JP6704562B2 - Method of inducing light-escape behavior of red tide-caused rafido algae - Google Patents
Method of inducing light-escape behavior of red tide-caused rafido algae Download PDFInfo
- Publication number
- JP6704562B2 JP6704562B2 JP2014264782A JP2014264782A JP6704562B2 JP 6704562 B2 JP6704562 B2 JP 6704562B2 JP 2014264782 A JP2014264782 A JP 2014264782A JP 2014264782 A JP2014264782 A JP 2014264782A JP 6704562 B2 JP6704562 B2 JP 6704562B2
- Authority
- JP
- Japan
- Prior art keywords
- light
- red tide
- causing
- algae
- inducing
- 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.)
- Active
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/80—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in fisheries management
- Y02A40/81—Aquaculture, e.g. of fish
Landscapes
- Farming Of Fish And Shellfish (AREA)
- Catching Or Destruction (AREA)
- Physical Water Treatments (AREA)
Description
本発明は、赤潮原因ラフィド藻類の光逃避行動を誘導する方法に関する。さらに詳しくは、赤潮原因ラフィド藻類に対して一定領域の波長の光を照射するあるいは除くことにより、光逃避行動を誘導する方法に関する。本発明はさらに、該方法を利用した赤潮の被害を軽減する方法や装置等に関する。 TECHNICAL FIELD The present invention relates to a method for inducing a light-escape behavior of red tide-causing rafido algae. More specifically, the present invention relates to a method for inducing a light-escape action by irradiating or removing light having a wavelength in a certain region with respect to red tide-causing rafido algae. The present invention further relates to a method, device, etc. for reducing the damage of red tide using the method.
従来から、魚介類の養殖産業等において、赤潮の発生による被害が問題となっていた。近年では、西日本の沿岸域において鞭毛藻類による有害赤潮が頻発しており、養殖業への被害総額は2009年および2010年には八代海でそれぞれ33億円および55億円、2012年には豊後水道で15億円と報告されている。 Traditionally, damage caused by the occurrence of red tide has been a problem in the seafood aquaculture industry and the like. In recent years, harmful red tides caused by flagellates have frequently occurred in coastal areas of western Japan, and the total damage to the aquaculture industry was 3.3 billion yen and 5.5 billion yen in the Yatsushiro Sea in 2009 and 2010, respectively, and Bungo Channel in 2012. It is reported to be 1.5 billion yen.
赤潮による被害を防ぐために、長年、様々な技術が考案されており、例えば、有害鞭毛藻類の赤潮駆除法として、化学物質(過酸化水素、水酸化マグネシウムなど)や生物(赤潮藻類感染ウイルス、殺藻細菌など)を散布する方法が考案されてきた。
このような技術のひとつとして、有害な赤潮の原因となるプランクトンの一種であるシャットネラ・アンティカ(Chattonella antiqua)に対して効力を有する、アミンを有効成分として含有する殺藻剤等も開発されている(特許文献1、参照)。
しかし、これらの化学物質や生物の散布には、赤潮発生時毎に莫大なコストが必要であり、適用範囲も狭く、環境や赤潮の原因となる生物以外の生物への負荷が大きい等の問題により、実用化には至っていないのが現状である。
Various techniques have been devised for many years to prevent red tide damage. For example, as a red tide control method for harmful flagellates, chemical substances (hydrogen peroxide, magnesium hydroxide, etc.) Methods have been devised.
As one of such technologies, an algaecide containing an amine as an active ingredient, which is effective against Chattonella antiqua, which is a kind of plankton that causes harmful red tide, has been developed. (See Patent Document 1).
However, spraying these chemicals and organisms requires enormous costs every time a red tide occurs, its application range is narrow, and the burden on the environment and organisms other than the organisms causing the red tide is large. Therefore, it is the current situation that it has not been put to practical use.
一般に実用化されている技術としては、赤潮発生前に餌止めによる赤潮耐性を向上させる手法があるが、赤潮発生を高率で予知する手法が構築されておらず、魚体に対するダメージや出荷遅延など漁業者の経営に大きな悪影響を及ぼすことなどの弱点がある。
また、生簀の周辺をビニールシート等で囲う等により、赤潮の原因となる生物と養殖魚介類との接触頻度を減じることにより、赤潮による被害を軽減する手法も考案されているが、生簀に対して水平方向から流れてくる赤潮は防げても、日周鉛直移動などにより上昇してくる赤潮には対応できず、実用化にあたり十分な効果があるとはいえない。
As a technology that is generally put into practical use, there is a method to improve red tide resistance by stopping food before the red tide occurs, but a method to predict the red tide occurrence at a high rate has not been established, and damage to fish bodies and delays in shipping etc. There are weaknesses such as having a great adverse effect on the management of fishermen.
