JPH0523681A - Treatment and device for photooxidation - Google Patents

Treatment and device for photooxidation

Info

Publication number
JPH0523681A
JPH0523681A JP20107191A JP20107191A JPH0523681A JP H0523681 A JPH0523681 A JP H0523681A JP 20107191 A JP20107191 A JP 20107191A JP 20107191 A JP20107191 A JP 20107191A JP H0523681 A JPH0523681 A JP H0523681A
Authority
JP
Japan
Prior art keywords
water
treated
fine particles
titanium dioxide
particulate
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
JP20107191A
Other languages
Japanese (ja)
Inventor
Koji Yamagata
光二 山形
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.)
RAIZAA KOGYO KK
Original Assignee
RAIZAA 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 RAIZAA KOGYO KK filed Critical RAIZAA KOGYO KK
Priority to JP20107191A priority Critical patent/JPH0523681A/en
Publication of JPH0523681A publication Critical patent/JPH0523681A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To efficiently separate and recover a particulate such as titanium dioxide by passing a water to be treated, in which the particulate such as titanium dioxide is suspended, around an ultraviolet lamp to ultraviolet irradiation treat and feeding to a sedimentation vessel to sedimentate the catalyst particulate in the water to be treated. CONSTITUTION:The water to be treated is fed from the water feed opening 2 into the reactor vessel 1, in which the catalyst particulate such as titanium dioxide is added and is suspended by the stirring apparatus M, to keep a specific water level. And the water to be treated flows down along the ultraviolet lamp 6 and is irradiated with ultraviolet rays to decompose an organic material in the water to be treated and to sterilizing treat or the like by catalytic action of the titanium dioxide particulate. The treated water is fed to the inner cylinder 9 of the 1st sedimentation vessel and the catalyst particulate, a part of which is catched by the filter membrane 10, is sedimentated. The other hand, the supernatant treated water is fed into the inner cylinder 13 of the 2nd sedimentation vessel and the residual catalyst particulate 7 is sedimentated and is catched by the filter membrane 14.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】この発明は、二酸化チタンなどの
半導体微粒子を触媒とした光酸化処理方法とその装置に
関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a photooxidation treatment method and apparatus using semiconductor fine particles such as titanium dioxide as a catalyst.

【0002】[0002]

【従来の技術】ハロゲン、有機物質等を含む廃水及びプ
ール水、飲料水等は活性汚泥、酸化分解等によって分解
処理されてきたが、これら既存の処理方法は長時間と広
大なスペースを必要とするため、合理的な方法とは言え
ない。また、プール水等の殺菌には従来塩素などの薬品
処理が行なわれてきたが、薬品による殺菌処理は人体へ
の影響から手控えられる傾向にある。
2. Description of the Related Art Waste water containing halogen, organic substances, etc., pool water, drinking water, etc. have been decomposed by activated sludge, oxidative decomposition, etc., but these existing treatment methods require a long time and a vast space. Therefore, it is not a rational method. Further, although sterilization of pool water or the like has conventionally been performed with chemicals such as chlorine, sterilization with chemicals tends to be refrained from the influence on the human body.

【0003】これに対して、紫外線を利用した被処理水
の殺菌は、薬品殺菌法と異なり、人体への影響が殆ど無
く効果的に難分解ハロゲン廃水などの分解処理と殺菌処
理が同時にできるなどの特性があり、種々の生産分野に
応用され、需要は増大されつつある。
On the other hand, the sterilization of water to be treated using ultraviolet rays, unlike the chemical sterilization method, has almost no effect on the human body and can effectively decompose and sterilize hardly-decomposable halogen wastewater at the same time. It has the characteristics of being applied to various production fields, and the demand is increasing.

【0004】この紫外線を利用した殺菌法として最も効
率が良いとされるのは、外周を保護管で被覆した紫外線
ランプを両端を開放した処理タンク内に挿入するととも
に、処理タンクの両端には被処理水の給水管乃至排水管
に接続するようにした光触媒反応槽を使用して、被処理
水が紫外線ランプの周囲を通過する間に難分解ハロゲン
分解処理と殺菌を同時に行なう方法である。
The most efficient sterilization method using ultraviolet rays is that an ultraviolet lamp whose outer periphery is covered with a protective tube is inserted into a processing tank whose both ends are open, and both ends of the processing tank are covered. This is a method in which a photocatalytic reaction tank connected to a water supply pipe or a drainage pipe of treated water is used to simultaneously perform the hardly decomposable halogen decomposition treatment and the sterilization while the treated water passes around the ultraviolet lamp.

