JP2001303494A - Adsorbing photocatalytic inorganic sheet - Google Patents

Adsorbing photocatalytic inorganic sheet

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Publication number
JP2001303494A
JP2001303494A JP2000157389A JP2000157389A JP2001303494A JP 2001303494 A JP2001303494 A JP 2001303494A JP 2000157389 A JP2000157389 A JP 2000157389A JP 2000157389 A JP2000157389 A JP 2000157389A JP 2001303494 A JP2001303494 A JP 2001303494A
Authority
JP
Japan
Prior art keywords
sheet
inorganic
photocatalytic
photocatalyst
adsorbent
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
Application number
JP2000157389A
Other languages
Japanese (ja)
Inventor
Hiroo Tanaka
浩雄 田中
Takuya Kitaoka
卓也 北岡
Hideaki Ichiura
英明 市浦
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Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP2000157389A priority Critical patent/JP2001303494A/en
Publication of JP2001303494A publication Critical patent/JP2001303494A/en
Pending legal-status Critical Current

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  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)
  • Paper (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a noncombustible adsorbing photocatalytic inorganic sheet effective for efficiently decomposing a harmful substance to cause the air pollution and odor generation and making the substance harmless. SOLUTION: The objective adsorbing photocatalytic inorganic sheet effective for efficiently decomposing a harmful substance to cause the air pollution and odor generation and making the substance harmless is produced by preparing a composite sheet using all components comprising an organic pulp, an adsorbent, a photocatalyst, an inorganic fiber, an inorganic substrate forming component and a polymer flocculant or using a material group composed of the above components excluding the organic pulp and the polymer flocculent by a semi-dry method or a wet method in a manner to obtain the sheet containing a larger amount of the adsorbent than the photocatalyst and baking the obtained sheet at >=500 deg.C to make the sheet noncombustible and increase the strength of the sheet.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、吸着と光触媒反応
を利用し、大気汚染物質や臭気物質などの有害物質を分
解し得る吸着性光触媒無機シートに関し、更に詳しくは
無機繊維および無機支持体形成成分を用いて、吸着剤お
よび光触媒が効率良くシート中に保持され、また良好な
強度を有する環境汚染修復効果に優れた吸着性光触媒無
機シートに関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an adsorptive photocatalytic inorganic sheet which can decompose harmful substances such as air pollutants and odorous substances by utilizing adsorption and photocatalytic reaction, and more particularly to formation of inorganic fibers and inorganic support. The present invention relates to an adsorptive photocatalytic inorganic sheet having a component, in which an adsorbent and a photocatalyst are efficiently held in a sheet, and having excellent strength and an excellent effect of remediating environmental pollution.

【0002】[0002]

【従来の技術および発明が解決しようとする課題】最
近、環境問題は日常生活に深刻な影響を与えており、そ
の改善が切望されている。改善策の一つとして有害物質
除去剤が活用されており、これには活性炭、シリカ、ア
ルミナおよび金属酸化物などの吸着剤が使用されている
が、吸着剤に有害物質が吸着されるに従い、次第に吸着
能力が低下するなど、使用上多くの問題があった。これ
を解決するために、近年光触媒を活用した有害物の除去
法が開発された。酸化チタンや酸化亜鉛等の光触媒によ
る有害物質の分解は、これらの光励起による有害物質の
光触媒的酸化作用であるため、長期に持続する。これは
吸着剤に比べ光触媒の大きな利点であるが、一方光触媒
は吸着性が低いため反応効率の劣る欠点を有している。
これらの欠点を改良するためにすでに吸着剤と光触媒の
複合化が行われている。これは低濃度の有害物質を吸着
剤で濃縮し、近傍に存在する光触媒で効率的に分解でき
るので極めて合理的な方法である。吸着剤としてしばし
ば活性炭が用いられているが、これは光触媒と複合化す
ると次第に酸化反応を受け劣化する欠点を有している。
また、有効な吸着剤や光触媒は粉体であるため、これら
をシート状に保持するのが困難なため、樹脂エマルジョ
ンなどの有機バインダーが用いられているが、バインダ
ーの光触媒による酸化反応・劣化を防止することは出来
ない。大気汚染物質除去材として屋外で使用する場合や
臭気物質除去材として屋内で使用する場合など、耐久性
に特に優れ、また不燃性の吸着性光触媒シートが要求さ
れている。
2. Description of the Related Art Recently, environmental problems have seriously affected daily life, and there is an urgent need for improvements. As one of the improvement measures, a harmful substance remover is used, and an adsorbent such as activated carbon, silica, alumina and metal oxide is used for this.As the harmful substance is adsorbed by the adsorbent, There have been many problems in use, such as the adsorption capacity gradually decreasing. In order to solve this problem, a method for removing harmful substances using a photocatalyst has recently been developed. Decomposition of harmful substances by a photocatalyst such as titanium oxide or zinc oxide is a photocatalytic oxidation action of harmful substances by these photoexcitations, and thus lasts for a long time. This is a great advantage of the photocatalyst as compared with the adsorbent, but the photocatalyst has a drawback that the reaction efficiency is inferior due to low adsorbability.
In order to remedy these drawbacks, adsorbents and photocatalysts have already been combined. This is a very rational method, since low-concentration harmful substances can be concentrated with an adsorbent and efficiently decomposed by a photocatalyst present in the vicinity. Activated carbon is often used as an adsorbent, but has the disadvantage that when it is combined with a photocatalyst, it is gradually degraded by an oxidation reaction.
In addition, since effective adsorbents and photocatalysts are powders, it is difficult to hold them in a sheet shape, and organic binders such as resin emulsions are used. It cannot be prevented. For use outdoors as an air pollutant remover or indoors as an odor remover, a nonflammable adsorptive photocatalyst sheet that is particularly excellent in durability is required.

