JPH11104632A - Device and method for cleaning water - Google Patents

Device and method for cleaning water

Info

Publication number
JPH11104632A
JPH11104632A JP27415497A JP27415497A JPH11104632A JP H11104632 A JPH11104632 A JP H11104632A JP 27415497 A JP27415497 A JP 27415497A JP 27415497 A JP27415497 A JP 27415497A JP H11104632 A JPH11104632 A JP H11104632A
Authority
JP
Japan
Prior art keywords
water
purified
reaction vessel
lamp
vertical axis
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
JP27415497A
Other languages
Japanese (ja)
Inventor
Takeshi Kaburagi
毅 鏑木
Itsuo Uragami
逸男 浦上
Ikuaki Orikata
郁映 織方
Jun Tanaka
順 田中
Makio Tamura
真紀夫 田村
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.)
Organo Corp
Chiyoda Kohan Co Ltd
Original Assignee
Organo Corp
Chiyoda Kohan Co Ltd
Japan Organo 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 Organo Corp, Chiyoda Kohan Co Ltd, Japan Organo Co Ltd filed Critical Organo Corp
Priority to JP27415497A priority Critical patent/JPH11104632A/en
Publication of JPH11104632A publication Critical patent/JPH11104632A/en
Pending legal-status Critical Current

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  • Physical Water Treatments (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a device and a method for cleaning water in which useless organic substances existing in water to be cleaned is efficiently decomposed and removed at large treatment capacity by using a low-voltage ultraviolet lamp of high output. SOLUTION: The device for cleaning water is equipped with a first reaction vessel 3 whose inside is a cylindrical shape, a UV-lamp 7 provided along the central vertical axis of the first reaction vessel 3, an injection nozzle 8 for injecting water to be cleaned in the circumferential direction in a belt-shape to the prescribed part of the outer periphery in the inside of the first reaction vessel and a dissolving circulation means 10 which draws out water to be cleaned from the lower part of the vicinity of the central vertical axis and dissolves ozone and circulates water to be cleaned to the injection nozzle 8. Furthermore, the device for cleaning water is equipped with a second reaction vessel 18 introducing intermediately cleaned water of the first reaction vessel 3, the UV-lamp 7 provided along the central vertical axis of the second reaction vessel 18, a circulation means 21 which diffuses gas in the lower part of the vicinity of the central vertical axis and circulates the introduced intermediately cleaned water and a pulling-out means 25 for flowing out cleaned water in which organic substances remaining in the intermediately cleaned water is decomposed and removed.

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、被浄化水中に存在
する無用な有機物を効率よく分解、除去する水浄化装置
及び水浄化方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a water purification apparatus and a water purification method for efficiently decomposing and removing useless organic substances present in water to be purified.

【0002】[0002]

【従来の技術】水中でオゾンに紫外線を照射して酸化力
の極めて強いヒドロキシラジカル(以下「OH・」とも
記す)を発生させ、それによって水中に存在する無用な
有機物を効率よく酸化分解し、殺菌又は工場排水の脱色
等、特にCOD、BOD、TOC(全有機炭素含量)等
の値を減少させる水浄化装置又は水浄化方法としては、
多種のものが提案又は実用化されており、その総てが縦
長の一つの反応筒の中で、その中心軸上乃至これに沿っ
て直管状の紫外線ランプを配置し、反応筒の底部から微
細気泡状のオゾン含有ガスを吹き込みつつ、又はオゾン
を前以て溶解した後に、その被浄化水を反応筒の下部又
は上部から連続的に導入し、紫外線を照射しながら浄化
するものである。
2. Description of the Related Art Ozone is irradiated with ultraviolet rays in water to generate hydroxyl radicals (hereinafter also referred to as "OH.") Having extremely strong oxidizing power, thereby efficiently oxidizing and decomposing unnecessary organic substances present in water. As a water purification device or a water purification method for reducing the values of sterilization or decolorization of factory wastewater, particularly COD, BOD, TOC (total organic carbon content), and the like,
Various types have been proposed or put into practical use, all of which have a single vertically elongated reaction tube, in which a straight-tube ultraviolet lamp is arranged on or along the center axis thereof, and a fine ultraviolet lamp is arranged from the bottom of the reaction tube. The water to be purified is continuously introduced from the lower or upper part of the reaction tube while blowing a bubble-like ozone-containing gas or after dissolving ozone in advance, and is purified by irradiating ultraviolet rays.

【0003】[0003]

【発明が解決しようとする課題】しかしながら、上記水
浄化装置又は水浄化方法は、その総てが光源として低出
力の低圧紫外線ランプを用いているため、大量の水を処
理しようとすると、紫外線ランプを多数使用せねばなら
ず、多数の紫外線ランプを装着した複雑な構造の、従っ
て取り扱いが不便で高価なものを用いるか、或は少数の
紫外線ランプを装着したものを多数必要とする等の問題
が有った。
However, since all of the above-mentioned water purifying apparatuses or water purifying methods use low-output low-pressure ultraviolet lamps as light sources, when a large amount of water is to be treated, the ultraviolet lamps are not used. A complicated structure with a large number of UV lamps installed, and therefore an inconvenient and expensive one is used, or a large number of those with a small number of UV lamps are required. There was.

【0004】一方、使用する紫外線ランプの本数を少な
くするために高出力の低圧紫外線ランプを用いる試みも
なされているが、効率が悪く実用性に乏しかった。
[0004] On the other hand, attempts have been made to use high-output low-pressure ultraviolet lamps in order to reduce the number of ultraviolet lamps used, but the efficiency is poor and the practicality is poor.

