JPH11319857A - Photocatalytic reaction apparatus - Google Patents

Photocatalytic reaction apparatus

Info

Publication number
JPH11319857A
JPH11319857A JP15060498A JP15060498A JPH11319857A JP H11319857 A JPH11319857 A JP H11319857A JP 15060498 A JP15060498 A JP 15060498A JP 15060498 A JP15060498 A JP 15060498A JP H11319857 A JPH11319857 A JP H11319857A
Authority
JP
Japan
Prior art keywords
water
photocatalyst
tank
treated
rotating body
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.)
Granted
Application number
JP15060498A
Other languages
Japanese (ja)
Other versions
JP2907814B1 (en
Inventor
Nobuya Ishio
暢弥 石尾
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.)
FUSO KENSETSU KOGYO
Fuso Kensetsu Kogyo KK
Original Assignee
FUSO KENSETSU KOGYO
Fuso Kensetsu Kogyo KK
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 FUSO KENSETSU KOGYO, Fuso Kensetsu Kogyo KK filed Critical FUSO KENSETSU KOGYO
Priority to JP15060498A priority Critical patent/JP2907814B1/en
Application granted granted Critical
Publication of JP2907814B1 publication Critical patent/JP2907814B1/en
Publication of JPH11319857A publication Critical patent/JPH11319857A/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Abstract

PROBLEM TO BE SOLVED: To provide a photocatalytic reaction water treating apparatus which enables continuous, stable radiation of ultraviolet of a specific strength to a catalyst surface, causes no toxicity, generates no by-product and has a low initial cost. SOLUTION: A photocatalytic reaction apparatus is equipped with mutually connected multiple water tanks 10-15 allowing the treated water to successively flow into the next tank, rotating bodies 1-6 carrying photocatalysts, which are individually placed in each tank and partially soaked in the treated water in the tank and ultraviolet radiation means 28-39 placed in the atmosphere adjacent to each rotating body. The treated water in each water tank 10-15 is stuck to the rotating bodies 1-6, transferred to the atmosphere by the rotation of the rotating body and irradiated with ultraviolet in the atmosphere to avoid decrement of the ultraviolet radiation strength generated in underwater radiation.

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、水処理技術に関
し、特に、光触媒反応を利用する水処理装置に関する。
The present invention relates to a water treatment technique, and more particularly, to a water treatment apparatus utilizing a photocatalytic reaction.

【0002】[0002]

【従来の技術】浄水処理及び海水淡水化における海水の
前処理等においては、しばしばオゾン(O3)による処
理が使われる。このオゾン処理は、カビ臭の除去、着色
した有機物質の脱色、凝集効果の改善、殺菌等、その効
果に関しては顕著なものがある。しかしながら、このオ
ゾン処理に要するイニシャルコストは甚大であり、しか
も、オゾンの発生に要するエネルギ効率は著しく低い。
オゾン発生器に関しては、今日に至るも19世紀に開発
されたジーメンス方式を改良したものが主流である。無
論、今日のエレクトロニクスの進歩は、オゾン発生器の
機能部品の改良に反映されてはいるが、オゾンの生成反
応の原理的なものから来る効率の低さは、あまり改善さ
れていないのが現状である。このような技術的な見地か
ら、爛熟期にあるものは徐々に他の新しい方式に置き換
えられていくと考えられる。そうした新しい方式の中
で、国の研究機関でも研究テーマとして取り上げられて
いるものが、光触媒を応用した水処理である。光触媒に
ついては、既に各種のものが知られているが、その中
で、人体に無害で、かつ比較的容易に入手若しくは加工
が可能なものは、二酸化チタン(TiO2)のみという
ことができる。
2. Description of the Related Art Ozone (O 3 ) treatment is often used in pretreatment of seawater in water purification treatment and seawater desalination. This ozone treatment has remarkable effects such as removal of mold odor, decolorization of a colored organic substance, improvement of a coagulation effect, and sterilization. However, the initial cost required for this ozone treatment is enormous, and the energy efficiency required for generating ozone is extremely low.
As for the ozone generator, an improved version of the Siemens system developed in the 19th century is still the mainstream. Of course, today's advances in electronics are reflected in improvements in the functional components of the ozone generator, but the low efficiency resulting from the fundamental ozone generation reaction has not been improved much. It is. From such a technical point of view, it is considered that those in the mature stage are gradually replaced by other new systems. Among these new methods, one of the research themes in national research institutes is water treatment using photocatalysts. Various types of photocatalysts are already known, and among them, titanium dioxide (TiO 2 ) is harmless to the human body and can be obtained or processed relatively easily.

