JP2003220318A - PHOTOCATALYST INORGANIC SHEET FOR EFFECTIVELY DECOMPOSING NOx - Google Patents

PHOTOCATALYST INORGANIC SHEET FOR EFFECTIVELY DECOMPOSING NOx

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Publication number
JP2003220318A
JP2003220318A JP2002059503A JP2002059503A JP2003220318A JP 2003220318 A JP2003220318 A JP 2003220318A JP 2002059503 A JP2002059503 A JP 2002059503A JP 2002059503 A JP2002059503 A JP 2002059503A JP 2003220318 A JP2003220318 A JP 2003220318A
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JP
Japan
Prior art keywords
sheet
inorganic
nox
photocatalyst
photocatalytic
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
JP2002059503A
Other languages
Japanese (ja)
Inventor
Hideaki Ichiura
英明 市浦
Takuya Kitaoka
卓也 北岡
Hiroo Tanaka
浩雄 田中
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Individual
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Individual
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Application filed by Individual filed Critical Individual
Priority to JP2002059503A priority Critical patent/JP2003220318A/en
Publication of JP2003220318A publication Critical patent/JP2003220318A/en
Pending legal-status Critical Current

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Abstract

<P>PROBLEM TO BE SOLVED: To provide a noncombustible/adsorbable/neutralizing photocatalyst inorganic sheet which decomposes/detoxifies NOX effectively. <P>SOLUTION: The photocatalyst inorganic sheet for effectively decomposing NOX is obtained by preparing a composite sheet in a semidrying condition or in a wet condition, calcining the resultant at 500°C or higher to impart the noncombustible property thereto using either one of an adsorbent or a metal oxide which has a NO<SB>2</SB>high retainability and a nitric acid binding ability, or both of them and all of organic pulp, a photocatalyst, an inorganic fiber, an inorganic supporting material forming component and a polymeric coagulant or a material group excluding one of the organic pulp, the polymeric coagulant and the adsorbent or the metal oxide among these materials. The obtained sheet has improved strength and decomposes/detoxifies NOX effectively. <P>COPYRIGHT: (C)2003,JPO

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、酸化チタンの光触
媒反応を活用して、大気汚染有害物質であるNOxを分
解し得る光触媒無機シートに関し、更に詳しくは生成す
る中間体を保持し分解を進めるとともに、生成物である
触媒毒成分の硝酸を吸着および化学反応により酸化チタ
ンから隔離して、触媒能の低下を防いでNOxの分解を
効率的、持続的に行わせる環境汚染修復効果の高い光触
媒担持無機シートに関するものである。
TECHNICAL FIELD The present invention relates to a photocatalytic inorganic sheet capable of decomposing NOx, which is a harmful substance of air pollution, by utilizing a photocatalytic reaction of titanium oxide, and more specifically, it holds an intermediate to be produced and promotes decomposition. At the same time, the photocatalyst with a high effect of remediating environmental pollution by separating nitric acid, which is a product of catalyst poison, from titanium oxide by adsorption and chemical reaction, preventing degradation of catalytic ability and efficiently and continuously decomposing NOx. The present invention relates to a supported inorganic sheet.

【0002】[0002]

【従来の技術および発明が解決しようとする課題】近
年、自動車交通量の増加に伴い、特に大都市交通渋滞地
域において、NOxによる環境汚染がぜんそく、頭痛、
めまいなどを誘発し、日常生活に重大な悪影響を与えて
いる。1日も早い改善が切望されているが、その改善策
としてNOx吸着能の高い樹木の道路側や中央分離帯へ
の植樹や酸化チタンの道路舖装剤への混合、混練による
NOx軽減が試行されている。しかし、樹木によるNO
x吸収は交通渋滞地域などNOx濃度の高い場所では不
十分であり、また酸化チタンを道路舖装剤に直接混ぜる
方法でも酸化チタンのNOx吸収能が低いため十分な効
果は得られず、さらにNOxの分解で生成するNO
よる二次汚染や硝酸による光触媒効率の低下などの問題
があり、実用化に際し、大きな障害となっている。
2. Description of the Related Art In recent years, as vehicle traffic has increased, NOx-induced environmental pollution, asthma, and headache
It induces dizziness and has a serious adverse effect on daily life. It is eagerly desired to improve as early as possible for one day, but as a measure to improve it, we try to reduce NOx by planting trees with high NOx adsorption capacity on the road side or median strip, mixing titanium oxide with roadside additives, and kneading. Has been done. However, NO due to trees
The x absorption is not sufficient in a place with high NOx concentration such as a traffic jam area, and even if the titanium oxide is directly mixed with the roadside material, the NOx absorption capacity of the titanium oxide is low, so that sufficient effect cannot be obtained. There are problems such as secondary pollution due to NO 2 generated by decomposition of OH and reduction of photocatalytic efficiency due to nitric acid, which is a major obstacle to practical use.

