JP2001347295A - Apparatus for cleaning seawater containing floating substance - Google Patents

Apparatus for cleaning seawater containing floating substance

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Publication number
JP2001347295A
JP2001347295A JP2000172618A JP2000172618A JP2001347295A JP 2001347295 A JP2001347295 A JP 2001347295A JP 2000172618 A JP2000172618 A JP 2000172618A JP 2000172618 A JP2000172618 A JP 2000172618A JP 2001347295 A JP2001347295 A JP 2001347295A
Authority
JP
Japan
Prior art keywords
seawater
tank
liquid
membrane
suspended substances
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP2000172618A
Other languages
Japanese (ja)
Other versions
JP3931279B2 (en
Inventor
Toshiyuki Hara
俊幸 原
Akira Torii
明 鳥居
Tetsuro Sakashita
哲朗 坂下
Masayuki Watabe
正之 渡部
Katsuyuki Machitani
勝幸 町谷
Michihiro Hatsuda
導弘 初田
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.)
Kansai Electric Power Co Inc
Idec Izumi Corp
Original Assignee
Kansai Electric Power Co Inc
Idec Izumi Corp
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 Kansai Electric Power Co Inc, Idec Izumi Corp filed Critical Kansai Electric Power Co Inc
Priority to JP2000172618A priority Critical patent/JP3931279B2/en
Publication of JP2001347295A publication Critical patent/JP2001347295A/en
Application granted granted Critical
Publication of JP3931279B2 publication Critical patent/JP3931279B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Separation Using Semi-Permeable Membranes (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Physical Water Treatments (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a seawater cleaning apparatus simple and small-sized in the constitution, easily controlled in operation and capable of shortening a treatment time. SOLUTION: A liquid to be cleaned is introduced into the flocculating and stirring tank 23 of a pressure float separation apparatus 22 to be subjected to flocculation treatment and the formed floes are floated by air bubbles in a floating tank 24 to be removed as scum by a scum rake 26. Subsequently, the treated liquid is filtered under membrane osmosis pressure in a membrane treatment apparatus 52 to be separated into clarified seawater and unclear seawater. Further, the clarified seawater is oxidized in an UV oxidizing apparatus 58 and the chemical oxygen demand(COD) thereof is lowered.

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】この発明は、海水中のクラゲ
や汚染物質等の浮遊物質を除去する浄化装置に関し、特
に火力発電所、製鉄所、石油精製所、石油化学工場、化
学工場等に好適な浮遊物質含有海水の浄化装置に関す
る。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a purification device for removing suspended substances such as jellyfish and pollutants in seawater, and is particularly suitable for a thermal power plant, a steel mill, an oil refinery, a petrochemical plant, a chemical plant, and the like. The present invention relates to a device for purifying seawater containing suspended substances.

【0002】[0002]

【従来の技術】発電所などでは、海水を冷却水として取
り入れているが、この海水中にはクラゲ、赤潮、アオコ
等と称される有機物からなる浮遊物質が含まれているこ
とがある.このような物質を含有した海水は浮遊物質
(SS)、化学的酸素要求量(COD)が増大した富栄
養化した状態であるため、これを冷却水として使用する
には、事前に浮遊物質等を取り除いて浄化しておくこと
が必要である。そこで、一般には、海水を導入する第1
段階でこれらの物質を除去し、浄化するための浄化装置
を設けている。図1は、発電所システムの概要を示して
いる。同図で、1は浄化装置、2は発電所である。海水
3は浄化装置1に導入されて浮遊物質が取り除かれた後
に発電所2の冷却水用に供給される。
2. Description of the Related Art In power plants and the like, seawater is taken as cooling water, and this seawater sometimes contains suspended matter composed of organic substances such as jellyfish, red tide, and blue-green algae. Since seawater containing such substances is in a eutrophic state in which the suspended solids (SS) and chemical oxygen demand (COD) are increased, in order to use this as cooling water, the suspended solids and the like must be used in advance. It is necessary to remove and purify it. Therefore, generally, the first method to introduce seawater is
A purification device for removing and purifying these substances in stages is provided. FIG. 1 shows an outline of the power plant system. In the figure, reference numeral 1 denotes a purification device, and 2 denotes a power plant. The seawater 3 is supplied to the purification device 1 and used for cooling water of the power plant 2 after removing suspended matters.

【0003】図2は、上記の発電所システム等に使用さ
れる従来の浄化装置の構成を示している。
FIG. 2 shows a configuration of a conventional purification device used in the above-described power plant system and the like.