【0003】[0003]

【課題を解決するための手段】本発明者らは、上記の課
題を解決すべく鋭意研究を重ねた結果、半乾式法で成型
したシートを500℃以上で焼成、または湿式抄造した
シートに無機バインダー処理を施し、500℃以上で焼
成して有機物を完全に焼却除去して、耐久性に優れた不
燃性の吸着性光触媒シートを完成するに至った。すなわ
ち本発明は、1.木材パルプやリンターパルプなどの有
機繊維の有無、ゼオライトやシリカなどの無機吸着剤、
酸化チタンや酸化亜鉛などの光触媒、セラミック繊維や
ガラス繊維などの無機繊維およびシリカゾルやアルミナ
ゾルなどの無機支持体形成成分よりなる混合物に少量の
水を加えてよく混練し、これを孔を有する金属板上に出
来るだけ均一に広げ、圧搾した後500℃以上に加熱し
て有機物を除去した吸着性光触媒無機シートを製造する
方法、2.木材パルプやリンターパルプなどの有機繊維
にポリジアリルジメチルアンモニウムクロリド、カチオ
ン性ポリアクリルアミドあるいはポリビニルアミンなど
の陽性凝集剤を加え、次いで無機吸着剤、光触媒および
無機繊維あるいはこれらの三者からなる水懸濁液を加
え、さらにアニオン性ポリアクリルアミドやポリアクリ
ル酸などの陰性凝集剤を加え、湿式により抄造したシー
トに、またはこれを乾燥したシートにアルミナゾルやシ
リカゾルなどの無機支持体形成成分を含浸法又は噴霧法
で加えて圧搾した後500℃以上に加熱して有機物を除
去した吸着性光触媒無機シートを製造する方法に関す
る。
Means for Solving the Problems The inventors of the present invention have conducted intensive studies to solve the above-mentioned problems, and as a result, a sheet molded by a semi-dry method has been calcined at 500 ° C. or higher, or an inorganic sheet has been formed on a wet-formed sheet. A binder treatment was performed, and the mixture was fired at 500 ° C. or higher to completely incinerate and remove organic substances, thereby completing a non-combustible adsorptive photocatalyst sheet having excellent durability. That is, the present invention provides: Presence of organic fibers such as wood pulp and linter pulp, inorganic adsorbents such as zeolite and silica,
A small amount of water is added to a mixture of a photocatalyst such as titanium oxide or zinc oxide, an inorganic fiber such as ceramic fiber or glass fiber, and an inorganic support-forming component such as silica sol or alumina sol, and the mixture is kneaded well. 1. A method for producing an adsorptive photocatalytic inorganic sheet from which organic matter has been removed by spreading the sheet as uniformly as possible, pressing it, and then heating it to 500 ° C. or higher; Add a positive coagulant such as polydiallyldimethylammonium chloride, cationic polyacrylamide or polyvinylamine to organic fibers such as wood pulp or linter pulp, and then add an inorganic adsorbent, photocatalyst and inorganic fibers or a water suspension composed of these three. Add a liquid, further add a negative coagulant such as anionic polyacrylamide or polyacrylic acid, and impregnate or spray an inorganic support-forming component such as alumina sol or silica sol on a wet-sheeted sheet or on a dried sheet. The present invention relates to a method for producing an adsorptive photocatalytic inorganic sheet from which organic matter has been removed by heating at 500 ° C. or higher after squeezing by adding a method.

