JPH11188269A - Photocatalystic body for decomposing organic material, proliferation preventing method of harmful organism using the same - Google Patents
Photocatalystic body for decomposing organic material, proliferation preventing method of harmful organism using the sameInfo
- Publication number
- JPH11188269A JPH11188269A JP9360975A JP36097597A JPH11188269A JP H11188269 A JPH11188269 A JP H11188269A JP 9360975 A JP9360975 A JP 9360975A JP 36097597 A JP36097597 A JP 36097597A JP H11188269 A JPH11188269 A JP H11188269A
- Authority
- JP
- Japan
- Prior art keywords
- photocatalyst
- water
- water surface
- carrier
- granular
- 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.)
- Withdrawn
Links
- 238000000034 method Methods 0.000 title claims description 16
- 230000035755 proliferation Effects 0.000 title abstract description 5
- 239000011368 organic material Substances 0.000 title abstract 5
- 239000011941 photocatalyst Substances 0.000 claims abstract description 98
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 94
- 238000007667 floating Methods 0.000 claims abstract description 22
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims abstract description 21
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 claims abstract description 19
- 239000000126 substance Substances 0.000 claims description 19
- 241000607479 Yersinia pestis Species 0.000 claims description 16
- 239000010883 coal ash Substances 0.000 claims description 15
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 4
- 239000001506 calcium phosphate Substances 0.000 claims description 4
- 229910000389 calcium phosphate Inorganic materials 0.000 claims description 4
- -1 calcium phosphate compound Chemical class 0.000 claims description 4
- 235000011010 calcium phosphates Nutrition 0.000 claims description 4
- 239000005445 natural material Substances 0.000 claims description 3
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 claims 1
- 229910052814 silicon oxide Inorganic materials 0.000 claims 1
- 230000001699 photocatalysis Effects 0.000 abstract description 10
- XLOMVQKBTHCTTD-UHFFFAOYSA-N Zinc monoxide Chemical compound [Zn]=O XLOMVQKBTHCTTD-UHFFFAOYSA-N 0.000 abstract description 4
- 239000011521 glass Substances 0.000 abstract description 4
- 238000000354 decomposition reaction Methods 0.000 abstract description 3
- 239000000835 fiber Substances 0.000 abstract description 2
- QGLKJKCYBOYXKC-UHFFFAOYSA-N nonaoxidotritungsten Chemical compound O=[W]1(=O)O[W](=O)(=O)O[W](=O)(=O)O1 QGLKJKCYBOYXKC-UHFFFAOYSA-N 0.000 abstract description 2
- 239000000123 paper Substances 0.000 abstract description 2
- 239000011347 resin Substances 0.000 abstract description 2
- 229920005989 resin Polymers 0.000 abstract description 2
- 229910001930 tungsten oxide Inorganic materials 0.000 abstract description 2
- 239000011787 zinc oxide Substances 0.000 abstract description 2
- 230000001747 exhibiting effect Effects 0.000 abstract 1
- 230000003647 oxidation Effects 0.000 abstract 1
- 238000007254 oxidation reaction Methods 0.000 abstract 1
- 230000033116 oxidation-reduction process Effects 0.000 abstract 1
- 238000010586 diagram Methods 0.000 description 7
- 230000001590 oxidative effect Effects 0.000 description 7
- 239000000463 material Substances 0.000 description 6
- 239000013535 sea water Substances 0.000 description 6
- 238000003912 environmental pollution Methods 0.000 description 5
- 230000005484 gravity Effects 0.000 description 5
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 4
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 description 4
- 241000251468 Actinopterygii Species 0.000 description 3
- 239000011324 bead Substances 0.000 description 3
- 239000013078 crystal Substances 0.000 description 3
- 239000007789 gas Substances 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 238000000465 moulding Methods 0.000 description 3
- 239000003921 oil Substances 0.000 description 3
- 239000005416 organic matter Substances 0.000 description 3
- 239000003513 alkali Substances 0.000 description 2
- 229910000147 aluminium phosphate Inorganic materials 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 description 2
- 239000000292 calcium oxide Substances 0.000 description 2
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 2
- 239000001569 carbon dioxide Substances 0.000 description 2
- 229910002092 carbon dioxide Inorganic materials 0.000 description 2
- 239000000969 carrier Substances 0.000 description 2
- 238000012851 eutrophication Methods 0.000 description 2
- 238000007654 immersion Methods 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 238000006864 oxidative decomposition reaction Methods 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 239000008262 pumice Substances 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 238000005507 spraying Methods 0.000 description 2
- 239000010409 thin film Substances 0.000 description 2
- VXUYXOFXAQZZMF-UHFFFAOYSA-N titanium(IV) isopropoxide Chemical compound CC(C)O[Ti](OC(C)C)(OC(C)C)OC(C)C VXUYXOFXAQZZMF-UHFFFAOYSA-N 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- 241000192700 Cyanobacteria Species 0.000 description 1
- 208000012868 Overgrowth Diseases 0.000 description 1
- 241000242583 Scyphozoa Species 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 1
- 239000002956 ash Substances 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000012876 carrier material Substances 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 239000004568 cement Substances 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 239000000470 constituent Substances 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 239000010779 crude oil Substances 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000006477 desulfuration reaction Methods 0.000 description 1
