JPH11347420A - Member having photocatalytic function - Google Patents

Member having photocatalytic function

Info

Publication number
JPH11347420A
JPH11347420A JP11014879A JP1487999A JPH11347420A JP H11347420 A JPH11347420 A JP H11347420A JP 11014879 A JP11014879 A JP 11014879A JP 1487999 A JP1487999 A JP 1487999A JP H11347420 A JPH11347420 A JP H11347420A
Authority
JP
Japan
Prior art keywords
particles
layer
photocatalyst
tio
glaze layer
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
JP11014879A
Other languages
Japanese (ja)
Inventor
Toshiya Watabe
俊也 渡部
Atsushi Kitamura
厚 北村
Eiichi Kojima
栄一 小島
Yoshimitsu Saeki
義光 佐伯
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Toto Ltd
Original Assignee
Toto Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Toto Ltd filed Critical Toto Ltd
Priority to JP11014879A priority Critical patent/JPH11347420A/en
Publication of JPH11347420A publication Critical patent/JPH11347420A/en
Pending legal-status Critical Current

Links

Landscapes

  • Finishing Walls (AREA)
  • Panels For Use In Building Construction (AREA)
  • Building Environments (AREA)
  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
  • Application Of Or Painting With Fluid Materials (AREA)
  • Laminated Bodies (AREA)
  • Catalysts (AREA)

Abstract

PROBLEM TO BE SOLVED: To improve the photocatalytic effect by forming a layer of photocatalyst particles on a binder layer on a substrate surface and using TiO2 fine particles having a specified range of average particle size as the photocatalyst particles. SOLUTION: A glaze layer 2 as a material which is hardly decomposed by the photocatalytic function of photocatalyst particles is applied on the surface of a tile base 1 as the planer member which constitutes walls, floors or ceilings. Then anatase type TiO2 particles in a sol state as photocatalyst particles are applied by spraying or the like on the surface of the glaze layer 2. After the glaze layer 2 is heated and fused, and then cooled and solidified. Then the layer is heated at 300 to 900 deg.C to form a photocatalyst layer consisting of the anatase TiO2 particles 3 having >=100 Å and <500 Åaverage particle size on the glaze layer 2.

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、脱臭、抗菌、防汚
等の光触媒機能を有する部材に関する。
The present invention relates to a member having a photocatalytic function such as deodorization, antibacterial and antifouling.

【0002】[0002]

【従来の技術】紫外線の照射を受けて脱臭反応を進行さ
せる光触媒としてアナターゼ型のTiO2が知られてい
る。そして、光触媒粒子をバインダに混練した原料を居
住空間の壁面を構成する部材の表面に塗布した後に焼成
することで、居住空間の壁面に脱臭壁機能をもたせるよ
うにした提案を本出願人は先に行なっている。
2. Description of the Related Art Anatase-type TiO 2 is known as a photocatalyst for promoting a deodorizing reaction upon irradiation with ultraviolet rays. The applicant of the present invention has proposed a proposal in which the raw material obtained by kneading the photocatalyst particles into a binder is applied to the surface of a member constituting the wall surface of the living space and then fired so that the wall surface of the living space has a deodorizing wall function. I have done it.

【0003】[0003]

【発明が解決しようとする課題】図10は脱臭壁の一部
部分拡大断面図であり、壁材100の表面にはバインダ
層101が形成され、このバインダ層101内に光触媒
粒子102が保持されている。
FIG. 10 is a partially enlarged cross-sectional view of a deodorizing wall. A binder layer 101 is formed on the surface of a wall material 100, and photocatalyst particles 102 are held in the binder layer 101. ing.

【0004】従来にあってはバインダ層101内に光触
媒粒子102が完全に埋まっているため、脱臭壁全体と
しては、全ての光触媒粒子102に直接紫外線が照射さ
れず、また、光触媒粒子102の平均粒径も比較的大き
く、十分な触媒作用を発揮することができない。
In the prior art, since the photocatalyst particles 102 are completely buried in the binder layer 101, the entire deodorizing wall does not directly irradiate all the photocatalyst particles 102 with ultraviolet rays. The particle size is relatively large, and a sufficient catalytic action cannot be exhibited.