【0004】[0004]

【発明の実施の形態】以下に本発明の吸着性光触媒無機
シートに係わる構成要素、次いでその製造方法について
詳細に説明する。
BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, components relating to the adsorptive photocatalytic inorganic sheet of the present invention, and a method for producing the same will be described in detail.

【0005】本発明に係わる無機吸着剤としてゼオライ
ト、活性白土、酸化亜鉛、アルミナ、セピオライト、ハ
ロイサイト、およびこれらの複合物等が挙げられるが、
殊にゼオライトは種々の有害物質に合わせて吸着効率を
最高にするようにその細孔の大きさを調節できるので、
無機吸着剤として有利に用いられる。
The inorganic adsorbents according to the present invention include zeolite, activated clay, zinc oxide, alumina, sepiolite, halloysite, and composites thereof.
In particular, zeolite can adjust its pore size to maximize the adsorption efficiency for various harmful substances,
It is advantageously used as an inorganic adsorbent.

【0006】本発明の光触媒として酸化チタン、酸化亜
鉛および酸化セリウム等の金属酸化物が挙げられるが、
殊に酸化チタンはその安定性、安全性および光触媒性高
分解能等に優れ、家屋や道路周辺において使用するには
最適であり、本発明に係わる光触媒として有利に用いら
れる。
The photocatalyst of the present invention includes metal oxides such as titanium oxide, zinc oxide and cerium oxide.
In particular, titanium oxide is excellent in stability, safety, photocatalytic high resolution, etc., is most suitable for use around houses and roads, and is advantageously used as a photocatalyst according to the present invention.

【0007】本発明に用いる無機繊維としてセラミック
繊維、ガラス繊維、鉱滓繊維、石綿等が挙げられるが、
安定性、安全性、強度等に優れたセラミック繊維が有利
に用いられる。
The inorganic fibers used in the present invention include ceramic fibers, glass fibers, slag fibers, and asbestos.
Ceramic fibers excellent in stability, safety, strength and the like are advantageously used.

【0008】本発明に係わる無機支持体形成成分として
アルミナゾル、シリカゾル、リン酸ナトリウム等が挙げ
られるが、粒子径や他の材料との親和性等が最も適した
アルミナゾルが有利に用いられる。
As the inorganic support-forming component according to the present invention, alumina sol, silica sol, sodium phosphate and the like can be mentioned, and the alumina sol having the most suitable particle diameter and affinity with other materials is advantageously used.

【0009】本発明の有機パルプとは、木材パルプ、リ
ンターパルプ、合成パルプ等の繊維状物質であるが、無
機粉体の高歩留まりに寄与することのできるフィブリル
化の容易な天然パルプが有利に用いられる。
The organic pulp of the present invention is a fibrous substance such as wood pulp, linter pulp, and synthetic pulp. Natural pulp which can contribute to a high yield of inorganic powder and is easily fibrillated is advantageous. Used.

【0010】半乾式成型には、繊維板やセメントボード
のシート成型機等を用いることができる。また多数の孔
を有する金属板に網を乗せ、この上に混練した原材料混
合物を出来るだけ均一に広げ試験用のプレスで圧締して
シートをつくることもできる。調製したシートを500
℃以上の一定温度に調節した電気炉で焼成し、吸着性光
触媒無機シートを得た。
For semi-dry molding, a sheet molding machine for a fiberboard or cement board can be used. Alternatively, a net can be placed on a metal plate having a large number of holes, and the kneaded raw material mixture can be spread as evenly as possible on the metal plate, and pressed with a test press to form a sheet. 500 sheets prepared
Calcination was performed in an electric furnace controlled at a constant temperature of not less than ° C. to obtain an adsorptive photocatalytic inorganic sheet.

【0011】湿式抄造には、円網抄紙機、長網抄紙機、
ツインワイヤー抄紙機を用いることができる。調製した
シートを無機支持体形成成分の分散液で含浸処理あるい
は噴霧処理をした後、500℃以上の一定温度に調節し
た電気炉で焼成し、吸着性光触媒シートを得た。
[0011] Wet papermaking includes a round paper machine, a fourdrinier paper machine,
A twin wire paper machine can be used. The prepared sheet was impregnated or sprayed with a dispersion of the inorganic support-forming component, and then fired in an electric furnace adjusted to a constant temperature of 500 ° C. or higher to obtain an adsorptive photocatalyst sheet.

