JP4976006B2 - Parasitic disease prevention and treatment method for marine fish - Google Patents
Parasitic disease prevention and treatment method for marine fish Download PDFInfo
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Description
本発明は、海産魚類に発生する寄生虫症の予防及び治療方法に関する。 The present invention relates to a method for preventing and treating parasitic diseases occurring in marine fish.
魚類に発生する寄生虫症は成長阻害の原因となり、死に至ることもある。養殖業においては、養殖魚の寄生虫症による損害は深刻な問題であり、種々の対応方法が検討されている。対応方法は大きくわけて、寄生虫症に有効な成分を飼料に添加して経口投与する方法と、有効成分を溶解させた水に魚類を浸漬させる方法がある。後者の例としては、ホルマリン浴、高塩分水浴、淡水浴、薬浴等が知られている(特許文献1〜5参照)。
淡水浴は寄生虫を駆除することができるが、魚類にとっても負担であり、例えば、ブリ類の場合、5分以上淡水浴すると鰓から出血し、斃死する場合があるため、淡水浴の時間は通常5〜10分程度に限られている。
Parasitic diseases that occur in fish cause growth inhibition and can lead to death. In the aquaculture industry, damage caused by parasitic diseases in cultured fish is a serious problem, and various countermeasures are being investigated. Corresponding methods are roughly divided into a method in which an ingredient effective for parasitic diseases is added to the feed and orally administered, and a method in which fish is immersed in water in which the active ingredient is dissolved. Examples of the latter include formalin baths, high salt water baths, fresh water baths, medicinal baths and the like (see Patent Documents 1 to 5).
A fresh water bath can control parasites, but it is also a burden for fish. For example, in the case of yellowtails, if a fresh water bath is used for more than 5 minutes, the fish may bleed and drown. Usually limited to about 5 to 10 minutes.
本発明は、魚類に薬効成分が残留するような心配がなく、環境水を汚染することもなく、しかも魚類に及ぼす影響も少ない寄生虫症の予防・治療方法を提供することを課題とする。 It is an object of the present invention to provide a method for preventing and treating parasitic diseases that does not cause concern that a medicinal component remains in fish, does not contaminate environmental water, and has little influence on fish.
海産魚類の寄生虫駆除のために淡水浴が行われている。淡水浴の作用機序としては浸透圧の違いによるものであろうと考えられてきたが、今回、発明者らは、淡水浴の効果が浸透圧の差によるものではなく、寄生虫にとって必須成分である特定の金属の欠如によるものであることを見出し、本発明を完成させた。すなわち、淡水を使用しなくても、海水に含まれる金属イオンのうち特定のイオンを除去することにより、寄生虫に対して淡水と同程度の効果を示すことが確認された。 Freshwater baths are used to control marine fish parasites. Although it has been thought that the mechanism of action of a fresh water bath may be due to a difference in osmotic pressure, the present inventors have now confirmed that the effect of a fresh water bath is not due to a difference in osmotic pressure, but an essential component for parasites. The inventors have found that this is due to the absence of certain metals and have completed the present invention. That is, even if it did not use fresh water, it was confirmed by removing a specific ion among the metal ions contained in seawater that it has the same effect on the parasite as fresh water.
本発明は、寄生虫の生存に必須の金属イオンであるカリウムイオン、カルシウムイオンのいずれか1種以上を除去、あるいは、カリウムイオン、カルシウムイオン、マグネシウムイオンのいずれか2種以上を1/2以上除去した海水又は人工海水で水浴させることを特徴とする海産魚類の寄生虫症予防及び/又は治療方法を要旨とする。海水から金属イオンを除去する方法は、当該金属イオンを含まない人工海水を製造するか、金属イオンをキレート剤によりキレートさせるか、又は金属イオンを不溶化する物質を添加して金属塩として沈殿させるなどの方法により行うことができる。海水又は人工海水から除去する、寄生虫の生存に必須の金属イオンとしては、カルシウムイオン及びマグネシウムイオンの2種の金属イオンを除去するのが好ましい。また、金属イオンの除去により変動する浸透圧を元の海水と同程度に戻るよう補正するのが好ましい。
The present invention removes at least one of potassium ions and calcium ions, which are metal ions essential for the survival of the parasite , or halves at least two of potassium ions, calcium ions, and magnesium ions. The gist is a method for preventing and / or treating parasitic diseases of marine fish characterized by bathing in the removed seawater or artificial seawater. The method for removing metal ions from seawater is to produce artificial seawater that does not contain the metal ions, chelate the metal ions with a chelating agent, or add a substance that insolubilizes the metal ions to precipitate it as a metal salt, etc. The method can be used. As metal ions essential for the survival of parasites to be removed from seawater or artificial seawater, it is preferable to remove two kinds of metal ions, calcium ions and magnesium ions. Moreover, it is preferable to correct the osmotic pressure, which fluctuates due to the removal of metal ions, so as to return to the same level as the original seawater.
従来の淡水浴と比べ魚に及ぼす影響が少なく、且つ、寄生虫症予防・治療効果において淡水浴と同等な効果が得られる。特殊な薬剤等を使用しないため、魚肉への薬剤の蓄積や環境への影響等の恐れがない。 Compared to conventional fresh water baths, it has less effect on fish and can provide the same effect as fresh water baths in preventing and treating parasitic diseases. Since no special chemicals are used, there is no fear of chemical accumulation in fish meat or environmental impact.