【0003】[0003]

【発明が解決しようとする課題】そこで、この二酸化チ
タンを利用した水処理装置が発想される。このような二
酸化チタンを用いた水処理における有機物質の処理技術
において、光触媒の水処理への適用の仕方は、光触媒表
面と光源である紫外線ランプとの間に処理しようとする
水を介在させ、紫外線の照射により光触媒表面に生成し
たOHラジカルなどの非常に強力な作用を持つ化学種を
水中の有機物、細菌等の分解反応や不活性化に用いるも
のである。したがって、光触媒がこれらの有効な化学種
を放出し続けるためには、然るべき強度の紫外線が、水
中の光触媒表面に安定的に照射され続けなければならな
い。しかしながら、水中で紫外線を照射させる方式を想
定した場合、光触媒の表面に到達するまでの紫外線の強
度の減衰が問題になる。
Therefore, a water treatment apparatus utilizing this titanium dioxide is conceived. In such a technology of treating an organic substance in water treatment using titanium dioxide, a method of applying a photocatalyst to water treatment involves interposing water to be treated between the photocatalyst surface and an ultraviolet lamp as a light source, Chemical species having a very strong action such as OH radicals generated on the photocatalyst surface by irradiation of ultraviolet rays are used for a decomposition reaction or inactivation of organic substances and bacteria in water. Therefore, in order for the photocatalyst to continue to emit these effective species, ultraviolet light of an appropriate intensity must be continuously irradiated on the photocatalyst surface in water. However, when a method of irradiating ultraviolet rays in water is assumed, attenuation of the intensity of the ultraviolet rays until reaching the surface of the photocatalyst becomes a problem.

【0004】本発明は、上記の問題に鑑みてなされたも
のであって、然るべき強度の紫外線を光触媒表面に安定
的に照射し続けることを可能とする装置を、毒性・副生
成物の少ない、イニシャルコストの低い装置として提供
することを第1の目的とする。ところで、未だ除濁が完
全でない水を処理しようとする場合には、常に光触媒表
面に付着しようとする微生物や濁質を除去しなくてはな
らない。そこで、本発明は、上記光触媒作用を低下させ
るように働き、常に水中の紫外線ランプ及び光触媒表面
に付着しようとする微生物や濁質を除去することを第2
の目的とする。更に、本発明は、生物処理との併用によ
り光触媒反応による効果を一層顕著にすることを第3の
目的とする。また、本発明は、装置としての処理効率を
高めることを第4の目的とする。
The present invention has been made in view of the above-mentioned problems, and an object of the present invention is to provide an apparatus capable of continuously irradiating the photocatalyst surface with ultraviolet rays of an appropriate intensity stably, with less toxic and by-products. A first object is to provide a device having a low initial cost. By the way, in the case of treating water whose turbidity is not yet complete, it is necessary to always remove microorganisms and turbid substances which are to adhere to the surface of the photocatalyst. Therefore, the present invention works to reduce the above-mentioned photocatalytic action and always removes microorganisms and turbid substances that are likely to adhere to the ultraviolet lamp and the photocatalytic surface in water.
The purpose of. Further, a third object of the present invention is to make the effect of the photocatalytic reaction more remarkable when used in combination with biological treatment. A fourth object of the present invention is to increase the processing efficiency of the apparatus.

【0005】[0005]

【課題を解決するための手段】上述した目的を達成する
ために、本発明は、光触媒反応装置を、被処理水を順次
次の水槽に流動可能に互いに連結された多数の水槽と、
一部を水槽内の被処理水に浸すように各水槽内に個々に
設置され、光触媒を担持した回転体と、各回転体に隣接
して空中に配置した紫外線照射手段とで構成すること
で、各水槽内の被処理水を回転体に付着させ、その回転
により空中に運び出し、空中で紫外線を照射することに
より処理するようにしている。この場合において、水中
に配置した紫外線照射手段を付加することができる。ま
た、第2の目的を達成するため、各水槽に被処理水を振
動させる超音波振動手段を設けている。更に、第3の目
的を達成するため、多数の水槽の上流に光触媒を担持し
ない回転体を配した水槽を連結している。そして、第4
の目的を達成するため、最下流側の水槽と最上流側の水
槽とを被処理水返送ラインにより連結している。
In order to achieve the above-mentioned object, the present invention provides a photocatalytic reactor comprising a plurality of water tanks connected to each other so that water to be treated can flow to the next water tank sequentially.
By arranging each part in each water tank so as to be immersed in the water to be treated in the water tank, a rotating body carrying a photocatalyst, and an ultraviolet irradiation means arranged in the air adjacent to each rotating body. The water to be treated in each water tank is attached to a rotating body, carried out to the air by the rotation thereof, and treated by irradiating ultraviolet rays in the air. In this case, an ultraviolet irradiation means arranged in water can be added. In order to achieve the second object, each of the water tanks is provided with an ultrasonic vibrating means for vibrating the water to be treated. Further, in order to achieve the third object, a water tank having a rotating body that does not carry a photocatalyst is connected upstream of a large number of water tanks. And the fourth
In order to achieve the above object, the most downstream water tank and the most upstream water tank are connected by a treated water return line.

