JPH06153744A - Method for diminishing parasite of fishes and bacterium and removing living thing attached to crawl net - Google Patents

Method for diminishing parasite of fishes and bacterium and removing living thing attached to crawl net

Info

Publication number
JPH06153744A
JPH06153744A JP4280721A JP28072192A JPH06153744A JP H06153744 A JPH06153744 A JP H06153744A JP 4280721 A JP4280721 A JP 4280721A JP 28072192 A JP28072192 A JP 28072192A JP H06153744 A JPH06153744 A JP H06153744A
Authority
JP
Japan
Prior art keywords
fish
bacteria
cage
parasites
organisms
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
JP4280721A
Other languages
Japanese (ja)
Inventor
Hideo Tagawa
英生 田川
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.)
RIYOUYOU SANGYO KK
Original Assignee
RIYOUYOU SANGYO KK
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by RIYOUYOU SANGYO KK filed Critical RIYOUYOU SANGYO KK
Priority to JP4280721A priority Critical patent/JPH06153744A/en
Publication of JPH06153744A publication Critical patent/JPH06153744A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/4606Treatment of water, waste water, or sewage by electrochemical methods for producing oligodynamic substances to disinfect the water
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/467Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
    • C02F1/4672Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation
    • C02F1/4674Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electrooxydation with halogen or compound of halogens, e.g. chlorine, bromine
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/46Apparatus for electrochemical processes
    • C02F2201/461Electrolysis apparatus
    • C02F2201/46105Details relating to the electrolytic devices
    • C02F2201/4612Controlling or monitoring
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/46Apparatus for electrochemical processes
    • C02F2201/461Electrolysis apparatus
    • C02F2201/46105Details relating to the electrolytic devices
    • C02F2201/4616Power supply
    • C02F2201/46165Special power supply, e.g. solar energy or batteries
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/04Disinfection

Abstract

PURPOSE:To diminish and remove parasite of fishes, bacteria and crawl net- attached living thing by which fishes are damaged. CONSTITUTION:Electrodes compased of a titanium anode 5a and a titanium cathode 5b are provided in a water tank 2 which fishes are cultured and direct current is allowed to flow from sodium hypochlorite concentration controlling and generating device 5 to generate residual chlorine in natural sea water and the residual chlorine is arbitrarily controlled. Thereby, parasite of fishes and bacteria and crawl-attached living thing in the water tank 2 are diminished and removed to protect fishes.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、養殖魚を弊死させる寄
生虫、例えばハダムシや生簀網に付着して海水の流通を
妨げ生簀内の酸素濃度を低減させる様々な付着生物等の
死滅、除去を行って養殖魚を保護することを目的とした
魚類寄生虫および細菌の死滅と生簀網付着生物の除去方
法に関する。
BACKGROUND OF THE INVENTION The present invention relates to the killing of various adherent organisms that attach to parasites that cause aggravation of cultured fish, such as beetle and cage nets, and prevent the circulation of seawater to reduce the oxygen concentration in cages. The present invention relates to a method for killing fish parasites and bacteria and removing organisms attached to fish cage nets for the purpose of removing and protecting cultured fish.

【0002】[0002]

【従来の技術】近年海面養殖において、ブリ、カンパチ
等に寄生するハダムシ等の寄生虫が日本沿岸各地で発生
して養殖漁業に大きな被害を与えている。これは、有機
錫系防汚剤の使用禁止によって生簀網付着生物が著しく
増加したため、潮の通りが悪くなって生簀内の溶存酸素
量の低下を来し、養殖魚の摂飼量の低下、及びストレス
の発生、並びにハダムシ等寄生虫の卵の着生場所とな
り、これに起因する寄生虫病および細菌性疾病にかかり
易くなったためである。これに対し、従来の網替え、淡
水浴、高塩分水浴、薬浴等を行うと、これ等にかかる費
用や労力等が大きな負担となっている。
2. Description of the Related Art In recent years, in marine aquaculture, parasites such as bedbugs parasitic on yellowtail, amberjack and the like have been generated in various places along the coast of Japan, and have seriously damaged aquaculture. This is because the ban on the use of organotin antifouling agents markedly increased the number of organisms attached to the cage net, which made the tide worse and resulted in a decrease in the amount of dissolved oxygen in the cage, a decrease in the amount of cultured fish fed, and This is because it becomes a place where stress is generated and the eggs of parasites such as beetles are settled, which makes it easier to suffer from parasitic diseases and bacterial diseases. On the other hand, if the conventional net change, fresh water bath, high salt water bath, chemical bath, etc. are performed, the cost and labor required for these are a great burden.

【0003】[0003]

【発明が解決しようとする課題】魚類寄生虫および細菌
の駆除の方法は、寄生虫が寄生してから魚類を集中させ
て薬浴させるものや、生物の卵塊が付着した生簀網を陸
上げして新替えするもの、薬剤散布して浮遊幼虫を死滅
させるもの等三つの方法が主流であるが、これ等の方法
では完全除去は不可能である。即ち、魚類を狭い場所に
集中して薬浴させるときは魚体が傷付き、酸欠を起こす
し、魚体重量の増大により何回にも分けて行う分割処理
等、その労働力増大(通常の規模で10人程度必要)及
び定期的処理(10〜20日毎)では、100パーセン
トの処理は困難であるため、寄生虫や生簀網付着生物は
残存し、寄生虫1個が再び300個もの卵を生むことに
なって、寄生虫による被害は絶滅し得ない。加えて寄生
虫の寄生により、生簀網に魚体をこすりつけて発生する
傷部よりの細菌性疾病には対策が無い現状となってい
る。生簀網の新替えでは、生簀網に付着する珪藻、ムラ
サキガイ、アカフジツボ等により生簀網の重量が増大
し、このため生簀網の引上げが困難となる。これに加
え、網目が小さくなっているから、潮通しが悪化し、溶
存酸素量の減少で魚類が弱って生長が遅れるところへ、
寄生虫からの卵塊が付着し易くなる。従って、寄生虫は
格好の産卵場所を有するため、これを死滅させることは
困難である。また、これを網替えするには、労力、費用
が増大するし、これを行わないと魚類は、低酸素状態環
境内でのストレス発生や細菌性疾病が増大することにな
る。生簀網収容の魚類に付着した寄生虫の卵塊は、網目
に付着後、水温25℃では5日間で孵化し、幼生として
浮遊し自由に移動し得るので、毎日飼料散布する際に魚
体に寄生し得る。これを防止するため餌止めすると魚体
が弱るので、薬剤を水中に散布するしか無いが、魚類へ
の毒性及び残留性、水中濃度の希釈等を考慮すると、有
用で即効を要求される薬剤は現在見当たらない。また、
細菌性疾病についても対策が見当たらない。以上、三つ
の方法は、実施しても効果を期待し得ないが、他に対策
が無いため続行するしか無く、上記のような悪循環を繰
り返す極めて問題点のある方法であった。本発明は上述
のような従来の問題を鑑みてなされたもので、人体にも
魚類にも安全で魚類寄生虫および細菌と生簀網付着生物
を死滅させるの優れた効果が得られると共に、コストの
低減化が可能となり、容易な取り扱いで長期間連続して
実行可能な魚類寄生虫および細菌の死滅と生簀網付着生
物の除去方法を提供することを目的とする。
DISCLOSURE OF THE INVENTION Problems to be Solved by the Invention The method of exterminating fish parasites and bacteria is to concentrate fishes after the parasites parasitize them and take a chemical bath, or to land a cage net to which the egg mass of organisms adheres. There are three main methods, such as renewal and new one, and spraying chemicals to kill floating larvae, but these methods cannot completely remove them. That is, when a fish is concentrated in a narrow space and subjected to a medicinal bath, the fish body is damaged and oxygen deficiency occurs, and due to the increase in the weight of the fish body, the labor force increases (normal scale). However, it is difficult to treat 100% by regular treatment (every 10 people are required) and regular treatment (every 10 to 20 days), so parasites and cage net-adhering organisms remain, and one parasite again produces 300 eggs. As a result, the damage caused by parasites cannot be extinguished. In addition, due to the parasite infestation, there is no countermeasure against bacterial diseases caused by scratching the fish net on the net. With the new replacement of the cage net, the weight of the cage net increases due to diatoms, mussels, red barnacles, etc. attached to the cage net, which makes it difficult to pull the cage net up. In addition to this, because the mesh is small, tidal flow deteriorates, where the dissolved oxygen amount decreases and the fish weaken and the growth is delayed,
Egg masses from parasites are more likely to attach. Therefore, it is difficult to kill parasites because they have a good spawning site. In addition, replacing this with a net requires a lot of labor and cost, and if this is not done, the stress generation and bacterial diseases in fish in a hypoxic environment will increase. Egg masses of parasites attached to fish stored in fish cage nets hatch in 5 days at a water temperature of 25 ° C after they attach to the nets and can float freely as larvae and move freely. obtain. If food is stopped to prevent this, the fish body will be weakened, so the only option is to spray the drug in water, but considering the toxicity and persistence to fish, dilution of the concentration in water, etc., the drug that is useful and requires immediate effect is currently I can't find it. Also,
No countermeasures are found for bacterial diseases. As described above, the three methods cannot be expected to be effective even if they are implemented, but since there is no other countermeasure, they can only be continued, and they are extremely problematic methods that repeat the vicious circle as described above. The present invention has been made in view of the above-mentioned conventional problems, and is excellent in killing fish parasites, bacteria and fish cage net-adhering organisms that are safe for both humans and fish, and at the same time It is an object of the present invention to provide a method of erasing fish parasites and bacteria and removing organisms attached to fish cage nets, which can be reduced in quantity, and can be carried out easily and continuously for a long period of time.