In addition, a method has also been devised to reduce the damage caused by red tide by reducing the frequency of contact between organisms that cause red tide and cultured seafood, such as by surrounding the cage with a vinyl sheet, etc. Even if the red tide flowing from the horizontal direction can be prevented, it cannot cope with the red tide rising due to vertical movements around the day, and it cannot be said to have a sufficient effect for practical use.
さらに、特許文献2において、特定領域の波長の光を照射することにより、赤潮の原因となる藻類の増殖を抑制する方法が開示されている。この技術では、550〜720nmのうち、特定の波長の光を照射することによりヘテロカプサ・サーキュラリスカーマ(Heterocapsa circularisquama)、カレニア・ミキモトイ(Karenia mikimotoi)、コックロディニウム・ポリクリコイデス(Cochlodinium polykrichoides)、ヘテロシグマ・アカシオ(Heterosigma akashiwo)等の増殖が抑制されたことを確認している。この技術により、光の照射によって赤潮の原因となる有害な藻類の増殖を抑制したり、有用な藻類の増殖を促進したりすることで藻類の増殖調節が可能となるが、既にその場に存在している有害な藻類を除去することはできない。そのため、室内の小規模実験系等の閉鎖空間においては赤潮の原因となる藻類の増殖を調節できるが、赤潮の原因となる藻類が常時流入し得る、湖沼や海等の広大な規模において発生する赤潮については、その被害増大を防ぐ上では十分な技術とはいえず、実用化できない。 Further, Patent Document 2 discloses a method of suppressing the growth of algae that causes red tide by irradiating light with a wavelength in a specific region. In this technology, by irradiating light with a specific wavelength of 550 to 720 nm, Heterocapsa circularisquama, Karenia mikimotoi, Cockrodinium polychrycoides, Cochlodich It has been confirmed that the growth of Heterosigma akashiwo and the like was suppressed. With this technology, it is possible to control the growth of algae by suppressing the growth of harmful algae that cause red tide by irradiating light, or by promoting the growth of useful algae, but it is already in place. It is not possible to remove the harmful algae that are being produced. Therefore, the growth of algae that cause red tide can be controlled in a closed space such as a small-scale experimental system in a room, but the algae that cause red tide can constantly flow in, and occurs in vast scales such as lakes and seas. Red tide is not a sufficient technology to prevent the increase in damage and cannot be put to practical use.
上述のように、長年様々な赤潮防除技術が考案されてきたが、実用化され、また、赤潮の被害を大きく軽減できた技術は皆無であった。そのため、現在においても、赤潮の発生による被害を抑制できる画期的な方策の構築や、駆除技術の開発が急務とされている。 As described above, various red tide control techniques have been devised for many years, but none have been put to practical use and capable of significantly reducing the damage of red tide. Therefore, even now, there is an urgent need to construct epoch-making measures that can suppress damage caused by the occurrence of red tide and to develop eradication technology.
本発明は、湖沼や海等の広大な規模において発生する赤潮の被害の軽減においても有効で、かつ、生物や環境への負荷が少ない画期的な赤潮発生防止策の方法の提供を課題とする。 The present invention is also effective in reducing the damage of red tides that occur in vast scales such as lakes and seas, and provides a method of an epoch-making red tide occurrence prevention method with less load on living organisms and the environment. To do.
本発明者らは、上記課題を解決するために鋭意検討を行った結果、多くの有害赤潮原因藻類が鞭毛運動を行って遊泳し、昼間定位する層の深度が光環境によって変化することを野外調査などによって見出した。
本発明者らのこの研究成果を受けて、一定領域の波長の光を照射することにより、赤潮原因ラフィド藻類の光逃避行動が誘導できることを見出し、本発明を完成するに至った。本発明ではさらに、この赤潮原因ラフィド藻類の光逃避行動を誘導することにより、養殖生簀等の赤潮の発生を防ぎたい場所からこれらの藻類を除去したり、外部からの流入を防御したりすることで赤潮の被害を軽減することが可能となる。
このような本発明の方法は、短時間の照射やフィルターなどの光学部品の設置によって赤潮原因ラフィド藻類の光逃避行動を誘導することができる上、養殖生簀内で適用し得るものであるため、赤潮被害の軽減においても、他の生物や環境への負荷が少なく、実用的な方法である。
As a result of intensive studies to solve the above problems, the present inventors have found that many harmful red tide-causing algae perform flagella movements and swim, and that the depth of the layer localized during the day changes depending on the light environment outdoors. It was found by investigation.