- 230000023556 desulfurization Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000001125 extrusion Methods 0.000 description 1
- 239000010408 film Substances 0.000 description 1
- 235000013312 flour Nutrition 0.000 description 1
- 210000002816 gill Anatomy 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 229910052588 hydroxylapatite Inorganic materials 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 150000002894 organic compounds Chemical class 0.000 description 1
- 239000003960 organic solvent Substances 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 229910001562 pearlite Inorganic materials 0.000 description 1
- XYJRXVWERLGGKC-UHFFFAOYSA-D pentacalcium;hydroxide;triphosphate Chemical compound [OH-].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O XYJRXVWERLGGKC-UHFFFAOYSA-D 0.000 description 1
- 238000007146 photocatalysis Methods 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 238000003825 pressing Methods 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 238000010298 pulverizing process Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 230000029058 respiratory gaseous exchange Effects 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000004065 semiconductor Substances 0.000 description 1
- 235000015170 shellfish Nutrition 0.000 description 1
- 229910052710 silicon Inorganic materials 0.000 description 1
- 239000010703 silicon Substances 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 230000001954 sterilising effect Effects 0.000 description 1
- 238000004659 sterilization and disinfection Methods 0.000 description 1
- VEALVRVVWBQVSL-UHFFFAOYSA-N strontium titanate Chemical compound [Sr+2].[O-][Ti]([O-])=O VEALVRVVWBQVSL-UHFFFAOYSA-N 0.000 description 1
- XJDNKRIXUMDJCW-UHFFFAOYSA-J titanium tetrachloride Chemical compound Cl[Ti](Cl)(Cl)Cl XJDNKRIXUMDJCW-UHFFFAOYSA-J 0.000 description 1
- 238000003911 water pollution Methods 0.000 description 1
- 239000002023 wood Substances 0.000 description 1
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、有機物分解用光触
媒体及び有害生物の増殖防止方法に係り、さらに詳しく
は湖沼や貯水池あるいは海などの水面に浮遊可能な有機
物分解用光触媒体、および湖沼や貯水池あるいは海など
の水面に浮遊可能な光触媒体を用いた有機物分解による
水中の有害生物の増殖防止方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a photocatalyst for decomposing organic substances and a method for preventing the growth of pests, and more particularly to a photocatalyst for decomposing organic substances which can be suspended on a water surface such as a lake, a reservoir or the sea. The present invention relates to a method for preventing the growth of pests in water by decomposing organic substances using a photocatalyst floating on a water surface such as a reservoir or the sea.
【0002】[0002]
【従来の技術】近年において、湖沼や貯水池あるいは海
洋の有機物汚染が大きな問題となっている。特に水が富
栄養化することにより、プランクトンが大量発生して水
産資源に多大の被害をもたらすなど、有害生物による被
害が大きな問題となり、その対策が急がれている。2. Description of the Related Art In recent years, organic matter pollution in lakes, marshes, reservoirs or the ocean has become a major problem. In particular, eutrophication of water causes a great deal of damage to pests, such as the occurrence of large quantities of plankton and enormous damage to marine resources, and countermeasures are urgently needed.
【0003】たとえば湖沼では有害生物であるアオコ
(青粉、水の華とも称されるプランクトン)が多量に発
生して、魚類のエラに詰まり魚類の呼吸を妨げたり、さ
らにはその死骸が水中の酸素を多量に消費して、水中の
酸素を欠乏させて魚介類を死滅させるなど、水産資源に
多大の被害をもたらしている。さらにアオコの多量発生
は湖水の汚濁や悪臭など、多くの環境汚染問題をも引き
起こしている。[0003] For example, in lakes and marshes, a large amount of pests (blue flour, plankton, also called water blossoms), which are pests, are caught in fish gills and hinder the respiration of fish. It consumes a large amount of oxygen and causes deficiency of oxygen in the water to kill fish and shellfish, causing great damage to marine resources. Furthermore, the abundance of blue-green algae has caused many environmental pollution problems such as lake water pollution and odor.
【0004】また海洋においても水の富栄養化によるプ
ランクトンの増殖が多くの問題を生じている。海洋のプ
ランクトンの過度の増殖は、水産資源に多大な被害をも
たしている。特にクラゲなどが大量発生して、発電所の
吸水口に押し寄せることから、電力会社はその対策に苦
慮している。[0004] In the ocean, the proliferation of plankton due to eutrophication of water causes many problems. Excessive overgrowth of marine plankton has caused enormous damage to marine resources. In particular, power companies are struggling to take countermeasures because jellyfish and the like are generated in large quantities and rush to the water intake of power plants.
【0005】他方、酸化チタンなどの光触媒は、太陽光
などの光の照射を受けると、光触媒作用によって強い酸
化作用を生じることが知られている。この強い酸化作用
によって、有機物は炭酸ガスと水などに酸化分解される
ので、光触媒作用は有害有機物の分解や殺菌などに応用
されている。[0005] On the other hand, it is known that a photocatalyst such as titanium oxide produces a strong oxidizing action by photocatalytic action when irradiated with light such as sunlight. The organic substance is oxidized and decomposed into carbon dioxide gas and water by the strong oxidizing action, so that the photocatalytic action is applied to the decomposition and sterilization of harmful organic substances.
【0006】即ち、水処理の分野では酸化チタンを水に
懸濁させ、これに光を当てて有機物分解することが行わ
れている。またガラスビーズ上に部分的に酸化チタン薄
膜をつけたものを海面に浮かべて、浮遊する原油の分解
に用いることも試みられている。さらに、この光触媒の
発生する強い酸化作用を、有害となるプランクトンの増
殖防止に応用する試みも公表されている。これは図7に
示すように、筏状の浮遊体12に光触媒1を固定し、こ
れを水面3に浮かべる方法である。That is, in the field of water treatment, titanium oxide is suspended in water and exposed to light to decompose organic substances. Attempts have also been made to use glass beads partially coated with a titanium oxide thin film on the sea surface to decompose floating crude oil. Furthermore, an attempt has been made to apply the strong oxidizing action generated by the photocatalyst to the prevention of harmful plankton proliferation. This is a method in which the photocatalyst 1 is fixed to a raft-shaped floating body 12 and floated on the water surface 3, as shown in FIG.