【0004】海水3はポンプ4によって原水槽5に導入
される。原水槽5に導入された海水3は、さらにポンプ
6により生物的処理のための硝化槽7に導かれる。この
硝化槽7には栄養剤7が投入され、微生物による処理が
行われる。さらに、海水3はメタノール注入装置9から
メタノールが投入された脱窒リアクタ10で脱窒処理さ
れ、また、気泡が形成されているタンク11内で再曝気
槽11を通過して、沈殿槽12に送られる。沈殿槽12
では浮遊物質を自重により沈殿させ、上澄み液を砂ろ過
装置13に送り、ろ過された海水を活性炭吸着装置14
に導入して逆洗処理を行い、処理水として排出する。
[0004] Seawater 3 is introduced into a raw water tank 5 by a pump 4. The seawater 3 introduced into the raw water tank 5 is further guided to a nitrification tank 7 for biological treatment by a pump 6. The nutrient 7 is introduced into the nitrification tank 7, and a treatment with microorganisms is performed. Further, the seawater 3 is subjected to a denitrification treatment in a denitrification reactor 10 into which methanol has been introduced from a methanol injection device 9, and further passes through a re-aeration tank 11 in a tank 11 in which bubbles are formed, and enters a sedimentation tank 12. Sent. Settling tank 12
In this method, suspended substances are settled by their own weight, the supernatant is sent to the sand filtration device 13 and the filtered seawater is collected by the activated carbon adsorption device 14.
And then backwashed and discharged as treated water.

【0005】以上のように、従来の浄化装置は、沈殿処
理、生物処理、化学的処理を複数段階組み合わせて海水
の浄化を行ったり、またはそれらの処理のいずれかを単
独で使用していた。
As described above, the conventional purification apparatus purifies seawater by combining a plurality of stages of sedimentation treatment, biological treatment, and chemical treatment, or uses any of these treatments alone.

【0006】[0006]

【発明が解決しようとする課題】しかしながら、従来の
浄化装置は、沈殿処理、生物処理、化学的処理を行うこ
とが必要であるため、これらの処理を行うための大がか
りな装置と大きな設置面積を必要としていた。また、生
物処理を行うには、その運転管理が比較的難しく、且
つ、処理に時間を要するという不都合があった。また、
生物処理部を含む装置では、クラゲ除去を目的として運
転する場合、夏場だけの運転となる。このため、秋、冬
場に設備が遊休となり、シーズン到来時には生物処理の
立ち上げに長期間(およそ1ヶ月)を要することになっ
て、機動性に欠けるという不都合もあった。さらに、こ
れらの処理を行うには、施設がおおがかりになるために
時間を要し、そのため被処理水が腐敗して作業環境が悪
化するという問題もあった。
However, since the conventional purification apparatus needs to perform a precipitation treatment, a biological treatment, and a chemical treatment, a large-scale apparatus for performing these treatments and a large installation area are required. Needed. In addition, there are inconveniences that the operation management is relatively difficult to perform the biological treatment, and that the treatment requires time. Also,
When the apparatus including the biological treatment section is operated for the purpose of removing jellyfish, the operation is performed only in summer. For this reason, the facilities are idle in autumn and winter, and when the season comes, it takes a long time (approximately one month) to start the biological treatment, and there is also an inconvenience of lack of mobility. Further, in order to perform these treatments, it takes time for the facilities to be overwhelmed, so that there is a problem that the water to be treated is spoiled and the working environment is deteriorated.

【0007】この発明の目的は、全体の構成を簡易且つ
小規模とすることができ、運転管理も容易で処理時間も
高速な海水浄化装置を提供することにある。
An object of the present invention is to provide a seawater purification apparatus which can be simplified and reduced in size as a whole, can be easily operated, and has a high processing time.

【0008】[0008]

【課題を解決するための手段】この発明は、上記の課題
を解決するために以下の構成を備えている。
The present invention has the following arrangement to solve the above-mentioned problems.

【0009】(1)取得した海水を被浄化液として一時
貯留する貯留槽と、該貯留槽に気泡を導入し浮遊物質を
該気泡に付着させることにより貯留槽内で浮上させる気
泡発生部と、浮上した浮遊物質を取り除く分離部と、か
らなる加圧浮上分離装置と、前記加圧浮上分離装置で浮
遊物質が取り除かれた被浄化液を膜浸透圧でろ過して清
澄海水と非清澄海水とを分離する膜処理装置と、前記清
澄海水を酸化する酸化処理装置と、を備えている、この
発明では、浮遊物質を気泡に付着させて浮上させ、これ
を分離部で取り除く。この操作は、気泡を強制発生させ
て、これに浮遊物質を付着させて浮遊させる物理的な作
用であるため、沈殿処理、生物処理、化学的処理とは異
なる。また、次の段階では、浮遊物質が取り除かれた被
浄化液を膜浸透圧でろ過して清澄海水と非清澄海水とを
分離させる物理的な処理を行うため、この段階でも、沈
殿処理、生物処理、化学的処理を含まない。さらに、次
の段階では、清澄海水の酸化を行って、化学的酸素要求
量(COD)を減少させる。この酸化処理は、有機物を
酸化するだけであるため、沈殿槽などの大きな装置は不
要である。
(1) A storage tank for temporarily storing the obtained seawater as a liquid to be purified, an air bubble generator for introducing air bubbles into the storage tank, and causing a floating substance to adhere to the air bubbles to float in the storage tank, A separation unit that removes the floating substances that have floated, a pressurized flotation apparatus, and a liquid to be purified from which the suspended substances have been removed by the pressure flotation apparatus are filtered by membrane osmotic pressure to obtain clear seawater and non-clear seawater. And a oxidizing apparatus for oxidizing the clarified seawater. In the present invention, the suspended substance is caused to adhere to the air bubbles to float, and is removed by the separation unit. This operation is different from sedimentation treatment, biological treatment, and chemical treatment because it is a physical action of forcibly generating air bubbles and causing a floating substance to adhere to and suspend the air bubbles. In the next step, the liquid to be purified from which suspended solids have been removed is subjected to physical treatment to separate the clarified seawater from the non-clarified seawater by filtration with a membrane osmotic pressure. Does not include treatment or chemical treatment. In the next step, the oxidation of clear seawater is performed to reduce the chemical oxygen demand (COD). Since this oxidation treatment only oxidizes organic substances, a large apparatus such as a precipitation tank is not required.