本発明は、寄生虫対策のため行われている淡水浴の代わりに特定の金属イオンを除去した海水または人工海水を使用して水浴を行うものである。既知の淡水浴のやり方、設備をそのまま使用することができる。淡水浴に比べて魚に対する負担が少ないので、従来の淡水浴よりも長い時間水浴させることが可能である。
本発明の対象となる海産魚類は、フグ科(トラフグ)、タイ科(マダイ、クロダイ)、アジ科(ブリ、ヒラマサ、カンパチ、ヒレナガカンパチ)、ハタ科(クエ、チャイロマルハタ、サラサハタ、マハタ)、サケ科(ギンザケ、アトランティックサーモン、トラウト、キングサーモン)、カレイ類(ヒラメ、ホシガレイ)など、広範な種類の魚類である。体表や鰓に寄生虫が寄生する魚類であれば本発明の対象とすることができる。また、稚魚から成魚にわたって対象とすることができる。
In the present invention, water bathing is performed using seawater or artificial seawater from which specific metal ions have been removed, instead of a freshwater bath used to combat parasitic diseases. Known fresh water bath methods and equipment can be used as they are. Compared to fresh water baths, the burden on fish is less, so it is possible to bathe for a longer time than conventional fresh water baths.
The marine fishes that are the subject of the present invention are the pufferfish family (Traphugu), the Thai family (Madai, Kurodai), the horse mackerel family (Buri, Hiramasa, Kampachi, Hiragakanpachi), the grouper family (Que, Chiromarata, Sarasahata, Mahata), salmon There are a wide variety of fishes such as coho salmon (coho salmon, atlantic salmon, trout, king salmon) and flounder (flounder, hoshigurai). Any fish that has parasites on its body surface or shark can be the subject of the present invention. Moreover, it can be targeted from fry to adult fish.
本発明の対象となる魚類寄生虫は、体表や鰓に寄生する寄生虫である。特に、実施例で示されたネオベネデニア、ヘテロボツリウム等の単生虫に属する寄生虫、例えば、ヘテラキシネ(Heteraxine)、ビバギナ(Bivagina)、ヘテロボツリウム(Hererobothrium)、ベネデニア(Benedenia)、ネオベネデニア(Benedenia serilae ; Neobenedenia)、ギロダクチルス(Gyrodactylus)等、また、50%海水で飼育すると増殖しないことが知られている原虫に属する寄生虫、例えば、白点虫(Cryptocaryon sp , Ichthyophithirius sp)、トリコジナ(Trichodina sp)、スクーチカ(Scuticociliatida)、イクチオボド(Ichthyobodo sp)、シュードダクチロギルス(Pseudodactylogyrus)等が例示される。
本発明において、寄生虫の生存に必須の金属イオンとは、ナトリウムイオン(Na+)、カリウムイオン(K+)、カルシウムイオン(Ca2+)、マグネシウムイオン(Mg2+)が例示される。特にカルシウムイオン及びマグネシウムイオンの両方を除去することにより寄生虫の生存率を淡水浴と同程度に低下させることができ好ましい。
The fish parasite that is the subject of the present invention is a parasite that parasitizes on the body surface and the coral. In particular, parasites belonging to monoprotozoa such as neobenedenia and heterobotulium shown in the examples, for example, Heteraxine, Bivagina, Hererobothrium, Benedenia, Benedenia serilae; Neobenedenia), Gyrodactylus, etc., and parasites belonging to protozoa known not to proliferate when bred in 50% seawater, for example, Cryptocaryon sp, Ichthyophithirius sp, Trichodina sp ), Scuticociliatida, Ichthyobodo sp, Pseudodactylogyrus and the like.
In the present invention, examples of metal ions essential for the survival of parasites include sodium ions (Na + ), potassium ions (K + ), calcium ions (Ca 2+ ), and magnesium ions (Mg 2+ ). In particular, the removal of both calcium ions and magnesium ions is preferable because the survival rate of the parasite can be reduced to the same extent as in a fresh water bath.
本発明において、金属イオンを除去した海水又は人工海水とは、海水からイオン交換樹脂などにより特定の金属イオンを除いたもの、あるいは、金属イオンのキレート剤などにより金属イオンを沈殿させたものなどを用いることができる。また、必要な塩を配合して、特定の金属イオン以外の海水成分を配合した人工海水を使用することもできる。
本発明で用いることができるキレート剤としてはクエン酸のような食品添加物として使用できるものを直接投入してもよいし、EDTAのような金属塩封鎖能力の高いキレート剤を使用することもできる。EDTA等を使用する場合、EDTAが回収可能なように、ポリマーなどに結合させ使用し、投入して金属イオンをキレートした後、沈殿物としてEDTAを回収するのが好ましい。キレート剤の使用量(g/リットル)は、「金属塩(mg/リットル)/キレート剤1gで封鎖できる金属塩量(mg)」により計算して用いる。
本発明では、金属塩と反応し、金属塩を沈殿物とする物質を投入することにより金属イオンを除去することもできる。例えば、炭酸ナトリウムを海水に投入することで、カルシウム塩は炭酸カルシウム沈殿となるため不溶化される。カルシウム、マグネシウムは炭酸塩、燐酸塩などにすることにより不溶性の塩となる。
In the present invention, seawater or artificial seawater from which metal ions have been removed is obtained by removing specific metal ions from seawater with an ion exchange resin or the like, or by precipitating metal ions with a metal ion chelating agent, etc. Can be used. Artificial seawater in which necessary salt is blended and seawater components other than specific metal ions are blended can also be used.
As a chelating agent that can be used in the present invention, a chelating agent that can be used as a food additive such as citric acid may be directly added, or a chelating agent having a high metal salt blocking ability such as EDTA may be used. . When EDTA or the like is used, it is preferable that the EDTA is recovered as a precipitate after being used by being bound to a polymer or the like so that EDTA can be recovered. The amount of the chelating agent used (g / liter) is calculated based on “metal salt (mg / liter) / amount of metal salt sequestered with 1 g of chelating agent (mg)”.
In the present invention, metal ions can also be removed by introducing a substance that reacts with a metal salt and makes the metal salt a precipitate. For example, by adding sodium carbonate to seawater, the calcium salt becomes calcium carbonate precipitate and is insolubilized. Calcium and magnesium become insoluble salts by making carbonates, phosphates, and the like.