【0005】本発明の課題は、被浄化水を浄化する水浄
化装置又は水浄化方法において、被浄化水中に存在する
無用な有機物を効率よく分解、除去することが出来、且
つ処理能力の大きいことである。
An object of the present invention is to provide a water purification apparatus or a water purification method for purifying water to be purified, in which unnecessary organic substances present in the water to be purified can be efficiently decomposed and removed, and the processing ability is large. It is.

【0006】[0006]

【課題を解決するための手段】本発明は、水中でオゾン
に紫外線を照射して酸化力の極めて強いOH・を発生さ
せ、それによって水中に存在する無用な有機物を効率よ
く酸化分解し、殺菌又は工場排水の脱色等、特にCO
D、BOD、TOC(全有機炭素含量)等の値を減少す
る水浄化装置又は水浄化方法であって、例えば一本の高
出力ランプを用いて従来の低出力ランプを装着したもの
の十乃至二十数倍の処理能力を有する効率の良い水浄化
装置又は水浄化方法を提供する。
The present invention irradiates ozone with ultraviolet light in water to generate OH. Having an extremely strong oxidizing power, thereby efficiently oxidizing and decomposing unnecessary organic substances present in the water and disinfecting it. Or decolorization of industrial wastewater, especially CO
A water purifying apparatus or a water purifying method for reducing the values of D, BOD, TOC (total organic carbon content), etc. Provided is an efficient water purification device or a water purification method having more than ten times the processing capacity.

【0007】本発明者等は、高出力ランプを用いて高い
照度でオゾンを含む被浄化水を照射した場合と、低出力
紫外線ランプを用いた場合とについて、反応系内の成分
組成の経時変化を詳細に比較検討した。その結果、ラン
プ出力の強さに応じた光の到達距離に見合った大きさの
反応筒を用いようとしても、オゾンによる紫外線の吸収
率が非常に高いために、反応槽を激しく撹拌して総ての
水がランプ表面に近づけるようにしない限り、紫外線ラ
ンプ表面の極く近傍のオゾンしかOH・の生成による水
浄化反応に使われず、紫外線ランプ出力の強化は装置の
スケールアップにそのまま寄与しないこと、更に、高い
紫外線照度は高濃度のオゾンから高濃度のOH・を生成
させるために、そのOH・は有機物と出会ってそれを酸
化分解するよりもOH・同士で出会ってH22に変化す
る割合が増大するために分解効率は低下すること等が分
かった。
[0007] The inventors of the present invention have found that the change in the composition of the components in the reaction system with time is different between the case where the purified water containing ozone is irradiated with high illuminance using a high output lamp and the case where a low output ultraviolet lamp is used. Were compared in detail. As a result, even if an attempt is made to use a reaction tube having a size commensurate with the light reaching distance according to the intensity of the lamp output, the absorption rate of ultraviolet light by ozone is extremely high. Unless all the water is brought close to the lamp surface, only the ozone in the immediate vicinity of the UV lamp surface is used for water purification reaction by the generation of OH.Enhancing the UV lamp output does not directly contribute to the scale-up of the equipment. further, high ultraviolet intensity in order to produce a high concentration OH · from a high concentration of ozone, change in H 2 O 2 met with OH · between than its OH · to oxidize and decompose it met organics It has been found that the decomposition efficiency is reduced due to an increase in the rate of the decomposition.

【0008】これらの知見に基づき、オゾンが分解した
後の有機物分解反応は紫外線によるH22のOH・への
変化という遅い反応を経由することになるから、その反
応に適した、均一に撹拌しながら照射する浄化装置乃至
浄化方法が必要なことを勘案し、鋭意工夫・検討を重ね
た結果、本発明に到達した。即ち、供給される被浄化水
中に含ませたオゾンに紫外線を照射して前記被浄化水中
に含まれる有機物を分解し、除去して流出させる水浄化
装置において、内部が円筒形状の反応容器と、該反応容
器の中心鉛直軸に沿って設けられた紫外線ランプと、前
記被浄化水を前記反応容器内周の周方向に吹き込みさせ
る吹込手段と、前記中心鉛直軸近傍の下から前記被浄化
水を抜き出してオゾンを溶解させ前記吹込手段に循環さ
せる溶解循環手段とを備えた第一反応槽と、該第一反応
槽で処理した中間浄化水を前記中心鉛直軸近傍の流出口
を介して導入する第二反応槽とからなり、該第二反応槽
は該反応槽の中心鉛直軸に沿って設けられた紫外線ラン
プと、前記導入された中間浄化水を循環させる循環手段
と、前記中間浄化水中の残りの有機物を分解し、除去し
た浄化水を流出させる抜出手段とを備えたことである。
[0008] Based on these findings, the decomposition reaction of organic matter after the decomposition of ozone passes through a slow reaction of changing H 2 O 2 to OH · by ultraviolet rays, so that it is suitable for the reaction, In consideration of the necessity of a purifying device or a purifying method for irradiation while stirring, the present inventors have made extensive studies and studies and as a result have arrived at the present invention. That is, in a water purification device that irradiates ultraviolet rays to ozone contained in the supplied purified water to decompose organic substances contained in the purified water and removes and removes the organic matter, a reaction vessel having a cylindrical inside, An ultraviolet lamp provided along the center vertical axis of the reaction vessel, blowing means for blowing the water to be purified in the circumferential direction of the inner periphery of the reaction vessel, and the water to be purified from below the vicinity of the center vertical axis. A first reaction tank provided with a dissolving and circulating means for extracting and dissolving ozone and circulating it to the blowing means, and intermediate purified water treated in the first reaction tank is introduced through an outlet near the central vertical axis. A second reaction tank, wherein the second reaction tank is provided with an ultraviolet lamp provided along a central vertical axis of the reaction tank, a circulating means for circulating the introduced intermediate purified water, and Break down the remaining organic matter, It is provided with a draw-out means for flowing out the removed purified water.