【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、酸化チタンとA
型ゼオライトの複合化により、NOxの吸収・濃縮およ
びNOの放散防止、さらにCaO、MgO、ZnO、
Alなどの金属酸化物を酸化チタンの近傍に共存
させて硝酸を除去することにより、酸化チタンの光触媒
能の低下を防止する高いNOx除去能と耐久性に優れた
光触媒無機シートを完成するに至った。すなわち本発明
は、 1.パルプなどの有機繊維の有無、ゼオライトなどの無
機吸着剤、水酸化カルシウムや水酸化マグネシウムなど
の金属水酸化物、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無機繊維およびシリカ
ゲルやアルミナゾルなどの無機質焼結成分からなる混合
物に適量の水を加えてよく混練し、これを孔を多数有す
る金属板上または同金属板に乗せた濾過布上に出来るだ
け均一に広げ、圧搾した後、500℃以上に加熱して有
機物を除去するとともに強度を付与したNOx高分解性
光触媒無機シートを製造する方法、 2.パルプなどの有機繊維にポリジアリルジメチルアン
モニウムクロリドなどのカチオン性凝集剤を加え、次い
で無機吸着剤、水酸化カルシウムなどの金属酸化物、光
触媒および無機繊維あるいはこれら四者からなる水懸濁
液を加え、さらにアニオン性ポリアクリルアミドなどの
アニオン性凝集剤を加え、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などの
無機質焼結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NOx高
分解性光触媒無機シートを製造する方法、 3.上記1および上記2の方法に準して、光触媒を含ま
ないシートを先ず調製し、このシートに酸化チタンゾル
などの光触媒懸濁液を含浸させた後、乾燥させたNOx
高分解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 As a result of intensive studies to solve the above problems, the present inventors have found that titanium oxide and A
By combining type zeolite, NOx absorption / concentration and NO 2 emission prevention, CaO, MgO, ZnO,
Completed a photocatalyst inorganic sheet with high NOx removal ability and excellent durability to prevent reduction of titanium oxide photocatalytic ability by removing nitric acid by making metal oxides such as Al 2 O 3 coexist near titanium oxide. Came to do. That is, the present invention is: Presence of organic fiber such as pulp, inorganic adsorbent such as zeolite, metal hydroxide such as calcium hydroxide and magnesium hydroxide, photocatalyst such as titanium oxide and zinc oxide,
Add a suitable amount of water to a mixture of inorganic fibers such as ceramic fibers and glass fibers and inorganic sintered components such as silica gel and alumina sol, knead them well, and put this on a metal plate with many holes or on a filter cloth placed on the metal plate. 1. A method for producing a NOx highly decomposable photocatalyst inorganic sheet, which is uniformly spread as much as possible, squeezed, and heated to 500 ° C. or higher to remove organic substances and impart strength. A cationic flocculant such as polydiallyldimethylammonium chloride is added to organic fibers such as pulp, and then an inorganic adsorbent, a metal oxide such as calcium hydroxide, a photocatalyst and inorganic fibers, or an aqueous suspension of these four is added. Further, an anionic coagulant such as an anionic polyacrylamide is further added, and a wet sheet-formed sheet or a dried sheet is added with an inorganic sinter component such as alumina sol by an impregnation method or a spraying method and squeezed. 2. A method for producing a NOx highly decomposable photocatalytic inorganic sheet, which is heated to a temperature of ℃ or above to remove organic substances, A sheet containing no photocatalyst is first prepared in accordance with the methods 1 and 2 above, and the sheet is impregnated with a photocatalyst suspension such as titanium oxide sol and then dried.
The present invention relates to a method for producing a high-degradability photocatalytic inorganic sheet.

