JPH10272355A - Improved harmful substance-removing member - Google Patents

Improved harmful substance-removing member

Info

Publication number
JPH10272355A
JPH10272355A JP9098846A JP9884697A JPH10272355A JP H10272355 A JPH10272355 A JP H10272355A JP 9098846 A JP9098846 A JP 9098846A JP 9884697 A JP9884697 A JP 9884697A JP H10272355 A JPH10272355 A JP H10272355A
Authority
JP
Japan
Prior art keywords
harmful substance
removing member
weight
parts
water
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
JP9098846A
Other languages
Japanese (ja)
Inventor
Hideo Tawara
英男 田原
Yoshihiko Murata
義彦 村田
Koji Obata
浩司 小幡
Kiyoshi Kamiya
清志 神谷
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.)
Mitsubishi Materials Corp
Original Assignee
Mitsubishi Materials Corp
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 Mitsubishi Materials Corp filed Critical Mitsubishi Materials Corp
Priority to JP9098846A priority Critical patent/JPH10272355A/en
Publication of JPH10272355A publication Critical patent/JPH10272355A/en
Pending legal-status Critical Current

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  • Catalysts (AREA)
  • Road Paving Machines (AREA)
  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
  • Treating Waste Gases (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

PROBLEM TO BE SOLVED: To obtain a harmful substance-removing member having good harmful substance removing and purifying capacities and suitable for protecting environment. SOLUTION: This harmful substance-removing member is a hydrated coagulated substance obtained from a mixture consisting of a hydraulic compd., aggregate, a photocatalyst and water and at least either one of slaked lime, a water- soluble salt of a strong base and weak acid, a high capacity water reducing agent and an adsorbable substance is further added to the mixture. The photocatalyst is a certain kind of a semiconductor substance, that is, titanium dioxide. The water-soluble salt is sodium carbonate, sodium bicarbonate, sodium acetate, sodium hypochlorite or a bleaching powder and the high capacity water reducing agent is a sodium salt of naphthalenesulfonic acid formaldehyde high condensate and the adsorbable substance is activated carbon zeolite, magadite or petalite. A harmful substance capable of being removed by this harmful substance removing member is NOx, mercaptans, ammonia, hydrogen sulfide, amines or ethylene.

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、改良された有害物
質除去部材に関し、更に詳しくは本発明は、浄化性能が
向上した有害物質除去部材に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an improved harmful substance removing member, and more particularly to a harmful substance removing member having improved purification performance.

【0002】[0002]

【従来の技術】最近、地球環境の破壊が問題視されるな
か、光触媒又は光触媒物質が地球環境の汚染防止乃至は
浄化に役に立つことが注目され、例えば、表面の汚れの
防止、大気中のNOX の浄化、水の浄化、抗菌・防カ
ビ、脱臭等に応用された製品の開発が進められている。
この光触媒としては半導体、例えば二酸化チタン等の光
電導体が用いられ、具体的に特開平2−273514号
公報には、二酸化チタンの半導体と粘土とを練り合わ
せ、乾燥して得られる有害物質の除去剤が開示されてい
る。また特開平6−327965号公報には、エチレン
等の有害物質の除去剤として、水硬性化合物の水和凝集
物に特定の半導体を分散したものが開示されている。
2. Description of the Related Art In recent years, as the destruction of the global environment has been regarded as a problem, it has been noticed that photocatalysts or photocatalytic substances are useful for preventing or purifying the global environment. Development of products applied to purification of X , purification of water, antibacterial / antifungal, deodorizing, etc. is being promoted.
As the photocatalyst, a semiconductor, for example, a photoconductor such as titanium dioxide is used. Specifically, JP-A-2-273514 discloses a remover for harmful substances obtained by kneading a titanium dioxide semiconductor with clay and drying the clay. Is disclosed. JP-A-6-327965 discloses a dispersion of a specific semiconductor in a hydrated aggregate of a hydraulic compound as an agent for removing harmful substances such as ethylene.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、前述の
如く、特開平2−273514号公報に記載の有害物質
の除去剤は、有害物質の除去速度が低いため除去剤を大
量に使用する必要があり今一つ問題があり、また特開平
6−327965号公報に記載の有害物質除去剤は、そ
の除去効率は改善されているものの、なおいっそうの改
良が望まれている。そこで本発明者等は、前述の如き有
害物質除去剤の除去速度乃至除去効率を向上させる点に
つき、種々検討したところ、光触媒の光吸収率を向上さ
せ得る有害物質除去部材の構成とし、また光吸収率を向
上させる環境を形成することにより優れた有害物質除去
性能が得られることを見出し、本発明は、この知見に基
づいてなされたものである。したがって、本発明が解決
しようとする課題は、良好な有害物質の除去性能乃至浄
化性能を有し、環境保護に好ましい有害物質除去部材を
提供することにある。
However, as described above, the harmful substance removing agent described in Japanese Patent Application Laid-Open No. Hei 2-273514 requires a large amount of the harmful substance removing agent because the harmful substance removing speed is low. There is another problem, and the harmful substance removing agent described in JP-A-6-327965 has been improved in its removal efficiency, but further improvement is desired. Therefore, the present inventors have conducted various studies on the point of improving the removal rate or removal efficiency of the harmful substance removing agent as described above. As a result, a structure of a harmful substance removing member capable of improving the light absorption rate of the photocatalyst was obtained. The present inventors have found that an excellent environment for removing harmful substances can be obtained by forming an environment for improving the absorptivity, and the present invention has been made based on this finding. Therefore, an object of the present invention is to provide a harmful substance removing member having good harmful substance removal performance or purification performance and preferable for environmental protection.

【0004】[0004]

【課題を解決するための手段】本発明の上記課題は、以
下の各発明によりそれぞれ達成される。
The above objects of the present invention are attained by the following inventions.

【0005】(1)水硬性化合物、骨材、光触媒及び水
からなる混合物から得られた水和凝集物であることを特
徴とする有害物質除去部材。 (2)混合物に消石灰を含有していることを特徴とする
前記第1項に記載の有害物質除去部材。 (3)混合物に強塩基と弱酸の水溶性塩を含有している
ことを特徴とする前記第1項又は第2項に記載の有害物
質除去部材。 (4)混合物に高性能減水剤を含有していることを特徴
とする前記第1項乃至第3項のいずれかに記載の有害物
質除去部材。 (5)混合物に吸着性物質を含有していることを特徴と
する前記第1項乃至第4項のいずれかに記載の有害物質
除去部材。
(1) A harmful substance removing member characterized by being a hydrated aggregate obtained from a mixture of a hydraulic compound, an aggregate, a photocatalyst and water. (2) The harmful substance removing member according to (1), wherein the mixture contains slaked lime. (3) The harmful substance removing member according to (1) or (2), wherein the mixture contains a water-soluble salt of a strong base and a weak acid. (4) The harmful substance removing member according to any one of (1) to (3), wherein the mixture contains a high-performance water reducing agent. (5) The harmful substance removing member according to any one of (1) to (4), wherein the mixture contains an adsorptive substance.