【0009】第一反応槽では被浄化水を反応容器内周の
周方向に吹き込みさせる吹込手段を備えたことにより、
被浄化水は内部が円筒形状の反応容器内周の周方向に吹
き込みされる。更に、中心鉛直軸近傍から被浄化水を抜
き出し、オゾンを溶解させてから上記吹込手段に循環さ
せる溶解循環手段により、被浄化水は当初反応容器内周
に沿って移動し、徐々に中心鉛直軸の紫外線ランプの周
囲をスパイラル状に移動乃至旋回しながら次第に紫外線
ランプに近づく。その過程で被浄化水中の有害な有機物
は分解される。
The first reaction tank is provided with a blowing means for blowing the water to be purified in the circumferential direction of the inner circumference of the reaction vessel.
The water to be purified is blown in the circumferential direction of the inner circumference of the reaction vessel having a cylindrical shape. Further, the water to be purified is drawn out from the vicinity of the center vertical axis, and the water to be purified initially moves along the inner periphery of the reaction vessel by the dissolving and circulating means for dissolving the ozone and then circulating the water to the blowing means, and gradually the central vertical axis. Gradually approaching the ultraviolet lamp while moving or turning in a spiral shape around the ultraviolet lamp. In the process, harmful organic matter in the water to be purified is decomposed.

【0010】上記分解反応が行なわれる第一反応槽は、
オゾンを含む被浄化水の全体が紫外線ランプの近傍を通
過するようにした構造で、被浄化水は反応容器中心鉛直
軸の紫外線ランプの遠い所から導入され、紫外線ランプ
の周囲をスパイラル状に循環しながら次第に紫外線ラン
プに近づく。このため、反応容器に導入されたばかりで
高濃度のオゾンを含む被浄化水は、当初ランプから遠く
て照度が弱い紫外線に照射されて低濃度のOH・を生成
するから、H22への変化の割合は少なく、効率良く有
機物と出会ってそれを分解し、これによって次第に低濃
度になるオゾン水は、次第に紫外線を吸収しなくなるか
ら光を遠くまで透過するようになるので、反応槽を大き
くしても反応槽の容積を有効に使うことが出来る。その
上、紫外線ランプに近づくに従って照度は高くなって
も、オゾン濃度は低くなっているので低濃度のOH・し
か生成しないから、H22の生成も遅く、有機物分解反
応を効率よく進めることが出来る。
[0010] The first reaction tank in which the above decomposition reaction is carried out comprises:
The structure is such that the whole of the water to be purified, including ozone, passes near the UV lamp. The water to be purified is introduced from the far side of the UV lamp on the vertical axis of the center of the reaction vessel, and circulates spirally around the UV lamp. As it gradually approaches the UV lamp. Therefore, the cleaning water containing a high concentration of ozone was only introduced into the reaction vessel, because generating a low concentration OH · of being irradiated to the far illuminance weak ultraviolet originally lamps, to H 2 O 2 The rate of change is small, and it efficiently encounters organic matter and decomposes it, and as a result, ozone water, which gradually becomes low in concentration, gradually absorbs ultraviolet light and transmits light far away. Even so, the volume of the reaction tank can be used effectively. In addition, even if the illuminance increases as the UV lamp is approached, the ozone concentration is low and only low-concentration OH is generated, so the generation of H 2 O 2 is slow and the organic matter decomposition reaction proceeds efficiently. Can be done.

【0011】更に、上記水浄化装置において、前記吹込
手段は、前記反応容器内周の所定の箇所に設けられ前記
被浄化水を周方向に帯状に吹き込みさせる吹込ノズルで
ある。この吹込ノズルにより確実に被浄化水を反応容器
の内周に沿って層流の帯状に吹き込み、スパイラル状に
移動乃至旋回させることを、簡便な構造で行なうことが
出来る。
Further, in the above-mentioned water purifying apparatus, the blowing means is a blowing nozzle provided at a predetermined position on the inner periphery of the reaction vessel for blowing the water to be purified in a belt shape in a circumferential direction. With this blowing nozzle, the water to be purified can be reliably blown in a laminar band along the inner periphery of the reaction vessel and moved or swirled in a spiral manner with a simple structure.

【0012】第二反応槽に導入された中間浄化水は、循
環手段によって循環されつつ、第一反応槽で生成したH
22は第二反応槽に備えられた紫外線ランプから発生す
る紫外線によって照射され、緩やかに分解してOH・と
なり、これによって中間浄化水中の残りの有機物を酸
化、分解する。
[0012] The intermediate purified water introduced into the second reaction tank is circulated by the circulating means while the H produced in the first reaction tank is circulated.
2 O 2 is irradiated by ultraviolet rays generated from an ultraviolet lamp provided in the second reaction tank, and is slowly decomposed into OH ·, thereby oxidizing and decomposing remaining organic substances in the intermediate purified water.

【0013】そして、前記の循環手段は、前記中心鉛直
軸近傍に設けられ気体を撒気させてエアリフト方式によ
り前記中間浄化水を循環させるものであり、中間浄化水
は中心鉛直軸上の紫外線ランプを中心とするドーナツ状
に循環させられるので、均一な紫外線照射を受ける。
The circulating means is provided in the vicinity of the central vertical axis to diffuse gas and circulate the intermediate purified water by an air lift method, and the intermediate purified water is an ultraviolet lamp on the central vertical axis. Circulates in the form of a donut centered at the center, and receives uniform ultraviolet irradiation.

