JPH09253637A - Fluid treatment apparatus - Google Patents

Fluid treatment apparatus

Info

Publication number
JPH09253637A
JPH09253637A JP8064248A JP6424896A JPH09253637A JP H09253637 A JPH09253637 A JP H09253637A JP 8064248 A JP8064248 A JP 8064248A JP 6424896 A JP6424896 A JP 6424896A JP H09253637 A JPH09253637 A JP H09253637A
Authority
JP
Japan
Prior art keywords
fluid
catalyst
catalytic reaction
granular
treated
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
JP8064248A
Other languages
Japanese (ja)
Inventor
Takemi Oketa
岳見 桶田
Tomohide Matsumoto
朋秀 松本
Yu Kawai
祐 河合
Satoshi Furuta
聡 古田
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.)
Panasonic Holdings Corp
Original Assignee
Matsushita Electric Industrial Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Matsushita Electric Industrial Co Ltd filed Critical Matsushita Electric Industrial Co Ltd
Priority to JP8064248A priority Critical patent/JPH09253637A/en
Publication of JPH09253637A publication Critical patent/JPH09253637A/en
Pending legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To provide a fluid treatment apparatus not lowered in capacity even in the case of long-term use and developing stable purifying and sterilizing capacity regardless of a contamination state of a fluid. SOLUTION: A circulating means 19 and a catalytic reaction means 25 are arranged to a circulating passage 18 and an ultraviolet lamp 26 is arranged in the catalytic reaction means 25. The catalytic reaction means 25 is packed with granular titanium oxide 27 capable of coming into contact with the ultraviolet lamp and particles of granular titanium oxide 27 are stirred by the flow of circulating water to be allowed to collide with each other to purify and sterilize circulating water while peeling the substance deposited on the surfaces of the particles to always obtain stable purifying capacity.

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】本発明は業務用もしくは家庭
用の水、空気などの流体の浄化、殺菌に関するものであ
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to purification or sterilization of a fluid such as water or air for business or household use.

【0002】[0002]

【従来の技術】従来の流体処理装置は、例えば水の浄化
の場合では、図3に示すように、循環流路に光触媒と光
源とを有する浄化殺菌筒を設け、触媒反応によって水中
の浄化及び殺菌を行うものがあった(例えば、特開平7
ー214053号公報)。同図において、1は浴槽で、
循環流路4に循環ポンプと浄化殺菌筒6と三方弁7、二
方弁8を備えている。浄化殺菌筒6の内部には、紫外線
ランプ9、光触媒10と多孔質セラミック11を備えて
いる。また、多孔質セラミック11の洗浄を行うため
に、バイパス流路13、排水路14、三方弁7、二方弁
15を備えている。紫外線ランプ9への通電は制御装置
12で行っている。また、16は電源を示し、矢印は水
の流れを示す。
2. Description of the Related Art In a conventional fluid treatment apparatus, for example, in the case of purifying water, as shown in FIG. 3, a purifying and sterilizing cylinder having a photocatalyst and a light source is provided in a circulation passage to purify and purify water by a catalytic reaction. Some have been sterilized (for example, Japanese Patent Laid-Open No. Hei 7
-214053). In the figure, 1 is a bathtub,
The circulation flow path 4 is equipped with a circulation pump, a purification / sterilization cylinder 6, a three-way valve 7, and a two-way valve 8. An ultraviolet lamp 9, a photocatalyst 10 and a porous ceramic 11 are provided inside the purification / sterilization cylinder 6. Further, in order to clean the porous ceramic 11, a bypass flow path 13, a drainage path 14, a three-way valve 7, and a two-way valve 15 are provided. The control device 12 energizes the ultraviolet lamp 9. Further, 16 indicates a power source, and arrows indicate the flow of water.

【0003】この構成において、動作を説明すると、循
環ポンプ5の働きによって、浴槽1の水は吸い込み口2
から循環流路4を通って、浄化殺菌筒6内に入る。浄化
殺菌筒6内において、光触媒10は紫外線ランプ9より
照射された紫外線によって水中の殺菌及び臭気成分の分
解を行う。その後、光触媒10の外部の多孔質セラミッ
ク11に繁殖させた微生物の働きにより、残りの有機物
の分解を行うものである。この結果、清浄な水が得られ
るものである。
The operation of this structure will be described. The circulation pump 5 works to suck the water in the bathtub 1 into the suction port 2.
Through the circulation channel 4 into the purifying / sterilizing cylinder 6. In the purification and sterilization cylinder 6, the photocatalyst 10 sterilizes the water and decomposes the odorous components by the ultraviolet rays emitted from the ultraviolet lamp 9. After that, the remaining organic substances are decomposed by the action of the microorganisms propagated on the porous ceramic 11 outside the photocatalyst 10. As a result, clean water is obtained.

【0004】[0004]

【発明が解決しようとする課題】しかしながら上記のよ
うな従来の流体処理装置では以下のような課題があっ
た。
However, the conventional fluid treatment apparatus as described above has the following problems.

【0005】(1)被処理流体の浄化を続けると、触媒
の表面に流体中の懸濁物質が堆積し、触媒表面での酸化
還元反応の効果が低減し、その結果徐々に浄化、殺菌性
能が低下してきて、最終的には触媒の浄化、殺菌能力が
なくなる。
(1) When the purification of the fluid to be treated is continued, suspended substances in the fluid are deposited on the surface of the catalyst, and the effect of the redox reaction on the surface of the catalyst is reduced. As a result, the purification and sterilization performance is gradually increased. Will eventually decrease, and eventually the catalyst's purification and sterilization capacity will be lost.

【0006】(2)微生物を繁殖させ、この働きにより
水中の有機物の分解を行っているので、周囲の温度変
化、微生物の栄養源の質的、量的変化などの環境要因の
変化によって微生物の浄化活性が変化するので、周囲の
環境が変化した場合には安定した浄化性能が得られな
い。
(2) Since microorganisms are propagated and organic substances in water are decomposed by this action, changes in environmental factors such as ambient temperature changes, qualitative and quantitative changes in nutrient sources of microorganisms cause changes in microorganisms. Since the purification activity changes, stable purification performance cannot be obtained when the surrounding environment changes.

【0007】(3)被処理流体中に紫外線ランプを備え
る構成なので、長期間流体の処理を続けると、紫外線ラ
ンプ上に有機物などが付着、堆積していき、紫外線ラン
プから光触媒へ照射できる紫外線量が低下する。よっ
て、光触媒における酸化還元反応が減少するので、浄
化、殺菌能力が低下する。
(3) Since the fluid to be processed is provided with an ultraviolet lamp, if the fluid is continuously processed for a long period of time, organic substances and the like will adhere and accumulate on the ultraviolet lamp, and the amount of ultraviolet light that can be irradiated from the ultraviolet lamp to the photocatalyst. Is reduced. Therefore, since the redox reaction in the photocatalyst is reduced, the purifying and sterilizing ability is lowered.

【0008】(4)被処理流体中に懸濁物質が多く、紫
外線透過率が低い場合には、光触媒への紫外線照射量が
減少することにより、触媒表面で酸化還元反応が抑制さ
れ、その結果、浄化、殺菌性能が低下する。
(4) When there are many suspended substances in the fluid to be treated and the UV transmittance is low, the amount of UV irradiation to the photocatalyst is reduced, so that the redox reaction is suppressed on the catalyst surface, and as a result, , Purification and sterilization performance will be reduced.

【0009】(5)微生物を繁殖させる微生物担体の近
傍に光触媒を設け、紫外線を照射して水の浄化を行うこ
とにより、装置がコンハ゜クトとなり、かつ微生物の有機物分解
効果との相乗効果により清浄な水が得られるが、特に被
処理水中に有機物濃度が高い場合や難分解性の物質が存
在する場合にはこれらの物質を分解するのに時間がかか
る。
(5) By providing a photocatalyst in the vicinity of a microbial carrier for propagating microorganisms and irradiating it with ultraviolet rays to purify water, the apparatus becomes compact, and a synergistic effect with the decomposition effect of microorganisms on organic matter results in cleanliness. Although water is obtained, it takes a long time to decompose these substances, particularly when the concentration of organic substances in the water to be treated is high or when a hardly decomposable substance is present.

【0010】[0010]

【課題を解決するための手段】本発明は上記課題を解決
するため、流路に被処理流体を搬送する搬送手段と、内
部に被処理流体中の物質を変化させる触媒を充填した触
媒反応手段と、触媒を撹拌する撹拌手段を設けた構成と
してある。
In order to solve the above-mentioned problems, the present invention solves the above-mentioned problems by carrying means for carrying a fluid to be treated into a flow passage and catalytic reaction means filled with a catalyst for changing a substance in the fluid to be treated. And a stirring means for stirring the catalyst.

