JPS6210715B2 - - Google Patents
Info
- Publication number
- JPS6210715B2 JPS6210715B2 JP7452181A JP7452181A JPS6210715B2 JP S6210715 B2 JPS6210715 B2 JP S6210715B2 JP 7452181 A JP7452181 A JP 7452181A JP 7452181 A JP7452181 A JP 7452181A JP S6210715 B2 JPS6210715 B2 JP S6210715B2
- Authority
- JP
- Japan
- Prior art keywords
- ozone
- water
- biofouling
- seawater
- adsorption
- 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.)
- Expired
Links
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F16—ENGINEERING ELEMENTS AND UNITS; GENERAL MEASURES FOR PRODUCING AND MAINTAINING EFFECTIVE FUNCTIONING OF MACHINES OR INSTALLATIONS; THERMAL INSULATION IN GENERAL
- F16L—PIPES; JOINTS OR FITTINGS FOR PIPES; SUPPORTS FOR PIPES, CABLES OR PROTECTIVE TUBING; MEANS FOR THERMAL INSULATION IN GENERAL
- F16L58/00—Protection of pipes or pipe fittings against corrosion or incrustation
Landscapes
- Engineering & Computer Science (AREA)
- General Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- Protection Of Pipes Against Damage, Friction, And Corrosion (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Description
この発明は海水等が流通している水管中の生物
付着を抑制するための装置に関するものである。
発電所や化学工場等では多量の海水等が冷却水
として使用されているが、用水中の微生物や藻類
に起因して、水管や熱交換器にスライム等が付着
し、管路の閉塞や熱交換効率の低下をきたす。こ
の種の生物障害防止対策のために、比較的高濃度
のオゾンを間欠的に水管に注入する装置が先行技
術としてある。高濃度のオゾンを間欠的に注入す
るための装置として、小型で小容量のオゾン発生
機を用い、これにより生成させたオゾンを吸着剤
に吸着蓄積し、オゾン注入時にオゾンを吸着剤か
ら脱着使用するものが、設備費および運転費の点
で有利である。
このような間欠オゾン注入のための装置の一例
として、次にその構成および動作を第1図により
説明する。第1図は従来の生物付着抑制装置を示
す系統図であり、図において、1はオゾン発生
機、2はこのオゾン発生機1へ酸素を供給する酸
素供給源、3は上記オゾン発生機1と吸脱着塔4
の循環系に設けられた循環ブロア、5は吸脱着塔
4を冷却するための冷却源、6は吸脱着塔4を加
熱するための加熱源、7は吸脱着塔4からのオゾ
ンを注入する水流エゼクタ、8a〜8gはそれぞ
れ切換弁、9は水流エゼクタ7に連絡するエゼク
タ駆動用水管、10はこのエゼクタ駆動用水管9
に連絡する冷却用水管、11はエゼクタ駆動用水
管9に設けられたエゼクタ駆動用ポンプである。
吸脱着塔4は二重筒になつており、そのうち内
筒4aにはオゾン吸着剤が充填され、外筒4bに
は熱媒体が充填されている。また吸着剤は一般に
シリカゲルが用いられ、熱媒体はエチレングリコ
ールやアルコール類が使用される。なお、上記循
環ブロア3、オゾン発生機1、吸脱着塔4はこの
順に一つの循環系を構成し、これに酸素供給源2
が連絡している。
次に動作について説明する。この動作にはオゾ
ンの吸着動作および脱着動作の二動作がある。
初めに吸着動作について説明する。酸素供給源
2より循環系内に、常時一定圧力となるように酸
素を供給する。この時の圧力は通常1.5Kg/cm2に
維持されており、切換弁8c,8dは開いてい
る。循環ブロア3により循環系内に酸素を流通さ
せると、オゾン発生機1の放電空隙中を通過する
間に無声放電により酸素の一部がオゾンに変換さ
れてオゾン化酸素となる。このオゾン化酸素は吸
脱着塔4へ搬送される。オゾン吸脱着塔4内の吸
着剤は、オゾンを選択的に吸着し、残りの酸素は
切換弁8cを介して循環ブロア3に返送される。
オゾンとして消費された酸素は酸素供給源2より
補充される。この時、オゾン吸着剤の温度は冷却
源5により−30℃以下に冷却されている。これは
吸着剤のオゾン吸着量が温度により大きく変化す
ることによる。すなわち温度を低下させると、オ
ゾンの吸着量は増加し、逆に温度が上昇するとオ
ゾンの吸着量は減少するからである。したがつて