【0014】要するに上記水浄化方法の特徴は、供給さ
れる被浄化水中にオゾンを含ませて、これに紫外線を照
射して前記被浄化水中に含まれる有機物を分解し、除去
して流出させる水浄化方法において、前記オゾンを含む
被浄化水及び紫外線から直接生成するヒドロキシラジカ
ル(OH・)によって有機物を分解する第1の水浄化工
程と、主として前記ヒドロキシラジカルから生成する過
酸化水素と紫外線、及びオゾンを含む水と紫外線から生
成するヒドロキシラジカルによって前記第1の水浄化工
程で前記被浄化水を浄化した中間浄化水中の残りの有機
物を分解する第2の水浄化工程とを含むことである。
In short, the feature of the water purification method is that ozone is contained in the supplied water to be purified, and ultraviolet light is applied to the water to decompose, remove, and remove the organic substances contained in the water to be purified. In the purification method, a first water purification step of decomposing an organic substance by a hydroxyl radical (OH.) Directly generated from the ozone-containing water to be purified and ultraviolet light, and hydrogen peroxide and ultraviolet light mainly generated from the hydroxy radical, and A second water purification step of decomposing remaining organic substances in the intermediate purified water, which has purified the water to be purified in the first water purification step, with hydroxyl radicals generated from water containing ozone and ultraviolet rays.

【0015】更に、上記水浄化方法の特徴は、前記第1
の水浄化工程では、前記オゾンを含む被浄化水を紫外線
ランプから遠い箇所に導入し、該紫外線ランプの周囲を
スパイラル状に循環させながら次第に該紫外線ランプに
近づけさせ、前記第2の水浄化工程では、前記第1の水
浄化工程で浄化された中間浄化水を出来るだけ均一に前
記紫外線ランプの照射する紫外線に当るように循環させ
ることである。
Further, the feature of the water purification method is that the first
In the water purification step, the water to be purified containing the ozone is introduced into a location far from the ultraviolet lamp, and is gradually approached to the ultraviolet lamp while being circulated in a spiral around the ultraviolet lamp. Then, the intermediate purified water purified in the first water purification step is circulated as uniformly as possible so as to irradiate the ultraviolet rays emitted by the ultraviolet lamp.

【0016】[0016]

【発明の実施の形態】以下、本発明の水浄化装置及び水
浄化方法の実施の形態の例を図面に基づいて具体的に説
明する。
BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, embodiments of a water purification apparatus and a water purification method of the present invention will be specifically described with reference to the drawings.

【0017】図1は、本発明に係る水浄化装置の一実施
の形態を示す系統図、図2は、図1の I−I 線断面図で
ある。本実施の形態の水浄化装置1は、ポンプ6又は重
力式で供給される被浄化水39中に含ませたオゾンに紫
外線を照射して被浄化水39中に含まれる有機物を分解
し、除去して流出させるもので、第一反応槽2と第二反
応槽17を主要部とする。即ち、第一反応槽2は、内部
が円筒形状の反応容器である第1反応容器3と、この第
1反応容器の中心鉛直軸4に沿って設けられたUVラン
プ(又は紫外線ランプ)7と、被浄化水39を第1反応
容器内周5の周方向に吹き込みさせる吹込手段としての
吹込ノズル8と、中心鉛直軸4近傍から被浄化水を抜き
出してオゾンを溶解させ吹込ノズル8に循環させる溶解
循環手段10とを備えている。
FIG. 1 is a system diagram showing an embodiment of a water purification apparatus according to the present invention, and FIG. 2 is a sectional view taken along the line II of FIG. The water purification device 1 of the present embodiment decomposes and removes organic substances contained in the water 39 to be purified by irradiating the ozone contained in the water 39 to be purified supplied by the pump 6 or gravity with ultraviolet rays. The first reaction tank 2 and the second reaction tank 17 are used as main parts. That is, the first reaction vessel 2 includes a first reaction vessel 3 whose inside is a cylindrical reaction vessel, and a UV lamp (or an ultraviolet lamp) 7 provided along the center vertical axis 4 of the first reaction vessel. A blowing nozzle 8 as a blowing means for blowing the water to be purified 39 in the circumferential direction of the inner periphery 5 of the first reaction vessel; And a dissolution circulation means 10.

【0018】図2に示すように、第1反応容器3は、少
なくとも内側形状が円筒形で、中心部にUVランプ7を
挿入するための保護管30が設けられている。勿論、保
護管30は紫外線を透過する材質で形成されている。吹
込ノズル8は、第1反応容器3内周の所定の箇所に設け
られ、被浄化水39を周方向に帯状に吹き込みさせるも
のである。更に、図1に示すように、吹込ノズル8は、
第1反応容器3の高さ寸法にできる限り近い寸法で縦方
向に設けられ、その中間位置又は下端に被浄化水39を
導入する導入口8aと、図2に示すように縦方向全長に
渡って均等な速度で帯状に吹き出すように開口したスリ
ット8bとが設けられている。尚、本実施の形態におい
ては、吹込ノズル8は一つであるが、円周方向に適宜複
数設けることも出来る。
As shown in FIG. 2, the first reaction vessel 3 has at least a cylindrical inner shape, and is provided with a protective tube 30 for inserting the UV lamp 7 at the center thereof. Of course, the protection tube 30 is formed of a material that transmits ultraviolet rays. The blowing nozzle 8 is provided at a predetermined position on the inner periphery of the first reaction vessel 3 and blows the purified water 39 in a belt shape in the circumferential direction. Further, as shown in FIG.
An inlet 8a for introducing purified water 39 at an intermediate position or a lower end of the first reaction vessel 3 at a length as close as possible to the height dimension of the first reaction vessel 3 is provided. And a slit 8b which is opened so as to blow out at a uniform speed in a strip shape. In the present embodiment, the number of the blow nozzles 8 is one, but a plurality of blow nozzles 8 may be provided as appropriate in the circumferential direction.