【0011】上記構成からなる流体処理装置は、流体を
流体搬送手段により触媒反応手段内に送り込み、撹拌手
段によって撹拌した触媒と反応させることになる。つま
り、流体を触媒反応手段内に送り込み、触媒と反応させ
る際に触媒を撹拌させておくことで、触媒同士を衝突さ
せ、表面に付着した有機物を剥離することになり、長期
間浄化、殺菌性能を維持することができる。
In the fluid processing apparatus having the above structure, the fluid is fed into the catalytic reaction means by the fluid carrying means and reacted with the catalyst stirred by the stirring means. In other words, by feeding the fluid into the catalyst reaction means and stirring the catalyst when reacting with the catalyst, the catalysts collide with each other and the organic substances adhering to the surface are peeled off. Can be maintained.

【0012】[0012]

【発明の実施の形態】本発明の請求項1にかかる流体処
理装置は、流路に被処理流体を搬送する搬送手段と、内
部に被処理流体中の物質を変化させる触媒を充填した触
媒反応手段と、触媒を撹拌する撹拌手段とを設けて構成
してあり、流体を触媒反応手段内に送り込み、触媒と反
応させる際に触媒を撹拌させておくことで、触媒同士を
衝突させ、表面に付着した有機物を剥離することがで
き、長期間浄化、殺菌性能を維持することができる。
DESCRIPTION OF THE PREFERRED EMBODIMENTS A fluid processing apparatus according to claim 1 of the present invention is a catalytic reaction in which a transport means for transporting a fluid to be treated into a flow channel and a catalyst for changing a substance in the fluid to be treated are filled inside. Means and stirring means for stirring the catalyst are provided, and by feeding the fluid into the catalyst reaction means and stirring the catalyst when reacting with the catalyst, the catalysts are caused to collide with each other, and The attached organic matter can be peeled off, and purification and sterilization performance can be maintained for a long period of time.

【0013】本発明の請求項2にかかる流体処理装置
は、流体を貯蔵する貯蔵手段と、前記貯蔵手段に循環流
路を接合し、前記循環流路に被処理流体を循環する循環
手段と、被処理流体中の物質を変化する触媒を充填した
触媒反応手段と、前記触媒を撹拌する撹拌手段を備えた
構成としてあり、貯蔵手段内の流体を循環手段によって
循環させて、触媒反応手段を何度も通過させることで、
内部の撹拌された触媒と流体内の物質とが接触する確立
を向上することができ、流体中の物質の浄化または細菌
の殺菌能力を向上することができる。
According to a second aspect of the present invention, there is provided a fluid treatment device, which comprises a storage means for storing a fluid, a circulation means for joining a circulation passage to the storage means, and a circulation means for circulating the fluid to be treated in the circulation passage. The catalyst reaction means filled with a catalyst for changing the substance in the fluid to be treated and the stirring means for stirring the catalyst are provided, and the fluid in the storage means is circulated by the circulation means to determine the catalytic reaction means. By also passing through,
It is possible to improve the contact between the agitated catalyst inside and the substance in the fluid, and it is possible to improve the purification ability of the substance in the fluid or the sterilizing ability of bacteria.

【0014】本発明の請求項3にかかる流体処理装置
は、前記触媒反応手段の流体の流入側と流出側に触媒流
出防止手段を設けてあり、流出防止手段が流体は通過さ
せるが、触媒は触媒反応手段内に抑留させるので、触媒
が触媒反応手段から流出するのを防止できる。
According to a third aspect of the present invention, there is provided a catalyst outflow prevention means on the fluid inflow side and the fluid outflow side of the catalyst reaction means, and the outflow prevention means allows the fluid to pass through, but the catalyst does not Since the catalyst is retained in the catalytic reaction means, it is possible to prevent the catalyst from flowing out of the catalytic reaction means.

【0015】発明の請求項4にかかる流体処理装置は、
前記触媒を粒状としてあり、被処理水中の単位時間当た
りの接触時間を多くでき、また、撹拌手段によって粒状
の触媒を撹拌しながら被処理流体と接触させることで、
触媒の表面全体を利用して被処理流体中の物質と効率よ
く反応させることができる。
A fluid processing apparatus according to claim 4 of the invention is
The catalyst is in the form of particles, the contact time per unit time in the water to be treated can be increased, and by bringing the granular catalyst into contact with the fluid to be treated while stirring,
The entire surface of the catalyst can be used to efficiently react with the substance in the fluid to be treated.

【0016】本発明の請求項5、6にかかる流体処理装
置は、前記触媒反応手段の内部に紫外線照射手段を設け
ると共に粒状の光触媒を充填し、粒状の光触媒を撹拌手
段で撹拌する構成としてあり、光触媒を撹拌手段で撹拌
し、紫外線照射手段の近傍で流体と接触させることで、
紫外線照射手段の表面に付着した物質を剥離しながら被
処理水中の物質の分解を行うことができる。よって、安
定した浄化性能をえることができる。さらに、触媒表面
への紫外線照射量が増加し、触媒表面にヒドロキシラジ
カルなどの活性酸素および光触媒表面に発生したホール
を効果的に生成し、酸化還元反応を起こさせることがで
きる。つまり、流体中の物質を効果的に酸化することが
できるので、流体中の難分解性有機物の分解速度を速め
ることができる。
The fluid treatment apparatus according to the fifth and sixth aspects of the present invention is configured such that an ultraviolet irradiation means is provided inside the catalytic reaction means, a granular photocatalyst is filled, and the granular photocatalyst is stirred by the stirring means. By stirring the photocatalyst with the stirring means and bringing it into contact with the fluid in the vicinity of the ultraviolet irradiation means,
The substance in the water to be treated can be decomposed while peeling off the substance adhering to the surface of the ultraviolet irradiation means. Therefore, stable purification performance can be obtained. Further, the irradiation amount of ultraviolet rays on the catalyst surface is increased, active oxygen such as hydroxy radicals and holes generated on the photocatalyst surface are effectively generated on the catalyst surface, and the redox reaction can be caused. That is, since the substance in the fluid can be effectively oxidized, the decomposition rate of the hardly decomposable organic substance in the fluid can be increased.

【0017】本発明の請求項7、8にかかる流体処理装
置は、前記光触媒反応手段内に金属元素を触媒表面に担
持した構成としてあり、被処理流体と光触媒との反応を
効果的に行うことができる。すなわち光触媒上に担持し
た金属元素と被処理流体が接触することにより、被処理
水中の物質の活性化エネルギーを低くすることができ、
被処理流体中の物質の酸化還元に必要なエネルギーを小
さくすることができる。よって、光触媒上に発生したヒ
ドロキシラジカルなどの活性酸素種およびホールとの反
応速度を向上することができる。さらに、金属元素が流
体中にイオン状態で溶けだすことにより、金属の微量作
用(オリゴダイナミック作用)により、流体中の細菌な
どの微生物を死滅することができ、殺菌性能を向上でき
る。これらの効果により浄化、殺菌性能を向上すること
ができる。
The fluid treatment apparatus according to claims 7 and 8 of the present invention has a structure in which a metal element is supported on the surface of the catalyst in the photocatalytic reaction means, and the reaction between the fluid to be treated and the photocatalyst is effectively performed. You can That is, by contacting the metal element carried on the photocatalyst and the fluid to be treated, the activation energy of the substance in the water to be treated can be lowered,
The energy required for redox of the substance in the fluid to be processed can be reduced. Therefore, the reaction rate with active oxygen species such as hydroxy radicals generated on the photocatalyst and holes can be improved. Furthermore, when the metal element begins to dissolve in the fluid in an ionic state, microbeads of the metal (oligodynamic action) can kill microorganisms such as bacteria in the fluid and improve sterilization performance. Purification and sterilization performance can be improved by these effects.

【0018】本発明の請求項9にかかる流体処理装置
は、被処理流体および触媒を加熱する温度調節手段を配
管中に設けてあり、流体と触媒の温度を上げて浄化を行
うことができるので、浄化、殺菌速度を向上させること
ができる。つまり、加熱手段により被処理流体及び触媒
の温度を高めることにより、被処理流体中の物質に熱エ
ネルギーを加え、触媒が物質を分解するのに必要なエネ
ルギー量を下げることで、通常よりも迅速に有機物の分
解を行うことができる。
In the fluid treatment apparatus according to the ninth aspect of the present invention, the temperature adjusting means for heating the fluid to be treated and the catalyst is provided in the pipe, and the temperature of the fluid and the catalyst can be raised for purification. , Purification, sterilization speed can be improved. In other words, by increasing the temperature of the fluid to be treated and the catalyst by the heating means, heat energy is added to the substance in the fluid to be treated, and the amount of energy required for the catalyst to decompose the substance is lowered, so that it is faster than usual. It can decompose organic substances.