【0006】[0006]

【作用】上記の構成からなる装置では、光触媒を担持す
る部分は、既に水処理における生物処理方法の1つとし
て定着した回転円板法に類似させることとした。そうす
ることによって、光触媒の担持された面と、処理を行お
うとする水との接触が十分に行われ、安定した処理効果
が期待されることからである。また、光触媒担持部分を
回転させることにより、紫外線の空気中での照射が可能
になる。本装置では、たとえ紫外線の照射が空気中で行
われるとしても、回転体の表面には常に水の薄膜が存在
しており、紫外線の光源と光触媒との間に水を介在させ
るという処理の基本形式は満たされている。また、紫外
線が水の薄膜を透過するだけであるので、水中のみで紫
外線を照射させる方式に比べ、光触媒の表面に到達する
までの紫外線の強度の減衰が少なく、効率のよい光触媒
の利用が可能になる。この場合、請求項2に記載のよう
に、水中に配置した紫外線照射手段を付加することによ
り、より効率のよい光触媒の利用が可能になる。
In the apparatus having the above structure, the portion supporting the photocatalyst is similar to the rotating disk method which has already been established as one of biological treatment methods in water treatment. By doing so, the surface on which the photocatalyst is supported and the water to be treated are sufficiently contacted, and a stable treatment effect is expected. Further, by rotating the photocatalyst-carrying portion, it becomes possible to irradiate ultraviolet rays in the air. In this device, even if the irradiation of ultraviolet rays is performed in the air, a thin film of water always exists on the surface of the rotating body, and the basic process of interposing water between the ultraviolet light source and the photocatalyst. The form is satisfied. In addition, since ultraviolet rays only pass through a thin film of water, the intensity of the ultraviolet rays before reaching the surface of the photocatalyst is less attenuated compared to the method of irradiating ultraviolet rays only in water, and efficient photocatalyst utilization is possible. become. In this case, more efficient use of the photocatalyst becomes possible by adding an ultraviolet irradiation means arranged in water as described in claim 2.

【0007】次に、被処理水の除濁が完全でない段階で
は、常に光触媒表面に付着しようとする微生物や濁質を
除去しなくてはならない。その手段として、請求項3に
記載の構成により、水中で超音波を作用させ、光触媒を
担持した回転体に付着しようとする水中の濁質を分散状
態に維持することが非常に有力な手段となり得る。更
に、超音波振動の付与は、比較的緩慢であるとされる光
触媒の反応を加速させる働きをする。なお、超音波が水
中の反応を加速するということは、既に事実として知ら
れているが、どのようなメカニズムに基づくのかという
点については、未だに定説がない。
Next, at the stage where the turbidity of the water to be treated is not perfect, it is necessary to always remove microorganisms and turbid substances which are to adhere to the surface of the photocatalyst. As the means, it is a very effective means to apply ultrasonic waves in water and maintain the suspended matter in water to be attached to the rotating body carrying the photocatalyst in a dispersed state. obtain. Furthermore, the application of ultrasonic vibrations serves to accelerate the reaction of the photocatalyst, which is said to be relatively slow. It is already known that ultrasonic waves accelerate reactions in water, but there is no established theory as to what mechanism is used.

【0008】更に、請求項4及び請求項5に記載の構成
によると、通常の生物処理である回転円板法の後続とし
て本法を使用することで、生物処理でなかなか分解除去
できない物質を補完的に分解することができる。生物処
理においては、原水の除濁効果が十分に期待できるもの
で、このコンビネーションは光触媒装置にとって有利に
働くものである。
Further, according to the constitutions of claims 4 and 5, the present method is used as a follow-up to the rotating disk method which is a normal biological treatment, thereby supplementing substances which cannot be easily decomposed and removed by the biological treatment. Can be decomposed. In biological treatment, the turbidity of raw water can be sufficiently expected, and this combination works advantageously for the photocatalytic device.

【0009】[0009]

【発明の実施の形態】以下、本発明の光触媒反応装置の
実施の形態を図面に基づいて説明する。本発明の光触媒
反応装置の一実施例を、図1〜図3を用いて説明する。
図1は本発明を具体化した光触媒反応装置の平面図(た
だし、上部のフードを除いて示す)である。この装置
は、主として光触媒を担持した回転体を構成する多数の
回転円板1〜6を設置した多数の水槽10〜15で構成
されている。図示のものでは、回転円板数が6枚の場合
を例示するが、円板数とそれに対応する水槽数は、必要
に応じて加減するものとする。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Embodiments of the photocatalytic reaction device of the present invention will be described below with reference to the drawings. One embodiment of the photocatalytic reaction device of the present invention will be described with reference to FIGS.
FIG. 1 is a plan view of a photocatalytic reactor embodying the present invention (however, an upper hood is omitted). This apparatus is mainly composed of a large number of water tanks 10 to 15 provided with a large number of rotating disks 1 to 6 constituting a rotating body carrying a photocatalyst. In the drawing, the case where the number of rotating disks is six is exemplified, but the number of disks and the number of water tanks corresponding thereto are adjusted as necessary.