【0006】このように本発明の有害物質除去部材は、
水硬性化合物、骨材、光触媒及び水からなる混合物から
得られた水和凝集物であり、特に骨材を混合したことに
より空隙ができ、光触媒の露出度が増大して光吸収率を
向上させることができ、その結果、優れた有害物質の除
去性能乃至浄化性能が得られるものである。また前記有
害物質除去部材に更に消石灰が含有していることにより
pHが向上し、その結果有害物質中、特にNOX を可溶
性塩として光触媒の系外に排出することにより光触媒の
浄化効率を向上させると共に自然環境の保護に好ましい
有害物質除去部材が得られる。また基体がコンクリート
である場合には、コンクリートの経時による酸性化を防
ぐことができる。
As described above, the harmful substance removing member of the present invention
A hydrated aggregate obtained from a mixture of a hydraulic compound, an aggregate, a photocatalyst, and water.Especially, when the aggregate is mixed, voids are formed, thereby increasing the degree of exposure of the photocatalyst and improving the light absorption rate. As a result, excellent harmful substance removal performance or purification performance can be obtained. Further, since the harmful substance removing member further contains slaked lime, pH is improved, and as a result, harmful substances, in particular, NO X are discharged as a soluble salt out of the photocatalyst system, thereby improving the purification efficiency of the photocatalyst. At the same time, a harmful substance removing member suitable for protecting the natural environment can be obtained. When the substrate is concrete, acidification of the concrete with the passage of time can be prevented.

【0007】本発明において、混合物に強塩基と弱酸の
水溶性塩を含有していることにより、NOxの分解で生
じた硝酸イオンをpHの緩衝作用のある前記水溶性塩に
よって中和してNOx浄化機能の低下を防止することが
できる。
In the present invention, since the mixture contains a water-soluble salt of a strong base and a weak acid, nitrate ions generated by the decomposition of NOx are neutralized by the water-soluble salt having a pH buffering action to form NOx. It is possible to prevent the purification function from lowering.

【0008】また本発明では、前記混合物に更に高性能
減水剤を含有していることにより、混合物を均一に分散
することができるので、したがって、光触媒も均一に存
在して光吸収作用に寄与することができる。更にまた前
記混合物に吸着性物質を含有していることにより、昼
間、光が当たっている状態では、有害物質は分解除去さ
れ、更に夜間では、有害物質は吸着性物質に吸着されて
除去される。更にまた昼間になり光が当たると吸着性物
質に吸着された有害物質が放出され光によって分解除去
される。したがって、昼夜にわたって有害物質の除去が
可能となるという優れた浄化性能を有するものである。
更に本発明では、半導体の特性から大気中のNOX の浄
化ばかりでなく、表面の汚れの防止、水の浄化、抗菌・
防カビ、脱臭等を行うことができ、したがって、多目的
に使用しうるばかりでなく個々の性質に絞った用途の製
品とすることもできる。
In the present invention, since the mixture further contains a high-performance water reducing agent, the mixture can be uniformly dispersed. Therefore, the photocatalyst is also present uniformly and contributes to the light absorbing action. be able to. Furthermore, by containing the adsorbing substance in the mixture, harmful substances are decomposed and removed in the daytime and in a state of light, and at night, the harmful substances are adsorbed and removed by the adsorbing substance. . Furthermore, when light strikes in the daytime, the harmful substances adsorbed by the adsorptive substance are released and decomposed and removed by the light. Therefore, it has an excellent purification performance that enables harmful substances to be removed day and night.
Further, in the present invention, not only the purification of the NO X in the air from the characteristics of the semiconductor, prevention of surface dirt, water purification, antibacterial,
It can prevent mold, deodorize, etc., and therefore can be used not only for multiple purposes but also for specific purposes.

【0009】[0009]

【発明の実施の形態】以下に、本発明の実施の形態を挙
げるが、本発明は、これに限定されるものではない。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Embodiments of the present invention will be described below, but the present invention is not limited thereto.

【0010】本発明の有害物質除去部材は、水硬性化合
物と光触媒とからなる混合物に、骨材、消石灰、高性能
減水剤又は吸着性物質の少なくとも1種を加えて混練し
た後、これを使用して製造した種々の水和凝集物であ
る。ここにその実施形態を挙げると、本発明の有害物質
除去部材は、水硬性化合物、骨材、光触媒及び水からな
る混合物から得られた水和凝集物であるが、本発明に用
いられる水硬性化合物は、水と反応して水和物を生成
し、かつ凝集する性質を有する無機化合物であり、特に
限定されるものではない。この水硬性化合物の具体例
は、セメント類、例えば、普通ポルトランドセメント、
早強ポルトランドセメント、中庸熱ポルトランドセメン
ト、超早強ポルトランドセメント、耐硫酸塩ポルトラン
ドセメント、白色ポルトランドセメント、高炉セメン
ト、フライアッシュセメント、シリカセメント、アルミ
ナセメント、超速硬セメント等が挙げられる。この他、
硫酸カルシウム、珪酸カルシウム、アルミン酸カルシウ
ム、鉄酸カルシウム、セリット、シーライト、ゲーレナ
イト、灰長石、ドロマイト等が挙げられる。好ましく
は、前記セメント類、特に白色ポルトランドセメントを
はじめ、硫酸カルシウム、焼き石膏である。
The harmful substance removing member of the present invention is used after adding at least one kind of aggregate, slaked lime, high-performance water reducing agent or adsorbent substance to a mixture comprising a hydraulic compound and a photocatalyst, and kneading the mixture. Various hydrated aggregates produced by the above method. According to the embodiment, the harmful substance removing member of the present invention is a hydrated aggregate obtained from a mixture of a hydraulic compound, an aggregate, a photocatalyst, and water. The compound is an inorganic compound having a property of forming a hydrate by reacting with water and aggregating, and is not particularly limited. Specific examples of the hydraulic compound include cements, for example, ordinary Portland cement,
Examples include early-strength Portland cement, moderately heated Portland cement, ultra-high-strength Portland cement, sulfate-resistant Portland cement, white Portland cement, blast furnace cement, fly ash cement, silica cement, alumina cement, and ultra-rapid hardening cement. In addition,
Calcium sulfate, calcium silicate, calcium aluminate, calcium ferrate, celite, celite, gehlenite, anorthite, dolomite and the like. Preferably, the cements, especially white Portland cement, calcium sulfate and calcined gypsum are used.