【0005】[0005]

【課題を解決するための手段】上記課題を解決すべく本
発明に係る光触媒機能を有する部材は、基材表面にバイ
ンダ層を介して光触媒粒子の層を設けるとともに、光触
媒粒子としては平均粒径が100Å以上500Å未満の
TiO2微粒子を用いるようにした。
Means for Solving the Problems To solve the above problems, a member having a photocatalytic function according to the present invention is provided with a layer of photocatalyst particles on a surface of a base material via a binder layer, and the photocatalyst particles have an average particle diameter. TiO 2 fine particles having a thickness of 100 ° or more and less than 500 ° are used.

【0006】このように、バインダ層を介して光触媒粒
子の層を保持することで、光触媒粒子に十分に紫外線を
照射することができ、更に光触媒粒子としてTiO2微粒
子を用い、且つその平均粒径を100Å以上500Å未
満とすることで、光触媒作用が更に向上する。
As described above, by holding the layer of the photocatalyst particles through the binder layer, the photocatalyst particles can be sufficiently irradiated with ultraviolet rays. Further, TiO 2 fine particles are used as the photocatalyst particles, and the average particle size thereof is used. Is set to 100 ° or more and less than 500 °, the photocatalytic action is further improved.

【0007】[0007]

【発明の実施の形態】以下に本発明の実施の形態を添付
図面に基づいて説明する。ここで、図1は本発明に係る
セラミック、陶器、ガラス、金属等の基材表面に光触媒
層を形成した光触媒機能を有する部材の製造方法を工程
順に示した図である。
Embodiments of the present invention will be described below with reference to the accompanying drawings. Here, FIG. 1 is a diagram showing a method of manufacturing a member having a photocatalytic function in which a photocatalytic layer is formed on the surface of a base material such as ceramic, pottery, glass, and metal according to the present invention in the order of steps.

【0008】本発明方法にあっては先ず図1(a)に示
すように、壁面、床面或いは天井面を構成する板状部材
としてのタイル素地1の表面に光触媒粒子による光触媒
機能によって分解されにくい材料である釉薬層2を塗布
し、次いで図1(b)に示すように釉薬層2の表面にス
プレー等を用いて光触媒粒子としてのアナターゼ型Ti
O2粒子3をゾル状にして吹き付け、次いで図1(c)
に示すように釉薬層2を加熱溶融せしめた後、冷却して
固化せしめる。尚、TiO2ゾルにはCuやAg等を添加し
て殺菌効果をもたせるようにしてもよい。添加の方法と
しては例えばCuSO4をNH3溶液でpH11程度に調
整したTiO2ゾルに添加する。
In the method of the present invention, first, as shown in FIG. 1 (a), the surface of a tile substrate 1 as a plate-like member constituting a wall surface, a floor surface or a ceiling surface is decomposed by a photocatalytic function of photocatalytic particles. A glaze layer 2, which is a difficult material, is applied, and then, as shown in FIG. 1B, the surface of the glaze layer 2 is sprayed or the like to form anatase Ti as photocatalyst particles.
The O2 particles 3 are sprayed in the form of a sol, and then FIG.
After the glaze layer 2 is heated and melted as shown in FIG. 3, it is cooled and solidified. Incidentally, Cu, Ag or the like may be added to the TiO 2 sol to have a bactericidal effect. As an addition method, for example, CuSO 4 is added to a TiO 2 sol adjusted to about pH 11 with an NH 3 solution.

【0009】そして、TiO2ゾルを前記したように釉薬
層2の表面に吹き付けた後に、300〜900℃の範囲
で加熱することで、釉薬層2上にアナターゼ型TiO2
子3からなる光触媒層が形成される。
After the TiO 2 sol is sprayed on the surface of the glaze layer 2 as described above, the sol is heated at a temperature in the range of 300 to 900 ° C. so that the photocatalytic layer composed of the anatase type TiO 2 particles 3 is formed on the glaze layer 2. Is formed.

【0010】また、紫外線がTiO2粒子3に照射される
と、吸着水と光触媒の正孔とが反応して水酸基ラジカル
(OH*)を生成し、この水酸基ラジカルとアンモニア
とが下式(1)のように反応し、また水酸基ラジカルと
メチルメルカプタンとが下式(2)のように反応して脱
臭すると考えられる。
When the TiO 2 particles 3 are irradiated with ultraviolet rays, the adsorbed water reacts with the holes of the photocatalyst to generate hydroxyl radicals (OH * ), and the hydroxyl radicals and ammonia are converted into the following formula (1). ), And the hydroxyl radical and methyl mercaptan react as shown in the following formula (2) to deodorize.