【0004】[0004]

【課題を解決するための手段】上述のような目的を達成
するために、本発明請求項1記載の魚類寄生虫および細
菌の死滅と生簀網付着生物の除去方法では、陽極および
陰極で形成された電極を魚類の棲息域内における天然海
水中に設け、該電極に直流電流を通電して次亜塩素酸ソ
ーダを発生させ、前記天然海水中の残留塩素濃度を調整
することにより、魚類を弊死させる魚類寄生虫および細
菌と生簀網付着生物を死滅除去する方法を採用した。
In order to achieve the above-mentioned object, in the method of killing fish parasites and bacteria and removing organisms attached to cage nets according to claim 1 of the present invention, an anode and a cathode are used. The electrode is installed in natural seawater within the habitat of the fish, direct current is applied to the electrode to generate sodium hypochlorite, and the residual chlorine concentration in the natural seawater is adjusted to kill the fish. The method of killing and removing the fish parasites and bacteria and the organisms attached to the cage nets was adopted.

【0005】また、請求項2記載の魚類寄生虫および細
菌の死滅と生簀網付着生物の除去方法では、天然海水中
の浮上生簀内外に陽極および陰極で形成された電極を設
けて該電極に直流電流を通電して次亜塩素酸ソーダを発
生させ生簀内の残留塩素濃度を調整することにより、生
簀に収容する魚類を弊死させる魚類寄生虫および細菌と
生簀網付着生物を死滅除去する方法を採用した。
Further, in the method for killing fish parasites and bacteria and removing organisms attached to fish cage nets according to claim 2, an electrode formed by an anode and a cathode is provided inside and outside the floating cage in natural seawater, and a direct current is applied to the electrode. A method of killing and removing fish parasites, bacteria and fish cage net-adhering organisms that kill fish stored in the cage by adjusting the residual chlorine concentration in the cage by applying an electric current to generate sodium hypochlorite. Adopted.

【0006】また、請求項3記載の魚類寄生虫および細
菌の死滅と生簀網付着生物の除去方法では、浮上ブイに
陽極および陰極で形成された電極を設け該電極に直流電
流を通電して次亜塩素酸ソーダを発生させ海水中の残留
塩素濃度を調整することにより魚類寄生虫および細菌と
生簀網付着生物を集中的に死滅除去する方法を採用し
た。
In the method for killing fish parasites and bacteria and removing organisms attached to fish cage nets according to a third aspect of the present invention, an electrode formed of an anode and a cathode is provided on the floating buoy, and a direct current is applied to the electrode to apply the current. We adopted a method of intensively killing and removing fish parasites and bacteria and fish cage net attachment organisms by generating sodium chlorite and adjusting the residual chlorine concentration in seawater.

【0007】また、請求項4記載の魚類寄生虫および細
菌の死滅と生簀網付着生物の除去方法では、船舶に設け
た天然海水を直接生簀内へ吸入排出できるタンク内で陽
極および陰極で形成された電極に直流電流を通電してタ
ンク内の次亜塩素酸ソーダを発生させタンク内の残留塩
素濃度を調整し、該タンク内部水を生簀内水域に還流さ
せることにより魚類寄生虫および細菌と生簀網付着生物
を死滅除去する方法を採用した。
Further, in the method for killing fish parasites and bacteria and removing organisms attached to fish cage nets according to claim 4, the natural seawater provided on a ship is formed by an anode and a cathode in a tank which can be directly sucked and discharged into the fish cage. A direct current is applied to the electrode to generate sodium hypochlorite in the tank to adjust the residual chlorine concentration in the tank, and the water inside the tank is returned to the water in the fish cage to repel fish parasites, bacteria, and fish cages. The method of killing and removing the net-attached organisms was adopted.

【0008】また、請求項5記載の魚類寄生虫および細
菌の死滅と生簀網付着生物の除去方法では、請求項1,
2,3または4記載の魚類寄生虫および細菌の死滅と生
簀網付着生物の除去方法において、前記残留塩素濃度調
整用の電極に加えて銅イオン発生用の陽極および陰極で
形成された電極を設け、該電極に直流電流を通電して海
水中に銅イオンを発生させることにより、魚類寄生虫お
よび細菌と生簀網付着生物を死滅除去する方法を採用し
た。
The method for killing fish parasites and bacteria and removing the organisms attached to cage nets according to claim 5,
In the method for killing fish parasites and bacteria and removing organisms attached to cages according to 2, 3 or 4, an electrode formed of an anode and a cathode for generating copper ions is provided in addition to the electrode for adjusting the residual chlorine concentration. A method of killing and removing fish parasites and bacteria and organisms attached to the cage net by applying a direct current to the electrode to generate copper ions in seawater was adopted.

【0009】[0009]

【作用】本発明請求項1記載の魚類寄生虫および細菌の
死滅と生簀網付着生物の除去方法では、以下に述べるよ
うな作用がある。本発明は天然海水中の塩素濃度18.
980ppmを電気分解により次亜塩素酸ソーダの生成
に転換し、この次亜塩素酸ソーダを残留塩素として任意
に例えば1ppm〜2ppmとすることで、天然海水中
の残留塩素の増加により任意の濃度に存在させることに
より、塩素による消毒効果を利用することを可能とした
ものであり、漁業への寄与効果は極めて大きい。天然海
水を利用して電気分解により、天然海水の構成元素であ
る塩素を残留塩素として増加させるだけのものであり、
これ等の残留塩素は、消毒、滅菌作用後は再び天然海水
に戻るため、自然環境には何らの害、副作用を与えるこ
とは無い。一般的に、海水のPHは8程度であるが、残
留塩素の海水中の減少は、海水中の還元性無機物,有機
物との反応、あるいは、光化学反応等によりみられるの
で、殺菌効果を維持するには、継続して次亜塩素酸ソー
ダを発生させる必要がある。このため、本発明は、天然
海水中のPHによる干渉も除外しうる安定した次亜塩素
酸ソーダの発生機構であり、かつ残留塩素の殺菌効果を
維持しうる作用がある。
The method of killing fish parasites and bacteria and removing the organisms attached to the nets according to the first aspect of the present invention has the following effects. The present invention has a chlorine concentration of 18.
980 ppm is converted to the production of sodium hypochlorite by electrolysis, and this sodium hypochlorite is voluntarily made to be, for example, 1 ppm to 2 ppm as residual chlorine, thereby increasing the residual chlorine in natural seawater to an arbitrary concentration. The presence of chlorine makes it possible to utilize the disinfection effect of chlorine, and the contribution to the fishery is extremely large. It is only to increase chlorine, which is a constituent element of natural seawater, as residual chlorine by electrolysis using natural seawater,
Since such residual chlorine returns to natural seawater after the disinfection and sterilization actions, it does not cause any harm or side effect to the natural environment. Generally, the pH of seawater is about 8, but the reduction of residual chlorine in seawater is observed due to the reaction with reducing inorganic substances and organic substances in seawater, or photochemical reaction, so that the bactericidal effect is maintained. Therefore, it is necessary to continuously generate sodium hypochlorite. Therefore, the present invention has a stable generation mechanism of sodium hypochlorite that can eliminate interference due to PH in natural seawater, and also has an effect of maintaining the bactericidal effect of residual chlorine.

