JP2008055352A - Method and apparatus for maintaining fine bubble of ozone gas in water, and ballast water treatment method - Google Patents

Method and apparatus for maintaining fine bubble of ozone gas in water, and ballast water treatment method Download PDF

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JP2008055352A
JP2008055352A JP2006236836A JP2006236836A JP2008055352A JP 2008055352 A JP2008055352 A JP 2008055352A JP 2006236836 A JP2006236836 A JP 2006236836A JP 2006236836 A JP2006236836 A JP 2006236836A JP 2008055352 A JP2008055352 A JP 2008055352A
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water
seawater
bubbles
ozone gas
refined
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Masabumi Matsumoto
正文 松本
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Mitsui Engineering and Shipbuilding Co Ltd
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Mitsui Engineering and Shipbuilding Co Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a method and apparatus for maintaining fine bubbles of ozone gas in water which can maintain the fine bubbles of ozone gas generated in water for a long time, and to provide a ballast water treatment method. <P>SOLUTION: The method for maintaining fine bubbles of ozone gas in water comprises a seawater introduction process for introducing seawater into an ozone dissolving tank, and an electrolytic water generating process for electrolyzing the seawater to generate strong acid electrolytic water on the anode side. The seawater introduction process comprises a fine bubble dissolving process for atomizing bubbles of ozone gas to generate fine bubbles and dissolving the fine bubbles in the seawater. The strong acid electrolytic water is added to a process before or after the fine bubble dissolving process. <P>COPYRIGHT: (C)2008,JPO&INPIT

Description

本発明は、水中のオゾンガスの微細化気泡の維持方法、維持装置及びバラスト水の処理方法に関し、詳しくは、例えば海水に溶解するオゾンガスの微細化気泡を長期間に渡って維持できる方法、装置及びバラスト水の処理方法に関する。   The present invention relates to a maintenance method, maintenance device, and ballast water treatment method for ozone gas in water, and more specifically, a method, an apparatus, and a device capable of maintaining ozone gas refinement bubbles dissolved in seawater, for example, over a long period of time. The present invention relates to a method for treating ballast water.

原油等を輸送する貨物用船舶には、航行時の船体の安定性を保つためにバラストタンク
が設けられている。通常、原油等が積載されていないときには、バラストタンク内をバラ
スト水で満たし、原油等を積み込む際にバラスト水を排出することにより、船体の浮力を
調整し、船体を安定化させている。
A cargo ship that transports crude oil or the like is provided with a ballast tank in order to maintain the stability of the hull during navigation. Usually, when crude oil or the like is not loaded, the inside of the ballast tank is filled with ballast water, and when the crude oil or the like is loaded, the ballast water is discharged to adjust the buoyancy of the hull and stabilize the hull.

このようにバラスト水は、船舶の安全な航行のために必要な水であり、通常、荷役を行
う港湾の海水が利用される。その量は、世界的にみると年間100億トンを超えるといわ
れている。
As described above, the ballast water is water necessary for the safe navigation of the ship, and the seawater of the port that performs cargo handling is usually used. The amount is said to exceed 10 billion tons per year worldwide.

ところで、バラスト水中には、それを取水した港湾に生息する水生生物が混入しており
、船舶の移動に伴い、これら水生生物が同時に異国に運ばれることになる。
By the way, aquatic organisms inhabiting the port where the water is taken are mixed in the ballast water, and these aquatic organisms are transported to foreign countries at the same time as the ship moves.

従って、もともとその海域には生息していなかった生物種が、既存生物種に取って代わ
るといった生態系の破壊が深刻化している。
Therefore, the destruction of ecosystems, such as the replacement of existing species with species that did not originally live in the sea, has become serious.

このような背景の中、国際海事機関(IMO)の外交会議において、船舶のバラスト水
及び沈殿物の規制及び管理のための条約(以下、条約という)が採択され、バラスト水処
理装置を用いたバラスト水管理の実施義務が2009年以降の建造船から適用される予定
となっている。
Against this background, a convention for the regulation and management of ship ballast water and sediment (hereinafter referred to as the Convention) was adopted at the diplomatic meeting of the International Maritime Organization (IMO), and the ballast water treatment device was used. The obligation to carry out ballast water management is expected to be applied from 2009 onwards.

