繊維の状態を拡大して示す図。FIG. 2 is an enlarged view showing a state of fibers of a paper-like material in which a photocatalyst powder and an adsorbent powder are formed into fibers.
【図3】光触媒粉及び吸着剤粉を抄き込んだ紙状体の脱
臭性能の測定装置の構成を示す図。FIG. 3 is a diagram showing a configuration of a measuring apparatus for measuring the deodorizing performance of a paper-like body into which a photocatalyst powder and an adsorbent powder have been incorporated.
【図4】吸着剤として活性炭を含む本発明の脱臭フィル
タと活性炭を含まない脱臭フィルタとによるアンモニア
の除去率(a)、アセトアルデヒドの除去率(b)、酢
酸の除去率(c)を示すグラフ。FIG. 4 is a graph showing the removal rate of ammonia (a), the removal rate of acetaldehyde (b), and the removal rate of acetic acid (c) by the deodorizing filter of the present invention containing activated carbon as an adsorbent and the deodorizing filter containing no activated carbon. .
【図5】(a)、(b)は、吸着剤として活性炭を含む
本発明の脱臭フィルタと活性炭を含まない脱臭フィルタ
とによる官能値の変化を示すグラフ。FIGS. 5 (a) and (b) are graphs showing changes in sensory values between the deodorizing filter of the present invention containing activated carbon as an adsorbent and the deodorizing filter not containing activated carbon.
1 ケーシング 2 吸気口 3 通風路 4 排気口 5 プレフィルタ 7 脱臭部 8 送風ファン 10 励起光源 11 脱臭フィルタ 12 反射板 DESCRIPTION OF SYMBOLS 1 Casing 2 Intake port 3 Ventilation path 4 Exhaust port 5 Pre-filter 7 Deodorizing part 8 Ventilation fan 10 Excitation light source 11 Deodorizing filter 12 Reflector
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI B01D 39/14 B01D 39/14 B M 53/38 B01J 20/20 B 53/81 21/06 A B01J 20/20 35/02 J 21/06 B01D 53/34 116B 35/02 116Z 53/36 J ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 6 Identification code FI B01D 39/14 B01D 39/14 BM 53/38 B01J 20/20 B 53/81 21/06 A B01J 20/20 35/02 J 21/06 B01D 53/34 116B 35/02 116Z 53/36 J
Claims (7)
置または空気清浄機に用いられる脱臭フィルタであっ
て、 粉状または繊維状の活性炭を含む1種または2種以上の
悪臭成分の吸着剤と、前記光源に励起されて悪臭成分を
光触媒反応により分解するための粉状光触媒と、粉状難
燃剤とを混合して抄き込んだ紙状材からなることを特徴
とする脱臭フィルタ。1. A deodorizing filter used in a deodorizing device or an air purifier having a light source for exciting a photocatalyst, comprising: an adsorbent for one or more types of malodorous components containing powdered or fibrous activated carbon; A deodorizing filter comprising a paper-like material obtained by mixing and mixing a powdery photocatalyst, which is excited by the light source to decompose malodorous components by a photocatalytic reaction, and a powdery flame retardant.
する前記吸着剤に含まれる活性炭の重量の比が、1:1
以下となっていることを特徴とする請求項1に記載の脱
臭フィルタ。2. The ratio of the weight of activated carbon contained in the adsorbent to the total weight of the adsorbent and the photocatalyst is 1: 1.
The deodorizing filter according to claim 1, wherein:
性炭からなることを特徴とする請求項1または請求項2
に記載の脱臭フィルタ。3. The activated carbon according to claim 1, wherein the activated carbon is an activated carbon that has not been subjected to an impregnation treatment.
The deodorizing filter according to 1.
ダ及び/または繊維状バインダを用いて前記脱臭用粉を
前記紙状材に抄き込んだことを特徴とする請求項1乃至
請求項3のいずれかに記載の脱臭フィルタ。4. The paper-like material according to claim 1, wherein said deodorizing powder is formed into said paper-like material by using a liquid binder and / or a fibrous binder so as to secure a required strength. The deodorizing filter according to any one of the above.
重量%の範囲で含むことを特徴とする請求項4に記載の
脱臭フィルタ。5. The method according to claim 1, wherein the liquid binder is 5% by weight to 10% by weight.
The deodorizing filter according to claim 4, which is contained in a range of weight%.
の範囲で含むことを特徴とする請求項4または請求項5
に記載の脱臭フィルタ。6. The method according to claim 4, wherein the fibrous binder is contained in a range of 10% by weight or less.
The deodorizing filter according to 1.
なり、 該水酸化アルミニウムを難燃比で1以上含むことを特徴
とする請求項1乃至請求項6のいずれかに記載の脱臭フ
ィルタ。7. The deodorizing filter according to claim 1, wherein the flame retardant comprises aluminum hydroxide, and the aluminum hydroxide has a flame retardant ratio of 1 or more.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9045615A JPH10235154A (en) | 1997-02-28 | 1997-02-28 | Deodorizing filter for deodorizing apparatus or air cleaner |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9045615A JPH10235154A (en) | 1997-02-28 | 1997-02-28 | Deodorizing filter for deodorizing apparatus or air cleaner |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH10235154A true JPH10235154A (en) | 1998-09-08 |
Family
ID=12724294
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP9045615A Pending JPH10235154A (en) | 1997-02-28 | 1997-02-28 | Deodorizing filter for deodorizing apparatus or air cleaner |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH10235154A (en) |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2002085536A (en) * | 2000-09-20 | 2002-03-26 | Fujitsu General Ltd | Deodorization filter |
WO2002051454A1 (en) * | 2000-12-26 | 2002-07-04 | Iwasaki Environmental Facilities Co., Ltd. | Device and method for treatment of polluted air |
JP2008036589A (en) * | 2006-08-09 | 2008-02-21 | Nippon Soda Co Ltd | Photocatalyst liquid composition |
JP2012125717A (en) * | 2010-12-16 | 2012-07-05 | Toyobo Co Ltd | Sheet for gas adsorption, and air cleaning filter |
CN109012619A (en) * | 2018-09-19 | 2018-12-18 | 南京林业大学 | A kind of active carbon-modified montmorillonoid composite adsorbing material and its preparation method and application |
JPWO2017221998A1 (en) * | 2016-06-23 | 2019-06-13 | 株式会社Nano Wave | Air purification device |
-
1997
- 1997-02-28 JP JP9045615A patent/JPH10235154A/en active Pending
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2002085536A (en) * | 2000-09-20 | 2002-03-26 | Fujitsu General Ltd | Deodorization filter |
WO2002051454A1 (en) * | 2000-12-26 | 2002-07-04 | Iwasaki Environmental Facilities Co., Ltd. | Device and method for treatment of polluted air |
JP2008036589A (en) * | 2006-08-09 | 2008-02-21 | Nippon Soda Co Ltd | Photocatalyst liquid composition |
JP2012125717A (en) * | 2010-12-16 | 2012-07-05 | Toyobo Co Ltd | Sheet for gas adsorption, and air cleaning filter |
JPWO2017221998A1 (en) * | 2016-06-23 | 2019-06-13 | 株式会社Nano Wave | Air purification device |
CN109012619A (en) * | 2018-09-19 | 2018-12-18 | 南京林业大学 | A kind of active carbon-modified montmorillonoid composite adsorbing material and its preparation method and application |
CN109012619B (en) * | 2018-09-19 | 2021-07-09 | 南京林业大学 | A kind of activated carbon-modified montmorillonite composite adsorption material and its preparation method and application |
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