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JP7410490B2 - Closed land aquaculture equipment and land aquaculture method using the same - Google Patents
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JP7410490B2 - Closed land aquaculture equipment and land aquaculture method using the same - Google Patents

Closed land aquaculture equipment and land aquaculture method using the same Download PDF

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JP7410490B2
JP7410490B2 JP2019136466A JP2019136466A JP7410490B2 JP 7410490 B2 JP7410490 B2 JP 7410490B2 JP 2019136466 A JP2019136466 A JP 2019136466A JP 2019136466 A JP2019136466 A JP 2019136466A JP 7410490 B2 JP7410490 B2 JP 7410490B2
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廣雄 武居
啓雄 加藤
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AQUA FUTURE LABORATORY COMPANY LIMITED
RISNI INCORPORATED
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    • YGENERAL 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
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この発明は、閉鎖型陸上養殖装置及びそれを用いた陸上養殖方法に関する。 The present invention relates to a closed land aquaculture device and a land aquaculture method using the same.

陸上の養殖池内にて養殖水を濾過循環させ、エビやカニなどの甲殻類あるいは魚類などの被養殖物を養殖する閉鎖型陸上養殖方法が種々提案されている。一方、マイクロバブルやナノバブルなどの微細気泡を養殖水中に形成しつつ養殖を行なうことで、エビなどの養殖物の成長促進を図る提案もなされている。例えば、特許文献1、2においては、絞り孔にねじ部材を配置したキャビテーションノズルを用いて微細気泡を発生させるようにしている。ここで、えら呼吸によって溶存酸素を取り込む魚類や甲殻類などの場合、養殖水中の酸素濃度はなるべく高い方が有利と認識されている。また、キャビテーションノズルは減圧沸騰により溶存酸素を消費して微細気泡化するので、粗大な気泡の浮上による溶存酸素の損失を補う意味でも、養殖水中の酸素濃度は高い方がよいと考えられている。 Various closed land aquaculture methods have been proposed in which aquaculture water is filtered and circulated in a land aquaculture pond to cultivate farmed products such as crustaceans such as shrimp and crabs or fish. On the other hand, proposals have also been made to promote the growth of shrimp and other cultured products by cultivating them while forming microbubbles, nanobubbles, or other microbubbles in the culture water. For example, in Patent Documents 1 and 2, microbubbles are generated using a cavitation nozzle in which a screw member is arranged in the aperture hole. Here, in the case of fish and crustaceans that take in dissolved oxygen through gill respiration, it is recognized that it is advantageous for the oxygen concentration in the culture water to be as high as possible. Additionally, since cavitation nozzles consume dissolved oxygen and turn it into fine bubbles through reduced-pressure boiling, it is thought that the oxygen concentration in the aquaculture water should be high to compensate for the loss of dissolved oxygen due to the surfacing of coarse bubbles. .

特許文献1、2においては、空気(酸素)ないしオゾンをアスピレータにより養殖水と気液混合し、さらにタンク内にて過飽和に加圧溶解処理した上でキャビテーションノズルに導いている。よって、養殖池内の養殖水の酸素濃度はほぼ飽和値(8ppm)に維持されていると考えられ、かつ、キャビテーションにより発生する大量の酸素を含有した微細気泡は、酸素濃度が飽和した養殖水の場合再溶解が進みにくいので、浮上により損失するまでの間は気泡の状態を保っているものと考えられる。この酸素微細気泡は、被養殖物による溶存酸素の消費を補う、いわば「酸素のリザーバ」としての機能が期待されるものである。 In Patent Documents 1 and 2, air (oxygen) or ozone is gas-liquid mixed with culture water using an aspirator, and then subjected to pressurized dissolution treatment to supersaturation in a tank, and then introduced to a cavitation nozzle. Therefore, it is thought that the oxygen concentration of the culture water in the culture pond is maintained at almost the saturated value (8 ppm), and the microbubbles containing a large amount of oxygen generated by cavitation are In this case, re-dissolution is difficult to proceed, so it is thought that the bubbles remain in the bubble state until they are lost due to levitation. These oxygen microbubbles are expected to function as an "oxygen reservoir," so to speak, to supplement the consumption of dissolved oxygen by the cultivated material.

特開2011-240206号公報Japanese Patent Application Publication No. 2011-240206 特開2012- 40448号公報Japanese Patent Application Publication No. 2012-40448

「ナノバブル水中のナノバブルの解析」 Nanotech Japan Bulletin Vol. 8, No. 4, 2015“Analysis of nanobubbles in nanobubbles in water” Nanotech Japan Bulletin Vol. 8, No. 4, 2015

しかしながら、本発明者が詳細に検討したところ、養殖水中に大量の微細気泡が浮遊していると魚類やエビ・カニなどの被養殖物のえらに気泡が付着し、溶存酸素の取り込みが返って阻害されて、被養殖物の生育が却って妨げられ、甚だしい場合には被養殖物の少なからぬ斃死を招く場合があることが判明した。 However, the inventor's detailed study revealed that if a large number of microbubbles are suspended in the aquaculture water, the bubbles will adhere to the gills of fish, shrimp, crabs, and other cultured animals, and the uptake of dissolved oxygen will be reduced. It has been found that the growth of the cultured objects is actually hindered, and in severe cases, this can lead to the death of a considerable number of the cultured objects.

本発明の課題は、養殖水のキャビテーション処理に伴う微細気泡の過剰発生を防止しつつも、被養殖物の生育促進等は問題なく図ることができる閉鎖型陸上養殖装置と、それを用いた陸上養殖方法とを提供することにある。 The object of the present invention is to provide a closed land-based aquaculture device that can promote the growth of cultivated products without any problems while preventing excessive generation of microbubbles accompanying cavitation treatment of aquaculture water, and a land-based aquaculture device using the same. The objective is to provide a cultivation method.

上記の課題を解決するために、本発明の閉鎖型陸上養殖装置は、養殖池内に養殖水と甲殻類又は魚類からなる被養殖動物とを収容し、主ポンプを用いて養殖池から養殖水を濾過槽に導き、養殖水中に浮遊する有機残渣を濾過しつつ養殖池内に戻して循環させながら、養殖池内に飼料を投入して被養殖動物を飼育するための閉鎖型陸上養殖装置において、養殖水の酸素濃度が2.5ppm以上7ppm以下に維持されるように養殖水に酸素含有気体を供給しつつ溶解する酸素溶解機構と、養殖池に養殖水の流入口が連通するとともに、他端側が養殖水の養殖池への戻し口とされたキャビテーション処理用配管と、キャビテーション処理用配管の途上に設けられ、一端に養殖水の入口を、他端に養殖水の出口を有するノズル流路が形成されるとともに、該ノズル流路の一部区間がキャビテーション処理部として定められたノズル本体と、キャビテーション処理部にてノズル本体に脚部先端側が流路内側に突出するように組付けられる複数のねじ部材とを備え、養殖水を養殖水入口から養殖水出口に向けて流通させ、キャビテーション処理部にてねじ部材の脚部外周面に形成されたねじ谷に養殖水を増速しつつ接触させることにより、該養殖水に対し溶存空気の減圧析出に基づくキャビテーション処理を行なうキャビテーションノズルと、キャビテーション処理用配管の途上に設けられ、キャビテーションノズルに養殖水をキャビテーション処理部における断面平均流速が8m/sec以上となる規定流量にて流通させるキャビテーション処理用ポンプとを備えたことを特徴とする。 In order to solve the above problems, the closed land aquaculture device of the present invention accommodates culture water and cultured animals such as crustaceans or fish in an aquaculture pond, and uses a main pump to pump the aquaculture water from the aquaculture pond. In a closed land aquaculture system, the aquaculture water is introduced into a filtration tank to filter out organic residues floating in the aquaculture water, and then circulated back into the aquaculture pond. The oxygen dissolving mechanism supplies and dissolves oxygen-containing gas to the aquaculture water so that the oxygen concentration is maintained at 2.5 ppm or more and 7 ppm or less, and the inlet of the aquaculture water communicates with the aquaculture pond, and the other end is connected to the aquaculture pond. A cavitation treatment pipe is used as a return port for water to the aquaculture pond, and a nozzle flow path is provided in the middle of the cavitation treatment pipe and has an inlet of the aquaculture water at one end and an outlet of the aquaculture water at the other end. and a nozzle body in which a part of the nozzle flow path is defined as a cavitation treatment section, and a plurality of screw members that are assembled to the nozzle body in the cavitation treatment section so that the tip ends of the legs protrude inside the flow path. By making the culture water flow from the culture water inlet to the culture water outlet, and bringing the culture water into contact with the thread valley formed on the outer peripheral surface of the leg of the threaded member in the cavitation treatment part while increasing the speed. , a cavitation nozzle that performs cavitation treatment based on reduced pressure precipitation of dissolved air on the culture water, and a cavitation nozzle installed in the middle of the cavitation treatment piping, and configured to supply the culture water to the cavitation nozzle at an average cross-sectional flow velocity of 8 m/sec or more in the cavitation treatment section. The invention is characterized by comprising a cavitation treatment pump that causes the flow to flow at a specified flow rate.

また、本発明の陸上養殖方法は、上記本発明の閉鎖型陸上養殖装置を用い、養殖池内に養殖水と被養殖動物とを収容し、主ポンプを用いて養殖池から養殖水を濾過槽に導き、養殖水中に浮遊する有機残渣を濾過しつつ養殖池内に戻して循環させながら、養殖池内に飼料を投入して被養殖動物を飼育することを特徴とする。 Furthermore, the terrestrial aquaculture method of the present invention uses the closed type terrestrial aquaculture device of the present invention described above, houses culture water and cultured animals in an aquaculture pond, and uses a main pump to transfer the aquaculture water from the aquaculture pond to a filter tank. The method is characterized in that the organic residues floating in the aquaculture water are filtered and circulated back into the aquaculture pond, and feed is introduced into the aquaculture pond to raise the farmed animals.

本発明において使用可能な酸素含有気体は、例えば空気、酸素ガス、あるいは酸素を周知の酸素濃縮装置等で濃縮した酸素濃化空気などであり、酸素以外の残部は窒素等の不活性ガスで構成するのがよい。なお、酸素含有気体中の酸素濃度は、大気組成に対応する例えば20体積%以上であれば特に限定されない。 The oxygen-containing gas that can be used in the present invention is, for example, air, oxygen gas, or oxygen-enriched air obtained by concentrating oxygen using a well-known oxygen concentrator, etc., and the remainder other than oxygen is composed of an inert gas such as nitrogen. It is better to do so. Note that the oxygen concentration in the oxygen-containing gas is not particularly limited as long as it is, for example, 20% by volume or more, which corresponds to the atmospheric composition.

本発明においては、被養殖物による消費により減少する養殖水中の酸素濃度を酸素溶解機構により補うとともに、養殖水の酸素濃度を飽和値未満である2.5ppm以上7ppm以下に維持する。そして、その養殖水をキャビテーション処理用ポンプにより、キャビテーション処理用配管を通じてキャビテーションノズルに導き、キャビテーション処理部における断面平均流速が8m/sec以上となる規定流量にて流通させることによりキャビテーション処理を行なう。養殖水の酸素濃度をあえて飽和値未満に維持することで、キャビテーションに伴う微細気泡の過剰発生が抑制され、被養殖物のえらに気泡が付着して溶存酸素の取り込みが阻害される等の不具合を効果的に防止することができる。 In the present invention, the oxygen concentration in culture water that decreases due to consumption by the cultivated product is compensated for by an oxygen dissolution mechanism, and the oxygen concentration in culture water is maintained at 2.5 ppm or more and 7 ppm or less, which is less than the saturation value. Then, the culture water is guided by a cavitation treatment pump to a cavitation nozzle through cavitation treatment piping, and is caused to flow at a specified flow rate such that the cross-sectional average flow velocity in the cavitation treatment section is 8 m/sec or more, thereby performing cavitation treatment. By intentionally maintaining the oxygen concentration in the culture water below the saturation value, excessive generation of microbubbles due to cavitation is suppressed, and problems such as bubbles adhering to the gills of the cultured animals inhibiting the uptake of dissolved oxygen. can be effectively prevented.

そして、断面平均流速が8m/sec以上となる規定流量をキャビテーション処理部において確保することで、養殖水の酸素濃度が従来技術よりも低く設定されているにも関わらず、被養殖物の生育促進等は問題なく図ることができる。キャビテーション処理部の流速を上記範囲に確保すれば、ねじ部材の特にねじ谷位置にて微細気泡の発生を伴うキャビテーションが確認できる。しかし、養殖水の酸素濃度が上記のように飽和値未満になっていると、キャビテーションによる強制的な減圧過飽和析出により発生した気泡(特に100nm以上の気泡径を有するもの)は、ノズルを通過して養殖池に戻された時点で再溶解が速やかに進み、周知の気泡径測定手法(例えば、レーザー散乱式粒度計を用いるもの)では、数分後には大半が観測不能となることが判明している。 By ensuring a specified flow rate with a cross-sectional average flow velocity of 8 m/sec or more in the cavitation treatment section, the growth of cultivated products is promoted even though the oxygen concentration of the aquaculture water is set lower than in conventional technology. etc. can be achieved without any problem. If the flow velocity of the cavitation treatment section is maintained within the above range, cavitation accompanied by the generation of microbubbles can be confirmed particularly at the thread root position of the threaded member. However, if the oxygen concentration of the culture water is below the saturation value as mentioned above, the bubbles (especially those with a bubble diameter of 100 nm or more) generated by forced vacuum supersaturated precipitation due to cavitation will not pass through the nozzle. It has been found that re-dissolution occurs rapidly when the particles are returned to the aquaculture pond, and most of them become unobservable after a few minutes using well-known bubble diameter measurement methods (for example, those using a laser scattering particle size meter). ing.

このような養殖水を使用すれば、被養殖物のえらに微細気泡を付着しにくくできることは明確である。しかし、養殖水の酸素濃度の絶対値を低下させれば、被養殖物の活動活性が大幅に損なわれる懸念も一方では生ずる。しかし、本発明者らが詳細に検討した結果、酸素濃度を上記の範囲に抑制した養殖水をキャビテーション処理すると、より酸素濃度の高い通常養殖水(キャビテーション処理を行わない養殖)と比較して、これと同等以上に被養殖物の活動及び成長活性が高められ、酸欠特有の疲弊もほとんど認められないことが判明したのである。 It is clear that if such aquaculture water is used, it is possible to make it difficult for microbubbles to adhere to the gills of the cultivated animals. However, if the absolute value of oxygen concentration in the culture water is lowered, there is a concern that the activity of the cultured animals will be significantly impaired. However, as a result of detailed study by the present inventors, when culture water with oxygen concentration suppressed to the above range is subjected to cavitation treatment, compared to normal culture water with higher oxygen concentration (aquaculture without cavitation treatment), It was found that the activity and growth activity of the cultivated animals were increased to a greater extent than this, and that the fatigue peculiar to oxygen deficiency was hardly observed.

その詳細な機構は不明であるが、現時点では有効な観察手段が見いだされていない、10nm未満のキャビテーション処理特有の超微細な生成物が関与し、溶存酸素を含有する水の生体組織への浸透性が著しく改善されている可能性がある。例えば水道水等をキャビテーション処理して得られる浸透性等の改善効果は、キャビテーション処理後1日程度を経ても大きく変化しないことから、該生成物は、一定時間は水中に持続的に存在しうる形態を有するとも考えられる。 The detailed mechanism is unknown, but ultrafine products of less than 10 nm, which are unique to cavitation processing, are involved, and no effective observation means have been found at this time, and water containing dissolved oxygen penetrates into living tissues. performance may have been significantly improved. For example, the effect of improving permeability obtained by cavitating tap water, etc. does not change significantly even after about one day after the cavitation treatment, so the product can exist continuously in water for a certain period of time. It is also considered to have a form.

また、100nm以上の酸素気泡が再溶解により寸法縮小する場合も、最終的には完全に気泡が溶解消滅するのではなく、上記のような生成物を水中に残留させる可能性が高い。例えば、非特許文献1には、外気と水とを旋回流により気液混合したナノバブル水を凍結し超高圧電子顕微鏡で観察した結果、平均径が7nm前後の気泡らしき生成物が大量に存在することが報告されている。観察された生成物の組成や、気泡であるか否かなどについては明らかでなく、また、本件発明の作用効果との因果関係も不明であるが、微細な核生成を起点として気泡を析出させるキャビテーション処理水の場合、同様の微細な生成物がさらに高密度に観察される可能性が高いと思われる。該生成物は、酸素ガスを主体にするものであったとしても、極度に微小化した気泡の表面張力が相当高圧になると推測される点に鑑みれば、酸素と水との固体系化合物(ハイドレート等)である可能性もある。 Further, even when oxygen bubbles of 100 nm or more are reduced in size due to redissolution, there is a high possibility that the bubbles will not completely dissolve and disappear in the end, but that the above-mentioned products will remain in the water. For example, in Non-Patent Document 1, as a result of freezing nanobubble water, which is a gas-liquid mixture of outside air and water using a swirling flow, and observing it with an ultra-high-pressure electron microscope, it was found that a large amount of bubble-like products with an average diameter of around 7 nm were present. It has been reported that. Although the composition of the observed product and whether or not it is a bubble is unclear, and the causal relationship with the action and effect of the present invention is also unclear, bubbles are precipitated starting from fine nucleation. In the case of cavitation-treated water, it seems likely that similar fine products would be observed at even higher densities. Even if the product is mainly composed of oxygen gas, considering that the surface tension of extremely small bubbles is assumed to be quite high, it is likely that the product is a solid compound of oxygen and water (hydrocarbons). rate, etc.).

いずれにしても、キャビテーション処理した養殖水と通常の養殖水との間で被養殖物の活動及び成長活性に著しい差を生ずることは実験的には明らかとなった。溶存酸素の吸収を媒介する水そのものの浸透性(例えば、水生生物のえら等の溶存酸素の吸収器官における毛細血管への浸透性)が改善されていれば、酸素濃度が多少低い水であっても、限られた量の溶存酸素を被養殖物が効率よく吸収し、被養殖物が活動及び成長活性を良好に維持できるようになる、との推測も成り立つ。 In any case, it has been experimentally revealed that there is a significant difference in the activity and growth activity of cultured animals between cavitation-treated culture water and normal culture water. If the permeability of the water itself, which mediates the absorption of dissolved oxygen (for example, the permeability to the capillaries in the dissolved oxygen absorbing organs such as the gills of aquatic organisms), is improved, even water with a somewhat low oxygen concentration can be used. It is also conjectured that the cultured products can efficiently absorb a limited amount of dissolved oxygen, allowing the cultured products to maintain good activity and growth activity.

養殖水の酸素濃度が2.5ppm未満であると、キャビテーション処理による酸素吸収効率の向上を考慮しても、被養殖物の酸素吸収量が不足し、活動活性の低下、生育不良等の不具合につながり、養殖継続に伴う費養殖物の死滅率の増大を招きやすくなる。一方、養殖水の酸素濃度が7ppmを超えるとキャビテーション処理に伴う気泡(特に気泡径100nm以上のもの)の過剰発生が生じやすくなり、被養殖物の活動活性が却って低下しやすくなる。酸素溶解機構により養殖水に酸素含有気体を供給しつつ溶解させる場合、養殖水の酸素濃度は、より望ましくは3ppm以上6ppm以下に維持するのがよい。 If the oxygen concentration in the culture water is less than 2.5 ppm, even if the improvement in oxygen absorption efficiency through cavitation treatment is taken into consideration, the amount of oxygen absorbed by the cultured product will be insufficient, resulting in problems such as decreased activity and poor growth. This can lead to an increase in the mortality rate of farmed products as a result of continued aquaculture. On the other hand, if the oxygen concentration of the culture water exceeds 7 ppm, excessive generation of bubbles (especially bubbles with a diameter of 100 nm or more) is likely to occur due to cavitation treatment, and the activity of the cultured product is likely to decrease. When dissolving oxygen-containing gas while supplying it to culture water using an oxygen dissolution mechanism, the oxygen concentration of the culture water is more desirably maintained at 3 ppm or more and 6 ppm or less.