また、条約によりバラスト水の排出基準は、以下の表1に示すように定められている。   In addition, the discharge standards for ballast water are defined by the Convention as shown in Table 1 below.

このため、バラスト水の排出時には外洋に存在する生物数の100分の1程度まで除去
あるいは殺滅することが必要となっている。
For this reason, when discharging ballast water, it is necessary to remove or kill up to about 1/100 of the number of organisms present in the open ocean.

以上のような背景から、上記のような問題を解決できるバラスト水の処理技術の開発が
急務となっている。
In view of the above background, there is an urgent need to develop ballast water treatment technology that can solve the above-described problems.

従来、特許文献1には、海水に蒸気の注入と同時または相前後してオゾンを注入するようにする技術が開示されている。
特開2004−160437号公報
Conventionally, Patent Document 1 discloses a technique for injecting ozone into seawater at the same time as or after injection of steam.
JP 2004-160437 A

特許文献1によると、蒸気注入管から、バラスト水中に蒸気を注入すると、注入された蒸気は、バラスト水中で拡大して、バラスト水中に気泡群が生成され、この気泡は、バラスト水で急冷されて崩壊し、気泡群の崩壊に伴なう衝撃波によってオゾンが微細化、活性化されると記載されている。   According to Patent Document 1, when steam is injected into the ballast water from the steam injection pipe, the injected steam expands in the ballast water, and bubbles are generated in the ballast water. The bubbles are rapidly cooled with the ballast water. It is described that ozone is refined and activated by the shock wave accompanying the collapse of the bubbles.

しかし、この微細化されたオゾンの気泡は、時間の経過と共に合体して、気泡サイズが大きくなってしまいオゾンの活性が失われる欠点がある。   However, the refined ozone bubbles are combined with the passage of time, and the bubble size increases, resulting in a disadvantage that the ozone activity is lost.

そこで、本発明の課題は、水中に生成したオゾンの微細化気泡を長期間維持できる水中のオゾンガスの微細化気泡の維持方法、維持装置及びバラスト水の処理方法を提供することにある。   Then, the subject of this invention is providing the maintenance method of the refinement | miniaturization bubble of the ozone gas in water which can maintain the refinement | miniaturization bubble of the ozone produced | generated in water for a long period of time, and the processing method of a ballast water.

本発明の他の課題は、以下の記載により明らかとなる。   Other problems of the present invention will become apparent from the following description.

上記課題は、以下の各発明によって解決される。   The above problems are solved by the following inventions.

(請求項1)
海水をオゾン溶解タンクに導入する海水導入工程と、海水を電気分解して陽極側に強酸性電解水を生成する電解水生成工程とを有し、
前記海水導入工程に、オゾンガスの気泡を微細化して微細化気泡を生成して前記海水中に溶解する微細化気泡溶解工程を有し、
前記微細化気泡溶解工程の前工程又は後工程で前記強酸性電解水を添加することを特徴とする水中のオゾンガスの微細化気泡の維持方法。
(Claim 1)
A seawater introduction step of introducing seawater into the ozone dissolution tank, and an electrolyzed water generation step of electrolyzing the seawater to produce strongly acidic electrolyzed water on the anode side,
In the seawater introduction step, there is a refined bubble dissolution step of refining ozone gas bubbles to generate refined bubbles and dissolving them in the seawater,
A method for maintaining the refined bubbles of ozone gas in water, wherein the strongly acidic electrolyzed water is added in a pre-process or a post-process of the refined-bubble dissolving process.

(請求項2)
オゾンガスの微細化気泡の径が、5〜500μmの範囲であることを特徴とする請求項1記載の水中のオゾンガスの微細化気泡の維持方法。
(Claim 2)
The diameter of the ozone gas refined bubbles is in the range of 5 to 500 µm, and the method for maintaining the refined bubbles of ozone gas in water according to claim 1.