【0005】一方、これら紫外線に照射される被処理水
中に二酸化チタン等の微粒子を懸濁させると、これら微
粒子の触媒作用により更に効果的な分解処理と殺菌同時
に処理が行なわれることが知られている。
On the other hand, it is known that when fine particles of titanium dioxide or the like are suspended in the water to be treated which is irradiated with ultraviolet rays, the catalytic action of these fine particles enables more effective decomposition treatment and simultaneous sterilization treatment. There is.

【0006】[0006]

【発明が解決しようとする課題】しかしながら、上述の
ように二方法を組み合わせ、被処理水中に二酸化チタン
等の微粒子を懸濁させて紫外線ランプの周囲を通過させ
て分解浄化殺菌処理を行なう場合には、処理後の水中か
ら二酸化チタン微粒子を分離、回収するのが極めて困難
であり、またこれら二酸化チタン微粒子を完全に分離、
回収するには大型の分離装置を必要とするなどの難点が
ある。
However, when the two methods are combined as described above and fine particles such as titanium dioxide are suspended in the water to be treated and passed around the ultraviolet lamp to carry out the decomposition purification sterilization treatment. Is extremely difficult to separate and recover titanium dioxide fine particles from the treated water, and these titanium dioxide fine particles are completely separated,
There is a problem that a large-scale separation device is required for recovery.

【0007】また二酸化チタン等の微粒子を各種の膜に
よって分離し、濃縮液と同時に回収して再利用する場
合、膜に目詰まりが生じないように定期的に洗浄を行な
わなければならない。
When fine particles of titanium dioxide or the like are separated by various types of membranes and are recovered and reused at the same time as the concentrated liquid, it is necessary to regularly wash the membranes so that the membranes are not clogged.

【0008】この発明は、上記実情に鑑み、被処理水中
に二酸化チタン等の微粒子を懸濁させて紫外線ランプの
周囲を通過させて紫外線照射処理を行なうに際して処理
後の水中に含まれる二酸化チタン等の微粒子を分離、回
収する方法とその装置を提案することを目的とする。
In view of the above situation, the present invention suspends fine particles of titanium dioxide or the like in the water to be treated and passes them around the ultraviolet lamp to carry out the ultraviolet irradiation treatment, so that titanium dioxide or the like contained in the water after the treatment. The object of the present invention is to propose a method and an apparatus for separating and recovering the above fine particles.

【0009】[0009]

【課題を解決するための手段】以上の課題を解決するた
めに、この発明では紫外線照射ランプを挿入した反応槽
に、1段又は2段以上の沈殿槽を並設し、反応槽には触
媒微粒子を懸濁させた被処理水を送入し、該反応槽での
水位を一定に保ちながら上記ランプより紫外線を照射し
て触媒微粒子により被処理水を浄化、処理し、次に反応
槽での処理水をオーバーフローさせて沈殿槽に送り込
み、該沈殿槽では処理水中の触媒微粒子を沈降分離さ
せ、沈殿槽の底部からは触媒微粒子を含む処理水の全部
又は一部を必要とあれば上記処理槽に戻すようにした光
酸化処理方法とその装置を提案するものである。
In order to solve the above problems, according to the present invention, a reaction tank having an ultraviolet irradiation lamp inserted therein is provided with one or two or more stages of precipitation tanks in parallel, and a catalyst is provided in the reaction tank. The water to be treated in which the fine particles are suspended is fed, and while the water level in the reaction tank is kept constant, ultraviolet rays are radiated from the lamp to purify and treat the water to be treated with the catalyst fine particles, and then in the reaction tank. The treated water of the above is sent to a settling tank by overflowing, the catalyst fine particles in the treated water are settled and separated in the settling tank, and all or part of the treated water containing the catalyst fine particles is treated from the bottom of the settling tank if necessary. The present invention proposes a photo-oxidation treatment method and apparatus for returning it to the bath.

【0010】なお、この発明において紫外線照射ランプ
としては、高圧水銀灯、中圧水銀灯、低圧水銀灯等を被
処理水の種類に応じて使用することができる。
In the present invention, as the ultraviolet irradiation lamp, a high pressure mercury lamp, a medium pressure mercury lamp, a low pressure mercury lamp or the like can be used depending on the type of water to be treated.