キャビテーション処理部における断面平均流速が8m/sec未満になるとキャビテーション処理により達成される効果が不足し、上記のように養殖水を低酸素化しても被養殖物の活動活性を維持できる効果が顕著でなくなる。特に、被養殖物の飼育密度が高く設定されている等の要因により、養殖水の酸素濃度が例えば3.5ppm以下に低下している状態にて断面平均流速が上記下限値を下回ることは、被養殖物の酸欠による衰弱や死滅を特に招きやすくなる。キャビテーション処理部における断面平均流速は、より望ましくは9m/sec以上確保されているのがよい。 If the cross-sectional average flow velocity in the cavitation treatment section is less than 8 m/sec, the effect achieved by cavitation treatment will be insufficient, and as mentioned above, even if the culture water is made low in oxygen, the effect of maintaining the activity of the cultured animals will be significant. It disappears. In particular, if the cross-sectional average flow velocity falls below the above-mentioned lower limit when the oxygen concentration of the aquaculture water has decreased to, for example, 3.5 ppm or less due to factors such as the breeding density of the aquaculture target being set high, Cultivated animals are particularly susceptible to weakening and death due to lack of oxygen. More preferably, the cross-sectional average flow velocity in the cavitation treatment section is maintained at 9 m/sec or more.

キャビテーションノズルは、ノズル流路が円形断面を有するものとして形成され、各キャビテーション処理部にはねじ部材として、ねじピッチ及びねじ谷深さが0.20mm以上0.40mm以下、公称ねじ径Mが1.0mm以上2.0mm以下のねじ部材が複数配置されるとともに、ノズル流路の中心軸線と直交する平面への投影にてノズル流路の断面中心から該ノズル流路の半径の70%以内の領域に位置する谷点の全ねじ配置面間で合計した総数を、ノズル流路の断面積で除した70%谷点面積密度と定義したとき、70%谷点面積密度の値が1.6個/mm以上に確保されたものを使用することが望ましい。 The cavitation nozzle is formed so that the nozzle flow path has a circular cross section, and each cavitation treatment section has a threaded member with a thread pitch and thread depth of 0.20 mm or more and 0.40 mm or less, and a nominal thread diameter M of 1. A plurality of threaded members with a diameter of .0 mm or more and 2.0 mm or less are arranged, and a screw member within 70% of the radius of the nozzle flow path from the cross-sectional center of the nozzle flow path when projected onto a plane perpendicular to the central axis of the nozzle flow path. When defined as the 70% valley point areal density, which is the total number of valley points located in the area divided by the cross-sectional area of the nozzle flow path, the value of the 70% valley point areal density is 1.6. It is desirable to use a material with a density of at least 2.0 mm/mm 2 or more.

70%谷点面積密度の値が1.6個/mm未満のキャビテーションノズルを使用した場合、キャビテーション処理効果が不足し、養殖水を低酸素化しても被養殖物の活動活性を維持できる効果が顕著でなくなる場合がある。キャビテーションノズルの70%谷点面積密度の値の上限に特に上限に制限はないが、キャビテーション処理部におけるねじ配置数の極度の増加に伴う圧損増大ひいては流速不足を招かない範囲で適宜設定できる(例えば、5個/mm)。70%谷点面積密度の値は、より望ましくは2.0個/mm以上に確保されているのがよい。 If a cavitation nozzle with a 70% valley point area density value of less than 1.6 pieces/ mm2 is used, the cavitation treatment effect will be insufficient, and the activity of cultured animals can be maintained even if the culture water is made hypoxic. may become less noticeable. There is no particular upper limit to the value of the 70% valley point areal density of the cavitation nozzle, but it can be set as appropriate within a range that does not cause an increase in pressure loss or insufficient flow rate due to an extreme increase in the number of screws arranged in the cavitation treatment section (for example, , 5 pieces/mm 2 ). The value of the 70% valley point area density is more desirably 2.0 pieces/mm 2 or more.

上記構成のキャビテーションノズルを使用する場合、キャビテーションノズルに対する養殖水の規定流量は、養殖池の貯水量をV1、キャビテーションノズルの1時間当たりの流通流量をV2としたとき、
K=V2/V1×100 (%)
にて表される流通循環比Kが2%以下となるように調整するのがよい。100nm以上のやや粗大な気泡がキャビテーションノズルにて発生した場合も、1時間当たりの養殖水の流通流量(規定流量)を、養殖池内の養殖水全体積の2%以下にとどめることで、上記粗大な気泡の再溶解を促進でき、被養殖物のえら等への付着による前述の不具合をさらに効果的に抑制できる。そして、養殖水全体積に対するキャビテーションノズルの流通循環比Kが極めて小さい値であるにも関わらず、上記構成のキャビテーションノズルを採用することで、被養殖物の活動及び成長活性を極めて良好に維持することが可能となる。なお、流通循環比Kが極度に小さくなりすぎると、被養殖物の活動及び成長活性を改善する効果が不十分となる。流通循環比Kの下限値は、キャビテーションノズルの70%谷点面積密度や設定流速により異なるが、例えば上記効果が損なわれないよう、例えば0.5%以上の値に確保するのがよい。
When using the cavitation nozzle with the above configuration, the specified flow rate of aquaculture water to the cavitation nozzle is as follows:
K=V2/V1×100 (%)
It is preferable to adjust so that the circulation ratio K expressed by is 2% or less. Even if somewhat coarse air bubbles of 100 nm or more are generated in the cavitation nozzle, the flow rate of culture water per hour (regulated flow rate) can be kept to 2% or less of the total volume of culture water in the culture pond. The re-dissolution of air bubbles can be promoted, and the above-mentioned problems caused by adhesion to the gills, etc. of cultured objects can be further effectively suppressed. Even though the circulation ratio K of the cavitation nozzle to the total volume of aquaculture water is an extremely small value, by adopting the cavitation nozzle with the above configuration, the activity and growth activity of the cultivated product can be maintained extremely well. becomes possible. Note that if the circulation ratio K becomes extremely small, the effect of improving the activity and growth activity of the cultivated product will be insufficient. The lower limit value of the flow circulation ratio K varies depending on the 70% valley point area density of the cavitation nozzle and the set flow rate, but it is preferably set to a value of 0.5% or more, for example, so as not to impair the above effects.

酸素溶解機構は、キャビテーションノズルにて酸素含有気体を溶解するために、キャビテーションノズルに酸素含有気体と養殖水との混相流を供給する混相流供給部を備えるものとして構成できる。本発明にて使用するキャビテーションノズルは、養殖水がねじ部材に衝突してその下流に迂回する際に、ねじ谷内にて絞られることにより増速してキャビテーションを起こすので、養殖水の溶存ガス成分は負圧により過飽和となり、気泡を析出しつつ養殖水を激しく撹拌し乱流域を生ずる。このとき、乱流域に供給する養殖水に気相(気体)を混合して混相流となすことで、上記攪拌により気液混合・攪拌が進行し、気相成分(酸素含有気体)の養殖水への溶解を効果的に進行させることができる。 The oxygen dissolution mechanism can be configured to include a multiphase flow supply section that supplies a multiphase flow of oxygen-containing gas and culture water to the cavitation nozzle in order to dissolve the oxygen-containing gas in the cavitation nozzle. In the cavitation nozzle used in the present invention, when the aquaculture water collides with the threaded member and detours downstream, it is squeezed in the thread valley, increasing the speed and causing cavitation, so that the dissolved gas components of the aquaculture water are becomes supersaturated due to negative pressure, and while bubbles are precipitated, the culture water is violently agitated, creating a turbulent region. At this time, by mixing the gas phase (gas) with the aquaculture water supplied to the turbulent area to create a multiphase flow, gas-liquid mixing and agitation progresses due to the above stirring, and the gas phase components (oxygen-containing gas) are absorbed into the aquaculture water. The dissolution can proceed effectively.

この場合、混相流がねじ部材に衝突する際に、ねじ谷の内側空間の全体が大きな気泡で覆われてしまうと、溶存気体を含有した養殖水とねじ谷との接触効率が下がり、キャビテーション効率の大幅な低下につながる(つまり、そのねじ谷は、キャビテーションポイントとして有効なねじ谷としての機能を失う)。その結果、気相成分の混合・攪拌の駆動力を生ずる乱流域の形成が顕著でなくなり、気体溶解効率が低下することにつながる。 In this case, when the multiphase flow collides with the threaded member, if the entire inner space of the thread valley is covered with large bubbles, the contact efficiency between the culture water containing dissolved gas and the thread valley decreases, resulting in cavitation efficiency. (i.e., the thread valley loses its function as an effective thread valley as a cavitation point). As a result, the formation of a turbulent region that generates the driving force for mixing and stirring gas phase components becomes less pronounced, leading to a decrease in gas dissolution efficiency.

そこで、一端に流入口、他端に流出口が形成される中空の外筒部材と、外筒部材の内側に設けられ、流入口と流出口とをつなぐ螺旋状流路を、該螺旋状流路の螺旋軸線が外筒部材の中心軸線に沿うように形成する流路形成部材とを備え、螺旋状流路がキャビテーションノズルのノズル流路に連通するように、キャビテーションノズルの養殖水入口側に設けられる気液ミキサーを設けることができ、混相流供給部は、気液ミキサーの流入口に混相流を供給するものとして構成できる。これにより、混相流は気液ミキサーの螺旋状流路内を流通させることにより、強制的に生ずる螺旋流の遠心力により気相と液相との攪拌・混合が進むので、気相は細かい気泡に粉砕された状態でキャビテーションノズルのねじ部材に供給される。これにより、養殖水とねじ谷との接触効率が上昇し、気体溶解効率を高めることができる。 Therefore, a hollow outer cylindrical member having an inlet at one end and an outlet at the other end, and a spiral flow path provided inside the outer cylindrical member that connects the inlet and the outlet are used for the spiral flow. a channel forming member formed such that the spiral axis of the channel is along the central axis of the outer cylinder member, and a channel forming member formed on the culture water inlet side of the cavitation nozzle so that the spiral channel communicates with the nozzle channel of the cavitation nozzle. A gas-liquid mixer can be provided, and the multiphase flow supply section can be configured to supply the multiphase flow to the inlet of the gas-liquid mixer. As a result, the multiphase flow is passed through the spiral flow path of the gas-liquid mixer, and the centrifugal force of the forcedly generated spiral flow promotes stirring and mixing of the gas and liquid phases, so the gas phase is made up of fine bubbles. It is supplied to the threaded member of the cavitation nozzle in a crushed state. Thereby, the contact efficiency between the culture water and the screw valley can be increased, and the gas dissolution efficiency can be increased.

気液ミキサーは、ねじ部材のねじピッチをh(mm)として気泡を、1.5h以下の気泡径に微粉砕するように構成することが望ましい。気液ミキサーでの微粉砕により得られる気泡径が1.5hを超えると、気体溶解効率の改善効果が顕著でなくなる場合がある。該気泡径は、より望ましくは1.0h以下であるのがよい。また、該気泡径の下限値に制限はないが、螺旋状流路を有した気液ミキサーによる混合攪拌の場合、0.2h程度が粉砕の限界となる場合もあり得る。 The gas-liquid mixer is desirably configured to finely pulverize bubbles to a bubble diameter of 1.5 h or less, with the thread pitch of the screw member being h (mm). If the diameter of the bubbles obtained by pulverization in the gas-liquid mixer exceeds 1.5 hours, the effect of improving gas dissolution efficiency may not be significant. The bubble diameter is more preferably 1.0 h or less. Further, there is no limit to the lower limit of the bubble diameter, but in the case of mixing and stirring using a gas-liquid mixer having a spiral flow path, about 0.2 hours may be the limit for pulverization.

気液ミキサーの流路形成部材は、帯状の金属板の幅方向の中心軸線を螺旋軸線とする形で該金属板をねじり加工したねじり板部材として構成できる。このようなねじり板部材を用いることで、気液ミキサーの螺旋状流路を簡単かつ安価に形成することができる。また、該ねじり板部材を用いることで螺旋状流路は、ねじり板部材の第一主面と外筒部材の円筒状の内周面との間の空間がなす第一螺旋状流路と、ねじり板部材の第二主面と外筒部材の円筒状の内周面との間の空間がなす第二螺旋状流路とからなるものとして構成できる。これにより、ねじり板部材の両側に、回転位相の異なる螺旋流を2系統形成でき、気相の粉砕効率を簡単な構造によりさらに向上できる。 The flow path forming member of the gas-liquid mixer can be configured as a twisted plate member obtained by twisting a band-shaped metal plate so that the central axis in the width direction of the metal plate is the helical axis. By using such a twisted plate member, the spiral flow path of the gas-liquid mixer can be easily and inexpensively formed. Further, by using the twisted plate member, the spiral flow path is formed by a first spiral flow path formed by a space between the first main surface of the twisted plate member and the cylindrical inner peripheral surface of the outer cylinder member, It can be configured to include a second spiral flow path formed by a space between the second main surface of the torsion plate member and the cylindrical inner circumferential surface of the outer cylinder member. Thereby, two systems of spiral flows having different rotational phases can be formed on both sides of the torsion plate member, and the gas phase crushing efficiency can be further improved with a simple structure.

外筒部材は、螺旋流路が1周期以上の螺旋区間を含むように全長が定められているのがよい。螺旋流路に含まれる螺旋区間が1周期未満であると、気液ミキサーの気相粉砕効率が低下し、下流側のキャビテーションノズルにおける気体溶解効率が不十分となる場合がある。外筒部材は、よりのぞましくは、螺旋流路が1.5周期以上、より望ましくは2周期以上の螺旋区間を含むように全長が定められているのがよい。 It is preferable that the total length of the outer cylinder member is determined so that the spiral flow path includes a spiral section of one period or more. If the spiral section included in the spiral flow path is less than one cycle, the gas phase pulverization efficiency of the gas-liquid mixer may decrease, and the gas dissolution efficiency in the cavitation nozzle on the downstream side may become insufficient. More preferably, the total length of the outer cylindrical member is determined such that the helical flow path includes a helical section of 1.5 cycles or more, more preferably 2 cycles or more.

また、外筒部材の円筒状の内周面の内径をDx(mm)、ねじり板部材の螺旋周期長をλ(mm)として、λ/Dxの値は1.5以上4以下に設定されているのがよい。λ/Dxの値が4を超えると、気液ミキサーの気相粉砕効率を確保するために必要な螺旋流路の周期数を確保する際に、外筒部材の全長が大きくなりすぎる不具合を招く場合がある。また、λ/Dxの値が1.5未満であると、ねじり板部材が形成する螺旋流路の流通抵抗が大きくなりすぎ、気液ミキサーの気相粉砕効率が低下して、下流側のキャビテーションノズルにおける気体溶解効率が不十分となる場合がある。 Further, the value of λ/Dx is set to 1.5 or more and 4 or less, where the inner diameter of the cylindrical inner peripheral surface of the outer cylinder member is Dx (mm), and the helical period length of the torsion plate member is λ (mm). It's good to be there. If the value of λ/Dx exceeds 4, the total length of the outer cylindrical member becomes too large, causing a problem when securing the number of cycles of the spiral flow path necessary to ensure the gas phase pulverization efficiency of the gas-liquid mixer. There are cases. In addition, if the value of λ/Dx is less than 1.5, the flow resistance of the spiral flow path formed by the twisted plate member becomes too large, the gas-phase pulverization efficiency of the gas-liquid mixer decreases, and cavitation occurs on the downstream side. Gas dissolution efficiency in the nozzle may be insufficient.

養殖水の被養殖物の活動及び成長活性を高める効果は、酸素を含有した養殖水を、キャビテーションノズルを通過させることにより、酸素の溶解プロセスとは無関係に達成できる。よって、酸素溶解機構は、キャビテーションノズルとは別に設けられ、養殖池を満たす養殖水に外部から供給される酸素含有気体を平均気泡径が0.5mm以上となるように噴射する周知の散気部を備えるものとして構成することもできる。ここで、被養殖物のえら等への付着による悪影響が懸念されるのは、100nm~30μm程度の微細な気泡であり、周知の散気部はこうした気泡が発生しにくい点においては有利である。ただし、酸素溶解効率はキャビテーションノズルに劣るので、キャビテーションノズルによる酸素溶解と併用することが望ましいともいえる。養殖水全体積に対するキャビテーションノズルの流通循環比Kが上記のように小さい場合は、キャビテーションノズルの酸素溶解能力のみでは所望の酸素濃度を維持できないこともありえる。この観点においても、散気部による酸素溶解とキャビテーションノズルによる酸素溶解とは併用することが望ましい。 The effect of increasing the activity and growth activity of the cultured animals in the culture water can be achieved independently of the oxygen dissolution process by passing the oxygen-containing culture water through a cavitation nozzle. Therefore, the oxygen dissolution mechanism is provided separately from the cavitation nozzle, and includes a well-known air diffuser that injects oxygen-containing gas supplied from the outside into the aquaculture water filling the aquaculture pond so that the average bubble diameter is 0.5 mm or more. It can also be configured as having the following. Here, it is the fine air bubbles of about 100 nm to 30 μm that may have an adverse effect due to adhesion to the gills of the cultivated product, and the well-known air diffuser is advantageous in that such air bubbles are less likely to occur. . However, since the oxygen dissolution efficiency is inferior to that of a cavitation nozzle, it can be said that it is desirable to use it in combination with oxygen dissolution using a cavitation nozzle. When the flow/circulation ratio K of the cavitation nozzle to the total volume of the culture water is small as described above, the desired oxygen concentration may not be maintained by the oxygen dissolving ability of the cavitation nozzle alone. From this point of view as well, it is desirable to use the oxygen dissolution by the aeration section and the oxygen dissolution by the cavitation nozzle in combination.

この場合、散気部による養殖水への酸素含有気体の供給流量をキャビテーションノズルへの酸素含有気体の供給流量よりも大きく設定するとさらによい。キャビテーションノズルへの酸素含有気体の供給流量を低くとどめることで、養殖池中の前述の微細気泡の存在密度を低減でき、被養殖物のえら等への付着による悪影響をさらに効果的に抑制できる。 In this case, it is more preferable to set the flow rate of the oxygen-containing gas supplied to the culture water by the aeration section to be larger than the flow rate of the oxygen-containing gas supplied to the cavitation nozzle. By keeping the flow rate of the oxygen-containing gas supplied to the cavitation nozzle low, it is possible to reduce the density of the above-mentioned microbubbles in the aquaculture pond, and it is possible to more effectively suppress the adverse effects caused by adhesion to the gills, etc. of the aquaculture products.