(請求項3)
海水をオゾン溶解水タンクに導入する経路に、オゾンガスの気泡を微細化して微細化気泡を生成して前記海水中に溶解する微細化気泡溶解手段を有し、
海水を導入して電気分解により陽極側に強酸性電解水を生成する電解水生成手段を有し、
前記電解水生成手段で生成された強酸性電解水を供給する配管を、前記微細化気泡溶解手段の前方又は後方に接続したことを特徴とする水中のオゾンガスの微細化気泡の維持装置。
(Claim 3)
In the path for introducing seawater into the ozone-dissolved water tank, there is a refined bubble dissolving means for refining ozone gas bubbles to generate refined bubbles and dissolving them in the seawater,
Having electrolyzed water generating means for introducing strong seawater electrolyzed water on the anode side by introducing seawater and electrolysis,
An apparatus for maintaining finely divided bubbles of ozone gas in water, wherein a pipe for supplying strongly acidic electrolyzed water generated by the electrolyzed water generating means is connected to the front or rear of the refined bubble dissolving means.

(請求項4)
前記微細化気泡溶解手段が、ベンチュリー管又は多孔板からなることを特徴とする請求項3記載のオゾンガスの微細化気泡の維持装置。
(Claim 4)
4. The apparatus for maintaining fine gas bubbles of ozone gas according to claim 3, wherein the fine gas bubble dissolving means comprises a venturi tube or a perforated plate.

(請求項5)
海水をバラストタンクに導入する経路にろ過膜又はスリット板を設けて、海水中の水生生物を処理するバラスト水処理方法において、前記ろ過膜又はスリット板により水生生物を処理後に、前記請求項1又は2記載の水中のオゾンガスの微細化気泡の維持方法により生成されたオゾン溶解水を添加することを特徴とするバラスト水の処理方法。
(Claim 5)
In the ballast water treatment method for treating aquatic organisms in seawater by providing a filtration membrane or a slit plate in a path for introducing seawater into a ballast tank, the aquatic organism is treated with the filtration membrane or the slit plate, and then the claim 1 or 2. A method for treating ballast water, which comprises adding ozone-dissolved water produced by the method for maintaining the refined bubbles of ozone gas in water.

本発明によれば、水中に生成したオゾンの微細化気泡を長期間維持できる水中のオゾンガスの微細化気泡の維持方法、維持装置及びバラスト水の処理方法を提供することができる。   ADVANTAGE OF THE INVENTION According to this invention, the maintenance method of the refinement | miniaturization bubble of the ozone gas in water which can maintain the refinement | miniaturization bubble of the ozone produced | generated in water for a long term, a maintenance apparatus, and the processing method of ballast water can be provided.

以下、本発明に係るオゾンガスの微細化気泡の維持方法を実施する維持装置の一例を図面に基づいて説明する。   Hereinafter, an example of the maintenance apparatus which implements the maintenance method of the refined | miniaturized bubble of ozone gas which concerns on this invention is demonstrated based on drawing.

図1において、1はバラストタンクであり、バラスト水が導入され、貯留される。バラスト水には、例えば海水、淡水などが用いられる。本発明では主に海水を使用した例について説明する。   In FIG. 1, reference numeral 1 denotes a ballast tank, in which ballast water is introduced and stored. As the ballast water, for example, seawater or fresh water is used. In the present invention, an example in which seawater is mainly used will be described.