【0007】ところが、酸化チタンを直接水に懸濁させ
る方法では、沈降したり、水棲生物に吸収されてしまう
などのために、懸濁状態を長期に保つことが困難である
こと、しかも光の届く水面近くに限って浮遊させること
ができない、などの問題があった。またガラスビーズ上
に部分的に酸化チタン薄膜をつけたものは、水との接触
面積が小さい、コスト高である、といった問題点があっ
た。However, in the method of directly suspending titanium oxide in water, it is difficult to maintain the suspended state for a long period of time due to sedimentation or absorption by aquatic organisms. There were problems such as being unable to float only near the surface of water that could reach it. In addition, those in which a titanium oxide thin film is partially applied on glass beads have problems that the contact area with water is small and the cost is high.
【0008】さらに筏状の浮遊体に光触媒を固定して水
面に浮かせたものは、広大な湖沼面を覆うのに大変なコ
ストがかかるという問題があった。即ち、図7のように
筏状浮遊体12を用いるには、紫外光をよく透過する材
料を必要とするので、材料選択の範囲が限られ高コスト
になってしまうこと、水面に浮かばせたり回収したりす
るのに労力を要するなどであった。[0008] In addition, a photocatalyst fixed to a raft-like floating body and floated on the water surface has a problem that it takes a great deal of cost to cover a vast lake surface. That is, as shown in FIG. 7, the use of the raft-shaped floating body 12 requires a material that transmits ultraviolet light well, so that the range of material selection is limited and the cost is high. It took some effort to collect them.
【0009】[0009]
【発明が解決しようとする課題】本発明は光触媒が示
す、有機物に対する強い酸化分解作用を用いて、有機物
を分解し、さらに有害となるプランクトンなどの小生物
の増殖防止を行う場合に、上記従来技術における問題点
を解決して、光触媒を光の照射する水面近くに安定して
浮遊させるとともに、水との接触面積を十分に確保し、
しかも広大な湖沼面において、光触媒体を浮遊させるこ
とによって有機物を分解し、有害となるプランクトンな
どの小生物の増殖防止を低コストで行うことを可能にす
る、有機物分解用の光触媒体、およびこの光触媒体を用
いた有害生物の増殖防止方法を提供することを課題とす
るものである。DISCLOSURE OF THE INVENTION The present invention relates to a method for decomposing an organic substance by using a strong oxidative decomposition action of an organic substance, which is exhibited by a photocatalyst, and for preventing the growth of harmful small organisms such as plankton. Solve the problems in the technology, stably float the photocatalyst near the water surface irradiated with light, ensure sufficient contact area with water,
In addition, a photocatalyst for decomposing organic substances, which enables organic substances to be decomposed by floating the photocatalysts on a vast lake surface to prevent the growth of harmful plankton and other small organisms at low cost, and An object of the present invention is to provide a method for preventing the growth of pests using a photocatalyst.
【0010】[0010]
【課題を解決するための手段】本発明の請求項1に係る
有機物分解用光触媒体は、粒状で多孔質の担体に光触媒
を担持させてなり、水面に浮遊可能であることを特徴と
するものである。また本発明の請求項3に係る水面有害
生物の増殖防止方法は、粒状で多孔質の担体に光触媒を
担持させてなる水面に浮遊可能な光触媒体を水面に散布
して浮遊させることを特徴とするものである。According to a first aspect of the present invention, there is provided a photocatalyst for decomposing an organic substance, wherein a photocatalyst is supported on a granular porous carrier, and is capable of floating on a water surface. It is. Further, the method for preventing the growth of water surface pests according to claim 3 of the present invention is characterized in that a photocatalyst capable of floating on the water surface, which is obtained by supporting a photocatalyst on a granular and porous carrier, is dispersed and floated on the water surface. Is what you do.
【0011】図1は本発明の光触媒体を模式的に示した
図であって、光触媒1を光触媒担体2に担持されてなる
光触媒体4を水面3に浮遊させている。本発明によれ
ば、光触媒が示す強い酸化分解作用を用い、水面近傍の
有機物を分解し、有害となるプランクトンなどの小生物
の増殖防止を行う場合の、上記従来技術における問題点
を解決して、光触媒を光の照射する水面近くに安定して
浮遊させるとともに、水との接触面積を十分に確保し、
しかも広大な湖沼面において有機物を分解し、有害とな
るプランクトンなどの小生物の増殖防止を低コストで行
うことができる。本発明における光触媒としては、光照
射によって酸化還元作用を示す物質であればいずれも使
用でき、例えば酸化チタン、酸化タングステン、酸化亜
鉛、チタン酸ストロンチウムなどの各種の光触媒物質を
用いることが可能である。FIG. 1 is a diagram schematically showing a photocatalyst of the present invention. A photocatalyst 4 having a photocatalyst 1 carried on a photocatalyst carrier 2 is floated on a water surface 3. According to the present invention, by using the strong oxidative decomposition action exhibited by the photocatalyst, decompose organic matter near the water surface, and in the case of preventing the growth of small organisms such as harmful plankton, solving the above-mentioned problems in the prior art. , While stably floating the photocatalyst near the surface of the water to be irradiated with light, and ensuring a sufficient contact area with water,
In addition, organic substances can be decomposed on a vast lake surface to prevent the growth of harmful small organisms such as plankton at low cost. As the photocatalyst in the present invention, any substance can be used as long as it exhibits a redox action by light irradiation. For example, various photocatalytic substances such as titanium oxide, tungsten oxide, zinc oxide and strontium titanate can be used. .