【0019】溶解循環手段10は、第1反応容器3の中
心部寄りに設けられた抜出口12と、この抜出口12か
ら浄化中の被浄化水を抜き出すと共に、オゾン(O3
41を強制的に溶解させて吹込ノズル8に循環させるポ
ンプ13と、これらをつなぐ循環配管とを有する。
The dissolving and circulating means 10 is provided with a discharge port 12 provided near the center of the first reaction vessel 3, and through this discharge port 12, water to be purified which is being purified is extracted, and ozone (O 3 ) is discharged.
It has a pump 13 for forcibly dissolving 41 and circulating it to the blowing nozzle 8, and a circulating pipe connecting these.

【0020】更に、本実施の形態の水浄化装置1は、第
二反応槽17を有し、この槽は、第1反応容器3で被浄
化水39が反応した中間浄化水40を第1反応容器3の
中心鉛直軸と共通の中心鉛直軸4近傍の流出口である開
口部15を介して導入する別の反応容器としての第2反
応容器18と、中心鉛直軸4に沿って設けられ第1反応
容器3の中心鉛直軸に沿って設けられたUVランプと共
通のUVランプ7と、導入された中間浄化水40を循環
させる循環手段21と、中間浄化水40中の残りの有機
物を分解し、除去した浄化水42を流出させる抜出手段
25とを備えている。
Further, the water purification apparatus 1 of the present embodiment has a second reaction tank 17, which converts the intermediate purified water 40 reacted with the purified water 39 in the first reaction vessel 3 into a first reaction tank 17. A second reaction vessel 18 as another reaction vessel introduced through an opening 15 which is an outlet near the central vertical axis 4 common to the central vertical axis of the vessel 3 and a second reaction vessel 18 provided along the central vertical axis 4 1 UV lamp 7 provided in common with a UV lamp provided along the central vertical axis of reaction vessel 3, circulating means 21 for circulating introduced intermediate purified water 40, and decomposing the remaining organic matter in intermediate purified water 40 And an extraction means 25 for allowing the purified water 42 removed to flow out.

【0021】第2反応容器18は、第1反応容器3と同
じく、少なくとも内側形状が円筒形で、中心部にUVラ
ンプ7を挿入するための保護管30が設けられている。
勿論、保護管30は紫外線を透過する材質で形成されて
いる。第2反応容器18の上面には排気孔31が設けら
れている。
The second reaction vessel 18, like the first reaction vessel 3, has at least a cylindrical inner shape and is provided with a protection tube 30 for inserting the UV lamp 7 at the center thereof.
Of course, the protection tube 30 is formed of a material that transmits ultraviolet rays. An exhaust hole 31 is provided on the upper surface of the second reaction vessel 18.

【0022】循環手段21は、中心鉛直軸4近傍に環状
撒気管22が設けられ気体(空気)43を撒気させて中
間浄化水40を第2反応容器18の中でドーナツ状に循
環させるものである。環状撒気管22には、その円周方
向に適宜気体43を撒気させる図示していない撒気孔が
設けられている。
The circulating means 21 is provided with an annular gas diffuser 22 in the vicinity of the central vertical axis 4 to diffuse gas (air) 43 to circulate the intermediate purified water 40 in a donut shape in the second reaction vessel 18. It is. The annular gas diffuser 22 is provided with a gas diffuser (not shown) through which gas 43 is appropriately diffused in the circumferential direction.

【0023】抜出手段25は、第2反応容器18内のド
ーナツ状循環流の略中心部から抜き出す抜出口26と、
抜き出した浄化水42を溢流口27から溢流させて貯め
る溢流タンク28と、これらを接続する配管とを有す
る。抜出口26は、第1反応容器3と第2反応容器18
との隔壁35の外周部の第一反応槽側、例えば位置37
辺りに取り付けられても良い。
The withdrawing means 25 has a withdrawal outlet 26 for withdrawing from a substantially central portion of the donut-shaped circulating flow in the second reaction vessel 18,
There is an overflow tank 28 for storing the extracted purified water 42 by overflowing from the overflow port 27, and a pipe for connecting these. The outlet 26 is provided between the first reaction vessel 3 and the second reaction vessel 18.
Of the outer peripheral portion of the partition wall 35 with the first reaction tank, for example, the position 37
It may be attached around.

【0024】以上の構造を有する本実施の形態の水浄化
装置1は、次のように作用する。即ち、被処理水39
は、ポンプ6により供給されるが、溶解循環手段10に
より、途中でオゾン溶解及び循環用ポンプ13を経てオ
ゾンを強制溶解される。更に、被浄化水39は、吹込ノ
ズル8により第1反応容器3の内周に沿って帯状に吹き
込まれ、当初第1反応容器3内周に沿って移動し、徐々
に中心鉛直軸のUVランプ7の周囲をスパイラル状に移
動乃至旋回しながら次第にUVランプ7に近づく。その
間に、溶解していたオゾンはOH・となり、その一部は
有機物の分解に使われ、残りはH22に変化する。
The water purifying apparatus 1 of the present embodiment having the above structure operates as follows. That is, the water 39 to be treated
Is supplied by a pump 6, and ozone is forcibly dissolved by a dissolving and circulating means 10 through an ozone dissolving and circulation pump 13 on the way. Further, the purified water 39 is blown in a band shape along the inner circumference of the first reaction vessel 3 by the blowing nozzle 8, initially moves along the inner circumference of the first reaction vessel 3, and gradually has a UV lamp having a central vertical axis. 7 gradually approaches the UV lamp 7 while moving or turning in a spiral around the periphery of the UV lamp 7. During that time, the dissolved ozone becomes OH. A part of the ozone is used for decomposing organic substances, and the rest is changed to H 2 O 2 .