【0012】[0012]

【実施例】次に、実施例をもって本発明を具体的に説明
する。当該分野の研究常識に照らし、本発明が以下に示
す実施例で用いる実験条件の末節に限定されないのは明
らかである。
Next, the present invention will be described specifically with reference to examples. In light of the common general knowledge in the art, it is clear that the present invention is not limited to the last part of the experimental conditions used in the examples described below.

【0013】[実施例1]CSF約350mlに叩解し
たリンターパルプ1.0部、ゼオライト(東ソー社製、
HSZ−320NAA)4.0部、酸化チタン(石原産
業社製、ST−31)2.0部、セラミック繊維(イソ
ライト工業製、カオウールバルクLS)3.0部および
アルミナゾル(日産化学工業社製、アルミナゾル−52
0)4.0部および水7.0部を加え、ニーダで湿練し
た。約10mm間隔で孔を有するステンレス板に80メ
ッシュの金網を乗せ、この上に混練した原料をできるだ
け均一に広げ、手すき紙用プレスを用いて3.5kP
a、5分間圧締した。出来たシートを700℃、20分
間焼成して坪量約250g/mの、実施例1の吸着性
光触媒無機シートを得た。
Example 1 1.0 part of linter pulp beaten to about 350 ml of CSF, zeolite (manufactured by Tosoh Corporation,
HSZ-320NAA) 4.0 parts, titanium oxide (manufactured by Ishihara Sangyo Co., ST-31) 2.0 parts, ceramic fiber (manufactured by Isolite Industries, Kao Wool Bulk LS) 3.0 parts and alumina sol (manufactured by Nissan Chemical Industries, Ltd.) Alumina sol-52
0) 4.0 parts and 7.0 parts of water were added and kneaded with a kneader. An 80-mesh wire mesh is placed on a stainless steel plate having holes at intervals of about 10 mm, and the kneaded raw material is spread as evenly as possible on this, and the kneaded material is 3.5 kP using a handsheet press.
a Pressed for 5 minutes. The resulting sheet was calcined at 700 ° C. for 20 minutes to obtain the adsorptive photocatalytic inorganic sheet of Example 1 having a basis weight of about 250 g / m 2 .

【0014】[実施例2]実施例1においてリンターパ
ルプを0部にする以外は、すべて実施例1と同一の方法
で、実施例2の吸着性光触媒無機シートを調製した。
Example 2 An adsorptive photocatalytic inorganic sheet of Example 2 was prepared in the same manner as in Example 1 except that the amount of linter pulp was changed to 0 parts.

【0015】[実施例3]実施例1においてゼオライト
を3.0部、酸化チタンを3.0部にする以外は、すべ
て実施例1と同一の方法で実施例3の吸着性光触媒無機
シートを調製した。
Example 3 The adsorbent photocatalytic inorganic sheet of Example 3 was prepared in the same manner as in Example 1 except that zeolite was changed to 3.0 parts and titanium oxide was changed to 3.0 parts. Prepared.

【0016】[実施例4]CSF約350mlに叩解し
たリンターパルプの4%水懸濁液10gを撹拌しなが
ら、0.1%ポリジアリルジメチルアンモニウムクロリ
ド水溶液25gを加え、3分後にゼオライト2.4g、
酸化チタン1.2g、セラミック繊維1.5gを含む水
懸濁液65gを追加し、さらに0.1%陰性凝集剤(栗
田工業社製、HI−351)25gを加え、5分後にJ
IS P 8209に準拠してシートを調製し、これを
無機支持体形成成分の分散液であるアルミナゾルに含浸
処理を施した。これを実施例1と同一の方法で圧締と焼
成を行い、実施例4の吸着性光触媒無機シートを得た。
Example 4 25 g of a 0.1% aqueous solution of polydiallyldimethylammonium chloride was added to 10 g of a 4% aqueous suspension of linter pulp beaten to about 350 ml of CSF, and 2.4 g of zeolite 3 minutes later. ,
65 g of an aqueous suspension containing 1.2 g of titanium oxide and 1.5 g of ceramic fibers were added, and 25 g of a 0.1% negative flocculant (HI-351 manufactured by Kurita Water Industries Ltd.) was added.
A sheet was prepared in accordance with ISP 8209, and the sheet was impregnated with alumina sol as a dispersion of the inorganic support-forming component. This was pressed and fired in the same manner as in Example 1 to obtain the adsorptive photocatalytic inorganic sheet of Example 4.