【0010】本発明請求項2記載の魚類寄生虫および細
菌の死滅と生簀網付着生物の除去方法では、天然海水又
は河川水中の浮上生簀の内外に陽極および陰極で形成さ
れた電極を設け直流電流を通電することにより生簀の外
部では、生簀網付着生物を死滅させて生簀内の溶存酸素
量の低下を防止すると共に、生簀内部では収容魚類の寄
生虫および細菌を死滅しうる二重の効果が発生する。浮
上生簀は単独ではなく数十個から数百個の単位で集合さ
れているので、従来魚類寄生虫および細菌や生簀網付着
生物等発生時には生簀の移動退避等の作業が発生したも
のが一切必要なくなり、かつ安心して蓄養が可能とな
る。加えて多数の生簀で次亜塩素酸ソーダを発生させて
いるため潮流の変化が生じても周辺の残留塩素により魚
類寄生虫および細菌や生簀網付着生物等は死滅している
ので無害となしうる効果が発生する。遠方の周辺海域へ
の影響も、残留塩素が天然海水に戻る作用のため無視し
うる。
In the method for killing fish parasites and bacteria and removing organisms attached to fish cage nets according to a second aspect of the present invention, an electrode formed of an anode and a cathode is provided inside and outside the floating cage in natural seawater or river water to provide a direct current. By energizing the outside of the cage, it is possible to kill the organisms attached to the cage net to prevent a decrease in the amount of dissolved oxygen in the cage, and inside the cage there is a double effect of killing the parasites and bacteria of the housed fish. Occur. Since the floating cages are assembled not in a single unit but in a unit of tens to hundreds, it is necessary to perform work such as moving and retracting cages when conventional fish parasites, bacteria, and cage-net attachment organisms occur. It will disappear and you will be able to farm with confidence. In addition, because sodium hypochlorite is generated in a large number of cages, even if the tidal current changes, fish parasites, bacteria, and cage net-adhering organisms have died due to residual chlorine in the vicinity, so it can be considered harmless. The effect occurs. Impacts on distant surrounding waters can be ignored because residual chlorine returns to natural seawater.

【0011】本発明請求項3記載の魚類寄生虫および細
菌の死滅と生簀網付着生物の除去方法では、浮上ブイに
前述の陽極と陰極を設け、該電極に直流電流を通電して
水中に次亜塩素酸ソーダを発生し濃度を調整する。この
浮上ブイは、魚類寄生虫および細菌や生簀網付着生物等
の流れと同一に移動することが可能であるため、浅い水
位や岩礁域等船舶が移動不可能な海域でも残留塩素濃度
を任意に調節できるので、魚類寄生虫および細菌や生簀
網付着生物等の集中水域において効果を発生する。
In the method for killing fish parasites and bacteria and removing organisms attached to fish cage nets according to claim 3 of the present invention, the above-mentioned anode and cathode are provided on the floating buoy, and a direct current is applied to the electrodes so that Generate sodium chlorite and adjust the concentration. Since this floating buoy can move in the same way as fish parasites, bacteria, and fish cage-attached organisms, the residual chlorine concentration can be arbitrarily adjusted even in shallow water levels or rocky reef areas where ships cannot move. Because it can be adjusted, it produces effects in concentrated waters such as fish parasites, bacteria, and cage net attachment organisms.

【0012】本発明請求項4記載の魚類寄生虫および細
菌の死滅と生簀網付着生物の除去方法では、船舶を魚類
寄生虫および細菌や生簀網付着生物等の発生が確認され
次第発生域に直行させ、発生域を周回させながら魚類寄
生虫および細菌や生簀網付着生物等を死滅させる。船舶
は行動範囲が広く魚類寄生虫および細菌や生簀網付着生
物等発生における初期効果が大きい。
[0012] In the method for killing fish parasites and bacteria and removing living fish net adhering organisms according to claim 4 of the present invention, the ship is directly moved to the area where the generation of fish parasites and bacteria and living fish net adhering organisms is confirmed. Then, the fish parasites and bacteria, organisms attached to cage nets, etc. are killed while orbiting the generation area. Ships have a wide range of action and have a large initial effect on the development of fish parasites, bacteria, and cage net attachment organisms.

【0013】本発明請求項5記載の魚類寄生虫および殺
菌の死滅と生簀網付着生物の除去方法では、前記天然海
水中、浮上生簀内外、浮上ブイ、船舶タンク等に次亜塩
素酸ソーダを海水の電気分解によって発生させる方法に
加え、同様にそれぞれの天然海水中の銅イオン濃度3p
pbを高濃度に、例えば30ppbとして次亜塩素酸ソ
ーダと併用することにより、殺菌、死滅除去効果も約2
倍となし得ると共に、銅イオン濃度を1/2、次亜塩素
酸ソーダ濃度も1/2の発生として少くすることが可能
である。このため、消費電力、電極の消耗も軽減し得る
相乗効果が大きい。銅イオン、塩素は、共に天然海水中
に存在するものであり、死滅作用後は、再び天然海水に
戻り再利用されるので、自然環境の汚染は全く無い。
In the method for killing fish parasites and sterilization of bacteria and removing organisms attached to cage nets according to claim 5 of the present invention, sodium hypochlorite is added to the natural seawater, inside and outside floating cages, floating buoys, ship tanks and the like. In addition to the method of generating by electrolysis of copper, copper ion concentration in each natural seawater is 3p
By using a high concentration of pb, for example, 30 ppb in combination with sodium hypochlorite, the sterilization and killing removal effect is about 2
It is possible to reduce the copper ion concentration to 1/2 and the sodium hypochlorite concentration to 1/2, thereby reducing the concentration. Therefore, there is a great synergistic effect that power consumption and electrode consumption can be reduced. Copper ions and chlorine are both present in natural seawater, and after killing, they are returned to natural seawater and reused, so there is no pollution of the natural environment.

【0014】[0014]

【実施例】以下本発明の実施例を図面に基づいて詳細に
説明する。まず、図1により第1実施例について説明す
る。図1は海面9に隣接して設けられた一般的蓄養水槽
2を示しており、該水槽2は、海面9とは防潮堤8が開
閉戸7により仕切られて必要の都度天然海水又は河川水
を交換できる構造である。そして、魚類寄生虫および細
菌や生簀網付着生物等4が開閉戸7の開閉によって取水
中に侵入しても魚類3に付着する魚類寄生虫および細菌
や生簀網付着生物等4を死滅させる方式を採用する。即
ち調整槽2aは取水管1a,ポンプ1,送水管1bの順
にパイプで接続され、天然海水又は河川水を取水する。
この調整槽2a内には、次亜塩素酸ソーダ濃度調整発生
装置5と電線6で接続されたチタン陽極5a、チタン陰
極5bが設けられ、次亜塩素酸ソーダ濃度調整発生装置
5で直流電流を通電することで次式のように次亜塩素酸
ソーダを発生する。
Embodiments of the present invention will now be described in detail with reference to the drawings. First, the first embodiment will be described with reference to FIG. FIG. 1 shows a general cultivated water tank 2 provided adjacent to the sea surface 9. The sea tank 9 is separated from the sea surface 9 by a door 7 that separates a seawall 8 from natural seawater or river water. It is a structure that can be exchanged. Then, even if the fish parasites and bacteria, organisms attached to fish cage nets 4 enter the water intake by opening and closing the door 7, a method of killing the fish parasites and bacteria attached to fish 3 and organisms attached to fish nets 4 adopt. That is, the adjusting tank 2a is connected by a pipe in the order of the intake pipe 1a, the pump 1, and the water supply pipe 1b to take in natural seawater or river water.
In this adjusting tank 2a, a titanium anode 5a and a titanium cathode 5b connected to the sodium hypochlorite concentration adjusting generator 5 by an electric wire 6 are provided, and a direct current is generated by the sodium hypochlorite concentration adjusting generator 5. By energizing, sodium hypochlorite is generated as shown in the following formula.

【0015】次亜塩素酸ソーダの発生 化学式1から化学式4までは陰極反応を示している。Generation of Sodium Hypochlorite Chemical formulas 1 to 4 show cathodic reactions.

【化1】 [Chemical 1]

【0016】[0016]

【化2】 [Chemical 2]

【0017】[0017]

【化3】 [Chemical 3]

【0018】[0018]

【化4】 [Chemical 4]

【0019】化学式5は陽極反応を示している。Chemical formula 5 shows an anodic reaction.

【化5】 [Chemical 5]

【0020】全体ではAs a whole

【化6】 [Chemical 6]

【0021】陰極で生じるNaOHと陽極で生じるCl
2 が反応し次亜塩素酸ソーダを発生する。
NaOH generated at the cathode and Cl generated at the anode
2 reacts to generate sodium hypochlorite.

【化7】 [Chemical 7]

【0022】この発生した次亜塩素酸ソーダによって、
水槽2内の魚類寄生虫および細菌や生簀網付着生物等を
死滅させる。この場合、天然海水中の残留塩素の濃度の
経時変化による減少は緩やかであるが、連続して海水を
電気分解することにより安定して供給し得る。
With this generated sodium hypochlorite,
Kill fish parasites, bacteria, organisms attached to cage nets, etc. in the aquarium 2. In this case, the concentration of residual chlorine in the natural seawater decreases slowly with time, but can be stably supplied by continuously electrolyzing the seawater.

【0023】この場合魚類寄生虫および細菌や生簀網付
着生物等4が水槽2に侵入しても天然海水中の残留塩素
濃度を0.5ppm以上に調整することで死滅させるこ
とができる。同時に魚類寄生虫の水中浮遊幼虫も死滅す
る。
In this case, even if fish parasites, bacteria, organisms attached to fish cage nets 4, etc. enter the aquarium 2, they can be killed by adjusting the residual chlorine concentration in natural seawater to 0.5 ppm or more. At the same time, floating parasites of fish parasites in water also die.