次に、キャビテーションノズルは、ノズルの狭小な絞り孔を水が通過する際に生ずる減圧沸騰効果を利用して微細気泡を発生させる原理上、被処理水の絞り孔における流速を10m/秒以上程度以上の高速に確保する必要がある。しかし、このキャビテーションノズルを上記のように濾過槽との循環経路に配置した場合、濾過槽への有機残渣の堆積により循環経路への養殖水の流通抵抗が増加すると、キャビテーションノズルを通過する養殖水の流速が不足し、キャビテーションによる微細気泡の発生量が不十分となる問題がある。この場合、キャビテーション処理用の循環経路を別に設けたとしても、養殖水がノズルに直接吸い込まれると、浮遊する有機残渣が絞り孔に詰まり微細気泡の発生は同様に阻害される。よって、これを防止するために、循環経路の養殖池側の入り口には結局のところ新たな濾過部を設けざるを得ないので、何ら問題の解決には至らないのである。 Next, cavitation nozzles generate fine bubbles by utilizing the reduced pressure boiling effect that occurs when water passes through the narrow aperture of the nozzle, so the flow rate of the water to be treated through the aperture is approximately 10 m/sec or more. It is necessary to secure a higher speed than that. However, when this cavitation nozzle is placed in the circulation path with the filtration tank as described above, if the flow resistance of the aquaculture water to the circulation path increases due to the accumulation of organic residue in the filtration tank, the aquaculture water passing through the cavitation nozzle may There is a problem that the flow rate is insufficient and the amount of microbubbles generated by cavitation is insufficient. In this case, even if a separate circulation path for cavitation treatment is provided, if the culture water is directly sucked into the nozzle, floating organic residues will clog the orifice and the generation of microbubbles will be similarly inhibited. Therefore, in order to prevent this, a new filtration part has to be installed at the entrance of the circulation path on the aquaculture pond side, so this does not solve the problem at all.

これを解決するためには、キャビテーション処理用配管の流入口に設けられ、養殖池内の浮遊物がキャビテーション処理用配管内に流入することを抑制するキャビテーション処理用濾過部と、キャビテーション処理用配管内を流通する養殖水の流量を検出する流量検出部と、キャビテーション処理用濾過部への浮遊物の堆積に伴う流量損失を補う形で、キャビテーション処理用ポンプによるキャビテーションノズルへの送液流量を規定流量に制御するキャビテーション流量制御部とを、本発明の装置にさらに付加することが望ましい。キャビテーション処理用配管の流量を流量検出部にモニタリングし、キャビテーション処理用濾過部へ浮遊物が堆積した場合に、キャビテーションノズルへの送液流量を上記規定範囲となるように補うキャビテーション流量制御部を設けることで、濾過部に有機残渣が堆積し流通抵抗が増加した場合でも、被養殖物に対する前記有利な効果は安定に維持できるようになる。 In order to solve this problem, a cavitation treatment filtration part is installed at the inlet of the cavitation treatment piping to prevent floating matter in the aquaculture pond from flowing into the cavitation treatment piping, and a The flow rate detection unit detects the flow rate of circulating aquaculture water, and the flow rate of liquid sent to the cavitation nozzle by the cavitation treatment pump is adjusted to the specified flow rate in order to compensate for the flow loss due to the accumulation of suspended matter in the cavitation treatment filtration unit. It is desirable to further add a cavitation flow rate control section to the apparatus of the present invention. A cavitation flow rate control unit is provided that monitors the flow rate of the cavitation treatment piping using a flow rate detection unit and compensates for the flow rate of liquid sent to the cavitation nozzle so that it falls within the above specified range when suspended matter accumulates in the cavitation treatment filtration unit. This makes it possible to stably maintain the advantageous effects on the cultivated product even when organic residue accumulates in the filtration section and flow resistance increases.

ここで、主ポンプとキャビテーション処理用ポンプとは別の構成としてもよいし、主ポンプをキャビテーション処理用ポンプに兼用させることもできる。また、キャビテーション処理用濾過部についても濾過槽と別に設けてもよいし、両者を兼用させる構成としてもよい。 Here, the main pump and the cavitation treatment pump may be configured separately, or the main pump may also be used as the cavitation treatment pump. Furthermore, the cavitation treatment filtration section may be provided separately from the filtration tank, or may be configured to serve as both.

例えば、次のような構成を採用することが可能である。すなわち、該構成では、濾過槽に養殖水の流入口が連通するとともに、他端側が養殖水の養殖池への戻し口とされた濾過用主配管と、濾過用主配管の流入口に設けられ、濾過槽内の浮遊物が濾過用主配管内に流入することを抑制する補助フィルタリング部とを備え、主ポンプが濾過用主配管上に設けられる。また、キャビテーション処理用配管は、主ポンプの下流側にて濾過用主配管から分岐し、かつ、濾過用主配管とは別位置にて養殖池に対する戻し口を開口させる形で設けられる。そして、濾過用主配管とキャビテーション処理用配管との分配比をバルブ開度に応じて調整する分配バルブが設けられる。キャビテーション流量制御部は、補助フィルタリング部への浮遊物の堆積に伴い主ポンプの送水流量が減少した場合に、養殖水のキャビテーション処理用配管への分配比が増加するように分配バルブの開度を調整制御するよう構成される。上記の構成では、主ポンプがキャビテーション処理用ポンプに、補助フィルタリング部がキャビテーション処理用濾過部にそれぞれ兼用されることとなり、装置構成の大幅な簡略化が実現されるとともに、主ポンプの出力制御をせずとも分配バルブの開度によりキャビテーション処理用配管の流量を規定範囲に安定的に保持することができる。 For example, it is possible to adopt the following configuration. That is, in this configuration, the inlet of the aquaculture water communicates with the filtration tank, and the main filtration pipe whose other end is the return port of the aquaculture water to the aquaculture pond, and the inlet of the main filtration pipe are provided. , and an auxiliary filtering section that suppresses floating matter in the filtration tank from flowing into the main filtration pipe, and the main pump is provided on the main filtration pipe. Further, the cavitation treatment pipe is provided in such a manner that it branches from the main filtration pipe on the downstream side of the main pump, and opens a return port to the aquaculture pond at a position different from the main filtration pipe. A distribution valve is provided that adjusts the distribution ratio between the main pipe for filtration and the pipe for cavitation treatment according to the valve opening degree. The cavitation flow rate control unit controls the opening degree of the distribution valve to increase the distribution ratio of aquaculture water to the cavitation treatment piping when the water flow rate of the main pump decreases due to accumulation of suspended matter in the auxiliary filtering unit. configured to coordinate control. In the above configuration, the main pump is also used as a cavitation treatment pump, and the auxiliary filtering section is also used as a cavitation treatment filtration section, which greatly simplifies the device configuration and controls the output of the main pump. Even without this, the flow rate of the cavitation treatment piping can be stably maintained within a specified range by adjusting the opening degree of the distribution valve.

本発明の作用及び効果の詳細については、「課題を解決するための手段」の欄にすでに記載したので、ここでは繰り返さない。 The details of the operation and effects of the present invention have already been described in the "Means for Solving the Problems" section, so they will not be repeated here.

本発明の閉鎖型陸上養殖装置の一例を示す概念図。FIG. 1 is a conceptual diagram showing an example of a closed land aquaculture apparatus of the present invention. 図1Aの閉鎖型陸上養殖装置に使用する気液ミキサーの一例を示す横断面図及び側面。A cross-sectional view and a side view showing an example of a gas-liquid mixer used in the closed land aquaculture device of FIG. 1A. 図1Aの閉鎖型陸上養殖装置に使用するキャビテーションノズルの一例を示す横断面図。FIG. 1B is a cross-sectional view showing an example of a cavitation nozzle used in the closed land aquaculture apparatus shown in FIG. 1A. 図1Cのキャビテーションノズルの各ねじ配置面におけるねじ部材レイアウトを示す軸断面図。FIG. 1C is an axial sectional view showing the screw member layout on each screw arrangement surface of the cavitation nozzle of FIG. 1C. 図2の要部を拡大して示す軸断面図。FIG. 3 is an axial sectional view showing an enlarged main part of FIG. 2; 図1Cのキャビテーションノズルにおいて、図2のレイアウトの面ねじ組を中心軸線方向に4組配置したキャビテーションノズルの要部横断面図。FIG. 1C is a cross-sectional view of a main part of the cavitation nozzle in which four sets of plane threads having the layout shown in FIG. 2 are arranged in the central axis direction. 同じく8組配置したキャビテーションノズルの要部横断面図。FIG. 6 is a cross-sectional view of the main parts of eight cavitation nozzles arranged in the same manner. 図1Cのキャビテーションノズルにおいて、一方の面ねじ組を45°回転させた構造を示す要部横断面図。FIG. 1C is a cross-sectional view of a main part of the cavitation nozzle shown in FIG. 1C, showing a structure in which one surface screw set is rotated by 45 degrees. 図1Cのキャビテーションノズルにおいて、一方の面ねじ組を図6のレイアウトとしたキャビテーションノズルの要部横断面図。FIG. 7 is a cross-sectional view of a main part of the cavitation nozzle shown in FIG. 1C, in which one surface screw set has the layout shown in FIG. 6; 図7の構造において、面ねじ組を互いに直交するねじ部材対に分割し、それぞれ中心軸線方向に位置をずらせて配置したキャビテーションノズルの要部横断面図。FIG. 8 is a cross-sectional view of a main part of the cavitation nozzle in which the surface screw set is divided into mutually orthogonal screw member pairs, and the respective positions are shifted in the central axis direction in the structure of FIG. 7 . 図7のキャビテーションノズルと同様の面ねじ組の対を中心軸線方向に2組配置したキャビテーションノズルの要部横断面図。FIG. 8 is a cross-sectional view of a main part of a cavitation nozzle in which two pairs of plane screw sets similar to the cavitation nozzle of FIG. 7 are arranged in the central axis direction. 図1Aの閉鎖型陸上養殖装置の気液ミキサーにベンチュリエジェクタを接続した状態を示す横断面図。FIG. 2 is a cross-sectional view showing a state in which a venturi ejector is connected to the gas-liquid mixer of the closed land aquaculture apparatus of FIG. 1A. キャビテーション流量制御部の電気的構成の一例を示すブロック図。FIG. 3 is a block diagram showing an example of an electrical configuration of a cavitation flow rate control section. 流量制御プログラムの処理の流れを示すフローチャート。5 is a flowchart showing the flow of processing of a flow rate control program. 酸素濃度制御プログラムの処理の流れを示すフローチャート。5 is a flowchart showing the flow of processing of an oxygen concentration control program. 2孔型のキャビテーションノズルの要部軸断面図。FIG. 2 is an axial sectional view of the main parts of a two-hole cavitation nozzle. 実験例に使用したキャビテーションノズルの各部の寸法関係を説明する図。The figure explaining the dimensional relationship of each part of the cavitation nozzle used in the experimental example. 分配バルブの変形例を示す模式図。FIG. 7 is a schematic diagram showing a modification of the distribution valve. 図1Aの閉鎖型陸上養殖装置の変形例を示す概念図。The conceptual diagram which shows the modification of the closed land aquaculture apparatus of FIG. 1A.

以下、本発明の実施の形態を添付の図面に基づき説明する。
図1Aは、本発明の一実施形態をなす閉鎖型陸上養殖装置の一例を使用形態とともに示す概念図である。閉鎖型陸上養殖装置300は、養殖池250内に養殖水Wと甲殻類又は魚類からなる被養殖物SPとを収容し、主ポンプ175を用いて養殖池250から養殖水Wを濾過槽252に導き、養殖水W中に浮遊する有機残渣を濾過しつつ養殖池250内に戻して循環させながら、養殖池250内に飼料を投入して被養殖物SPを飼育するためのものである。
Embodiments of the present invention will be described below with reference to the accompanying drawings.
FIG. 1A is a conceptual diagram showing an example of a closed-type land-based aquaculture device, which is an embodiment of the present invention, along with a usage pattern. The closed land aquaculture device 300 accommodates aquaculture water W and a cultured product SP consisting of crustaceans or fish in an aquaculture pond 250, and uses a main pump 175 to transfer the aquaculture water W from the aquaculture pond 250 to a filter tank 252. This is for raising a cultured product SP by introducing feed into the aquaculture pond 250 while filtering the organic residue floating in the aquaculture water W and circulating it back into the aquaculture pond 250.

被養殖物SPは本実施形態ではエビであるが、カニ等の他の甲殻類であってもよい。また、甲殻類以外ではマダイ、マグロ、ブリ、マス、サーモン、フグ及びコイなどの魚類であってもよい。また、被養殖物SPをエビとする場合のエビの種別は、例えばクルマエビ科に属するエビであり、クルマエビ、バナメイエビ、ウシエビ(通称:ブラックタイガーエビ)、クマエビ及びコウライエビ(通称:タイショウエビ)などから選択されるものである。また、養殖水Wは被養殖物の種別に応じ、海水(塩分濃度:3.0~4.0質量%)、汽水(塩分濃度:0.05~3.0質量%)及び淡水のなかから適宜選択される。 Although the cultivated product SP is shrimp in this embodiment, it may be other crustaceans such as crabs. Furthermore, other than crustaceans, fish such as red sea bream, tuna, yellowtail, trout, salmon, pufferfish, and carp may be used. In addition, when the cultivated product SP is shrimp, the type of shrimp is, for example, a shrimp belonging to the family Prawnidae, such as black tiger shrimp, vannamei shrimp, black tiger shrimp, black tiger shrimp, and oriole shrimp (common name: Japanese tiger shrimp). It is selected. In addition, the aquaculture water W can be selected from seawater (salt concentration: 3.0 to 4.0 mass%), brackish water (salt concentration: 0.05 to 3.0 mass%), and fresh water depending on the type of the cultivated product. Selected appropriately.

閉鎖型陸上養殖装置300には、養殖水Wの酸素濃度を2.5ppm以上7ppm以下に維持されるように養殖水Wに酸素含有気体を供給しつつ溶解する酸素溶解機構が設けられる(後述)。また、さらに次のような構成要素を備える。
・キャビテーション処理用配管181:養殖池250に養殖水Wの流入口が連通するとともに、他端側が養殖水Wの養殖池250への戻し口とされる。
・キャビテーションノズル1:構造については追って詳述する。
・キャビテーション処理用ポンプ:本実施形態では主ポンプ175が兼用している。キャビテーション処理用配管181(濾過用主配管180の流入口側の一部区間はキャビテーション処理用配管に兼用されている)の途上に設けられ、キャビテーションノズル1に養殖水Wを、キャビテーション処理部における断面平均流速が8m/sec以上となる規定流量にて流通させる。
・キャビテーション処理用濾過部:補助フィルタリング部253fがこれに該当し、濾過用主配管(キャビテーション処理用配管)180の流入口に設けられ、養殖池250内の浮遊物がキャビテーション処理用配管181内に流入することを抑制する。
・流量検出部182:超音波流量計等で構成され、キャビテーションノズル1の例えば下流側にキャビテーション処理用配管181内を流通する養殖水Wの流量を検出する。・制御部185(キャビテーション流量制御部):キャビテーション処理用濾過部253fへの浮遊物の堆積に伴う流量損失を補う形で、キャビテーション処理用ポンプ181pによるキャビテーションノズル1への送液流量を上記規定流量に制御する。
The closed land aquaculture device 300 is provided with an oxygen dissolving mechanism that supplies and dissolves oxygen-containing gas to the culture water W so that the oxygen concentration of the culture water W is maintained at 2.5 ppm or more and 7 ppm or less (described later). . Furthermore, the following components are provided.
- Cavitation treatment pipe 181: An inlet for aquaculture water W communicates with the aquaculture pond 250, and the other end serves as a return port for the aquaculture water W to the aquaculture pond 250.
- Cavitation nozzle 1: The structure will be explained in detail later.
- Pump for cavitation treatment: In this embodiment, the main pump 175 also serves as a pump. It is provided in the middle of the cavitation treatment pipe 181 (a part of the section on the inlet side of the main filtration pipe 180 is also used as the cavitation treatment pipe), and the culture water W is supplied to the cavitation nozzle 1. It is made to flow at a specified flow rate such that the average flow velocity is 8 m/sec or more.
- Cavitation treatment filtration part: The auxiliary filtering part 253f corresponds to this, and is provided at the inlet of the main filtration pipe (cavitation treatment pipe) 180 to prevent floating matter in the aquaculture pond 250 from entering the cavitation treatment pipe 181. Control the influx.
- Flow rate detection unit 182: Comprised of an ultrasonic flow meter or the like, and detects the flow rate of the culture water W flowing through the cavitation treatment pipe 181, for example, on the downstream side of the cavitation nozzle 1. - Control unit 185 (cavitation flow rate control unit): In order to compensate for the flow rate loss due to the accumulation of suspended matter in the cavitation treatment filtration unit 253f, the flow rate of the liquid sent to the cavitation nozzle 1 by the cavitation treatment pump 181p is adjusted to the above specified flow rate. to control.

本実施形態では、具体的には、濾過槽252に養殖水Wの流入口が連通するとともに、他端側が養殖水Wの養殖池250への戻し口とされた濾過用主配管180が設けられ、また、濾過用主配管180の流入口には濾過槽252内の浮遊物が濾過用主配管180内に流入することを抑制する、金属網等で構成された補助フィルタリング部253fが設けられている。また、主ポンプ175は濾過用主配管180上に設けられる。一方、キャビテーション処理用配管181は、主ポンプ175の下流側にて濾過用主配管180から分岐し、かつ、濾過用主配管180とは別位置にて養殖池250に対する戻し口を開口させる形で設けられる。 Specifically, in this embodiment, a main filtration pipe 180 is provided, in which an inlet for aquaculture water W communicates with the filtration tank 252, and the other end serves as a return port for the aquaculture water W to the aquaculture pond 250. Further, an auxiliary filtering section 253f made of a metal net or the like is provided at the inlet of the main filtration pipe 180 to suppress floating substances in the filtration tank 252 from flowing into the main filtration pipe 180. There is. Moreover, the main pump 175 is provided on the main pipe 180 for filtration. On the other hand, the cavitation treatment pipe 181 is branched from the main filtration pipe 180 on the downstream side of the main pump 175, and has a return port for the aquaculture pond 250 opened at a different position from the main filtration pipe 180. provided.

また、閉鎖型陸上養殖装置300には、濾過用主配管180とキャビテーション処理用配管181との分配比をバルブ開度に応じて調整する分配バルブ183が設けられる。本実施形態では、分配バルブ183は濾過用主配管180とキャビテーション処理用配管181との分岐点に設けられた比例制御型の電磁三方バルブとして構成されているが、図16に示すように、分岐点より下流側にて濾過用主配管180とキャビテーション処理用配管181とにそれぞれ個別に設けられた1対の比例制御バルブ183A,183Bとして構成してもよい。キャビテーション流量制御部185は、補助フィルタリング部253fへの浮遊物の堆積に伴い主ポンプ175の送水流量が減少した場合に、養殖水Wのキャビテーション処理用配管181への分配比が増加するように分配バルブ183の開度を調整駆動制御する。以上の構成では、主ポンプ175がキャビテーション処理用ポンプに兼用され、補助フィルタリング部253fがキャビテーション処理用濾過部に兼用されている。 Moreover, the closed land aquaculture apparatus 300 is provided with a distribution valve 183 that adjusts the distribution ratio between the main filtration pipe 180 and the cavitation treatment pipe 181 according to the valve opening degree. In this embodiment, the distribution valve 183 is configured as a proportional control type electromagnetic three-way valve provided at the branch point between the main filtration pipe 180 and the cavitation treatment pipe 181, but as shown in FIG. A pair of proportional control valves 183A and 183B may be provided in the main filtration pipe 180 and the cavitation treatment pipe 181, respectively, on the downstream side of the point. The cavitation flow rate control unit 185 distributes so that the distribution ratio of the culture water W to the cavitation treatment pipe 181 increases when the water flow rate of the main pump 175 decreases due to accumulation of suspended matter in the auxiliary filtering unit 253f. The opening degree of the valve 183 is adjusted and controlled. In the above configuration, the main pump 175 is also used as a cavitation treatment pump, and the auxiliary filtering section 253f is also used as a cavitation treatment filtration section.