【0010】光触媒を担持した回転円板1〜6は、適度
な浸漬率、例えば、浸漬率30〜40%程度となるよう
に回転円板の下方を囲う水槽10〜15内に設置されて
いる。これらの水槽は、前後互いに連結していて、前段
の水槽10から後段の水槽15に移行するに従って処理
の程度は進む配列とされている。
The rotating disks 1 to 6 carrying the photocatalyst are placed in water tanks 10 to 15 surrounding the lower part of the rotating disk so as to have an appropriate immersion rate, for example, about 30 to 40%. . These water tanks are connected to each other in the front and rear, and are arranged in such a manner that the degree of processing increases as the water tank 10 in the preceding stage shifts to the water tank 15 in the subsequent stage.

【0011】図2に示すように、回転円板1〜6が浸か
る各水槽10〜15の底部には、発振器42で駆動する
ことで超音波を発生させる超音波振動手段、具体的には
振動子函20〜25が設置されている。これら振動子函
20〜25は、回転円板1〜6が回転している間は、振
動子を作動させ、円板表面に付着しようとする濁質、生
物を分散させ、円板表面を常時清浄にし、照射された紫
外線が円板上に担持した光触媒上に効率よく到達するの
を助けるために設けられている。これにより与えられる
超音波振動は、同時に超音波独自の反応促進作用によ
り、水中に移行したOHラジカルや活性酸素による有機
物の分解反応を進め、装置全体としての必要反応時間を
短縮し、装置のコンパクト化を図る意図をも持ってい
る。
As shown in FIG. 2, on the bottom of each of the water tanks 10 to 15 in which the rotating disks 1 to 6 are immersed, ultrasonic vibration means for generating ultrasonic waves by driving with an oscillator 42, specifically, Child boxes 20 to 25 are provided. These vibrator boxes 20 to 25 actuate the vibrator while the rotating disks 1 to 6 are rotating, disperse turbidity and organisms that are to adhere to the disk surface, and constantly keep the disk surface It is provided to help clean and irradiate the irradiated ultraviolet light efficiently on the photocatalyst supported on the disk. The ultrasonic vibrations given by this process simultaneously promote the decomposition reaction of organic substances by OH radicals and active oxygen transferred into water by the reaction promoting action unique to ultrasonic waves, shortening the required reaction time of the entire device, and making the device compact. It also has the intent to make it happen.

【0012】光触媒を担持した回転円板1〜6は同一の
直径である。これらの円板は、回転用シャフト9に固定
してあり、シャフト9の一端には、回転用モータ26が
減速機27を介して設置されている。これらは、紫外線
が透過する水の薄膜の厚さを適切に調整するため、円板
の周速をモータ26の回転数を制御して変更させること
を可能とするものである。また、本実施例においては、
光触媒を担持した回転円板1〜6及び後述の光触媒を担
持していない回転円板7,8を同一の回転用シャフト9
に固定し、同じ回転数で回転するように構成したが、原
水の水質によっては、光触媒を担持した回転円板1〜6
と担持していない回転円板7,8を、それぞれ別の回転
用シャフトに取り付けたり、減速機を介して取り付ける
ことにより、各々が最適の回転数で回転するように構成
することもできる。
The rotating disks 1 to 6 carrying the photocatalyst have the same diameter. These disks are fixed to a rotation shaft 9, and a rotation motor 26 is installed at one end of the shaft 9 via a speed reducer 27. These allow the peripheral speed of the disk to be changed by controlling the rotation speed of the motor 26 in order to appropriately adjust the thickness of the thin film of water through which the ultraviolet light passes. In the present embodiment,
The rotating disks 1 to 6 supporting the photocatalyst and the rotating disks 7 and 8 not supporting the photocatalyst described later are
And rotating at the same number of revolutions, but depending on the quality of the raw water, the rotating disks 1 to 6 carrying the photocatalyst
By mounting the rotating disks 7 and 8 that do not carry the same on separate rotation shafts or via a reduction gear, each can be configured to rotate at an optimum rotation speed.

【0013】被処理水としての原水が円板1を配した水
槽10の前段にある水槽17にまず流入するように、水
槽17が原水流入口18により原水の供給ラインに連結
されている。水槽17には光触媒を担持していないプラ
スチック製の通常のタイプの回転円板7が他の回転円板
と共通の回転用シャフト9に固定して設置されている。
この回転円板7は、前述したように、原水中の濁質をあ
る程度生物処理により除去するものである。この除濁が
単一の生物処理用回転円板7で十分でない場合は、適宜
円板数を増やすことで対応する。
The water tank 17 is connected to a raw water supply line by a raw water inflow port 18 so that raw water as the water to be treated first flows into a water tank 17 at a stage preceding the water tank 10 on which the disk 1 is disposed. In the water tank 17, a plastic ordinary rotating disk 7 that does not carry a photocatalyst is fixedly mounted on a rotating shaft 9 common to the other rotating disks.
As described above, the rotating disk 7 removes turbidity in raw water to some extent by biological treatment. If this turbidity is not sufficient with a single biological treatment rotating disk 7, the number of disks may be increased as appropriate.