【0024】次に図2,図3により第2実施例を説明す
る。尚、第1実施例と同一構成部分は同一の符号を付す
る。この実施例では浮上生簀に次亜塩素酸ソーダ濃度調
整発生装置とチタン陽極とチタン陰極とを設け、その内
外部に次亜塩素酸ソーダを発生させて魚類寄生虫および
細菌や生簀網付着生物等の侵入を防止、死滅させるもの
である。海面9に浮子11により浮上する浮上生簀10
a,10b,10cは、歩行板12上部に設けた次亜塩
素酸ソーダ濃度調整発生装置5で直流電流を発生させ、
生簀に吊り下げたチタン陽極5a,チタン陰極5bに電
線6で通電することにより生簀内外に次亜塩素酸ソーダ
を発生し、外部よりの魚類寄生虫および細菌や生簀網付
着生物等を死滅させて侵入を防止すると共に内部収容の
魚類の付着寄生虫を同様死滅除去させるものである。本
装置の次亜塩素酸ソーダ濃度調製発生装置5は、海面で
の浮上生簀が近接する場合には陸上に設けて同様な残留
塩素の殺菌効果を発生させることも可能である。浮上生
簀は通常海上において夫々が固定されるため、単体とし
ての効果に加えて集合体としての残留塩素の拡散がある
から、より強力なる殺菌効果として相乗される。図3に
おいてチタン陽極5aとチタン陰極5bとを交互に配置
しておくと、浮上生簀の内周面を周回するように電流が
発生し、魚類寄生虫および細菌や生簀網付着生物等が潮
流によってどの方向から侵入してきても全周に生じた残
留塩素によって完全に死滅する。また、潮流が変わって
も充分に対処しうるよう最外側の潮流側の浮上生簀には
外部にチタン陽極5aまたはチタン陰極5bを配置する
ことができるよう配慮する。
Next, a second embodiment will be described with reference to FIGS. The same components as those in the first embodiment are designated by the same reference numerals. In this example, the floating cage is provided with a sodium hypochlorite concentration adjusting generator, a titanium anode and a titanium cathode, and sodium hypochlorite is generated inside and outside of the floating cage to cause fish parasites, bacteria, and cage net attachment organisms, etc. It prevents the invasion of and kills them. Levitation cage 10 that floats on the sea surface 9 by a float 11.
a, 10b, 10c generate a direct current with the sodium hypochlorite concentration adjusting generator 5 provided on the upper part of the walking board 12,
By energizing the titanium anode 5a and the titanium cathode 5b suspended in the cage with the electric wire 6, sodium hypochlorite is generated inside and outside the cage, and kills fish parasites and bacteria and organisms attached to the cage net from the outside. In addition to preventing invasion, it also kills and removes adherent parasites of fish contained inside. The sodium hypochlorite concentration adjusting and generating device 5 of this device can be installed on land to generate a similar sterilizing effect of residual chlorine when the floating cage on the sea surface is close. Floating cages are usually fixed on the sea, so that in addition to the effect as a single substance, residual chlorine diffuses as an aggregate, which synergizes as a stronger bactericidal effect. When the titanium anodes 5a and the titanium cathodes 5b are alternately arranged in FIG. 3, an electric current is generated so as to circulate on the inner peripheral surface of the floating cage, and fish parasites, bacteria, fish cage net attachment organisms, etc. No matter which direction it enters, it will be completely killed by the residual chlorine generated all around. Also, in order to be able to sufficiently cope with the change of tidal current, it is considered that the outermost tidal current side floating cage can be provided with a titanium anode 5a or a titanium cathode 5b outside.

【0025】次に図4により第3実施例を説明する。図
面は浮上ブイ15を魚類寄生虫および細菌や生簀網付着
生物等の発生海域に放置することにより魚類寄生虫およ
び細菌や生簀網付着生物等の潮流による回遊と同様に自
然に流れることによって濃密なる魚類寄生虫および細菌
や生簀網付着生物等の集中海域に搬入し、内蔵するバッ
テリ−より直流電流をブイ下面に設けたチタン陽極、チ
タン陰極に通電し次亜塩素酸ソーダを発生させて魚類寄
生虫および細菌や生簀網付着生物等を死滅させるもので
ある。そして、浮上ブイ15は海面9を魚類寄生虫およ
び細菌や生簀網付着生物等4と共に浮遊し、内蔵するバ
ッテリ−16により発生する直流電流が電線6を介し次
亜塩素酸ソーダ濃度調整発生装置5によりチタン陽極5
a,チタン陰極5bに送られ次亜塩素酸ソーダを発生し
魚類寄生虫および細菌や生簀網付着生物等を死滅させ
る。また、同時に内蔵するタイマ−17によって電柱1
4に設けた電灯13に送電し夜間のみ点灯する。低水
位、岩礁地帯等通行が難しい海域でも充分に次亜塩素酸
ソーダを発生しうるよう強力なケ−スに収容し、夜間は
点灯しうる方式とすることで、複雑なる海域における魚
類寄生虫および細菌や生簀網付着生物等の死滅を自動的
に行わしめることができる。尚、バッテリー16には太
陽電池および波力発電装置により充電させ長期的に使用
することもできる。また、ブイ所在発信機等も備えるこ
とができる。魚類寄生虫および細菌や生簀網付着生物等
は風向、風力、潮流、波浪によってその流域が微妙に変
化するため、本方式を採用することで魚類寄生虫および
細菌や生簀網付着生物等の存在場所を把握する効果が生
じると共に死滅効果も相乗される。魚類寄生虫および細
菌や生簀網付着生物等は水深の高低に拘らず風流、水流
に乗って移動するため浮上ブイは魚類寄生虫および細菌
や生簀網付着生物等と共に移動し死滅させる効果を有す
る。
Next, a third embodiment will be described with reference to FIG. The drawing shows that the floating buoy 15 is left in the sea area where fish parasites, bacteria, and fish cage net attachment organisms, etc. It is carried into a concentrated sea area of fish parasites, bacteria, and fish net-adhering organisms, and a direct current is supplied from the built-in battery to the titanium anode and titanium cathode provided on the lower surface of the buoy to generate sodium hypochlorite and generate fish parasite. It kills insects, bacteria, organisms attached to cage nets, etc. The floating buoy 15 floats on the sea surface 9 together with fish parasites, bacteria, and cage net attachment organisms 4, and the direct current generated by the built-in battery 16 is passed through the electric wire 6 to generate the sodium hypochlorite concentration adjustment generator 5 By titanium anode 5
a, sent to the titanium cathode 5b to generate sodium hypochlorite and kill fish parasites, bacteria, organisms attached to cage nets and the like. In addition, the utility pole 1 is installed by the timer-17 that is built in at the same time.
Electric power is transmitted to the electric lamp 13 provided in No. 4 and is turned on only at night. Fish parasites in complex waters are housed in a strong case that can generate enough sodium hypochlorite even in low water levels, rocky areas, and other difficult water passages, and can be turned on at night. In addition, it is possible to automatically kill bacteria and organisms attached to the cage net. The battery 16 can be charged by a solar cell and a wave power generator for long-term use. It can also be equipped with a buoy location transmitter. The location of fish parasites, bacteria, and fish net-adhering organisms, etc. can be determined by adopting this method because the basin of fish parasites, bacteria and fish-netting organisms may change subtly due to wind direction, wind force, tidal current, and waves. Along with the effect of grasping, the killing effect is synergized. Since the fish parasites and bacteria and organisms attached to the fish nets move along with the wind and water currents regardless of the depth of the water, the floating buoy has the effect of migrating along with the fish parasites and bacteria and organisms attached to the fish net.