【0011】本発明に用いられる光触媒は、一種の半導
体物質であり、具体的には、二酸化すず、酸化亜鉛、三
酸化タングステン、酸化セリウム、二酸化チタン、チタ
ン酸バリウム、酸化第二鉄等の金属酸化物;硫化亜鉛、
硫化カドミウム、硫化鉛、セレン化亜鉛、セレン化カド
ミウム等の金属カルコゲナイト;シリコン、ゲルマニウ
ム等の第IV族金属;ガリウムリン、ガリウム砒素、イ
ンジウムリン等の第III族元素と第V族元素との化合
物;ポリアセチレン、ポリピロール、ポリチオフェン、
ポリアニリン、ポリビニルカルバゾール等の有機半導体
が挙げられる。これらのうち、更に好ましいものは、二
酸化チタン、酸化亜鉛、酸化セレニウム、三酸化タング
ステン、ポリビニルカルバゾール等の半導体である。ま
た半導体に亜鉛、鉄、バナジウム等の金属又は金、白金
等の貴金属を共に用いることにより有害物質除去性能を
向上させることができる。本発明に用いられる半導体
は、粉末で用いられ、該半導体粉末を水硬性化合物に混
合して分散する。
The photocatalyst used in the present invention is a kind of semiconductor substance, and specifically, a metal such as tin dioxide, zinc oxide, tungsten trioxide, cerium oxide, titanium dioxide, barium titanate, and ferric oxide. Oxides: zinc sulfide,
Metal chalcogenites such as cadmium sulfide, lead sulfide, zinc selenide, and cadmium selenide; Group IV metals such as silicon and germanium; and compounds of Group III elements and Group V elements such as gallium phosphide, gallium arsenide, and indium phosphide Polyacetylene, polypyrrole, polythiophene,
Organic semiconductors such as polyaniline and polyvinyl carbazole are exemplified. Of these, semiconductors such as titanium dioxide, zinc oxide, selenium oxide, tungsten trioxide, and polyvinyl carbazole are more preferable. In addition, by using a metal such as zinc, iron and vanadium or a noble metal such as gold and platinum together with the semiconductor, the performance of removing harmful substances can be improved. The semiconductor used in the present invention is used as a powder, and the semiconductor powder is mixed and dispersed in a hydraulic compound.

【0012】本発明に用いられる半導体物質は、水硬性
化合物100重量部に対して5重量部〜800重量部で
あり、好ましくは水硬性化合物100重量部に対して1
0重量部〜600重量部であり、更に好ましくは水硬性
化合物100重量部に対して10重量部〜300重量部
である。これは骨材を配合することにより浄化性能を向
上させることができるので、骨材を含まないものに比べ
て相対的に少なくて済むという優れた効果を奏するもの
である。
The semiconductor substance used in the present invention is used in an amount of 5 to 800 parts by weight, preferably 1 to 100 parts by weight of the hydraulic compound.
The amount is 0 to 600 parts by weight, and more preferably 10 to 300 parts by weight based on 100 parts by weight of the hydraulic compound. This is an excellent effect that the purification performance can be improved by blending the aggregate, so that the amount can be relatively reduced as compared with the one containing no aggregate.

【0013】また本発明において、混合物に更に消石灰
を加えてもよく、この消石灰を加えることにより、排水
の酸性化を防ぐことができる。特に水硬性化合物の水和
凝集物がセメントの場合、セメントは経時において中性
化によってアルカリ性を失って劣化されるが、消石灰に
よりアルカリ性が保たれるばかりでなく、NOX の如き
有害物質が光触媒で酸性物質に変化するときは、これを
中和して無害化することができる。また本発明において
は、前記混合物に強塩基と弱酸の水溶性塩が含有されて
おり、この水溶性塩としては、炭酸ナトリウム、炭酸水
素ナトリウム、酢酸ナトリウム、次亜塩素酸ナトリウ
ム、さらし粉等が挙げられる。これらは強塩基と弱酸の
水溶性塩であるので、pHの緩衝作用を有している。
In the present invention, slaked lime may be further added to the mixture, and by adding the slaked lime, acidification of wastewater can be prevented. Particularly when the hydrated agglomerates hydraulic compound is a cement, but the cement is degraded loses alkaline by neutralization in time, not only alkalinity is maintained by slaked lime, such as of the NO X toxic substances photocatalyst When it is changed to an acidic substance by the above, it can be neutralized and made harmless. In the present invention, the mixture contains a water-soluble salt of a strong base and a weak acid. Examples of the water-soluble salt include sodium carbonate, sodium hydrogen carbonate, sodium acetate, sodium hypochlorite, bleached powder, and the like. Can be Since these are water-soluble salts of a strong base and a weak acid, they have a pH buffering action.

【0014】更に本発明においては、骨材が用いられ、
この骨材としては、砂、砕石、珪砂、ガラス等が挙げら
れる。この骨材の大きさは、通常、砂の大きさが好まし
いが、これに限定されることなく、粒径が0.1mm〜
10mmの範囲の粒度でよい。また本発明では、混合物
に更に高性能減水剤が加えるのがよく、この高性能減水
剤としては、ナフタレンスルホン酸ホルムアルデヒド高
縮合物のナトリウム塩、クレオソート油スルホン酸縮合
物のナトリウム塩等が挙げられる。高性能減水剤を加え
ることにより混合物を均一に分散することができ、その
結果光触媒に均一に光が当たり浄化性能を向上させるこ
とができる。
Further, in the present invention, an aggregate is used,
Examples of the aggregate include sand, crushed stone, silica sand, and glass. Usually, the size of the aggregate is preferably the size of sand, but is not limited thereto, and the particle size is 0.1 mm to
A particle size in the range of 10 mm may be sufficient. In the present invention, a high-performance water reducing agent is preferably added to the mixture. Examples of the high-performance water reducing agent include a sodium salt of a naphthalenesulfonic acid formaldehyde polycondensate, a sodium salt of a creosote oil sulfonic acid condensate, and the like. Can be By adding the high-performance water reducing agent, the mixture can be uniformly dispersed, and as a result, the photocatalyst can be uniformly illuminated with light and the purification performance can be improved.

【0015】本発明において、混合物には、更に吸着性
物質を加えることができ、具体的には、活性炭、シリカ
ゲル、ゼオライト、マガディアイト、ペタライト等が挙
げられる。マガディアイトは、Na2 Si1429nH2
Oの化学式を有し、吸着性物質として有効である。更に
ペタライトは外観が石英に似て白色や灰色の鉱物で、鉱
物学的には長石族に属する珪酸塩鉱物(Li2 OAl2
3 8SiO2 )である。吸着性能に優れている。これ
らの吸着性物質は、いずれも吸着性能に優れており、有
害物質を吸収することにより除去することができる。こ
の吸着性物質の作用を更に詳しく説明すると、日中の太
陽光(これに含有される紫外線)によりNOx 等の有害
物質が浄化除去されるばかりでなく夜間でも該吸着材料
に有害物質が吸着され、これが日中、紫外線により分解
されることにより、有害物質の浄化が行われる。これら
の吸着性物質のうち、好ましくは活性炭がよい。
In the present invention, an adsorbing substance can be further added to the mixture, and specific examples include activated carbon, silica gel, zeolite, magadiite, petalite and the like. Magadiite is Na 2 Si 14 O 29 nH 2
It has the chemical formula of O and is effective as an adsorptive substance. Further, petalite is a white or gray mineral similar in appearance to quartz, and is a silicate mineral (Li 2 OAl 2
O 3 8SiO 2 ). Excellent adsorption performance. All of these adsorbing substances have excellent adsorption performance and can be removed by absorbing harmful substances. The action of the adsorbent substance will be described in more detail. Not only is the harmful substance such as NO x not only purified and removed by daylight (ultraviolet rays contained therein) but also at night, This is decomposed by ultraviolet light during the day to purify harmful substances. Activated carbon is preferred among these adsorptive substances.