【0019】本発明の請求項10にかかる流体処理装置
は、前記配管または前記循環流路に濾過手段を設けてあ
り、流体中の大きい粒子し除去し、下流側の触媒反応手
段内に大きい粒子の少ない流体を送り込むことができる
ので、触媒反応手段内の触媒の流出防止手段の目詰まり
を防止することができる。
In the fluid treatment apparatus according to the tenth aspect of the present invention, the pipe or the circulation passage is provided with a filtering means for removing large particles in the fluid and removing the large particles in the catalytic reaction means on the downstream side. Since a fluid with a small amount can be sent in, it is possible to prevent clogging of the catalyst outflow prevention means in the catalyst reaction means.

【0020】本発明の請求項11にかかる流体処理装置
は、前記濾過手段の洗浄手段を備えた構成としてあり、
長期間の使用により濾過手段内の濾材表面及び隙間に有
機物の粒子が堆積した場合、洗浄手段を動作させ、濾過
手段内の濾材を洗浄し、濾材の表面に堆積した有機物な
どを排出するので、濾過手段の粒子除去性能を維持し、
圧力損失の上昇を抑えることができる。
A fluid treatment apparatus according to an eleventh aspect of the present invention has a configuration including a cleaning means for the filtering means,
When particles of organic matter are deposited on the surface of the filter medium and the gaps in the filter means due to long-term use, the cleaning means is operated to wash the filter medium in the filter means and discharge the organic matter deposited on the surface of the filter medium. Maintains the particle removal performance of the filtration means,
An increase in pressure loss can be suppressed.

【0021】本発明の請求項12にかかる流体処理装置
は、前記濾過手段の上流方向に流体中の物質を凝集する
凝集手段を設けてあり、流体中の粒子径を大きくして濾
過手段によって除去することで流体の紫外線透過率を向
上することができ、光触媒表面に到達する紫外線量を多
くすることができる。従って安定して酸化還元反応を起
こすことができる。
The fluid treatment apparatus according to claim 12 of the present invention is provided with an aggregating means for aggregating the substance in the fluid in the upstream direction of the filtering means, and the particle diameter in the fluid is increased to remove it by the filtering means. By doing so, the ultraviolet transmittance of the fluid can be improved, and the amount of ultraviolet rays reaching the photocatalyst surface can be increased. Therefore, a redox reaction can be stably caused.

【0022】以下本発明の実施例を図1を参照して説明
する。図1に本発明の実施例における流体処理装置の構
成図を示す。尚、処理する流体として入浴後の浴槽水を
用いた。同図において、浴槽17内には浴槽水が入って
いる。浴槽17には循環流路18がつながっており、循
環流路18には浴槽17内の浴槽水を循環する搬送ある
いは循環手段となる循環ポンプ19と、浴槽水の大きい
懸濁物質を除去する濾過装置20と、その下流方向に触
媒反応手段25と加熱手段29を配置している。濾過手
段20の内部には濾材21と濾材21を支持する濾材支
持板22を備えている。また、濾過手段20には濾材の
上流方向に凝集手段となるアルミニウム電極23とステ
ンレス電極24が備わっており、アルミニウム電極23
を陽極、ステンレス電極24を陰極として通電を行って
いる。
An embodiment of the present invention will be described below with reference to FIG. FIG. 1 shows a block diagram of a fluid processing apparatus in an embodiment of the present invention. The bath water after bathing was used as the fluid to be treated. In the figure, bathtub water is contained in the bathtub 17. A circulation flow path 18 is connected to the bathtub 17. The circulation flow path 18 is a circulation pump 19 that serves as a transfer or circulation means for circulating the bath water in the bath 17, and a filtration that removes large suspended substances in the bath water. The device 20, and the catalytic reaction means 25 and the heating means 29 are arranged downstream thereof. Inside the filtering means 20, a filter medium 21 and a filter medium support plate 22 for supporting the filter medium 21 are provided. Further, the filtering means 20 is provided with an aluminum electrode 23 and a stainless steel electrode 24 which serve as aggregating means in the upstream direction of the filtering material.
Is used as an anode, and the stainless steel electrode 24 is used as a cathode.

【0023】触媒反応手段25には流体の入り口側と出
口側に光触媒の粒状酸化チタン27の流出を防止する流
出防止板28が備わっており、中心付近に紫外線照射手
段となる紫外線ランプ26を備えている。さらに、濾過
手段20の洗浄を行うための三方弁30、31及び二方
弁33と配管34、35が備えられている。電極23、
24と紫外線ランプ26、温度調節手段となる加熱装置
29及び三方弁30、31、二方弁33のON−OFF
制御及び開閉の制御はコントローラー36によって行っ
ている。矢印は浴槽水の流れを示している。
The catalytic reaction means 25 is provided with an outflow prevention plate 28 for preventing the outflow of the granular titanium oxide 27 of the photocatalyst on the inlet side and the outlet side of the fluid, and an ultraviolet lamp 26 serving as an ultraviolet irradiation means is provided near the center. ing. Further, three-way valves 30, 31 and two-way valve 33 and pipes 34, 35 for cleaning the filtering means 20 are provided. Electrode 23,
ON / OFF of 24 and ultraviolet lamp 26, heating device 29 serving as temperature adjusting means, three-way valves 30, 31 and two-way valve 33.
The control and opening / closing control are performed by the controller 36. The arrows indicate the flow of bath water.

【0024】なお、濾過手段20内部の粒状濾材21は
圧力損失と濾過性能のことを考慮にいれて、粒子径0.
2〜0.8mmの多孔質のセラミック製の比重が3.5以
上のものを用いている。また、本実施例では濾材支持板
22及び流出防止板28にポリメチルメタアクリレート
製の多孔質板を用いているが、耐食性、通水性、洗浄性が
良く強度が高いものが望まれるので、ポリメチルメタア
クリレートのほかにABS、ポリエチレン、ポリプロピ
レン、セラミックなどをもちいてもよい。また、触媒反
応手段25内には粒子径0.2〜0.8、比重約2.0
の結晶構造がアナターゼ型の酸化チタンを用いた。
The granular filter material 21 inside the filtering means 20 has a particle diameter of 0.
A porous ceramic having a specific gravity of 2 to 0.8 mm and a specific gravity of 3.5 or more is used. Further, in this embodiment, a porous plate made of polymethylmethacrylate is used for the filter medium support plate 22 and the outflow prevention plate 28. However, since it is desired that the plate has good corrosion resistance, water permeability, cleanability and high strength, In addition to methyl methacrylate, ABS, polyethylene, polypropylene, ceramics, etc. may be used. In the catalytic reaction means 25, the particle diameter is 0.2 to 0.8 and the specific gravity is about 2.0.
Anatase type titanium oxide having a crystal structure of was used.

【0025】また、本実施例では光触媒としてTiO2
を用いたが、そのほかにSrTiO2、ZnO、などを
用いても良い。さらに、本実施例の粒状の光触媒はシリ
カアルミナセラミックに酸化チタンを練り込んで焼成し
たものを用いているが、光触媒が粒子の表面に存在する
ものであればよいので、例えば、表面を酸化チタンなど
の光触媒でコーティングしたものや酸化チタンなどの光
触媒を粒状にしたものなどでもよい。また、浴槽水中の
有機物を凝集するために陽極にアルミニウム電極を用い
て通電を行ったが、凝集作用のある物質を生成できるも
のであればよいので、アルミニウム以外に例えば鉄、銅
などを用いてもよい。
In this embodiment, TiO 2 is used as a photocatalyst.
Although SrTiO 2 , ZnO, or the like may be used instead. Furthermore, although the granular photocatalyst of this embodiment is obtained by kneading and firing titanium oxide in silica-alumina ceramic, any photocatalyst may be present on the surface of the particles. It may be coated with a photocatalyst such as or a granular photocatalyst such as titanium oxide. Further, in order to agglomerate the organic matter in the bath water, electricity was conducted using an aluminum electrode as an anode, but any substance capable of producing a substance having an aggregating action may be used. Good.