【0026】次に図5により第4実施例を説明する。図
面は天然海水又は河川域を移動する船舶に魚類寄生虫お
よび細菌や生簀網付着生物等の吸入、排水配管と次亜塩
素酸ソーダ濃度調整発生装置を装着したタンクを設け、
タンク上部からチタン陽極、チタン陰極をタンク中に吊
り下げ、次亜塩素酸ソーダを発生させることによりタン
ク内の魚類寄生虫および細菌や生簀網付着生物等を死滅
させると共に、残留塩素濃度の高い排水を魚類寄生虫お
よび細菌や生簀網付着生物等の集中海域に放出すること
で二重の魚類寄生虫および細菌や生簀網付着生物等死滅
効果を生じるものである。すなわち船舶19の内部に設
けた水吸入箱18から取水管1a,ポンプ1、送水管1
bを経由してタンク20に送水し、次亜塩素酸ソーダ濃
度発生装置5と電線6で接続されたタンク20内のチタ
ン陽極5a、チタン陰極5bに通電してタンク20内部
に次亜塩素酸ソーダを発生する。タンク20内部で死滅
した魚類寄生虫および細菌や生簀網付着生物等は排水管
21により海面9に放出される。この場合、魚類寄生虫
および細菌や生簀網付着生物等の水深が約4mであるの
で、魚類寄生虫および細菌や生簀網付着生物等4の集中
している水位から効率的に吸入できるように位置を変え
て複数の水吸入箱を設けて取水の調節が出来得るものと
する。尚、船舶19は順次魚類寄生虫および細菌や生簀
網付着生物等を求めて死滅させ順次移動し得るものとす
る。従来、魚類寄生虫および細菌や生簀網付着生物等の
死滅対策としては確定されたものはないので、本実施例
により魚類寄生虫および細菌や生簀網付着生物等発生の
初期において広範囲に集中的に死滅させる効果が得られ
る。
Next, a fourth embodiment will be described with reference to FIG. The drawing shows a tank that is equipped with a suction pipe for fish parasites and bacteria, organisms attached to cage nets, drainage pipes, and a sodium hypochlorite concentration adjustment generator on a ship that moves in natural seawater or river areas.
By suspending titanium anode and titanium cathode from the top of the tank in the tank and generating sodium hypochlorite, fish parasites and bacteria in the tank and organisms attached to cage nets are killed, and wastewater with high residual chlorine concentration Is released into the concentrated sea area of fish parasites, bacteria, and fish cage net attachment organisms, etc. to produce a double effect of killing fish parasites, bacteria, fish cage net attachment organisms, and the like. That is, from the water suction box 18 provided inside the ship 19, the intake pipe 1a, the pump 1, the water supply pipe 1
Water is sent to the tank 20 via b, and the titanium anode 5a and the titanium cathode 5b in the tank 20, which are connected to the sodium hypochlorite concentration generator 5 by the electric wire 6, are energized to enter the tank 20 into the hypochlorous acid. Generates soda. The fish parasites, bacteria, organisms attached to the cage nets, and the like that have died inside the tank 20 are discharged to the sea surface 9 by the drainage pipe 21. In this case, since the water depth of fish parasites, bacteria, and organisms attached to fish cage nets is about 4m, it is possible to efficiently inhale from the water level where fish parasites, bacteria, organisms attached to fish cage nets, etc. 4 are concentrated. It shall be possible to adjust the water intake by installing multiple water suction boxes by changing the above. The ship 19 is assumed to be capable of sequentially dying in order to find fish parasites, bacteria, organisms attached to cage nets, etc., and to move sequentially. Conventionally, there is no definite measure for killing fish parasites, bacteria, and cage-net adhering organisms, etc. Has the effect of killing.

【0027】次に図6により第5実施例を説明する。図
6は、前記浮上生簀10aに設けた次亜塩素酸ソーダ発
生用の電極に加えて銅電極5c,鉄電極5dを設け、電
線6で銅イオン濃度発生装置22と接続した状態を示し
ている。この銅イオン濃度発生装置22により銅電極5
c,鉄電極5dに直流電流を通電することで任意濃度の
銅イオン23を発生させる。この場合、次亜塩素酸ソー
ダも同様に発生しているので、消毒効果のある残留塩
素、例えば塩素が5ppmだけの場合よりも、銅イオン
を付加した塩化銅CuCl2 を発生させることで、塩素
を2.5ppmと塩化銅を0.15ppm併用した方が
残留塩素量の接続が長く、殺菌効果が2倍となる効果を
発生する。勿論、実施上では、この数値は規制値以内と
して無公害とする。この場合、銅イオンの水産庁瀬戸内
海海水基準値である30ppbに銅イオンの発生を調整
すると、銅イオンは、寄生虫、微生物、藻類等の体内に
浸透し、原形質を凝固させ、一方の残留塩素Cl2 (H
Cl,ClO)を500ppbとすることで細菌類を瞬
時に死滅させ、200ppbでも10分間で死滅させ、
また、珪藻類は500ppb〜1ppm、原生動物は3
00ppbから1ppmで死滅させた。また、浮上生簀
10aが金属製の場合は、鉄電極5dに替えて浮上生簀
10aを陰極とすることも可能である。この場合、魚類
寄生虫の幼生や卵塊は、浮上生簀金網に直接付着してい
るので、殺菌効果に加えての通電効果及び陰極、陽極を
遂次電源を切替えることにより、発生する水素ガスによ
る剥離効果が生じるため、金網より容易に死滅離脱す
る。
Next, a fifth embodiment will be described with reference to FIG. FIG. 6 shows a state in which a copper electrode 5c and an iron electrode 5d are provided in addition to the electrodes for generating sodium hypochlorite provided on the floating cage 10a, and the wires 6 are connected to the copper ion concentration generator 22. . With this copper ion concentration generator 22, the copper electrode 5
c, by supplying a direct current to the iron electrode 5d, copper ions 23 having an arbitrary concentration are generated. In this case, since sodium hypochlorite is also generated, it is possible to generate residual chlorine having a disinfecting effect, for example, by generating copper chloride CuCl 2 to which copper ions are added, as compared with the case where chlorine is only 5 ppm. The combination of 2.5 ppm and 0.15 ppm of copper chloride results in a longer residual chlorine connection and doubles the bactericidal effect. As a matter of course, in practice, this value is within the regulation value and no pollution occurs. In this case, if the generation of copper ions is adjusted to 30 ppb, which is the Seto Inland Sea seawater standard value for copper ions, the copper ions will penetrate into the body of parasites, microorganisms, algae, etc., coagulate protoplasts, and leave one residue. Chlorine Cl 2 (H
Cl, ClO) to 500 ppb to kill bacteria instantly, even 200 ppb to kill in 10 minutes,
Also, diatoms are 500 ppb-1ppm, and protozoa are 3
It was killed at 1 ppm from 00 ppb. When the floating cage 10a is made of metal, the floating cage 10a can be used as a cathode instead of the iron electrode 5d. In this case, the fish parasite larvae and egg mass are directly attached to the floating cage net, so in addition to the bactericidal effect, the energization effect and the separation of the cathode and anode by the successive generation of hydrogen gas causes the exfoliation. As it produces an effect, it is more easily killed and separated from wire mesh.

【0028】以上の実施例において次のような効果を奏
した。 (1) 薬浴では魚類にも被害が発生するので、時間的
な制約が生じるが、本発明の次亜塩素酸ソーダを電気化
学作用により500ppb以上とすることでは魚類への
被害は発生せず、逆に魚類への寄生虫を死滅させる効果
が発生する。尚、死滅した魚類寄生虫および細菌や生簀
網付着生物等は海底に沈下する。 (2) 付着生物としての貝類の死滅効果としては、ア
カフジツボの幼生を250ppb6分で死滅させた。ま
た、マガキ幼生は200ppb7分で死滅し、ムラサキ
イガイの幼生を500ppb10分で死滅させたので、
生簀網付着生物としての貝類は、完全に幼生のうちに除
去し得る。 (3) 同様に、付着生物としての生簀網への被害の大
きい珪藻は、銅イオンにより500ppb10分で死滅
した。 (4) 赤潮(ギムノディニウム,ミキモトイ)は次亜
塩素酸ソーダ50ppbで瞬時に膨出し死滅した。同じ
くシャトネラ、アンテイカも同様死滅した。この場合銅
イオン20ppbを加えることで、次亜塩素酸ソーダは
20ppbでの死滅効果を発揮した。
The following effects are obtained in the above embodiment. (1) In the medicinal bath, the fish is also damaged, so that there is a time restriction. However, if the sodium hypochlorite of the present invention has an electrochemical action of 500 ppb or more, the fish is not damaged. Conversely, the effect of killing parasites on fish occurs. In addition, dead fish parasites, bacteria and organisms attached to cage nets sink to the seabed. (2) As for the effect of killing shellfish as adhering organisms, the larvae of red barnacles were killed at 250 ppb 6 minutes. Also, the oyster larvae were killed at 200 ppb 7 minutes, and the blue mussel larvae were killed at 500 ppb 10 minutes.
The shellfish as a living cage net attachment organism can be completely removed in the larva. (3) Similarly, the diatom, which is a large damage to the cage net as an attached organism, was killed by copper ions at 500 ppb for 10 minutes. (4) Red tide (Gymnodinium, Mikimotoi) swelled and died instantly with 50 ppb of sodium hypochlorite. Similarly, Shatonella and Antica also died. In this case, by adding 20 ppb of copper ion, sodium hypochlorite exhibited a killing effect at 20 ppb.

【表1】 上記条件にて魚類寄生虫(ハダムシ:ベネデニア、セリ
オラ)や生簀網付着生物等は10分間で死滅した。海底
沈下した魚類寄生虫や生簀網付着生物等は海底での生物
連鎖の餌料となるが、無公害である。
[Table 1] Under the above-mentioned conditions, fish parasites (Haddamushi: Benedenia, Ceriora), fish cage net-adhering organisms, etc. died in 10 minutes. Sea-submerged fish parasites and fish cage net-adhering organisms serve as food for the biological chain on the seabed, but are non-polluting.