オゾン脱着する時は吸着剤の温度を上昇させる。
オゾン吸脱着塔4の吸着剤がオゾン飽和吸着量
近くまで吸着すると脱着動作へ移行する。脱着動
作ではオゾン発生機1、循環ブロア3、冷却源5
が稼動を停止し、切換弁8a,8b,8c,8d
が閉じる。その後、加熱源6、水流エゼクタ7が
稼動を始めて切換弁8e,8f,8gが開く。こ
の時吸着剤に吸着されていたオゾンが脱着し易い
ように加熱源6より熱が加えられ、吸着剤の温度
を上昇させる。そして水流エゼクタ7でオゾン吸
脱着塔4内のオゾンを減圧吸引し、水流エゼクタ
7内で水中に分散して溶解し、これにより生成す
るオゾン水は使用箇所すなわち冷却用水管10に
送られ、生物付着抑制に供される。この時、減圧
吸引することによる吸脱着塔4内の到達圧力は略
−70cmHgとなる。このように脱着期間が終了す
ると、再び初期の吸着動作へと移行して連続的に
運転が繰り返される。
従来の生物付着抑制装置は上記のように構成さ
れているので、上記装置により、冷却用水管10
等の水管中にオゾンが間欠的に注入できるが、臨
海工業地帯近辺の海水が冷却用海水として使用さ
れている場合は、多くの場合、その海水が汚染さ
れているために、また、汚染の度合が日によつ
て、または時間ごとに大きく変動するために、清
浄海水を使用する場合に比較し、必要オゾン量が
増大するとともに、一定量の必要な残留オゾンを
残すことが困難となり、清浄海水を使用する場合
と同じオゾン注入量では、生物付着抑制ができな
くなる。
表1に臨海工業地帯近辺の海水と清浄海水の水
質の例を示す。
This invention relates to a device for suppressing biofouling in water pipes through which seawater or the like flows. A large amount of seawater is used as cooling water in power plants, chemical factories, etc., but due to microorganisms and algae in the water, slime and other substances adhere to water pipes and heat exchangers, causing blockage of pipes and heat exchangers. This causes a decrease in exchange efficiency. As a measure to prevent this type of biological damage, there is a device in the prior art that intermittently injects relatively high concentration ozone into water pipes. A small, small-capacity ozone generator is used as a device for intermittently injecting high-concentration ozone.The ozone generated by this is adsorbed and accumulated on an adsorbent, and the ozone is desorbed from the adsorbent during ozone injection. It is advantageous in terms of equipment costs and operating costs. As an example of such a device for intermittent ozone injection, its structure and operation will be explained below with reference to FIG. FIG. 1 is a system diagram showing a conventional biofouling control device. In the figure, 1 is an ozone generator, 2 is an oxygen supply source that supplies oxygen to the ozone generator 1, and 3 is the ozone generator 1. Adsorption/desorption tower 4
5 is a cooling source for cooling the adsorption/desorption tower 4, 6 is a heating source for heating the adsorption/desorption tower 4, and 7 is for injecting ozone from the adsorption/desorption tower 4. A water ejector, 8a to 8g are respective switching valves, 9 is a water pipe for driving the ejector connected to the water ejector 7, and 10 is a water pipe 9 for driving the ejector.