【0004】[0004]

【発明の実施の形態】以下に本発明のNOx高分解性光
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 The constituent elements relating to the NOx highly decomposable photocatalytic inorganic sheet of the present invention and the method for producing the same are described in detail below.

【0005】本発明に係わる吸着剤として各種ゼオライ
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、
特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、A型ゼ
オライトは窒素酸化物の吸着剤として有利に用いられ
る。
Examples of the adsorbent according to the present invention include various zeolites, activated clay, zinc oxide, alumina, sepiolite, halloysite, and composites thereof.
In particular, zeolite can be adjusted in its pore size so as to maximize the adsorption efficiency according to various harmful substances, and A-type zeolite is advantageously used as a nitrogen oxide adsorbent.

【0006】本発明に用いる硝酸除去剤として、焼成に
より金属酸化物に変成する各種金属水酸化物が挙げられ
るが、変成の容易さ等に優れたCa(OH)、Mg
(OH)、Zn(OH)などの2価金属イオンの水
酸化物および安定で溶解度の低い酸化物を生成するAl
(OH)が有利に用いられる。
Examples of the nitric acid removing agent used in the present invention include various metal hydroxides which are converted into metal oxides by firing. Ca (OH) 2 and Mg are excellent in easiness of conversion.
Al that forms hydroxides of divalent metal ions such as (OH) 2 and Zn (OH) 2 and oxides that are stable and have low solubility
(OH) 3 is advantageously used.

【0007】本発明の光触媒として酸化チタンや酸化セ
リウム等の金属酸化物が挙げられるが、安定性、安全性
および光触媒性高分解能等に優れた酸化チタンが有利に
用いられる。
Examples of the photocatalyst of the present invention include metal oxides such as titanium oxide and cerium oxide. Titanium oxide excellent in stability, safety and photocatalytic high resolution is advantageously used.

【0008】本発明に係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。
Examples of the inorganic fibers according to the present invention include ceramic fibers, glass fibers, slag fibers, asbestos, etc., but ceramic fibers excellent in stability, safety and strength are advantageously used.

【0009】本発明で用い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適なアル
ミナゾルが有利に用いられる。
Examples of the inorganic support-forming component used in the present invention include alumina sol, silica sol, sodium phosphate and the like, and alumina sol having the optimum particle size and affinity with other materials is advantageously used.

【0010】本発明のパルプとは、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 pulp of the present invention is a fibrous substance such as wood pulp, linter pulp, synthetic pulp, etc., and natural pulp which can contribute to a high yield of inorganic powder and is easily fibrillated is advantageously used. To be

【0011】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
を有する金属板に金網や濾布を乗せ、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、
NOx高分解性光触媒無機シートを得た。
For the semi-dry molding, a sheet molding machine for fiber board or cement board can be used. It is also possible to put a wire net or a filter cloth on a metal plate having a large number of holes, spread the kneaded raw material mixture on it as evenly as possible, and press it with a press for a test to make a sheet. The prepared sheet is fired in an electric furnace adjusted to a constant temperature of 500 ° C or higher,
An NOx highly decomposable photocatalytic inorganic sheet was obtained.

【0012】湿式抄造には、和紙などの手抄装置、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、NOx高分解
性光触媒無機シートを得た。
For the wet papermaking, a handmade paper making machine such as Japanese paper, a cylinder paper making machine, a fourdrinier paper making machine or a twin wire paper making machine can be used. The prepared sheet was impregnated or sprayed with a dispersion liquid of components for forming an inorganic support, and then fired in an electric furnace adjusted to a constant temperature of 500 ° C. or higher to obtain a NOx highly decomposable photocatalytic inorganic sheet.

【0013】[0013]

【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。
EXAMPLES Next, the present invention will be specifically described with reference to examples. Obviously, the present invention is not limited to the last section of the experimental conditions used in the examples shown below, in the light of common research knowledge in the field.