Based on the research results of the present inventors, it was found that the light escape behavior of the red tide-causing rafidoalgae can be induced by irradiating light with a wavelength in a certain region, and the present invention has been completed. In the present invention, further, by inducing the light-escape behavior of the red tide-causing rafido algae, removing these algae from places where it is desired to prevent the occurrence of red tides such as aquaculture cages, or to prevent the inflow from the outside. It is possible to reduce the damage of the red tide.
Such a method of the present invention is capable of inducing the light-escape behavior of red tide-caused rafidoalgae by installing optical components such as irradiation and filters for a short period of time, and since it can be applied in aquaculture cages, It is also a practical method for reducing red tide damage, as it has less impact on other organisms and the environment.
すなわち、本発明は次の(1)〜(10)に記載の赤潮原因ラフィド藻類の光逃避行動を誘導する方法等に関する。
(1)320nm〜440nm(UV−B〜青色領域)および/または640nm〜680nm(赤色領域)の波長の光を照射することにより、赤潮原因ラフィド藻類の光逃避行動を誘導する方法。
(2)上記(1)に記載の方法であって、さらに、480〜560nm(緑色領域)の波長の光をカットすることにより、赤潮原因ラフィド藻類の光逃避行動を誘導する方法。
(3)光の照射が上方向および/または左右方向からの照射である、上記(1)または(2)に記載の赤潮原因ラフィド藻類の光逃避行動を誘導する方法。
(4)上記(1)〜(3)のいずれかに記載の方法により、赤潮原因ラフィド藻類の光逃避行動を誘導することにより赤潮の被害を軽減する方法。
(5)赤潮原因ラフィド藻類がシャットネラ・アンティカ(Chattonella antiqu)である上記(1)〜(4)のいずれかに記載の方法。
(6)320nm〜440nm(UV−B〜青色領域)および/または640nm〜680nm(赤色領域)の波長の光を照射する手段を含む、赤潮原因ラフィド藻類の光逃避行動を誘導する装置。
(7)上記(6)に記載の装置であって、さらに、480〜560nm(緑色領域)の波長の光をカットする手段を含む、赤潮原因ラフィド藻類の光逃避行動を誘導する装置。
(8)光の照射が上方向および/または左右方向からである、上記(6)または(7)に記載の赤潮原因ラフィド藻類の光逃避行動を誘導する装置。
(9)上記(6)〜(8)のいずれかに記載の装置であって、生簀あるいは海水濾過機構またはこれらの近傍にセットする手段を含む、赤潮の被害を軽減するための装置。
(10)赤潮原因ラフィド藻類がシャットネラ・アンティカ(Chattonella antiqua)である上記(6)〜(9)のいずれかに記載の装置。
That is, the present invention relates to the following methods (1) to (10) for inducing the light-escape behavior of the red tide-causing rafido algae.
(1) A method of inducing a light-escape action of a red tide-caused raphidid algae by irradiating with light having a wavelength of 320 nm to 440 nm (UV-B to blue region) and/or 640 nm to 680 nm (red region).
(2) The method according to (1) above, which further cuts off light having a wavelength of 480 to 560 nm (green region) to induce a light-escape action of the red tide-caused rafidoalgae.
(3) The method for inducing the light-escape behavior of the red tide-caused raphidid alga according to (1) or (2) above, wherein the light irradiation is from the upward direction and/or the lateral direction.
(4) The method according to any one of (1) to (3) above, which reduces the damage of red tide by inducing the light-escape behavior of the red tide-causing rafidoalgae.
(5) The method according to any one of (1) to (4) above, wherein the red tide-causing rafido alga is Chattonella antique.
(6) A device for inducing a light-escape action of red tide-caused raphidid algae, which comprises a means for irradiating light with a wavelength of 320 nm to 440 nm (UV-B to blue region) and/or 640 nm to 680 nm (red region).
(7) The device according to (6) above, which further comprises means for cutting off light having a wavelength of 480 to 560 nm (green region), and which induces the light-escape behavior of the red tide-causing Rafido algae.
(8) The device for inducing the light-escape behavior of the red tide-caused rafidophyte according to (6) or (7), wherein the light irradiation is from the upward and/or the lateral direction.
(9) The device according to any one of (6) to (8) above, which comprises a cage or seawater filtration mechanism or means for setting in the vicinity thereof, for reducing red tide damage.
(10) The apparatus according to any of (6) to (9) above, wherein the red tide-causing rafido alga is Chattonella antiqua.