【0017】[実施例5]実施例4において、ゼオライ
ト1.8gおよび酸化チタン1.8gにする以外は、す
べて実施例4と同一の方法で実施例5の吸着性光触媒シ
ートを得た。
Example 5 The adsorptive photocatalyst sheet of Example 5 was obtained in the same manner as in Example 4 except that 1.8 g of zeolite and 1.8 g of titanium oxide were used.

【0018】[実施例6]実施例4においてCSF約3
50mlに叩解したリンターパルプのかわりにCSF約
270mlに叩解したLBKPを用いる以外は、すべて
実施例4と同一の方法で実施例6の吸着性光触媒無機シ
ートを得た。
[Embodiment 6] In Embodiment 4, the CSF is about 3
An adsorbent photocatalytic inorganic sheet of Example 6 was obtained in the same manner as in Example 4 except that LBKP beaten to about 270 ml of CSF was used instead of linter pulp beaten to 50 ml.

【0019】[実施例7]実施例5において、CSF約
350mlに叩解したリンターパルプのかわりにCSF
約270mlに叩解したLBKPを用いる以外は、すべ
て実施例5と同一の方法で実施例7の吸着性光触媒無機
シートを得た。
[Example 7] In Example 5, CSF was used instead of linter pulp beaten to about 350 ml of CSF.
An adsorbent photocatalytic inorganic sheet of Example 7 was obtained in the same manner as in Example 5 except that LBKP beaten to about 270 ml was used.

【0020】[比較例1]実施例1において、ゼオライ
トを2.2部、酸化チタンを4.4部にする以外は、す
べて実施例1と同一の方法で比較例1の吸着性光触媒無
機シートを調製した。この試料を比較例1の吸着性光触
媒無機シートとした。
Comparative Example 1 The adsorptive photocatalytic inorganic sheet of Comparative Example 1 was prepared in the same manner as in Example 1, except that 2.2 parts of zeolite and 4.4 parts of titanium oxide were used. Was prepared. This sample was used as the adsorptive photocatalytic inorganic sheet of Comparative Example 1.

【0021】[比較例2]実施例1において、ゼオライ
トを0部、酸化チタンを6.6部にする以外は、すべて
実施例1と同一の方法で比較例2の吸着性光触媒無機シ
ートを調製した。この試料を比較例2の吸着性光触媒無
機シートとした。
Comparative Example 2 An adsorbent photocatalytic inorganic sheet of Comparative Example 2 was prepared in the same manner as in Example 1 except that zeolite was changed to 0 parts and titanium oxide was changed to 6.6 parts. did. This sample was used as the adsorptive photocatalytic inorganic sheet of Comparative Example 2.

【0022】[比較例3]実施例4において、0.1%
ポリジアリルジメチルアンモニウムクロリド25gを5
0gに、また0.1%陰性凝集剤25gを0gにする以
外は、すべて実施例4と同一の方法で比較例3の吸着性
光触媒無機シートを調製した。この試料を比較例3の吸
着性光触媒無機シートとした。
Comparative Example 3 In Example 4, 0.1%
25 g of polydiallyldimethylammonium chloride in 5
An adsorbent photocatalytic inorganic sheet of Comparative Example 3 was prepared in the same manner as in Example 4 except that 0 g and 25 g of 0.1% negative flocculant were changed to 0 g. This sample was used as the adsorptive photocatalytic inorganic sheet of Comparative Example 3.

【0023】[比較例4]実施例4において0.1%ポ
リジアリルジメチルアンモニウムクロリド25gを0g
に、また0.1%陰性凝集剤25gを50gにする以外
は、すべて実施例4と同一の方法で比較例4の吸着性光
触媒無機シートを調製した。この試料を比較例4の吸着
性光触媒無機シートとした。
Comparative Example 4 In Example 4, 25 g of 0.1% polydiallyldimethylammonium chloride was added in an amount of 0 g.
The adsorptive photocatalytic inorganic sheet of Comparative Example 4 was prepared in the same manner as in Example 4, except that the amount of the 25% 0.1% negative coagulant was changed to 50 g. This sample was used as the adsorptive photocatalytic inorganic sheet of Comparative Example 4.