バラスト水は、動物プランクトン、植物プランクトン、細菌などの水生生物を含み、かかる水生生物を含む海水は、図示しないポンプで汲み上げられて、たとえば膜処理装置2で所定径までの微生物等を除去し、その後オゾン処理されてバラストタンク1に送られる。本バラスト水は、膜処理装置2からバラストタンク1に至るバラストタンク送液配管10に、微細気泡化されたオゾンを含むオゾン溶解水が所定量添加供給されて、前記膜処理装置2で除去できなかった水生生物が殺虫あるいは殺菌され、バラストタンク1内に水生生物を含まないバラスト水を貯留できるようにする。   Ballast water includes aquatic organisms such as zooplankton, phytoplankton, and bacteria, and seawater containing such aquatic organisms is pumped up by a pump (not shown), for example, removes microorganisms and the like up to a predetermined diameter by the membrane treatment apparatus 2, Thereafter, it is treated with ozone and sent to the ballast tank 1. This ballast water can be removed by the membrane treatment apparatus 2 by supplying a predetermined amount of ozone-dissolved water containing ozone that has been microbubbled to the ballast tank liquid delivery pipe 10 extending from the membrane treatment apparatus 2 to the ballast tank 1. The aquatic organisms that have not existed are killed or sterilized so that ballast water that does not contain aquatic organisms can be stored in the ballast tank 1.

3はオゾン溶解タンクであり、該タンク3の入口には微細化気泡溶解手段4が設けられている。微細化気泡溶解手段4は、図示の例ではベンチュリー管40を用いている。   Reference numeral 3 denotes an ozone dissolution tank. At the inlet of the tank 3, a fine bubble dissolution means 4 is provided. The refined bubble dissolving means 4 uses a Venturi tube 40 in the illustrated example.

41は図示しない海水ポンプにより海水を導入する導入管であり、ベンチュリー管40の入口部42に接続されている。   Reference numeral 41 denotes an introduction pipe for introducing seawater by a seawater pump (not shown), and is connected to an inlet 42 of the venturi pipe 40.

5はオゾン発生装置であり、該発生装置5で発生したオゾンは、配管50を介してベンチュリー管40の前方に供給される。   Reference numeral 5 denotes an ozone generator, and the ozone generated by the generator 5 is supplied to the front of the venturi tube 40 through the pipe 50.

かかるベンチュリー管40の存在により、海水中に導入されたオゾン気泡は、微細気泡化する(この気泡をマイクロバブルとも称する)。微細化気泡の径は5〜500μmの範囲が好ましく、より好ましくは50〜300μmの範囲である。   Due to the presence of the venturi tube 40, the ozone bubbles introduced into the seawater become fine bubbles (this bubbles are also referred to as microbubbles). The diameter of the fine bubbles is preferably in the range of 5 to 500 μm, more preferably in the range of 50 to 300 μm.

微細化気泡は、海水に分散・混入された状態で存在しており、かかる状態を本発明では微細化気泡の溶解と表現している。   The refined bubbles are present in a state of being dispersed and mixed in seawater, and this state is expressed as dissolution of the refined bubbles in the present invention.

6は電解水生成手段である。電解水生成手段6は陽極60と陰極61を備えており、陽極室62と陰極室63が隔膜64によって仕切られている。   6 is electrolyzed water production | generation means. The electrolyzed water generating means 6 includes an anode 60 and a cathode 61, and the anode chamber 62 and the cathode chamber 63 are partitioned by a diaphragm 64.

電解水生成手段6に海水が導入されると、電気分解により、希薄食塩水の電解の場合と同様に、陽極60に酸素、陰極61に水素が発生し、陽極60付近に希薄塩酸水溶液が、陰極61付近には希薄水酸化ナトリウム水溶液が生じる。   When seawater is introduced into the electrolyzed water generating means 6, electrolysis generates oxygen at the anode 60 and hydrogen at the cathode 61, as in the case of dilute saline electrolysis, and a dilute hydrochloric acid aqueous solution is formed near the anode 60. A dilute aqueous sodium hydroxide solution is generated in the vicinity of the cathode 61.

以下に電解反応を示す。   The electrolytic reaction is shown below.