【0029】以上説明したように、水中に設けた電極に
直流電流を通電して次亜塩素酸ソーダを発生させる方法
では、魚類寄生虫および細菌や生簀網付着生物等被害と
しての魚類寄生虫および細菌や生簀網付着生物等自身の
魚毒性、魚類寄生虫および細菌や生簀網付着生物等の分
解による有毒物質の発生、魚類寄生虫および細菌や生簀
網付着生物等の大量発生による環境水中の酸素不足、魚
類寄生虫および細菌が魚介類の表皮及び鰓に寄生するこ
とによる呼吸の機械的障害、及びストレス等が挙げられ
ているが、従来対策としてなすべきものがみられず魚類
寄生虫および細菌や生簀網付着生物等被害は打つべき手
法があげられなかったことから脱却して前向きに対応し
得ることが可能となった。近年、外国よりの養殖用種苗
の輸入により、種苗が細菌性疾病に汚染された状態で各
地に分散され発病することが増加しているが、これ等の
防疾対策としても充分対応し得る効果を有する。今後は
漁業者の将来への生活設計としての養殖事業、天然漁業
への夢も危険にさらされることもなくなるため、若年者
の後継者難が発生せず、本方法によって長期的な効果が
期待できる。
As described above, in the method of generating direct current through the electrode provided in water to generate sodium hypochlorite, fish parasites and bacteria and fish parasites causing damage to fish cage net attachment organisms, etc. Oxygen in environmental water due to bacterial toxicity of fish and fish attached to fish cage nets, generation of toxic substances due to decomposition of fish parasites and bacteria and fish attached to fish nets, large amount of fish parasites and generation of bacteria and fish attached to fish nets. Insufficiency, mechanical disorders of respiration due to parasitism of fish and shellfish epidermis and gill, and stress, etc. are mentioned. Since there was no method to deal with damage such as organisms attached to fish and cage nets, it was possible to take a positive approach by withdrawing. In recent years, the import of aquaculture seedlings from foreign countries has increased the number of seeds and seedlings that are dispersed in various places and become sick while being contaminated with bacterial diseases. Have. In the future, the dream of the aquaculture business and natural fishery as a life plan for the fishermen in the future will not be endangered, so the succession of young people will not occur, and this method is expected to have a long-term effect. it can.

【0030】本発明の実施例を図面により詳述してきた
が、本発明の具体的な方法及びこの方法に用いられる部
材や装置類の具体的な設計変更等があっても本発明に含
まれる。例えば、次亜塩素酸ソーダ濃度は任意に設定で
きるものであり、魚類寄生虫および細菌や生簀網付着生
物等として認められる多くの種類において個々の死滅最
適値を設定することができる。
Although the embodiment of the present invention has been described in detail with reference to the drawings, the present invention includes a specific method of the present invention and a specific design change of members and devices used in the method. . For example, the sodium hypochlorite concentration can be arbitrarily set, and individual killing optimum values can be set for many types recognized as fish parasites, bacteria, fish cage net attachment organisms, and the like.

【0031】また、陽極および陰極の材質は任意であ
り、例えば、不銹綱等の鉄材、または黒鉛等とすること
ができる。また、チタン電極に白金被覆や酸化被膜を付
加することもできる。
The material of the anode and the cathode is arbitrary, and for example, iron material such as stainless steel or graphite can be used. It is also possible to add a platinum coating or an oxide coating to the titanium electrode.

【0032】電気分解用の直流電源は、太陽電池や波力
発電装置等によっても供給することができる。
The DC power source for electrolysis can also be supplied by a solar cell, a wave power generator, or the like.

【0033】陽極または陰極はブロック状、線状等、形
状は任意に設定することができる。また、生簀網を金属
として電極に使用した場合、陰極部と陽極部を混在させ
てもよい。
The shape of the anode or the cathode can be arbitrarily set, such as a block shape or a linear shape. Further, when the cage net is used as a metal for the electrode, the cathode part and the anode part may be mixed.

【0034】次亜塩素酸ソーダ発生用の電極に加えて銅
電極5c,鉄電極5dを設けて海中の銅イオン濃度を調
整するのは、浮上生簀10aで行うのを説明したが、こ
の外、畜養水槽、浮上ブイ、タンク等にても行うことが
できる。
The copper electrode 5c and the iron electrode 5d are provided in addition to the electrode for generating sodium hypochlorite to adjust the concentration of copper ions in the sea in the floating cage 10a. It can also be performed in a livestock tank, a floating buoy, a tank, or the like.

【0035】[0035]

【発明の効果】本発明請求項1記載の魚類寄生虫および
細菌の死滅と生簀網付着生物の除去方法では、前記方法
を採用したため、従来から何ら改善対策されることのな
かった魚類寄生虫および細菌や生簀網付着生物死滅除去
のための使用に関わる困難な取扱方法、貯蔵、大量運
搬、大量の一度の放出等を含めて人件費、薬品代のコス
トに比べてきわめて低価格で魚類寄生虫および細菌や生
簀網付着生物等の死滅と除去効果を完全に持続し得ると
共に作業を無人化し得る効果がある。又、本発明は食品
用の殺菌剤として使用されている次亜塩素酸ソーダを海
中にて海水の電気分解を行って現場で無公害に生産し得
る画期的発明であり、充分に各水質基準値以内として使
用しながらの効果が抜群であるので、現在漁業者の置か
れている被害額、後継者難、精神的、人為的、財政的な
負担を一挙に解決できるものである。特に種苗生産及び
中間育成用としての稚魚は、魚類寄生虫および細菌や生
簀網付着生物等に弱いため格段の効果が発生する。
EFFECTS OF THE INVENTION In the method for killing fish parasites and bacteria and removing organisms attached to cage nets according to claim 1 of the present invention, since the above-mentioned method is adopted, fish parasites which have not been conventionally improved or improved. Bacteria and fish parasites are extremely low in price compared to labor costs, drug costs, including difficult handling methods related to use for killing and removing organisms attached to fish cages, storage, large-scale transportation, large-scale single release, etc. It also has the effect of completely sustaining the effect of killing and removing bacteria and organisms attached to cage nets, and of making the work unmanned. Further, the present invention is an epoch-making invention capable of producing pollution-free sodium on the site of sodium hypochlorite used as a bactericidal agent for food products by electrolyzing seawater in the sea. Since the effect is outstanding while using it within the standard value, it is possible to solve the damage amount, the difficulty of successors, the mental, artificial and financial burdens currently placed by fishermen all at once. In particular, juvenile fish for seed and seedling production and intermediate breeding have a remarkable effect because they are vulnerable to fish parasites, bacteria, and organisms attached to cage nets.

【0036】本発明請求項2記載の魚類寄生虫および細
菌の死滅と生簀網付着生物の除去方法では、前記方法を
採用したため、現在の漁業は沖合養殖が主流であり、ま
た、出荷前の本養殖生簀において最も危険にさらされ易
い浮上生簀において魚類寄生虫および細菌や生簀網付着
生物等の集中攻撃を受ける場合には、被害金額も数十億
円の単位であり、かつ数年かかって育成した魚類が一日
にて全滅するため、漁業者の精神的な疲労も甚だしいが
浮上生簀は複数集中して固定するため、その固定間隔に
歩行板を設け或いは作業船を置き、その上部に次亜塩素
酸ソーダ濃度発生調整装置を置き、浮上生簀外部及び内
部に陽電極及び陰電極を配置することで潮流の変動に対
処することによって、被害を未然に防止することができ
る。また、発電装置は、太陽電池、波力発電装置、ディ
ーゼル発電装置等を使用し、洋上で電力を容易に得るこ
とができる。尚、電極に発生する水素ガスによって対流
作用を促進する効果が生じる。浮上生簀の網目に付着す
る海洋生物は残留塩素によって剥離するため潮通しが良
好となり、残餌や排泄物等の生簀下部への脱落が良好と
なる効果が生じると共に寄生虫の除去作用も併せて発生
する相乗効果がある。
In the method for killing fish parasites and bacteria and removing organisms attached to cage nets according to claim 2 of the present invention, since the above method is adopted, offshore aquaculture is the mainstream of the current fishing industry, and the book before shipment is used. When a floating cage that is most likely to be exposed to aquaculture cages is subjected to a concentrated attack of fish parasites, bacteria, or fish cage net-attached organisms, the damage amount is in the unit of billions of yen and it takes several years to grow. Since the fish that have disappeared are completely wiped out in one day, mental fatigue of the fishermen is also great, but in order to fix multiple floating cages in a concentrated manner, a walking board or a work boat is placed at the fixed interval, and next to the upper part of it. Damage can be prevented in advance by coping with fluctuations in tidal current by placing a sodium chlorite concentration generation control device and arranging a positive electrode and a negative electrode outside and inside the floating cage. In addition, as the power generator, a solar cell, a wave power generator, a diesel power generator, or the like is used, and electric power can be easily obtained on the ocean. The hydrogen gas generated in the electrodes has the effect of promoting convection. Marine organisms adhering to the nets of floating cages are stripped by residual chlorine, which improves tidal flow, resulting in better removal of leftover food and excrement from the bottom of the cage, and the effect of removing parasites. There is a synergistic effect that occurs.