養殖池250の出口配管250eから排出される養殖水は、沈殿槽251にて粗大な浮遊物が沈殿除去され、該沈殿槽251からオーバーフローする養殖水Wは濾過槽252に導かれる。濾過槽252には不織布や多孔質樹脂などからなるフィルタ252fが配置され、該フィルタ252fを通過した養殖水Wは濾過槽252からバッファ層253に流下する。濾過槽252にてフィルタ252fには好気性微生物の繁殖媒体層(例えば多孔質セラミック)を介在させることができ、有機浮遊物の分解を行なうバイオフィルタとして構成することが可能である。一方、バッファ層253内には濾過用主配管180の入り口側端部が浸漬されており、金属網等で構成された補助フィルタリング部253fにより開口部が覆われている。養殖池250の長期の使用に伴い、濾過槽252からバッファ層253へはフィルタ252fにて除去しきれなかった浮遊物が流入する。該浮遊物は補助フィルタリング部253fにより分離され、濾過用主配管180に侵入することが抑制される。 The culture water discharged from the outlet pipe 250e of the culture pond 250 undergoes sedimentation and removal of coarse suspended matter in a settling tank 251, and the culture water W overflowing from the settling tank 251 is guided to a filter tank 252. A filter 252f made of nonwoven fabric, porous resin, or the like is arranged in the filtration tank 252, and the culture water W that has passed through the filter 252f flows down from the filtration tank 252 to the buffer layer 253. In the filtration tank 252, the filter 252f can be provided with a propagation medium layer (for example, porous ceramic) for aerobic microorganisms, and can be configured as a biofilter that decomposes organic suspended matter. On the other hand, the entrance side end of the main filtration pipe 180 is immersed in the buffer layer 253, and the opening is covered by an auxiliary filtering part 253f made of a metal net or the like. As the aquaculture pond 250 is used for a long period of time, suspended matter that cannot be removed by the filter 252f flows from the filter tank 252 into the buffer layer 253. The floating substances are separated by the auxiliary filtering section 253f, and are prevented from entering the main filtration pipe 180.

次に、キャビテーション処理用配管181には混相流供給部165、気液ミキサー150及びキャビテーションノズル1が上流側からこの順に設けられている。養殖水Wには、該混相流供給部165にて気体供給配管171を経て気体供給源170より酸素含有気体としての空気が混合され、さらに気液ミキサー150にて導入された空気が微粉砕され、キャビテーションノズル1にて該気体の少なくとも一部が溶解され、養殖水池250に戻される。この気液ミキサー150はキャビテーションノズル1と協働して酸素溶解機構の一部を構成する。 Next, the cavitation treatment piping 181 is provided with a multiphase flow supply section 165, a gas-liquid mixer 150, and a cavitation nozzle 1 in this order from the upstream side. The aquaculture water W is mixed with air as an oxygen-containing gas from the gas supply source 170 via the gas supply pipe 171 in the multiphase flow supply section 165, and the air introduced in the gas-liquid mixer 150 is further pulverized. At least a portion of the gas is dissolved in the cavitation nozzle 1 and returned to the aquaculture pond 250. This gas-liquid mixer 150 cooperates with the cavitation nozzle 1 to constitute a part of the oxygen dissolution mechanism.

図1Bは、気液ミキサー150の一構成例を示すものである。気液ミキサー150は、外筒部材151と流路形成部材155とを備える。外筒部材151は、一端に流入口159、他端に流出口160が形成される中空円筒状に形成される。材質は例えば金属ないしポリ塩化ビニル等のプラスチックであり、本実施形態ではステンレス鋼が採用されている。外筒部材151の両端部には他の配管要素と接続するための継ぎ手部、本実施形態ではおねじ部152が形成されている。 FIG. 1B shows an example of the configuration of the gas-liquid mixer 150. The gas-liquid mixer 150 includes an outer cylinder member 151 and a flow path forming member 155. The outer cylinder member 151 is formed into a hollow cylindrical shape with an inlet 159 formed at one end and an outlet 160 formed at the other end. The material is, for example, metal or plastic such as polyvinyl chloride, and in this embodiment stainless steel is used. At both ends of the outer cylindrical member 151, a joint portion for connecting to another piping element, and in this embodiment, a male thread portion 152 is formed.

一方、流路形成部材155は外筒部材151の内側に設けられ、流入口159と流出口160とをつなぐ螺旋状流路157,158を、該螺旋状流路157,158の螺旋軸線HCが外筒部材151の中心軸線に沿うように形成する。本実施形態において流路形成部材155は、帯状の金属板の幅方向の中心軸線Oを螺旋軸線HCとする形で該金属板をねじり加工したねじり板部材(以下、ねじり板部材155ともいう)として構成できる。流路形成部材155の材質は、例えばステンレス鋼(SUS316等)を採用可能であるが、海水や汽水を使用する場合はチタンないしチタン合金等、海水に対する耐食性がさらに良好な金属で構成することがより望ましい。 On the other hand, the flow path forming member 155 is provided inside the outer cylinder member 151, and the spiral flow paths 157, 158 connecting the inlet 159 and the outlet 160 are formed so that the helical axis HC of the helical flow paths 157, 158 It is formed along the central axis of the outer cylinder member 151. In this embodiment, the flow path forming member 155 is a twisted plate member (hereinafter also referred to as the twisted plate member 155) obtained by twisting a band-shaped metal plate so that the central axis O in the width direction is the helical axis HC. It can be configured as The flow path forming member 155 can be made of, for example, stainless steel (SUS316, etc.), but if seawater or brackish water is used, it may be made of a metal that has better corrosion resistance against seawater, such as titanium or a titanium alloy. More desirable.

外筒部材151の内側にてねじり板部材155は、該ねじり板部材155の第一主面と外筒部材151の内周面との間に第一螺旋状流路157を、同じく第二主面と外筒部材151の内周面との間に第二螺旋状流路158を形成している。そして、外筒部材151は、螺旋状流路が1周期以上、本実施形態では2周期の螺旋区間156を含むように全長が定められている。また、外筒部材151の円筒状の内周面の内径をDx(mm)、ねじり板部材155の螺旋周期長をλ(mm)として、λ/Dxの値は1.5以上4以下に設定されている。Dxは例えば5mm以上30mm以下(例えば15mm)あり、λの値は例えば20mm以上300mm以下(例えば50mm)である。また、ねじり板部材155を構成する板材の厚みはDxの1/4超えない範囲にて、例えば0.3mm以上4mm以下の範囲で選定される(例えば1mm)。 Inside the outer cylindrical member 151, the torsion plate member 155 has a first spiral flow path 157 between the first main surface of the torsion plate member 155 and the inner peripheral surface of the outer cylindrical member 151; A second spiral flow path 158 is formed between the surface and the inner peripheral surface of the outer cylinder member 151. The total length of the outer cylindrical member 151 is determined so that the helical flow path includes a helical section 156 of one period or more, and in this embodiment, two periods. Further, the value of λ/Dx is set to 1.5 or more and 4 or less, where the inner diameter of the cylindrical inner peripheral surface of the outer cylinder member 151 is Dx (mm), and the helical period length of the torsion plate member 155 is λ (mm). has been done. Dx is, for example, 5 mm or more and 30 mm or less (for example, 15 mm), and the value of λ is, for example, 20 mm or more and 300 mm or less (for example, 50 mm). Further, the thickness of the plate material constituting the torsion plate member 155 is selected within a range not exceeding 1/4 of Dx, for example, in a range of 0.3 mm or more and 4 mm or less (for example, 1 mm).

また、本実施形態においては、酸素溶解機構として、キャビテーションノズル1とは別に設けられ、養殖池250を満たす養殖水Wに外部から供給される酸素含有気体を平均気泡径が0.5mm以上となるように噴射する散気部174が養殖池250内に設けられている。散気部174は、気孔を多数形成した散気板あるいは連通気孔が多数形成されたセラミック、樹脂ないし金属製の散気モジュール、あるいは旋回流式気液混合型のディフューザなど周知の構成を有するものであり、気体供給管173を介してエアコンプレッサー170から酸素含有気体としての空気が供給されるようになっている。 Further, in this embodiment, an oxygen dissolving mechanism is provided separately from the cavitation nozzle 1, and the oxygen-containing gas supplied from the outside to the culture water W filling the culture pond 250 has an average bubble diameter of 0.5 mm or more. A diffuser 174 is provided in the aquaculture pond 250 to emit air in a manner similar to that shown in FIG. The air diffuser 174 has a well-known structure such as an air diffuser plate with a large number of pores, a ceramic, resin, or metal air diffuser module with a large number of communicating holes, or a swirling gas-liquid mixing type diffuser. Air as an oxygen-containing gas is supplied from the air compressor 170 via the gas supply pipe 173.

キャビテーションノズル1(混相流供給部165)に向かう気体供給管171、及び散気部174に向かう気体供給管173には、それぞれ電磁バルブ172,184が設けられ、制御部185からの制御信号を受けて開閉駆動される。電磁バルブ172,184が開けばキャビテーションノズル1及び散気部174への空気の供給すなわち養殖水への酸素溶解処理がなされ、電磁バルブ172,184が閉じれば空気の供給すなわち養殖水への酸素溶解処理が停止する。養殖池250内には酸素センサ186(光学式ないしポーラログラフ式の周知の構成のものである)が設けられており、制御部185は該酸素センサ186による養殖水の酸素濃度を読み取るとともに、該酸素濃度が2.5ppm以上7ppm以下(望ましくは3ppm以上6ppm以下)となるように電磁バルブ172,184を開閉制御する。なお、本実施形態では、散気部174への空気供給流量がキャビテーションノズル1における空気供給流量よりも大きく設定されている。 The gas supply pipe 171 heading toward the cavitation nozzle 1 (multiphase flow supply section 165) and the gas supply pipe 173 heading toward the aeration section 174 are provided with electromagnetic valves 172 and 184, respectively, and receive control signals from the control section 185. It is driven to open and close. When the electromagnetic valves 172 and 184 open, air is supplied to the cavitation nozzle 1 and the aeration unit 174, that is, oxygen is dissolved in the culture water. When the electromagnetic valves 172 and 184 are closed, air is supplied, that is, oxygen is dissolved in the culture water. Processing stops. An oxygen sensor 186 (of a well-known optical or polarographic configuration) is provided in the aquaculture pond 250, and the control unit 185 reads the oxygen concentration of the aquaculture water measured by the oxygen sensor 186, and also controls the oxygen concentration of the aquaculture water. The electromagnetic valves 172 and 184 are controlled to open and close so that the concentration is 2.5 ppm or more and 7 ppm or less (preferably 3 ppm or more and 6 ppm or less). Note that in this embodiment, the air supply flow rate to the air diffuser 174 is set to be larger than the air supply flow rate to the cavitation nozzle 1.

次に、図1Cは、キャビテーションノズル1の一例を示す横断面図である。このキャビテーションノズル1は、ノズル流路3が形成されたノズル本体2を備える。ノズル本体2は円筒状に形成され、その中心軸線Oの向きに円形断面の1つのノズル流路3が貫通形成されている。ノズル流路3は一方の端(図面右側)に養殖水入口4を、他方の端に養殖水出口5を開口しており、その流れ方向中間位置には養殖水入口4及び養殖水出口5よりも径小の絞り孔9がノズル流路3の一部区間をなす形で形成されている。ノズル流路3は絞り孔9よりも養殖水入口4側が流入室6とされ、養殖水出口5側が流出室7とされる。そして、絞り孔9には、脚部先端側が流路内側に突出するようにねじ部材10が組み付けられ、キャビテーション処理部CVを形成している。 Next, FIG. 1C is a cross-sectional view showing an example of the cavitation nozzle 1. This cavitation nozzle 1 includes a nozzle body 2 in which a nozzle flow path 3 is formed. The nozzle body 2 is formed into a cylindrical shape, and one nozzle flow path 3 having a circular cross section is formed through the nozzle body 2 in the direction of the central axis O thereof. The nozzle channel 3 has an aquaculture water inlet 4 at one end (on the right side of the drawing) and an aquaculture water outlet 5 at the other end, and an aquaculture water inlet 4 and an aquaculture water outlet 5 at an intermediate position in the flow direction. A throttle hole 9 with a small diameter is also formed to form a part of the nozzle flow path 3. In the nozzle flow path 3, the side closer to the aquaculture water inlet 4 than the throttle hole 9 is an inflow chamber 6, and the side closer to the aquaculture water outlet 5 is an outflow chamber 7. A screw member 10 is attached to the throttle hole 9 so that the tip end of the leg protrudes inside the flow path, thereby forming a cavitation treatment section CV.

ノズル本体2の材質は、たとえばABS、ナイロン、ポリカーボネート、ポリアセタール、ポリ塩化ビニル、PTFEなどの樹脂であるが、チタンないしチタン合金やステンレス鋼などの金属、さらにはアルミナ等のセラミックスで構成される。また、ねじ部材10の材質はたとえばSUS316等のステンレス鋼であるが、海水や汽水を使用する場合はチタンないしチタン合金等、海水に対する耐食性がさらに良好な金属で構成することがより望ましい。また、石英やアルミナなどのセラミック材料を用いることも可能である。 The material of the nozzle body 2 is, for example, a resin such as ABS, nylon, polycarbonate, polyacetal, polyvinyl chloride, or PTFE, but it is also composed of a metal such as titanium or a titanium alloy, stainless steel, or even a ceramic such as alumina. Further, the material of the screw member 10 is, for example, stainless steel such as SUS316, but when seawater or brackish water is used, it is more preferable to use a metal such as titanium or a titanium alloy that has better corrosion resistance against seawater. It is also possible to use ceramic materials such as quartz and alumina.

ねじ部材10は、ねじピッチ及びねじ谷深さが0.20mm以上0.40mm以下、公称ねじ径Mが1.0mm以上2.0mm以下のものが使用されている。本実施形態にてねじ部材10は、JISに定められた0番1種なべ小ねじが使用されている。キャビテーション処理部CVには、ノズル流路3の中心軸線Oと直交する仮想的なねじ配置面が該中心軸線Oに沿って複数、図1CにおいてはLP1,LP2の2面が設定されている。上記のねじ部材10は、脚部の長手方向が個々のねじ配置面LP1,LP2に沿うように配置される。図1Cの実施形態においてねじ部材10の総数は8であり(後述するように、8を超える数であってもよい)、各ねじ配置面LP1,LP2に対し2つ以上、図1Cにおいては4つずつ分配されている。なお、ねじ配置面(面ねじ組)を1つのみ形成することも可能である。 The threaded member 10 used has a thread pitch and thread root depth of 0.20 mm or more and 0.40 mm or less, and a nominal thread diameter M of 1.0 mm or more and 2.0 mm or less. In this embodiment, the screw member 10 is a No. 0 class 1 pan head machine screw defined by JIS. In the cavitation treatment section CV, a plurality of virtual screw arrangement surfaces perpendicular to the central axis O of the nozzle flow path 3 are set along the central axis O, two surfaces LP1 and LP2 in FIG. 1C. The screw member 10 described above is arranged such that the longitudinal direction of the leg portions is along the respective screw arrangement surfaces LP1 and LP2. In the embodiment of FIG. 1C, the total number of screw members 10 is eight (as described later, the number may exceed eight), and there are two or more screw members 10 for each screw placement surface LP1, LP2, and four in FIG. 1C. are distributed one by one. Note that it is also possible to form only one screw arrangement surface (plane screw set).

図1Cにおいて各ねじ配置面LP1,LP2においてねじ部材10は、図2に示すレイアウトに従い配置されている。具体的には、各ねじ配置面LP1,LP2上の4本のねじ部材10は互いに直交する十字形態に配置され、各々ノズル本体2に形成されたねじ孔19内面のめねじ部にて、その壁部外周面側から脚部先端が絞り孔9内へ突出するようにねじ込まれている。ねじ孔19とねじ部材10とは接着剤等によりセッティング固定することができる。図3は、絞り孔9の内側をさらに拡大して示すものであり、ねじ部材10と絞り孔9の内周面との間には主流通領域21が形成されている。また、各絞り孔9において、4つの衝突部10が形成する十字の中心位置には、流通ギャップ15が形成されている。流通ギャップ15(図3)を形成する4つの衝突部10の先端面は平坦に形成され、前述の投影において流通ギャップ15は正方形状に形成されている。 In FIG. 1C, the screw members 10 are arranged on each screw arrangement surface LP1, LP2 according to the layout shown in FIG. 2. Specifically, the four screw members 10 on each of the screw placement surfaces LP1 and LP2 are arranged in a cross shape orthogonal to each other, and each has a female threaded portion on the inner surface of a screw hole 19 formed in the nozzle body 2. The legs are screwed so that the tips of the legs protrude into the throttle hole 9 from the outer peripheral surface of the wall. The screw hole 19 and the screw member 10 can be set and fixed using an adhesive or the like. FIG. 3 shows a further enlarged view of the inside of the throttle hole 9, and a main flow area 21 is formed between the screw member 10 and the inner peripheral surface of the throttle hole 9. Furthermore, in each throttle hole 9, a circulation gap 15 is formed at the center of the cross formed by the four collision parts 10. The end surfaces of the four collision parts 10 forming the circulation gap 15 (FIG. 3) are formed flat, and the circulation gap 15 is formed in a square shape in the projection described above.

図3において、各ねじ配置面LP1,LP2における養殖水流通領域の面積(キャビテーション処理部におけるノズル流路の断面積:以下、全流通断面積ともいう)aを、ノズル流路の投影領域の外周縁内側の全面積(ここでは、図1Cの絞り孔9の円形軸断面の面積:内径をdとしてπd/4))をS1、衝突部10(4本のねじ部材)の投影領域面積をS2として、
a=S1-S2 (単位:mm
として定義する。この実施形態では、主流通領域21と流通ギャップ15との合計面積が全流通断面積aに相当する。図1Cに示すごとく、養殖水入口4及び養殖水出口5の開口径は、絞り孔9の内径よりも大きい。すなわち、養殖水入口4及び養殖水出口5の開口断面積は全流通断面積aよりも大きく設定されている。また、流入室6及び流出室7の絞り孔9に連なる内周面はそれぞれテーパ部13,14とされている。養殖水出口5側のテーパ部14と養殖水入口4側のテーパ部13とは絞り比は同じであるが、区間長はテーパ部14の方が大きく設定されている。そして、各ねじ配置面LP1,LP2において、全流通断面積aは3.8mm以上確保され、ノズル流路の全断面積S1に占める全流通断面積aの割合(すなわち、a/S1×100(%))として定められる面内流通面積率は40%以上に確保されている。
In Fig. 3, the area of the culture water flow area (cross-sectional area of the nozzle flow path in the cavitation treatment section: hereinafter also referred to as the total flow cross-sectional area) a on each screw arrangement surface LP1, LP2 is calculated from the outside of the projected area of the nozzle flow path. The total area inside the periphery (here, the area of the circular axial cross section of the throttle hole 9 in FIG. 1C: πd 2 /4 with the inner diameter as d)) is S1, and the projected area area of the collision part 10 (four screw members) is As S2,
a=S1-S2 (unit: mm 2 )
Define as . In this embodiment, the total area of the main circulation area 21 and the circulation gap 15 corresponds to the total circulation cross-sectional area a. As shown in FIG. 1C, the opening diameters of the culture water inlet 4 and the culture water outlet 5 are larger than the inner diameter of the throttle hole 9. That is, the opening cross-sectional area of the aquaculture water inlet 4 and the aquaculture water outlet 5 is set larger than the total flow cross-sectional area a. Further, the inner circumferential surfaces of the inflow chamber 6 and the outflow chamber 7 that are connected to the throttle hole 9 are tapered portions 13 and 14, respectively. The tapered portion 14 on the side of the culture water outlet 5 and the taper portion 13 on the side of the culture water inlet 4 have the same drawing ratio, but the section length of the tapered portion 14 is set larger. In each screw arrangement surface LP1, LP2, a total flow cross-sectional area a of 3.8 mm2 or more is ensured, and the ratio of the total flow cross-sectional area a to the total cross-sectional area S1 of the nozzle flow path (i.e., a/S1×100 The in-plane distribution area ratio defined as (%)) is ensured at 40% or more.