【0012】これらの中で、酸化チタンは光触媒活性の
点で特に優れ、太陽光に対し触媒活性を有するという利
点があり、しかも化学的に安定であること、資源が豊富
で低コストであり、しかも無公害であることなどの特徴
があるため、本発明の光触媒として特に望ましいもので
ある。Among these, titanium oxide is particularly excellent in terms of photocatalytic activity, has the advantage of having catalytic activity against sunlight, is chemically stable, has abundant resources and is inexpensive. Moreover, it is particularly desirable as a photocatalyst of the present invention because it has features such as being non-polluting.
【0013】酸化チタンにはアナターゼ型の結晶構造を
有するものとルチル型の結晶構造を有するものとが存在
し、高い光触媒活性は、酸化アナターゼ型に認められ
る。従って高い光触媒活性を得るには、少なくともアナ
ターゼ型の結晶構造の酸化チタンを含有するものを使用
することが望ましい。Titanium oxide has an anatase-type crystal structure and a rutile-type crystal structure, and high photocatalytic activity is observed in the oxidized anatase type. Therefore, in order to obtain high photocatalytic activity, it is desirable to use a material containing at least titanium oxide having an anatase type crystal structure.
【0014】本発明の粒状で多孔質の光触媒担体は、水
面に散布しても環境汚染を起こさない材料であることが
望ましい。そのような観点から、本発明の粒状で多孔質
の光触媒担体としては、酸化チタンなどの光触媒そのも
のを粒状で多孔質にしたもののほかに、以下に詳述する
石炭灰成型体のほか、ガラス成型体、樹脂、繊維、紙な
どによって構成される、環境汚染のない成型体が好適に
使用できる。The particulate and porous photocatalyst carrier of the present invention is preferably a material which does not cause environmental pollution even when sprayed on the water surface. From such a point of view, as the granular and porous photocatalyst carrier of the present invention, in addition to a granular and porous photocatalyst such as titanium oxide, in addition to a coal ash molded body described in detail below, glass molding A molded article made of a body, resin, fiber, paper, etc. and free from environmental pollution can be suitably used.
【0015】これらの中で石炭灰を含有する多孔質体
は、以下の理由により特に望ましい。即ち、石炭灰はシ
リカとアルミナを主成分として、さらに酸化カルシウム
を含み、その組成は天然の鉱物であるパーライトなどに
近く、化学的には安定であって、光触媒によって酸化さ
れて劣化するようなことがない。[0015] Of these, porous bodies containing coal ash are particularly desirable for the following reasons. In other words, coal ash contains silica and alumina as main components and further contains calcium oxide, and its composition is close to natural minerals such as pearlite, and is chemically stable, and is oxidized and deteriorated by a photocatalyst. Nothing.
【0016】本発明に用いる石炭灰を含有する粒状多孔
質担体として、少なくとも表面にカルシウムの燐酸化合
物を有するものが望ましく使用できる。石炭灰はその成
分として酸化カルシウムを有するので燐酸で処理するこ
とによってカルシウムの燐酸化合物であるヒドロキシア
パタイトなどのカルシウムの燐酸化合物を生成する。こ
のような化合物は生体に対して親和性があるため、この
ような担体を用いることにより、光触媒担体による有害
生物の増殖防止を効果的に行うことができる。石炭灰は
一般廃棄物の焼却灰とは異なって、重金属などの有害な
成分が少ないので、環境汚染の心配がない。また同じ産
炭地、同じ燃焼炉の石炭灰は品質が安定しているため、
成型や光触媒の担持が再現性よく安定して行えるという
特徴がある。As the granular porous carrier containing coal ash used in the present invention, those having a calcium phosphate compound on at least the surface can be desirably used. Since coal ash has calcium oxide as a component thereof, it is treated with phosphoric acid to produce a calcium phosphate compound such as hydroxyapatite which is a calcium phosphate compound. Since such a compound has affinity for a living body, the use of such a carrier can effectively prevent the growth of pests by the photocatalytic carrier. Coal ash, unlike incinerated ash from general waste, has less harmful components such as heavy metals, so there is no concern about environmental pollution. In addition, coal ash from the same coal production area and the same combustion furnace has stable quality,
There is a feature that molding and loading of a photocatalyst can be stably performed with good reproducibility.
【0017】石炭灰を主成分とし、水に浮遊可能な多孔
質体は、例えば金型を用いたプレス成形や押し出し成形
を用いて容易に製造することができる。石炭灰多孔質成
型体は、すでに火力発電所の排ガスの脱硫装置に適用さ
れ、経済性に優れることが実証されている。なお、石炭
灰は年間数百万トン排出され、そのうち約半分はセメン
ト原料などとして有効利用されているが、残りは埋立廃
棄されており、その有効利用が望まれていものである。A porous body containing coal ash as a main component and capable of floating in water can be easily manufactured by, for example, press molding or extrusion molding using a mold. The coal ash porous molded body has already been applied to an exhaust gas desulfurization device of a thermal power plant, and has been proved to be excellent in economic efficiency. Millions of tons of coal ash are discharged annually, and about half of it is effectively used as a raw material for cement, but the rest is disposed of in landfills, and it is desired to use it effectively.