【0037】本発明請求項3記載の魚類寄生虫および細
菌の死滅と生簀網付着生物の除去方法では、魚類寄生虫
および細菌や生簀網付着生物等集中水域において、浮上
ブイに設けたバッテリーの直流電流を次亜塩素酸ソーダ
濃度発生調整装置を介してブイの下部の陽電極、陰電極
に通電した状態で、浮上ブイが魚類寄生虫および細菌や
生簀網付着生物等の集中水域の潮流によって移動する魚
類寄生虫および細菌や生簀網付着生物等と共に移動し得
るため、残留塩素効果が相乗的に発揮し得る。魚類寄生
虫および細菌や生簀網付着生物等は浅い水位でも狭い水
路でも通過するため、船舶等での追跡が困難なる場所に
放置する他に、魚類寄生虫および細菌や生簀網付着生物
等が侵入しては困る場所、例えば浮上生簀の集団場所等
に関所として複数配置してこの場所で完全に死滅させる
効果がある。
According to the method for killing fish parasites and bacteria and removing organisms attached to fish nets according to claim 3 of the present invention, a direct current of a battery provided on a floating buoy in a concentrated water area of fish parasites and bacteria and organisms attached to fish nets. Levitating buoys are moved by the tidal current in a concentrated water area such as fish parasites, bacteria, and cage net attachment organisms while the current is applied to the positive and negative electrodes under the buoy via the sodium hypochlorite concentration generator. Since they can move together with living fish parasites and bacteria and organisms attached to cage nets, the residual chlorine effect can be synergistically exerted. Since fish parasites, bacteria, and fish cage net-attachment organisms pass through shallow water levels and narrow waterways, they are left in places where it is difficult to track them by ships, etc. If there is a problem, for example, a group of floating cages, etc., will be placed in multiple places as galleries, and there will be the effect of completely killing them.

【0038】本発明請求項4記載の魚類寄生虫および細
菌の死滅と生簀網付着生物の除去方法では、魚類寄生虫
および細菌や生簀網付着生物等集中海域を船舶により魚
類寄生虫および細菌や生簀網付着生物等と共に移動し最
も密度の濃い場所に集中して高濃度の次亜塩素酸ソーダ
を発生し瞬時に死滅させることが可能であり容量的に大
型の次亜塩素酸ソーダ濃度調整発生装置を装備し魚類寄
生虫および細菌や生簀網付着生物等の発生と共に移動さ
せることにより未然に魚類の被害を防止する効果があ
る。他の魚類寄生虫および細菌や生簀網付着生物や赤潮
等の防止対策として開発検討中の魚類寄生虫および細菌
や生簀網付着生物等の除去(粘土散布による凝集沈殿)
及び魚類寄生虫および細菌や生簀網付着生物等毒性の不
活性化(解毒剤の開発)酸素補充(ビニ−ルシ−トの設
置及び酸素分散機の配置)等の対策に比較して安価に確
実に、早期に魚類寄生虫および細菌や生簀網付着生物等
を重点的に死滅させる効果を有する。
In the method for killing fish parasites and bacteria and removing the organisms attached to fish cage nets according to the fourth aspect of the present invention, fish parasites and bacteria and fish cages are collected from a concentrated area of fish parasites and bacteria and organisms attached to fish cage nets by ship. It moves with net-attached organisms and concentrates in the densest place to generate a high concentration of sodium hypochlorite, which can be instantly killed, and is a large capacity sodium hypochlorite concentration adjustment generator It is effective to prevent damage to fishes by equipping them with fish parasites, bacteria, and organisms attached to fish cage nets. Removal of other fish parasites, bacteria, fish cage net-attached organisms, red tides, and other fish parasites under development and investigation (aggregation by clay spraying)
In addition, it is cheaper and more reliable than countermeasures such as inactivation of toxicity of fish parasites, bacteria and organisms attached to cage nets (development of antidote), oxygen supplementation (installation of vinyl sheet and installation of oxygen disperser), etc. In addition, it has an effect of predominantly killing fish parasites, bacteria and organisms attached to the cage net at an early stage.

【0039】本発明請求項5記載の魚類寄生虫および細
菌の死滅と生簀網付着生物の除去方法では、前記方法を
採用したため、水槽や浮上生簀、浮上ブイ、タンク等等
で次亜塩素酸ソーダを発生させるのに加えて直流電流に
より天然海水を電気分解させて銅イオンを発生させるた
め、天然海水の含有元素である塩素および銅イオンを高
濃度にして殺菌効果を約2倍とすることができる。ま
た、発生イオン濃度も少くてよいため、消費電力も減少
させることができる。塩素の残留濃度は、銅イオンとの
化合により塩化銅として長期に亘って持続すると共に、
銅イオンと塩素との殺菌能力の相乗効果が得られる。ま
た、銅イオンと次亜塩素酸ソーダの発生と、この発生作
業を継続して天然海水中の銅イオンおよび残留塩素を濃
度調整することによって、魚類寄生虫および細菌と生簀
網付着生物を完全に死滅させるという大きな相乗効果が
得られる。生簀網を金属にして銅イオン発生用の電極と
して使用すると、通電によって生簀網に付着した卵塊、
幼生を死滅させ、ガス発生による剥離効果が相乗され
る。従って、天然海水中、浮上生簀内外、浮上ブイ、船
舶タンク等に海水の電気分解によって次亜塩素酸ソーダ
を発生させる方法に加えて銅イオンの発生を行うことに
よって、漁業者の種々の不安の解消と共にコスト低減、
魚類の成長に大きく寄与することができる。
In the method for killing fish parasites and bacteria according to claim 5 of the present invention and for removing organisms attached to fish cage nets, the method described above is used. Therefore, sodium hypochlorite is used in an aquarium, floating cage, floating buoy, tank or the like. In addition to generating water, electrolysis of natural seawater by direct current to generate copper ions. Therefore, chlorine and copper ions, which are elements contained in natural seawater, can be made to have high concentrations to double the bactericidal effect. it can. Further, since the generated ion concentration may be low, the power consumption can be reduced. The residual concentration of chlorine will continue as copper chloride for a long time due to its combination with copper ions,
A synergistic effect of the sterilizing ability of copper ions and chlorine is obtained. In addition, generation of copper ions and sodium hypochlorite, and by continuing this generation work to adjust the concentration of copper ions and residual chlorine in natural seawater, fish parasites and bacteria, and fish cage net attachment organisms were completely eliminated. A great synergistic effect of dying can be obtained. When the metal net is used as an electrode for generating copper ions, the egg mass attached to the fish net by energization,
The larvae are killed, and the exfoliation effect by gas generation is synergized. Therefore, in addition to the method of generating sodium hypochlorite by electrolysis of seawater in natural seawater, inside and outside floating cages, floating buoys, ship tanks, etc. Cost reduction with elimination
It can greatly contribute to the growth of fish.

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

【図1】本発明請求項1記載の方法に使用する装置を示
す説明図である。
FIG. 1 is an explanatory view showing an apparatus used for a method according to claim 1 of the present invention.

【図2】本発明請求項2記載の方法に使用する装置を示
す説明図である。
FIG. 2 is an explanatory view showing an apparatus used for the method according to claim 2 of the present invention.

【図3】本発明請求項2記載の方法に使用する装置を示
す説明図である。
FIG. 3 is an explanatory view showing an apparatus used for the method according to claim 2 of the present invention.

【図4】本発明請求項3記載の方法に使用する装置を示
す説明図である。
FIG. 4 is an explanatory view showing an apparatus used for the method according to claim 3 of the present invention.

【図5】本発明請求項4記載の方法に使用する装置を示
す説明図である。
FIG. 5 is an explanatory view showing an apparatus used for the method according to claim 4 of the present invention.

【図6】本発明請求項5記載の方法に使用する装置を示
す説明図である。
FIG. 6 is an explanatory view showing an apparatus used for the method according to claim 5 of the present invention.