【0014】[実施例1]CSF約265mlに叩解し
た木材パルプ1.0部、ゼオライトA型(和光純薬社、
A−4)2.0部、水酸化カルシウム2.0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−520)4.0部および水7.0部を加え、
ニーダで混練した。多数の孔を有するステンレス板に8
0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、試験用プレスを用いて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NOx
高分解性光触媒無機シートを得た。
Example 1 1.0 part of wood pulp beaten to about 265 ml of CSF, zeolite A type (Wako Pure Chemical Industries, Ltd.,
A-4) 2.0 parts, calcium hydroxide 2.0 parts, titanium oxide (Ishihara Sangyo Co., Ltd., ST-31) 2.0 parts, ceramic fiber (Isolite Kogyo, Kaowool Bulk LS)
3.0 parts and 4.0 parts of alumina sol (Alumina sol-520 manufactured by Nissan Chemical Industries, Ltd.) and 7.0 parts of water were added,
Kneaded with a kneader. 8 on stainless plate with many holes
Place a 0 mesh wire mesh, spread the kneaded raw material on this as evenly as possible, and use a test press to remove 3.5 kP
a, it was clamped for 5 minutes. The NOx of Example 1 having a basis weight of about 250 g / m 2 by firing the resulting sheet at 700 ° C. for 20 minutes
A high-degradability photocatalytic inorganic sheet was obtained.

【0015】[実施例2]実施例1において木材パルプ
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NOx高分解性光触媒無機シートを調製し
た。
[Example 2] The same method as in Example 1 was repeated except that the wood pulp in Example 1 was changed to 0 part.
The NOx highly decomposable photocatalytic inorganic sheet of Example 2 was prepared.

【0016】[実施例3]実施例1においてゼオライト
A型を3.0部、水酸化カルシウム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NOx高分解性光触媒無機シートを調製し
た。
[Example 3] Example 3 was carried out in the same manner as in Example 1 except that zeolite A type was 3.0 parts, calcium hydroxide was 0 part, and titanium oxide was 3.0 parts. A NOx high-degradability photocatalytic inorganic sheet of No. 3 was prepared.

【0017】[実施例4]実施例1においてゼオライト
A型を0部、水酸化カルシウム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4のNOx高分解性光触媒無機シートを調製し
た。
[Example 4] Example 4 was carried out in the same manner as in Example 1 except that zeolite A type was 0 part, calcium hydroxide was 3.0 parts, and titanium oxide was 3.0 parts. A NOx high-degradability photocatalytic inorganic sheet of No. 4 was prepared.

【0018】[実施例5]CSF約265mlに叩解し
た木材パルプの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A型1.2g、
水酸化カルシウム1.2g、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%アニオン性凝集剤(栗田工業社製、HH−
351)50gを加え、5分後にJIS 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5
のNOx高分解性光触媒無機シートを得た。
Example 5 While stirring 10 g of a 4% aqueous suspension of wood pulp beaten to about 265 ml of CSF,
25 g of 0.1% polydiallyldimethylammonium chloride aqueous solution was added, and after 3 minutes 1.2 g of zeolite A type,
65 g of an aqueous suspension containing 1.2 g of calcium hydroxide, 1.2 g of titanium oxide, and 1.5 g of ceramic fibers was added, and a 0.1% anionic flocculant (HH- manufactured by Kurita Water Industries Ltd.) was added.
351) 50 g was added, and 5 minutes later, JIS P 8209
A sheet was prepared according to the above procedure, and the sheet was impregnated with alumina sol, which is a dispersion liquid of components for forming an inorganic support. This is pressed and fired in the same manner as in Example 1, and Example 5
A highly decomposable photocatalytic inorganic sheet of NOx was obtained.

【0019】[実施例6]実施例5において、ゼオライ
トA型1.8g、水酸化カルシウム0gおよび酸化チタ
ン1.8gにする以外は、すべて実施例5と同一の方法
で実施例6のNOx高分解性光触媒シートを得た。
[Example 6] In the same manner as in Example 5, except that the amount of zeolite A used was 1.8 g, the amount of calcium hydroxide was 0 g, and the amount of titanium oxide was 1.8 g, the NOx content of Example 6 was increased. A degradable photocatalyst sheet was obtained.