(+)陽極反応
2Cl → 2Cl + 2e
(+) Anodic reaction 2Cl → 2Cl + 2e

陽極で生じる原子状塩素Clは、水と反応してHCl微量の酸素が発生する。
2Cl + HO → 2HCl + 1/2O
The atomic chlorine Cl generated at the anode reacts with water to generate a trace amount of HCl.
2Cl + H 2 O → 2HCl + 1 / 2O 2

(−)陰極反応
2Na + 2HO → 2NaOH + H
(−) Cathode reaction 2Na + + 2H 2 O → 2NaOH + H 2

以上の電解反応から、陽極60側では、塩酸が生成し、強酸性電解水が得られる。この強酸性電解水は配管65を介して、前記微細化気泡溶解手段4の前方又は後方の何れかに供給される。従って、配管65は前記微細化気泡溶解手段4の前方又は後方の何れかに接続される。   From the above electrolytic reaction, hydrochloric acid is generated on the anode 60 side, and strongly acidic electrolyzed water is obtained. This strongly acidic electrolyzed water is supplied to either the front or the rear of the refined bubble dissolving means 4 through the pipe 65. Accordingly, the pipe 65 is connected to either the front or the rear of the fine bubble dissolving means 4.

本発明では、強酸性電解水の供給により、微細化気泡が溶解して海水は、酸性となり、微細化気泡の再結合を防止できる効果がある。   In the present invention, by supplying strong acidic electrolyzed water, the refined bubbles are dissolved, and the seawater becomes acidic, which has an effect of preventing recombination of the refined bubbles.

また本発明において、海水を電気分解する電解水生成手段6を設けると、強酸性液を別途手配する必要がない。特にバラスト水を積載する船舶においては、低コスト化が望まれているので、かかる要望も満足する。   In the present invention, if electrolyzed water generating means 6 for electrolyzing seawater is provided, it is not necessary to separately prepare a strongly acidic liquid. In particular, a ship loaded with ballast water satisfies the demand because cost reduction is desired.

次に、本発明において、微細化気泡の再結合を防止できる作用を説明する。   Next, in the present invention, an operation capable of preventing recombination of fine bubbles will be described.

海水の中の気液界面に存在するHとOHは電気的にバランスしているが、海水が酸性となりpHが低下すると、気液界面のゼータ電位が下がり(マイナスの絶対値が小さくなり)、OHを極性化しやすくなることにより、気泡同士は反発しあい、オゾンガス微細気泡の合体(再結合)が抑制されると推測されている。 H + and OH present at the gas-liquid interface in seawater are electrically balanced, but when seawater becomes acidic and pH decreases, the zeta potential at the gas-liquid interface decreases (the absolute value of minus decreases). ), It becomes presumed that by making OH easier to polarize, bubbles repel each other and coalescence (recombination) of ozone gas fine bubbles is suppressed.

従って、微細化気泡(マイクロバブル)を長期間維持することが可能となり、配管30を介してオゾン溶解水をバラストタンクやその前のバラスト水導入管に添加すると、短時間に効率的に殺菌効果を発揮する。   Therefore, it becomes possible to maintain the fine bubbles (micro bubbles) for a long period of time, and when the ozone-dissolved water is added to the ballast tank or the preceding ballast water introduction pipe via the pipe 30, the bactericidal effect can be efficiently performed in a short time. Demonstrate.

以上の説明では、オゾン処理の前処理として膜処理の例を説明したが、図2に示すようなスリット板を用いることもできる。   In the above description, the example of the film treatment has been described as the pretreatment of the ozone treatment, but a slit plate as shown in FIG. 2 can also be used.

スリット板20は図3に示すような直線状のスリット200が複数形成されており、スリット200の開口幅は、好ましくは200μm〜500μmの範囲である。   The slit plate 20 is formed with a plurality of linear slits 200 as shown in FIG. 3, and the opening width of the slits 200 is preferably in the range of 200 μm to 500 μm.

バラスト水がスリット板20に向かって配管21内を圧送され、その圧送されたバラスト水は乱流状態のままスリット板20のスリット200を通過しようとする。スリット200を通過しようとする際に剪断現象が生じることで液中の水生生物を破壊して殺減する。   Ballast water is pumped through the pipe 21 toward the slit plate 20, and the pumped ballast water attempts to pass through the slit 200 of the slit plate 20 in a turbulent state. A shearing phenomenon occurs when trying to pass through the slit 200, thereby destroying and killing aquatic organisms in the liquid.