人工海水の成分組成は種々知られているが、主成分は塩化ナトリウム、塩化カリウム、塩化カルシウム、塩化マグネシウム、硫酸マグネシウム、pH緩衝剤であり、それに、その他の微量成分が追加される。本発明の効果を得るためには、寄生虫に必須の金属イオンが除去されていれば良いので、いずれの成分組成の人工海水であっても適用することができる。特定の金属イオンを除去した場合、浸透圧、pHは元の人工海水に近い方が魚にとっての負担が少ないので、塩化ナトリウムなどの塩類を用いて調節するのが好ましい。
本発明において水浴させるとは、通常の飼育水から本発明の金属イオンを除いた海水に一定時間魚を移すことである。通常、魚を網ですくって水浴槽に入れ、一定時間経過後、元の飼育水に戻すということを行う。淡水浴で使用されている方法であれば、いずれの方法でも良い。
本発明の水浴液は淡水よりも魚にとって負荷の少ないものであるから、従来淡水浴が行われている魚種について、淡水浴に採用されている条件と同等の条件(水浴時間等)で水浴を実施すればよい。さらに淡水浴よりも水浴時間を長くすることもできる。
Although the component composition of artificial seawater is variously known, the main components are sodium chloride, potassium chloride, calcium chloride, magnesium chloride, magnesium sulfate, and a pH buffer, and other trace components are added thereto. In order to obtain the effects of the present invention, it is only necessary to remove metal ions essential to the parasite, and therefore any artificial seawater having any component composition can be applied. When a specific metal ion is removed, the osmotic pressure and pH are preferably adjusted using salts such as sodium chloride because the burden on fish is less when it is closer to the original artificial seawater.
In the present invention, to bathe is to transfer the fish for a certain period of time to normal seawater in which the metal ions of the present invention are removed. Usually, fish are put in a net with a net and returned to the original breeding water after a certain period of time. Any method may be used as long as it is a method used in a fresh water bath.
Since the water bath liquid of the present invention has less burden on fish than fresh water, the fish species that have been used in the conventional fresh water bath are bathed under the same conditions (water bath time, etc.) as those used in the fresh water bath. Should be implemented. Further, the water bath time can be made longer than that of the fresh water bath.
本発明の特定の金属イオンを除去した海水で魚類を水浴すると、実施例で示したように寄生虫の成虫を駆除することができるだけでなく、寄生虫の卵の孵化率も低下させることができる。これらの両効果により魚類の寄生虫症の予防及び/又は治療することができる。
本発明の寄生虫の生存に必須の金属イオンを除去した人工海水の素とは、人工海水の素として販売されている塩類の混合物から特定の金属イオンを除いたものである。マグネシウムイオンとカルシウムイオンを除いたものが好ましい。塩化ナトリウム等の塩類を用いて浸透圧、pH等を通常の人工海水と同程度に調節したものが好ましい。この人工海水の素を適切な濃度になるよう一定量の水に溶解し、魚類を水浴させることにより寄生虫症を予防及び/又は治療することができる。
By bathing fish in seawater from which specific metal ions of the present invention have been removed, it is possible not only to combat adult parasites as shown in the Examples, but also to reduce the hatching rate of parasite eggs. . Both these effects can prevent and / or treat fish parasitic diseases.
The element of artificial seawater from which metal ions essential for the survival of the parasites of the present invention are removed is a mixture of salts sold as elements of artificial seawater, excluding specific metal ions. What remove | excluded magnesium ion and calcium ion is preferable. What adjusted osmotic pressure, pH, etc. to the same extent as normal artificial seawater using salts, such as sodium chloride, is preferred. Parasitic diseases can be prevented and / or treated by dissolving the artificial seawater in a certain amount of water to an appropriate concentration and bathing the fish.
以下に本発明の実施例を記載するが、本発明はこれらに何ら限定されるものではない。 Examples of the present invention will be described below, but the present invention is not limited thereto.
<Na+、K+、Ca2+および Mg2+を単独で除去した人工海水の抗ネオベネデニア活性(in vitro 試験)>
Na+、K+、Ca2+および Mg2+を単独で除去した人工海水を作製し、これら海水のネオベネデニア( Neobenedenia girellae 、ハダ虫)成虫に対する致死効果を調べた。
<Anti-Neo Benedenia Activity of Artificial Seawater from which Na + , K + , Ca 2+ and Mg 2+ have been removed alone (in vitro test)>
Artificial seawater from which Na + , K + , Ca 2+, and Mg 2+ were removed alone was prepared, and the lethal effect of these seawaters on neobenedenia (Neobenedenia girellae) was examined.
材料と方法
試験区:人工海水区(対照区)、Na+除去人工海水区、K+除去人工海水区、Ca2+除去人工海水区、Mg2+除去人工海水区、蒸留水区(淡水区)の6区とした。
人工海水:対照区の人工海水の組成は塩化ナトリウム0.4638M、塩化カリウム0.01M、塩化カルシウム・2水和物0.0092M、塩化マグネシウム・6水和物0.0359M、硫酸マグネシウム・7水和物0.0175M、Hepes 0.01M(pH8.0)とした。 これをベースとしてNa+、K+、Ca2+およびMg2+除去人工海水を調整した。また、Na+除去人工海水の浸透圧調節剤としてマンニトール(糖)を、K+、Ca2+および Mg2+除去人工海水の浸透圧調節剤として塩化ナトリウムを用い、それらを加えることで浸透圧の不足分を補った。
ネオベネデニアへの人工海水の曝露:孵化後12〜15日のネオベネデニア成虫を、人工海水を含む12穴ディッシュにそれぞれ20個体ずつ入れた。各穴を人工海水で2回洗浄した後、通常人工海水、蒸留水、それぞれの金属イオンを単独で除去した人工海水を添加し、25℃で2時間培養した。培養開始5、10、15、20、25、30、60 および 120 分後に本虫の生存率を調べた。
Materials and methods Test zone: Artificial seawater zone (control zone), Na + removal artificial seawater zone, K + removal artificial seawater zone, Ca2 + removal artificial seawater zone, Mg2 + removal artificial seawater zone, distilled water zone ( It was set as 6 districts of freshwater district).