【0014】最終段の光触媒反応槽15の後段には、通
常の回転円板処理槽16が設けてある。ここで使用する
回転円板8の素材は、前記回転円板7のものと同一とす
る。この槽16の中の水は、既にほとんど無菌的になっ
ており、マクロ的に処理水質が良好に維持されている
が、この状態は、回転円板8の表面を観察することによ
って知ることができる。また、原水の水質によっては、
光触媒で低分子化した有機物を後段の回転円板8で生物
処理するといった使い方も可能である。
In the subsequent stage of the photocatalytic reaction tank 15 in the last stage, a usual rotating disk processing tank 16 is provided. The material of the rotating disk 8 used here is the same as that of the rotating disk 7. The water in the tank 16 is already almost aseptic, and the quality of the treated water is maintained in a good condition macroscopically. This state can be known by observing the surface of the rotating disk 8. it can. Also, depending on the quality of the raw water,
It is also possible to use the organic substance degraded by the photocatalyst by biological treatment with the rotating disk 8 at the subsequent stage.

【0015】光触媒を担持した回転円板1〜6に紫外線
を照射するために、各円板の近傍に、紫外線照射手段と
して、円板を挟むように対をなす水銀ランプ28〜39
が空中に位置するように、適宜の手段で支持されてい
る。この場合において、必要に応じて、紫外線照射手段
として空中に配置した水銀ランプ28〜39の下方の水
中に、水銀ランプ28〜39と対応するように、水銀ラ
ンプ28’〜39’を配置することができ、これによ
り、より効率のよい光触媒の利用が可能になる。
In order to irradiate the rotating disks 1 to 6 carrying the photocatalyst with ultraviolet rays, a pair of mercury lamps 28 to 39 sandwiching the disks are disposed near each disk as an ultraviolet irradiation means.
Are supported by appropriate means so as to be positioned in the air. In this case, if necessary, mercury lamps 28 'to 39' may be arranged in the water below the mercury lamps 28 to 39 arranged in the air as ultraviolet irradiation means so as to correspond to the mercury lamps 28 to 39. This enables more efficient use of the photocatalyst.

【0016】図示してないが、装置上部には、異物の侵
入と汚染防止のため、UVカット可能なフードを取り付
ける。このフードは、紫外線の連続照射により低濃度の
オゾン(O3)が発生するので、オゾンの装置外への漏
出を防ぐためにも必要である。
Although not shown, a UV-cuttable hood is attached to the upper part of the apparatus to prevent foreign substances from entering and preventing contamination. Since the hood generates low-concentration ozone (O 3 ) by continuous irradiation of ultraviolet rays, it is necessary to prevent ozone from leaking out of the apparatus.

【0017】また、この光触媒反応装置で低分子化した
有機物質を再度生物処理すると、低分子化により生物へ
の摂取状態が改善されているため、生物分解性が高ま
り、結果的に装置全体としての処理効率が高められるこ
とになる。そこで、この装置では、被処理水を返送又は
場合によって循環させる返送ライン40が、図1に示す
ように処理水槽16の下流と原水の供給ラインを連結す
るように設けられている。この返送ラインによる返送処
理については、処理水質の状況によって実施するか否か
を判断する。そのため、返送ライン40には流路切換用
のコック41を設けてある。
In addition, when the organic substance reduced in molecular weight is subjected to biological treatment again in this photocatalytic reaction device, the state of ingestion into living organisms is improved by the reduction in molecular weight, so that the biodegradability is enhanced, and as a result, the overall device becomes The processing efficiency is improved. Therefore, in this apparatus, a return line 40 for returning or circulating the water to be treated is provided so as to connect the downstream of the treatment water tank 16 and the supply line of raw water as shown in FIG. It is determined whether or not to perform the return processing by the return line depending on the condition of the treated water. Therefore, the return line 40 is provided with a cock 41 for switching the flow path.

【0018】更に、光触媒の活性化を向上させるため
に、図示しない光触媒反応装置部分のフードは、密閉型
となるようにし、フード内部に小型のオゾン発生装置か
ら発生するオゾン化空気を通導できるようにするのも有
効である。この場合、オゾンモニタを使用し、内部のオ
ゾン濃度が適度になるようにコントロールする。そし
て、点検時にはオゾン発生器を停止させ、排風器でフー
ド内部の空気を排気し、不要なオゾンは活性炭に吸着さ
せ、環境に配慮する。
Further, in order to improve the activation of the photocatalyst, the hood of the photocatalyst reaction unit (not shown) is made to be a closed type, and the ozonized air generated from a small-sized ozone generator can be introduced into the hood. It is also effective to do so. In this case, an ozone monitor is used to control the internal ozone concentration to an appropriate level. At the time of inspection, the ozone generator is stopped, the air inside the hood is exhausted by an exhaust fan, and unnecessary ozone is adsorbed on activated carbon, giving consideration to the environment.