本発明の赤潮原因ラフィド藻類の光逃避行動を誘導する方法の提供により、赤潮の被害を軽減するにあたり、有効でかつ、小規模で生物や環境への負荷が少ない画期的な赤潮発生防止策の提供が可能となる。また、本発明により、特定の波長の光を照射するあるいはフィルター等の光学部品を設置することにより、赤潮原因ラフィド藻類の光逃避行動を誘導し、赤潮の被害を軽減するための装置の提供も可能となる。 By providing a method of inducing the light-escape behavior of the red tide-causing rafido algae of the present invention, it is effective in reducing the damage of the red tide, and is an epoch-making red tide occurrence prevention measure that is small and has a small load on living organisms and the environment. Can be provided. Further, according to the present invention, by irradiating light of a specific wavelength or by installing an optical component such as a filter, it is possible to provide a device for inducing the light-escape action of the red tide-causing rafidoalgae and reducing the damage of the red tide. It will be possible.
本発明の「赤潮原因ラフィド藻類の光逃避行動を誘導する方法」は、320nm〜440nm(UV−B〜青色領域)および/または640nm〜680nm(赤色領域)の波長の光を照射する、あるいは緑色領域(520nm付近)のみを除去することで、赤潮原因ラフィド藻類の光逃避行動を誘導できる方法であればよい。
このような方法であれば、赤潮原因ラフィド藻類が存在する養殖生簀において320nm〜440nm(UV−B〜青色領域)の波長または640nm〜680nm(赤色領域)の波長のいずれかの光を照射してもよく、これらの両方の光を照射してもよい。さらに、緑色領域(520nm付近)のみを除去してもよい。
The “method of inducing the light-escape behavior of the red tide-causing rafidoalgae” of the present invention is to irradiate light having a wavelength of 320 nm to 440 nm (UV-B to blue region) and/or 640 nm to 680 nm (red region), or green. Any method can be used as long as it can induce the light-escape behavior of the red tide-causing rafidoalgae by removing only the region (around 520 nm).
According to such a method, the cultured cage containing the red tide-causing rafido algae is irradiated with light having a wavelength of 320 nm to 440 nm (UV-B to blue region) or a wavelength of 640 nm to 680 nm (red region). Alternatively, both of these lights may be irradiated. Further, only the green region (near 520 nm) may be removed.
本発明における「光逃避行動」とは、光を照射すると赤潮原因ラフィド藻類が下方向あるいは光量の少ない方向に移動することをいう。例えば、上記波長の光を上方から下方に照射した場合は、赤潮原因ラフィド藻類は下方に移動することになる。 The "light escape behavior" in the present invention means that the red tide-causing rafidoalgae move downward or in the direction of low light intensity when irradiated with light. For example, when the light of the above wavelength is irradiated from the upper side to the lower side, the red tide-causing rafido algae moves downward.
本発明の「赤潮原因ラフィド藻類の光逃避行動を誘導する方法」では、さらに、520nm付近(緑色領域)の波長の光が照射されるのをカットすることが好ましい。
このような緑色光をカットする方法としては、バンドパスフィルターなど各種光学部品を用いることになる。
In the “method of inducing the light-escape behavior of red tide-causing rafidoalgae” of the present invention, it is preferable to further prevent irradiation with light having a wavelength of around 520 nm (green region).
As a method of cutting such green light, various optical parts such as a bandpass filter are used.
本発明の「赤潮原因ラフィド藻類の光逃避行動を誘導する方法」では、赤潮原因ラフィド藻類が存在する環境に対して、赤潮原因ラフィド藻類を走行させたい方向とは逆の方向から上記の特定の波長の光を照射することが好ましい。
このような光の照射の方向としては、上方向や左右方向からの照射が効果的であり、上方向からの照射と左右方向からの照射を組み合わせて同時に照射したり、交互に照射したり、一定のリズムで照射してもよい。
In the "method of inducing the light-escape behavior of red tide-causing rafido algae" of the present invention, the environment in which the red tide-causing rafido algae is present, the specific direction from the direction opposite to the direction in which the red tide-causing rafido algae is desired to run It is preferable to irradiate light having a wavelength.
As the direction of such light irradiation, it is effective to irradiate from the upper direction or the left-right direction, and the irradiation from the upper direction and the irradiation from the left-right direction are combined at the same time or alternately, You may irradiate with a fixed rhythm.
本発明のこのような「赤潮原因ラフィド藻類の光逃避行動を誘導する方法」は、光環境を人為的に変化させて生物の行動を操る、集魚灯漁法(サンマ漁・イカ釣り等)のように水産の現場で実際に活用されている方法と同様の方法であることから、赤潮被害の軽減等への活用においても、他の生物や環境への負荷が少なく、実用的な方法であるといえる。
特に本発明において照射する青色領域の光は、海水中に最も透過しやすい光であるため、海水等への適応において効果的である。
The "method of inducing the light-escape behavior of the red tide-caused rafido algae" of the present invention is a method of artificially changing the light environment to control the behavior of living things, such as a fish-collecting fishing method (saury fishing, squid fishing, etc.). Since it is a method similar to the method actually used in the field of fisheries, it is a practical method even when used to reduce red tide damage, etc., because it has less load on other organisms and the environment. I can say.