【0011】 NH3+3OH*→1/2N2+3H2O・・・・・・・・・・・(1) CH3SH+OH*→CH3S+H2O 2CH3S+2OH*+5O2→2CO2+4H2O+2SO2 ・・(2)NH 3 + 3OH * → 1 / 2N 2 + 3H 2 O (1) CH 3 SH + OH * → CH 3 S + H 2 O 2 CH 3 S + 2OH * + 5O 2 → 2CO 2 + 4H 2 O + 2SO 2・ ・ (2)

【0012】図2乃至図6は別実施例を示す図であり、
図2に示す実施例にあっては、釉薬層2の表面に印刷に
よってインク層4を形成し、このインク層4の表面にT
iO2粒子3をその一部が露出するように吹き付け、その
後は前記と同様に加熱し冷却する。
FIGS. 2 to 6 show another embodiment.
In the embodiment shown in FIG. 2, an ink layer 4 is formed on the surface of the glaze layer 2 by printing, and T
The TiO 2 particles 3 are sprayed so that a part thereof is exposed, and then heated and cooled in the same manner as described above.

【0013】図3に示す実施例は、離型紙5の表面に水
溶性バインダ6を介して釉薬層2を形成し、この釉薬層
2の表面にバインダ層7を形成し、このバインダ層7の
表面にTiO2粒子3を吹き付けてシートSを得る。そし
て、離型紙5を剥離してシートSをタイル素地1表面に
貼着し、この後前記と同様にして加熱し冷却する。この
ように光触媒機能を有するシートSを別体として用意し
ておけば、既存のタイル等にも脱臭等の光触媒機能を簡
単に付与することができる。
In the embodiment shown in FIG. 3, a glaze layer 2 is formed on the surface of a release paper 5 via a water-soluble binder 6, and a binder layer 7 is formed on the surface of the glaze layer 2. The sheet S is obtained by spraying TiO2 particles 3 on the surface. Then, the release paper 5 is peeled off, the sheet S is adhered to the surface of the tile substrate 1, and then heated and cooled in the same manner as described above. If the sheet S having the photocatalytic function is prepared separately as described above, a photocatalytic function such as deodorization can be easily imparted to existing tiles and the like.

【0014】図4に示す実施例は、インク層4の表面に
部分的にTiO2粒子3を付着せしめて絵柄とし、装飾効
果を高めるようにしたものであり、TiO2粒子3を釉薬
層2の表面に形成してもよい。
[0014] embodiment shown in FIG. 4, the pattern partially by adhering the TiO 2 particles 3 on the surface of the ink layer 4, which was set to increase the decorative effect, the glaze layer 2 of TiO 2 particles 3 May be formed on the surface.

【0015】図5(a)、(b)に示す実施例は、タイ
ル素地1に滑り止め等の目的で形成した凹部に釉薬層2
を介してTiO2粒子3を保持したものである。このよう
に凹部を形成した場合には凹部に汚れが入り込み汚れが
落ちにくいが、TiO2粒子3を保持することで、凹部内
の汚れが分解されるので汚れを簡単に除去できる。
In the embodiment shown in FIGS. 5A and 5B, a glaze layer 2 is formed in a recess formed in a tile base 1 for the purpose of preventing slippage.
And the TiO 2 particles 3 are held through the intermediary. When the concave portion is formed in this way, the dirt enters the concave portion and the dirt is difficult to remove. However, the dirt in the concave portion is decomposed by holding the TiO 2 particles 3, so that the dirt can be easily removed.

【0016】図6に示す実施例は、釉薬層2とTiO2
子3との間に蒸着アルミニウム粉末やマグネシア等から
なる紫外線反射層8を介在させたものであり、このよう
な構成とすることで、一旦TiO2粒子3の層を透過した
紫外線を再びTiO2粒子3に照射することができ、触媒
作用が向上する。
In the embodiment shown in FIG. 6, an ultraviolet reflecting layer 8 made of vapor-deposited aluminum powder or magnesia is interposed between the glaze layer 2 and the TiO 2 particles 3. in, once the ultraviolet rays transmitted through a layer of TiO 2 particles 3 again can be irradiated to the TiO 2 particles 3, catalysis can be improved.