【0026】上記構成において、次に本実施例の作用、
動作について説明する。浴槽17内の浴槽水は、循環ポ
ンプ19の働きにより流路18を通って、濾過手段20
を通過した後、触媒反応手段25に入る。触媒反応手段
25内では紫外線ランプ26により励起した紫外線を粒
状酸化チタン27が受ける。この粒状酸化チタン27は
浴槽水の流れにより触媒反応手段25内で攪拌される。
この粒状酸化チタン27の表面近傍には水との反応でで
きたヒドロキシラジカルなどの活性酸素や、紫外線を受
けたことによるホールを存在させることができる。ま
た、入浴により、浴槽17内の浴槽水中には人体から剥離
した角質、皮脂、及び細菌などが混入する。この混入した
角質により浴槽水の濁度が上昇する。入浴により混入し
た角質の平均粒径は30μm前後あり、この程度の粒子
であれば濾過手段20内の粒状濾材21によって除去す
ることができる。
In the above structure, the operation of this embodiment will be described next.
The operation will be described. The bath water in the bath 17 passes through the flow path 18 by the action of the circulation pump 19 and the filtering means 20.
And then enters the catalytic reaction means 25. In the catalytic reaction means 25, the particulate titanium oxide 27 receives the ultraviolet light excited by the ultraviolet lamp 26. The granular titanium oxide 27 is agitated in the catalytic reaction means 25 by the flow of bath water.
In the vicinity of the surface of the granular titanium oxide 27, active oxygen such as hydroxy radicals formed by the reaction with water and holes caused by receiving ultraviolet rays can be present. Further, due to bathing, keratin, sebum, bacteria and the like exfoliated from the human body are mixed in the bath water in the bath 17. Due to this mixed keratin, the turbidity of bath water increases. The average particle size of the keratin mixed by the bath is around 30 μm, and particles of this size can be removed by the granular filter material 21 in the filtering means 20.

【0027】しかし、浴槽水中の細菌が角質、皮脂を利用
して増殖することにより、浴槽水に臭いが発生し、増殖し
た細菌により、濁りが激しくなる。そこで、触媒反応手段
25内の光触媒27の表面に発生したヒドロキシラジカ
ルなどの活性酸素および粒状酸化チタン27表面のホー
ルと臭い成分、細菌が酸化還元反応を起こし、臭気成分を
酸化分解し、濁りのもととなる細菌を殺菌、分解すること
により、浴槽水の臭いと濁りの上昇を抑制する。よって、
浴槽水の臭いや濁りの上昇を抑制することができる。し
かし、触媒反応手段25内の粒状酸化チタン27が流動
性がない場合、有機物含量の高い水を浄化長期間行う
と、水中に存在する角質や皮脂と溶存するカルシウムな
どの金属元素と結合してできた湯垢及び細菌などが酸化
チタンの表面に堆積し、その結果徐々に触媒活性を失
い、最終的には触媒のほとんどの部分がこれらの物質に
覆われ、活性を失ってしまう。
However, when bacteria in the bath water grow by utilizing keratin and sebum, an odor is generated in the bath water, and the grown bacteria cause turbidity. Therefore, active oxygen such as hydroxy radicals generated on the surface of the photocatalyst 27 in the catalytic reaction means 25 and holes on the surface of the granular titanium oxide 27 and odorous components and bacteria cause an oxidation-reduction reaction to oxidatively decompose the odorous components, resulting in turbidity. By sterilizing and decomposing the underlying bacteria, the increase in odor and turbidity of bath water is suppressed. Therefore,
It is possible to suppress an increase in odor and turbidity of bath water. However, when the granular titanium oxide 27 in the catalytic reaction means 25 has no fluidity, if water having a high organic matter content is purified for a long period of time, it will bond with metal elements such as calcium dissolved in keratin and sebum present in water. The resulting scales and bacteria deposit on the surface of titanium oxide, and as a result, the catalytic activity is gradually lost, and eventually most of the catalyst is covered with these substances and loses the activity.

【0028】しかしながら本実施例の構成で水の浄化を
行うと、触媒反応手段25内で粒状酸化チタン26が撹
拌されることにより、粒状酸化チタン27同士が回転し
ながら衝突を繰り返すので、表面に堆積した角質や湯垢
や細菌などが剥離される。よって、酸化チタン27の表
面全体は常に紫外線を受けることができ、酸化還元反応
を起こすことができるので、長期間浴槽17内の浴槽水
の臭い成分や細菌を分解しかつ細菌の増殖を抑制でき
る。さらに、本実施例ではシリカアルミナセラミックに
酸化チタンを練り込んだものを焼成して粒状に成型して
いるので、粒子同士のが衝突による酸化チタンのコーテ
ィング層の剥離がない。むしろ、焼成温度、などを調整
して粒子の強度を柔かくすることによって、長時間微量
ずつ削れることにより、付着物のない表面を露出するこ
とができるので、光触媒の浄化、殺菌性能を維持するこ
とができる。
However, when water is purified by the structure of this embodiment, the granular titanium oxide 26 is agitated in the catalytic reaction means 25, so that the granular titanium oxides 27 repeatedly rotate and collide with each other. Accumulated keratin, scale and bacteria are exfoliated. Therefore, the entire surface of the titanium oxide 27 can always receive ultraviolet rays and can cause an oxidation-reduction reaction, so that the odorous components and bacteria of the bath water in the bath 17 can be decomposed and the growth of bacteria can be suppressed. . Further, in this embodiment, since the silica-alumina ceramic in which titanium oxide is kneaded is fired to be formed into particles, the titanium oxide coating layer is not peeled off due to collision between particles. Rather, by adjusting the calcination temperature, etc. to soften the strength of the particles, it is possible to expose the surface without deposits by scraping a small amount for a long time, so that the purification and sterilization performance of the photocatalyst should be maintained. You can

【0029】また、循環流路18に循環手段19と触媒
反応手段25を設けることにより、浴槽17内の浴槽水
は触媒反応手段25および浴槽17内を循環することが
できる。よって、触媒反応手段25内に浴槽水中の臭い
成分や細菌が何度も通過することになり、触媒反応手段
25内で紫外線ランプ26によって紫外線を照射され、
水との触媒反応によって発生したヒドロキしラジカルの
ような活性酸素種及び、紫外線の照射により触媒27上
に発生したホールとの接触回数を増すことができる。よ
って、浴槽水中の臭い成分や細菌の分解及び殺菌効率を
向上することができる。
By providing the circulation means 19 and the catalytic reaction means 25 in the circulation passage 18, the bath water in the bath 17 can circulate in the catalytic reaction means 25 and the bath 17. Therefore, the odorous components and bacteria in the bath water pass through the catalytic reaction means 25 many times, and the ultraviolet rays are irradiated by the ultraviolet lamp 26 in the catalytic reaction means 25,
It is possible to increase the number of times of contact with active oxygen species such as hydroxyl radicals generated by the catalytic reaction with water and the holes generated on the catalyst 27 by irradiation of ultraviolet rays. Therefore, the decomposition and sterilization efficiency of odorous components and bacteria in the bath water can be improved.

【0030】また、触媒反応手段25内に粒状酸化チタ
ン27を充填し、攪拌しながら浴槽水の浄化を行うと、粒
状酸化チタン27が触媒反応手段25から流出しないよ
うにするために攪拌速度が制限され、粒状酸化チタン2
7との接触時間が短くなる。そのため、十分な分解及び
殺菌能力を得るためには、触媒反応手段25の容積を大
きくする必要がある。
Further, when the granular titanium oxide 27 is filled in the catalytic reaction means 25 and the bath water is purified while stirring, the stirring speed is set to prevent the granular titanium oxide 27 from flowing out of the catalytic reaction means 25. Limited, granular titanium oxide 2
The contact time with 7 becomes shorter. Therefore, in order to obtain sufficient decomposition and sterilization ability, it is necessary to increase the volume of the catalytic reaction means 25.