【0025】この際、被浄化水の大部分は、第1反応容
器3の底部UVランプ7に近い抜出口12から抜き出さ
れ、他の一部は溶け残った少量のオゾンと大部分の酸素
の泡と共に開口部15を通って第2反応容器18に移行
する。抜出口12から抜き出された被浄化水はポンプ1
3によって再びオゾンを溶解されて導入口8aを介して
第1反応容器3内に導入され循環される。
At this time, most of the water to be purified is withdrawn from the outlet 12 near the UV lamp 7 at the bottom of the first reaction vessel 3, and the other part is a small amount of dissolved ozone and most of the oxygen. Then, the liquid flows through the opening 15 to the second reaction vessel 18 together with the foam. The purified water extracted from the outlet 12 is pump 1
The ozone is dissolved again by 3 and introduced into the first reaction vessel 3 through the inlet 8a and circulated.

【0026】第一反応槽2は、オゾンを含む被浄化水の
全体をUVランプ7の表面に向けて暫次近づかせるよう
に設計されており、被浄化水は第1反応容器3の中心鉛
直軸のUVランプ7から円筒型反応器の接線方向に導入
され、UVランプ7の周囲をスパイラル状に循環しなが
ら次第にUVランプ7に近づく。このため、第1反応容
器3に導入されたばかりの被浄化水に含まれる高濃度の
オゾンはUVランプ7から遠くて照度が弱い紫外線で照
射されて低濃度のOH・を生成するから、H22への変
化の割合は少なく、効率良く有機物と出会ってそれを分
解し、それによって次第に低濃度になるオゾン水は、次
第に紫外線を吸収しなくなるから光を遠くまで透過する
ようになり、大きくした反応槽の容積を有効に使うこと
が出来る。その上、UVランプ7に近づくに従って照度
は高くなっても、オゾン濃度は低くなっているので低濃
度のOH・しか生成しないから、H22の生成も遅く、
有機物分解反応を効率よく進めることが出来る。
The first reaction tank 2 is designed so that the whole of the water to be purified containing ozone is temporarily approached toward the surface of the UV lamp 7. The UV light is introduced from the axial UV lamp 7 in the tangential direction of the cylindrical reactor, and gradually approaches the UV lamp 7 while circulating in a spiral around the UV lamp 7. Therefore, since a high concentration of ozone contained in the purified water that has just been introduced into the first reaction vessel 3 produces a far illuminance is irradiated with weak ultraviolet lightly doped OH · from UV lamp 7, H 2 The rate of change to O 2 is small, and the ozone water that efficiently meets organic matter and decomposes it, thereby gradually reducing the concentration, gradually loses the absorption of ultraviolet rays, so that it transmits light far away, The used capacity of the reaction tank can be used effectively. Moreover, even if the illumination is higher as the distance from the UV lamp 7, the ozone concentration is lower because not low concentration OH · of only a generation, slower generation of H 2 O 2,
The organic matter decomposition reaction can proceed efficiently.

【0027】更に、第二反応槽17に導入された中間浄
化水40は、循環手段21によって、同伴された気泡と
環状撤気管22から撤気される補助空気の泡によるエリ
アリフト作用によりUVランプ7近傍の照度の高いとこ
ろを上昇し、その間に第一反応槽で生成したH22はO
H・に分解され、このOH・が中間浄化水40中の残存
する残りの有機物とが反応し分解する。循環手段21に
よって分解残のH22を含む中間浄化水40はドーナツ
状循環流となってUV照度の強いところから弱いところ
に掛けて循環、滞留し、H22は殆ど分解し尽くされ、
最終抜出口26を経て溢流口27から溢流となって排出
され、気泡は排気孔31から排出される。
Further, the intermediate purified water 40 introduced into the second reaction tank 17 is circulated by the circulating means 21 so that the UV lamp is illuminated by the area lift effect of the entrained air bubbles and the auxiliary air bubbles evacuated from the annular evacuation pipe 22. The H 2 O 2 generated in the first reaction tank rises at a high illuminance near 7 and O 2
H. The OH. Reacts with the remaining organic matter remaining in the intermediate purified water 40 to be decomposed. The intermediate purified water 40 containing the residual H 2 O 2 is converted into a doughnut-shaped circulating flow by the circulating means 21 to circulate and stay from a place where the UV illuminance is strong to a place where the UV illuminance is weak, and H 2 O 2 is almost completely decomposed. And
The air is discharged as overflow from the overflow port 27 through the final outlet 26, and the air bubbles are discharged from the exhaust hole 31.

【0028】更に、本実施の形態の水浄化装置1は、溶
解したオゾンの濃度及びUVランプの照度から決定され
るそれぞれの最適平均滞留時間で、被浄化水が第一反応
槽2及び第二反応槽17を通過するように、被浄化水処
理量に合わせて設計される。上記の例では、第一反応槽
2と第二反応槽17を下上に配置してUVランプ保護管
を共用しているが、二槽に分離しても効果は同じであ
る。
Further, in the water purification apparatus 1 of the present embodiment, the water to be purified is supplied to the first reaction tank 2 and the second reaction tank 2 at the respective optimum average residence times determined from the concentration of dissolved ozone and the illuminance of the UV lamp. It is designed so as to pass through the reaction tank 17 according to the amount of water to be purified. In the above example, the first reaction tank 2 and the second reaction tank 17 are arranged below and share the UV lamp protection tube, but the effect is the same even if they are separated into two tanks.