Artificial seawater: The composition of artificial seawater in the control zone is 0.4638M sodium chloride, 0.01M potassium chloride, 0.0092M calcium chloride dihydrate, 0.0359M magnesium chloride hexahydrate, 0.0175M magnesium sulfate heptahydrate Hepes 0.01M (pH 8.0). Na + , K + , Ca 2+ and Mg 2+ removed artificial seawater was prepared based on this. Also, mannitol (sugar) is used as an osmotic pressure regulator for Na + -removed artificial seawater, and sodium chloride is used as an osmotic pressure regulator for K + , Ca 2+ and Mg 2+ -removed artificial seawater. Supplemented the minute.
Exposure of artificial seawater to Neo Benedenia: Twenty individual adults of Neo Benedenia 12-15 days after hatching were placed in a 12-well dish containing artificial sea water. After each hole was washed twice with artificial seawater, artificial seawater, distilled water, and artificial seawater from which each metal ion was removed independently were added and cultured at 25 ° C. for 2 hours. The viability of the worms was examined 5, 10, 15, 20, 25, 30, 60 and 120 minutes after the start of culture.
結果と考察
結果を図1に示した。人工海水区(対照区)の生存率は100%であった。蒸留水区は培養開始5分後に全ての本虫が死亡した。従って、養殖現場で実施されている淡水浴の有効性が示された。一方、金属イオン除去人工海水区では、Na+除去人工海水区、Ca2+除去人工海水区、K+除去人工海水区で明らかな生存率の低下が認められた。その中でもNa+除去人工海水区の生存率が最も低く、その生存率は60分後で6.7%、120分後では4.2%であった。Ca2+除去人工海水区およびK+除去人工海水区の生存率は120分後で50%程度であった。従って、これら金属イオンは本虫の恒常性を保つために必須であり、Na+、K+およびCa2+いずれかを除去した海水、または含まない人工海水は、魚類寄生虫に対し駆虫効果を有することが明らかとなった。
The results and discussion results are shown in FIG. The survival rate of the artificial seawater area (control area) was 100%. In the distilled water section, all the worms died 5 minutes after the start of the culture. Therefore, the effectiveness of the fresh water bath carried out at the aquaculture site was shown. On the other hand, in the metal ion-removed artificial seawater area, a clear decrease in the survival rate was observed in the Na + removed artificial seawater area, the Ca 2+ removed artificial seawater area, and the K + removed artificial seawater area. Among them, the survival rate of the Na + -removed artificial seawater zone was the lowest, and the survival rate was 6.7% after 60 minutes and 4.2% after 120 minutes. The survival rate of the Ca 2+ removed artificial seawater zone and the K + removed artificial seawater zone was about 50% after 120 minutes. Therefore, these metal ions are essential for maintaining the homeostasis of the worms, and seawater from which any of Na + , K + and Ca 2+ is removed or artificial seawater which does not contain has an anthelmintic effect on fish parasites. It became clear.
<Ca2+および Mg2+を単独または複合的に除去した人工海水の抗ネオベネデニア活性(in vitro 試験)>
Ca2+および Mg2+を単独または複合的に除去した海水を作製し、これら海水のネオベネデニア( Neobenedenia girellae 、ハダ虫)成虫に対する致死効果を調べた。
<Anti-Neo-Benedenia activity of artificial seawater from which Ca 2+ and Mg 2+ are removed alone or in combination (in vitro test)>
Seawater from which Ca 2+ and Mg 2+ were removed alone or in combination was prepared, and the lethal effect of these seawaters against adult neobenedenia girellae was examined.
材料と方法
試験区:人工海水区(対照区)、Ca2+除去人工海水区、Mg2+除去人工海水区、Ca2+及びMg2+を人工海水の1/2量としたCa2+,Mg2+1/2除去海水区、Ca2+及びMg2+を人工海水の1/4量としたCa2+,Mg2+3/4除去海水区、Ca2+及びMg2+を含まないCa2+,Mg2+除去海水区、蒸留水区(淡水区)の7区とした。
人工海水:対照区の人工海水の組成は、塩化ナトリウム0.4638M、塩化カリウム0.01M、塩化カルシウム・2水和物0.0092M、塩化マグネシウム・6水和物0.0359M、硫酸マグネシウム・7水和物0.0175M、Hepes 0.01M(pH8.0)とした。これをベースとしてCa2+及びMg2+除去人工海水を調整した。また、Ca2+及びMg2+除去人工海水の浸透圧調節剤として塩化ナトリウムを用い、それを加えることで浸透圧の不足分を補った。
ネオベネデニアへの人工海水の曝露:孵化後12〜15日のネオベネデニア成虫を、人工海水を含む12穴ディッシュにそれぞれ20匹ずつ入れた。各穴を人工海水で2回洗浄した後、通常人工海水、蒸留水、それぞれのイオン除去人工海水を添加し、25℃で2時間培養した。培養開始5、10、15、20、25、30、60 および 120 分後に本虫の生存率を調べた。また、各人工海水が虫体にどのような影響を及ぼしているのかを組織学的に検討するために、それぞれの海水で飼育した本虫を採取し、透過型電子顕微鏡を用いて観察した。
Materials and Methods <br/> test group: artificial seawater District (control group), Ca 2+ removed artificial seawater ku, Mg 2+ removed artificial seawater ku, Ca 2+ and Mg 2+ Ca 2+ was 1/2 the amount of artificial sea water, mg 2+ 1/2 removing seawater ku, Ca 2+ and 1/4 amount of mg 2+ artificial seawater and were Ca 2+, mg 2+ 3/4 removing seawater ku, Ca 2+ and mg 2+ does not contain Ca 2+, mg 2+ removed Seven zones, a seawater zone and a distilled water zone (freshwater zone), were used.