【0031】一方、撹拌速度を上げると粒状酸化チタン
27の触媒反応手段25内に粒状酸化チタン27が循環
流路18に漏れだし、弁30、31、33や循環ポンプ
19に詰まり、故障や誤動作の原因となる。そこで、粒
状酸化チタン27の流出を防止する流出防止板28を設
けたことにより、浴槽水の循環流量を上げた場合でも、
触媒27の巻き上がりによる粒状酸化チタン27の循環
流路18及び浴槽17への流出を防止することができ
る。よって、配管中に漏れ出た粒状酸化チタン27によ
る循環ポンプ19や弁30、31、33の詰まり、故障
をなくすことができる。さらに、流速増加による粒状酸
化チタン27の流出を気にすることなく循環流量を上昇
することができるので、触媒反応手段25内の粒状酸化
チタン27近傍に発生したヒドロキシラジカルなどの活
性酸素種及び粒状酸化チタン27表面上に形成したホー
ルと浴槽水中の臭い成分及び細菌との単位時間当たりの
接触効率を向上することができる。よって、浴槽水中の
臭い成分の分解及び細菌の分解、殺菌が効果的に行うこ
とができ、触媒反応手段25を小型化できる。
On the other hand, when the stirring speed is increased, the granular titanium oxide 27 leaks into the circulation passage 18 into the catalytic reaction means 25 of the granular titanium oxide 27, and the valves 30, 31, 33 and the circulation pump 19 are clogged, causing malfunction or malfunction. Cause of. Therefore, by providing the outflow prevention plate 28 for preventing the outflow of the granular titanium oxide 27, even when the circulating flow rate of the bath water is increased,
It is possible to prevent the granular titanium oxide 27 from flowing out to the circulation flow path 18 and the bath 17 due to the rolling up of the catalyst 27. Therefore, it is possible to prevent the circulation pump 19 and the valves 30, 31, 33 from being clogged and broken by the granular titanium oxide 27 leaking into the pipe. Furthermore, since the circulation flow rate can be increased without having to worry about the outflow of the granular titanium oxide 27 due to the increase in the flow velocity, active oxygen species such as hydroxy radicals and granular particles generated in the vicinity of the granular titanium oxide 27 in the catalytic reaction means 25 and the granular particles. It is possible to improve the contact efficiency per unit time between the holes formed on the surface of titanium oxide 27 and the odorous components and bacteria in the bath water. Therefore, the odorous components in the bath water and the bacteria can be effectively decomposed and sterilized, and the catalytic reaction means 25 can be downsized.

【0032】なお、流失防止板として本実施例では0.
1mm前後の開孔径の多孔質板を用いているが、粒状酸化
チタン27の粒子径よりも小さい開孔径のものを選べば
よく、圧力損失のことを考慮にいれて、粒子径の約1/
2の開孔径のものを使用している。また、流出防止板2
8の素材は表面が耐食性、通水性、洗浄性がよく、強度が
高いものを選ぶ必要があるので、本実施例では高分子樹
脂のポリメチルメタアクリレート製の多孔質板を使用し
ている。
It should be noted that, in this embodiment, as a washout prevention plate,
Although a porous plate having an opening diameter of about 1 mm is used, one having an opening diameter smaller than the particle diameter of the granular titanium oxide 27 may be selected, and considering the pressure loss, about 1 / of the particle diameter is used.
A hole diameter of 2 is used. In addition, the outflow prevention plate 2
Since it is necessary to select the material of No. 8 whose surface has good corrosion resistance, water permeability, cleanability and high strength, a porous plate made of polymethylmethacrylate which is a polymer resin is used in this embodiment.

【0033】また、触媒反応手段25内の粒状酸化チタ
ン27の形状が粒状なので、単位体積当たりの表面積を
最大にできる。よって、循環ポンプ19によって送り込
まれた浴槽水との接触面積が大きくなり、粒状酸化チタ
ン27の表面積が大きくなると紫外線ランプ26によっ
て発生した紫外線を受ける面積も大きくなるので、表面
にヒドロキシラジカルなどの活性酸素やホールを多く生
成できる。よって、浴槽水中の臭気物質及び細菌とこれ
らの物質の接触が増え、単位時間当たり浴槽水中の臭気
成分及び細菌の分解や殺菌性能を向上することができ
る。なお、粒状酸化チタン27を撹拌しながら紫外線を
受け、浴槽水と接触することで、粒状酸化チタン27の
表面全体を利用して浄化、殺菌を行っているので、さら
に効果的に浴槽水の浄化殺菌を行うことができる。
Further, since the granular titanium oxide 27 in the catalytic reaction means 25 has a granular shape, the surface area per unit volume can be maximized. Therefore, the contact area with the bath water sent by the circulation pump 19 becomes large, and the surface area of the granular titanium oxide 27 becomes large, the area receiving the ultraviolet rays generated by the ultraviolet lamp 26 also becomes large. Can generate a lot of oxygen and holes. Therefore, the contact of these substances with the odorous substances and bacteria in the bath water increases, and the decomposition and sterilization performance of the odorous components and bacteria in the bath water per unit time can be improved. It should be noted that the granular titanium oxide 27 is subjected to ultraviolet rays while being agitated and brought into contact with the bath water, so that the entire surface of the granular titanium oxide 27 is used for purification and sterilization. Sterilization can be performed.

【0034】また、浴槽17内の水は多くの場合水道水
を使用する。近年、水道水中に存在するトリハロメタン
などのハロゲン化合物の有害性の可能性が示唆されてき
ている。このトリハロメタンは難分解性で、微生物処理
では分解できにくいが、光触媒を用いた構成であれば、
ある程度分解可能ある。しかし、夏場の水道水中の塩素
添加量が高い場合には当然トリハロメタンなどのハロゲ
ン化合物の存在量も大きくなっている。このような条件
下で光触媒を用いて浄化するためには光触媒の表面積を
大きくとる必要がある。そこで、触媒反応手段25内に
粒状酸化チタン27を充填し、循環水の流れによって撹
拌することによって、粒状酸化チタン27表面全体に紫
外線ランプ26で発生した紫外線を受けることができ
る。すなわち、粒状酸化チタン27の表面全体を利用し
てヒドロキシラジカルなどの活性酸素種とホールを形成
することができる。
As the water in the bath 17, tap water is used in many cases. In recent years, it has been suggested that halogen compounds such as trihalomethane existing in tap water may be harmful. This trihalomethane is difficult to decompose, it is difficult to decompose by microbial treatment, but if the photocatalyst is used,
It can be decomposed to some extent. However, when the amount of chlorine added to tap water in the summer is high, the amount of halogen compounds such as trihalomethane is naturally large. In order to purify using the photocatalyst under such conditions, it is necessary to increase the surface area of the photocatalyst. Therefore, by filling the granular titanium oxide 27 in the catalytic reaction means 25 and stirring by the flow of circulating water, it is possible to receive the ultraviolet rays generated by the ultraviolet lamp 26 on the entire surface of the granular titanium oxide 27. That is, the entire surface of the granular titanium oxide 27 can be utilized to form holes with active oxygen species such as hydroxy radicals.

【0035】一般に、酸化チタンなどの光触媒によるハ
ロゲン化合物のような難分解性の有機物の分解は光触媒
反応によって発生する活性酸素やホールによって行われ
ているといわれている。よって、紫外線ランプ26近傍
で粒状酸化チタン27に紫外線を照射することで粒状酸
化チタン27に照射される紫外線量をますことができ、
これによって多量の活性酸素種を生成することができる
ので、水中のハロゲン化合物の分解速度を増すことがで
きる。また、本実施例のように循環系で触媒反応手段2
5内に浴槽水を何度も循環させることで、難分解性の有
機化合物の分解効率をさらに向上することができる。長
期間浄化殺菌運転を行うと、浴槽水中の微小な角質や湯
垢や細菌などの有機物が付着するので、紫外線ランプ2
6から照射する紫外線量が著しく低下し、浄化性能が低
下する。しかし、触媒反応手段25内の中心部に紫外線
ランプ26を設置し、粒状酸化チタン27を充填し、酸
化チタン27を攪拌することにより紫外線ランプ26の
表面に衝突させることで、紫外線ランプ26表面に付着
した微小な角質や細菌などの有機物を剥離することがで
きる。よって、触媒反応手段25における浄化、殺菌能
力を維持することができる。
In general, it is said that the decomposition of a hardly decomposable organic substance such as a halogen compound by a photocatalyst such as titanium oxide is carried out by active oxygen or holes generated by the photocatalytic reaction. Therefore, by irradiating the granular titanium oxide 27 with ultraviolet rays in the vicinity of the ultraviolet lamp 26, the amount of ultraviolet rays irradiated on the granular titanium oxide 27 can be increased,
As a result, a large amount of active oxygen species can be generated, so that the decomposition rate of the halogen compound in water can be increased. In addition, as in this embodiment, the catalytic reaction means 2 is used in the circulation system.
By repeatedly circulating the bath water in 5, it is possible to further improve the decomposition efficiency of the hardly decomposable organic compound. If you carry out purification and sterilization operation for a long period of time, minute horny substances in the bath water and organic substances such as scales and bacteria will adhere, so the UV lamp 2
The amount of ultraviolet rays irradiated from No. 6 is significantly reduced, and the purification performance is reduced. However, by disposing the ultraviolet lamp 26 in the center of the catalytic reaction means 25, filling the granular titanium oxide 27, and stirring the titanium oxide 27 to collide with the surface of the ultraviolet lamp 26, the surface of the ultraviolet lamp 26 is It is possible to peel off the adhered minute keratin and organic substances such as bacteria. Therefore, the purifying and sterilizing ability of the catalytic reaction means 25 can be maintained.