なお、スリットは直線状に限定されず、円弧状(曲線状の一例)でもよい。またスリット板の枚数は1枚でもよいが、2以上の複数枚でもよい。   In addition, a slit is not limited to linear form, A circular arc shape (an example of curvilinear shape) may be sufficient. The number of slit plates may be one, but may be two or more.

上記態様では、微細化気泡溶解手段4として、ベンチュリー管40を用いたが、これに限定されず、多孔板又はオリフィス板を用いることもでき、またマイクロバブルを生成可能であれば、種々の装置を使用でき、例えばエジェクター、スタティックミキサーなどの混合機を使用できる。   In the above embodiment, the venturi tube 40 is used as the microbubble-dissolving means 4, but the invention is not limited to this, and a porous plate or an orifice plate can be used, and various devices can be used as long as microbubbles can be generated. For example, a mixer such as an ejector or a static mixer can be used.

オゾンの全バラスト水に対する注入率は、膜処理やスリット板によって分離又は殺減できない細菌類などを殺菌する上で、最大で5ppm(gオゾン/mバラスト水)が好ましく、より好ましくは0.5〜5ppmの範囲である。 The injection rate of ozone with respect to the total ballast water is preferably 5 ppm (g ozone / m 3 ballast water) at the maximum in order to sterilize bacteria that cannot be separated or killed by membrane treatment or slit plates, and more preferably is 0. It is in the range of 5 to 5 ppm.

なお、本発明では、海水の電解によって陰極61側に生成した水酸化ナトリウムは、例えば、バラストタンク1の手前のバラストタンク送液配管10に注入することで、pHを中性化してオゾンガス微細気泡の再結合を促進してバラストタンク1内へのオゾンガス混入を防止する。   In the present invention, sodium hydroxide generated on the cathode 61 side by electrolysis of seawater is neutralized to pH by injecting into the ballast tank liquid feeding pipe 10 in front of the ballast tank 1, for example. Is promoted to prevent ozone gas from being mixed into the ballast tank 1.

本発明の実施態様を示すフロー図Flow chart showing an embodiment of the present invention 本発明に使用できるスリット板を示す概略断面図Schematic sectional view showing a slit plate that can be used in the present invention 図2のIII−III線概略断面図Fig. 2 is a schematic sectional view taken along line III-III in Fig. 2.

符号の説明Explanation of symbols

1:バラストタンク
10:バラストタンク送液配管
2:膜処理装置
20:スリット板
200:スリット
21:配管
3:オゾン溶解タンク
30:配管
4:微細化気泡溶解手段
40:ベンチュリー管
41:導入管
42:入口部
5:オゾン発生装置
50:配管
6:電解水生成手段
60:陽極
61:陰極
62:陽極室
63:陰極室
64:隔膜
65:配管
DESCRIPTION OF SYMBOLS 1: Ballast tank 10: Ballast tank liquid feeding piping 2: Membrane processing apparatus 20: Slit board 200: Slit 21: Piping 3: Ozone dissolution tank 30: Piping 4: Fine bubble dissolving means 40: Venturi pipe 41: Introducing pipe 42 : Inlet part 5: Ozone generator 50: Piping 6: Electrolyzed water generating means 60: Anode 61: Cathode 62: Anode chamber 63: Cathode chamber 64: Diaphragm 65: Piping

Claims (5)