【0017】図7はCH3SH濃度と経過時間との関係
を熱処理(焼成)温度毎に試験した結果を示すグラフで
あり、グラフ中τ1/10は濃度が1/10になるまでの時
間を示し、点線は紫外線を照射しない場合を示す。また
アナターゼ型TiO2粒子は平均粒径100Åのものを用
いた。
FIG. 7 is a graph showing the test results of the relationship between the CH 3 SH concentration and the elapsed time for each heat treatment (firing) temperature. In the graph, τ 1/10 represents the time until the concentration becomes 1/10. The dotted line shows the case where no ultraviolet light is irradiated. The anatase type TiO 2 particles having an average particle diameter of 100 ° were used.

【0018】また、図8は熱処理温度と30分後の臭気
除去率との関係を実験した結果を示すグラフであり、図
9は平均粒径500Åのアナターゼ型TiO2を用いた場
合のCH3SH濃度と経過時間との関係(熱処理温度;
700℃)を示すグラフである。
FIG. 8 is a graph showing the results of an experiment on the relationship between the heat treatment temperature and the odor removal rate after 30 minutes. FIG. 9 shows CH 3 when anatase type TiO 2 having an average particle size of 500 ° was used. Relationship between SH concentration and elapsed time (heat treatment temperature;
700 ° C.).

【0019】これら図7、図8及び図9から以下のこと
が言える。第1に紫外線の存在下においてアナターゼ型
TiO2は触媒作用を発揮する。第2に触媒作用は700
℃付近で最大値を示し、30分後の臭気除去率を50%
以上とするには300℃以上で900℃未満とする必要
がある。これは熱処理温度が300℃未満では活性が生
じにくく900℃を超えるとTiO2の構造がアナターゼ
からルチルに変化するからと考えられる。第3に触媒作
用は、粒径のある程度小さな、具体的には平均粒径10
0Å〜500Åのアナターゼがよいことが分る。
The following can be said from FIG. 7, FIG. 8 and FIG. First, in the presence of ultraviolet light, anatase-type TiO 2 exerts a catalytic action. Second, the catalysis is 700
The maximum value is shown around ℃, and the odor removal rate after 30 minutes is 50%.
In order to achieve the above, it is necessary to set the temperature to 300 ° C. or higher and lower than 900 ° C. This is presumably because the activity is unlikely to occur when the heat treatment temperature is lower than 300 ° C, and the structure of TiO 2 changes from anatase to rutile when the heat treatment temperature exceeds 900 ° C. Third, the catalytic action is that the particle size is somewhat small, specifically, the average particle size is 10%.
It can be seen that 0 to 500 degrees anatase is good.

【0020】[0020]

【発明の効果】以上に説明した如く本発明によれば、基
材表面にバインダ層を介して光触媒粒子の層を設けると
ともに、光触媒粒子としては平均粒径が100Å以上5
00Å未満のTiO2微粒子を用いるようにしたので、光
触媒作用が向上する。
As described above, according to the present invention, a layer of photocatalyst particles is provided on the surface of a base material via a binder layer, and the average particle size of the photocatalyst particles is 100 ° or more.
Since the TiO2 fine particles of less than 00 ° are used, the photocatalytic action is improved.

【図面の簡単な説明】[Brief description of the drawings]

【図1】本発明に係る光触媒機能を有する部材の製造方
法を工程順に示した図。
FIG. 1 is a view showing a method of manufacturing a member having a photocatalytic function according to the present invention in the order of steps.

【図2】別実施例を示す部材の断面図。FIG. 2 is a sectional view of a member showing another embodiment.

【図3】別実施例を示す部材の断面図。FIG. 3 is a sectional view of a member showing another embodiment.

【図4】別実施例を示す部材の断面図。FIG. 4 is a sectional view of a member showing another embodiment.

【図5】別実施例を示す部材の断面図。FIG. 5 is a sectional view of a member showing another embodiment.

【図6】別実施例を示す部材の断面図。FIG. 6 is a sectional view of a member showing another embodiment.