【0024】[比較例5]実施例4において、ゼオライ
トを1.2g、酸化チタン2.4gにする以外は、すべ
て実施例4と同一の方法で比較例5の吸着性光触媒無機
シートを調製した。この試料を比較例5の吸着性光触媒
無機シートとした。
Comparative Example 5 The adsorptive photocatalytic inorganic sheet of Comparative Example 5 was prepared in the same manner as in Example 4 except that zeolite was changed to 1.2 g and titanium oxide to 2.4 g. . This sample was used as the adsorptive photocatalytic inorganic sheet of Comparative Example 5.

【0025】[比較例6]実施例4において、ゼオライ
トを0g、酸化チタンを3.6gにする以外は、すべて
実施例4と同一の方法で比較例6の吸着性光触媒無機シ
ートを調製した。この試料を比較例6の吸着性光触媒無
機シートとした。
Comparative Example 6 An adsorptive photocatalytic inorganic sheet of Comparative Example 6 was prepared in the same manner as in Example 4 except that zeolite was changed to 0 g and titanium oxide to 3.6 g. This sample was used as the adsorptive photocatalytic inorganic sheet of Comparative Example 6.

【0026】[比較例7]実施例4において、ゼオライ
トを3.6g、酸化チタンを0gにする以外は、すべて
実施例4と同一に方法で比較例7の吸着性光触媒無機シ
ートを調製した。この試料を比較例7の吸着性光触媒無
機シートとした。
Comparative Example 7 The adsorptive photocatalytic inorganic sheet of Comparative Example 7 was prepared in the same manner as in Example 4 except that zeolite was changed to 3.6 g and titanium oxide was changed to 0 g. This sample was used as the adsorptive photocatalytic inorganic sheet of Comparative Example 7.

【0027】以上、実施例および比較例で得られた吸着
性光触媒無機シートは、以下の方法で試験を行い、紫外
線を照射していない場合の結果を表1に、紫外線を照射
した場合の結果を表2に示した。
The adsorptive photocatalytic inorganic sheets obtained in Examples and Comparative Examples were tested by the following method. Table 1 shows the results when no ultraviolet rays were irradiated, and Table 1 shows the results when ultraviolet rays were irradiated. Are shown in Table 2.

【0028】[無機物の歩留まり]調製したシートを7
00℃の電気炉中で20分間焼成し、残存灰分より求め
た。
[Yield of inorganic substance]
It was baked for 20 minutes in an electric furnace at 00 ° C. and determined from the residual ash content.

【0029】[無機シートの強度]圧縮強さ試験(リン
グクラッシュ法)Tappi T 818−87に準拠
して測定した。
[Strength of Inorganic Sheet] A compressive strength test (ring crush method) was measured in accordance with Tappi T 818-87.

【0030】[吸着性・光触媒分解性]石英製のカバー
を有する体積200ccのステンレス反応容器に2.5
cm×2.5cmの大きさの実施例および比較例の吸着
性光触媒無機シートを設置した後、反応容器に125p
pmになるように、一酸化窒素またはホルムアルデヒド
をマイクロシリンジで注入した。所定時間ごとに反応容
器内の一酸化窒素またはホルムアルデヒド濃度を測定し
た。一酸化窒素の分析には、化学発光方式のNOx分析
計を、ホルムアルデヒドの分析にはガスクロマトグラフ
ィーを用いて測定した。また、同一の実験を、試料に波
長365nm、4ワットの紫外線ランプを10cmの高
さから照射して行った。一酸化窒素またはホルムアルデ
ヒドの初期減少速度から吸着性を、1時間後の濃度から
光触媒分解性を評価した。
[Adsorption / Photocatalytic Decomposition] 2.5 cc stainless steel reaction vessel having a quartz cover
After installing the adsorptive photocatalytic inorganic sheets of Examples and Comparative Examples having a size of cm × 2.5 cm, 125 p
Nitric oxide or formaldehyde was injected with a microsyringe to pm. At predetermined time intervals, the concentration of nitric oxide or formaldehyde in the reaction vessel was measured. Nitrogen monoxide was analyzed using a chemiluminescent NOx analyzer, and formaldehyde was analyzed using gas chromatography. In addition, the same experiment was performed by irradiating a sample with an ultraviolet lamp having a wavelength of 365 nm and 4 watts from a height of 10 cm. The adsorptivity was evaluated from the initial reduction rate of nitric oxide or formaldehyde, and the photocatalytic degradation was evaluated from the concentration after 1 hour.