【0019】このように構成された装置において、供給
ラインから原水を供給しつつモータ26の駆動により減
速機27及び回転用シャフト9を介して全ての回転円板
1〜6,7,8を回転させ、空中に配置した水銀ランプ
28〜39及び水中に配置した水銀ランプ28’〜3
9’を点灯させて回転円板1〜6に担持させた光触媒に
紫外線を照射し、更に、発振器42により各振動子函2
0〜25を超音波振動させ、必要に応じて小型のオゾン
発生装置から発生するオゾン化空気をフード内部に通導
させることで、装置を稼働させる。これにより、まず原
水流入口18から水槽17に入った原水が生物処理用円
板7に付着して生物処理された後、連結部を経て水槽1
0に入る。水槽10に流入した被処理水は、超音波振動
により濁質を分離された状態で回転円板1に付着して空
中に持ち出され、紫外線の照射を受ける。処理後の水は
連結部を経て次の水槽10に流れる。以下同様にして被
処理水は最終的に水槽16に至り、モニタ用円板8に付
着した状態で水質確認され、処理水として排出される。
このモニタ用円板8によるモニタリングで、更に、処理
が必要と判断される場合には、コック14を開き、処理
水を返送ライン40を経て原水流入口側にフィードバッ
クする。
In the apparatus configured as described above, while the raw water is supplied from the supply line, all the rotating disks 1 to 6, 7, and 8 are rotated by the driving of the motor 26 via the reduction gear 27 and the rotating shaft 9. Mercury lamps 28-39 placed in the air and mercury lamps 28'-3 placed in the water.
9 ′ is turned on to irradiate the photocatalyst carried on the rotating disks 1 to 6 with ultraviolet light.
The apparatus is operated by ultrasonically vibrating 0 to 25 and conducting ozonized air generated from a small-sized ozone generator into the hood as necessary. Thereby, first, the raw water entering the water tank 17 from the raw water inflow port 18 adheres to the biological treatment disk 7 and is subjected to biological treatment.
Enter 0. The water to be treated that has flowed into the water tank 10 adheres to the rotating disk 1 in a state where turbidity is separated by ultrasonic vibration, is taken out into the air, and is irradiated with ultraviolet rays. The water after the treatment flows to the next water tank 10 via the connecting portion. In the same manner, the water to be treated finally reaches the water tank 16, the water quality is checked with the water attached to the monitoring disk 8, and the water is discharged as treated water.
If it is determined by the monitoring by the monitoring disk 8 that further treatment is necessary, the cock 14 is opened and the treated water is fed back to the raw water inlet side through the return line 40.

【0020】ところで、従来のオゾンを用いた水処理の
場合、専用の反応装置が必要である。その発生装置は屋
内に格納する必要があるため、専用の建物が必要であ
る。更に、残留オゾン除去のため排オゾン処理装置が必
要になり、安全性の確保のため、これらを含めたイニシ
ャルコストは高い。これに比べて、光触媒反応装置にお
いては、反応槽、電源が必要であるが、オゾンを用いた
水処理のように格納する建物、空気源用のコンプレッ
サ、ブロワ、放電管の冷却装置などの相応に高額の付帯
設備が少ない。しかも部品点数が少ない分、メンテナン
スが楽になるという利点もある。
Incidentally, in the case of conventional water treatment using ozone, a dedicated reaction device is required. Since the generator must be stored indoors, a dedicated building is required. Further, an exhaust ozone treatment device is required for removing residual ozone, and the initial cost including these is high for ensuring safety. In contrast, a photocatalytic reactor requires a reaction tank and power supply, but it is necessary to use a storage facility such as ozone-based water treatment, an air source compressor, a blower, and a discharge tube cooling device. There are few expensive facilities. In addition, there is an advantage that maintenance becomes easy because the number of parts is small.

【0021】ところで、二酸化チタンによる光触媒の本
格的な研究は、太陽光を用いて水から酸素と水素を得、
それからエネルギを獲得するという(例えば、通産省の
サンシャイン計画)から始まった。有機物の酸化にも応
用できることが指摘されて以来、二酸化チタンはトルク
ロロエチレン、モノクロロ酢酸、PCB、ダイオキシン
類など難分解性有機塩素化合物を対象にした分解実験が
行われ、いずれについても高い分解能を示すことが示さ
れている。また、下水についても光触媒を使用し、その
効果を見たところ、COD、BOD及びTOCのいずれ
の値とも有意な減少を示してしる。また、二酸化チタン
をガラスなどの表面にコーティングする技術も既に確立
されている。この技術により本来粉末である二酸化チタ
ンの回収といった煩わしさを省くことができ、浄水処理
分野での連続運転が可能になった。現在まだ実装置とし
て稼働している例はないが、先に述べたような様々な利
点を持つことにより、21世紀初頭の主流になる高度処
理として期待されている技術である。
By the way, a full-scale study of a photocatalyst using titanium dioxide has been carried out by obtaining oxygen and hydrogen from water using sunlight.
It then began with gaining energy (eg, MITI's Sunshine Program). Since it was pointed out that titanium dioxide can be applied to the oxidation of organic substances, decomposition experiments were conducted on titanium dioxide, which is a difficult-to-decompose organic chlorine compound such as trichloroethylene, monochloroacetic acid, PCB, and dioxins. Is shown. In addition, a photocatalyst was used for sewage, and the effect was observed. As a result, all of COD, BOD and TOC showed a significant decrease. In addition, a technique for coating titanium dioxide on a surface of glass or the like has already been established. With this technology, the trouble of collecting titanium dioxide, which is originally a powder, can be eliminated, and continuous operation in the water purification treatment field has become possible. At present, there is no example of operating as a real device, but it is a technology expected as a mainstream advanced processing in the early 21st century due to the various advantages described above.