【0018】本発明の粒状で多孔質光触媒は、光触媒体
を担持させて水中に投入した場合に、水面に浮遊可能な
ものが用いられる。浮遊が可能であるためには、湖水ま
たは海水に比べて実効的な比重が小さいことが必要であ
る。このためには、担体を構成する材質の真比重を海水
または湖水に比べて小さくするか、あるいは構成材質の
真比重は大きいものの、内部に閉じた空孔を持たせるこ
とによって、海水または湖水に比べて実効的な比重を小
さくして光触媒体の浮遊を可能にする。As the granular and porous photocatalyst of the present invention, a photocatalyst capable of floating on the water surface when loaded into water with a photocatalyst supported thereon is used. In order to be able to float, it is necessary that the effective specific gravity is smaller than that of lake water or sea water. For this purpose, the true specific gravity of the material constituting the carrier is made smaller than that of seawater or lake water, or the true specific gravity of the constituent material is large, but by having closed pores inside, In comparison with this, the effective specific gravity is made smaller to allow the photocatalyst to float.
【0019】本発明の光触媒体として、図2に示すよう
に、粒状担体に成形されたものに光触媒を担持させたも
のを用いることができる。このような光触媒体は、光触
媒が担体の表面または表面近くに担持されるので、光触
媒を有効に作用させることができる。As the photocatalyst of the present invention, as shown in FIG. 2, a photocatalyst carried on a granular carrier can be used. In such a photocatalyst, since the photocatalyst is supported on or near the surface of the carrier, the photocatalyst can act effectively.
【0020】粒状担体を成形した後に光触媒を担持させ
る方法としては、例えば酸化チタンの原料塩の溶液に担
体を含浸し、アルカリを加えて液のpHを高めることによ
り担体表面に酸化チタン成分を付着させ、これを熱処理
する方法を挙げることができる。また加熱した電気炉中
に担体を配置し、これに例えばチタンテトライソプロポ
キシドの有機溶剤溶液を霧化したものを空気で電気炉中
に気相輸送し、担体表面で熱分解して膜状に形成しても
よい。As a method of supporting the photocatalyst after forming the granular carrier, for example, the carrier is impregnated with a solution of a raw salt of titanium oxide, and the pH of the solution is increased by adding an alkali to attach the titanium oxide component to the surface of the carrier. And heat-treating it. In addition, a carrier is placed in a heated electric furnace, and for example, an atomized solution of titanium tetraisopropoxide in an organic solvent is vapor-transported into an electric furnace by air, and thermally decomposed on the surface of the carrier to form a film. May be formed.
【0021】また、本発明の光触媒を担持した粒状担体
は、図3に示すように、粒状担体の成形前に担体原料に
光触媒を混合することによって光触媒を担持させること
もできる。このようにして光触媒を担持させてなるもの
は、光触媒は担体に強固に担持されているため、脱落の
おそれがない。Further, as shown in FIG. 3, the particulate carrier carrying the photocatalyst of the present invention can be loaded with a photocatalyst by mixing the carrier material before the formation of the particulate carrier. In the case where the photocatalyst is supported in this way, the photocatalyst is firmly supported by the carrier, and thus there is no risk of falling off.
【0022】なお、このようにして得られる光触媒体
は、燐酸で処理してそのpHを調整することができる。The pH of the thus obtained photocatalyst can be adjusted by treating it with phosphoric acid.
【0023】さらに、本発明において、光触媒体を水面
に散布した場合に、できれば水面の景観を損なわないこ
とが望ましい。このような観点から本発明においては、
上記成型体のほかに、天然に存在する軽石などの鉱物
や、木材などの植物からなる天然素材を、粒状で多孔質
の光触媒担体として光触媒を担持させて、好適に使用す
ることができる。Further, in the present invention, when the photocatalyst is sprayed on the water surface, it is desirable that the water surface scene is not spoiled if possible. From such a viewpoint, in the present invention,
In addition to the above-mentioned molded product, a naturally occurring mineral such as pumice or a natural material made of a plant such as wood can be suitably used by supporting a photocatalyst as a granular and porous photocatalyst carrier.
【0024】本発明における光触媒体は、水中に投入し
水面に浮遊させるのに適した大きさのものである。光触
媒を担持した粒状担体を水面に浮遊させ、太陽光などの
光の照射による光触媒作用によって水面および水面近傍
の有機物を分解する際には、その大きさを比較的小さく
した方が、光の照射を受ける比率及び水と接触する比率
が多くなって有利である。しかし回収することを考慮す
れば、光触媒体の大きさは回収に適した大きさにとどめ
る必要がある。こうした観点から光触媒体の大きさは適
宜選択することができる。The photocatalyst of the present invention has a size suitable for being put into water and floating on the water surface. When the particulate carrier supporting the photocatalyst is suspended on the water surface and the organic matter near the water surface or near the water surface is decomposed by the photocatalysis caused by irradiation of light such as sunlight, it is better to make the size relatively small. It is advantageous to increase the ratio of receiving water and the ratio of contact with water. However, in consideration of recovery, the size of the photocatalyst needs to be limited to a size suitable for recovery. From such a viewpoint, the size of the photocatalyst can be appropriately selected.
【0025】本発明における光触媒体を水面に散布し浮
遊させる方法ついて、何ら限定はない。光触媒体を回収
する方法についても、何ら限定はなく、例えば捕集網を
用いたり、水面付近の担体を含む水を吸入濾過するなど
の方法で、ごく容易に行うことができる。The method of spraying and floating the photocatalyst on the water surface in the present invention is not limited at all. The method for recovering the photocatalyst is not particularly limited, and can be very easily performed by, for example, using a collecting net or suction-filtrating water containing a carrier near the water surface.