【0031】[0031]

【表1】 [Table 1]

【0032】[0032]

【表2】 [Table 2]

【0033】[0033]

【発明の効果】上に記した説明により明らかなように、
本発明による吸着性光触媒無機シートは吸着剤、光触
媒、無機繊維および支持体形成成分よりなる不燃性の吸
着性光触媒無機シート、または、デュアルポリマーシス
テムにより有機繊維、吸着剤、光触媒および無機繊維か
らなる水性懸濁液を適度に凝集させた後、湿式抄造した
シートあるいはこれを乾燥したシートに支持体形成成分
を含浸処理または噴霧処理後、500℃以上に加熱し
て、焼成した吸着性光触媒無機シートであって、大気汚
染物質や揮発性有機化合物などの有害物質の分解性に優
れ、且つハニカム構造体成型あるいは金属板や各種建材
への貼付などシートの後加工性に優れることから、近年
社会問題化している高速道路や都市部の交通渋滞箇所の
側壁への付設によるNOx、SOx、炭化水素などの高
効率吸着光分解による大気浄化、家屋の内装材によるホ
ルムアルデヒド、トルエンなどの揮発性有機化合物、腐
敗臭、加齢臭などの生活不快性物質の高効率吸着光分解
による室内空気浄化、また近年において小型化や薄型化
の要求のある家庭用、および車載用等の空気清浄器の濾
過部材等に有用性の高いものである。多くの場合、上記
の汚染物質は低濃度で存在するので、まずこれらを吸着
剤で効率的に補集・濃縮することが重要であり、一旦、
濃縮されると汚染物質は吸着剤の近傍に存在する光触媒
により高効率で分解される。よって、シート中の吸着剤
の重量が光触媒の重量より大きい場合に、特に性能の優
れた吸着性光触媒無機シートを提供するものである。更
に、不燃性であることを特徴とする本発明の吸着性光触
媒無機シートは、衝突による車火災の危険のある道路に
近接して、また発熱を伴う光触媒励起光源、及び放電発
火の恐れがある光源や空調材など電気機器の接点と近傍
して使用し得るものであり、さらに家屋の内装に使用す
ればその難燃化が達成される等の利点があり、非情に有
用性の高いものである。
As is clear from the above description,
The adsorptive photocatalytic inorganic sheet according to the present invention comprises a noncombustible adsorptive photocatalytic inorganic sheet comprising an adsorbent, a photocatalyst, inorganic fibers and a support-forming component, or an organic fiber, an adsorbent, a photocatalyst and inorganic fibers by a dual polymer system. After the aqueous suspension is appropriately agglomerated, a wet-formed sheet or a dried sheet is impregnated or sprayed with a support-forming component, heated to 500 ° C. or higher, and calcined, and the adsorbent photocatalytic inorganic sheet is fired. In recent years, since it has excellent decomposability of harmful substances such as air pollutants and volatile organic compounds, and has excellent post-processability of sheets such as honeycomb structure molding or sticking to metal plates and various building materials, it has become a social problem in recent years. High-efficiency adsorption photolysis of NOx, SOx, hydrocarbons, etc. by attaching to the side wall of traffic congestion points in urban expressways and urban areas Air purification, indoor air purification by highly efficient adsorption photolysis of volatile organic compounds such as formaldehyde and toluene, decay odor, aging odor and other living unpleasant substances from interior materials of houses, and miniaturization and thinning in recent years It is highly useful as a filter member for air purifiers for home use and on-vehicle use where there is a demand. In many cases, the above contaminants are present at low concentrations, so it is important to first efficiently collect and concentrate them with an adsorbent.
When concentrated, the contaminants are decomposed with high efficiency by the photocatalyst present near the adsorbent. Therefore, when the weight of the adsorbent in the sheet is larger than the weight of the photocatalyst, an adsorptive photocatalytic inorganic sheet having particularly excellent performance is provided. Furthermore, the adsorptive photocatalytic inorganic sheet of the present invention, which is characterized by being nonflammable, is close to a road where there is a risk of a car fire due to a collision, a photocatalytic excitation light source with heat generation, and a risk of discharge ignition. It can be used in the vicinity of electrical equipment such as light sources and air conditioners, and has the advantage of achieving flame retardance if used in the interior of a house. is there.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) B01J 37/02 301 B01J 37/08 37/08 D21H 13/38 D21H 13/38 17/67 17/67 21/14 Z 21/14 27/00 C 27/00 B01D 53/36 J Fターム(参考) 4C080 AA05 AA07 AA10 BB02 CC01 HH08 JJ06 KK08 MM02 NN02 NN03 NN04 NN06 QQ03 4D048 AA06 AA19 AA22 AB03 BA03X BA07X BA41X BB08 EA01 EA04 4G069 AA03 AA08 AA11 BA01A BA01B BA02A BA04A BA04B BA07A BA07B BA29A BA29B BA48A BB14A BC02A CA10 CA17 EA07 EA12 EA13 FA03 FB06 FB15 FB24 FB30 FC07 4L055 AA08 AF05 AF08 AG17 AG19 AG28 AG71 AG94 BD12 BD13 BE08 BE10 BF01 GA31 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification symbol FI theme coat ゛ (Reference) B01J 37/02 301 B01J 37/08 37/08 D21H 13/38 D21H 13/38 17/67 17/67 21 / 14 Z 21/14 27/00 C 27/00 B01D 53/36 JF term (reference) 4C080 AA05 AA07 AA10 BB02 CC01 HH08 JJ06 KK08 MM02 NN02 NN03 NN04 NN06 QQ03 4D048 AA06 AA19 AA22 AB03 BA03X BA07X BA41XBB04X04 AA03 AA08 AA11 BA01A BA01B BA02A BA04A BA04B BA07A BA07B BA29A BA29B BA48A BB14A BC02A CA10 CA17 EA07 EA12 EA13 FA03 FB06 FB15 FB24 FB30 FC07 4L055 AA08 AF05 AF08 AG17 AG10 AG28 AG71 AG94 BD12