A cooling water pipe 11 connected to the ejector driving water pipe 11 is an ejector driving pump provided in the ejector driving water pipe 9. The adsorption/desorption tower 4 has a double cylinder structure, of which the inner cylinder 4a is filled with an ozone adsorbent, and the outer cylinder 4b is filled with a heat medium. Furthermore, silica gel is generally used as the adsorbent, and ethylene glycol or alcohol is used as the heat medium. The circulation blower 3, ozone generator 1, and adsorption/desorption tower 4 constitute one circulation system in this order, and the oxygen supply source 2 is connected to this circulation system.
is in contact. Next, the operation will be explained. This operation includes two operations: an ozone adsorption operation and an ozone desorption operation. First, the suction operation will be explained. Oxygen is supplied from the oxygen supply source 2 into the circulation system so that a constant pressure is maintained at all times. The pressure at this time is normally maintained at 1.5 kg/cm 2 and the switching valves 8c and 8d are open. When oxygen is passed through the circulation system by the circulation blower 3, part of the oxygen is converted into ozone by silent discharge while passing through the discharge gap of the ozone generator 1, and becomes ozonized oxygen. This ozonized oxygen is transported to the adsorption/desorption tower 4. The adsorbent in the ozone adsorption/desorption tower 4 selectively adsorbs ozone, and the remaining oxygen is returned to the circulation blower 3 via the switching valve 8c.
Oxygen consumed as ozone is replenished from the oxygen supply source 2. At this time, the temperature of the ozone adsorbent is cooled to −30° C. or lower by the cooling source 5. This is because the amount of ozone adsorbed by the adsorbent varies greatly depending on the temperature. That is, when the temperature is lowered, the amount of ozone adsorbed increases, and conversely, when the temperature is raised, the amount of ozone adsorbed is decreased. Therefore, when desorbing ozone, the temperature of the adsorbent is increased. When the adsorbent in the ozone adsorption/desorption tower 4 adsorbs ozone to a level close to the saturated adsorption amount, a transition is made to the desorption operation. During desorption operation, ozone generator 1, circulation blower 3, and cooling source 5 are used.
stops operating, and the switching valves 8a, 8b, 8c, 8d
closes. Thereafter, the heat source 6 and water ejector 7 start operating, and the switching valves 8e, 8f, and 8g open. At this time, heat is applied from the heating source 6 to increase the temperature of the adsorbent so that the ozone adsorbed on the adsorbent is easily desorbed. Then, the ozone in the ozone adsorption/desorption tower 4 is sucked under reduced pressure by the water jet ejector 7, and is dispersed and dissolved in water in the water jet ejector 7. The ozone water thus generated is sent to the point of use, that is, the cooling water pipe 10, and is Used to suppress adhesion. At this time, the ultimate pressure within the adsorption/desorption tower 4 due to vacuum suction is approximately -70 cmHg. When the desorption period ends in this manner, the initial adsorption operation is resumed and the operation is continuously repeated. Since the conventional biofouling control device is configured as described above, the cooling water pipe 10 is
Ozone can be intermittently injected into water pipes such as water pipes, etc. However, when seawater near coastal industrial areas is used as seawater for cooling, it is often the case that the seawater is contaminated. Because the degree of ozone varies greatly from day to day or hour to hour, the amount of ozone required increases compared to when using clean seawater, and it becomes difficult to leave a certain amount of residual ozone. If the same amount of ozone is injected as when using seawater, it will not be possible to suppress biofouling. Table 1 shows examples of the water quality of seawater and clean seawater near the coastal industrial area.