Artificial seawater: The composition of artificial seawater in the control plot is: sodium chloride 0.4638M, potassium chloride 0.01M, calcium chloride dihydrate 0.0092M, magnesium chloride hexahydrate 0.0359M, magnesium sulfate heptahydrate 0.0175 M, Hepes 0.01M (pH 8.0). Ca 2+ and Mg 2+ removed artificial seawater was prepared based on this. Moreover, sodium chloride was used as the osmotic pressure regulator of the Ca 2+ and Mg 2+ removed artificial seawater, and the lack of osmotic pressure was compensated for by adding it.
Artificial seawater exposure to Neo Benedenia: 20 neobenedenia adults 12-15 days after hatching were each placed in a 12-well dish containing artificial seawater. After each hole was washed twice with artificial seawater, normal artificial seawater, distilled water, and respective ion-removed artificial seawater were added and cultured at 25 ° C. for 2 hours. The viability of the worms was examined 5, 10, 15, 20, 25, 30, 60 and 120 minutes after the start of culture. In addition, in order to examine histologically what kind of influence each artificial seawater has on the worm body, the main insects raised in each seawater were collected and observed using a transmission electron microscope.
結果と考察
本虫生存率の結果を図2に示した。人工海水区(対照区)の本虫生存率は100%であった。イオン除去人工海水試験区では、Mg2+除去海水区を除く全ての区で明らかな本虫生存率の低下が見られ、実施例1の結果が再現された。その中でもCa2+,Mg2+除去海水区の本虫生存率が最も低く、その生存率は5分後で24.2%、10分後では3.7%であった。本試験区において、培養開始20分で全ての本虫の死亡が観察された。Ca2+,Mg2+除去海水区の全ての寄生虫を死亡させるのに要する時間は蒸留水区と同等な値であり、Ca2+,Mg2+除去海水(人工海水)の本虫致死効果(駆虫効果)は淡水浴と同等であると考えられた。Ca2+,Mg2+1/2除去海水区、Ca2+,Mg2+3/4除去海水区は、同様に致死効果(駆虫効果)を示したが、その効果はCa2+,Mg2+除去海水区と比べ低く、その値はCa2+除去人工海水区と同等であった。以上の結果は、単独で金属イオンを除去したものよりも複合的に金属イオンを除去した方が本虫の生存率を低下させるのに有効であることを示している。
組織観察の結果を図3に示した。Ca2+除去人工海水およびCa2+,Mg2+除去海水に曝露し死亡した本虫の体後方の組織を調べたところ、細胞間に大きな間隙が多数形成されていた。一方、対照の人工海水暴露個体ではそのような間隙は観察されなかった。Ca2+とMg2+は細胞接着に関わっていることが知られている。細胞接着因子の一つであるカドヘリンはCa2+依存的であることが明らかにされている。これらのことから、Ca2+除去海水、Ca2+とMg2+複合除去海水は本虫の細胞間の結合力を弱め、本虫を死亡させると考えられた。
Results and Discussion FIG. 2 shows the results of the present worm survival rate. The survival rate of the worms in the artificial seawater area (control area) was 100%. In the ion-removed artificial seawater test section, a clear decrease in the worm survival rate was observed in all sections except for the Mg 2 + -removed seawater section, and the results of Example 1 were reproduced. Among them, the Ca 2+ and Mg 2+ removed seawater sections had the lowest survival rate of the worms, and the survival rate was 24.2% after 5 minutes and 3.7% after 10 minutes. In this test group, death of all worms was observed 20 minutes after the start of culture. The time required to kill all parasites in the Ca 2+ , Mg 2+ removed seawater section is the same value as that in the distilled water section, and the lethal effect of the insects in the Ca 2+ , Mg 2+ removed seawater (artificial seawater) ) Was considered equivalent to a fresh water bath. Ca 2+, Mg 2+ 1/2 removing seawater ku, Ca 2+, Mg 2+ 3/4 removing seawater Ward showed similarly lethal effect (antiparasitic effect), the effect is Ca 2+, and Mg 2+ removed seawater Zone The value was lower than that of the Ca 2 + -removed artificial seawater area. The above results indicate that the removal of metal ions in combination is more effective in reducing the survival rate of the worms than the removal of metal ions alone.
The results of tissue observation are shown in FIG. When the tissue behind the body of the dead worm was exposed to Ca 2+ -removed artificial seawater and Ca 2+ , Mg 2+ -removed seawater, many large gaps were formed between the cells. On the other hand, such a gap was not observed in the control artificial seawater-exposed individuals. Ca 2+ and Mg 2+ are known to be involved in cell adhesion. Cadherin, one of the cell adhesion factors, has been shown to be Ca 2+ dependent. From these, it was considered that Ca 2 + -removed seawater, Ca 2+ and Mg 2+ combined-removed seawater weaken the binding force between cells of the worms and cause the worms to die.
<Ca2+およびMg2+を単独または複合的に除去した人工海水の抗ネオベネデニア活性・in vivo 試験>
Ca2+およびMg2+を単独または複合的に除去した海水を作製し、これら海水の宿主に寄生しているネオベネデニア( Neobenedenia girellae 、ハダ虫)成虫に対する致死効果を調べた。
<Anti-Neo-Benedenia Activity / In Vivo Test of Artificial Seawater from which Ca 2+ and Mg 2+ are Removed Single or Combined>
Seawater from which Ca 2+ and Mg 2+ were removed singly or in combination was prepared, and the lethal effect on adult neobenedenia girellae (parasitoid) parasitic on the seawater host was examined.