【0010】このように、この発明では、沈殿槽等のお
おがかりな設備を必要とせず、また、処理に長時間を要
したり運転管理も複雑・煩雑化することがない。
As described above, according to the present invention, no large-scale equipment such as a sedimentation tank is required, and a long time is not required for the treatment and the operation management is not complicated and complicated.

【0011】(2)前記酸化処理装置は、清澄海水に紫
外線を照射することで該清澄海水を酸化する。
(2) The oxidation treatment device oxidizes the clarified seawater by irradiating the clarified seawater with ultraviolet rays.

【0012】被浄化液内の有機物の酸化を紫外線により
行うようにすることで、装置の小型化と処理の高速化、
容易化を実現できる。
By oxidizing organic substances in the liquid to be purified by ultraviolet rays, the apparatus can be reduced in size and the processing speed can be increased.
Easy implementation can be realized.

【0013】(3)前記酸化処理装置は、清澄海水にオ
ゾンを注入することで該清澄海水を酸化する。
(3) The oxidation treatment device oxidizes the clear seawater by injecting ozone into the clear seawater.

【0014】被浄化液にオゾンを注入することでも、有
機物の酸化を促進することができる。構造もオゾン注入
装置を設けるだけであるため簡単であり、小型化と処理
の高速化も実現可能である。
By injecting ozone into the liquid to be purified, the oxidation of organic substances can be promoted. The structure is also simple because only an ozone injection device is provided, and miniaturization and high-speed processing can be realized.

【0015】(4)前記膜処理装置の前段に設けられ、
海水を貯留するタンク内に凝集剤等の薬剤を投入するこ
とで海水内の浮遊物質を凝集させる凝集郡を設けた。
(4) The film processing apparatus is provided before the film processing apparatus,
A flocculation group was set up to flocculate suspended substances in seawater by introducing a chemical such as a flocculant into a tank for storing seawater.

【0016】この発明では、海水を一旦凝集部に集め、
その後に加圧浮上分離装置に導入する。凝集部は、浮遊
物質を凝集させてフロックを形成するもので、後工程で
の処理の効率化を図る。すなわち、フロックを加圧浮上
装置に導くことにより、気泡へのフロックの付着が促さ
れることになり、結果として浮上する浮遊物質の量を増
大することができる。
In the present invention, the seawater is once collected in the coagulation part,
Then, it is introduced into a pressure flotation device. The aggregating section forms flocs by aggregating suspended substances, and aims to increase the efficiency of processing in a subsequent step. In other words, by guiding the flocs to the pressurized flotation device, the adhesion of the flocs to the air bubbles is promoted, and as a result, the amount of floating substances that float can be increased.

【0017】(5)前記加圧浮上分離装置と膜処理装置
間に海水の一時貯蔵郡を設ける。
(5) A temporary storage group of seawater is provided between the pressure flotation device and the membrane treatment device.

【0018】加圧浮上分離装置と膜処理装置とは、それ
ぞれ物理的な作用により浮遊物質を分離・除去するもの
で、その処理速度は、沈殿処理、生物処理、化学的処理
により浮遊物質を取り除く従来の装置に比較してかなり
高速である。このため、これらの2つの装置間に処理速
度の差があると、処理の効率が低下してしまう。そこ
で、この発明では、これらの加圧浮上分離装置と膜処理
装置間に海水の一時貯蔵部を設け、この一時貯留部をバ
ッファとして使う。これにより、これらの2つの装置間
に処理速度の差があっても、これによる全体の処理速度
の低下を緩和することができる。
The pressure flotation device and the membrane treatment device separate and remove suspended substances by physical action, respectively. The processing speed is settled, biological treatment, and chemical treatment to remove suspended substances. It is much faster than conventional devices. For this reason, if there is a difference in processing speed between these two devices, processing efficiency will be reduced. Therefore, in the present invention, a temporary storage section of seawater is provided between the pressurized flotation apparatus and the membrane processing apparatus, and the temporary storage section is used as a buffer. As a result, even if there is a difference in processing speed between these two devices, it is possible to mitigate a decrease in the overall processing speed due to the difference.