【0036】また、浴槽水中の臭気成分や細菌などの有
機物濃度が高い場合には、通常の酸化チタンで浄化を行
っても水質を目標レベルまで浄化、殺菌するのに時間が
かかる。そこで、図2に示すように表面に銀36と銅3
7を担持した粒状酸化チタン27を用いて浴槽水の浄化
を行うことで、浴槽水の浄化性能を向上させることがで
きる。つまり、粒状酸化チタン27上に担持した銅及び
銀の触媒作用により、浴槽水中の臭気物質や細菌の細胞
膜の活性化エネルギーを低くすることができるので、こ
れらの物質を分解するのに必要なエネルギーを小さくす
ることができる。これらの活性化エネルギーの小さくな
った臭気物質や細菌と光触媒反応によって発生したヒド
ロキシラジカルなどの活性酸素種やホールとを反応させ
ることで、反応速度を向上させることができる。よっ
て、分解反応速度を増すことができ、単位時間当たりの
臭気成分、細菌などの有機物分解及び殺菌量を増加させ
ることができる。さらに、粒状酸化チタン27に担持し
た銀36、銅37が微量に溶出し、オリゴダイナミック
作用(微量金属作用)により殺菌効果を向上することが
できる。以上のことから、浴槽水の浄化、殺菌能力を向
上することができる。
Further, when the concentration of odorous components and organic substances such as bacteria in the bath water is high, it takes time to purify and sterilize the water quality to the target level even if purification is performed using normal titanium oxide. Therefore, as shown in FIG. 2, silver 36 and copper 3 are formed on the surface.
By purifying the bath water by using the granular titanium oxide 27 carrying No. 7, the purification performance of the bath water can be improved. In other words, the catalytic action of copper and silver supported on the granular titanium oxide 27 can reduce the activation energy of the odorous substances in the bath water and the cell membrane of bacteria, so that the energy required to decompose these substances can be reduced. Can be made smaller. The reaction rate can be improved by reacting these odorous substances and bacteria with reduced activation energy with active oxygen species such as hydroxy radicals generated by photocatalytic reaction and holes. Therefore, the decomposition reaction rate can be increased, and the amount of odorous components, organic substances such as bacteria, decomposed and sterilized per unit time can be increased. Furthermore, a small amount of silver 36 and copper 37 carried on the granular titanium oxide 27 is eluted, and the sterilizing effect can be improved by the oligodynamic action (trace metal action). From the above, the purification and sterilizing ability of bath water can be improved.

【0037】また、循環流路18に加熱装置29を備
え、浴槽水を加熱することで、浴槽水及び粒状酸化チタ
ン27の温度を上げることができ、粒状酸化チタン27
はその雰囲気の温度を上げることによって光触媒反応速
度を増し、浄化、殺菌性能を向上することができる。つ
まり、加熱により浴槽水中の臭気成分や細菌の構成物質
に熱エネルギーを加え、粒状酸化チタン27表面に発生
したヒドロキシラジカルなどの活性酸素種及びホールの
物質の分解に必要なエネルギーを低減できる。よって、
酸化還元反応の速度を増すことができ、臭気成分などの
有機物の分解、細菌の殺菌速度をますことができる。
Further, by providing the heating device 29 in the circulation passage 18 and heating the bath water, it is possible to raise the temperature of the bath water and the granular titanium oxide 27, and the granular titanium oxide 27.
By increasing the temperature of the atmosphere, the photocatalytic reaction rate can be increased, and the purification and sterilization performance can be improved. That is, heat energy can be applied to the odorous components in the bath water and the constituent substances of the bacteria to reduce the energy required to decompose the active oxygen species such as hydroxy radicals generated on the surface of the granular titanium oxide 27 and the substance of the holes. Therefore,
The rate of redox reaction can be increased, the decomposition rate of organic substances such as odorous components, and the sterilization rate of bacteria can be increased.

【0038】また、一般に細菌には増殖最適温度域があ
り、この温度よりも高いと増殖能力が急激に低下すると
いわれている。よって、加熱装置29によって浴槽水の
温度が上昇することにより、浴槽水中の細菌の増殖速度
を低下することができ、このような細菌が触媒反応手段
25にはいり、粒状酸化チタン27と紫外線の光触媒反
応により発生したヒドロキシラジカルなどの活性酸素や
ホールと接触することにより、殺菌性能を向上できる。
なお、前述のように表面上に金属元素を担持した光触媒
を用いることでさらに浄化、殺菌性能が向上することは
いうまでもない。
In general, bacteria have an optimum growth temperature range, and it is said that if the temperature is higher than this temperature, the growth ability will be sharply reduced. Therefore, the temperature of the bath water is increased by the heating device 29, so that the growth rate of the bacteria in the bath water can be reduced. Such bacteria enter the catalytic reaction means 25, and the granular titanium oxide 27 and the photocatalyst for the ultraviolet rays. The sterilization performance can be improved by contacting with active oxygen such as hydroxy radicals generated by the reaction or holes.
Needless to say, the purification and sterilization performance is further improved by using the photocatalyst supporting the metal element on the surface as described above.

【0039】次に、水の浄化運転を連続して続けると、
触媒反応手段25内の流失防止板28に入浴によって混
入した角質や湯垢や繁殖した細菌の塊によって、目詰ま
りを起こす。この結果、流出防止板28部分の圧力損失
が増大し、循環流量が減少するので、処理できる被処理
水量が減少する。そこで、流路18に濾過手段20を備
え、内部に粒状濾材21を充填し、粒状濾材21同士の
隙間により浴槽水中の角質や細菌の塊を除去することが
できる。つまり、浴槽水中の角質や細菌の塊などの懸濁
物を濾過除去し、流失防止板28への懸濁物質の付着を
小さくすることにより、目詰まりを低減することができ
る。なお、本実施例では、浴槽水中の角質や細菌の塊を
除去するために、濾過手段20内に粒状濾材21を充填
する構成としたが、流出防止板28の細孔を目詰まりさ
せる物質が除去できればよいので、例えば膜、糸巻きフ
ィルター、などを用いても良い。
Next, when the water purification operation is continuously continued,
Clogging occurs due to keratin and scales mixed with the bath in the wash-out prevention plate 28 in the catalytic reaction means 25, and lumps of grown bacteria. As a result, the pressure loss in the outflow prevention plate 28 portion increases and the circulation flow rate decreases, so that the amount of water to be treated that can be treated decreases. Therefore, the flow path 18 is provided with the filtering means 20 and the inside thereof is filled with the granular filter medium 21 so that keratin and lumps of bacteria in the bath water can be removed by the gaps between the granular filter mediums 21. That is, clogging can be reduced by filtering and removing suspensions such as keratin and lumps of bacteria in the bath water to reduce the adhesion of suspended substances to the wash-out prevention plate 28. In the present embodiment, in order to remove keratin and lumps of bacteria in the bath water, the filtering means 20 is filled with the granular filter material 21, but a substance that clogs the pores of the outflow prevention plate 28 is used. As long as it can be removed, a membrane, a wound filter, or the like may be used.

【0040】しかし、長期間浴槽水の浄化を続けると、
濾過手段20内の粒状濾材21に浴槽水中の角質や湯垢
や細菌の塊などが徐々に堆積していき、粒状濾材21同
士の隙間を閉塞し、その結果、圧力損失が大きくなり、
時間当たりの処理能力が低下する。そこで、制御装置3
6のはたらきにより、濾過手段20の濾材支持板22方
向から浴槽水が流入するように三方弁30及び三方弁3
1を切り換え、二方弁33を開き、排水管34から浴槽
水を排出することで、粒状濾材21及び濾材21の隙間
を閉塞している角質や細菌の塊などの懸濁物質を浮揚
し、排水管34から排出する。粒状濾材21の隙間を閉
塞していた懸濁物質を排出できたら、二方弁33を閉
じ、三方弁30、31を切り換えて、通常の循環回路に
戻す。この動作により、濾過手段20の圧力損失の上昇
を抑えることができ、常に一定の処理流量を得ることが
できる。
However, if the bath water is continuously purified for a long time,
On the granular filter material 21 in the filtering means 20, horny cells, scales of bacteria, lumps of bacteria and the like in the bath water gradually accumulate, closing the gaps between the granular filter materials 21 and, as a result, increasing the pressure loss.
The processing capacity per hour is reduced. Therefore, the control device 3
By the function of 6, the three-way valve 30 and the three-way valve 3 are provided so that bath water flows from the direction of the filter medium support plate 22 of the filtering means 20.
1 is switched, the two-way valve 33 is opened, and the bath water is discharged from the drain pipe 34 to levitate suspended matter such as horny cells and bacterial clumps that block the gaps between the granular filter medium 21 and the filter medium 21, Discharge from the drain pipe 34. When the suspended substance that has blocked the gap of the granular filter medium 21 can be discharged, the two-way valve 33 is closed and the three-way valves 30 and 31 are switched to return to the normal circulation circuit. By this operation, an increase in the pressure loss of the filtering means 20 can be suppressed, and a constant processing flow rate can always be obtained.