材料と方法
試験区:天然海水区、人工海水区(対照区)、Ca2+除去人工海水区、Mg2+除去人工海水区、Ca2+及びMg2+を人工海水の1/2量としたCa2+,Mg2+1/2除去人工海水区、Ca2+及びMg2+を人工海水の1/4量としたCa2+,Mg2+3/4除去人工海水区、Ca2+及びMg2+を含まないCa2+,Mg2+除去人工海水区の7区とした。
人工海水:対照区の人工海水の組成は塩化ナトリウム0.4638M、塩化カリウム0.01M、塩化カルシウム・2水和物0.0092M、塩化マグネシウム・6水和物0.0359M、硫酸マグネシウム・7水和物0.0175M、Hepes 0.01M(pH8.0)とした。これをベースとしてCa2+及びMg2+除去人工海水を調整した。また、Ca2+及びMg2+除去人工海水の浸透圧調節剤として塩化ナトリウムを用い、それを加えることで浸透圧の不足分を補った。
宿主に寄生しているネオベネデニアへの海水の曝露:孵化後12〜15日のネオベネデニア成虫約200個体寄生しているホシガレイを、各試験海水4リットルを含む10リットル水槽へ移し、1時間飼育した。1時間後に本虫の生存有無を調べ、生残率を算出した。同試験を3回実施した。
Materials and methods Test zone: Natural seawater zone, artificial seawater zone (control zone), Ca2 + -removed artificial seawater zone, Mg2 + -removed artificial seawater zone, Ca2 + and Mg2 + as 1/2 amount of artificial seawater the Ca 2+, Mg 2+ 1/2 removing artificial seawater ku, Ca 2+ was 1/4 the amount of artificial seawater Ca 2+ and Mg 2+, Mg 2+ 3/4 removing artificial seawater ku, without Ca 2+ and Mg 2+ Seven sections of Ca 2+ and Mg 2+ removal artificial seawater sections were used.
Artificial seawater: The composition of artificial seawater in the control zone is 0.4638M sodium chloride, 0.01M potassium chloride, 0.0092M calcium chloride dihydrate, 0.0359M magnesium chloride hexahydrate, 0.0175M magnesium sulfate heptahydrate Hepes 0.01M (pH 8.0). Ca 2+ and Mg 2+ removed artificial seawater was prepared based on this. Moreover, sodium chloride was used as the osmotic pressure regulator of the Ca 2+ and Mg 2+ removed artificial seawater, and the lack of osmotic pressure was compensated for by adding it.
Exposure of seawater to neobenedenia parasitizing host: Hoshigarei infested with about 200 adult neobenedenia 12-12 days after hatching was transferred to a 10 liter aquarium containing 4 liters of each test seawater and bred for 1 hour. One hour later, the presence or absence of the worm was examined and the survival rate was calculated. The same test was conducted three times.
結果と考察
結果を図4に示した。Ca2+除去人工海水区およびCa2+,Mg2+除去人工海水区の本虫生存率はそれぞれ67.4%、14.7%であり、Ca2+除去人工海水区とCa2+,Mg2+除去人工海水区で明らかな駆虫効果が認められた。また、これら海水条件下において、ホシガレイに異常遊泳などの外観的な異常は観察されなかった。金属イオン除去海水の場合、淡水と比べ魚に及ぼす影響が少なく且つ淡水浴と同等な効果が得られるため、これら金属イオン除去海水(人工海水)は観賞用を含む海産魚の寄生虫駆除用薬浴剤として利用できることが示された。
The results and discussion results are shown in FIG. Ca 2+ removed artificial seawater Ward and Ca 2+, Mg 2+ removed artificial seawater District of the insect survival, respectively 67.4%, was 14.7% Ca 2+ removed artificial seawater Zone and Ca 2+, Mg 2+ removed artificial seawater A clear anthelmintic effect was observed in the ward. Also, under these seawater conditions, no abnormal appearance such as abnormal swimming was observed in the flounder. In the case of seawater from which metal ions have been removed, there is less influence on fish compared to freshwater, and the same effect as freshwater baths can be obtained. It was shown that it can be used as an agent.
<Na+、K+、Ca2+およびMg2+を単独で除去した人工海水のヘテロボツリウム卵に対する孵化阻止作用(in vitro 試験)>
Na+、K+、Ca2+およびMg2+を単独で除去した海水を作製し、これら海水のヘテロボツリウム(Heterobothrium okamotoi、エラ虫)卵に対する孵化阻止作用を調べた。
<Inhibition of hatching of artificial seawater from which Na + , K + , Ca 2+, and Mg 2+ have been removed alone against heterobotulium eggs (in vitro test)>
Seawater from which Na + , K + , Ca 2+, and Mg 2+ were removed alone was prepared, and the hatching-inhibiting action of these seawaters on heterobotlium (Heterobothrium okamotoi) was examined.
材料と方法
試験区:天然海水区、人工海水区(対照区)、Na+除去人工海水区、K+除去人工海水区、Ca2+除去人工海水区、Mg2+除去人工海水区の6区とした。
人工海水:対照区の人工海水の組成はVan’t Hoffのものとした。1リットル当たりの組成は、塩化ナトリウム26.75g、塩化カリウム0.75g、塩化カルシウム0.51g、塩化マグネシウム3.42g、硫酸マグネシウム2.1g、重炭酸0.21gであった。これをベースとしてNa+、K+、Ca2+およびMg2+イオン除去人工海水を調整した。
ヘテロボツリウム卵への人工海水の曝露:産卵されてから12時間以内の卵を回収し、各試験海水300mlを含むプラスチックビーカーへ移し、14日間、25℃で培養した。各区に供試した卵数は約500個であった。毎日、卵を顕微鏡で観察するとともに試験海水を交換した。培養開始14日後に、孵化率を算出した。
Materials and methods Test zone: Natural seawater zone, artificial seawater zone (control zone), Na + removal artificial seawater zone, K + removal artificial seawater zone, Ca2 + removal artificial seawater zone, Mg2 + removal artificial seawater zone It was set as 6 wards.