【0016】本発明において、有害物質除去部材は、水
硬性化合物、骨材、光触媒及び水の混合物を均一に混練
して製造するが、これらの各成分の添加順序は特に限定
されるものではない。好ましくは骨材、水の一部、水硬
性化合物、光触媒及び水の残部の順に添加混合するのが
よい。混合物の混練後、適宜の形態で使用するものであ
り、その形態の一つ目は、前記混練物の水和凝集物を粉
砕して、粒状体として使用することである。この粒状体
は、装置として用いる場合には、このまま透明容器に入
れ、光を照射しながら、この容器中へ汚染媒体を通すこ
とにより汚染媒体の浄化に使用することができる。また
その形態の二つ目は、前記混練物を成形手段を用いて各
種の形状に成形する方法である。この方法により板状体
を形成することにより光を照射しながら、空気の浄化、
水の浄化をすることができる。更に、抗菌・防カビ、防
汚染等の用途に使用することができる。また光触媒の量
を多くすることにより光が当たらなくても抗菌・防カ
ビ、防汚染等の用途に使用することができる。更に混練
物は、板状体の表面に適用することも可能であり、これ
により光触媒のコストダウンを図ることができ、いっそ
う経済的である。
In the present invention, the harmful substance removing member is produced by uniformly kneading a mixture of a hydraulic compound, an aggregate, a photocatalyst and water, but the order of adding these components is not particularly limited. . Preferably, the aggregate, a part of the water, the hydraulic compound, the photocatalyst and the remainder of the water are added and mixed in this order. After kneading the mixture, the mixture is used in an appropriate form. The first form is that the hydrated aggregate of the kneaded product is pulverized and used as granules. When used as an apparatus, this granular material can be used for purification of a contaminated medium by putting it in a transparent container as it is and passing the contaminated medium through the container while irradiating light. A second form of the method is a method of molding the kneaded material into various shapes using a molding means. By irradiating light by forming a plate-shaped body by this method, air purification,
Water can be purified. Furthermore, it can be used for applications such as antibacterial, antifungal and antifouling. In addition, by increasing the amount of the photocatalyst, it can be used for applications such as antibacterial, antifungal, and antifouling even if it is not exposed to light. Further, the kneaded material can be applied to the surface of the plate-like body, whereby the cost of the photocatalyst can be reduced, and it is more economical.

【0017】本発明の有害物質除去部材の各成分の重量
割合は、通常の水硬性化合物の水和凝集物の形成の時の
重量割合でよいが、好ましくは水硬性化合物100重量
部に対して、骨材50重量部〜500重量部、光触媒5
重量部〜200重量部及び水10重量部〜300重量部
である。更に好ましくは水硬性化合物100重量部に対
して、骨材100重量部〜300重量部、光触媒10重
量部〜100重量部及び水20重量部〜150重量部で
ある。これらの範囲を越えると、実質的に有害物質除去
性能がないばかりかコスト的に好ましくない。本発明の
有害物質除去部材において、消石灰の量は、水硬性化合
物100重量部に対して1重量〜50重量であり、好ま
しくは水硬性化合物100重量部に対して5重量〜30
重量であある。消石灰の量は、水硬性化合物100重量
部に対して1重量未満のときは、有害物質の浄化性能の
向上に寄与しない。また消石灰の量が、50重量を越え
ると、かえって光触媒の量が相対的に減り浄化性能が落
ちるので好ましくない。
The weight ratio of each component of the harmful substance removing member of the present invention may be a weight ratio at the time of forming a hydrated aggregate of a normal hydraulic compound, but is preferably 100 parts by weight of the hydraulic compound. , 50 to 500 parts by weight of aggregate, photocatalyst 5
Parts by weight to 200 parts by weight and water 10 parts by weight to 300 parts by weight. More preferably, the amount is 100 parts by weight to 300 parts by weight of the aggregate, 10 parts by weight to 100 parts by weight of the photocatalyst, and 20 parts by weight to 150 parts by weight of water with respect to 100 parts by weight of the hydraulic compound. If the ratio exceeds these ranges, not only is there substantially no harmful substance removal performance, but it is not preferable in terms of cost. In the harmful substance removing member of the present invention, the amount of slaked lime is 1 to 50 parts by weight based on 100 parts by weight of the hydraulic compound, and preferably 5 to 30 parts by weight based on 100 parts by weight of the hydraulic compound.
Weight. When the amount of slaked lime is less than 1 part by weight with respect to 100 parts by weight of the hydraulic compound, it does not contribute to improvement in the purification performance of harmful substances. On the other hand, if the amount of slaked lime exceeds 50 weight, the amount of photocatalyst is relatively reduced and purification performance is lowered, which is not preferable.

【0018】本発明において、前記の強塩基と弱酸の水
溶性塩の添加量は、水硬性化合物100重量部に対して
0.5重量〜30重量であり、好ましくは水硬性化合物
100重量部に対して1重量〜10重量であある。この
水溶性塩の量は、水硬性化合物100重量部に対して
0.5重量未満のときは、有害物質の浄化性能の向上に
寄与しない。また水溶性塩の量が、30重量を越える
と、セメントの硬化反応である水和反応に悪影響を及ぼ
し、硬化体強度が得られないばかりか光触媒の量が相対
的に減り浄化性能が落ちるので好ましくない。
In the present invention, the amount of the water-soluble salt of the strong base and the weak acid is 0.5 to 30 parts by weight, preferably 100 parts by weight of the hydraulic compound. The weight is 1 to 10% by weight. When the amount of the water-soluble salt is less than 0.5 part by weight with respect to 100 parts by weight of the hydraulic compound, it does not contribute to the improvement of harmful substance purification performance. Further, if the amount of the water-soluble salt exceeds 30 weight, it adversely affects the hydration reaction, which is a curing reaction of cement, and not only does not obtain a cured body strength, but also the amount of photocatalyst is relatively reduced and purification performance is lowered. Not preferred.