【0041】また、浴槽水中の微小な角質や湯垢や細菌
の塊の懸濁物質よりも粒状濾材21同士の隙間径よりも
小さい場合には流出防止板28の目詰まりの原因とはな
りにくいものの、浴槽水の透明度が低下しないため、触媒
反応手段25内での紫外線の透過率が低下し、その結果
浄化・殺菌能力が低下する。そこで、この水中の微小な懸
濁物質を凝集により濾過手段20で除去可能にすること
により、浄化殺菌性能を維持できる。つまり、濾過手段
20の内部にアルミニウム電極23とステンレス電極2
4を設け、アルミニウム電極23を陽極として通電し、ア
ルミニウムを浴槽水中に溶出させる。浴槽水中でアルミ
ニウムは水和物の水酸化アルミニウムとなり浴槽水中の
微小な垢や細菌を凝集し、塊を形成し、粒子径を大きくし
て下流方向の粒状濾材21で除去を行う。このように、
微小な垢や細菌を除去することにより、浴槽水の紫外線
透過率を向上することで、触媒反応手段25内の光触媒
27での反応を効果的に行うことができる。
Further, when the size of the gap between the granular filter media 21 is smaller than the suspended matter of minute horny cells, scales of water, or bacterial mass in the bath water, the outflow prevention plate 28 is less likely to be clogged. Since the transparency of the bath water does not decrease, the transmittance of ultraviolet rays in the catalytic reaction means 25 decreases, and as a result, the purification / sterilization ability decreases. Therefore, purification and sterilization performance can be maintained by allowing the filtering means 20 to remove the minute suspended matter in water by coagulation. That is, the aluminum electrode 23 and the stainless steel electrode 2 are provided inside the filtering means 20.
4 is provided and electricity is applied using the aluminum electrode 23 as an anode to elute aluminum in bath water. In the bath water, aluminum becomes a hydrated aluminum hydroxide, agglomerates minute dust and bacteria in the bath water, forms a lump, increases the particle size, and removes it with the granular filter medium 21 in the downstream direction. in this way,
By removing minute dirt and bacteria, the ultraviolet transmittance of the bath water is improved, so that the reaction at the photocatalyst 27 in the catalytic reaction means 25 can be effectively performed.

【0042】[0042]

【発明の効果】以上説明したように本発明の流体処理装
置によると以下の効果が得られる。
As described above, according to the fluid treatment apparatus of the present invention, the following effects can be obtained.

【0043】(1)被処理流体を流体搬送手段で流路に
送り込み、触媒反応手段内の触媒を流体の流れによって
撹拌しているので、触媒同士が衝突し、触媒自身の表面
に付着した懸濁物質を剥離することができるので、触媒
上での酸化還元反応の能力を常に維持できる。よって、
長期間浄化、殺菌性能を維持することができる。
(1) Since the fluid to be treated is sent to the flow path by the fluid conveying means and the catalyst in the catalytic reaction means is agitated by the flow of the fluid, the catalysts collide with each other and are suspended on the surface of the catalyst itself. Since the suspended substance can be removed, the ability of the redox reaction on the catalyst can be maintained at all times. Therefore,
Purification and sterilization performance can be maintained for a long time.

【0044】(2)循環流路に循環手段を設け、貯蔵手
段内の被処理流体を循環させて触媒反応手段に送り込
み、触媒反応手段内の触媒と接触させることで、被処理
流体中の有機物及び細菌との接触効率を向上できるの
で、被処理水の有機物濃度の低減および、殺菌能力を向
上できる。よって、流体の浄化、殺菌性能を向上するこ
とができる。
(2) An organic substance in the fluid to be treated is provided by providing a circulation means in the circulation passage to circulate the fluid to be treated in the storage means to feed it to the catalytic reaction means and bring it into contact with the catalyst in the catalytic reaction means. Also, since the efficiency of contact with bacteria can be improved, the concentration of organic substances in the water to be treated can be reduced and the sterilization ability can be improved. Therefore, the fluid purification and sterilization performance can be improved.

【0045】(3)触媒反応手段の被処理流体の流出方
向に触媒の流出を防止する流出防止手段を装着すること
により、触媒の流路中への流出を防止でき、流路中の流
体搬送手段や流路切り換え手段の故障を防ぐことができ
る。また、触媒反応手段から光触媒の流出を気にせず被
処理流体の循環速度を上げることができので、単位時間
当たりの処理量を増すことができる。よって、被処理流
体の浄化能力を上げることができる。
(3) The catalyst can be prevented from flowing into the flow path by mounting the flow-out preventing means for preventing the catalyst from flowing out in the flow-out direction of the fluid to be treated of the catalyst reaction means, and the fluid can be conveyed in the flow path. It is possible to prevent failure of the means and the flow path switching means. Moreover, since the circulation speed of the fluid to be treated can be increased without worrying about the outflow of the photocatalyst from the catalytic reaction means, the treatment amount per unit time can be increased. Therefore, the purification ability of the fluid to be treated can be improved.

【0046】(4)触媒反応手段内の触媒を粒状にする
ことによって、被処理流体の接触面積を増やすことがで
き、触媒を撹拌手段によって撹拌しながら被処理流体と
接触させることで、触媒表面全体と被処理流体を接触さ
せることができるので、単位時間当たりの分解、殺菌性
能を向上できる。
(4) By making the catalyst in the catalytic reaction means granular, the contact area of the fluid to be treated can be increased, and by bringing the catalyst into contact with the fluid to be treated while stirring by the stirring means, the catalyst surface Since the whole and the fluid to be treated can be brought into contact with each other, decomposition and sterilization performance per unit time can be improved.

【0047】(5)触媒反応手段内に粒状の光触媒を充
填し、紫外線照射装置を備え撹拌手段により光触媒を撹
拌することで、紫外線照射装置に粒状の光触媒を衝突さ
せながら被処理流体の浄化、殺菌を行うことで、紫外線
照射装置の表面に堆積する物質を剥離することができる
ので、光触媒に照射する紫外線量を常に一定に保つこと
ができる。よって、安定した浄化、殺菌性能を維持する
ことができる。
(5) Purification of the fluid to be treated by colliding the granular photocatalyst with the ultraviolet irradiation device by filling the catalyst reaction means with the granular photocatalyst and agitating the photocatalyst with the ultraviolet irradiation device and stirring means. By performing the sterilization, the substance deposited on the surface of the ultraviolet irradiation device can be peeled off, so that the amount of ultraviolet rays applied to the photocatalyst can always be kept constant. Therefore, stable purification and sterilization performance can be maintained.

【0048】(6)光触媒の表面上に光触媒の反応速度
を向上する金属触媒を担持することで、光触媒上での酸
化還元反応の反応速度を上げることができる。よって、
浄化速度を向上することができ、さらに微量に溶出した
金属のオリゴダイナミック効果との相乗効果により殺菌
能力を高めることができる。
(6) By supporting a metal catalyst which improves the reaction rate of the photocatalyst on the surface of the photocatalyst, the reaction rate of the redox reaction on the photocatalyst can be increased. Therefore,
The purification rate can be improved, and the sterilizing ability can be enhanced by the synergistic effect with the oligodynamic effect of the metal eluted in a trace amount.

【0049】(7)流路に温度調節手段を設け、被処理
流体と粒状の光触媒の温度を上げることにより、触媒の
反応速度を増すことができるので、光触媒上での酸化還
元反応の速度を上げることができる。よって、触媒反応
手段での浄化、殺菌速度を上げることができる。
(7) Since the reaction rate of the catalyst can be increased by providing temperature control means in the flow path and raising the temperature of the fluid to be treated and the granular photocatalyst, the rate of redox reaction on the photocatalyst can be increased. Can be raised. Therefore, the rate of purification and sterilization by the catalytic reaction means can be increased.

【0050】(8)流路に濾過手段を備えることによ
り、被処理流体中の大きい粒子を除去することができ
る。よって、被処理流体から流出防止手段の細孔を閉塞
する粒子を除去することができ、閉塞による圧力損失の
上昇を防止することができるので、常に一定量の被処理
流体を処理できる。よって、長期間にわたり安定した浄
化、殺菌性能が得られる。
(8) Large particles in the fluid to be treated can be removed by providing the flow path with the filtering means. Therefore, particles that block the pores of the outflow prevention means can be removed from the fluid to be processed, and the pressure loss can be prevented from increasing due to the blockage, so that a certain amount of fluid to be processed can be always processed. Therefore, stable purification and sterilization performance can be obtained for a long period of time.