【表】
第2図は汚染海水および清浄淡水中におけるオ
ゾン濃度の経時変化を示す線図である。生物付着
を抑制するためには、生物が付着する接触面に、
所定濃度のオゾンが所定時間接触する必要がある
と考えられているが、第2図から明らかなよう
に、汚染海水ではオゾンを所定濃度に長時間維持
することは困難である。汚染海水が流通している
水管内で、オゾンを所定濃度以上に保つために
は、清浄海水が流通している水管内に注入するオ
ゾン量に比較して多量のオゾンを注入するか、水
管へのオゾン注入点をいくつか設けるか、汚染濃
度に応じてオゾン注入量を制御するオゾン注入量
制御装置を設ける等の必要があり、実用上大きな
障害になるという欠点があつた。
この発明は、上記のような従来のものの欠点を
除去するためになされたもので、間欠オゾン注入
装置から水管にオゾンを注入する際、オゾンを注
入して溶解させる水を海水等の汚染水から清浄淡
水にすることにより、水中でのオゾンの寿命を延
ばすようにした生物付着抑制装置を提供すること
を目的としている。
以下、本発明の一実施例を第3図により説明す
る。第3図は本発明の一実施例による生物付着抑
制装置を示す系統図であり、第1図と同一部分に
は同じ符号を付し、説明を省略する。図において
12は電磁弁、13はこの電磁弁12を介して淡
水供給源14から冷却用水管10に清浄淡水を供
給するポンプ、15は冷却用水管10に設けられ
た別の電磁弁である。
次にこの装置の動作について説明する。吸脱着
塔4内の吸着剤が、オゾンを飽和吸着量近くまで
吸着すると、脱着動作に切換わり、切換弁8a,
8b,8c,8dが閉じ、切換弁8e,8fが開
いて加熱源6が稼動しはじめる。その後、エゼク
タ駆動用ポンプ11およびこれと連動して電磁弁
12が開となつて、電磁弁15が閉となり、かつ
ポンプ13が作動して淡水注入が開始され、その
後切換弁8gが開いて、冷却用水管10へのオゾ
ン注入が開始される。オゾン脱着動作は1日1
回、1回5〜10分間程度であり、このオゾン脱着
期間が終了すると、再び電磁弁12が閉、電磁弁
15が開となつて、淡水注入が停止され、エゼク
タ駆動ポンプ11が停止されて、再び冷却用水管
10中に海水が流通しオゾン吸着動作へ移行する
過程が繰返えされる。
第2図に示すように、汚染海水中では10ppm
のオゾンを注入したとき、注入時から30秒後には
0.1ppmになるのに対し、清浄淡水中では、同じ
時間後で、7.4ppm60秒経過後でも、5.5ppmと高
い残存オゾン濃度を保持する。高い残存オゾン濃
度は必然的にそれと接触する面で高い殺菌力とな
つて現われるため、生物付着抑制効果を高めるこ
とになる。
なお淡水供給装置としては第3図の構成に限ら
ず、他の構成のものでもよく、また電磁弁12,
15およびポンプ13の形式、構造も限定されな
い。さらにオゾン発生機1、吸脱着塔4の形式、
構造等も限定されない。またオゾンを注入する水
管としては、冷却用水管に限らず、他の水管であ
つてもよく、上記実施例と同様の効果を奏する。
また、この発明は海水に限らず汚染水の流通して
いる水管に適用できる。
以上のとおり、本発明によれば、間欠オゾン注
入時に、オゾンを溶解させる水を海水等から清浄
淡水に置換することにより、海水の汚染度の高低
および時間的変動にかかわらず、常に一定量の、
比較的少量のオゾン注入で生物付着抑制ができ、
供給される淡水も、1日1回、1回5〜10分間程
度であるので、少くて済み、全体としてより経済
的な生物付着抑制装置を得ることができる。[Table] Figure 2 is a diagram showing changes over time in ozone concentration in contaminated seawater and clean freshwater. In order to suppress biofouling, it is necessary to apply
It is thought that ozone at a predetermined concentration needs to be in contact for a predetermined time, but as is clear from FIG. 2, it is difficult to maintain ozone at a predetermined concentration for a long time in contaminated seawater. In order to maintain ozone at a predetermined concentration or higher in water pipes through which contaminated seawater is flowing, it is necessary to inject a large amount of ozone into the water pipes compared to the amount of ozone injected into water pipes through which clean seawater is flowing. However, it is necessary to install several ozone injection points or to install an ozone injection amount control device that controls the amount of ozone injection depending on the concentration of contaminants, which poses a major practical problem. This invention was made to eliminate the drawbacks of the conventional ones as described above, and when injecting ozone into water pipes from an intermittent ozone injection device, the water to be injected and dissolved is separated from contaminated water such as seawater. The purpose of the present invention is to provide a biofouling control device that extends the life of ozone in water by providing clean fresh water. An embodiment of the present invention will be described below with reference to FIG. FIG. 3 is a system diagram showing a biofouling suppression device according to an embodiment of the present invention, and the same parts as in FIG. In the figure, 12 is a solenoid valve, 13 is a pump that supplies clean fresh water from a fresh water supply source 14 to the cooling water pipe 10 via the solenoid valve 12, and 15 is another solenoid valve provided in the cooling water pipe 10. Next, the operation of this device will be explained. When the adsorbent in the adsorption/desorption tower 4 adsorbs ozone close to the saturated adsorption amount, it switches to desorption operation, and the switching valves 8a,