【0026】本発明における光触媒体を浮遊させる領域
を限定するには、例えばオイルフェンスのような簡単な
囲いを設けてこれを行うことができる。また光触媒体を
例えばビーズ状などにしてロープに結んだものを水に浮
遊させ、ロープを固定することによって移動を防ぐこと
もできる。In order to limit the region in which the photocatalyst is floated in the present invention, a simple enclosure such as an oil fence can be provided, for example. In addition, it is also possible to prevent the photocatalyst from moving by suspending the photocatalyst tied to a rope in the form of beads or the like in water and fixing the rope.
【0027】本発明において、光触媒体の水面からの浸
漬の程度としては、水とよく接触するよう浸漬してお
り、しかも光がよく照射される程度に浮遊していること
が望ましい。その浸漬深さはの調整は、粒状担体の実効
的な比重を選択することによって行うことができる。In the present invention, the degree of immersion of the photocatalyst from the water surface is preferably such that the photocatalyst is immersed so as to be in good contact with water and is floating to such an extent that light is well irradiated. The adjustment of the immersion depth can be performed by selecting an effective specific gravity of the granular carrier.
【0028】本発明の光触媒体は、湖沼、貯水池や海洋
などの水面に散布し、浮遊させて用いることができ、と
くに水が富栄養化の傾向にある区域に用いれば効果的で
ある。例えば湖沼、海洋などにおいて、富栄養水の流入
する河口付近、あるいは発電所の取水口付近に領域を限
定して重点的に散布浮遊させて用いることができる。そ
してこのように限定した領域において、増殖防止の対象
となる有害生物に応じて浮遊させる光触媒体の量を適宜
選択することができる。The photocatalyst of the present invention can be used by spraying and floating on the surface of water such as lakes, marshes, reservoirs and the ocean. It is particularly effective when used in areas where water tends to be eutrophic. For example, in lakes, marshes, oceans, and the like, they can be used by being scattered and floated with a limited area near the estuary to which eutrophic water flows or near the intake of a power plant. In such a limited area, the amount of the photocatalyst to be suspended can be appropriately selected depending on the pest to be prevented from growing.
【0029】[0029]
【作用】水面に浮遊する光触媒体に太陽光が照射する
と、半導体である光触媒内部に電子と正孔の対が生成
し、この正孔によって非常に強い酸化作用が生じる。光
触媒体は水面に浮遊しているので、この酸化作用によっ
て水面の近くに存在する微生物などの有機化合物を水と
炭酸ガスなどに酸化分解する。この有機物分解によって
有害生物の増殖を防止することができる。When the photocatalyst floating on the water surface is irradiated with sunlight, a pair of electrons and holes is generated inside the photocatalyst which is a semiconductor, and the holes generate a very strong oxidizing action. Since the photocatalyst is floating on the water surface, this oxidizing action oxidizes and decomposes organic compounds such as microorganisms existing near the water surface into water and carbon dioxide gas. This decomposition of organic substances can prevent the growth of pests.
【0030】本発明においては、光触媒が直接水面に浮
遊しているので、光を遮られることがない。また多孔質
であって水に接触しているので、光触媒による酸化作用
は水を介して行われ、水面及び水面近くの水中における
有機物が酸化分解される。これによって有害生物の増殖
が防止される。光触媒担体はいずれも化学的に安定なも
のが用いられるので、担体が酸化されてしまうことがな
い。In the present invention, since the photocatalyst is directly floating on the water surface, the light is not blocked. Further, since it is porous and in contact with water, the oxidizing action by the photocatalyst is performed through water, and organic substances in the water surface and in water near the water surface are oxidized and decomposed. This prevents the growth of pests. Since all of the photocatalyst carriers are chemically stable, the carriers are not oxidized.
【0031】[0031]
【発明の実施の形態】以下に実施例に基づき、発明の実
施の形態を説明する。Embodiments of the present invention will be described below based on examples.
【0032】(実施例1)図4に示す大きさ2m×2m
×1mの水槽に富栄養化した湖水7を満たした。この湖
水にはプランクトン11の存在が認められた。水槽に水
面から約0.7mの深さまでを覆うオイルフェンス9を
用い、水槽を2分した。この水槽は日照がある限り、日
の出から日没まで太陽光が遮られることなく照射するよ
うに設計され、水温は25℃に制御されている。この2
分された水槽の一方に、図1に示すように、表面に酸化
チタンを担持した光触媒体4を浮遊させた。(Embodiment 1) The size shown in FIG.
A × 1 m aquarium was filled with eutrophic lake water 7. Plankton 11 was observed in this lake. Using an oil fence 9 covering the water tank up to a depth of about 0.7 m from the water surface, the water tank was divided into two minutes. The water tank is designed to irradiate sunlight from sunrise to sunset without interruption as long as there is sunshine, and the water temperature is controlled at 25 ° C. This 2
In one of the divided water tanks, as shown in FIG. 1, a photocatalyst 4 having titanium oxide supported on the surface was floated.
【0033】ここで用いた光触媒体は、図2に示す工程
により、まず石炭灰を粉砕混合して粒状に加圧成形し、
熱処理して水に浮遊する粒状で多孔質担体を作り、これ
を塩化チタンの溶液に含浸してから、アルカリを加え液
のpHを高めることによって、担体表面に酸化チタン成分
を付着させてなるものを、さらに熱処理して表面に酸化
チタンを担持させてなるものである。The photocatalyst used here is obtained by first pulverizing and mixing coal ash and pressing it into granules by the process shown in FIG.
A porous carrier in the form of particles suspended in water by heat treatment, impregnated with a solution of titanium chloride, and then added with an alkali to increase the pH of the solution, thereby allowing a titanium oxide component to adhere to the surface of the carrier. Is further heat-treated to support titanium oxide on the surface.