【0051】(9)流路に濾過手段の洗浄を行う洗浄手
段をもうけ、濾過手段の濾材および濾材支持板が目詰ま
りを起こしたら、洗浄手段により濾材を浮揚し、閉塞し
ていた懸濁物質や付着していた懸濁物質を剥離し、再度
水に懸濁し、排出することで、触媒反応手段内の流出防
止板の細孔の目詰まりを防止することができる。よっ
て、長期間安定した浄化、殺菌性能を維持することがで
きる。
(9) A washing means for washing the filtering means is provided in the flow path, and when the filter medium of the filtering means and the filter medium support plate are clogged, the washing medium is floated by the washing means to suspend the suspended substance. It is possible to prevent clogging of the pores of the outflow prevention plate in the catalytic reaction means by peeling off the suspended substances that have adhered to the substrate and resuspending them in water and discharging them. Therefore, stable purification and sterilization performance can be maintained for a long period of time.

【0052】(10)流路に濾過手段を設け、濾過手段
内に凝集手段となるアルミニウム電極とステンレス陰極
を備えアルミニウムが陽極となるように通電すること
で、被処理水中の微小なあか、細菌などの微小な懸濁物
質を凝集し、濾過手段で除去することで、被処理水の紫
外線透過率を向上することができ、光触媒上での酸化還
元反応を効率的に行うことができる。よって、安定した
浄化、殺菌性能が得られる。
(10) A filtering means is provided in the flow path, and an aluminum electrode and a stainless cathode serving as an aggregating means are provided in the filtering means to energize so that aluminum serves as an anode. By aggregating a minute suspended substance such as, for example, and removing it with a filtering means, the ultraviolet transmittance of the water to be treated can be improved, and the redox reaction on the photocatalyst can be efficiently performed. Therefore, stable purification and sterilization performance can be obtained.

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

【図1】本発明の一実施例における流体処理装置の構成
FIG. 1 is a configuration diagram of a fluid treatment device according to an embodiment of the present invention.

【図2】本発明の流体処理装置に用いる光触媒の他の例
を示す断面図
FIG. 2 is a sectional view showing another example of the photocatalyst used in the fluid treatment apparatus of the present invention.

【図3】従来の流体処理装置の構成図FIG. 3 is a configuration diagram of a conventional fluid treatment device.

【符号の説明】[Explanation of symbols]

18 循環流路 19 循環手段(循環ポンプ) 20 濾過手段(凝集装置) 23,24 凝集手段(電極) 25 触媒反応手段 26 紫外線照射手段(紫外線ランプ) 27 粒状酸化チタン 28 流出防止手段(流出防止板) 29 温度調節手段(加熱装置) 36 銀 37 銅 18 Circulation Flow Path 19 Circulation Means (Circulation Pump) 20 Filtration Means (Aggregator) 23, 24 Aggregation Means (Electrode) 25 Catalytic Reaction Means 26 Ultraviolet Irradiation Means (Ultraviolet Lamp) 27 Granular Titanium Oxide 28 Outflow Prevention Means (Outflow Prevention Plate) ) 29 temperature control means (heating device) 36 silver 37 copper

───────────────────────────────────────────────────── フロントページの続き (72)発明者 古田 聡 大阪府門真市大字門真1006番地 松下電器 産業株式会社内 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Satoshi Furuta 1006 Kadoma, Kadoma City, Osaka Prefecture Matsushita Electric Industrial Co., Ltd.

Claims (12)

【特許請求の範囲】[Claims] 【請求項1】流路と、この流路に設けられ、被処理流体
を搬送する搬送手段と、内部に前記被処理流体中の物質
を浄化する触媒を充填した触媒反応手段と、前記触媒反
応手段内で触媒を撹拌する撹拌手段を有する流体処理装
置。
1. A flow passage, a conveying means provided in the flow passage for conveying a fluid to be treated, a catalytic reaction means filled with a catalyst for purifying a substance in the fluid to be treated, and the catalytic reaction. A fluid treatment device having stirring means for stirring the catalyst in the means.
【請求項2】被処理流体を貯蔵する貯蔵手段と、貯蔵手
段内の流体を循環する循環手段と、前記貯蔵手段と循環
手段の間に配設された循環流路と、前記循環流路に被処
理流体中の物質を浄化する触媒を充填した触媒反応手段
と、前記触媒反応手段内で触媒を撹拌する撹拌手段を有
する流体処理装置。
2. A storage means for storing a fluid to be processed, a circulation means for circulating a fluid in the storage means, a circulation flow path arranged between the storage means and the circulation means, and a circulation flow path. A fluid treatment apparatus comprising a catalytic reaction means filled with a catalyst for purifying substances in a fluid to be treated, and a stirring means for stirring the catalyst in the catalytic reaction means.
【請求項3】前記触媒反応手段内の被処理流体の流入側
と流出側に触媒の流出を防止する流出防止手段を有する
請求項1または2記載の流体処理装置。
3. The fluid treatment apparatus according to claim 1, further comprising outflow prevention means for preventing the outflow of the catalyst on the inflow side and the outflow side of the fluid to be treated in the catalytic reaction means.
【請求項4】前記触媒反応手段の内部に粒状の触媒を充
填した請求項1または2記載の流体処理装置。
4. The fluid processing apparatus according to claim 1, wherein the catalyst reaction means is filled with a granular catalyst.
【請求項5】前記触媒反応手段に紫外線照射手段を備
え、前記触媒に粒状の光触媒を用いた構成の請求項1な
いし4のいずれか1項記載の流体処理装置 。
5. The fluid treatment apparatus according to claim 1, wherein the catalytic reaction means is provided with an ultraviolet irradiation means, and a granular photocatalyst is used as the catalyst.
【請求項6】前記粒状の光触媒を結晶構造がアナターゼ
型の酸化チタンとした請求項5記載の流体処理装置。
6. The fluid treatment apparatus according to claim 5, wherein the granular photocatalyst is titanium oxide having anatase type crystal structure.
【請求項7】前記光触媒と、少なくとも1種類以上の金
属元素を担持した請求項5または6記載の流体処理装
置。
7. The fluid treatment apparatus according to claim 5, wherein the photocatalyst and at least one metal element are supported.
【請求項8】前記金属元素を銅及び銀とした請求項7記
載の流体処理装置。
8. The fluid processing apparatus according to claim 7, wherein the metal elements are copper and silver.
【請求項9】前記流路に被処理流体の温度調節手段を備
えた請求項1ないし5のいずれか1項記載の流体処理装
置。
9. The fluid processing apparatus according to claim 1, wherein the flow path is provided with temperature control means for the fluid to be processed.
【請求項10】前記循環流路に濾過手段を有する請求項
1ないし5のいずれか1項記載の流体処理装置。
10. The fluid treatment device according to claim 1, wherein the circulation passage has a filtering means.
【請求項11】前記濾過手段を洗浄する洗浄手段を有す
る請求項9記載の流体処理装置。
11. The fluid treatment apparatus according to claim 9, further comprising a cleaning unit that cleans the filtering unit.
【請求項12】前記濾過手段の上流方向に凝集手段を設
けた請求項9記載の流体処理装置。
12. The fluid treatment apparatus according to claim 9, further comprising an aggregating unit provided upstream of the filtering unit.
JP8064248A 1996-03-21 1996-03-21 Fluid treatment apparatus Pending JPH09253637A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP8064248A JPH09253637A (en) 1996-03-21 1996-03-21 Fluid treatment apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8064248A JPH09253637A (en) 1996-03-21 1996-03-21 Fluid treatment apparatus

Publications (1)

Publication Number Publication Date
JPH09253637A true JPH09253637A (en) 1997-09-30

Family

ID=13252675

Family Applications (1)

Application Number Title Priority Date Filing Date
JP8064248A Pending JPH09253637A (en) 1996-03-21 1996-03-21 Fluid treatment apparatus

Country Status (1)

Country Link
JP (1) JPH09253637A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2004014437A1 (en) * 2002-08-07 2004-02-19 Albagaia Limited Apparatus and method for treatment of chemical and biological hazards
JP2008518759A (en) * 2004-11-03 2008-06-05 ナノプロプリエタリー,インコーポレイテッド Photocatalytic process

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2004014437A1 (en) * 2002-08-07 2004-02-19 Albagaia Limited Apparatus and method for treatment of chemical and biological hazards
US7491339B2 (en) 2002-08-07 2009-02-17 Albagaia Limited Apparatus and method for treatment of chemical and biological hazards
JP2008518759A (en) * 2004-11-03 2008-06-05 ナノプロプリエタリー,インコーポレイテッド Photocatalytic process

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