【0020】[実施例7]実施例5において、ゼオライ
トA型0g、水酸化カルシウム1.8gおよび酸化チタ
ン1.8gにする以外は、すべて実施例5と同一の方法
で実施例7のNOx高分解性光触媒シートを得た。
[Example 7] The NOx content of Example 7 was increased in the same manner as in Example 5, except that 0 g of zeolite A type, 1.8 g of calcium hydroxide and 1.8 g of titanium oxide were used in Example 5. A degradable photocatalyst sheet was obtained.

【0021】[実施例8]CSF約265 mlに叩解
した木材パルプの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A型1.8g、
水酸化カルシウム1.8g、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%アニオン
性凝集剤(栗田工業社製、HH−351)50gを加
え、5分後にJIS P 8209に準拠してシートを
調製し、これを酸化チタンゾル(石原産業社製、STS
−01)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8のNOx高分解性光
触媒無機シートを得た。
Example 8 While stirring 10 g of a 4% water suspension of wood pulp beaten to about 265 ml of CSF,
25 g of 0.1% polydiallyldimethylammonium chloride aqueous solution was added, and after 3 minutes, 1.8 g of zeolite A type,
65 g of an aqueous suspension containing 1.8 g of calcium hydroxide and 1.5 g of ceramic fibers was added, and 50 g of 0.1% anionic flocculant (HH-351 manufactured by Kurita Water Industries Ltd.) was added, and after 5 minutes JIS. A sheet was prepared in accordance with P 8209, and the sheet was prepared by using titanium oxide sol (STS manufactured by Ishihara Sangyo Co., Ltd.
-01) was impregnated. This was pressed and fired in the same manner as in Example 1 to obtain a NOx highly decomposable photocatalytic inorganic sheet of Example 8.

【0022】[実施例9]実施例8において、ゼオライ
トA型3.6g、水酸化カルシウム0gにする以外は、
すべて実施例8と同一の方法で実施例9のNOx高分解
性光触媒シートを得た。
[Example 9] In Example 8 except that 3.6 g of zeolite A type and 0 g of calcium hydroxide were used,
The NOx highly decomposable photocatalyst sheet of Example 9 was obtained in the same manner as in Example 8.

【0023】[実施例10]実施例8において、ゼオラ
イトA型0g、水酸化カルシウム3.6gにする以外
は、すべて実施例8と同一の方法で実施例10のNOx
高分解性光触媒シートを得た。
[Example 10] The same procedure as in Example 8 was repeated except that the amount of zeolite A was 0 g and the amount of calcium hydroxide was 3.6 g.
A highly decomposable photocatalyst sheet was obtained.

【0024】[比較例1]CSF約265mlに叩解し
た木材パルプ1.0部、ゼオライトY型(東ソー社製、
HSZ−320NAA)2.0部、水酸化マグネシウム
2.0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−520)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3.5kPa、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250
g/mの、比較例1のNOx分解性光触媒無機シート
を得た。
Comparative Example 1 1.0 part of wood pulp beaten to about 265 ml of CSF, zeolite Y type (manufactured by Tosoh Corporation,
HSZ-320NAA) 2.0 parts, magnesium hydroxide 2.0 parts, titanium oxide (made by Ishihara Sangyo Co., Ltd., ST-31)
2.0 parts, 3.0 parts of ceramic fibers (Isolite Kogyo, Kao Wool Bulk LS), 4.0 parts of alumina sol (Alumina sol-520 manufactured by Nissan Chemical Industries, Ltd.) and 7.0 parts of water were added, and the mixture was kneaded with a kneader. did. Place a wire mesh of 80 mesh on a stainless plate having holes at intervals of about 10 mm,
The kneaded raw material was spread thereon as evenly as possible, and was pressed at 3.5 kPa for 5 minutes using a handmade paper press. The resulting sheet is baked at 700 ° C for 20 minutes and the basis weight is about 250.
A NOx-decomposable photocatalytic inorganic sheet of Comparative Example 1 with g / m 2 was obtained.