【符号の説明】[Explanation of symbols]

2 蓄養水槽 3 魚類 4 魚類寄生虫および細菌や生簀網付着生物等 5 次亜塩素酸ソーダ濃度調整発生装置 5a チタン陽極 5b チタン陰極 5c 銅電極 5d 鉄電極 10a 浮上生簀 10b 浮上生簀 10c 浮上生簀 15 浮上ブイ 16 バッテリー 19 船舶 20 タンク 21 排水管 22 銅イオン濃度調整発生装置 2 Fermented water tank 3 Fish 4 Fish parasite and bacteria, fish cage net attachment organisms 5 Sodium hypochlorite concentration adjusting generator 5a Titanium anode 5b Titanium cathode 5c Copper electrode 5d Iron electrode 10a Floating cage 10b Floating cage 10c Floating cage Buoy 16 Battery 19 Ship 20 Tank 21 Drain pipe 22 Copper ion concentration adjustment generator

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.5 識別記号 庁内整理番号 FI 技術表示箇所 C02F 1/46 A 9344−4D 1/50 101 ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 5 Identification code Internal reference number FI technical display location C02F 1/46 A 9344-4D 1/50 101

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 陽極および陰極で形成された電極を魚類
の棲息域内における天然海水中に設け、該電極に直流電
流を通電して次亜塩素酸ソーダを発生させ、前記天然海
水中の残留塩素濃度を調整することにより、魚類を弊死
させる魚類寄生虫および細菌と生簀網付着生物を死滅除
去することを特徴とする魚類寄生虫および細菌の死滅と
生簀網付着生物の除去方法。
1. An electrode formed of an anode and a cathode is provided in natural seawater in the habitat of fish, and a direct current is applied to the electrode to generate sodium hypochlorite, whereby residual chlorine in the natural seawater is generated. A method for eradicating fish parasites and bacteria and removing organisms attached to fish cages, which comprises killing and removing fish parasites and bacteria that cause fishes to die, and organisms attaching fish cage nets by adjusting the concentration.
【請求項2】 天然海水中の浮上生簀内外に陽極および
陰極で形成された電極を設けて該電極に直流電流を通電
して次亜塩素酸ソーダを発生させ生簀内の残留塩素濃度
を調整することにより、生簀に収容する魚類を弊死させ
る魚類寄生虫および細菌と生簀網付着生物を死滅除去す
ることを特徴とする魚類寄生虫および細菌の死滅と生簀
網付着生物の除去方法。
2. An electrode formed of an anode and a cathode is provided inside and outside the floating cage in natural seawater, and a direct current is applied to the electrode to generate sodium hypochlorite to adjust the residual chlorine concentration in the cage. A method for killing fish parasites and bacteria and removing organisms attached to fish cages, which comprises killing and removing fish parasites and bacteria and organisms that adhere to fish cage nets, thereby killing fish contained in cages.
【請求項3】 浮上ブイに陽極および陰極で形成された
電極を設け該電極に直流電流を通電して次亜塩素酸ソー
ダを発生させ海水中の残留塩素濃度を調整することによ
り魚類寄生虫および細菌と生簀網付着生物を集中的に死
滅除去することを特徴とする魚類寄生虫および細菌の死
滅と生簀網付着生物の除去方法。
3. A floating buoy is provided with electrodes formed of an anode and a cathode, a direct current is passed through the electrodes to generate sodium hypochlorite, and the residual chlorine concentration in seawater is adjusted to control fish parasites and A method for killing fish parasites and bacteria and removing organisms attached to fish nets, which is characterized by intensively removing bacteria and organisms attached to fish nets.
【請求項4】 船舶に設けた天然海水を直接生簀内へ吸
入排出できるタンク内で陽極および陰極で形成された電
極に直流電流を通電してタンク内の次亜塩素酸ソーダを
発生させタンク内の残留塩素濃度を調整し、該タンク内
部水を生簀内水域に還流させることにより魚類寄生虫お
よび細菌と生簀網付着生物を死滅除去することを特徴と
する魚類寄生虫および細菌の死滅と生簀網付着生物の除
去方法。
4. In a tank, which is installed in a ship and can directly inhale and discharge natural seawater into the cage, a direct current is applied to an electrode formed by an anode and a cathode to generate sodium hypochlorite in the tank Killing and removing fish parasites and bacteria and organisms attached to fish cage nets by adjusting the residual chlorine concentration in the tank and returning the water inside the tank to the water inside the fish cages. Method of removing attached organisms.
【請求項5】 請求項1,2,3または4記載の魚類寄
生虫および細菌の死滅と生簀網付着生物の除去方法にお
いて、 前記残留塩素濃度調整用の電極に加えて銅イオン発生用
の陽極および陰極で形成された電極を設け、該電極に直
流電流を通電して海水中に銅イオンを発生させることに
より、魚類寄生虫および細菌と生簀網付着生物を死滅除
去することを特徴とする魚類寄生虫および細菌の死滅と
生簀網付着生物の除去方法。
5. The method for killing fish parasites and bacteria and removing organisms attached to fish cage nets according to claim 1, 2, 3 or 4, in addition to the electrode for adjusting the residual chlorine concentration, an anode for generating copper ions. And an electrode formed of a cathode, by applying a direct current to the electrode to generate copper ions in seawater, the fish characterized by killing and removing fish parasites and bacteria and organisms attached to the cage net Method of killing parasites and bacteria and removing organisms attached to cage nets.
JP4280721A 1992-09-25 1992-09-25 Method for diminishing parasite of fishes and bacterium and removing living thing attached to crawl net Pending JPH06153744A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4280721A JPH06153744A (en) 1992-09-25 1992-09-25 Method for diminishing parasite of fishes and bacterium and removing living thing attached to crawl net

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4280721A JPH06153744A (en) 1992-09-25 1992-09-25 Method for diminishing parasite of fishes and bacterium and removing living thing attached to crawl net

Publications (1)

Publication Number Publication Date
JPH06153744A true JPH06153744A (en) 1994-06-03

Family

ID=17629023

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4280721A Pending JPH06153744A (en) 1992-09-25 1992-09-25 Method for diminishing parasite of fishes and bacterium and removing living thing attached to crawl net

Country Status (1)

Country Link
JP (1) JPH06153744A (en)

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JPH06198285A (en) * 1992-12-28 1994-07-19 Takenaka Komuten Co Ltd Moving tape sea area cleaning device
JPH0833441A (en) * 1994-07-25 1996-02-06 Nippon Boshoku Kogyo Kk Method for improving hatching rate of fertilized egg of fishes and shellfishes
WO1997044280A1 (en) * 1996-05-21 1997-11-27 Toyo Tanso Co., Ltd. Floating electrode for electrolysis, electrolytic apparatus and plant growing method
JPH09308886A (en) * 1996-05-20 1997-12-02 Riyouyou Sangyo Kk Method for sterlizing seawater
JP2001198572A (en) * 2000-01-18 2001-07-24 Pentel Corp Electrochemically antifouling method and device
JP2001299189A (en) * 2000-04-27 2001-10-30 Tsuchiya Rubber Kk Body for preventing organism from attachment
WO2001089997A3 (en) * 2000-05-11 2002-05-02 Megaton Systems As Means for electrochemical treatment of water
JP2002136972A (en) * 2000-10-31 2002-05-14 Pentel Corp Electrochemical antistaining method and apparatus
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JP2003304796A (en) * 2002-02-14 2003-10-28 Chugoku Electric Power Co Inc:The Method of preventing barnacles from sticking
JP2004230244A (en) * 2003-01-29 2004-08-19 Mizu Kankyo Kagaku Kenkyusho:Kk System for improving submarine bottom sediment by applying crystallization process to use electrolytic electrode
JP2004275028A (en) * 2003-03-13 2004-10-07 Kansai Electric Power Co Inc:The Method for removing or inhibiting proliferation of polyp
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JP2006306834A (en) * 2005-03-29 2006-11-09 Nippon Suisan Kaisha Ltd Method for preventing and treating parasitic disease of marine fishes
US7442306B2 (en) * 2003-09-30 2008-10-28 Laurent Olivier Autotrofic sulfur denitration chamber and calcium reactor
KR200445602Y1 (en) * 2007-10-23 2009-08-19 한국남동발전 주식회사 Hypochlorite Diffuser of The Sea Water Electrolyzing System
JP2009213375A (en) * 2008-03-07 2009-09-24 Chugoku Electric Power Co Inc:The Bioassay apparatus
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JP2014169609A (en) * 2013-03-05 2014-09-18 Osaka Gas Co Ltd Marine organism sticking prevention device for seawater utilization facility and seawater utilization facility
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WO2018090157A1 (en) * 2016-11-17 2018-05-24 Alvarez Gatica Raul Hernan System for the elimination of parasites adhered to fish, by directly applying electricity to the fish, removing the parasites without harming the fish
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JPH01168224A (en) * 1987-12-24 1989-07-03 Mitsubishi Heavy Ind Ltd Electrically conductive rope used under sea water and stain-proof fishing net used under sea water
JPH02145140A (en) * 1988-11-29 1990-06-04 Mitsubishi Heavy Ind Ltd Submarine immersion netlike structure

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JPH01168224A (en) * 1987-12-24 1989-07-03 Mitsubishi Heavy Ind Ltd Electrically conductive rope used under sea water and stain-proof fishing net used under sea water
JPH02145140A (en) * 1988-11-29 1990-06-04 Mitsubishi Heavy Ind Ltd Submarine immersion netlike structure

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Publication number Priority date Publication date Assignee Title
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JPH09308886A (en) * 1996-05-20 1997-12-02 Riyouyou Sangyo Kk Method for sterlizing seawater
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JP2004230244A (en) * 2003-01-29 2004-08-19 Mizu Kankyo Kagaku Kenkyusho:Kk System for improving submarine bottom sediment by applying crystallization process to use electrolytic electrode
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