【0034】図5にこの実施例における水槽内の湖水面
におけるプランクトンの増殖曲線を示す。図でAは光触
媒体を浮遊させた側の水面の増殖曲線、Pは光触媒体を
浮遊させなかった水面の増殖曲線である。この図に示さ
れたように、光触媒体を浮遊させた側の水面では、プラ
ンクトンの増殖が防止されることが確認された。FIG. 5 shows a plankton growth curve on a lake surface in a water tank in this embodiment. In the figure, A is a growth curve on the water surface on which the photocatalyst is suspended, and P is a growth curve on the water surface on which the photocatalyst is not suspended. As shown in this figure, it was confirmed that plankton growth was prevented on the water surface on which the photocatalyst was suspended.
【0035】(実施例2)光触媒を担持する粒状で多孔
質の担体として、軽石を用い、これに酸化チタンを担持
させてなるものを用いた以外は、実施例1と全く同様に
し、プランクトンの増殖を調べた。図5のBにその結果
を示す。この光触媒体を浮遊させた場合においても同様
にプランクトンの増殖が防止されることが確認できた。(Example 2) Except that pumice was used as a granular and porous carrier for supporting a photocatalyst and that a titanium oxide was supported on it, a plankton The growth was examined. FIG. 5B shows the result. It was also confirmed that plankton growth was similarly prevented when the photocatalyst was suspended.
【0036】(実施例3)水槽に満たす水として富栄養
化した海水を用いた以外は、実施例1と全く同様にしプ
ランクトンの増殖を調べた。この海水には微小生物の存
在が認められた。図6に水槽内の海水面におけるプラン
クトンの増殖曲線を示す。図でDは光触媒体を浮遊させ
た側の海水面の増殖曲線、Qは光触媒体を浮遊させなか
った海水面の増殖曲線である。この図に示されたよう
に、海水においても光触媒体を浮遊させた側の水面で
は、プランクトンの増殖が防止されることが確認され
た。(Example 3) Plankton growth was examined in exactly the same manner as in Example 1 except that eutrophicized seawater was used as water to fill the water tank. The presence of micro-organisms was found in this seawater. FIG. 6 shows a plankton growth curve on the sea surface in the water tank. In the figure, D is a growth curve of the sea surface on the side where the photocatalyst is suspended, and Q is a growth curve of the sea surface where the photocatalyst is not suspended. As shown in this figure, it was confirmed that plankton growth was prevented on the water surface on the side where the photocatalysts were suspended even in seawater.
【0037】[0037]
【発明の効果】本発明において、粒状で多孔質な担体に
光触媒を担持させ、水面に浮遊可能にすることにより、
これを直接水面に浮遊させ、しかも水によく接触しなが
ら有効に光照射を受けることができる。このため、粒状
多孔質光触媒体の強い酸化力は水を介して作用し、効果
的に有機物の分解を行うことができる。また光触媒体は
必要な箇所に必要な数量を浮遊させることができ、その
回収も容易である。According to the present invention, a photocatalyst is supported on a granular and porous carrier so that the photocatalyst can float on the water surface.
This can be floated directly on the water surface, and can be effectively irradiated with light while being in good contact with water. For this reason, the strong oxidizing power of the granular porous photocatalyst acts through water, and organic substances can be effectively decomposed. In addition, the required amount of the photocatalyst can be floated at a required location, and the collection thereof is easy.
【0038】また本発明において、シリコンとアルミニ
ウムとの酸化物を主成分として含有する粒状で多孔質の
担体、とくに石炭灰を含有する粒状で多孔質の担体を用
いることにより、環境を汚染せず、廃棄物である石炭灰
の有効活用が可能となり、経済性の面のみならず、環境
対策の面からも望ましい効果が得られる。Further, in the present invention, the use of a granular porous carrier containing an oxide of silicon and aluminum as a main component, particularly a granular porous carrier containing coal ash, does not pollute the environment. In addition, coal ash, which is waste, can be effectively used, and desirable effects can be obtained not only in terms of economy but also in terms of environmental measures.
【0039】さらに本発明において、粒状の担体として
天然素材を用いていることにより、環境汚染を防ぎ、し
かも水面の景観を損なわずに有害生物の増殖防止を行う
ことが可能である。Further, in the present invention, by using a natural material as the granular carrier, it is possible to prevent environmental pollution and prevent the growth of pests without impairing the landscape of the water surface.
【図1】本発明の光触媒体を水面に浮遊させた状態を模
式的に示した図。FIG. 1 is a diagram schematically showing a state in which a photocatalyst of the present invention is floated on a water surface.
【図2】光触媒を担持した粒状の担体の製造方法を示し
た図。FIG. 2 is a diagram showing a method for producing a granular carrier supporting a photocatalyst.
【図3】光触媒を担持した粒状の担体の製造方法を示し
た図。FIG. 3 is a diagram showing a method for producing a granular carrier supporting a photocatalyst.
【図4】本発明の実施例の水槽の構成を示す図FIG. 4 is a diagram showing a configuration of an aquarium according to an embodiment of the present invention.
【図5】湖水中の植物性プランクトンの増殖曲線を示し
た図。FIG. 5 is a diagram showing a growth curve of phytoplankton in lake water.
【図6】海水中のプランクトンの増殖曲線を示した図。FIG. 6 is a view showing a growth curve of plankton in seawater.
【図7】従来技術である、筏状の浮遊体に光触媒を固定
し水面に浮遊させた図。FIG. 7 is a diagram showing a conventional technique in which a photocatalyst is fixed to a raft-shaped floating body and floated on the water surface.