【0025】[比較例2]比較例1においてゼオライト
Y型を0部、水酸化マグネシウムを0部、酸化チタンを
6.0部にする以外は、すべて比較例2と同一の方法で
比較例2のNOx分解性光触媒無機シートを調製した。
[Comparative Example 2] Comparative Example 2 was carried out in the same manner as Comparative Example 2 except that the zeolite Y type was 0 part, the magnesium hydroxide was 0 part, and the titanium oxide was 6.0 parts in Comparative Example 1. A NOx decomposable photocatalytic inorganic sheet was prepared.

【0026】[比較例3]比較例1においてゼオライト
Y型を3.0部、水酸化マグネシウムを0部、酸化チタ
ンを3.0部にする以外は、すべて比較例1と同一の方
法で比較例3のNOx分解性光触媒無機シートを調製し
た。
[Comparative Example 3] Comparative Example 3 was carried out in the same manner as Comparative Example 1 except that the zeolite Y type was 3.0 parts, the magnesium hydroxide was 0 part, and the titanium oxide was 3.0 parts. The NOx decomposable photocatalytic inorganic sheet of Example 3 was prepared.

【0027】[比較例4]比較例1においてゼオライト
Y型を0部、水酸化マグネシウムを3.0部、酸化チタ
ンを3.0部にする以外は、すべて比較例1と同一の方
法で比較例4のNOx分解性光触媒無機シートを調製し
た。
[Comparative Example 4] Comparative Example 1 is the same as Comparative Example 1 except that the zeolite Y type is 0 part, magnesium hydroxide is 3.0 parts, and titanium oxide is 3.0 parts. The NOx decomposable photocatalytic inorganic sheet of Example 4 was prepared.

【0028】[比較例5]CSF約265mlに叩解し
た木材パルプの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分後に酸化チタン3.6g、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%アニオン性凝集剤(栗田工業社製、HH−
351)50gを加え、5分後にJIS 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、比較例5
のNOx分解性光触媒無機シートを得た。
[Comparative Example 5] While stirring 10 g of a 4% aqueous suspension of wood pulp beaten to about 265 ml of CSF,
25 g of 0.1% polydiallyldimethylammonium chloride aqueous solution was added, and after 3 minutes, 65 g of water suspension containing 3.6 g of titanium oxide and 1.5 g of ceramic fiber was added, and further 0.1% anionic flocculant (Kurita HH- manufactured by Kogyo Co., Ltd.
351) 50 g was added, and 5 minutes later, JIS P 8209
A sheet was prepared according to the above procedure, and the sheet was impregnated with alumina sol, which is a dispersion liquid of components for forming an inorganic support. This was pressed and fired in the same manner as in Example 1, and Comparative Example 5
A NOx decomposable photocatalytic inorganic sheet was obtained.

【0029】[比較例6]CSF約265mlに叩解し
た木材パルプの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Y型1.8g、
酸化チタン1.8g、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%アニオン性凝集
剤(栗田工業社製、HH−351)50gを加え、5分
後にJIS 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、比較例6のNOx分解性光触媒無機シ
ートを得た。
Comparative Example 6 While stirring 10 g of a 4% water suspension of wood pulp beaten to about 265 ml of CSF,
25 g of 0.1% polydiallyldimethylammonium chloride aqueous solution was added, and after 3 minutes, 1.8 g of zeolite Y type,
65 g of an aqueous suspension containing 1.8 g of titanium oxide and 1.5 g of ceramic fiber was added, and 50 g of 0.1% anionic flocculant (HH-351 manufactured by Kurita Water Industries Ltd.) was added, and after 5 minutes, JIS P Prepare a sheet according to 8209,
This was impregnated with alumina sol, which is a dispersion liquid of the inorganic support-forming component. This was pressed and fired in the same manner as in Example 1 to obtain a NOx decomposable photocatalytic inorganic sheet of Comparative Example 6.