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】無機吸着剤、光触媒、無機繊維および無機
支持体形成成分からなり、無機吸着剤が光触媒の50%
以上を占める吸着性光触媒無機シート。
1. An inorganic adsorbent, a photocatalyst, an inorganic fiber and an inorganic support-forming component, wherein the inorganic adsorbent is 50% of the photocatalyst.
The adsorptive photocatalytic inorganic sheet occupying the above.
【請求項2】水分散有機繊維に陽性凝集剤を加えた後、
無機吸着剤、光触媒および無機繊維またはこれらの三者
からなる水懸濁液を、さらに陰性凝集剤を追加添加して
湿式により抄造したシート、またはこれを乾燥したシー
トに無機支持体形成成分の浸漬処理あるいは噴霧処理を
施し、さらに500℃以上で焼成した吸着性光触媒無機
シート。
2. After adding a positive coagulant to the water-dispersed organic fiber,
Immersion of the inorganic support-forming component in a sheet obtained by adding an inorganic adsorbent, a photocatalyst and an inorganic fiber or an aqueous suspension composed of the three, and further adding a negative coagulant to the sheet, or by drying the sheet, An adsorptive photocatalytic inorganic sheet which has been subjected to a treatment or spraying treatment and further calcined at 500 ° C. or higher.
JP2000157389A 2000-04-19 2000-04-19 Adsorbing photocatalytic inorganic sheet Pending JP2001303494A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006037269A (en) * 2004-07-26 2006-02-09 Nippon Sheet Glass Co Ltd Heat-resistant ceramic sheet
JP2007117926A (en) * 2005-10-28 2007-05-17 Em Research Organization Foamed material containing photocatalyst and manufacturing method of the same
JP2015188847A (en) * 2014-03-28 2015-11-02 宇部興産株式会社 Porous photocatalyzer and production method thereof
CN107469869A (en) * 2017-08-23 2017-12-15 浙江理工大学 A kind of preparation method of photocatalytic fiber net

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006037269A (en) * 2004-07-26 2006-02-09 Nippon Sheet Glass Co Ltd Heat-resistant ceramic sheet
JP2007117926A (en) * 2005-10-28 2007-05-17 Em Research Organization Foamed material containing photocatalyst and manufacturing method of the same
JP4536639B2 (en) * 2005-10-28 2010-09-01 株式会社Em研究機構 Foaming material containing photocatalyst and method for producing the same
JP2015188847A (en) * 2014-03-28 2015-11-02 宇部興産株式会社 Porous photocatalyzer and production method thereof
CN107469869A (en) * 2017-08-23 2017-12-15 浙江理工大学 A kind of preparation method of photocatalytic fiber net
CN107469869B (en) * 2017-08-23 2020-06-23 浙江理工大学 Preparation method of photocatalytic fiber web

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