In particular, the light in the blue region to be irradiated in the present invention is the light that is most easily transmitted into seawater, and is therefore effective in adaptation to seawater and the like.
本発明における「赤潮原因ラフィド藻類」とは、赤潮の原因となる鞭毛を有する藻類のことをいう。赤潮原因ラフィド藻類(raphidophytes)のうち、本発明の光逃避行動を誘導する藻類として、特にシャットネラ・アンティカ(Chattonella antiqua)やヘテロシグマ・アカシオ(Heterosigma akashiwo)などのラフィド藻を対象とすることが好ましい。 The “red tide-causing rafido algae” in the present invention refers to algae having flagella that cause red tide. Among the red tide-causing raphidophytes, as the algae that induce the light-escape behavior of the present invention, particularly the rafidoalga such as Chattonella antica and Heterosigma akashiwo are preferable.
本発明の「赤潮の被害を軽減する方法」は、上記の特定の波長の光を照射することによる「赤潮原因ラフィド藻類の光逃避行動を誘導する方法」により、赤潮原因ラフィド藻類の存在する環境におけるこれらの比率を低減させることで、赤潮の被害を軽減できる方法であれば良い。
この「赤潮原因ラフィド藻類の光逃避行動を誘導する方法」のみを活用する方法であっても良く、従来知られているその他の赤潮の被害を軽減するための方法と組み合わせても良い。
The "method of reducing damage of red tide" of the present invention is an "environment where red tide-causing rafidoalgae exists" by "a method of inducing a light-escape action of red tide-causing rafidoalgae" by irradiating with light of the above specific wavelength. Any method that can reduce the damage of the red tide by reducing these ratios in
This “method of inducing light-escape behavior of red tide-causing rafido algae” alone may be used, or it may be combined with other conventionally known methods for reducing damage of red tide.
本発明の「赤潮原因ラフィド藻類の光逃避行動を誘導する装置」としては、本発明の320nm〜440nm(UV−B〜青色領域)および/または640nm〜680nm(赤色領域)の波長の光の照射が可能な装置であればよく、これらの光源やそれらを含む装置であることが好ましい。
さらに、520nm付近(緑色領域)の波長の光をカットできる光学フィルター等を有する装置であることが好ましい。
これらの装置は、例えば養殖魚類を育成するための生簀にセットできる装置や、海岸から海水をくみ上げて使用している種苗保存施設や実験施設等における海水濾過過程(貯水槽など)において出水口からの有害赤潮藻類の侵入を防ぐことが可能な装置であることが好ましい。
The “device for inducing the light-escape action of red tide-causing rafidoalgae” of the present invention is irradiation with light having a wavelength of 320 nm to 440 nm (UV-B to blue region) and/or 640 nm to 680 nm (red region) of the present invention. Any device capable of performing the above is preferable, and a device including these light sources or a device including them is preferable.
Further, it is preferable that the device has an optical filter or the like capable of cutting off light having a wavelength near 520 nm (green region).
These devices are, for example, devices that can be set in cages for cultivating cultured fish, or from the outlet in the seawater filtration process (water tank, etc.) at seedling preservation facilities and experimental facilities that use seawater drawn from the coast. It is preferable that the device is capable of preventing invasion of harmful red tide algae.
以下に本発明の実施例を挙げて本発明をさらに詳細に説明するが、本発明は、これらに何ら限定されるものではない。 Hereinafter, the present invention will be described in more detail with reference to Examples of the present invention, but the present invention is not limited thereto.
特に断りがない限り、本発明の実施例では、次のように調整した赤潮原因ラフィド藻類を用い、次の条件で試験、解析を行った。
1.赤潮原因ラフィド藻類
赤潮原因ラフィド藻類として、25℃、300μmolm−2s−1(白色蛍光灯)、12時間明:12時間暗の明暗周期(6:00〜18:00)で継代培養した、有害赤潮原因ラフィド藻シャットネラ・アンティカ(Chattonella antiqua)を用いた。
試験前日に、細胞密度が5000cells/mLになるように新鮮な培地と培養液を混合して角型水槽(水深5cm)に入れ、明期の光強度を20μmolm−2s−1に下げて培養した後、試験に供した。
Unless otherwise specified, in the examples of the present invention, the red tide-causing rafidoalgae prepared as described below were used and tested and analyzed under the following conditions.