【0030】[比較例7]CSF約265mlに叩解し
た木材パルプの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分後に水酸化マグネシウム1.8
g、酸化チタン1.8g、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%アニオン性
凝集剤(栗田工業社製、HH−351)50gを加え、
5分後にJIS 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、比較例7のNOx分解性光触媒無
機シートを得た。
Comparative Example 7 While stirring 10 g of a 4% aqueous suspension of wood pulp beaten to about 265 ml of CSF,
25 g of 0.1% polydiallyldimethylammonium chloride aqueous solution was added, and 3 minutes later, magnesium hydroxide 1.8 was added.
g, 1.8 g of titanium oxide, and 65 g of an aqueous suspension containing 1.5 g of ceramic fibers were added, and further 50 g of 0.1% anionic flocculant (HH-351 manufactured by Kurita Water Industries Ltd.) was added,
After 5 minutes, a sheet was prepared according to JIS P 8209 and impregnated with an alumina sol which is a dispersion liquid of components for forming an inorganic support. This was pressed and fired in the same manner as in Example 1 to obtain a NOx decomposable photocatalytic inorganic sheet of Comparative Example 7.

【0031】[比較例8]CSF約265mlに叩解し
た木材パルプの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Y型1.8g、
水酸化マグネシウム1.8g、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%アニオ
ン性凝集剤(栗田工業社製、HH−351)50gを加
え、5分後にJIS P 8209に準拠してシートを
調製し、これを酸化チタンゾル(石原産業社製、STS
−01)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、比較例8のNOx分解性光触
媒無機シートを得た。
[Comparative Example 8] While stirring 10 g of a 4% aqueous suspension of wood pulp beaten to about 265 ml of CSF,
25 g of 0.1% polydiallyldimethylammonium chloride aqueous solution was added, and after 3 minutes, 1.8 g of zeolite Y type,
Magnesium hydroxide 1.8g, ceramic fiber 1.5g
65 g of a water suspension containing 0.1 g of 0.1% anionic flocculant (HH-351 manufactured by Kurita Water Industries Ltd.) was added, and after 5 minutes, a sheet was prepared according to JIS P 8209. Titanium oxide sol (made by Ishihara Sangyo Co., Ltd., STS
-01) was impregnated. This was pressed and fired in the same manner as in Example 1 to obtain a NOx decomposable photocatalytic inorganic sheet of Comparative Example 8.

【0032】[比較例9]比較例8においてゼオライト
Y型を3.6g、水酸化マグネシウムを0gにする以外
は、すべて比較例8と同一の方法で比較例9のNOx分
解性光触媒無機シートを調製した。
[Comparative Example 9] A NOx decomposable photocatalytic inorganic sheet of Comparative Example 9 was prepared in the same manner as Comparative Example 8 except that the amount of zeolite Y type was 3.6 g and the amount of magnesium hydroxide was 0 g. Prepared.

【0033】[比較例10]比較例8においてゼオライ
トY型を0、水酸化マグネシウムを3.6gにする以外
は、すべて比較例8と同一の方法で比較例10のNOx
分解性光触媒無機シートを調製した。
[Comparative Example 10] NOx of Comparative Example 10 was the same as Comparative Example 8 except that the amount of zeolite Y type was 0 and the amount of magnesium hydroxide was 3.6 g.
A degradable photocatalytic inorganic sheet was prepared.

【0034】以上、実施例および比較例で得られたNO
x分解性光触媒無機シートは、以下の方法で試験を行
い、その結果を表に示した。
The NO values obtained in the above examples and comparative examples
The x-decomposable photocatalytic inorganic sheet was tested by the following method, and the results are shown in the table.

【0035】[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 Material]
It was calcined for 20 minutes in an electric furnace at 00 ° C., and determined from the residual ash content.

【0036】[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] It was measured according to the compression strength test (ring crush method) Tappi T 818-87.

【0037】[光触媒分解能]窒素酸化物測定装置(島
津製作所、CLAD−1000A型)を用いて、窒素酸
化物濃度を測定した。100ppm濃度のNOを空気で
0.25ppmに希釈して模擬NOxを調製した。これ
を相対湿度50%に調湿し、1.5L/minの流量で
装置に連続して供給した。装置に付属した反応室に実施
例および比較例で調製したシート(25×75mm)を
置き、UV照射(0.3mW/cm)を行った。測定
は5時間連続して行い、この間に分解されたNO量と発
生したNO量から光触媒分解能を評価した。
[Photocatalytic Decomposition] The nitrogen oxide concentration was measured using a nitrogen oxide measuring device (CLAD-1000A type, manufactured by Shimadzu Corporation). Simulated NOx was prepared by diluting 100 ppm NO to 0.25 ppm with air. This was conditioned to a relative humidity of 50% and continuously supplied to the device at a flow rate of 1.5 L / min. The sheets (25 × 75 mm) prepared in Examples and Comparative Examples were placed in a reaction chamber attached to the apparatus, and UV irradiation (0.3 mW / cm 2 ) was performed. The measurement was continuously performed for 5 hours, and the photocatalytic resolution was evaluated from the amount of NO decomposed and the amount of NO 2 generated during this period.