【0011】[0011]

【作用】即ち、この発明では反応槽内で触媒微粒子を含
む被処理水に紫外線を照射して被処理水を浄化、処理し
た後、この処理水を沈殿槽にオーバーフローさせ、沈殿
槽では処理水中に含まれる触媒微粒子を沈降分離させる
ため、光酸化処理法に用いる二酸化チタン等の触媒微粒
子を効果的に分離、回収することができるのである。
That is, in the present invention, the treated water containing the catalyst fine particles is irradiated with ultraviolet rays in the reaction tank to purify and treat the treated water, and the treated water is allowed to overflow into the settling tank. Since the catalyst fine particles contained in (3) are precipitated and separated, the catalyst fine particles such as titanium dioxide used in the photooxidation treatment method can be effectively separated and recovered.

【0012】[0012]

【実施例】以下、この発明を図示の実施例に基づいて説
明する。第1図は、この発明の一実施例を示すもので、
1は上部に給水口2、下部に排水口3を有する反応槽
で、反応槽1の外周にはヒータ4が設けられ、反応槽1
の内部にはその外周に石英製の保護管5を設けた紫外線
ランプ6を挿入する。なお、反応槽1の底部乃至側部に
は攪拌装置Mが設けられている。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below based on the illustrated embodiments. FIG. 1 shows an embodiment of the present invention.
Reference numeral 1 is a reaction tank having a water supply port 2 in the upper part and a drain port 3 in the lower part, and a heater 4 is provided on the outer periphery of the reaction tank 1.
An ultraviolet lamp 6 having a quartz protective tube 5 provided on the outer periphery thereof is inserted into the inside of the container. A stirrer M is provided on the bottom or side of the reaction tank 1.

【0013】被処理水は給水口2から反応槽1内に供給
され、反応槽1内では一定の水位aを保つようにすると
ともに、二酸化チタン等の触媒微粒子7,…を加える。
反応槽1内では攪拌装置Mにより触媒微粒子7,…を水
中に懸濁させる。また、ヒータ4により加温され、この
ような状態で紫外線ランプ6に沿って流下する。この
間、紫外線照射を受けるとともに、二酸化チタンの微粒
子の触媒作用により被処理水中の有機物の分解、殺菌処
理等が行なわれる。
The water to be treated is supplied from the water supply port 2 into the reaction tank 1 so as to keep a constant water level a in the reaction tank 1 and to add catalyst fine particles 7 such as titanium dioxide.
In the reaction tank 1, the catalyst fine particles 7, ... Are suspended in water by the stirrer M. In addition, the heater 4 heats it, and in such a state, it flows down along the ultraviolet lamp 6. During this period, while being irradiated with ultraviolet rays, the organic substances in the water to be treated are decomposed and sterilized by the catalytic action of fine particles of titanium dioxide.

【0014】8は、縮径状の底部を有する第1沈殿槽
で、第1沈殿槽8内には縦方向に内筒9を挿入し、内筒
9の底部には濾過膜10が設けられ、また第1沈殿槽8の
上部には排水口11が設けられる。同様に、12は縮径状の
底部を有する第2沈殿槽で、第2沈殿槽12内には縦方向
に内筒13を挿入し、内筒13の底部には濾過膜14が設けら
れ、第2沈殿槽11の上部には排水口15が設けられる。
Reference numeral 8 is a first settling tank having a diameter-reduced bottom. An inner cylinder 9 is inserted into the first settling tank 8 in the vertical direction, and a filtration membrane 10 is provided at the bottom of the inner cylinder 9. Further, a drainage port 11 is provided above the first settling tank 8. Similarly, 12 is a second settling tank having a diameter-reduced bottom. An inner cylinder 13 is inserted into the second settling tank 12 in the vertical direction, and a filtration membrane 14 is provided at the bottom of the inner cylinder 13. A drain port 15 is provided above the second settling tank 11.

【0015】一方、反応槽1の底部に設けられた排水口
3には第1排水路16が設けられ、第1排水路16はその頂
部が反応槽1内の被処理水の水位aより下位にあるよう
にしてその排水口を第1沈殿槽8上の中央に位置させ
る。
On the other hand, a drainage port 3 provided at the bottom of the reaction tank 1 is provided with a first drainage channel 16, and the top of the first drainage channel 16 is lower than the water level a of the water to be treated in the reaction vessel 1. The drainage port is located at the center on the first settling tank 8 as described in 1.

【0016】同様に、第1沈殿槽8の上部に設けられた
排水口11には第2排水路17が設けられ、第2排水路17は
その頂部が反応槽1内の被処理水の水位aより下位にあ
るようにしてその排水口を第2沈殿槽12上の中央に位置
させる。
Similarly, the drainage port 11 provided in the upper part of the first settling tank 8 is provided with the second drainage channel 17, and the top of the second drainage channel 17 is the water level of the treated water in the reaction tank 1. The drainage port is located at the center on the second settling tank 12 so as to be lower than a.