1. Red tide-causing rafido algae As red tide-causing rafido algae, subculture was performed at 25° C., 300 μmolm −2 s −1 (white fluorescent lamp), 12 hours light: 12 hours dark/dark cycle (6:00 to 18:00), The rafido alga, Chattonella antiqua, which causes harmful red tide, was used.
On the day before the test, a fresh medium and a culture solution were mixed so that the cell density would be 5000 cells/mL, and the mixture was placed in a rectangular water tank (water depth 5 cm), and the light intensity in the light period was lowered to 20 μmolm −2 s −1 and cultured. After that, it was subjected to the test.
2.試験・解析条件
試験はシャットネラ・アンティカが日周鉛直移動により、表層に集積する時間帯である8:30〜15:00に実施した。
シャットネラ・アンティカの遊泳行動は赤外線(850nm)を観察光としてCCDカメラ(CFW、Scion Corporation、Frederick、MD、USA)で観察し、その後Image J(http://rsb.info.nih.gov/ij/)を用いて画像解析を施すことで表層の細胞密度を定量した。
2. Test/Analysis Conditions The test was conducted from 8:30 to 15:00, which is the time zone when Shutnera Antica accumulates on the surface due to the daily vertical movement.
The swimming behavior of Chattonella Antica was observed with a CCD camera (CFW, Scion Corporation, Frederick, MD, USA) using infrared rays (850 nm) as observation light, and then Image J (http://rsb.info.nih.gov/ij). The cell density of the surface layer was quantified by performing image analysis using /).
〔実施例1〕
光逃避行動の作用スペクトルの検討
岡崎大型スペクトログラフ(基礎生物学研究所)により、シャットネラ・アンティカに320〜680nmの40nm間隔、50μmolm−2s−1の単色光を上方向から照射し、遊泳行動を経時的に観察した。図1に光照射3分後の表層における細胞の減少量を照射開始時の相対値(%)として示した。
その結果、図1に示されるように、320〜480nmおよび640〜680nmの単色光下で、表層の細胞密度が経時的に低下した。3分後の表層細胞密度の減少量は440nm(青色光)で最大値、520nm(緑色光)で最低値となった。
従って、この結果より、シャットネラ・アンティカの光逃避行動を誘導するには、320nm〜440nm(UV−B〜青色領域)または640nm〜680nm(赤色領域)、特に440nm(青紫色)の単色光照射することが有用であることが確認できた。
なお、本実施例は、大型スペクトログラフを用いたものであり、現在市販されている他の波長も多少混ざっているLED光源では成し得ないものである。
[Example 1]
Examination of action spectrum of light-escape behavior By Okazaki large-scale spectrograph (Institute of Basic Biology), Shutnera Antica is irradiated with monochromatic light of 50 μmolm −2 s −1 from above in 40 nm interval of 320 to 680 nm, and swimming behavior Was observed over time. FIG. 1 shows the amount of decrease in cells in the surface layer 3 minutes after light irradiation as a relative value (%) at the start of irradiation.
As a result, as shown in FIG. 1, the cell density of the surface layer decreased with time under the monochromatic light of 320 to 480 nm and 640 to 680 nm. The amount of decrease in the surface layer cell density after 3 minutes reached the maximum value at 440 nm (blue light) and reached the minimum value at 520 nm (green light).
Therefore, from this result, in order to induce the light-escape behavior of Shutnera antica, monochromatic light irradiation of 320 nm to 440 nm (UV-B to blue region) or 640 nm to 680 nm (red region), particularly 440 nm (blue-violet) is performed. It was confirmed that it was useful.
It should be noted that this embodiment uses a large-scale spectrograph, and cannot be realized by an LED light source which is mixed with other wavelengths currently on the market.
〔実施例2〕
光逃避行動を誘導する光強度および照射時間の検討
LED光源(ホロライトHL01型455nm、パイホトニクス社製)により、異なる光強度(10、30、100、150μmolm−2s−1)の青色光(455nm)をシャットネラに照射し、遊泳行動を経時的に観察した。
図2に表層における細胞の減少量を照射開始時の相対値(%)として示した。図2に示されるように、30μmolm−2s−1、100μmolm−2s−1または150μmolm−2s−1の青色光を照射した場合には、照射開始後3分以内に表層細胞密度の低下が観察された。また、100μmolm−2s−1および150μmolm−2s−1の青色光を照射した場合には、照射開始後3分以内に表層細胞密度の減少量が飽和し、光強度を上げても該密度が減少しないことが確認された。
従って、この結果より、シャットネラ・アンティカの光逃避行動を光照射開始後3分以内に誘導するために必要な青色光(455nm)の光強度の閾値は10〜30μmolm−2s−1であることが確認できた。
[Example 2]
Examination of light intensity and irradiation time for inducing light-escape behavior Blue light (455 nm) having different light intensities (10, 30, 100, 150 μmolm −2 s −1 ) depending on the LED light source (Hololite HL01 type 455 nm, manufactured by Pi Photonics). ) Was irradiated to Shutnera and the swimming behavior was observed over time.