【0038】[0038]

【表】 【table】

【0039】[0039]

【発明の効果】本発明方法により調製したNOx高分解
能光触媒無機シートは、NOxの光酸化中間体を効率的
に共存無機吸着剤で保持し、これがさらに酸化されて生
成する光触媒効果を低下させる硝酸を共存金属酸化物と
反応させて中和するので光触媒反応が持続し、高効率で
長期間使用出来るので、非常に有用性の高いものであ
る。
INDUSTRIAL APPLICABILITY The NOx high-resolution photocatalytic inorganic sheet prepared by the method of the present invention efficiently retains a photooxidation intermediate of NOx by a coexisting inorganic adsorbent, and further nitric acid reduces the photocatalytic effect produced by further oxidation. Is neutralized by reacting with the coexisting metal oxide, so that the photocatalytic reaction can be continued and can be used with high efficiency for a long period of time, which is very useful.

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 4D048 AA06 AB03 BA07X BA41X CA06 EA01 EA04 4G069 AA03 AA08 BA04B CA01 CA10 CA13 DA05 EA07 FA01 FB15 FB68 FB70    ─────────────────────────────────────────────────── ─── Continued front page    F-term (reference) 4D048 AA06 AB03 BA07X BA41X                       CA06 EA01 EA04                 4G069 AA03 AA08 BA04B CA01                       CA10 CA13 DA05 EA07 FA01                       FB15 FB68 FB70

Claims (3)

【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るNOx高分解性光触媒無機シー
ト。
1. A NOx highly decomposable photocatalytic inorganic sheet comprising an inorganic adsorbent, a photocatalyst, an inorganic fiber and an inorganic support-forming component.
【請求項2】金属酸化物、光触媒、無機繊維および無機
支持体形成成分からなるNOx高分解性光触媒無機シー
ト。
2. An NOx highly decomposable photocatalyst inorganic sheet comprising a metal oxide, a photocatalyst, an inorganic fiber and an inorganic support-forming component.
【請求項3】無機吸着剤、金属酸化物、光触媒、無機繊
維および無機支持体形成成分からなるNOx高分解性光
触媒無機シート。
3. A NOx highly decomposable photocatalyst inorganic sheet comprising an inorganic adsorbent, a metal oxide, a photocatalyst, an inorganic fiber and an inorganic support-forming component.
JP2002059503A 2002-01-30 2002-01-30 PHOTOCATALYST INORGANIC SHEET FOR EFFECTIVELY DECOMPOSING NOx Pending JP2003220318A (en)

Priority Applications (1)

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JP2002059503A JP2003220318A (en) 2002-01-30 2002-01-30 PHOTOCATALYST INORGANIC SHEET FOR EFFECTIVELY DECOMPOSING NOx

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2002059503A JP2003220318A (en) 2002-01-30 2002-01-30 PHOTOCATALYST INORGANIC SHEET FOR EFFECTIVELY DECOMPOSING NOx

Publications (1)

Publication Number Publication Date
JP2003220318A true JP2003220318A (en) 2003-08-05

Family

ID=27751111

Family Applications (1)

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Country Link
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006297351A (en) * 2005-04-25 2006-11-02 Showa Denko Kk Photocatalyst film and manufacturing method
JP2006297350A (en) * 2005-04-25 2006-11-02 Showa Denko Kk Photocatalyst film and manufacturing method

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006297351A (en) * 2005-04-25 2006-11-02 Showa Denko Kk Photocatalyst film and manufacturing method
JP2006297350A (en) * 2005-04-25 2006-11-02 Showa Denko Kk Photocatalyst film and manufacturing method

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