【0029】[0029]

【実施例】次に本発明の実施例を示す。図1、2の水浄
化装置において、第一反応槽2の直径100cm、深さ
25cm、第二反応槽17の直径100cm、深さ75
cm、被処理水39の流入量0.9m3/hr、そのT
OC値2ppm、低圧UVランプ出力1.5KW、ポン
プ13による循環速度3.4m3/hrの場合に溢流口
27から溢流された処理完了の浄化水42のTOCは5
00ppbであった。
Next, examples of the present invention will be described. 1 and 2, the first reaction tank 2 has a diameter of 100 cm and a depth of 25 cm, and the second reaction tank 17 has a diameter of 100 cm and a depth of 75 cm.
cm, the inflow rate of the water 39 to be treated 0.9 m 3 / hr, and its T
When the OC value is 2 ppm, the low-pressure UV lamp output is 1.5 KW, and the circulation speed by the pump 13 is 3.4 m 3 / hr, the TOC of the purified water 42 that has been processed and overflowed from the overflow port 27 is 5
00 ppb.

【0030】図3は、比較例としての水浄化装置100
の系統図である。水浄化装置100は、図1、2の水浄
化装置1のような隔壁35の無い反応槽で、被処理水1
01をポンプ102によって反応槽105に供給する。
反応槽105に供給された被処理水101は、反応槽1
05内を循環した後、上部寄りの流出口107から中間
浄化水108としてポンプ103によって抜き出され、
オゾン104を強制溶解されて再度流入口109から反
応槽105に供給され、反応槽105の中心部に配置さ
れたUVランプ106によって浄化される。この水浄化
装置100の場合、同じ流速と循環速度で行なった反応
の結果、排出された浄化水のTOCは、1.8ppm
で、上記本実施の形態の水浄化装置1の値500ppb
に比べ格段に大きく、本実施の形態の水浄化装置1は、
水浄化装置100に比べ被浄化水中の有機物を効率よく
分解、除去することがわかる。
FIG. 3 shows a water purification apparatus 100 as a comparative example.
FIG. The water purification device 100 is a reaction tank without a partition 35 like the water purification device 1 of FIGS.
01 is supplied to the reaction tank 105 by the pump 102.
The water to be treated 101 supplied to the reaction tank 105 is
After circulating through the inside of the pump 05, it is withdrawn from the outlet 107 near the top by the pump 103 as intermediate purified water 108,
Ozone 104 is forcibly dissolved and supplied again to the reaction tank 105 from the inflow port 109, and is purified by the UV lamp 106 disposed at the center of the reaction tank 105. In the case of this water purification apparatus 100, as a result of the reaction performed at the same flow rate and circulation speed, the TOC of the purified water discharged is 1.8 ppm.
Then, the value of the water purification device 1 of the present embodiment is 500 ppb.
The water purification device 1 of the present embodiment is much larger than
It can be seen that the organic matter in the water to be purified is decomposed and removed more efficiently than the water purification apparatus 100.

【0031】[0031]

【発明の効果】本発明の水浄化装置及び水浄化方法によ
れば、被浄化水中に存在する無用な有機物を効率よく分
解、除去することが出来、且つ処理能力が大きい。
According to the water purification apparatus and the water purification method of the present invention, unnecessary organic substances present in the water to be purified can be efficiently decomposed and removed, and the processing capacity is large.

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

【図1】本発明に係る水浄化装置の一実施の形態を示す
系統図である。
FIG. 1 is a system diagram showing one embodiment of a water purification device according to the present invention.

【図2】図1の I−I 線断面図である。FIG. 2 is a sectional view taken along line II of FIG. 1;

【図3】比較例としての水浄化装置の系統図である。FIG. 3 is a system diagram of a water purification device as a comparative example.

【符号の説明】[Explanation of symbols]

1 水浄化装置 2 第一反応槽 3 第1反応容器(反応容器) 4 中心鉛直軸 5 内周 7 UVランプ(紫外線ランプ) 8 吹込ノズル(吹込手段) 10 溶解循環手段 15 開口部(流出口) 17 第二反応槽 21 循環手段 25 抜出手段 39 被浄化水 40 中間浄化水 42 浄化水 DESCRIPTION OF SYMBOLS 1 Water purification apparatus 2 First reaction tank 3 First reaction vessel (reaction vessel) 4 Center vertical axis 5 Inner circumference 7 UV lamp (ultraviolet lamp) 8 Blowing nozzle (blowing means) 10 Melting circulation means 15 Opening (outlet) 17 Second reaction tank 21 Circulation means 25 Extraction means 39 Purified water 40 Intermediate purified water 42 Purified water

───────────────────────────────────────────────────── フロントページの続き (72)発明者 織方 郁映 東京都世田谷区砧8−8−23 (72)発明者 田中 順 埼玉県戸田市川岸1丁目4番9号 オルガ ノ株式会社総合研究所内 (72)発明者 田村 真紀夫 埼玉県戸田市川岸1丁目4番9号 オルガ ノ株式会社総合研究所内 ──────────────────────────────────────────────────続 き Continued on the front page (72) Inventor Ikuei Origata 8-8-23 Kinuta, Setagaya-ku, Tokyo (72) Inventor Jun Tanaka 1-4-9 Kawagishi, Toda City, Saitama Prefecture Organo Corporation In-house (72) Inventor Makio Tamura 1-4-9 Kawagishi, Toda City, Saitama Prefecture Organo Research Institute