8b, 8c, and 8d are closed, switching valves 8e, 8f are opened, and the heat source 6 starts operating. After that, the ejector drive pump 11 and the electromagnetic valve 12 are opened in conjunction with the ejector drive pump 11, the electromagnetic valve 15 is closed, and the pump 13 is activated to start fresh water injection, and then the switching valve 8g is opened, Ozone injection into the cooling water pipe 10 is started. Ozone desorption operation is once a day.
Once this ozone desorption period is over, the solenoid valve 12 is closed again, the solenoid valve 15 is opened, the fresh water injection is stopped, and the ejector drive pump 11 is stopped. The process of flowing seawater into the cooling water pipe 10 again and shifting to the ozone adsorption operation is repeated. As shown in Figure 2, 10ppm in contaminated seawater.
When injecting ozone, 30 seconds after injection,
In contrast, in clean fresh water, the residual ozone concentration remains as high as 5.5ppm even after 60 seconds of 7.4ppm after the same amount of time. A high residual ozone concentration inevitably results in a high bactericidal effect on surfaces that come into contact with it, thereby increasing the biofouling inhibiting effect. The fresh water supply device is not limited to the configuration shown in FIG. 3, but may have other configurations, and the solenoid valve 12
The types and structures of 15 and pump 13 are not limited either. Furthermore, the type of ozone generator 1 and adsorption/desorption tower 4,
The structure etc. are not limited either. Further, the water pipe for injecting ozone is not limited to the cooling water pipe, but may be any other water pipe, and the same effects as in the above embodiment can be achieved.
Further, the present invention is applicable not only to seawater but also to water pipes through which contaminated water flows. As described above, according to the present invention, by replacing the water that dissolves ozone with clean fresh water from seawater etc. during intermittent ozone injection, a constant amount of water is always maintained regardless of the level of contamination of seawater and temporal fluctuations. ,
Biofouling can be suppressed by injecting a relatively small amount of ozone.
Since the amount of fresh water supplied is only once a day for about 5 to 10 minutes, less amount is required, and a more economical biofouling control device can be obtained as a whole.
第1図は従来の生物付着抑制装置を示す系統
図、第2図は汚染海水および清浄淡水中における
オゾン濃度の経時変化を示す線図、第3図はこの
発明の実施例による生物付着抑制装置を示す系統
図である。
図において、1はオゾン発生機、2は酸素供給
源、3は循環ブロア、4は吸脱着塔、5は冷却
源、6は加熱源、7は水流エゼクタ、8a〜8g
は切換弁、9はエゼクタ駆動用水管、10は冷却
用水管、11はエゼクタ駆動用ポンプ、12,1
5は電磁弁、13はポンプ、14は淡水供給源で
ある。なお図中同一符号は同一または相当部分を
示す。
Fig. 1 is a system diagram showing a conventional biofouling control device, Fig. 2 is a diagram showing changes in ozone concentration over time in contaminated seawater and clean fresh water, and Fig. 3 is a biofouling control device according to an embodiment of the present invention. FIG. In the figure, 1 is an ozone generator, 2 is an oxygen supply source, 3 is a circulation blower, 4 is an adsorption/desorption tower, 5 is a cooling source, 6 is a heating source, 7 is a water ejector, 8a to 8g
1 is a switching valve, 9 is a water pipe for driving the ejector, 10 is a water pipe for cooling, 11 is a pump for driving the ejector, 12,1
5 is a solenoid valve, 13 is a pump, and 14 is a fresh water supply source. Note that the same reference numerals in the figures indicate the same or corresponding parts.