【0019】[0019]

【発明の実施の形態】図3は、この発明の実施形態であ
る海水浄化装置の横成図である。
FIG. 3 is a horizontal sectional view of a seawater purification apparatus according to an embodiment of the present invention.

【0020】原水槽20には図外のポンプから海水が導
入され、被浄化液はこの原水槽20から原水ポンプ21
より取水される。取水された被浄化液は、加圧浮上分離
装置22に導かれる。加圧浮上分離装置22は、凝集撹
はん槽23と、浮上槽24と、気泡水製造装置25と、
スカムレーキ26とを備えている。
Seawater is introduced into the raw water tank 20 from a pump (not shown), and the liquid to be purified is supplied from the raw water tank 20 to the raw water pump 21.
More water is taken. The liquid to be purified, which has been taken, is guided to the pressure flotation device 22. The pressure flotation / separation device 22 includes a coagulation stirrer tank 23, a flotation tank 24, a bubble water production device 25,
And a scum rake 26.

【0021】擬集撹はん槽23は、急速撹はん槽23a
と、緩速撹はん槽23bとで構成され、急速撹はん槽2
3aには塩鉄を含む擬集剤27と苛性ソーダ29がポン
プ28とポンプ32により供給され、緩速撹はん槽23
bには高分子凝集剤31がポンプ32により供給され
る。擬集剤27は、後段の浮上槽24でスカムを効果的
に浮上させるために有機物を適切に凝集させる。苛性ソ
ーダ29は、PH調整を行う中和割として供給される。
また、高分子凝集剤31は、凝集助剤として機能し、ス
カム生成の効率を高める。また、急速撹はん槽23aに
は撹はん羽根33が、緩速撹はん槽23bには撹はん羽
根34がそれぞれ配置されている。
The simulated stirring tank 23 includes a rapid stirring tank 23a.
And a slow stirring tank 23b.
3a, a pseudo-collector 27 containing salt iron and caustic soda 29 are supplied by a pump 28 and a pump 32, and a slow stirring tank 23 is provided.
A polymer flocculant 31 is supplied to b by a pump 32. The simulating agent 27 appropriately aggregates organic substances in order to effectively float the scum in the floating tank 24 at the subsequent stage. The caustic soda 29 is supplied as a neutralization rate for adjusting pH.
Further, the polymer flocculant 31 functions as a flocculant, and enhances the efficiency of scum generation. Further, a stirring blade 33 is arranged in the rapid stirring tank 23a, and a stirring blade 34 is arranged in the slow stirring tank 23b.

【0022】前記気泡水製造装置25は、超微細気泡を
生成し、この気泡を擬集撹はん槽23からの被浄化液と
ともに浮上槽24に導入する。これらは、浮上槽24の
底面から導入することが好ましく、これにより、気泡が
浮上するまでの期間に被浄化液内の凝集物(有機物)が
気泡表面に十分に付着してスカムとして液成分と分離さ
れる。
The bubble water producing apparatus 25 generates ultrafine bubbles, and introduces the bubbles into the floating tank 24 together with the liquid to be purified from the collection and stirring tank 23. These are preferably introduced from the bottom of the floating tank 24, whereby the aggregates (organic substances) in the liquid to be purified sufficiently adhere to the surface of the bubbles during the period until the bubbles float, and the liquid components as scum are mixed with the liquid components. Separated.

【0023】前記浮上槽24の上部には、板状のスカム
レーキ26が液面に沿って回転可能に配置されている。
モータ33は、このスカムレーキ26を回転し、スカム
レーキ26が浮上槽24の液面上を回転することによ
り、その液面に浮上しているスカムをすくい取り、スカ
ム取り出し口35に排出する。このスカム取り出し口3
5に排出されたスカムはスカム排出パイプ36によりス
カム槽34に排出される。これにより、被浄化液に含ま
れる固形の有機物のかなりの量が分離・排出される。
A plate-shaped scum lake 26 is disposed above the floating tank 24 so as to be rotatable along the liquid surface.
The motor 33 rotates the scum lake 26, and the scum lake 26 rotates on the liquid surface of the floating tank 24, thereby scooping the scum floating on the liquid surface and discharging the scum to the scum take-out port 35. This scum outlet 3
The scum discharged to 5 is discharged to a scum tank 34 by a scum discharge pipe 36. As a result, a considerable amount of solid organic matter contained in the liquid to be purified is separated and discharged.