【図7】平均粒径100Åのアナターゼ型TiO2を用い
た場合の経過時間とCH3SH濃度との関係を示すグラ
フ。
FIG. 7 is a graph showing the relationship between elapsed time and CH 3 SH concentration when anatase type TiO 2 having an average particle size of 100 ° is used.

【図8】熱処理温度と30分後の臭気除去率との関係を
示すグラフ。
FIG. 8 is a graph showing the relationship between the heat treatment temperature and the odor removal rate after 30 minutes.

【図9】平均粒径500Åのアナターゼ型TiO2を用い
た場合の経過時間とCH3SH濃度との関係を示すグラ
フ。
FIG. 9 is a graph showing the relationship between elapsed time and CH 3 SH concentration when anatase type TiO 2 having an average particle size of 500 ° is used.

【図10】従来の製造方法によって得られた光触媒機能
を有する部材の断面図。
FIG. 10 is a cross-sectional view of a member having a photocatalytic function obtained by a conventional manufacturing method.

【符号の説明】[Explanation of symbols]

1…タイル素地、2…釉薬層、3…TiO2粒子、4…イ
ンク層、5…離型紙、6…水溶性バインダ、7…バイン
ダ層、8…紫外線反射層、S…シート、100…壁材、
101…バインダ層、102…光触媒粒子。
1 ... tile base material, 2 ... glaze layer, 3 ... TiO 2 particles, 4 ... ink layer, 5 ... release paper 6 ... water-soluble binder, 7 ... binder layer, 8 ... UV-reflecting layer, S ... sheet, 100 ... wall Timber,
101: binder layer, 102: photocatalyst particles.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI B32B 9/00 B32B 9/00 A E04B 1/92 E04B 1/92 E04C 2/04 E04C 2/04 C E04F 13/08 E04F 13/08 A (72)発明者 小島 栄一 福岡県北九州市小倉北区中島2丁目1番1 号 東陶機器株式会社内 (72)発明者 佐伯 義光 福岡県北九州市小倉北区中島2丁目1番1 号 東陶機器株式会社内──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 6 Identification code FI B32B 9/00 B32B 9/00 A E04B 1/92 E04B 1/92 E04C 2/04 E04C 2/04 C E04F 13/08 E04F 13 / 08 A (72) Inventor Eiichi Kojima 2-1-1 Nakajima, Kokurakita-ku, Kitakyushu-city, Fukuoka Prefecture Inside Totoki Equipment Co., Ltd. (72) Yoshimitsu Saeki 2-1-1 Nakajima, Kokurakita-ku, Kitakyushu-shi, Fukuoka Prefecture No. Totoki Co., Ltd.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 基材表面にバインダ層を介して光触媒粒
子の層を保持した光触媒機能を有する部材であって、前
記光触媒粒子は平均粒径が100オングストローム以上
500オングストローム未満のTiO2微粒子であること
を特徴とする光触媒機能を有する部材。
1. A member having a photocatalytic function in which a layer of photocatalyst particles is held on a surface of a base material via a binder layer, wherein the photocatalyst particles are TiO 2 fine particles having an average particle diameter of 100 Å to less than 500 Å. A member having a photocatalytic function.
JP11014879A 1999-01-22 1999-01-22 Member having photocatalytic function Pending JPH11347420A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11014879A JPH11347420A (en) 1999-01-22 1999-01-22 Member having photocatalytic function

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11014879A JPH11347420A (en) 1999-01-22 1999-01-22 Member having photocatalytic function

Related Parent Applications (1)

Application Number Title Priority Date Filing Date
JP10159671A Division JPH1120068A (en) 1998-06-08 1998-06-08 Material having photocatalytic function and manufacture thereof

Related Child Applications (1)

Application Number Title Priority Date Filing Date
JP11062579A Division JPH11322524A (en) 1999-03-10 1999-03-10 Material having antibacterial activity

Publications (1)

Publication Number Publication Date
JPH11347420A true JPH11347420A (en) 1999-12-21

Family

ID=11873312

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11014879A Pending JPH11347420A (en) 1999-01-22 1999-01-22 Member having photocatalytic function

Country Status (1)

Country Link
JP (1) JPH11347420A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001199001A (en) * 2000-01-20 2001-07-24 Akira Fujishima Laminated structure having photocatalyst layer

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001199001A (en) * 2000-01-20 2001-07-24 Akira Fujishima Laminated structure having photocatalyst layer

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