Artificial seawater: The composition of the artificial seawater in the control area was that of Van't Hoff. The composition per liter was 26.75 g sodium chloride, 0.75 g potassium chloride, 0.51 g calcium chloride, 3.42 g magnesium chloride, 2.1 g magnesium sulfate and 0.21 g bicarbonate. Na + , K + , Ca 2+ and Mg 2+ ion-removed artificial seawater was prepared based on this.
Artificial seawater exposure to heterobotulium eggs: Eggs within 12 hours of egg laying were collected, transferred to a plastic beaker containing 300 ml of each test seawater, and cultured at 25 ° C. for 14 days. The number of eggs used in each section was about 500. Every day, the eggs were observed under a microscope and the test seawater was changed. The hatching rate was calculated 14 days after the start of culture.
結果と考察
結果を図5に示した。人工海水区(対照区)の孵化率は93.0%であり、天然海水と同等な孵化率を示した。一方、金属イオン除去海水区の孵化率は、対照区と比べ全ての区で明らかに低い値となった。従って、金属イオン除去海水は魚類寄生虫に対する駆虫作用だけではなく、寄生虫卵の孵化を阻止する作用も有することが明らかとなった。
以上の結果から、金属イオン除去海水、特にCa2+及びMg2+複合除去海水は淡水浴と同等の駆虫効果を持ち、宿主に与える影響が小さいことから、水浴液として有効であると考えられる。特に、外界の影響を受けやすい仔稚魚に対する寄生虫対策に大きな効果を発揮する。また、これら海水は孵化阻止作用を有しており、長期間にわたり飼育するような、海産魚の陸上循環養殖時の寄生虫予防且つ治療用として飼育水に利用可能である。
Results and discussion results are shown in FIG. The hatching rate of the artificial seawater zone (control zone) was 93.0%, indicating a hatching rate equivalent to that of natural seawater. On the other hand, the hatching rate of the metal ion-removed seawater area was clearly lower in all areas than in the control area. Therefore, it has been clarified that the seawater from which metal ions have been removed has not only an anthelmintic action on fish parasites but also an action to inhibit hatching of parasite eggs.
From the above results, the seawater from which metal ions have been removed, particularly Ca2 + and Mg2 + combined seawater, has an anthelmintic effect equivalent to that of a freshwater bath and has a small effect on the host, and thus is considered to be effective as a bathing solution. In particular, it is very effective in combating parasites against juvenile fish that are susceptible to the outside world. In addition, these seawaters have a hatching-inhibiting action, and can be used for breeding water for the prevention and treatment of parasites during marine fish culturing on land, which are bred for a long time.
<Ca2+およびMg2+を単独または複合的に除去した人工海水のブリに及ぼす影響検討試験>
Ca2+およびMg2+を単独または複合的に除去した海水を作製し、これら海水のブリへの影響を調べた。
<Effect study on the effect of artificial seawater from which Ca 2+ and Mg 2+ have been removed either alone or in combination>
Seawater from which Ca 2+ and Mg 2+ were removed alone or in combination was prepared, and the influence of these seawaters on yellowtail was examined.
材料と方法
試験区:天然海水区、人工海水区(対照区)、Ca2+除去人工海水区、Mg2+除去人工海水区、Ca2+及びMg2+を人工海水の1/4量としたCa2+・Mg2+3/4除去人工海水区、Ca2+ 及びMg2+を含まないCa2+・Mg2+除去人工海水区、蒸留水区(淡水浴区)の 7 区とした。
人工海水:対照区の人工海水の組成は塩化ナトリウム 0.4638M、塩化カリウム 0.01M、塩化カルシウム・2水和物 0.0092M、塩化マグネシウム・6水和物 0.0359M、硫酸マグネシウム・7水和物 0.0175M、Hepes 0.01M (pH8.0) とした。これをベースとしてCa2+及びMg2+除去人工海水を調整した。また、Ca2+及びMg2+除去人工海水の浸透圧調整剤として塩化ナトリウムを用い、それを加えることで浸透圧の不足分を補った。
ブリへの各試験海水および淡水の曝露:ブリの幼魚3個体を各試験海水20リットルを含む100リットル水槽へ移し、1 時間飼育した。飼育時間中、ブリを観察し、1 時間後に生残率を算出した。また、各人工海水がブリにどのような影響を及ぼしているのかを組織学的に検討するために、それぞれの海水で飼育したブリの鰓を採取し、組織学的観察を行った。
Materials and methods Test zone: natural seawater zone, artificial seawater zone (control zone), Ca2 + -removed artificial seawater zone, Mg2 + -removed artificial seawater zone, Ca2 + and Mg2 + as 1/4 amount of artificial seawater the Ca 2+ · Mg 2+ 3/4 removing artificial seawater ku, Ca 2+ and Mg 2+ does not contain a Ca 2+ · Mg 2+ removed artificial seawater Ward, was 7 ° distilled water gu (freshwater bath Ward).
Artificial seawater: The composition of artificial seawater in the control zone is sodium chloride 0.4638M, potassium chloride 0.01M, calcium chloride dihydrate 0.0092M, magnesium chloride hexahydrate 0.0359M, magnesium sulfate heptahydrate 0.0175M Hepes 0.01M (pH 8.0). Ca 2+ and Mg 2+ removed artificial seawater was prepared based on this. Further, sodium chloride was used as an osmotic pressure adjusting agent for Ca 2+ and Mg 2+ removed artificial seawater, and the lack of osmotic pressure was compensated for by adding it.
Each test seawater and fresh water exposure to yellowtail: Three juveniles of yellowtail were transferred to a 100 liter water tank containing 20 liters of each test seawater and reared for 1 hour. The yellowtail was observed during the breeding time, and the survival rate was calculated after 1 hour. In addition, in order to examine histologically what effect each artificial seawater has on the yellowtail, we collected the coral of the yellowtail raised in each seawater and performed histological observations.