Claims (1)
に注入し、水管内の生物付着を防止する生物付着
抑制装置において、オゾン注入時に、オゾンを注
入する水管中に清浄淡水を供給する淡水供給装置
を備えたことを特徴とする生物付着抑制装置。 2 淡水供給装置は電磁弁を介して淡水供給源か
ら淡水を水管に注入するポンプと、上記水管に設
けられた別の電磁弁を備えていることを特徴とす
る特許請求の範囲第1項記載の生物付着抑制装
置。[Scope of Claims] 1. In a biofouling control device that prevents biofouling in water pipes by intermittently injecting ozone into water pipes through which contaminated water is flowing, when ozone is injected, clean water is added to the water pipes into which ozone is injected. A biofouling suppression device characterized by comprising a freshwater supply device that supplies freshwater. 2. Claim 1, characterized in that the fresh water supply device includes a pump that injects fresh water from a fresh water supply source into a water pipe via a solenoid valve, and another solenoid valve provided in the water pipe. biofouling control device.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP7452181A JPS57190189A (en) | 1981-05-18 | 1981-05-18 | Inhibitor for adhesion of organism |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP7452181A JPS57190189A (en) | 1981-05-18 | 1981-05-18 | Inhibitor for adhesion of organism |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS57190189A JPS57190189A (en) | 1982-11-22 |
| JPS6210715B2 true JPS6210715B2 (en) | 1987-03-07 |
Family
ID=13549701
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP7452181A Granted JPS57190189A (en) | 1981-05-18 | 1981-05-18 | Inhibitor for adhesion of organism |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS57190189A (en) |
-
1981
- 1981-05-18 JP JP7452181A patent/JPS57190189A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS57190189A (en) | 1982-11-22 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| JPS6048444B2 (en) | Intermittent ozone supply device | |
| US5591349A (en) | Microorganism removing method | |
| JP2005506891A (en) | Refrigerated purifier | |
| JP5860196B1 (en) | Water treatment system and water treatment method | |
| JPS592559B2 (en) | Microorganism removal device | |
| JP6129289B2 (en) | Water treatment system and water treatment method | |
| US6086772A (en) | Method and apparatus for preventing biofouling in cooling water system | |
| JP4087927B2 (en) | Ozone supply device | |
| JPS6210715B2 (en) | ||
| JP2014064976A (en) | Water treatment apparatus | |
| CN1329322C (en) | Membrane treatment system for separating virus | |
| JPS6356163B2 (en) | ||
| JPS6210714B2 (en) | ||
| JPS6026081Y2 (en) | Biofouling control device | |
| JPH02284B2 (en) | ||
| JPH09187783A (en) | Operating method of biological contact filtration equipment for water purification | |
| JPS59193192A (en) | Device for supplying ozone intermittently | |
| CN209917630U (en) | A biological trickling filter organic waste gas treatment device | |
| JP4101316B2 (en) | Intermittent ozone supply device | |
| JP3215720B2 (en) | Water purification equipment | |
| JPS6034483B2 (en) | Intermittent ozone supply method | |
| JPS6320194B2 (en) | ||
| JP3532334B2 (en) | Intermittent ozone supply method | |
| JP4373992B2 (en) | Ozone supply device | |
| JPH05305290A (en) | Biofouling prevention device |