FIG. 2 shows the amount of cells reduced in the surface layer as a relative value (%) at the start of irradiation. As shown in FIG. 2, when blue light of 30 μmolm −2 s −1 , 100 μmolm −2 s −1, or 150 μmolm −2 s −1 was irradiated, the surface cell density decreased within 3 minutes after the start of irradiation. Was observed. When 100 μmolm −2 s −1 and 150 μmolm −2 s −1 of blue light was irradiated, the decrease amount of the surface layer cell density was saturated within 3 minutes after the start of irradiation, and even if the light intensity was increased, the density decreased. Was confirmed not to decrease.
Therefore, from this result, the threshold value of the light intensity of blue light (455 nm) required to induce the light-escape behavior of Shutnera antica within 3 minutes after the start of light irradiation is 10 to 30 μmolm −2 s −1. Was confirmed.
〔実施例3〕
緑色光による光逃避行動の阻害効果の検討
LED光源(ISL−150X150−HGB45、CCS株式会社)により、シャットネラに青色光(450nm、50μmolm−2s−1)または緑色光(525nm、50μmolm−2s−1)を単独で照射した。また、同じ強度の青色光および緑色光を同時に照射し、照射直前と3分後の細胞の表層細胞密度を比較した。
[Example 3]
The study of the inhibitory effect of light escape behavior by the green LED light source (ISL-150X150-HGB45, CCS Inc.), blue light chattonella (450nm, 50μmolm -2 s -1) or green light (525nm, 50μmolm -2 s -1 ) was irradiated alone. Further, blue light and green light having the same intensity were simultaneously irradiated, and the cell density of the surface layer of the cells was compared immediately before and 3 minutes after the irradiation.
図3に表層における細胞の減少量を照射開始時の相対値(%)として示した。図3の暗条件とは光を何も照射していない条件を示す。図3に示されるように、青色光を単独で照射した場合のみ、表層細胞密度の低下が観察された。
従って、この結果より、50μmolm−2s−1の青色光(450nm)を照射した場合、緑色領域の光(525nm)を青色光と同じ以上の強度で同時に照射するとシャットネラの光逃避行動の誘導が阻害されるため、実環境中では太陽光から緑色領域の光をカットすることによっても光逃避行動を誘導することができることが示唆された。
FIG. 3 shows the amount of cells reduced in the surface layer as a relative value (%) at the start of irradiation. The dark condition in FIG. 3 indicates a condition where no light is applied. As shown in FIG. 3, a decrease in surface cell density was observed only when blue light was irradiated alone.
Therefore, from this result, when 50 μmolm −2 s −1 blue light (450 nm) is irradiated, when light in the green region (525 nm) is simultaneously irradiated with an intensity equal to or higher than that of blue light, the induction of light escape behavior of the Shutnera is induced. Therefore, it was suggested that light-escape behavior could be induced by cutting light in the green region from sunlight in the real environment.
本発明の特定の波長の光を照射する赤潮原因ラフィド藻類の光逃避行動を誘導する方法を活用することにより、赤潮の被害を軽減するための装置の提供等が可能となる。
By utilizing the method of inducing the light-escape behavior of the red tide-causing rafidoalgae that irradiates with light of a specific wavelength according to the present invention, it is possible to provide a device for reducing damage of the red tide.