1……光触媒 2……多孔質光触媒担体, 3…水
面 4……光触媒体, 6……水槽, 7……水,
8……砂礫,9……オイルフェンス, 10……アン
カワイヤ 11……プランクトン 12……筏状浮遊体Reference Signs List 1 photocatalyst 2 porous photocatalyst carrier 3 water surface 4 photocatalyst body 6 water tank 7 water
8 ... sand and gravel, 9 ... oil fence, 10 ... anchor wire 11 ... plankton 12 ... raft-like floating body
Claims (6)
てなる、水面に浮遊可能な有機物分解用光触媒体。1. A photocatalyst for decomposing organic substances which can be suspended on a water surface, wherein the photocatalyst is supported on a granular porous carrier.
分として含有する多孔質体に、酸化チタンを含有する光
触媒を担持させてなることを特徴とする請求項1記載の
有機物分解用光触媒体。2. The photocatalyst for decomposing organic substances according to claim 1, wherein a photocatalyst containing titanium oxide is supported on a porous body containing silicon oxide and aluminum oxide as main components.
てなる、水面に浮遊可能な光触媒体を水面に散布して浮
遊させることを特徴とする有害生物の増殖防止方法。3. A method for preventing the growth of pests, wherein a photocatalyst capable of floating on a water surface, comprising a particulate porous carrier carrying a photocatalyst, is sprayed and floated on the water surface.
有する粒状多孔質担体であることを特徴とする請求項3
記載の有害生物の増殖防止方法。4. The granular porous carrier according to claim 3, wherein the porous carrier is a granular porous carrier containing coal ash.
The method for preventing the growth of pests according to the above.
少なくとも表面にカルシウムの燐酸化合物を有すること
を特徴とする請求項3記載の有害生物の増殖防止方法。5. The method for preventing the growth of pests according to claim 3, wherein a calcium phosphate compound is present on at least the surface of the granular porous carrier containing coal ash.
あることを特徴とする請求項3記載の有害生物の増殖防
止方法。6. The method for preventing the growth of pests according to claim 3, wherein the granular and porous carrier is a natural material.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9360975A JPH11188269A (en) | 1997-12-26 | 1997-12-26 | Photocatalystic body for decomposing organic material, proliferation preventing method of harmful organism using the same |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9360975A JPH11188269A (en) | 1997-12-26 | 1997-12-26 | Photocatalystic body for decomposing organic material, proliferation preventing method of harmful organism using the same |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH11188269A true JPH11188269A (en) | 1999-07-13 |
Family
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Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP9360975A Withdrawn JPH11188269A (en) | 1997-12-26 | 1997-12-26 | Photocatalystic body for decomposing organic material, proliferation preventing method of harmful organism using the same |
Country Status (1)
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JP (1) | JPH11188269A (en) |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2001024927A1 (en) * | 1999-10-01 | 2001-04-12 | Showa Denko Kabushiki Kaisha | Composite member for deodorization or waste water treatment |
US6803023B1 (en) | 1999-10-01 | 2004-10-12 | Showa Denko Kabushiki Kaisha | Composite structure for deodorization or wastewater treatment |
EP1735072A1 (en) * | 2004-04-06 | 2006-12-27 | Kinetico Incorporated | Buoyant filter media |
WO2008136532A1 (en) * | 2007-05-08 | 2008-11-13 | Masaru Akakura | Method of improving quality of water in water tank and device for improving water quality therefor |
EP2595923A2 (en) * | 2010-07-23 | 2013-05-29 | UV Cleaning Systems, Inc. | Solar-activated photochemical purification of fluids |
US9017613B2 (en) | 2007-06-20 | 2015-04-28 | Uvcleaning Systems, Inc. | Ultraviolet photoreactor for the purification of fluids |
CN109878069A (en) * | 2019-02-11 | 2019-06-14 | 福建师范大学 | A kind of dendritic phthalocyanine@SiO2The preparation method of photocatalytic device |
-
1997
- 1997-12-26 JP JP9360975A patent/JPH11188269A/en not_active Withdrawn
Cited By (11)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2001024927A1 (en) * | 1999-10-01 | 2001-04-12 | Showa Denko Kabushiki Kaisha | Composite member for deodorization or waste water treatment |
US6803023B1 (en) | 1999-10-01 | 2004-10-12 | Showa Denko Kabushiki Kaisha | Composite structure for deodorization or wastewater treatment |
EP1735072A1 (en) * | 2004-04-06 | 2006-12-27 | Kinetico Incorporated | Buoyant filter media |
EP1735072A4 (en) * | 2004-04-06 | 2008-08-06 | Kinetico Inc | Buoyant filter media |
WO2008136532A1 (en) * | 2007-05-08 | 2008-11-13 | Masaru Akakura | Method of improving quality of water in water tank and device for improving water quality therefor |
JP2008279325A (en) * | 2007-05-08 | 2008-11-20 | Masaru Akakura | Method for improving quality of water in water tank and water quality improver therefor |
US9017613B2 (en) | 2007-06-20 | 2015-04-28 | Uvcleaning Systems, Inc. | Ultraviolet photoreactor for the purification of fluids |
EP2595923A2 (en) * | 2010-07-23 | 2013-05-29 | UV Cleaning Systems, Inc. | Solar-activated photochemical purification of fluids |
EP2595923A4 (en) * | 2010-07-23 | 2014-01-22 | Uv Cleaning Systems Inc | Solar-activated photochemical purification of fluids |
CN109878069A (en) * | 2019-02-11 | 2019-06-14 | 福建师范大学 | A kind of dendritic phthalocyanine@SiO2The preparation method of photocatalytic device |
CN109878069B (en) * | 2019-02-11 | 2020-11-24 | 福建师范大学 | Dendritic phthalocyanine @ SiO2Preparation method of photocatalytic device |
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