ねじ部材(衝突部)10の投影外形線に現れる谷部21の深さhは0.2mm以上確保されている。また、中心軸線Oの投影点を中心としてノズル流路の内周縁までの距離の70%に相当する半径にて描いた円を基準円C70として定めたとき、谷部21の最底位置を表す谷点のうち、基準円C70の内側に位置するもの(○で表示)の数、つまり、中心軸線Oと直交する平面への投影にてノズル流路3の断面中心から該ノズル流路3の半径の70%以内の領域に位置する谷点の数を70%谷点数N70と定義する。そして、該70%谷点数N70の値を全ねじ配置面について合計した値を、ノズル流路3(絞り孔9)の断面積S1で除した値を70%谷点面積密度と定義する。図1Cのキャビテーションノズル1においては、70%谷点面積密度の値が1.6個/mm以上に確保されている。 The depth h of the valley portion 21 appearing in the projected outline of the screw member (collision portion) 10 is ensured to be 0.2 mm or more. In addition, when a circle drawn with a radius corresponding to 70% of the distance to the inner circumferential edge of the nozzle flow path with the projected point of the central axis O as the center is defined as the reference circle C70 , the bottom position of the valley portion 21 is Among the valley points represented, the number of valley points located inside the reference circle C 70 (indicated by ○), that is, the number of valley points located inside the reference circle C 70, that is, the number of valley points located inside the reference circle C 70, that is, the number of valley points located from the cross-sectional center of the nozzle channel 3 to the nozzle channel 3 when projected onto a plane perpendicular to the central axis O. The number of valley points located in an area within 70% of the radius of 3 is defined as the number of 70% valley points N70 . Then, the value obtained by dividing the sum of the values of the 70% valley point number N70 for all screw arrangement surfaces by the cross-sectional area S1 of the nozzle flow path 3 (throttle hole 9) is defined as the 70% valley point areal density. In the cavitation nozzle 1 of FIG. 1C, the value of the 70% valley point area density is ensured to be 1.6 pieces/mm 2 or more.

図1Cにおいて、互いに隣接するねじ配置面LP1,LP2間にてねじ部材10の脚部は、中心軸線Oと直交する平面への投影において長手方向を一致させつつ互いに重なり合う位置関係にて配置されている。具体的には、十字状に配置された4本のねじ部材10からなる面ねじ組が、ねじ配置面LP1,LP2間にて互いに重なり合う位置関係(すなわち、十字状の面ねじ組の中心軸線O周りの配置角度位相が互いに一致する位置関係:以下、このような配置を「同相配置」という)にて配置されている。また、隣接するねじ配置面LP1,LP2間の間隔dpは、図2のねじ頭部10hの外径をdh、ねじ脚部10fの公称ねじ径をMとして、例えば1.05dh以上2M以下に設定されている。 In FIG. 1C, the legs of the screw member 10 are arranged between mutually adjacent screw placement surfaces LP1 and LP2 in a positional relationship in which they overlap each other while making their longitudinal directions coincide when projected onto a plane perpendicular to the central axis O. There is. Specifically, the positional relationship is such that a plane screw assembly consisting of four screw members 10 arranged in a cross shape overlaps each other between the screw arrangement surfaces LP1 and LP2 (i.e., the central axis O of the cross-shaped plane screw assembly). They are arranged in a positional relationship in which the surrounding arrangement angle phases match each other (hereinafter, such an arrangement will be referred to as "in-phase arrangement"). Further, the distance dp between the adjacent screw placement surfaces LP1 and LP2 is set to, for example, 1.05dh or more and 2M or less, where dh is the outer diameter of the screw head 10h in FIG. 2, and M is the nominal thread diameter of the screw leg 10f. has been done.

図1Cのキャビテーションノズル1に対し、たとえば、養殖水出口5側を開放して養殖水入口4に動圧が通常水道圧(例えば、0.077MPa)程度となるように、養殖水として例えば水を流通させた場合の作用について説明する。水流はまずテーパ部13及び絞り孔9で絞られ、ねじ部材10と絞り孔9内周面との間に形成される図2の主流通領域21と流通ギャップ15とからなる液流通領域にてねじ部材10に衝突しながらこれを通過する。 For the cavitation nozzle 1 in FIG. 1C, for example, the culture water outlet 5 side is opened and the culture water inlet 4 is supplied with water, for example, so that the dynamic pressure is about the normal tap pressure (for example, 0.077 MPa). The effect when distributed will be explained. The water flow is first constricted by the taper portion 13 and the throttle hole 9, and then reaches a liquid flow region formed between the screw member 10 and the inner circumferential surface of the throttle hole 9 and consisting of the main flow region 21 and the flow gap 15 in FIG. It passes through the threaded member 10 while colliding with it.

そして、ねじ部材10の外周面を通過するときに、ねじ谷部に高速領域を、ねじ山部に低速領域をそれぞれ形成する。すると、ねじ谷部の高速領域はベルヌーイの定理により負圧領域となり、キャビテーションが生ずる。ねじ谷部はねじ部材の外周に複数巻形成され、かつ8本以上のねじ部材10が複数のねじ配置面LP1、LP2に分配配置されていることから、キャビテーションは絞り孔9内の谷部にて同時多発的に起こることとなる。すると、水流がねじ部材10に衝突する際に、ねじ谷部での溶存空気の減圧析出が沸騰的に激しく起こり、ねじ部材10の表面及びノズル流路3の内面との間で水流を激しく摩擦しつつ撹拌する。 When passing through the outer circumferential surface of the threaded member 10, a high speed region is formed at the thread root and a low speed region is formed at the thread crest. Then, the high-speed region of the thread root becomes a negative pressure region according to Bernoulli's theorem, and cavitation occurs. Since the thread trough is formed in multiple turns around the outer periphery of the threaded member, and eight or more threaded members 10 are distributed over the plurality of screw placement surfaces LP1 and LP2, cavitation occurs in the trough in the throttle hole 9. This will occur multiple times at the same time. Then, when the water flow collides with the threaded member 10, dissolved air is violently precipitated under reduced pressure at the thread root, causing violent friction between the water flow and the surface of the threaded member 10 and the inner surface of the nozzle channel 3. Stir while stirring.

前述のごとく、図1Cのキャビテーションノズル1は、各ねじ配置面LP1,LP2にて、面内流通面積率が40%以上に確保され、全流通断面積が3.8mm以上に確保され、さらに隣接するねじ配置面LP1,LP2(面ねじ組)の間隔dpが、使用されるねじ部材10の公称ねじ径よりも大きく確保されている。これにより、面ねじ組を流路中心軸線Oの方向に複数連ねて配置してもノズルの圧損増加を極めて小さくとどめることができる。その結果、1つのノズル流路3内に多くのねじ部材が配置されているにも関わらず、断面内にて必要な流速を十分に確保できるようになる。該構成は、キャビテーション処理の効率を高めた大流量のノズルが望まれる場合に特に有利である。 As mentioned above, the cavitation nozzle 1 in FIG. 1C has an in-plane flow area ratio of 40% or more on each screw arrangement surface LP1, LP2, a total flow cross-sectional area of 3.8 mm 2 or more, and The interval dp between adjacent screw arrangement surfaces LP1 and LP2 (plane screw set) is ensured to be larger than the nominal thread diameter of the screw member 10 used. As a result, even if a plurality of surface screw sets are arranged in series in the direction of the flow path center axis O, the increase in pressure loss of the nozzle can be kept extremely small. As a result, even though many screw members are arranged in one nozzle flow path 3, a sufficient flow velocity can be ensured within the cross section. This configuration is particularly advantageous when a high flow rate nozzle with increased cavitation treatment efficiency is desired.

図10に示すように、気液ミキサー150は、螺旋状流路157,158がキャビテーションノズル1のノズル流路3に連通するように、キャビテーションノズル1の養殖水入口側に配置されている。具体的には、外筒部材151の流出口側のおねじ部152をノズル本体2のめねじ部16に螺合させる形で接続されている。気液ミキサー150とキャビテーションノズル1との間には中継配管等の別配管要素(図示せず)が介在していてもよいが、該別配管要素内を流通する間に二次気泡BSが合体・粗大化する懸念もあり、気液ミキサー150とキャビテーションノズル1とは図10のように直結されていることが望ましい。 As shown in FIG. 10, the gas-liquid mixer 150 is arranged on the culture water inlet side of the cavitation nozzle 1 so that the spiral channels 157 and 158 communicate with the nozzle channel 3 of the cavitation nozzle 1. Specifically, the male threaded portion 152 on the outlet side of the outer cylinder member 151 is screwed into the female threaded portion 16 of the nozzle body 2 . A separate piping element (not shown) such as a relay pipe may be interposed between the gas-liquid mixer 150 and the cavitation nozzle 1, but secondary bubbles BS may coalesce while flowing through the separate piping element. - There is also a concern that the gas-liquid mixer 150 and the cavitation nozzle 1 may become coarse, so it is desirable that the gas-liquid mixer 150 and the cavitation nozzle 1 be directly connected as shown in FIG.

また、混相流供給部165は、気液ミキサー150の流入口159に、気体と養殖水との混相流を供給する。本実施形態では混相流供給部165はベンチュリエジェクタとして構成され、その絞り孔に連通する気体供給孔166に気体導入用継手167を介して気体供給配管171(図1A)により気体が供給され、混相流が形成される。本実施形態では、混相流供給部165もまた気液ミキサー150の流入口159側に直結されている。混相流は、第一螺旋状流路157及び第二螺旋状流路158に分配され、それぞれ第一螺旋流TR1と第二螺旋流TR2を形成しつつ気相を二次気泡BSに粉砕する。 Further, the multiphase flow supply unit 165 supplies a multiphase flow of gas and culture water to the inlet 159 of the gas-liquid mixer 150. In this embodiment, the multiphase flow supply unit 165 is configured as a venturi ejector, and gas is supplied to the gas supply hole 166 communicating with the throttle hole by the gas supply piping 171 (FIG. 1A) via the gas introduction joint 167. A flow is formed. In this embodiment, the multiphase flow supply section 165 is also directly connected to the inlet 159 side of the gas-liquid mixer 150. The multiphase flow is distributed into a first spiral flow path 157 and a second spiral flow path 158, and crushes the gas phase into secondary bubbles BS while forming a first spiral flow TR1 and a second spiral flow TR2, respectively.

該混相流中の一次気泡BPは、気液ミキサー150の螺旋状流路157,158内を流通させることにより遠心力により養殖水と混合・微粉砕され、図1Cのキャビテーションノズル1のねじ部材10のねじピッチをh(mm)として、気泡径1.5h以下(望ましくは1h以下)の二次気泡BSに微粉砕される。二次気泡BSを含んだ養殖水はキャビテーションノズル1に供給され、キャビテーション処理部CVに生ずる乱流域に巻き込まれることにより溶解する。 The primary bubbles BP in the multiphase flow are mixed and finely pulverized with the culture water by centrifugal force by flowing through the spiral channels 157 and 158 of the gas-liquid mixer 150, and are mixed with the culture water and pulverized by the threaded member 10 of the cavitation nozzle 1 in FIG. 1C. The secondary cells BS are pulverized into secondary cells BS having a cell diameter of 1.5h or less (preferably 1h or less), with the screw pitch of h (mm). The culture water containing the secondary bubbles BS is supplied to the cavitation nozzle 1, and is dissolved by being caught in the turbulent area generated in the cavitation treatment section CV.

混相流中の気相が、より細かい二次気泡BSに粉砕された状態でキャビテーションノズル1のねじ部材に供給されることにより、気体を含有した養殖水とねじ谷との接触効率が上昇する。これにより、気相成分の混合・攪拌の駆動力を生ずる乱流域の形成が顕著となり、気体溶解効率を高めることができる。また、キャビテーション処理部CV内では、溶解した気体の一部は直ちにキャビテーションにより再析出することから、ねじ谷部内でのキャビテーション効率は大幅に改善される。 By supplying the gas phase in the multiphase flow to the screw member of the cavitation nozzle 1 in a state of being crushed into finer secondary bubbles BS, the contact efficiency between the gas-containing culture water and the screw valley increases. As a result, the formation of a turbulent region that generates a driving force for mixing and stirring the gas phase components becomes significant, and the gas dissolution efficiency can be improved. Further, in the cavitation treatment section CV, a portion of the dissolved gas is immediately reprecipitated by cavitation, so that the cavitation efficiency within the thread root portion is significantly improved.

次に、図11は、制御部185の電気的構成の一例を示すブロック図である。制御部185はCPU191と、該CPU191が実行する制御プログラム(ノズル流量制御プログラム193a及び酸素濃度制御プログラム193b)を格納したROM193と、プログラム実行メモリを形成するRAM192と、入出力部194と、これらを接続するバスライン195とを備えるマイコンハードウェアを主体に構成されている。入出力部194には、バルブ開度(バルブ位置)の指示値を示すデジタル信号をアナログ電圧指示値に変換するD/A変換部199を介して、前述の分配バルブ183が接続されている。また、流量計186と酸素センサ186のアナログセンサ出力は、A/D変換部196,197によりデジタル信号に変換され入出力部194に入力される。さらに、散気ノズル174及びキャビテーションノズル1への空気の供給を開閉する電磁バルブ172及び184は、駆動回路172A,184Aを介して入出力部194に接続されている。 Next, FIG. 11 is a block diagram showing an example of the electrical configuration of the control section 185. The control unit 185 includes a CPU 191, a ROM 193 that stores control programs executed by the CPU 191 (nozzle flow rate control program 193a and oxygen concentration control program 193b), a RAM 192 that forms a program execution memory, and an input/output unit 194. It is mainly composed of microcomputer hardware including a connecting bus line 195. The aforementioned distribution valve 183 is connected to the input/output section 194 via a D/A converter section 199 that converts a digital signal indicating an instruction value of the valve opening degree (valve position) into an analog voltage instruction value. Further, the analog sensor outputs of the flow meter 186 and the oxygen sensor 186 are converted into digital signals by A/D converters 196 and 197 and input to the input/output section 194. Furthermore, electromagnetic valves 172 and 184 that open and close the supply of air to the aeration nozzle 174 and the cavitation nozzle 1 are connected to the input/output section 194 via drive circuits 172A and 184A.

以下、図1Aの閉鎖型陸上養殖装置300の動作について説明する。
まず、養殖池250内に養殖水Wを注水する。図11の制御部185に対しては、キャビテーションノズル1の流通断面積の値に応じ、養殖水Wの断面平均流速が8m/sec以上、望ましくは9m/以上となる規定流量範囲(上限値Q、下限値Q)を入力部198を用いて設定しておく。また、投入する被養殖物SPの個体数に応じて養殖水Wの規定酸素濃度範囲(上限値C、下限値C)を、同様に入力部198を用いて設定する。これらの設定値は、図11のRAM192に記憶される。
The operation of the closed land aquaculture apparatus 300 shown in FIG. 1A will be described below.
First, aquaculture water W is poured into the aquaculture pond 250. For the control unit 185 in FIG. 11, a specified flow rate range (upper limit Q U , lower limit value QL ) are set using the input section 198. Further, the specified oxygen concentration range (upper limit value C U , lower limit value C L ) of the culture water W is similarly set using the input unit 198 according to the number of the cultured product SP to be input. These setting values are stored in the RAM 192 in FIG.

以上の設定が終了すれば、主ポンプ175の動作と、制御部185によるキャビテーションノズル1の流量及び養殖水Wへの酸素溶解の制御を開始する。そして、流量計182が示すキャビテーションノズル1の流量と、酸素センサ186が示す酸素濃度とが規定範囲内にて制御され、これらの値が安定した段階で養殖水Wに被養殖物SPを投入する。 When the above settings are completed, the operation of the main pump 175 and the control of the flow rate of the cavitation nozzle 1 and the dissolution of oxygen into the culture water W by the control unit 185 are started. Then, the flow rate of the cavitation nozzle 1 indicated by the flow meter 182 and the oxygen concentration indicated by the oxygen sensor 186 are controlled within a specified range, and when these values are stabilized, the cultured material SP is introduced into the culture water W. .

図12は流量制御プログラムの処理の流れの一例を示すフローチャートである。S101では、図1Aの分配バルブ183の開度Sをデフォルト値であるS0に設定する。該デフォルト値は、例えば図1Aの補助フィルタリング部253fが新品の状態であり、かつ主ポンプ175が定格出力にて回転駆動されたときに、キャビテーションノズル1の流量が規定流量範囲の中心値を示すように設定することができる。S102では、流量計182の流量値Q2を読み取る。次に、この流量値Q2を規定流量範囲の下限値Q及び上限値Qと比較する。S103にてQ2<Qならば流量が不足しているのでS104に進み、開度Sをキャビテーション処理用配管181側に予め定められた増分ΔSだけ増加するよう分配バルブ183を駆動する。その余の場合はS105に進み、Q<Q2ならば流量が過剰なので、S106にて開度Sをキャビテーション処理用配管181側に増分ΔSだけ減少するように分配バルブ183を駆動する。そして、Q<Q2<Qの場合は流量が適正であり、S107に進んで分配バルブ183の開度Sの現在値を維持する。以降、S108で終了でなければS101に戻り、以下の処理を繰り返す。流量の上限値Qは、養殖池250の貯水量をV1、キャビテーションノズル1の1時間当たりの流通流量をV2としたとき、
K=V2/V1×100 (%)
にて表される流通循環比Kが例えば2%を超えないように設定される。
FIG. 12 is a flowchart showing an example of the processing flow of the flow rate control program. In S101, the opening degree S of the distribution valve 183 in FIG. 1A is set to the default value S0. The default value indicates that, for example, when the auxiliary filtering section 253f in FIG. 1A is new and the main pump 175 is rotated at the rated output, the flow rate of the cavitation nozzle 1 indicates the center value of the specified flow rate range. It can be set as follows. In S102, the flow rate value Q2 of the flow meter 182 is read. Next, this flow rate value Q2 is compared with the lower limit value Q L and the upper limit value Q U of the specified flow rate range. If Q2< QL in S103, the flow rate is insufficient, so the process proceeds to S104, and the distribution valve 183 is driven so as to increase the opening degree S toward the cavitation treatment pipe 181 by a predetermined increment ΔS. In other cases, the process proceeds to S105, and if Q U <Q2, the flow rate is excessive, so in S106, the distribution valve 183 is driven so that the opening degree S is decreased by the increment ΔS toward the cavitation treatment pipe 181 side. If Q L <Q2 <Q U , the flow rate is appropriate, and the process advances to S107 to maintain the current value of the opening degree S of the distribution valve 183. Thereafter, if the process does not end in S108, the process returns to S101 and the following process is repeated. The upper limit value QU of the flow rate is defined as the amount of water stored in the aquaculture pond 250 as V1, and the hourly flow rate of the cavitation nozzle 1 as V2.
K=V2/V1×100 (%)
The distribution/circulation ratio K expressed by is set, for example, so as not to exceed 2%.