【0019】本発明の有害物質除去部材において、高性
能減水剤の量は、セメントの技術分野で通常用いられる
量でよく、水硬性化合物100重量部に対して0.1重
量〜10重量であり、好ましくは水硬性化合物100重
量部に対して0.5重量〜5.0重量であある。高性能
減水剤の量は、水硬性化合物100重量部に対して0.
1重量未満のときは、混合物の均一分散することができ
ない。また高性能減水剤の量が、10重量を越えると、
コストアップを招き好ましくない。更に本発明の有害物
質除去部材において、吸着性物質の量は、その種類にも
よるが、水硬性化合物100重量部に対して5重量部〜
50重量部であり、好ましくは水硬性化合物100重量
部に対して10重量部〜30重量部であある。吸着性物
質の量は、水硬性化合物100重量部に対して5重量部
未満のときは、有害物質の吸着が十分行えないので、浄
化性能を向上させることができない。また吸着性物質の
量が、50重量部を越えると、かえって光触媒の量が相
対的に減り浄化性能が落ちるので好ましくない。
In the harmful substance removing member of the present invention, the amount of the high-performance water reducing agent may be an amount generally used in the technical field of cement, and is 0.1 to 10 parts by weight based on 100 parts by weight of the hydraulic compound. And preferably 0.5 to 5.0 parts by weight based on 100 parts by weight of the hydraulic compound. The amount of the high-performance water reducing agent is set to be 0.1 to 100 parts by weight of the hydraulic compound.
If it is less than 1 weight, the mixture cannot be uniformly dispersed. When the amount of the high performance water reducing agent exceeds 10 weight,
It is not preferable because the cost is increased. Further, in the harmful substance removing member of the present invention, the amount of the adsorptive substance is from 5 parts by weight to 100 parts by weight of the hydraulic compound, depending on the type.
The amount is 50 parts by weight, preferably 10 parts by weight to 30 parts by weight based on 100 parts by weight of the hydraulic compound. When the amount of the adsorptive substance is less than 5 parts by weight with respect to 100 parts by weight of the hydraulic compound, the harmful substance cannot be sufficiently adsorbed, so that the purification performance cannot be improved. On the other hand, if the amount of the adsorbing substance exceeds 50 parts by weight, the amount of the photocatalyst is relatively reduced and the purification performance is lowered, which is not preferable.

【0020】本発明の有害物質除去部材の使用に際し、
照射される光は、紫外線を含む光がよく、その光の波長
範囲は、200nm〜400nmが好ましい。特に紫外
線が好ましいが、戸外で使用するときは、太陽光で十分
である。また室内での使用は、超高圧水銀灯、キセノン
ランプ、低圧水銀灯灯からでる紫外線を有害物質除去部
材に照射する。この際、有害物質除去部材にできるだけ
近づけて用いることが好ましい。この有害物質除去部材
で除去可能な有害物質は、NOX 、メルカプタン類、ア
ンモニア、硫化水素、アミン類、エチレン等が好ましく
除去される。本発明において、有害物質除去部材の使用
量は、有害物質の種類、光照度等を考慮して決めること
ができる。しかしながら、本発明では、有害物質除去部
材の除去乃至浄化性能が高いので、その使用量は少なく
てよい。
In using the harmful substance removing member of the present invention,
The light to be irradiated is preferably light containing ultraviolet light, and the wavelength range of the light is preferably 200 nm to 400 nm. Ultraviolet rays are particularly preferred, but when used outdoors, sunlight is sufficient. For indoor use, ultraviolet rays from an ultra-high pressure mercury lamp, a xenon lamp, or a low pressure mercury lamp are irradiated to the harmful substance removing member. At this time, it is preferable to use the harmful substance removing member as close as possible. The hazardous substance removing member in a removable harmful substances, NO X, mercaptans, ammonia, hydrogen sulfide, amines, ethylene and the like are preferably removed. In the present invention, the usage amount of the harmful substance removing member can be determined in consideration of the type of harmful substance, light illuminance, and the like. However, in the present invention, since the removal or purification performance of the harmful substance removing member is high, the use amount thereof may be small.

【0021】[0021]

【実施例】以下に本発明を実施例を挙げて更に詳しく説
明するが、本発明はこの例にのみ限定されるものではな
い。
The present invention will be described below in more detail with reference to examples, but the present invention is not limited to these examples.

【0022】〔実施例1〕白色セメント100重量部、
砂220重量部、二酸化チタン粉末25重量部及び水3
0重量部を混練した後、10×20cmの型枠に該混練
物を入れ振動成形して成形体を成形した。この試験体は
養生後、粉砕して粒径1〜10mmの有害物質除去部材
とした。ついで、この有害物質除去部材を入り口と出口
のある透明容器に入れ、下記の試験方法でNO除去率の
測定を行った。比較例としては、白色セメント100重
量部及び二酸化チタン粉末25重量部を水で混練したも
のを同様にして成形、養生、粉砕して、有害物質除去部
材を製造した。比較例の有害物質除去部材を使用したと
きは、NO除去率は、65%であるのに対して、本発明
の有害物質除去部材の場合は、NO除去率は、73%で
あり、浄化性能の向上がみられた。
Example 1 100 parts by weight of white cement,
220 parts by weight of sand, 25 parts by weight of titanium dioxide powder and water 3
After kneading 0 parts by weight, the kneaded material was put in a mold frame of 10 × 20 cm and subjected to vibration molding to form a molded body. After curing, the specimen was pulverized to obtain a harmful substance removing member having a particle size of 1 to 10 mm. Next, this harmful substance removing member was placed in a transparent container having an entrance and an exit, and the NO removal rate was measured by the following test method. As a comparative example, a mixture obtained by kneading 100 parts by weight of white cement and 25 parts by weight of titanium dioxide powder with water was molded, cured, and pulverized in the same manner to produce a harmful substance removing member. When the harmful substance removing member of the comparative example was used, the NO removal rate was 65%, whereas in the case of the harmful substance removing member of the present invention, the NO removal rate was 73%, and the purification performance was high. Improvement was seen.

【0023】〔NO除去試験方法1〕試験は試験体を密
閉容器に入れ、入口から1ppmのNOガスを含む模擬
ガスを流した。出口からでるガスの濃度を測定し、これ
からNOの除去率を測定した。試験は24時間行い、1
0分毎の除去率を平均した数値を試験結果とした。な
お、試験方法1では、10W×3本の紫外線ランプを2
4時間点灯したままで試験を行った。
[NO Removal Test Method 1] In the test, a test sample was placed in a closed container, and a simulation gas containing 1 ppm of NO gas was flowed from the inlet. The concentration of the gas leaving the outlet was measured, from which the NO removal rate was measured. The test was conducted for 24 hours, 1
The numerical value obtained by averaging the removal rates every 0 minutes was used as the test result. In test method 1, 10 W × 3 ultraviolet lamps were
The test was performed with the lights on for 4 hours.