結果と考察
ブリ生残率の結果を図6に示した。人工海水区(対照区)のブリ生残率は100%であった。蒸留水区(淡水区)では、飼育開始後 7 〜10 分で全てのブリが鰓から出血し、死亡した。一方、金属イオン除去人工海水区では、1時間の処理において、全ての区で全供試魚が生存していた。ネオベネデニア(Neobenedenia girellae 、ハダムシ) 成虫に対する致死効果がもっとも高かったCa2+・Mg2+除去人工海水区においても異常遊泳などの外観的な異常は観察されなかった。このことから、長時間の淡水浴は宿主に大きなダメージを与えること、金属イオン除去人工海水浴は淡水浴に比べ宿主に与える影響がはるかに少ないことが判明した。
組織観察の結果を図7に示した。天然海水区では鰓組織に異常は観察されなかった。蒸留水区では二次鰓弁の上皮細胞、二次鰓弁間細胞や壁柱細胞の膨張が観察され、一部では二次鰓弁からこれら細胞の剥離も観察された。Ca2+・Mg2+除去人工海水区では一部の細胞の膨張が観察されたが、天然海水区と大きな差は認められなかった。
以上のことより、金属イオン除去海水は淡水に比べブリに与える影響は著しく小さく、寄生虫駆除用薬浴剤として利用できることが示された。
Results and discussion The results of the survival rate of yellowtail are shown in FIG. The survival rate of yellowtail in the artificial seawater area (control area) was 100%. In the distilled water section (freshwater section), all yellowtails bleed and died 7-10 minutes after the start of breeding. On the other hand, in the artificial seawater area from which metal ions were removed, all the test fish were alive in all sections in the treatment for 1 hour. Neobenedenia (Neobenedenia girellae, Hadamushi) appearance abnormalities such as even abnormal swimming in Ca 2+ · Mg 2+ removed artificial seawater ku lethal effect was highest for adult was observed. From this, it was found that a long-time fresh water bath causes great damage to the host, and an artificial sea water bath with metal ion removal has much less influence on the host than the fresh water bath.
The results of tissue observation are shown in FIG. No abnormalities were observed in the coral tissue in the natural seawater area. In the distilled water section, secondary epithelial cells, secondary intercostal cells, and wall column cells were observed to swell, and in some cases, detachment of these cells from the secondary sputum was also observed. Although expansion of some cells was observed in the Ca 2 + · Mg 2+ -removed artificial seawater area, no significant difference was observed from the natural seawater area.
From the above, it was shown that the metal ion-removed seawater has a significantly smaller effect on yellowtail than fresh water, and can be used as a bath salt for controlling parasites.
本発明の金属イオン除去海水(人工海水)は養殖魚、観賞用魚を含む海産魚の寄生虫駆除用水浴液として利用できる。本発明の金属イオン除去海水(人工海水)は海産魚の陸上循環養殖用飼育水として、寄生虫防除目的で利用することができる。 The metal ion-removed seawater (artificial seawater) of the present invention can be used as a bath solution for controlling parasites of marine fish including cultured fish and ornamental fish. The metal ion-removed seawater (artificial seawater) of the present invention can be used for the control of parasites as breeding water for onshore circulation culture of marine fish.
Claims (4)
Removing the metal ions is essential for the survival of the parasite, of claims 1 to 3 parasitic diseases of any marine fish using seawater or artificial seawater was correct for variations in osmotic pressure due to the removal of metal ions prevention and / Or a treatment method.
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| JP2005356671A JP4976006B2 (en) | 2005-03-29 | 2005-12-09 | Parasitic disease prevention and treatment method for marine fish |
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| JP2005093708 | 2005-03-29 | ||
| JP2005093708 | 2005-03-29 | ||
| JP2005356671A JP4976006B2 (en) | 2005-03-29 | 2005-12-09 | Parasitic disease prevention and treatment method for marine fish |
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| Publication Number | Publication Date |
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| JP2006306834A JP2006306834A (en) | 2006-11-09 |
| JP4976006B2 true JP4976006B2 (en) | 2012-07-18 |
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Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| NO20181276A1 (en) * | 2016-03-04 | 2018-10-02 | Slagstad Leiv | Preparation containing sea water added a potassium compound |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2009185002A (en) * | 2008-02-08 | 2009-08-20 | Yatsuka:Kk | Agent and method for preventing and treating parasitic disease of aquatic animal |
| CL2016002937A1 (en) * | 2016-11-17 | 2017-03-03 | Raul Hernan Alvarez Gatica | System for the elimination of parasites attached to fish by means of the direct application of electricity to the fish, which causes the removal of parasites without damaging the fish. |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH02182127A (en) * | 1989-01-07 | 1990-07-16 | Riyouyou Sangyo Kk | Concentrated natural sea water for remedy of fish disease, production of concentrated sea water for remedy of fish disease and treatment of fish disease |
| JPH06153744A (en) * | 1992-09-25 | 1994-06-03 | Riyouyou Sangyo Kk | Method for diminishing parasite of fishes and bacterium and removing living thing attached to crawl net |
| JP4024886B2 (en) * | 1996-08-29 | 2007-12-19 | 第一製網株式会社 | Parasiticides for cultured fish and methods for controlling them |
| JP4023761B2 (en) * | 1999-04-26 | 2007-12-19 | 日本水産株式会社 | The parasite prevention method of trough parasites |
| JP3782999B2 (en) * | 2003-03-17 | 2006-06-07 | 独立行政法人科学技術振興機構 | Artificial seawater and method for producing durable eggs using the same |
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Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
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| NO20181276A1 (en) * | 2016-03-04 | 2018-10-02 | Slagstad Leiv | Preparation containing sea water added a potassium compound |
| EP3422856A4 (en) * | 2016-03-04 | 2019-10-30 | Lutra AS | PREPARATION CONTAINING ADDITIONAL SEA WATER OF POTASSIUM COMPOUND |
| NO347249B1 (en) * | 2016-03-04 | 2023-08-07 | Vestland Pharma As | Water based potassium ion-containing preparation |
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| JP2006306834A (en) | 2006-11-09 |
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