図13は酸素濃度制御プログラムの処理の流れの一例を示すフローチャートである。S201では、デフォルト設定状態として、図1Aの散気部174側の電磁バルブ184をON(開)とし、キャビテーションノズル1側の電磁バルブ172もON(開)とする。S202では、酸素センサ186の酸素濃度検出値Cを読み取る。次に、この酸素濃度検出値Cを規定酸素濃度範囲の下限値C及び上限値Cと比較する。S103にてC<Cならば酸素濃度が不足しているのでS204に進み、散気部174側の電磁バルブ184をON(開)とし、キャビテーションノズル1側の電磁バルブ172もON(開)とする状態を維持する。その余の場合はS205に進み、C<Cならば酸素濃度が過剰なので、S206にて散気部174側の電磁バルブ184はON(開)とし、キャビテーションノズル1側の電磁バルブ172はOFF(閉)として、キャビテーションノズル1での酸素溶解を抑制し、養殖水W中の酸素濃度を低下させる。なお、酸素濃度の下げ幅をより大きくしたい場合は、散気部174側の電磁バルブ184もOFF(閉)とする処理を行なうことも可能である。そして、C<C2<Qの場合は酸素濃度が適正であり、S207に進んで散気部174側の電磁バルブ184をON(開)とし、キャビテーションノズル1側の電磁バルブ172は断続的にON/OFFして現在の酸素濃度値を維持するようにする。以降、S208で終了でなければS201に戻り、以下の処理を繰り返す。養殖水W中の酸素濃度Cは例えば中心目標値C0を4~6ppmの範囲内で固定的に定め(例えば5ppm)、上限値Cは該中心目標値C0を基準に例えばC0+0.5~C0+2ppmの値(例えば6ppm)とし、下限値Cは中心目標値C0を基準に例えばC0-0.5~C0-2ppmの値(例えば4ppm)として設定することができる。 FIG. 13 is a flowchart showing an example of the processing flow of the oxygen concentration control program. In S201, as a default setting state, the electromagnetic valve 184 on the side of the air diffuser 174 in FIG. 1A is turned ON (open), and the electromagnetic valve 172 on the side of the cavitation nozzle 1 is also turned ON (open). In S202, the oxygen concentration detection value C of the oxygen sensor 186 is read. Next, this detected oxygen concentration value C is compared with the lower limit value C L and the upper limit value C U of the specified oxygen concentration range. If C<C L in S103, the oxygen concentration is insufficient, so the process proceeds to S204, where the solenoid valve 184 on the diffuser 174 side is turned on (opened), and the solenoid valve 172 on the cavitation nozzle 1 side is also turned on (opened). Maintain the state as follows. In other cases, the process proceeds to S205, and if C U <C, the oxygen concentration is excessive, so in S206, the solenoid valve 184 on the diffuser 174 side is turned on (opened), and the solenoid valve 172 on the cavitation nozzle 1 side is turned off. (closed) to suppress oxygen dissolution in the cavitation nozzle 1 and reduce the oxygen concentration in the culture water W. Note that if it is desired to further reduce the oxygen concentration, it is also possible to turn off (close) the electromagnetic valve 184 on the side of the air diffuser 174. If C L < C2 < Q U , the oxygen concentration is appropriate, and the process proceeds to S207, where the solenoid valve 184 on the diffuser 174 side is turned on (opened), and the solenoid valve 172 on the cavitation nozzle 1 side is intermittently turned on. Turn it ON/OFF to maintain the current oxygen concentration value. Thereafter, if the process does not end in S208, the process returns to S201 and the following process is repeated. For example, the oxygen concentration C in the culture water W is fixedly set within a range of 4 to 6 ppm (for example, 5 ppm) with a central target value C0, and the upper limit C U is set to, for example, C0 + 0.5 to C0 + 2 ppm based on the central target value C0. (for example, 6 ppm), and the lower limit value C L can be set, for example, as a value of C0-0.5 to C0-2 ppm (for example, 4 ppm) based on the central target value C0.

被養殖物SPによる消費により減少する養殖水W中の酸素濃度は、上記制御により、突発的な要因による酸素濃度の変動を考慮しても、養殖水W中の酸素濃度は飽和値未満である2.5ppm以上7ppm以下(望ましくは3ppm以上8ppm以下)の範囲に維持されるようになる。そして、その養殖水Wをキャビテーションノズル1に導き、キャビテーション処理部における断面平均流速が8m/sec以上となる規定流量にて流通させることによりキャビテーション処理がなされる。養殖水Wの酸素濃度をあえて飽和値未満に維持することで、キャビテーションに伴う微細気泡の過剰発生が抑制され、被養殖物SPのえらに気泡が付着して溶存酸素の取り込みが阻害される等の不具合を効果的に防止することができる。そして、キャビテーション処理部における断面平均流速が8m/sec以上となる規定流量を確保することで、養殖水Wの酸素濃度が従来技術よりも低く設定されているにも関わらず、被養殖物SPの生育促進等は問題なく図ることができる。 Due to the above control, the oxygen concentration in the culture water W, which decreases due to consumption by the cultured product SP, is lower than the saturation value even when fluctuations in oxygen concentration due to sudden factors are taken into account. The content is maintained within a range of 2.5 ppm or more and 7 ppm or less (preferably 3 ppm or more and 8 ppm or less). Then, the culture water W is guided to the cavitation nozzle 1, and cavitation treatment is performed by flowing it at a specified flow rate such that the cross-sectional average flow velocity in the cavitation treatment section is 8 m/sec or more. By intentionally maintaining the oxygen concentration of the culture water W below the saturation value, excessive generation of microbubbles due to cavitation is suppressed, and the bubbles adhere to the gills of the cultured product SP, inhibiting the uptake of dissolved oxygen, etc. problems can be effectively prevented. By ensuring a specified flow rate at which the cross-sectional average flow velocity in the cavitation treatment section is 8 m/sec or more, even though the oxygen concentration of the culture water W is set lower than in the conventional technology, the Growth promotion etc. can be achieved without any problem.

以下、本発明にて採用可能なキャビテーションノズルの種々の変形例について説明する。
図4は、図1Cのキャビテーションノズル1のキャビテーション処理部CVを、図2に示すレイアウトの面ねじ組を中心軸線Oの方向に4組配置した構成を示す。具体的には、中心軸線Oの向きに4つのねじ配置面LP1~LP4が、図1Cと同じ面間隔dpにて配置され、図2の十字状の面ねじ組が互いに重なるように(すなわち、同相に)配置されている。この場合、16本のねじ部材10が4つのねじ配置面LP1~LP4に分配されることとなる。また、図5は、図2の面ねじ組を8つのねじ配置面LP1~LP8に対し同相に配置したキャビテーション処理部CVの例を示す。この場合、32本のねじ部材10が8つのねじ配置面LP1~LP8に分配されることとなる。各キャビテーション処理部CVの70%谷点面積密度は、図2の構成と比較して、図4の構成では2倍に、図5の構成では4倍に増加させることができる。これにより、キャビテーション処理の効率が向上し、本発明の前述の効果をより安定的に達成することが可能となる。
Hereinafter, various modifications of the cavitation nozzle that can be employed in the present invention will be described.
FIG. 4 shows a configuration in which the cavitation treatment section CV of the cavitation nozzle 1 of FIG. 1C has four sets of surface threads arranged in the direction of the central axis O in the layout shown in FIG. Specifically, the four screw arrangement surfaces LP1 to LP4 are arranged in the direction of the central axis O with the same surface spacing dp as in FIG. 1C, so that the cross-shaped surface screw sets in FIG. in phase). In this case, the 16 screw members 10 will be distributed to the four screw placement surfaces LP1 to LP4. Further, FIG. 5 shows an example of a cavitation treatment section CV in which the surface screw set of FIG. 2 is arranged in the same phase with respect to eight screw arrangement surfaces LP1 to LP8. In this case, 32 screw members 10 are distributed over eight screw placement surfaces LP1 to LP8. The 70% valley point areal density of each cavitation treatment section CV can be increased twice in the configuration of FIG. 4 and four times in the configuration of FIG. 5 compared to the configuration in FIG. 2. This improves the efficiency of cavitation treatment and makes it possible to achieve the above-described effects of the present invention more stably.

次に、図6は、図1Cのキャビテーションノズル1と同様の面ねじ組を45°回転させた状態を示している。そして、図1Cのキャビテーションノズル1の2つのねじ配置面LP1,LP2のうち、一方のねじ配置面LP2の十字状の面ねじ組を、他方のねじ配置面LP1の面ねじ組に対して中心軸線Oの周りに45°だけ回転させ、図6の状態とした場合のキャビテーション処理部CVの例を、図7に示している。該構成のキャビテーション処理部CVは、図2の構成と同等の70%谷点面積密度を実現できるが、ねじ配置面LP1,LP2の面間隔dpが図1Cの構成と同一の場合は、養殖水流通時の圧損が若干大きくなる。しかし、面間隔dpを適度に拡大することで該圧損は減じられ、図2の構成のキャビテーション処理部CVとほぼ同等のキャビテーション処理能力を発揮する。また、養殖水の乱流攪拌効果は図1Cの構成よりも大きいため、混相流供給により気体を養殖水に溶解させる目的においてはより有利となる。 Next, FIG. 6 shows a state in which a surface screw set similar to the cavitation nozzle 1 of FIG. 1C is rotated by 45 degrees. Of the two screw placement surfaces LP1 and LP2 of the cavitation nozzle 1 in FIG. FIG. 7 shows an example of the cavitation treatment section CV when the cavitation treatment section CV is rotated by 45 degrees around O and brought into the state shown in FIG. The cavitation treatment section CV with this configuration can achieve the same 70% valley point area density as the configuration in FIG. Pressure loss during circulation will be slightly larger. However, by appropriately enlarging the surface spacing dp, this pressure loss is reduced, and cavitation processing capacity approximately equivalent to that of the cavitation processing section CV having the configuration shown in FIG. 2 is exhibited. Further, since the turbulent agitation effect of the culture water is greater than that of the configuration shown in FIG. 1C, this configuration is more advantageous for dissolving gas in the culture water by supplying a multiphase flow.

図8は、図7の構成において、面ねじ組を互いに直交するねじ部材対に分割し、それぞれ中心軸線Oの向きに位置をずらせて配置したキャビテーション処理部CVの例を示す。具体的には、図1Cにおいてねじ配置面LP1,LP2上に配置されていた各々4本のねじ部材10が、図7の構成では、ねじ部材10の公称ねじ径Mだけ隔てられた2つのねじ配置面LP1,LP1’及びLP2,LP2’に、互いに直交する2本ずつを分散させて配置している。すなわち、8本のねじ部材10を4つのねじ配置面LP1,LP1’,LP2,LP2’に分配した例を示すものである。また、ねじ配置面LP1’とねじ配置面LP2との間隔は、公称ねじ径Mよりも大きく(例えば1.5M~2.0M程度)に設定されている。該構成における70%谷点面積密度は図2の構成と同等である。 FIG. 8 shows an example of the cavitation treatment section CV in which the surface screw set is divided into mutually orthogonal screw member pairs, and the respective positions are shifted in the direction of the central axis O in the configuration of FIG. 7. Specifically, the four screw members 10 arranged on the screw arrangement surfaces LP1 and LP2 in FIG. 1C are replaced by two screws separated by the nominal thread diameter M of the thread members 10 in the configuration of FIG. Two mutually orthogonal wires are distributed and arranged on the arrangement planes LP1, LP1' and LP2, LP2'. That is, an example is shown in which eight screw members 10 are distributed to four screw placement surfaces LP1, LP1', LP2, and LP2'. Further, the distance between the screw placement surface LP1' and the screw placement surface LP2 is set to be larger than the nominal thread diameter M (for example, about 1.5M to 2.0M). The 70% valley point area density in this configuration is equivalent to the configuration in FIG.

また、図9は、図2のレイアウトの面ねじ組と、図6のレイアウトの面ねじ組とを、4つのねじ配置面LP1~LP4に対し、交互に2つずつ合計4組配置したキャビテーション処理部CVの例を示す。この例では、16本のねじ部材10が4つのねじ配置面LP1~LP4に4本ずつ分配配置されている。該構成における70%谷点面積密度は図2の構成の2倍となる。 In addition, FIG. 9 shows cavitation treatment in which two sets of surface screws having the layout of FIG. 2 and two sets of surface screws having the layout of FIG. 6 are arranged alternately on the four screw placement surfaces LP1 to LP4. An example of part CV is shown below. In this example, 16 screw members 10 are distributed and arranged, four each on four screw placement surfaces LP1 to LP4. The 70% valley point areal density in this configuration is twice that of the configuration in FIG.

図14は、キャビテーション処理部に形成した隔壁部8に2つの絞り孔9を形成し、各絞り孔9について十字形態に4本のねじ部材10を配置したキャビテーションノズルの例を示すものである。 FIG. 14 shows an example of a cavitation nozzle in which two throttle holes 9 are formed in a partition wall 8 formed in a cavitation treatment section, and four screw members 10 are arranged in a cross shape for each throttle hole 9.

また、閉鎖型陸上養殖装置300は、図17に示すように、キャビテーション処理用配管182及びキャビテーション処理用ポンプ181pを濾過用主配管180及び主ポンプ175とは独立して設ける構成とすることもできる。キャビテーション処理用配管182の入り口は養殖池250内に開口しており、補助フィルタリング部253fと同様の構成のキャビテーション処理用濾過部181fが設けられている。キャビテーション処理用ポンプ181pの駆動入力は電源アンプ181vにより可変とされており、制御部185からの信号により該電源アンプ181vの出力を制御することでキャビテーションノズル1への送液流量が前述の規定流量範囲に維持される。その余の構成は図1と同様であるので、詳細な説明は略する。 Further, the closed land aquaculture device 300 may have a configuration in which the cavitation treatment pipe 182 and the cavitation treatment pump 181p are provided independently of the filtration main pipe 180 and the main pump 175, as shown in FIG. . The entrance of the cavitation treatment piping 182 opens into the aquaculture pond 250, and is provided with a cavitation treatment filter section 181f having the same configuration as the auxiliary filtering section 253f. The drive input of the cavitation treatment pump 181p is made variable by a power amplifier 181v, and by controlling the output of the power amplifier 181v based on a signal from the control unit 185, the flow rate of liquid sent to the cavitation nozzle 1 is adjusted to the above-mentioned specified flow rate. maintained within range. The rest of the configuration is the same as that in FIG. 1, so detailed explanation will be omitted.

以下、キャビテーションノズルの効果を確認するために行った種々の実験の結果について説明する。
(実施例1)
キャビテーションノズルA,Bとして、図1Cに示す形状のものを作成した。なお、キャビテーションノズルAについては、図2に示す4本のねじからなる面ねじ組を1つのみ配置し、キャビテーションノズルBについては面ねじ組を2つ互いに重なる位置関係にて配置している。図21に図1Cの各部の寸法関係を図示している。ノズル本体2の材質はABS樹脂であり、養殖水入口4と養殖水出口5の内径はφ20mm、流入室6及び流出室7の流れ方向の長さはそれぞれ15mm及び45mmである。キャビテーション処理部において絞り孔9の長さは12mmである。また、絞り孔9の内径Dは、キャビテーションノズルAについてはφ5.0mm、キャビテーションノズルBについてはφ14.0mmに設定した。採用したねじ部材は、JIS:B0205(1997)に規定されたメートル並目ピッチを有する0番1種なべ小ねじであり、材質はチタンである。また、脚部の公称ねじ径はM1.4mmである。
Below, the results of various experiments conducted to confirm the effectiveness of the cavitation nozzle will be explained.
(Example 1)
Cavitation nozzles A and B having the shapes shown in FIG. 1C were created. Note that for the cavitation nozzle A, only one set of surface threads consisting of four screws shown in FIG. 2 is arranged, and for the cavitation nozzle B, two sets of surface threads are arranged in an overlapping positional relationship. FIG. 21 illustrates the dimensional relationship of each part in FIG. 1C. The material of the nozzle body 2 is ABS resin, the inner diameter of the culture water inlet 4 and the culture water outlet 5 is 20 mm, and the lengths of the inlet chamber 6 and the outlet chamber 7 in the flow direction are 15 mm and 45 mm, respectively. The length of the throttle hole 9 in the cavitation treatment section is 12 mm. Further, the inner diameter D of the throttle hole 9 was set to 5.0 mm for cavitation nozzle A, and 14.0 mm for cavitation nozzle B. The screw member used was a No. 0 class 1 pan head machine screw having a metric coarse pitch specified in JIS: B0205 (1997), and was made of titanium. Further, the nominal thread diameter of the leg portion is M1.4 mm.

また、絞り孔内のねじ部材のレイアウトを示す投影画像上で全流通断面積a(絞り孔の全断面積からねじにより占有される領域の面積を除いた値)を算出した。さらに、図3の基準円C70の内側に存する70%谷点数を計数し、絞り孔の全断面積S1で除することにより、70%谷点面積密度の値を各試験ノズルについて算出した。作成した各ノズルA,Bについて、絞り孔内径、面内流通断面積70%谷点総数、70%谷点面積密度、及び養殖池の全水量を50tとしたときの流通循環比Kの各値を、表1にまとめて示している。いずれのノズルも70%谷点密度は2.0個/mm以上に確保されている上記のキャビテーションノズルを図10の気液ミキサー150とともに図1Aの閉鎖型陸上養殖装置300に組み込んだ。 In addition, the total flow cross-sectional area a (the value obtained by subtracting the area of the area occupied by the screws from the total cross-sectional area of the throttle hole) was calculated on the projected image showing the layout of the screw members in the throttle hole. Furthermore, the value of the 70% valley point area density was calculated for each test nozzle by counting the number of 70% valley points existing inside the reference circle C70 in FIG. 3 and dividing by the total cross-sectional area S1 of the aperture hole. For each nozzle A and B created, each value of the aperture hole inner diameter, in-plane flow cross-sectional area 70% total number of troughs, 70% trough area density, and flow circulation ratio K when the total water volume of the aquaculture pond is 50 t. are summarized in Table 1. The above cavitation nozzle, in which the 70% valley point density of all nozzles was ensured to be 2.0 pieces/mm 2 or more, was incorporated into the closed land aquaculture apparatus 300 of FIG. 1A together with the gas-liquid mixer 150 of FIG. 10.

Figure 0007410490000001
Figure 0007410490000001

次に、養殖池250に塩分濃度が2.0%の汽水域となるように調整した人工海水を50t(水深:約1.5m)注入するとともに、主ポンプ175による循環を初期流量100L/分にて開始した。そして、各ノズルA,Bについて表1に示す流量設定となるように、分配バルブ183の開度をすでに詳細に説明した方式により制御した。また、養殖水の制御目標となる酸素濃度を、下記表2に示す番号1~6の各条件(2.0ppm~7.5ppm、番号1(2.0ppm)及び番号6(7.5ppm)は比較例)となるように設定し、図1Aの電磁バルブ184及び174を駆動制御して養殖水の酸素濃度を各設定値に維持した。なお、散気部174の空気噴出流量は50NL/分(平均気泡径:0.3mm)とした。キャビテーションノズル1への空気供給流量は、大気圧換算での体積流量(NL/分)にて水流量の10%となるように調整した。さらに、図示しない圧力計にて計測した上記流量設定時のキャビテーションノズルの動水圧の値と、流量値と全流通断面積とから算出した絞り孔(キャビテーション処理部)内の平均流速の値も表1に合わせて示している。いずれの条件においても、キャビテーション処理部の平均流速は9m/秒の値に確保されている。 Next, 50 tons (water depth: approximately 1.5 m) of artificial seawater adjusted to have brackish water with a salinity of 2.0% is injected into the aquaculture pond 250, and the main pump 175 circulates the water at an initial flow rate of 100 L/min. It started at. Then, the opening degree of the distribution valve 183 was controlled by the method already described in detail so that the flow rate settings for each nozzle A and B were as shown in Table 1. In addition, the oxygen concentration that is the control target of the aquaculture water is determined under each of the conditions numbered 1 to 6 shown in Table 2 below (2.0 ppm to 7.5 ppm, number 1 (2.0 ppm) and number 6 (7.5 ppm)). Comparative Example), and the electromagnetic valves 184 and 174 in FIG. 1A were driven and controlled to maintain the oxygen concentration of the culture water at each set value. Note that the air ejection flow rate of the air diffuser 174 was 50 NL/min (average bubble diameter: 0.3 mm). The air supply flow rate to the cavitation nozzle 1 was adjusted to be 10% of the water flow rate in terms of volumetric flow rate (NL/min) converted to atmospheric pressure. Furthermore, the value of the dynamic hydraulic pressure of the cavitation nozzle at the above flow rate setting measured with a pressure gauge (not shown), and the value of the average flow velocity in the throttle hole (cavitation processing section) calculated from the flow rate value and the total flow cross-sectional area are also displayed. It is shown according to 1. Under any conditions, the average flow velocity in the cavitation treatment section was maintained at a value of 9 m/sec.