【0024】〔実施例2〕実施例1と同じ有害物質除去
部材を製造した。NO除去試験方法1において、NOガ
スにかえ、エチレンを用いた以外,同様にしてこの有害
物質除去部材の性能を調べた。砂の有無により本発明の
有害物質除去部材は、比較例の有害物質除去部材を使用
したときは、エチレンの除去率は、55%であるのに対
して、本発明の有害物質除去部材の場合は、エチレンの
除去率は、64%であり、エチレンの除去率の向上した
ものが得られた。なお、エチレンの出口の濃度は、ガス
クロマトグラフィーで測定された。エチレンの除去率の
向上したものが得られた。更に本発明では、この有害物
質除去部材に更に吸着性物質として、活性炭、ゼオライ
ト、マガディアイト、ペタライトのいずれかを加えるこ
とにより夜間に有害物質を吸収し、昼間それらを放出し
て分解するので、いっそうの有害物質除去性能を向上さ
せることができる。
Example 2 The same harmful substance removing member as in Example 1 was manufactured. In the NO removal test method 1, the performance of the harmful substance removing member was examined in the same manner except that ethylene was used instead of NO gas. According to the harmful substance removing member of the present invention, the use of the harmful substance removing member of the comparative example resulted in an ethylene removal rate of 55%, whereas the harmful substance removing member of the present invention did not. In Example 1, the ethylene removal rate was 64%, and a product having an improved ethylene removal rate was obtained. The concentration at the outlet of ethylene was measured by gas chromatography. A product having an improved ethylene removal rate was obtained. Furthermore, in the present invention, the harmful substance removing member further absorbs harmful substances at night by adding any of activated carbon, zeolite, magadiite, and petalite as an adsorptive substance, and releases and decomposes them during the day. Further harmful substance removal performance can be improved.

【0025】〔実施例3〕焼石膏100重量部、砂22
0重量部、二酸化チタン粉末50重量部及び水30重量
部を混練した後、実施例1と同様にして有害物質除去部
材を製造した。砂の有無により本発明の有害物質除去部
材は、NO除去率の向上したものが得られた。
Example 3 100 parts by weight of calcined gypsum, sand 22
After kneading 0 parts by weight, 50 parts by weight of titanium dioxide powder and 30 parts by weight of water, a harmful substance removing member was manufactured in the same manner as in Example 1. Depending on the presence or absence of sand, the harmful substance removing member of the present invention was obtained with an improved NO removal rate.

【0026】〔実施例4〕ブロック基層の配合としてポ
ルトランドセメント100重量部、砕石195重量部、
砂240重量部及び水31を混練した後、10×20c
mの型枠に該混練物を入れ振動成形してコンクリート基
層を成形した。この上に表面として、白色セメント10
0重量部、砂220重量部及び二酸化チタン粉末25重
量部を水30重量部で混練したものを流し込み成形し
た。得られた成形体は養生した。また比較例としては、
前記の成形体の製造において、砂を除いた混練物を同様
にして成形、養生して有害物質除去部材を製造した。こ
れらの成形体をそれぞれ密閉容器に入れ、実施例1と同
様にしてNO除去率の測定を行った。比較例の有害物質
除去部材を使用したときは、NO除去率は、60%であ
るのに対して、本発明の有害物質除去部材の場合は、N
O除去率は、72%であり、浄化性能の向上がみられ
た。白色セメントの代わりにポルトランドセメントを用
いてもNOX の浄化性能の向上がみられた。
Example 4 The composition of the block base layer was 100 parts by weight of Portland cement, 195 parts by weight of crushed stone,
After kneading 240 parts by weight of sand and water 31, 10 × 20c
The kneaded product was placed in a m mold frame and subjected to vibration molding to form a concrete base layer. On this surface, white cement 10
A mixture obtained by kneading 0 parts by weight, 220 parts by weight of sand and 25 parts by weight of titanium dioxide powder with 30 parts by weight of water was poured and molded. The obtained molded body was cured. As a comparative example,
In the production of the above-mentioned molded product, the kneaded material from which sand was removed was molded and cured in the same manner to produce a harmful substance removing member. Each of these compacts was placed in a closed container, and the NO removal rate was measured in the same manner as in Example 1. When the harmful substance removing member of the comparative example was used, the NO removal rate was 60%, whereas in the case of the harmful substance removing member of the present invention, the NO removal rate was 60%.
The O removal rate was 72%, and the purification performance was improved. Improvement of purification performance even NO X using Portland cement instead of the white cement was observed.

【0027】〔実施例5〕実施例4に記載の表面層の混
練物として、白色セメント100重量部、砂220重量
部、二酸化チタン粉末25重量部及び消石灰30重量部
を水30重量部で混練したものを流し込み成形した。得
られた成形体は養生した。また比較例としては、前記の
成形体の製造において、砂を除いた混練物を同様にして
成形、養生して有害物質除去部材を製造した。これらの
成形体をそれぞれ密閉容器に入れ、実施例1と同様にし
てNO除去率の測定を行った。この際、成形体に上から
雨のように水をふりかけた。比較例の有害物質除去部材
を使用したときは、NO除去率は、60%であるのに対
して、本発明の有害物質除去部材の場合は、NO除去率
は、74%であり、浄化性能の向上がみられると共に、
更に比較例では酸性の水が得られたのに対して本発明で
は、中性乃至弱アルカリ性の水が得られ、自然環境保護
の観点からも好ましいものであった。
Example 5 As the kneaded material of the surface layer described in Example 4, 100 parts by weight of white cement, 220 parts by weight of sand, 25 parts by weight of titanium dioxide powder and 30 parts by weight of slaked lime were kneaded with 30 parts by weight of water. This was cast and molded. The obtained molded body was cured. As a comparative example, in the production of the above-mentioned molded body, the kneaded material from which sand was removed was similarly molded and cured to produce a harmful substance removing member. Each of these compacts was placed in a closed container, and the NO removal rate was measured in the same manner as in Example 1. At this time, water was sprinkled from above on the molded body like rain. When the harmful substance removing member of the comparative example was used, the NO removal rate was 60%, whereas in the case of the harmful substance removing member of the present invention, the NO removal rate was 74%, and the purification performance was high. Has been improved,
Further, in the comparative example, acidic water was obtained, whereas in the present invention, neutral to weakly alkaline water was obtained, which was preferable from the viewpoint of protecting the natural environment.

【0028】〔実施例6〕実施例4に記載の表面層の混
練物に、更に高性能減水剤0.6重量部を添加した以外
は、実施例4と同様にして本発明の成形体かなる有害物
質除去部材を製造し、実施例4と同様にNO除去率の測
定を行った。得られた成形体は均一に分散され、その結
果、NOの除去率が向上した。
Example 6 A molded article of the present invention was prepared in the same manner as in Example 4 except that 0.6 parts by weight of a high-performance water reducing agent was further added to the kneaded product of the surface layer described in Example 4. A harmful substance removing member was manufactured, and the NO removal rate was measured in the same manner as in Example 4. The obtained compact was uniformly dispersed, and as a result, the NO removal rate was improved.

【0029】〔実施例7〕実施例4に記載の表面層の混
練物に、更に吸着性物質として活性炭25重量部を混合
した以外は、実施例4と同様にして本発明の成形体かな
る有害物質除去部材を製造した。NO除去率の測定は、
以下のNO除去試験方法2で行った。比較例では活性炭
を加えないもので比較したところ、NO除去率は、比較
例に比べて30%〜60%の向上が見られた。なお、吸
着性物質として、ゼオライト、マガディアイト、ペタラ
イトを用いても同様に浄化性能に優れたものが得られ
た。
Example 7 A molded article of the present invention is obtained in the same manner as in Example 4, except that 25 parts by weight of activated carbon as an adsorbent is further added to the kneaded material of the surface layer described in Example 4. A harmful substance removing member was manufactured. The measurement of NO removal rate
The following NO removal test method 2 was used. In the comparative example, comparison was made with no added activated carbon. As a result, the NO removal rate was improved by 30% to 60% as compared with the comparative example. Even when zeolite, magadiite, and petalite were used as the adsorptive substance, a substance having excellent purification performance was similarly obtained.