【0022】以下に本発明の光触媒反応装置の用途と効
果の関係を列記する。浄水処理において、フミン質の分
解に用いると、活性炭への吸着効果が増大し、トリハロ
メタン生成能が減少する。また、色度の減少効果が得ら
れる。同じく浄水処理における細菌類の不活性化に用い
ると、活性炭処理に不必要な細菌の除去により活性炭処
理の性能が安定する。また浄水処理におけるFe、Mn
の酸化に用いると、水質の改善効果が得られる。また、
活性炭処理と組み合わせれば色度低下につながる。同じ
く浄水処理における臭気物質の分解に用いると、水質の
向上によりオゾン処理施設が不要となる。また、浄水処
理におけるオゾン処理施設の代替に用いると、イニシャ
ルコストの低減により、水道料金の増加が抑えられる。
The relationship between the use and effect of the photocatalytic reactor of the present invention will be listed below. In the water purification treatment, when used for the decomposition of humic substances, the effect of adsorbing on activated carbon increases, and the ability to generate trihalomethane decreases. Further, an effect of reducing chromaticity can be obtained. Similarly, when used for inactivating bacteria in water purification treatment, the performance of activated carbon treatment is stabilized by removing bacteria unnecessary for activated carbon treatment. In addition, Fe, Mn in water purification treatment
When used for oxidation of water, an effect of improving water quality can be obtained. Also,
Combined with activated carbon treatment will lead to lower chromaticity. Similarly, when used for the decomposition of odorous substances in water purification treatment, an ozone treatment facility becomes unnecessary due to improvement in water quality. Further, when used as a substitute for an ozone treatment facility in water purification treatment, an increase in water charges can be suppressed due to a reduction in initial costs.

【0023】上記以外の用途として、逆浸透膜による海
水淡水化の前処理に用いると、膜のファウリングを起こ
し易い有機物質の分解により分離膜寿命が延長し、ラン
ニングコストの削減が可能となる。また、海水淡水化の
前処理における次亜臭素酸の発生に用いると、塩素剤使
用量の減少により、薬品補給量の減少を図ることができ
る。また、海水中の膜の性能劣化に係る細菌の繁殖抑制
に効果がある。更に、魚類飼育槽内の殺菌、殺藻による
衛生状態維持に用いることができる。更に、塩素剤の添
加を嫌う貯留水槽の殺菌装置として使用することもでき
る。更に、水中のダイオキシン類の分解装置として使用
することもできる。
When used for pretreatment of seawater desalination using a reverse osmosis membrane as an application other than the above, the life of the separation membrane is prolonged due to decomposition of an organic substance which easily causes fouling of the membrane, and the running cost can be reduced. . Further, when used for the generation of hypobromite in the pretreatment of seawater desalination, the amount of chemical replenishment can be reduced due to the decrease in the amount of chlorine agent used. Further, it is effective in suppressing the growth of bacteria related to the performance degradation of the membrane in seawater. Furthermore, it can be used for sterilization in a fish breeding tank and maintenance of hygiene by algicidation. Further, it can be used as a sterilizer for a storage water tank that refuses to add a chlorine agent. Further, it can be used as a device for decomposing dioxins in water.

【0024】[0024]

【発明の効果】本発明によれば、紫外線の照射を空気中
で行いながら、光触媒担持部分を回転させることによ
り、回転体の表面には常に水の薄膜が存在しており、紫
外線照射手段と光触媒との間に水を介在させるという処
理の基本形式は満たされている。その結果、紫外線が水
の薄膜を透過するだけであるので、水中で紫外線を照射
させる方式に比べ、光触媒の表面に到達するまでの紫外
線の強度の減衰が少ない。したがって、光触媒の担持さ
れた面と、被処理水との接触が十分に行われ、安定した
処理効果が得られる。そして、特に、請求項2に記載の
構成によると、より効率のよい光触媒の利用が可能にな
る。また、請求項3に記載の構成によると、常に光触媒
表面に付着しようとする微生物や濁質を水中の濁質を分
散状態に維持することで除去し、しかも比較的緩慢であ
るとされる光触媒の反応を加速することができる。ま
た、請求項4又は請求項5に記載の構成によると、生物
処理との併用で、処理効果を一層顕著なものとすること
ができる。
According to the present invention, a thin film of water is always present on the surface of the rotating body by rotating the photocatalyst-carrying portion while irradiating the ultraviolet light in the air. The basic form of the process of interposing water between the photocatalyst is satisfied. As a result, since the ultraviolet light only passes through the thin film of water, the intensity of the ultraviolet light before reaching the surface of the photocatalyst is less attenuated than in the method of irradiating the ultraviolet light in water. Therefore, the surface where the photocatalyst is supported and the water to be treated are sufficiently contacted, and a stable treatment effect is obtained. And especially according to the structure of Claim 2, more efficient use of a photocatalyst becomes possible. According to the third aspect of the present invention, microorganisms and turbid substances that are always attached to the surface of the photocatalyst are removed by maintaining the suspended substances in water in a dispersed state, and the photocatalyst is relatively slow. Reaction can be accelerated. Further, according to the configuration of claim 4 or claim 5, the treatment effect can be made more remarkable when used in combination with biological treatment.