【0017】更に、反応槽1の上部、第1沈殿槽8の底
部及び第2沈殿槽12の底部を結ぶ連絡路18が設けられ、
反応槽1と第1沈殿槽8の間の連絡路18には圧送ポンプ
19が設けられ、また第1沈殿槽8乃至第2沈殿槽12の底
部下の連絡路18には一方をドレインに通ずるバルブ20,2
0 が設けられる。
Further, there is provided a connecting path 18 connecting the upper part of the reaction tank 1, the bottom of the first settling tank 8 and the bottom of the second settling tank 12,
A pressure pump is provided in the communication path 18 between the reaction tank 1 and the first settling tank 8.
19 is provided, and valves 20 and 2 are provided in the connecting passage 18 below the bottoms of the first settling tank 8 and the second settling tank 12, one of which is connected to the drain.
0 is provided.

【0018】以上のような光酸化処理装置において、上
述のように反応槽1内で処理された水は第1排水路16よ
り反応槽1の水位aの水位差により第1沈殿槽8の内筒
9内に供給される。
In the photooxidation treatment apparatus as described above, the water treated in the reaction tank 1 as described above is stored in the first settling tank 8 by the water level difference of the water level a of the reaction tank 1 from the first drainage channel 16. It is supplied into the cylinder 9.

【0019】供給された処理水は内筒9内で触媒微粒子
7,…が沈降分離され、分離された触媒微粒子7,…の
一部は濾過膜10に捕集される。
In the supplied treated water, the catalyst fine particles 7, ... Are sedimented and separated in the inner cylinder 9, and a part of the separated catalyst fine particles 7 ,.

【0020】一方、触媒微粒子7,…を沈降分離した上
澄みの処理水は第2排水路17より反応槽1の水位差aに
より第2沈殿槽12の内筒13内に供給され、上記同様に内
筒13内では処理水中に含まれる触媒微粒子7,…が沈降
分離され、分離された触媒微粒子7,…の一部は濾過膜
14に捕集され、また上澄みの処理水は排水口15より排水
される。
On the other hand, the supernatant treated water obtained by settling and separating the catalyst fine particles 7, ... Is supplied from the second drainage channel 17 into the inner cylinder 13 of the second settling tank 12 due to the water level difference a of the reaction tank 1, and the same as above. In the inner cylinder 13, the catalyst fine particles 7, ... contained in the treated water are sedimented and separated, and a part of the separated catalyst fine particles 7 ,.
The treated water collected in 14 and the supernatant is drained from the drain port 15.

【0021】更に、第1沈殿槽8と第2沈殿槽12の底部
に溜る触媒微粒子7,…を含んだ処理水はバルブ20,20
をドレイン側に切り替えて外部に排出させるようにして
もよいが、圧送ポンプ19を作動してその全部又は一部を
処理槽1に戻すようにしてもよい。
Further, the treated water containing the catalyst fine particles 7, ... Collected at the bottoms of the first settling tank 8 and the second settling tank 12 are valves 20, 20.
May be switched to the drain side to be discharged to the outside, or the pressure feed pump 19 may be operated to return all or part of it to the processing tank 1.

【0022】なお、第1沈殿槽8と第2沈殿槽12に供給
される処理水の割合は例えば3:1とする。
The ratio of treated water supplied to the first settling tank 8 and the second settling tank 12 is, for example, 3: 1.

【0023】[0023]

【発明の効果】以上要するに、この発明によれば被処理
水中に二酸化チタン等の微粒子を懸濁させて赤外線ラン
プの周囲を通過させて紫外線照射処理を行なうに際して
処理後の水中に含まれる二酸化チタン等の微粒子の分
離、回収が効率的に行なうことができる。
In summary, according to the present invention, fine particles such as titanium dioxide are suspended in the water to be treated and passed through the periphery of the infrared lamp to carry out the ultraviolet irradiation treatment, so that the titanium dioxide contained in the treated water is treated. It is possible to efficiently separate and collect fine particles such as.