【0024】図4は、浮上槽24内での凝集物の気泡付
着状態を示している。液体成分39には、多くの超微細
気泡38が混合していて、この気泡38表面に、凝集物
37が付着している。同図に示すように、気泡38は、
凝集物35の体積に比してかなり小さいため、凝集物3
5には複数の気泡36が接触する。このため、凝集物の
浮力を十分に大きくすることができ、液面上にこれらを
集めて凝集物の大きな塊のスカムとして抽出することが
できる。
FIG. 4 shows a state in which air bubbles adhere to the aggregates in the floating tank 24. Many ultra-fine bubbles 38 are mixed in the liquid component 39, and aggregates 37 adhere to the surface of the bubbles 38. As shown in FIG.
Since the volume of the aggregate 35 is considerably smaller than that of the aggregate 35, the aggregate 3
A plurality of bubbles 36 contact 5. Therefore, the buoyancy of the aggregate can be sufficiently increased, and these can be collected on the liquid surface and extracted as a scum of a large lump of the aggregate.

【0025】なお、浮上槽24でスカムが取り除かれた
被浄化液は、一旦、被浄化液貯留部40に排出され、こ
れの一部がポンプ41により気泡水製造装置25に導か
れる。このため、浮上槽24に供給される気泡水はスカ
ムの取り除かれたきれいな液内に超微細気泡の形成され
たものとなる。
The liquid to be purified from which the scum has been removed in the floating tank 24 is once discharged into a liquid-to-be-purified storage section 40, and a part thereof is guided to the bubble water producing apparatus 25 by the pump 41. For this reason, the bubble water supplied to the floating tank 24 has ultrafine bubbles formed in a clean liquid from which scum has been removed.

【0026】被浄化液貯留部40内の被浄化液は、処理
水貯蔵タンク50に導かれる。この貯蔵タンク50は、
加圧浮上分離装置22の処理速度と後段の膜処理装置5
2の処理速度の相違を吸収する働きをするバッファとし
て機能する。加圧浮上分離装置22と膜処理装置52
は、双方とも沈殿設備などを用いない物理的な処理を行
うものであるため処理速度が大きい。そこで、この貯蔵
タンク50を設けることにより、それらの処理速度の相
違を吸収することが可能になる。
The to-be-purified liquid in the to-be-purified liquid storage section 40 is guided to a treated water storage tank 50. This storage tank 50
Processing speed of pressure flotation device 22 and subsequent membrane processing device 5
2 functions as a buffer that functions to absorb the difference in processing speed. Pressure flotation device 22 and membrane processing device 52
Are both physical processes that do not use sedimentation equipment and the like, and therefore have a high processing speed. Therefore, by providing the storage tank 50, it is possible to absorb the difference in the processing speed.

【0027】処理水貯蔵タンク50に一旦貯蔵された被
浄化液は、ポンプ51により膜処理装置52に導かれ
る。この装置は、前記加圧浮上分離装置で浮遊物質が取
り除かれた海水を膜浸透圧でろ過して清澄海水と非清澄
海水とを分離する。膜処理装置52は、原水槽53と、
その原水槽に貯留した被浄化液を取り出すポンプ54
と、ポンプ54で取り出された被浄化液を導入して浸透
圧により清澄海水と非清澄海水とを分離するモジュール
55と、膜面に付着している有機物をエアーにより下方
に押し出すためのコンプレッサー56と、を備えてい
る。逆洗排水槽57には、膜面の有機物を含む汚染液が
排水される。また、ろ過排水、ドレイン排水も逆洗排水
槽57に対して行われる。
The liquid to be purified once stored in the treated water storage tank 50 is guided to a membrane treatment device 52 by a pump 51. This apparatus separates clear seawater and non-clear seawater by filtering seawater from which suspended substances have been removed by the pressurized flotation device with a membrane osmotic pressure. The membrane processing device 52 includes a raw water tank 53,
Pump 54 for taking out the liquid to be purified stored in the raw water tank
And a module 55 for introducing the liquid to be purified taken out by the pump 54 to separate clarified seawater and non-clarified seawater by osmotic pressure, and a compressor 56 for pushing out organic substances adhering to the membrane surface by air. And The contaminated liquid containing organic substances on the membrane surface is drained into the backwash drain tank 57. Further, filtration drainage and drain drainage are also performed for the backwash drainage tank 57.

【0028】UV酸化装置58は、以上のようにして有
機物を除去した被浄化液を紫外線照射により酸化して、
有機物に由来する化学的酸素要求量(COD)の酸化分
解を行う。このUV酸化装置58は、被浄化液に対して
紫外線を照射するだけであるために、大掛かりなものと
はならない。
The UV oxidizing device 58 oxidizes the liquid to be purified from which organic substances have been removed as described above by irradiating it with ultraviolet light.
Performs oxidative decomposition of chemical oxygen demand (COD) derived from organic matter. The UV oxidizing device 58 only irradiates the liquid to be purified with ultraviolet light, and therefore does not become large-scale.