海水をオゾン溶解タンクに導入する海水導入工程と、海水を電気分解して陽極側に強酸性電解水を生成する電解水生成工程とを有し、
前記海水導入工程に、オゾンガスの気泡を微細化して微細化気泡を生成して前記海水中に溶解する微細化気泡溶解工程を有し、
前記微細化気泡溶解工程の前工程又は後工程で前記強酸性電解水を添加することを特徴とする水中のオゾンガスの微細化気泡の維持方法。
A seawater introduction step of introducing seawater into the ozone dissolution tank, and an electrolyzed water generation step of electrolyzing the seawater to produce strongly acidic electrolyzed water on the anode side,
In the seawater introduction step, there is a refined bubble dissolution step of refining ozone gas bubbles to generate refined bubbles and dissolving them in the seawater,
A method for maintaining the refined bubbles of ozone gas in water, wherein the strongly acidic electrolyzed water is added in a pre-process or a post-process of the refined-bubble dissolving process.
オゾンガスの微細化気泡の径が、5〜500μmの範囲であることを特徴とする請求項1記載の水中のオゾンガスの微細化気泡の維持方法。   The diameter of the ozone gas refined bubbles is in the range of 5 to 500 µm, and the method for maintaining the refined bubbles of ozone gas in water according to claim 1. 海水をオゾン溶解水タンクに導入する経路に、オゾンガスの気泡を微細化して微細化気泡を生成して前記海水中に溶解する微細化気泡溶解手段を有し、
海水を導入して電気分解により陽極側に強酸性電解水を生成する電解水生成手段を有し、
前記電解水生成手段で生成された強酸性電解水を供給する配管を、前記微細化気泡溶解手段の前方又は後方に接続したことを特徴とする水中のオゾンガスの微細化気泡の維持装置。
In the path for introducing seawater into the ozone-dissolved water tank, there is a refined bubble dissolving means for refining ozone gas bubbles to generate refined bubbles and dissolving them in the seawater,
Having electrolyzed water generating means for introducing strong seawater electrolyzed water on the anode side by introducing seawater and electrolysis,
An apparatus for maintaining finely divided bubbles of ozone gas in water, wherein a pipe for supplying strongly acidic electrolyzed water generated by the electrolyzed water generating means is connected to the front or rear of the refined bubble dissolving means.
前記微細化気泡溶解手段が、ベンチュリー管又は多孔板からなることを特徴とする請求項3記載の水中のオゾンガスの微細化気泡の維持装置。   4. The apparatus for maintaining the micronized bubbles of ozone gas in water according to claim 3, wherein the micronized bubble dissolving means comprises a venturi tube or a perforated plate. 海水をバラストタンクに導入する経路にろ過膜又はスリット板を設けて、海水中の水生生物を処理するバラスト水処理方法において、前記ろ過膜又はスリット板により水生生物を処理後に、前記請求項1又は2記載の水中のオゾンガスの微細化気泡の維持方法により生成されたオゾン溶解水を添加することを特徴とするバラスト水の処理方法。
In the ballast water treatment method for treating aquatic organisms in seawater by providing a filtration membrane or a slit plate in a path for introducing seawater into a ballast tank, the aquatic organism is treated with the filtration membrane or the slit plate, and then the claim 1 or 2. A method for treating ballast water, which comprises adding ozone-dissolved water produced by the method for maintaining the refined bubbles of ozone gas in water.
JP2006236836A 2006-08-31 2006-08-31 Method and apparatus for maintaining fine bubble of ozone gas in water, and ballast water treatment method Pending JP2008055352A (en)

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KR101191147B1 (en) 2010-07-30 2012-10-15 한국기계연구원 Ballast water treatment apparatus based on electro lysis using micro bubble
KR101225491B1 (en) * 2010-07-15 2013-01-23 한국기계연구원 Ballast water treatment apparatus discharging using micro bubble
KR101330092B1 (en) 2012-10-04 2013-11-18 참좋은우리 주식회사 Apparatus for manufacturing ozone sterilized water
WO2016181947A1 (en) * 2015-05-13 2016-11-17 株式会社 片野工業 Stirring device
KR101803368B1 (en) * 2009-08-03 2017-12-28 내셔널 유니버시티 오브 싱가포르 Emissions control system and method

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US20120164024A1 (en) * 2008-05-02 2012-06-28 Han Sup Uhm Sterilization effects of acidic ozone water
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JPWO2016181947A1 (en) * 2015-05-13 2017-08-31 株式会社 片野工業 Stirrer

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