この状態で、200匹/トンの個体密度となるようにバナメイエビの稚エビを投入するとともに、池内の稚エビには、魚粉、オキアミミール、イカミール及び小麦粉を配合した飼料をエビの成長度合いに応じて適宜投与し、飼育を行なった。飼育継続に伴い、養殖水にはエビの排せつ物や食べ残された飼料などが池内に有機残渣となって浮遊するようになる。養殖水の上記循環により、該浮遊物は図1Aの濾過槽252である程度除去されるが、長期間の飼育を継続すれば、除去しきれなかった浮遊物が下流側のバッファ槽側に流出し、補助フィルタリング部253f(キャビテーション処理用濾過部)に次第に堆積する。その結果、主ポンプ175による濾過用主配管180への吸い込み負荷が増大し、キャビテーション処理用配管1との分岐点よりも上流側において濾過用主配管180の循環流量は徐々に減少する。しかし、図1Aの閉鎖型陸上養殖装置の構成が採用されていることで、いずれの条件においても、キャビテーション処理用配管181(すなわちキャビテーションノズル1)側への分配流量は、設定された規定流量範囲内に維持することができた。なお、濾過槽252内のフィルタ252fについては、濾過用主配管180の総流量が30L/分以下に低下した場合に、一旦循環を止めて新しいものと適宜交換するようにした。なお、濾過槽252内は図示しないばっ気機構により空気ばっ気を行ない、腐植形成に関与するバシルス属等の好気性微生物を繁殖させることにより、濾過された有機残渣の腐植化を同時に行なうようにしている。 In this state, young vannamei shrimp were introduced to the population density of 200 shrimp/ton, and feed containing fishmeal, krill meal, squid meal, and wheat flour was fed to the young shrimp in the pond according to the growth level of the shrimp. The animals were given appropriate doses and reared. As breeding continues, shrimp excrement and uneaten feed become suspended in the culture water as organic residue in the pond. Due to the above-mentioned circulation of the culture water, the floating matter is removed to some extent in the filter tank 252 in FIG. 1A, but if breeding continues for a long period of time, the floating matter that could not be completely removed will flow into the downstream buffer tank. , gradually accumulates on the auxiliary filtering section 253f (filtering section for cavitation treatment). As a result, the suction load on the main filtration pipe 180 by the main pump 175 increases, and the circulation flow rate of the main filtration pipe 180 gradually decreases on the upstream side of the branch point with the cavitation treatment pipe 1. However, because the configuration of the closed land aquaculture device shown in FIG. 1A is adopted, under any conditions, the flow rate distributed to the cavitation treatment piping 181 (i.e., cavitation nozzle 1) is within the specified flow rate range. I was able to keep it within. Regarding the filter 252f in the filtration tank 252, when the total flow rate of the main filtration pipe 180 drops to 30 L/min or less, the circulation is temporarily stopped and the filter 252f is replaced with a new one as appropriate. Note that the interior of the filter tank 252 is aerated with air by an aeration mechanism (not shown), and aerobic microorganisms such as Bacillus that are involved in humus formation are propagated, thereby simultaneously converting the filtered organic residue into humus. ing.

上記の養殖試験を開始後、30日、90日及び120日の各日数が経過後に下記の項目について確認・評価した。
(1)COD値
養殖水をサンプリングし、JIS K 0102(2013)17に規定の方法により各々測定した。
(2)平均体長
養殖中のエビを30匹無作為に抽出し、各々体長を測定して平均値を求めた。
(3)死滅率
養殖池上に斃死して浮上するエビの死骸の数を3時間ごとに確認し、各日までの合計斃死数から死滅率を算出した。なお、比較のため、図1においてキャビテーションノズル1を用いず、キャビテーション処理用配管181に気液ミキサー150のみを取り付けた場合についても、同様の実験を行なった(キャビテーション処理なし)。以上の結果を表2に示す。
The following items were confirmed and evaluated after 30 days, 90 days, and 120 days had elapsed after starting the above culture test.
(1) COD value Aquaculture water was sampled and measured according to the method specified in JIS K 0102 (2013) 17.
(2) Average body length Thirty shrimp under cultivation were randomly selected, and the body length of each shrimp was measured and the average value was determined.
(3) Mortality rate The number of shrimp carcasses that died and surfaced on the aquaculture pond was checked every 3 hours, and the mortality rate was calculated from the total number of dead shrimp for each day. For comparison, a similar experiment was also conducted in a case where the cavitation nozzle 1 in FIG. 1 was not used and only the gas-liquid mixer 150 was attached to the cavitation treatment piping 181 (no cavitation treatment). The above results are shown in Table 2.

Figure 0007410490000002
*は比較例。
Figure 0007410490000002
* is a comparative example.

養殖水の酸素濃度が本発明の範囲内となる番号2~5の酸素濃度については、キャビテーション処理を行なった養殖水を用いることにより、キャビテーション処理を行なわない養殖水を用いた場合と比較して、養殖水が同じ酸素濃度を示していてもエビの成長が格段に早いことが明らかである。また、キャビテーション処理を行なうことで養殖水のCOD値は顕著に低くなっており、養殖水の汚染が進みにくくなっていることがわかる。特に3~4ppmの低酸素濃度領域では、キャビテーション処理を行なわない場合のエビの死滅率が著しく高くなっているのに対し、キャビテーション処理を行なった場合の死滅率は大幅に低減されていることもわかる。 Regarding the oxygen concentration of numbers 2 to 5, where the oxygen concentration of the culture water is within the range of the present invention, by using culture water that has been subjected to cavitation treatment, compared to the case where culture water that has not been subjected to cavitation treatment is used. It is clear that shrimp grow much faster even when the culture water has the same oxygen concentration. Furthermore, by performing the cavitation treatment, the COD value of the cultured water was significantly lowered, indicating that the pollution of the cultured water was less likely to progress. Particularly in the low oxygen concentration region of 3 to 4 ppm, the mortality rate of shrimp without cavitation treatment is extremely high, whereas the mortality rate with cavitation treatment is significantly reduced. Recognize.

また、養殖水の酸素濃度が本発明の範囲の下限値を下回る番号1(2ppm)の条件の場合、キャビテーション処理を行なっても120日経過の時点で死滅率が高まっており、COD値の悪化が見られている。他方、養殖水の酸素濃度が本発明の範囲の上限値を上回る番号6の条件(7.5ppm)の場合、キャビテーション処理を行なわなかった場合よりも死滅率が高くなっていることがわかる。番号6の条件は酸素濃度が高いばかりでなく、養殖水W全体積に対するキャビテーションノズル1の流通循環比Kが大きいためキャビテーションノズル1にて100nm~30μm程度に成長した気泡の発生量が過剰となり、この気泡がエビのえらに付着して溶存酸素の取り込みが困難になったことが原因と考えられた。 In addition, in the case of condition No. 1 (2 ppm) in which the oxygen concentration of the culture water is lower than the lower limit of the range of the present invention, the mortality rate increases after 120 days even if cavitation treatment is performed, and the COD value worsens. is being watched. On the other hand, it can be seen that in the case of condition No. 6 (7.5 ppm) in which the oxygen concentration of the culture water exceeds the upper limit of the range of the present invention, the mortality rate is higher than when cavitation treatment is not performed. Condition No. 6 not only has a high oxygen concentration, but also has a large circulation ratio K of the cavitation nozzle 1 to the total volume of the culture water W, so the amount of bubbles that have grown to about 100 nm to 30 μm in the cavitation nozzle 1 is excessive. The cause was thought to be that these air bubbles adhered to the gills of the shrimp, making it difficult for them to take in dissolved oxygen.

(実施例2)
キャビテーションノズルとして、キャビテーション処理部の構造を図14の形態(絞り孔9を2個形成)に変更した以外は、図1Cに示すものと同様の寸法関係にて作成した。なお、各絞り孔の内径Dについてはφ3.9mm(キャビテーションノズルCと称する)及びφ4.9mm(キャビテーションノズルDと称する)の2種類用意した。また、大流量用として、図1Cに示すものと同様の絞り孔9が1組のキャビテーションノズルを、絞り孔内径Dがφ9.8mm(キャビテーションノズルEと称する)及びφ15.0mm(キャビテーションノズルFと称する)の2種類用意した。前者については図2に示す4本のねじからなる面ねじ組を2組とし、後者については面ねじ組を1~3組の各値にて、それぞれ互いに重なる位置関係にて配置している。いずれのノズルも70%谷点密度は2.0個/mm以上に確保されている
(Example 2)
A cavitation nozzle was created with the same dimensional relationship as that shown in FIG. 1C, except that the structure of the cavitation treatment section was changed to the form shown in FIG. 14 (two aperture holes 9 were formed). Two types of inner diameter D of each throttle hole were prepared: φ3.9 mm (referred to as cavitation nozzle C) and φ4.9 mm (referred to as cavitation nozzle D). In addition, for large flow applications, cavitation nozzles with a set of throttle holes 9 similar to those shown in FIG. Two types were prepared. For the former, there are two sets of surface screw sets consisting of four screws shown in FIG. 2, and for the latter, the set of surface screws are arranged at each value of 1 to 3 sets in a mutually overlapping positional relationship. The 70% valley point density of all nozzles is ensured at 2.0 pieces/mm2 or higher.

これらのノズルを図1Aの閉鎖型陸上養殖装置に組み込み、以下の試験条件にて実施例1と同様の実験及び評価を行なった。いずれの条件においても養殖水に対する設定酸素濃度は4ppmとし、被養殖物(バナメイエビ)の個体密度は200匹/tonとした。キャビテーションノズルCについては制御流量値を4.6~6.1L/分に設定することで、キャビテーション処理部における流速を7.5~9.9m/secの各値に調整した。キャビテーションノズルDについては制御流量値を6.0~11.7L/分に設定することで、キャビテーション処理部における流速を5.2~9.9m/secの各値に調整した。キャビテーションノズルE及びFについては制御流量値を33.1L/分及び86.7L/分に設定することで、キャビテーション処理部における流速を9.9m/secに調整した。また、養殖池の水量については50t~500tの範囲で種々設定しているが、キャビテーションノズルの種類及び流量との組み合わせにより、流通循環比Kの値が0.5%以上2%以下に収まるように設定されている。以上の結果を表3に示す(キャビテーション処理を行なったものにつき、90日目と120日目の結果を示している)。 These nozzles were incorporated into the closed land aquaculture apparatus shown in FIG. 1A, and experiments and evaluations similar to those in Example 1 were conducted under the following test conditions. Under all conditions, the set oxygen concentration for the culture water was 4 ppm, and the population density of the cultured product (vannamei shrimp) was 200 shrimp/ton. For cavitation nozzle C, the flow velocity in the cavitation treatment section was adjusted to each value of 7.5 to 9.9 m/sec by setting the control flow rate value to 4.6 to 6.1 L/min. For cavitation nozzle D, the flow velocity in the cavitation treatment section was adjusted to each value of 5.2 to 9.9 m/sec by setting the control flow rate value to 6.0 to 11.7 L/min. For cavitation nozzles E and F, the flow velocity in the cavitation treatment section was adjusted to 9.9 m/sec by setting the control flow values to 33.1 L/min and 86.7 L/min. In addition, the amount of water in the aquaculture pond is variously set in the range of 50t to 500t, but depending on the type of cavitation nozzle and the combination with the flow rate, the value of the distribution circulation ratio K can be kept within 0.5% or more and 2% or less. is set to . The above results are shown in Table 3 (results on the 90th and 120th day are shown for those subjected to cavitation treatment).

Figure 0007410490000003
Figure 0007410490000003

70%谷点面積密度が1.6個/mm以上のキャビテーションノズルを使用し、キャビテーション処理部における平均流速が8m/secとなる条件が確保されている条件(番号51、53、54、56、56~58)では、実施例1の酸素濃度4ppm(番号3)のキャビテーションなしの場合と比較しても明らかな通り、エビの成長が促進され、水質を示すCOD値も良好に維持され、死滅率も低いことがわかる。一方、キャビテーション処理部における平均流速が8m/sec未満となる比較例(番号52、55)については、死滅率が高く、COD値も悪化していることがわかる。また、70%谷点面積密度が1.6個/mmを下回るキャビテーションノズルを使用した番号59の条件では、70%谷点面積密度が1.6個/mm以上のキャビテーションノズルを使用した場合と比較して、エビの成長がやや遅く、死滅率も増加していることがわかる。 Conditions where a cavitation nozzle with a 70% valley point area density of 1.6 pieces/mm2 or more is used and the average flow velocity in the cavitation treatment section is 8 m/sec (numbers 51, 53, 54, 56) , 56 to 58), shrimp growth is promoted and the COD value indicating water quality is maintained well, as is clear from comparison with the case of Example 1 with an oxygen concentration of 4 ppm (number 3) without cavitation. It can be seen that the mortality rate is also low. On the other hand, it can be seen that in the comparative examples (numbers 52 and 55) in which the average flow velocity in the cavitation treatment section is less than 8 m/sec, the mortality rate is high and the COD value is also deteriorated. In addition, under the condition No. 59 in which a cavitation nozzle with a 70% valley point area density of less than 1.6 pieces/ mm2 was used, a cavitation nozzle with a 70% valley point area density of 1.6 pieces/mm2 or more was used. It can be seen that the growth of shrimp is slightly slower and the mortality rate is increased compared to the case.

(実施例3)
実施例1と全く同じキャビテーションノズルA,Bを図10の気液ミキサー150とともに図1Aの閉鎖型陸上養殖装置300に組み込み、養殖池250に塩分濃度が3.5%の人工海水を50t(水深:約2m)注入するとともに、主ポンプ175による循環を初期流量100L/分にて開始した。そして、各ノズルA,Bについて実施例1と同じ流量設定となるように、分配バルブ183の開度を制御する一方、養殖水の制御目標となる酸素濃度を、4.0ppm~7.5ppm(7.5ppm)は比較例)となるように設定し、図1Aの電磁バルブ184及び174を駆動制御して養殖水の酸素濃度を各設定値に維持した。散気部174の空気噴出流量は50NL/分(平均気泡径:0.3mm)とした。キャビテーションノズル1への空気供給流量は、大気圧換算での体積流量(NL/分)にて水流量の10%となるように調整した。また、図示しない圧力計にて計測した上記流量設定時のキャビテーションノズルの動水圧の値と、流量値と全流通断面積とから算出した絞り孔(キャビテーション処理部)内の平均流速の値も表1に合わせて示している。いずれの条件においても、キャビテーション処理部の平均流速は9m/秒以上の値に確保されている。
(Example 3)
Cavitation nozzles A and B, which are exactly the same as in Example 1, are incorporated into the closed land aquaculture device 300 of FIG. 1A together with the gas-liquid mixer 150 of FIG. : approximately 2 m), and circulation by the main pump 175 was started at an initial flow rate of 100 L/min. Then, while controlling the opening degree of the distribution valve 183 so that the flow rate setting is the same as in Example 1 for each nozzle A and B, the oxygen concentration, which is the control target of the aquaculture water, is set to 4.0 ppm to 7.5 ppm ( 7.5 ppm) in the comparative example), and the electromagnetic valves 184 and 174 in FIG. 1A were driven and controlled to maintain the oxygen concentration of the culture water at each set value. The air ejection flow rate of the air diffuser 174 was set to 50 NL/min (average bubble diameter: 0.3 mm). The air supply flow rate to the cavitation nozzle 1 was adjusted to be 10% of the water flow rate in terms of volumetric flow rate (NL/min) converted to atmospheric pressure. In addition, the value of the dynamic hydraulic pressure of the cavitation nozzle at the above flow rate setting measured with a pressure gauge (not shown), and the value of the average flow velocity in the throttle hole (cavitation processing section) calculated from the flow rate value and the total flow cross-sectional area are also displayed. It is shown according to 1. Under any conditions, the average flow velocity in the cavitation treatment section was maintained at a value of 9 m/sec or more.

この状態で、40匹/トンの個体密度となるように真鯛の稚魚を投入するとともに、池内の真鯛には、イワシ系のモイストペレットを真鯛の成長度合いに応じて適宜投与し、飼育を行なった。本実施形態においても、濾過槽252内のフィルタ252fは濾過用主配管180の総流量が30L/分以下に低下した場合は、一旦循環を止めて新しいものと適宜交換するようにした。また、濾過槽252内は図示しないばっ気機構により空気ばっ気を行ない、好気性微生物を繁殖させることにより、濾過された有機残渣の腐植化を同時に行なうようにしている。 In this state, young red sea bream were introduced to achieve an individual density of 40 fish/ton, and sardine-based moist pellets were administered to the red sea bream in the pond as appropriate depending on the growth level of the red sea bream. . Also in this embodiment, when the total flow rate of the main filtration pipe 180 drops to 30 L/min or less, the filter 252f in the filtration tank 252 is temporarily stopped circulating and replaced with a new one as appropriate. Furthermore, the inside of the filtration tank 252 is aerated with air by an aeration mechanism (not shown), thereby propagating aerobic microorganisms, thereby simultaneously converting the filtered organic residue into humus.

上記の養殖試験を開始後、240日及び510日の各日数が経過後に、真鯛の平均体重と死滅率とを計測した。なお、比較のため、図1においてキャビテーションノズル1を用いず、キャビテーション処理用配管181に気液ミキサー150のみを取り付けた場合についても、同様の実験を行なった(キャビテーション処理なし)。以上の結果を表4に示す。 After 240 days and 510 days had elapsed after starting the above culture test, the average weight and mortality rate of the red sea bream were measured. For comparison, a similar experiment was also conducted in a case where the cavitation nozzle 1 in FIG. 1 was not used and only the gas-liquid mixer 150 was attached to the cavitation treatment piping 181 (no cavitation treatment). The above results are shown in Table 4.

Figure 0007410490000004
Figure 0007410490000004

養殖水の酸素濃度が本発明の範囲内となる番号101、102の酸素濃度については、キャビテーション処理を行なった養殖水を用いることで、キャビテーション処理を行なわない養殖水を用いた場合と比較して、養殖水が同じ酸素濃度を示していても真鯛の成長が格段に早いことが明らかである。特に4ppmの低酸素濃度領域では、キャビテーション処理を行なわない場合の真鯛の死滅率が著しく高くなっているのに対し、キャビテーション処理を行なった場合の死滅率は大幅に低減されていることもわかる。他方、養殖水の酸素濃度が本発明の範囲の上限値を上回る番号103の条件(7.5ppm)の場合、キャビテーション処理を行なわなかった場合よりも死滅率が高くなっていることがわかる。 Regarding the oxygen concentration of numbers 101 and 102, where the oxygen concentration of the culture water is within the range of the present invention, by using culture water that has been subjected to cavitation treatment, compared to the case where culture water that has not been subjected to cavitation treatment is used. It is clear that red sea bream grow much faster even if the culture water has the same oxygen concentration. In particular, it can be seen that in the low oxygen concentration region of 4 ppm, the mortality rate of red sea bream is significantly high when cavitation treatment is not performed, whereas the mortality rate when cavitation treatment is performed is significantly reduced. On the other hand, it can be seen that in the case of condition No. 103 (7.5 ppm) in which the oxygen concentration of the culture water exceeds the upper limit of the range of the present invention, the mortality rate is higher than when no cavitation treatment is performed.