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 供給される被浄化水中に含ませたオゾン
に紫外線を照射して前記被浄化水中に含まれる有機物を
分解し、除去して流出させる水浄化装置において、内部
が円筒形状の反応容器と、該反応容器の中心鉛直軸に沿
って設けられた紫外線ランプと、前記被浄化水を前記反
応容器内周の周方向に吹き込みさせる吹込手段と、前記
中心鉛直軸近傍の下から前記被浄化水を抜き出してオゾ
ンを溶解させ前記吹込手段に循環させる溶解循環手段と
を備えた第一反応槽と、該第一反応槽を通過した中間浄
化水を前記中心鉛直軸近傍の流出口を介して導入する第
二反応槽とからなり、該第二反応槽は該反応槽の中心鉛
直軸に沿って設けられた紫外線ランプと、前記導入され
た中間浄化水を循環させる循環手段とを備え、更に前記
第二反応槽の紫外線ランプと前記循環手段とによって前
記中間浄化水中の残りの有機物を分解し、除去した浄化
水を流出させる抜出手段とを備えたことを特徴とする水
浄化装置。
1. A water purification apparatus for irradiating ozone contained in supplied water to be irradiated with ultraviolet rays to decompose, remove, and flow out organic substances contained in the water to be purified, and has a cylindrical reaction inside. A vessel, an ultraviolet lamp provided along the center vertical axis of the reaction vessel, blowing means for blowing the water to be purified in the circumferential direction of the inner circumference of the reaction vessel, and the vessel from below the vicinity of the center vertical axis. A first reaction tank provided with a dissolving and circulating means for extracting purified water to dissolve ozone and circulating the purified water to the blowing means, and passing the intermediate purified water passing through the first reaction tank through an outlet near the center vertical axis. A second reaction tank, which is provided along the central vertical axis of the reaction tank, and a circulating means for circulating the introduced intermediate purified water, Further, the ultraviolet rays in the second reaction tank A water purifying apparatus comprising: a discharge means for decomposing remaining organic matter in the intermediate purified water by the lamp and the circulation means, and for discharging the purified water removed.
【請求項2】 請求項1において、前記吹込手段は、前
記反応容器内周の所定の箇所に設けられ前記被浄化水を
周方向に帯状に吹き込みさせる吹込ノズルであることを
特徴とする水浄化装置。
2. The water purification apparatus according to claim 1, wherein the blowing means is a blowing nozzle provided at a predetermined location on the inner periphery of the reaction vessel and configured to blow the water to be purified in a belt shape in a circumferential direction. apparatus.
【請求項3】 請求項1又は2において、前記循環手段
は、前記中心鉛直軸近傍下方に設けられ気体を撒気させ
て前記中間浄化水を循環させるものであることを特徴と
する水浄化装置。
3. The water purifying apparatus according to claim 1, wherein the circulating means is provided below the vicinity of the center vertical axis and diffuses gas to circulate the intermediate purified water. .
【請求項4】 供給される被浄化水中に含ませたオゾン
に紫外線を照射して前記被浄化水中に含まれる有機物を
分解し、除去して流出させる水浄化方法において、前記
オゾンを含む被浄化水及び紫外線から直接生成するヒド
ロキシラジカル(OH・)によって有機物を分解する第
1の水浄化工程と、主として前記ヒドロキシラジカルか
ら生成する過酸化水素と紫外線、及びオゾンを含む水と
紫外線から生成するヒドロキシラジカルによって前記第
1の水浄化工程で前記被浄化水を処理した中間浄化水中
の残りの有機物を分解する第2の水浄化工程とを含むこ
とを特徴とする水浄化方法。
4. A water purification method for irradiating ultraviolet light to ozone contained in supplied water to be purified to decompose, remove, and flow out organic substances contained in the water to be purified, wherein the ozone-containing water is purified. A first water purification step of decomposing organic substances by hydroxyl radicals (OH.) Directly generated from water and ultraviolet rays, and a hydrogen peroxide and ultraviolet rays mainly generated from the hydroxyl radicals, and a hydroxyl group generated from water and ultraviolet rays containing ozone. A second water purification step of decomposing remaining organic matter in the intermediate purified water obtained by treating the water to be purified in the first water purification step by radicals.
【請求項5】 請求項4において、前記第1の水浄化工
程は、前記オゾンを含む被浄化水を紫外線ランプから遠
い箇所に導入し、該紫外線ランプの周囲をスパイラル状
に循環させながら次第に該紫外線ランプに近づけさせ、
前記第2の水浄化工程は、前記第1の水浄化工程で浄化
された中間浄化水を出来るだけ均一に前記紫外線ランプ
の照射する紫外線に当るように循環させることを特徴と
する水浄化方法。
5. The method according to claim 4, wherein in the first water purification step, the water to be purified containing ozone is introduced into a location far from an ultraviolet lamp, and gradually circulated around the ultraviolet lamp in a spiral manner. Make it closer to the UV lamp,
In the second water purification step, the intermediate purified water purified in the first water purification step is circulated as uniformly as possible so as to irradiate the ultraviolet rays emitted by the ultraviolet lamp.
JP27415497A 1997-10-07 1997-10-07 Device and method for cleaning water Pending JPH11104632A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP27415497A JPH11104632A (en) 1997-10-07 1997-10-07 Device and method for cleaning water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP27415497A JPH11104632A (en) 1997-10-07 1997-10-07 Device and method for cleaning water

Publications (1)

Publication Number Publication Date
JPH11104632A true JPH11104632A (en) 1999-04-20

Family

ID=17537791

Family Applications (1)

Application Number Title Priority Date Filing Date
JP27415497A Pending JPH11104632A (en) 1997-10-07 1997-10-07 Device and method for cleaning water

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Publication number Priority date Publication date Assignee Title
JP2004358467A (en) * 2004-07-16 2004-12-24 National Institute Of Advanced Industrial & Technology Waste liquid treatment equipment

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2004358467A (en) * 2004-07-16 2004-12-24 National Institute Of Advanced Industrial & Technology Waste liquid treatment equipment

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