Claims (10)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2014264782A JP6704562B2 (en) | 2014-12-26 | 2014-12-26 | Method of inducing light-escape behavior of red tide-caused rafido algae |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2014264782A JP6704562B2 (en) | 2014-12-26 | 2014-12-26 | Method of inducing light-escape behavior of red tide-caused rafido algae |
Publications (2)
Publication Number | Publication Date |
---|---|
JP2016123288A JP2016123288A (en) | 2016-07-11 |
JP6704562B2 true JP6704562B2 (en) | 2020-06-03 |
Family
ID=56356608
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2014264782A Active JP6704562B2 (en) | 2014-12-26 | 2014-12-26 | Method of inducing light-escape behavior of red tide-caused rafido algae |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP6704562B2 (en) |
Family Cites Families (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS55157379A (en) * | 1979-05-26 | 1980-12-08 | Nippon Carbide Ind Co Ltd | Method of controlling red tide and substance used therefor |
JPH07102059B2 (en) * | 1991-09-05 | 1995-11-08 | 菱洋産業株式会社 | How to eliminate red tide |
JPH10103896A (en) * | 1996-09-30 | 1998-04-24 | Tokyo Electric Power Co Inc:The | Water sprinkler for open rack evaporator |
JP2007068419A (en) * | 2005-09-05 | 2007-03-22 | Japan Science & Technology Agency | Method for inhibiting increase of harmful algae causing red tide |
JP6183825B2 (en) * | 2013-03-04 | 2017-08-23 | 国立大学法人 東京大学 | Method and apparatus for concentrating microalgae culture solution |
-
2014
- 2014-12-26 JP JP2014264782A patent/JP6704562B2/en active Active
Also Published As
Publication number | Publication date |
---|---|
JP2016123288A (en) | 2016-07-11 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Gambardella et al. | Ecotoxicological effects of polystyrene microbeads in a battery of marine organisms belonging to different trophic levels | |
Dehghani | Removal of cyanobacterial and algal cells from water by ultrasonic waves—A review | |
JP5961771B1 (en) | How to prevent attached organisms | |
KR102020699B1 (en) | Method for stopping attachment-period larvae from swimming or crawling | |
GB2491500A (en) | System and method for treating fish | |
JP6215967B2 (en) | How to kill airfoil and barnacles by light irradiation | |
Giannakis et al. | Elucidating bacterial regrowth: Effect of disinfection conditions in dark storage of solar treated secondary effluent | |
CN104990031A (en) | Combination light source with good trapping effect for citrus psylla adults | |
Deininger et al. | Simulated terrestrial runoff triggered a phytoplankton succession and changed seston stoichiometry in coastal lagoon mesocosms | |
Gao et al. | The green tide-forming macroalga Ulva linza outcompetes the red macroalga Gracilaria lemaneiformis via allelopathy and fast nutrients uptake | |
EP3181760B1 (en) | Method for preventing formation of biofilm | |
JP6704562B2 (en) | Method of inducing light-escape behavior of red tide-caused rafido algae | |
JP2007068419A (en) | Method for inhibiting increase of harmful algae causing red tide | |
Putri et al. | Adsorption of Cd and Pb using biomass of microalgae Spirulina platensis | |
KR20170110273A (en) | Fish Cage red tide prevention device. | |
Praeger et al. | Maximising the productivity of the attached cultivation of Ulva tepida in land-based systems | |
Flagella et al. | Ship ballast water as a main vector of marine introductions in the Mediterranean Sea | |
CN109264817A (en) | A method of control algal grown and inhibition Microcystin | |
KR101742789B1 (en) | Red tides and water bloom Remedial Method utilizing salvation substance Consisting of ocher and cockle shell in accordance with algal concentration | |
Kett et al. | Solar UV radiation modulates animal health and pathogen prevalence in coastal habitats knowledge gaps and implications for bivalve aquaculture | |
KR101871376B1 (en) | Efficient Control of Macroalgae by Simultaneous Treatment of Physical and Chemical method | |
Klemenčič et al. | The efficiency of ultrasound on algal control in a closed loop water treatment system for cyprinid fish farms | |
KR20130108851A (en) | A method for controling growth of algae by using light emitting diodes | |
CN209858578U (en) | Research device for plankton migration behavior | |
CN105884034B (en) | Control the screening verification method of algae tool biology |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A711 | Notification of change in applicant |
Free format text: JAPANESE INTERMEDIATE CODE: A711 Effective date: 20171205 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A821 Effective date: 20171206 |
|
A621 | Written request for application examination |
Free format text: JAPANESE INTERMEDIATE CODE: A621 Effective date: 20171225 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20180115 |
|
A977 | Report on retrieval |
Free format text: JAPANESE INTERMEDIATE CODE: A971007 Effective date: 20180718 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20180725 |
|
A601 | Written request for extension of time |
Free format text: JAPANESE INTERMEDIATE CODE: A601 Effective date: 20180921 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20190508 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20190708 |
|
TRDD | Decision of grant or rejection written | ||
A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20200108 |
|
A61 | First payment of annual fees (during grant procedure) |
Free format text: JAPANESE INTERMEDIATE CODE: A61 Effective date: 20200205 |
|
R150 | Certificate of patent or registration of utility model |
Ref document number: 6704562 Country of ref document: JP Free format text: JAPANESE INTERMEDIATE CODE: R150 |
|
S531 | Written request for registration of change of domicile |
Free format text: JAPANESE INTERMEDIATE CODE: R313531 |
|
R350 | Written notification of registration of transfer |
Free format text: JAPANESE INTERMEDIATE CODE: R350 |
|
R250 | Receipt of annual fees |
Free format text: JAPANESE INTERMEDIATE CODE: R250 |