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

【図1】この発明の一実施例を示す概略図FIG. 1 is a schematic view showing an embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1 反応槽 6 紫外線ランプ 7,… 触媒微粒子 8 第1沈殿槽 12 第2沈殿槽 1 reaction tank 6 UV lamp 7, ... Catalyst fine particles 8 First settling tank 12 Second settling tank

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 紫外線照射ランプを挿入した反応槽に、
1段又は2段以上の沈殿槽を並設し、反応槽には触媒微
粒子を懸濁させた被処理水を送入し、該反応槽での水位
を一定に保ちながら上記ランプより紫外線を照射して触
媒微粒子により被処理水を浄化、処理し、次に反応槽で
の処理水をオーバーフローさせて沈殿槽に送り込み、該
沈殿槽では処理水中の触媒微粒子を沈降分離させ、沈殿
槽の底部からは触媒微粒子を含む処理水の全部又は一部
を必要とあれば上記反応槽に戻すようにしたことを特徴
とする光酸化処理方法。
1. A reaction tank in which an ultraviolet irradiation lamp is inserted,
One or two or more stages of settling tanks are installed side by side, and water to be treated in which catalyst fine particles are suspended is fed into the reaction tank, and ultraviolet rays are irradiated from the above lamp while keeping the water level in the reaction tank constant. Then, the water to be treated is purified and treated with the catalyst fine particles, and then the treated water in the reaction tank is overflowed and sent to the settling tank, where the catalyst fine particles in the treated water are separated by sedimentation from the bottom of the settling tank. Is a photooxidation treatment method, wherein all or part of the treated water containing catalyst fine particles is returned to the above reaction tank if necessary.
【請求項2】 紫外線照射ランプを挿入した反応槽に、
1段又は2段以上の沈殿槽を並設したことを特徴とする
光酸化処理装置。
2. A reaction vessel having an ultraviolet irradiation lamp inserted therein,
A photo-oxidation treatment device, wherein one or two or more stages of precipitation tanks are arranged in parallel.
JP20107191A 1991-07-17 1991-07-17 Treatment and device for photooxidation Pending JPH0523681A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP20107191A JPH0523681A (en) 1991-07-17 1991-07-17 Treatment and device for photooxidation

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP20107191A JPH0523681A (en) 1991-07-17 1991-07-17 Treatment and device for photooxidation

Publications (1)

Publication Number Publication Date
JPH0523681A true JPH0523681A (en) 1993-02-02

Family

ID=16434911

Family Applications (1)

Application Number Title Priority Date Filing Date
JP20107191A Pending JPH0523681A (en) 1991-07-17 1991-07-17 Treatment and device for photooxidation

Country Status (1)

Country Link
JP (1) JPH0523681A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE4040060A1 (en) * 1989-12-22 1991-07-04 T An T Kk SLIDE SWITCH
KR100390652B1 (en) * 1999-07-16 2003-07-07 주식회사 에콜로넷 Method for treating a waste water using a photocatalytic reaction
CN103183396A (en) * 2013-03-23 2013-07-03 宁波大学 Expansion method of reactor for secondary-pollution-preventing wastewater degradation through ultraviolet catalysis
CN103193290A (en) * 2013-03-23 2013-07-10 宁波大学 Large-capacity ultraviolet light catalysis device having function of preventing secondary pollution and used for wastewater degradation
CN103204565A (en) * 2013-03-23 2013-07-17 宁波大学 Microwave synergistic photocatalysis wastewater degradation reactor capable of avoiding secondary pollution of surplus ozone
JP2018043233A (en) * 2016-09-09 2018-03-22 パナソニックIpマネジメント株式会社 Method and apparatus for liquid treatment

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6342792A (en) * 1986-08-07 1988-02-23 Hosokawa Micron Kk Method for cleaning liquid by utilizing titanium oxide
JPH02298393A (en) * 1989-05-15 1990-12-10 Raizaa Kogyo Kk Photo-oxidation treatment method and apparatus

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6342792A (en) * 1986-08-07 1988-02-23 Hosokawa Micron Kk Method for cleaning liquid by utilizing titanium oxide
JPH02298393A (en) * 1989-05-15 1990-12-10 Raizaa Kogyo Kk Photo-oxidation treatment method and apparatus

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE4040060A1 (en) * 1989-12-22 1991-07-04 T An T Kk SLIDE SWITCH
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CN103183396A (en) * 2013-03-23 2013-07-03 宁波大学 Expansion method of reactor for secondary-pollution-preventing wastewater degradation through ultraviolet catalysis
CN103193290A (en) * 2013-03-23 2013-07-10 宁波大学 Large-capacity ultraviolet light catalysis device having function of preventing secondary pollution and used for wastewater degradation
CN103204565A (en) * 2013-03-23 2013-07-17 宁波大学 Microwave synergistic photocatalysis wastewater degradation reactor capable of avoiding secondary pollution of surplus ozone
JP2018043233A (en) * 2016-09-09 2018-03-22 パナソニックIpマネジメント株式会社 Method and apparatus for liquid treatment

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