【0029】以上の構成により、原水槽20に取水され
た海水は、以下の工程により有機物の浮遊物質(SS)
が除去され、また、化学的酸素要求量(COD)が低下
される。
With the above structure, the seawater taken into the raw water tank 20 can be used as a suspension of organic matter (SS) by the following steps.
Is removed and the chemical oxygen demand (COD) is reduced.

【0030】海水は、まず、凝集撹はん槽23によりフ
ロック形成される。このフロックは浮上槽24で気泡に
付着することで浮上してスカムとなり、スカムレーキ2
6により取り除かれる。ここまでの段階で、被浄化液
(海水)に含まれるかなりの量の浮遊物質(SS)が除
去される。
First, seawater is floc-formed by the coagulation and stirring tank 23. The flock floats and becomes scum by adhering to the air bubbles in the floating tank 24, and the scum lake 2
6 removed. At this stage, a considerable amount of suspended solids (SS) contained in the liquid to be purified (seawater) is removed.

【0031】次に、このようにして浮遊物質(SS)が
除去された被浄化液は、膜処理装置52において、浸透
圧により清澄海水と非清澄海水とに分離される。非清澄
海水は逆洗排水槽57にろ過排水として排水され、清澄
海水だけが取り出される。この処理により、非常に微細
な浮遊物質(SS)も除去される。
Next, the liquid to be purified from which the suspended substances (SS) have been removed in this manner is separated into clarified seawater and non-clarified seawater in the membrane treatment device 52 by osmotic pressure. The non-clear seawater is drained as filtered water into the backwashing drainage tank 57, and only the clearing seawater is taken out. This process also removes very fine suspended solids (SS).

【0032】次の段階では、浮遊物質(SS)のほとん
どが除去された被浄化液が紫外線照射により酸化され、
化学的酸素要求量(COD)が低下される。
In the next stage, the liquid to be purified from which most of the suspended solids (SS) have been removed is oxidized by irradiation with ultraviolet light,
Chemical oxygen demand (COD) is reduced.

【0033】図5は、上記の装置により、各工程で浮遊
物質(SS)と化学的酸素要求量(COD)の低下状態
を示す。第3工程の膜処理装置52の工程を終了した段
階でも430mg/Lから70mg/L以下に低下す
る。第4工程のUV酸化処理を行うと、化学的酸素要求
量(COD)が<50mg/Lまで低下する。
FIG. 5 shows the reduced state of the suspended solids (SS) and the chemical oxygen demand (COD) in each step by the above-mentioned apparatus. Even at the stage when the process of the film processing apparatus 52 of the third process is completed, the concentration is reduced from 430 mg / L to 70 mg / L or less. Performing the fourth step of UV oxidation reduces the chemical oxygen demand (COD) to <50 mg / L.

【0034】なお、UV酸化装置58に替えて、他の酸
化手段を使用することも可能である。例えば、清澄海水
にオゾンを注入することで該清澄海水を酸化することも
可能である。このような装置も清澄海水を酸化するだけ
であるために、おおがかりなものとはならない。
It is to be noted that other oxidizing means can be used in place of the UV oxidizing device 58. For example, it is possible to oxidize the clear seawater by injecting ozone into the clear seawater. Such a device also does not become overwhelming because it only oxidizes clear water.

【0035】[0035]

【発明の効果】この発明によれば、装置が小型で処理速
度が高速の加圧浮上分離装置と膜処理装置を用いるため
に、沈殿槽等のおおがかりな設備を必要とせず、また、
処理に長時間を要することがない。また、微生物を使用
したりすることもないため、運転管理が容易である。
According to the present invention, the use of a pressure flotation apparatus and a membrane processing apparatus having a small apparatus and a high processing speed does not require a large-scale facility such as a sedimentation tank.
No long processing time is required. Also, since no microorganisms are used, operation management is easy.

【0036】また、被浄化液内の有機物の酸化を紫外線
やオゾンにより行うようにすることで、装置の小型化と
処理の高速化を容易に実現できる。
Further, by oxidizing the organic substances in the liquid to be purified with ultraviolet rays or ozone, it is possible to easily realize the miniaturization of the apparatus and the high-speed processing.

【0037】また、海水を一旦凝集部に集め、その後に
加圧浮上分離装置に導入することにることができる。
In addition, seawater can be once collected in a flocculation section and then introduced into a pressure flotation device.

【0038】また、これらの加圧浮上分離装置と膜処理
装置間に海水の一時貯蔵部を設けることより、これらの
2つの装置間に処理速度の差があっても、これによる全
体の処理速度の低下を防ぐことができる。
Further, by providing a temporary storage of seawater between the pressure flotation device and the membrane processing device, even if there is a difference in the processing speed between these two devices, the overall processing speed can be increased. Can be prevented from decreasing.