【0030】〔NO除去性能試験方法2〕NO除去性能
試験方法1を行う場合において、紫外線ランプを2時間
毎に点灯、消灯を繰り返した。したがって24時間の試
験時間中、ランプが点灯していたのは12時間であっ
た。
[NO removal performance test method 2] When performing NO removal performance test method 1, the ultraviolet lamp was repeatedly turned on and off every two hours. Thus, during the 24 hour test period, the lamp was on for 12 hours.

【0031】〔実施例8〕実施例5に記載の表面層の混
練物に、更に吸着性物質として活性炭25重量部を混合
した以外は、実施例5と同様にして本発明の成形体かな
る有害物質除去部材を製造した。NO除去率の測定は、
以下のNO除去試験方法2で行った。比較例では活性炭
を加えないもので比較したところ、NO除去率は、比較
例に比べて30%〜60%の向上が見られた。更に消石
灰が添加されているので、中性乃至弱アルカリ性の水が
得られ、自然環境保護の観点からも好ましいものであっ
た。
Example 8 A molded article of the present invention is obtained in the same manner as in Example 5, except that 25 parts by weight of activated carbon is further mixed as an adsorbent with the kneaded material of the surface layer described in Example 5. A harmful substance removing member was manufactured. The measurement of NO removal rate
The following NO removal test method 2 was used. In the comparative example, comparison was made with no added activated carbon. As a result, the NO removal rate was improved by 30% to 60% as compared with the comparative example. Furthermore, since slaked lime is added, neutral or weakly alkaline water is obtained, which is preferable from the viewpoint of protecting the natural environment.

【0032】〔実施例9〕実施例1と同じ有害物質除去
部材を製造した。NO除去試験方法1において、NOガ
スにかえ、メチルメルカプタンを用いた以外,同様にし
てこの有害物質除去部材の性能を調べた。砂の有無によ
り本発明の有害物質除去部材は、比較例の有害物質除去
部材を使用したときは、メチルメルカプタンの除去率
は、40%であるのに対して、本発明の有害物質除去部
材の場合は、メチルメルカプタンの除去率は、55%で
あり、悪臭の除去率の向上したものが得られた。なお、
硫化水素、アンモニアについても本発明の有害物質除去
部材を用いて同様に試験したところ、十分な悪臭の除去
ができた。
Example 9 The same harmful substance removing member as in Example 1 was manufactured. In the NO removal test method 1, the performance of this harmful substance removing member was examined in the same manner except that methyl mercaptan was used instead of NO gas. When the harmful substance removing member of the present invention is used according to the presence or absence of sand, the removal ratio of methyl mercaptan is 40% when the harmful substance removing member of the comparative example is used, whereas the harmful substance removing member of the present invention has a removal rate of 40%. In this case, the removal rate of methyl mercaptan was 55%, and a product having an improved removal rate of offensive odor was obtained. In addition,
Hydrogen sulfide and ammonia were similarly tested using the harmful substance removing member of the present invention. As a result, sufficient odor could be removed.

【0033】〔実施例10〕実施例4に記載の本発明の
有害物質除去部材及び比較例の有害物質除去部材の二酸
化チタンの量を表1の如くかえて製造し、日光の当たら
ない場所でかつ湿気の多い作業場の外壁材として用い、
6ヵ月後、黴の状態を調査し、表2の結果を得た。黴の
状態を、僅かに付着している場合、僅少;全く付着して
いない場合、良;として評価した。
Example 10 The harmful substance removing member of the present invention described in Example 4 and the harmful substance removing member of the comparative example were produced by changing the amount of titanium dioxide as shown in Table 1, and were produced in a place where no sunlight was exposed. And used as an outer wall material of a humid workplace,
Six months later, the state of the mold was investigated, and the results shown in Table 2 were obtained. The state of the mold was evaluated as slight when it was slightly adhered; good when not adhered at all.

【0034】[0034]

【表1】 [Table 1]

【0035】〔実施例11〕白色セメント100重量
部、砂220重量部、二酸化チタン粉末25重量部、炭
酸ナトリウム3重量部及び水30重量部を混練した後、
10×20cmの型枠に該混練物を入れ振動成形して成
形体を成形した。この試験体は養生後、粉砕して粒径1
〜10mmの有害物質除去部材とした。ついで、この有
害物質除去部材を入り口と出口のある透明容器に入れ、
実施例1に記載のNO除去試験方法1でNO除去率の測
定を行った。実施例1の有害物質除去部材を使用したと
きは、NO除去率は、73%であるのに対して、強塩基
と弱酸の塩を含有する有害物質除去部材の場合は、NO
除去率は、78%であり、浄化性能の向上がみられ、ま
た実施例1のものよりも長期間の持続性を有していた。
なお、NOxばかりでなくエチレン、メルカプタンにつ
いても、同様に試験したところ、優れた分解効率で分解
できることがわかった。
Example 11 100 parts by weight of white cement, 220 parts by weight of sand, 25 parts by weight of titanium dioxide powder, 3 parts by weight of sodium carbonate and 30 parts by weight of water were kneaded.
The kneaded material was placed in a mold frame of 10 × 20 cm and subjected to vibration molding to form a molded body. After curing, the specimen was pulverized to a particle size of 1
A harmful substance removing member of 10 to 10 mm was used. Then, put this harmful substance removing member in a transparent container with an entrance and an exit,
The NO removal rate was measured by the NO removal test method 1 described in Example 1. When the harmful substance removing member of Example 1 was used, the NO removal rate was 73%, whereas in the case of the harmful substance removing member containing a salt of a strong base and a weak acid, NO was removed.
The removal rate was 78%, the purification performance was improved, and the durability was longer than that of Example 1.
In addition, not only NOx but also ethylene and mercaptan were similarly tested, and it was found that they could be decomposed with excellent decomposition efficiency.

【0036】〔実施例12〕セメントクリンカーに二酸
化チタン及び石膏を混合し、粉砕して得た水硬性混合物
(白色セメント4:二酸化チタン粉末1)125重量
部、砂220重量部、炭酸ナトリウム3重量部及び水3
0重量部を混練した以外は、実施例11と同様にして有
害物質除去部材を製造した。この方法で製造した場合に
は、セメントに二酸化チタン粉末を混合する方法よりN
Ox浄化機能が優れていた。
EXAMPLE 12 125 parts by weight of a hydraulic mixture (white cement 4: titanium dioxide powder 1) obtained by mixing titanium dioxide and gypsum in a cement clinker, 220 parts by weight of sand, and 3 parts by weight of sodium carbonate Part and water 3
A harmful substance removing member was manufactured in the same manner as in Example 11 except that 0 parts by weight was kneaded. In the case of manufacturing by this method, the method of mixing the titanium dioxide powder with the cement has a higher N content.
The Ox purification function was excellent.