1 キャビテーションノズル
2 ノズル本体
3 ノズル流路
5 養殖水出口
4 養殖水入口
9 絞り孔
10 ねじ部材
150 気液ミキサー
151 外筒部材
155 流路形成部材
156 螺旋区間
157 第一螺旋状流路
158 第二螺旋状流路
159 流入口
160 流出口
165 混相流供給部
174 散気部
175 主ポンプ
180 濾過用主配管
181 キャビテーション処理用配管
181p キャビテーション処理用ポンプ
182 流量検出部
183 分配バルブ
185 キャビテーション流量制御部
250 養殖池
252 濾過槽
253f 補助フィルタリング部(キャビテーション処理用濾過部)
300 閉鎖型陸上養殖装置
W 養殖水
SP 被養殖物
LP1~LP4 ねじ配置面
CV キャビテーション処理部

1 Cavitation nozzle 2 Nozzle body 3 Nozzle channel 5 Culture water outlet 4 Culture water inlet 9 Throttle hole 10 Screw member 150 Gas-liquid mixer 151 Outer cylinder member 155 Channel forming member 156 Spiral section 157 First spiral channel 158 Second Spiral flow path 159 Inlet 160 Outlet 165 Multiphase flow supply section 174 Diffusion section 175 Main pump 180 Main filtration piping 181 Cavitation treatment piping 181p Cavitation treatment pump 182 Flow rate detection section 183 Distribution valve 185 Cavitation flow control section 250 Aquaculture pond 252 Filtration tank 253f Auxiliary filtering section (filtration section for cavitation treatment)
300 Closed land aquaculture equipment W Aquaculture water SP Cultured product LP1 to LP4 Screw arrangement surface CV Cavitation treatment section

Claims (9)

養殖池内に養殖水と甲殻類又は魚類からなる被養殖動物とを収容し、主ポンプを用いて前記養殖池から前記養殖水を濾過槽に導き、前記養殖水中に浮遊する有機残渣を濾過しつつ前記養殖池内に戻して循環させながら、前記養殖池内に飼料を投入して前記被養殖動物を飼育するための閉鎖型陸上養殖装置において、
前記養殖水の酸素濃度が2.5ppm以上7ppm以下に維持されるように前記養殖水に酸素含有気体を供給しつつ溶解する酸素溶解機構と、
前記養殖池に前記養殖水の流入口が連通するとともに、他端側が前記養殖水の前記養殖池への戻し口とされたキャビテーション処理用配管と、
前記キャビテーション処理用配管の途上に設けられ、一端に前記養殖水の入口を、他端に前記養殖水の出口を有するノズル流路が形成されるとともに、該ノズル流路の一部区間がキャビテーション処理部として定められたノズル本体と、前記キャビテーション処理部にて前記ノズル流路の中心軸線と直交する仮想的なねじ配置面内に前記ノズル本体に脚部先端側が流路内側に突出するように組付けられる複数のねじ部材とを備え、前記ねじ配置面における全流通断面積が3.8mm以上確保されるとともに、前記養殖水を前記養殖水入口から前記養殖水出口に向けて流通させ、前記キャビテーション処理部にて前記ねじ部材の脚部外周面に形成されたねじ谷に前記養殖水を増速しつつ接触させることにより、該養殖水に対し溶存空気の減圧析出に基づくキャビテーション処理を行なうキャビテーションノズルと、
前記キャビテーション処理用配管の途上において前記主ポンプに兼用されているか又は前記主ポンプとは独立に設けられ、前記キャビテーションノズルに前記養殖水を、前記キャビテーション処理部における断面平均流速が8m/sec以上となるよう前記キャビテーションノズルの前記全流通断面積に応じて定められる規定流量にて流通させるキャビテーション処理用ポンプと、
を備え、
前記酸素溶解機構は、前記キャビテーションノズルとは別に設けられた、前記養殖池を満たす養殖水に外部から供給される前記酸素含有気体を平均気泡径が0.1mm以上0.5mm以下となるように噴射する散気部を含むことを特徴とする閉鎖型陸上養殖装置。
Culture water and cultured animals consisting of crustaceans or fish are housed in an aquaculture pond, and a main pump is used to guide the aquaculture water from the aquaculture pond to a filter tank, while filtering organic residues floating in the aquaculture water. In a closed land aquaculture device for raising the cultured animals by feeding feed into the aquaculture pond while circulating it back into the aquaculture pond,
an oxygen dissolving mechanism that dissolves while supplying an oxygen-containing gas to the culture water so that the oxygen concentration of the culture water is maintained at 2.5 ppm or more and 7 ppm or less;
a cavitation treatment pipe whose inlet of the aquaculture water communicates with the aquaculture pond, and whose other end serves as a return port for the aquaculture water to the aquaculture pond;
A nozzle flow path is provided in the middle of the cavitation treatment piping and has an inlet of the culture water at one end and an outlet of the culture water at the other end, and a part of the nozzle flow path is subjected to the cavitation treatment. A nozzle body defined as a part is assembled in the cavitation treatment part in a virtual screw arrangement plane perpendicular to the central axis of the nozzle flow path so that the tip end side of the leg protrudes inside the flow path. a plurality of screw members to be attached, the total flow cross-sectional area on the screw arrangement surface is ensured to be 3.8 mm 2 or more, and the culture water is made to flow from the culture water inlet to the culture water outlet, Cavitation treatment in which cavitation treatment is performed on the culture water based on reduced pressure precipitation of dissolved air by bringing the culture water into contact with the thread valley formed on the outer circumferential surface of the leg of the threaded member at a cavitation treatment section while increasing the speed. a nozzle and
In the middle of the cavitation treatment piping, it is also used as the main pump or is provided independently from the main pump, and the culture water is supplied to the cavitation nozzle at an average cross-sectional flow velocity of 8 m/sec or more in the cavitation treatment section. a cavitation treatment pump that causes the flow to flow at a prescribed flow rate determined according to the total flow cross-sectional area of the cavitation nozzle;
Equipped with
The oxygen dissolving mechanism is provided separately from the cavitation nozzle and is configured to supply the oxygen-containing gas from the outside to the aquaculture water filling the aquaculture pond so that the average bubble diameter is 0.1 mm or more and 0.5 mm or less. A closed land aquaculture device characterized by including a diffuser that sprays air.
養殖池内に養殖水と甲殻類又は魚類からなる被養殖動物とを収容し、主ポンプを用いて前記養殖池から前記養殖水を濾過槽に導き、前記養殖水中に浮遊する有機残渣を濾過しつつ前記養殖池内に戻して循環させながら、前記養殖池内に飼料を投入して前記被養殖動物を飼育するための閉鎖型陸上養殖装置において、
前記養殖水の酸素濃度が2.5ppm以上7ppm以下に維持されるように前記養殖水に酸素含有気体を供給しつつ溶解する酸素溶解機構と、
前記養殖池に前記養殖水の流入口が連通するとともに、他端側が前記養殖水の前記養殖池への戻し口とされたキャビテーション処理用配管と、
前記キャビテーション処理用配管の途上に設けられ、一端に前記養殖水の入口を、他端に前記養殖水の出口を有するノズル流路が形成されるとともに、該ノズル流路の一部区間がキャビテーション処理部として定められたノズル本体と、前記キャビテーション処理部にて前記ノズル流路の中心軸線と直交する仮想的なねじ配置面内に前記ノズル本体に脚部先端側が流路内側に突出するように組付けられる複数のねじ部材とを備え、前記ねじ配置面における全流通断面積が3.8mm 以上確保されるとともに、前記養殖水を前記養殖水入口から前記養殖水出口に向けて流通させ、前記キャビテーション処理部にて前記ねじ部材の脚部外周面に形成されたねじ谷に前記養殖水を増速しつつ接触させることにより、該養殖水に対し溶存空気の減圧析出に基づくキャビテーション処理を行なうキャビテーションノズルと、
前記キャビテーション処理用配管の途上において前記主ポンプに兼用されているか又は前記主ポンプとは独立に設けられ、前記キャビテーションノズルに前記養殖水を、前記キャビテーション処理部における断面平均流速が8m/sec以上となるよう前記キャビテーションノズルの前記全流通断面積に応じて定められる規定流量にて流通させるキャビテーション処理用ポンプと、
を備え、
前記酸素溶解機構は、前記キャビテーションノズルにて前記酸素含有気体を溶解するために、前記キャビテーションノズルに前記酸素含有気体と前記養殖水との混相流を供給する混相流供給部を含み、前記キャビテーションノズルは前記酸素溶解機構の一部として機能することを特徴とする閉鎖型陸上養殖装置
Culture water and cultured animals consisting of crustaceans or fish are housed in an aquaculture pond, and a main pump is used to guide the aquaculture water from the aquaculture pond to a filter tank, while filtering organic residues floating in the aquaculture water. In a closed land aquaculture device for raising the cultured animals by feeding feed into the aquaculture pond while circulating it back into the aquaculture pond,
an oxygen dissolving mechanism that dissolves while supplying an oxygen-containing gas to the culture water so that the oxygen concentration of the culture water is maintained at 2.5 ppm or more and 7 ppm or less;
a cavitation treatment pipe whose inlet of the aquaculture water communicates with the aquaculture pond, and whose other end serves as a return port for the aquaculture water to the aquaculture pond;
A nozzle flow path is provided in the middle of the cavitation treatment piping and has an inlet of the culture water at one end and an outlet of the culture water at the other end, and a part of the nozzle flow path is subjected to the cavitation treatment. A nozzle body defined as a part is assembled in the cavitation treatment part in a virtual screw arrangement plane perpendicular to the central axis of the nozzle flow path so that the tip end side of the leg protrudes inside the flow path. a plurality of screw members to be attached, the total flow cross-sectional area on the screw arrangement surface is ensured to be 3.8 mm 2 or more, and the culture water is made to flow from the culture water inlet to the culture water outlet, Cavitation treatment in which cavitation treatment is performed on the culture water based on reduced pressure precipitation of dissolved air by bringing the culture water into contact with the thread valley formed on the outer circumferential surface of the leg of the threaded member at a cavitation treatment section while increasing the speed. a nozzle and
In the middle of the cavitation treatment piping, it is also used as the main pump or is provided independently from the main pump, and the culture water is supplied to the cavitation nozzle at an average cross-sectional flow velocity of 8 m/sec or more in the cavitation treatment section. a cavitation treatment pump that causes the flow to flow at a prescribed flow rate determined according to the total flow cross-sectional area of the cavitation nozzle;
Equipped with
The oxygen dissolving mechanism includes a multiphase flow supply unit that supplies a multiphase flow of the oxygen-containing gas and the culture water to the cavitation nozzle in order to dissolve the oxygen-containing gas in the cavitation nozzle, and the cavitation nozzle A closed terrestrial aquaculture device characterized in that functions as a part of the oxygen dissolution mechanism .
一端に流入口、他端に流出口が形成される中空の外筒部材と、前記外筒部材の内側に設けられ、前記流入口と前記流出口とをつなぐ螺旋状流路を、該螺旋状流路の螺旋軸線が前記外筒部材の中心軸線に沿うように形成する流路形成部材とを備え、前記螺旋状流路が前記キャビテーションノズルの前記ノズル流路に連通するように、前記キャビテーションノズルの前記養殖水入口側に設けられる気液ミキサーを備え、
前記混相流供給部は、前記気液ミキサーの前記流入口に前記混相流を供給するものである請求項2記載の閉鎖型陸上養殖装置
A hollow outer cylindrical member having an inlet at one end and an outlet at the other end, and a spiral flow path provided inside the outer cylindrical member and connecting the inlet and the outlet. a flow path forming member formed such that a helical axis of the flow path is along a central axis of the outer cylindrical member, and the cavitation nozzle is configured such that the helical flow path communicates with the nozzle flow path of the cavitation nozzle. a gas-liquid mixer provided on the inlet side of the aquaculture water,
The closed land aquaculture apparatus according to claim 2, wherein the multiphase flow supply section supplies the multiphase flow to the inlet of the gas-liquid mixer..
前記酸素溶解機構は前記養殖水の酸素濃度が3ppm以上6ppm以下に維持されるように前記養殖水に前記酸素含有気体を供給しつつ溶解するものである請求項1から3のいずれか1項に記載の閉鎖型陸上養殖装置。 4. The oxygen dissolving mechanism is configured to dissolve the oxygen-containing gas while supplying the oxygen-containing gas to the culture water so that the oxygen concentration of the culture water is maintained at 3 ppm or more and 6 ppm or less. The closed land aquaculture device described. 前記キャビテーションノズルは、前記ノズル流路が円形断面を有するものとして形成され、各前記キャビテーション処理部には前記ねじ部材として、ねじピッチ及びねじ谷深さが0.20mm以上0.40mm以下、公称ねじ径Mが1.0mm以上2.0mm以下のねじ部材が複数配置されるとともに、前記ノズル流路の中心軸線と直交する平面への投影にて前記ノズル流路の断面中心から該ノズル流路の半径の70%以内の領域に位置する谷点の全ねじ配置面間で合計した総数を、前記ノズル流路の断面積で除した70%谷点面積密度と定義したとき、前記70%谷点面積密度の値が1.6個/mm2以上に確保されたものが使用されてなる請求項1から4のいずれか1項に記載の閉鎖型陸上養殖装置。 The cavitation nozzle is formed such that the nozzle flow path has a circular cross section, and each of the cavitation treatment parts has a threaded member having a thread pitch and a thread depth of 0.20 mm or more and 0.40 mm or less, and a nominal thread. A plurality of screw members having a diameter M of 1.0 mm or more and 2.0 mm or less are arranged, and the nozzle flow path is connected from the cross-sectional center of the nozzle flow path when projected onto a plane perpendicular to the central axis of the nozzle flow path. The 70% valley point is defined as the 70% valley point area density, which is defined as the total number of valley points located within 70% of the radius between all screw placement surfaces divided by the cross-sectional area of the nozzle flow path. The closed land aquaculture device according to any one of claims 1 to 4, wherein an area density value of 1.6 pieces/mm2 or more is used. 前記キャビテーションノズルの1時間当たりの流通流量が、前記養殖池の貯水量をV1、前記キャビテーションノズルの1時間当たりの流通流量をV2として、
K=V2/V1×100 (%)
にて表される流通循環比Kが2%以下となるように調整される請求項に記載の閉鎖型陸上養殖装置。
The flow rate of the cavitation nozzle per hour is V1, the water storage amount of the aquaculture pond is V2, and the flow rate of the cavitation nozzle per hour is V2.
K=V2/V1×100 (%)
The closed land aquaculture device according to claim 5 , wherein the distribution/circulation ratio K expressed by is adjusted to be 2% or less.
前記キャビテーション処理用配管の前記流入口に設けられ、前記養殖池内の浮遊物が前記キャビテーション処理用配管内に流入することを抑制するキャビテーション処理用濾過部と、
前記キャビテーション処理用配管内を流通する前記養殖水の流量を検出する流量検出部と、
前記キャビテーション処理用濾過部への前記浮遊物の堆積に伴う流量損失を補う形で、前記キャビテーション処理用ポンプによる前記キャビテーションノズルへの送液流量を前記規定流量に制御するキャビテーション流量制御部とを備える請求項1ないし請求項のいずれか1項に記載の閉鎖型陸上養殖装置。
a cavitation treatment filtration section that is provided at the inlet of the cavitation treatment piping and suppresses floating matter in the aquaculture pond from flowing into the cavitation treatment piping;
a flow rate detection unit that detects the flow rate of the aquaculture water flowing through the cavitation treatment piping;
and a cavitation flow rate control unit that controls the flow rate of liquid sent to the cavitation nozzle by the cavitation treatment pump to the specified flow rate in order to compensate for the flow rate loss due to the accumulation of suspended matter in the cavitation treatment filtration unit. The closed land aquaculture device according to any one of claims 1 to 6 .
前記濾過槽に前記養殖水の流入口が連通するとともに、他端側が前記養殖水の前記養殖池への戻し口とされた濾過用主配管と、
前記濾過用主配管の前記流入口に設けられ、前記濾過槽内の浮遊物が前記濾過用主配管内に流入することを抑制する補助フィルタリング部とを備え、前記主ポンプが前記濾過用主配管上に設けられるとともに、
前記キャビテーション処理用配管が、前記主ポンプの下流側にて前記濾過用主配管から分岐し、かつ、前記濾過用主配管とは別位置にて前記養殖池に対する前記戻し口を開口させる形で設けられ、
また、前記養殖水の前記主配管と前記キャビテーション処理用配管との分配比をバルブ開度に応じて調整する分配バルブが設けられ、
前記主ポンプが前記キャビテーション処理用ポンプに、前記補助フィルタリング部が前記キャビテーション処理用濾過部にそれぞれ兼用されるとともに、
前記キャビテーション流量制御部は、前記補助フィルタリング部への前記浮遊物の堆積に伴い前記主ポンプの送水流量が減少した場合に、前記養殖水の前記キャビテーション処理用配管への分配比が増加するように前記分配バルブの開度を調整制御するものである請求項に記載の閉鎖型陸上養殖装置。
a main pipe for filtration, the inlet of the aquaculture water communicating with the filtration tank, and the other end serving as a return port of the aquaculture water to the aquaculture pond;
an auxiliary filtering section that is provided at the inlet of the main filtration pipe and suppresses floating substances in the filtration tank from flowing into the main filtration pipe, and the main pump is connected to the main filtration pipe. Along with being provided on top,
The cavitation treatment pipe is provided in such a manner that it branches from the main filtration pipe on the downstream side of the main pump, and opens the return port to the aquaculture pond at a position different from the main filtration pipe. is,
Further, a distribution valve is provided that adjusts a distribution ratio between the main piping and the cavitation treatment piping of the aquaculture water according to a valve opening degree,
The main pump is also used as the cavitation treatment pump, and the auxiliary filtering section is also used as the cavitation treatment filtration section, and
The cavitation flow rate control unit is configured to increase a distribution ratio of the aquaculture water to the cavitation treatment piping when the flow rate of the main pump decreases due to the accumulation of suspended matter in the auxiliary filtering unit. The closed land aquaculture apparatus according to claim 7 , wherein the opening degree of the distribution valve is adjusted and controlled.
請求項1ないし請求項のいずれか1項に記載の閉鎖型陸上養殖装置を用い、前記養殖池内に前記養殖水と前記被養殖動物とを収容し、前記主ポンプを用いて前記養殖池から前記養殖水を前記濾過槽に導き、前記養殖水中に浮遊する有機残渣を濾過しつつ前記養殖池内に戻して循環させながら、前記養殖池内に飼料を投入して前記被養殖動物を飼育することを特徴とする陸上養殖方法。 Using the closed land aquaculture apparatus according to any one of claims 1 to 8 , the aquaculture water and the cultured animals are accommodated in the aquaculture pond, and the main pump is used to remove the aquaculture water from the aquaculture pond. The aquaculture water is introduced into the filtration tank, and while organic residues floating in the aquaculture water are filtered and circulated back into the aquaculture pond, feed is introduced into the aquaculture pond to raise the aquaculture animals. Characteristic land-based aquaculture method.
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