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

【図1】は、海水浄化装置が適用される発電所システム
の概略図
FIG. 1 is a schematic diagram of a power plant system to which a seawater purification device is applied.

【図2】は、従来の海水浄化システムの構成図FIG. 2 is a configuration diagram of a conventional seawater purification system.

【図3】は、この発明の実施形態である海水浄化装置の
構成図
FIG. 3 is a configuration diagram of a seawater purification device according to an embodiment of the present invention.

【図4】は、加圧浮上分離装置の動作を説明するための
FIG. 4 is a diagram for explaining the operation of the pressure flotation device.

【図5】は、名工程でのSSとCODの低下状態を示す
FIG. 5 is a diagram showing a reduction state of SS and COD in a name process.

【符号の説明】[Explanation of symbols]

22:加圧浮上分離装置 23:凝集撹はん槽 24:浮上槽 25:気泡水製造装置 52:膜処理装置 58:UV酸化装置 22: Pressurized flotation device 23: Coagulation stirrer tank 24: Flotation tank 25: Bubble water production device 52: Membrane treatment device 58: UV oxidation device

フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) C02F 9/00 502 C02F 9/00 502R 502Z 503 503A 1/24 1/24 C 1/32 1/32 1/44 1/44 H 1/52 1/52 K 1/56 1/56 K 1/72 101 1/72 101 1/78 1/78 (72)発明者 鳥居 明 大阪市北区中之島3丁目3番22号 関西電 力株式会社内 (72)発明者 坂下 哲朗 大阪市北区中之島3丁目3番22号 関西電 力株式会社内 (72)発明者 渡部 正之 大阪市淀川区西宮原1丁目7番31号 和泉 電気株式会社内 (72)発明者 町谷 勝幸 大阪市淀川区西宮原1丁目7番31号 和泉 電気株式会社内 (72)発明者 初田 導弘 大阪市淀川区西宮原1丁目7番31号 和泉 電気株式会社内 Fターム(参考) 4D006 GA03 JA67A KA02 KA71 KB04 KB13 KB30 KC03 KC14 KD21 PA01 PB03 4D015 BA19 BA24 BB08 BB12 CA18 CA20 DA13 DB01 DC02 EA07 EA15 EA33 FA02 FA17 FA24 4D037 AA06 AB01 AB02 BA03 BA18 BB07 CA03 CA08 CA12 CA14 4D050 AA06 AB07 BB01 BB02 BC09 BD06 CA04 CA09 CA13 CA16 4D062 BA19 BA24 BB08 BB12 CA18 CA20 DA13 DB01 DC02 EA07 EA15 EA33 FA02 FA17 FA24Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat II (reference) C02F 9/00 502 C02F 9/00 502R 502Z 503 503A 1/24 1/24 C 1/32 1/32 1/44 1 / 44 H 1/52 1/52 K 1/56 1/56 K 1/72 101 1/72 101 1/78 1/78 (72) Inventor Akira Torii 3-3-22 Nakanoshima, Kita-ku, Osaka Kansai Inside Electric Power Company (72) Inventor Tetsuro Sakashita 3-3-22 Nakanoshima, Kita-ku, Osaka City Inside Kansai Electric Power Company (72) Inventor Masayuki Watanabe 1-7-131 Nishimiyahara, Yodogawa-ku, Osaka Izumi Electric Co., Ltd. Inside the company (72) Inventor Katsuyuki Machiya 1-7-31 Nishinomiyahara, Yodogawa-ku, Osaka-shi Inside Izumi Electric Co., Ltd. Term (reference) 4D006 GA03 JA67A KA02 KA71 KB04 KB13 KB30 KC03 KC14 KD21 PA01 PB03 4D015 BA19 BA24 BB08 BB12 CA18 CA20 DA13 DB01 DC02 EA07 EA15 EA33 FA02 FA17 FA24 4D037 AA06 AB01 AB02 BA03 BA18 BB07 CA03 CA08 CA12 CA14 4D050 AA06 AB07 BB01 BB02 BC09 BD06 CA04 CA09 CA13 CA16 4D062 BA19 BA24 BB08 BB12 CA18 CA20 DA13 DB01 DC02 EA07 EA15 EA33 FA02 FA17 FA24