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

【図1】本発明の一実施例に係る光触媒反応装置の平面
図である。
FIG. 1 is a plan view of a photocatalytic reactor according to one embodiment of the present invention.

【図2】同装置の断面図である。FIG. 2 is a sectional view of the device.

【図3】同装置を斜め下方より見た斜視図である。FIG. 3 is a perspective view of the same device as viewed obliquely from below.

【符号の説明】[Explanation of symbols]

1〜6 回転円板(回転体) 7 生物処理用円板(回転体) 8 モニタ用円板(回転体) 9 回転用シャフト 10〜17 水槽 18 原水流入口 19 処理水流出口 20〜25 超音波振動子函(超音振動手段) 26 モータ 27 減速機 28〜39 水銀ランプ(紫外線照射手段) 28’〜39’ 水銀ランプ(紫外線照射手段) 40 処理水返送ライン 41 切換コック 1-6 Rotating disk (rotating body) 7 Biological treatment disk (rotating body) 8 Monitor disk (rotating body) 9 Rotating shaft 10-17 Water tank 18 Raw water inlet 19 Treated water outlet 20-25 Ultrasonic wave Transducer box (supersonic vibration means) 26 Motor 27 Reduction gear 28-39 Mercury lamp (ultraviolet irradiation means) 28'-39 'Mercury lamp (ultraviolet irradiation means) 40 Treated water return line 41 Switching cock

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 被処理水を順次次の水槽に流動可能に互
いに連結された多数の水槽と、一部を水槽内の被処理水
に浸すように各水槽内に個々に設置され、光触媒を担持
した回転体と、各回転体に隣接して空中に配置した紫外
線照射手段とを備え、各水槽内の被処理水を回転体に付
着させ、その回転により空中に運び出し、空中で紫外線
を照射することにより処理するようにしたことを特徴と
する光触媒反応装置。
1. A large number of water tanks which are connected to each other so that water to be treated is successively flowed to the next water tank, and a plurality of water tanks are individually installed in each of the water tanks so as to be partially immersed in the water to be treated. A rotating body that is carried, and an ultraviolet irradiation means disposed in the air adjacent to each rotating body, the treatment water in each water tank is adhered to the rotating body, carried out into the air by its rotation, and irradiated with ultraviolet light in the air. A photocatalytic reaction device characterized in that the photocatalytic reaction device is processed by performing the following.
【請求項2】 水中に配置した紫外線照射手段を付加し
たことを特徴とする請求項1記載の光触媒反応装置。
2. The photocatalytic reactor according to claim 1, further comprising an ultraviolet irradiation means disposed in water.
【請求項3】 前記各水槽に被処理水を振動させる超音
波振動手段を設けたことを特徴とする請求項1又は2記
載の光触媒反応装置。
3. The photocatalytic reactor according to claim 1, wherein an ultrasonic vibration unit for vibrating the water to be treated is provided in each of the water tanks.
【請求項4】 前記多数の水槽の上流に、光触媒を担持
しない回転体を配した水槽を連結したことを特徴とする
請求項1、2又は3記載の光触媒反応装置。
4. The photocatalytic reaction apparatus according to claim 1, wherein a water tank having a rotating body not carrying a photocatalyst is connected upstream of the plurality of water tanks.
【請求項5】 最下流側の水槽と最上流側の水槽とを被
処理水返送ラインにより連結したことを特徴とする請求
項1、2、3又は4記載の光触媒反応装置。
5. The photocatalytic reactor according to claim 1, wherein the most downstream water tank and the most upstream water tank are connected by a treated water return line.
JP15060498A 1998-05-13 1998-05-13 Photocatalytic reactor Expired - Fee Related JP2907814B1 (en)

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JPH11319857A true JPH11319857A (en) 1999-11-24

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GB2356859A (en) * 1999-07-21 2001-06-06 Procter & Gamble Combined photocatalytic and ultrasonic degradation of organic contaminants
JP2002307057A (en) * 2001-04-12 2002-10-22 Haruo Ariyoshi Photocatalyst unit
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