【0037】[0037]

【発明の効果】本発明の有害物質除去部材は、水硬性化
合物、骨材、光触媒及び水からなる混合物から得られた
水和凝集物であり、特に骨材を混合したことにより空隙
ができ、光触媒の露出度が増大して光吸収率を向上させ
ることができ、その結果、優れた有害物質の除去性能乃
至浄化性能が得られるものである。また前記有害物質除
去部材に消石灰が含有していることによりpHが向上
し、その結果有害物質中、特にNOX を可溶性塩として
光触媒の系外に排出することにより光触媒の浄化効率を
向上させると共に自然環境の保護に好ましい有害物質除
去部材が得られる。
The harmful substance removing member of the present invention is a hydrated aggregate obtained from a mixture of a hydraulic compound, an aggregate, a photocatalyst and water, and in particular, a void is formed by mixing the aggregate, The degree of exposure of the photocatalyst is increased, so that the light absorptivity can be improved. As a result, excellent harmful substance removal performance or purification performance can be obtained. The improved pH is due to contain the slaked lime to the hazardous substance removing member, as a result harmful substances in, in particular improves the purification efficiency of the photocatalyst by the NO X discharged to the outside of the photocatalyst as a soluble salt A harmful substance removing member suitable for protecting the natural environment can be obtained.

【0038】また本発明において、混合物に強塩基と弱
酸の水溶性塩を含有していることにより、NOxの分解
で生じた硝酸イオンをpHの緩衝作用のある前記水溶性
塩によって中和してNOx浄化機能の低下を防止するこ
とができる。また本発明では、前記混合物に高性能減水
剤を含有していることにより、混合物を均一に分散する
ことができるので、したがって、光触媒も均一に存在し
て光吸収作用に寄与することができる。更にまた前記混
合物に活性炭を含有していることにより、昼間、光が当
たっている状態では、有害物質は分解除去され、更に夜
間では、有害物質は吸着性物質に吸着されて除去され
る。更にまた昼間になり光が当たると吸着性物質に吸着
された有害物質が放出され光によって分解除去される。
したがって、昼夜に渡って有害物質の除去が可能となる
という優れた浄化性能を有するものである。
In the present invention, since the mixture contains a water-soluble salt of a strong base and a weak acid, nitrate ions generated by the decomposition of NOx are neutralized by the water-soluble salt having a pH buffering action. A decrease in the NOx purification function can be prevented. Further, in the present invention, since the mixture contains the high-performance water reducing agent, the mixture can be dispersed uniformly, and therefore, the photocatalyst can be uniformly present and contribute to the light absorbing action. Furthermore, since the mixture contains activated carbon, harmful substances are decomposed and removed in the daytime under light, and at night, the harmful substances are adsorbed and removed by the adsorptive substance. Furthermore, when light strikes in the daytime, the harmful substances adsorbed by the adsorptive substance are released and decomposed and removed by the light.
Therefore, it has an excellent purification performance that enables harmful substances to be removed day and night.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 FI E01C 19/00 (72)発明者 神谷 清志 埼玉県大宮市北袋町一丁目297番地 三菱 マテリアル株式会社セメント研究所内──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 6 Identification code FI E01C 19/00 (72) Inventor Kiyoshi Kamiya 1-297 Kitabukuro-cho, Omiya-shi, Saitama Mitsubishi Materials Corporation Cement Research Institute

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】水硬性化合物、骨材、光触媒及び水からな
る混合物から得られた水和凝集物であることを特徴とす
る有害物質除去部材。
1. A member for removing harmful substances, which is a hydrated aggregate obtained from a mixture comprising a hydraulic compound, an aggregate, a photocatalyst and water.
【請求項2】混合物に消石灰を含有していることを特徴
とする請求項1に記載の有害物質除去部材。
2. The harmful substance removing member according to claim 1, wherein the mixture contains slaked lime.
【請求項3】混合物に強塩基と弱酸の水溶性塩を含有し
ていることを特徴とする請求項1又は請求項2に記載の
有害物質除去部材。
3. The harmful substance removing member according to claim 1, wherein the mixture contains a water-soluble salt of a strong base and a weak acid.
【請求項4】混合物に高性能減水剤を含有していること
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
有害物質除去部材。
4. The harmful substance removing member according to claim 1, wherein the mixture contains a high-performance water reducing agent.
【請求項5】混合物に吸着性物質を含有していることを
特徴とする請求項1乃至請求項4のいずれかに記載の有
害物質除去部材。
5. The harmful substance removing member according to claim 1, wherein the mixture contains an adsorptive substance.
JP9098846A 1997-01-28 1997-04-16 Improved harmful substance-removing member Pending JPH10272355A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9098846A JPH10272355A (en) 1997-01-28 1997-04-16 Improved harmful substance-removing member

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
JP1379197 1997-01-28
JP9-13791 1997-01-28
JP9098846A JPH10272355A (en) 1997-01-28 1997-04-16 Improved harmful substance-removing member

Publications (1)

Publication Number Publication Date
JPH10272355A true JPH10272355A (en) 1998-10-13

Family

ID=26349633

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9098846A Pending JPH10272355A (en) 1997-01-28 1997-04-16 Improved harmful substance-removing member

Country Status (1)

Country Link
JP (1) JPH10272355A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6589912B2 (en) * 1999-07-01 2003-07-08 Hiroshi Kawai Composition for being sprayed on foliage of plant and use of the same
US7300514B2 (en) * 2002-10-03 2007-11-27 Ciments Francais Photocatalytic granular mixture for mortar and concrete and its use
JP2009214029A (en) * 2008-03-11 2009-09-24 Denki Kagaku Kogyo Kk Porous cleaning material and cleaning method using porous filter made with the same
JP2009214027A (en) * 2008-03-11 2009-09-24 Denki Kagaku Kogyo Kk Porous cleaning material and cleaning method using porous filter made with the same
CN115073049A (en) * 2022-05-23 2022-09-20 唐山冀东水泥外加剂有限责任公司 Polycarboxylate superplasticizer and preparation method and use method thereof

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6589912B2 (en) * 1999-07-01 2003-07-08 Hiroshi Kawai Composition for being sprayed on foliage of plant and use of the same
US7300514B2 (en) * 2002-10-03 2007-11-27 Ciments Francais Photocatalytic granular mixture for mortar and concrete and its use
US7556683B2 (en) 2002-10-03 2009-07-07 Ciments Francais Photocatalytic granular mixture for mortar and concrete and its use
JP2009214029A (en) * 2008-03-11 2009-09-24 Denki Kagaku Kogyo Kk Porous cleaning material and cleaning method using porous filter made with the same
JP2009214027A (en) * 2008-03-11 2009-09-24 Denki Kagaku Kogyo Kk Porous cleaning material and cleaning method using porous filter made with the same
CN115073049A (en) * 2022-05-23 2022-09-20 唐山冀东水泥外加剂有限责任公司 Polycarboxylate superplasticizer and preparation method and use method thereof

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