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 取得した海水を被浄化液として一時貯留
する貯留槽と、該貯留槽に気泡を導入し浮遊物質を該気
泡に付着させることにより貯留槽内で浮上させる気泡発
生部と、浮上した浮遊物質を取り除く分離部と、からな
る加圧浮上分離装置と、 前記加圧浮上分離装置で浮遊物質が取り除かれた被浄化
液を膜浸透圧でろ過して清澄海水と非清澄海水とを分離
する膜処理装置と、 前記清澄海水を酸化する酸化処理装置と、を備えてな
る、浮遊物質含有海水の浄化装置。
1. A storage tank for temporarily storing the obtained seawater as a liquid to be purified, a bubble generator for introducing air bubbles into the storage tank and causing a floating substance to adhere to the air bubbles to float in the storage tank, A separation unit that removes suspended substances that have been removed, a pressurized flotation device, and a liquid to be purified from which suspended substances have been removed by the pressurized flotation device are filtered by membrane osmotic pressure to obtain clear seawater and non-clear seawater. An apparatus for purifying seawater containing suspended solids, comprising: a membrane treatment apparatus for separating; and an oxidation treatment apparatus for oxidizing the clear seawater.
【請求項2】 前記酸化処理装置は、清澄海水に紫外線
を照射することで該清澄海水を酸化する、請求項1記載
の浮遊物質含有海水の浄化装置。
2. The apparatus for purifying seawater containing suspended substances according to claim 1, wherein the oxidation treatment apparatus oxidizes the clearwater by irradiating ultraviolet light to the clearwater.
【請求項3】 前記酸化処理装置は、清澄海水にオゾン
を注入することで該清澄海水を酸化する、請求項1記載
の浮遊物質含有海水の浄化装置。
3. The apparatus for purifying seawater containing suspended substances according to claim 1, wherein the oxidation treatment apparatus oxidizes the clarified seawater by injecting ozone into the clarified seawater.
【請求項4】 前記膜処理装置の前段に設けられ、海水
を貯留するタンク内に凝集剤を投入することで海水内の
浮遊物質を凝集させる凝集部を設けた、請求項1〜3の
いずれかに記載の浮遊物質含有海水の浄化装置。
4. An aggregating unit which is provided at a preceding stage of the membrane processing apparatus and which agglomerates a floating substance in seawater by charging an aggregating agent into a tank for storing seawater. An apparatus for purifying seawater containing suspended substances according to the present invention.
【請求項5】 前記加圧浮上分離装置と膜処理装置間に
海水の一時貯蔵部を設けた請求項1〜4のいずれかに記
載の浮遊物質含有海水の浄化装置。
5. The apparatus for purifying seawater containing suspended substances according to claim 1, wherein a temporary storage section of seawater is provided between the pressure flotation device and the membrane treatment device.
JP2000172618A 2000-06-08 2000-06-08 Water purification equipment for suspended solids Expired - Fee Related JP3931279B2 (en)

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JP2000172618A JP3931279B2 (en) 2000-06-08 2000-06-08 Water purification equipment for suspended solids

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Application Number Priority Date Filing Date Title
JP2000172618A JP3931279B2 (en) 2000-06-08 2000-06-08 Water purification equipment for suspended solids

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JP2001347295A true JP2001347295A (en) 2001-12-18
JP3931279B2 JP3931279B2 (en) 2007-06-13

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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003170157A (en) * 2001-12-06 2003-06-17 Kansai Electric Power Co Inc:The Cleaning equipment for suspended solid-containing seawater
JP2003251365A (en) * 2002-02-27 2003-09-09 Japan Organo Co Ltd Microcystis-containing water treatment apparatus and its treatment method
JP2005329397A (en) * 2004-04-23 2005-12-02 Mitsubishi Rayon Co Ltd Method and apparatus for separation
KR100579117B1 (en) 2004-03-11 2006-05-12 주식회사 환경정보컨설팅 Apparatus for purificating of closed water area by dissolved air flotation
WO2014181583A1 (en) * 2013-05-10 2014-11-13 水ing株式会社 Apparatus for seawater desalination and method therefor
JP2018030071A (en) * 2016-08-23 2018-03-01 王子ホールディングス株式会社 Method and system for producing bactericidal water

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003170157A (en) * 2001-12-06 2003-06-17 Kansai Electric Power Co Inc:The Cleaning equipment for suspended solid-containing seawater
JP4549000B2 (en) * 2001-12-06 2010-09-22 Idec株式会社 Water purification equipment for suspended solids
JP2003251365A (en) * 2002-02-27 2003-09-09 Japan Organo Co Ltd Microcystis-containing water treatment apparatus and its treatment method
KR100579117B1 (en) 2004-03-11 2006-05-12 주식회사 환경정보컨설팅 Apparatus for purificating of closed water area by dissolved air flotation
JP2005329397A (en) * 2004-04-23 2005-12-02 Mitsubishi Rayon Co Ltd Method and apparatus for separation
WO2014181583A1 (en) * 2013-05-10 2014-11-13 水ing株式会社 Apparatus for seawater desalination and method therefor
JPWO2014181583A1 (en) * 2013-05-10 2017-02-23 水ing株式会社 Seawater desalination apparatus and method
JP2018030071A (en) * 2016-08-23 2018-03-01 王子ホールディングス株式会社 Method and system for producing bactericidal water

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