Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPS5950289B2 - Method and equipment for breeding benthic fish - Google Patents
[go: Go Back, main page]

JPS5950289B2 - Method and equipment for breeding benthic fish - Google Patents

Method and equipment for breeding benthic fish

Info

Publication number
JPS5950289B2
JPS5950289B2 JP56067429A JP6742981A JPS5950289B2 JP S5950289 B2 JPS5950289 B2 JP S5950289B2 JP 56067429 A JP56067429 A JP 56067429A JP 6742981 A JP6742981 A JP 6742981A JP S5950289 B2 JPS5950289 B2 JP S5950289B2
Authority
JP
Japan
Prior art keywords
tank
water
sand layer
pedestal
organic residue
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired
Application number
JP56067429A
Other languages
Japanese (ja)
Other versions
JPS57181626A (en
Inventor
淳 久保
高司 中村
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Mitsui Engineering and Shipbuilding Co Ltd
Original Assignee
Mitsui Engineering and Shipbuilding Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Mitsui Engineering and Shipbuilding Co Ltd filed Critical Mitsui Engineering and Shipbuilding Co Ltd
Priority to JP56067429A priority Critical patent/JPS5950289B2/en
Publication of JPS57181626A publication Critical patent/JPS57181626A/en
Publication of JPS5950289B2 publication Critical patent/JPS5950289B2/en
Expired legal-status Critical Current

Links

Classifications

    • 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/80Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in fisheries management
    • Y02A40/81Aquaculture, e.g. of fish

Landscapes

  • Farming Of Fish And Shellfish (AREA)

Description

【発明の詳細な説明】 この発明は、底棲魚類の増養殖方法およびその装置に係
り、その目的とするところは水槽内の水質の悪化を防止
し、底棲魚類の収容密度を高めるとともに、発生する有
機物を餌料の一部として利用せんとするものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method and apparatus for breeding benthic fish, and its purpose is to prevent deterioration of water quality in an aquarium, increase the housing density of benthic fish, and The aim is to use the organic matter generated as part of the feed.

従来、底棲魚類例えばクルマエビの養殖形態は廃止塩田
跡を利用した方式、海岸に堤防を築いた方式、陸上水槽
方式の三つに大別され、いずれも給餌養殖であり底面は
砂層が形成されている。
Traditionally, the cultivation methods for benthic fish such as prawns have been roughly divided into three types: methods using abandoned salt fields, methods built on coastal embankments, and land-based aquarium methods. All of these methods involve feeding, and a sand layer is formed on the bottom. ing.

砂層の表面においては、残餌、排泄物などの有機物の堆
積があり、とくに収容密度が高い場合は多量に発生し、
腐敗、ヘドロ化の傾向をたどり、硫化物の発生や病原性
細菌の繁殖などの悪条件の要素となっている。
On the surface of the sand layer, organic matter such as leftover food and excrement is deposited, especially in large quantities when the housing density is high.
It tends to rot and turn into sludge, and is an element of adverse conditions such as the generation of sulfides and the growth of pathogenic bacteria.

これらの条件により収容密度は成長および歩留りに密接
な関係を有することとなり、これらの影響を免れるため
には止むなく収容密度を低く押えたり、高密度に収容し
た場合には多量の換水により有機物の残渣を系外に排出
する方法が採られている。
Due to these conditions, the packing density has a close relationship with growth and yield, and in order to avoid these effects, it is necessary to keep the packing density low, or if the packing density is high, the organic matter is removed by large amounts of water exchange. A method is used to discharge the residue out of the system.

しかしながら収容密度を低く押えることは生産量に大き
く影響を及ぼし、高密度に収容し、多量の換水操作によ
す環境悪化防止する方法では換水に要する電気等のエネ
ルギーの大量消費に加えて有機物残渣の未利用といった
資源エネルギーのロスにつながるものであるとともに、
これら有機物残渣を地先海域に放出することとなり、沿
岸海域の汚染を助長する要因ともなっている。
However, keeping the storage density low has a significant impact on production, and methods to prevent environmental deterioration due to high density storage and large volume water changes consume a large amount of energy such as electricity required for water changes, and generate organic residue. This leads to the loss of resource energy such as unused energy, and
These organic residues are released into the surrounding sea area, and are a contributing factor to the pollution of coastal sea areas.

この発明は上記の収容密度、及び有機物残渣に関し水槽
を使用し発生する有機物を有効に利用することにより、
従来の欠点を解消し高密度の収容、並びに給餌量の節約
を行う増養殖法および装置である。
This invention achieves the above-mentioned storage density and organic matter residue by effectively utilizing the organic matter generated by using a water tank.
This is an aquaculture method and device that eliminates the drawbacks of the conventional methods, allows for high-density housing, and saves on the amount of feed.

以下本発明の具体的実施例を図面を参照することにより
詳述する。
Hereinafter, specific embodiments of the present invention will be described in detail with reference to the drawings.

1は円形水槽で、コンクリートブロック、鉄板等で製作
されており、底部はコンクリートあるいはビニール、ゴ
ム等のシートを敷いても可能で底面には砂層15を設け
ている。
1 is a circular water tank made of concrete blocks, iron plates, etc., and the bottom can be covered with concrete or a sheet of vinyl, rubber, etc., and a sand layer 15 is provided on the bottom.

2は架橋で、円形水槽1の中心部に設けた架台9を中心
に槽の外壁上に設けた走行路10上を駆動モーター11
および駆動輪12からなる駆動装置の働きにより、1時
間当り1〜5回転の速さで常時ゆるやかに走行する。
Reference numeral 2 is a bridge in which a drive motor 11 runs on a running path 10 provided on the outer wall of the tank, centering on a pedestal 9 provided at the center of the circular water tank 1.
Due to the action of a drive device consisting of drive wheels 12, the vehicle always runs slowly at a speed of 1 to 5 revolutions per hour.

また架橋2には旋回流水管3、ジェット噴流水管4およ
び自動給餌器13、溶存酸素計14等を設ける。
The bridge 2 is also provided with a swirling water pipe 3, a jet water pipe 4, an automatic feeder 13, a dissolved oxygen meter 14, and the like.

旋回流水管3は噴射ノズルを有し、ポンプ5により供給
された槽内水を噴射ノズルから槽1の接線方向にシャワ
ー状に放出することにより、曝気を兼ねて槽内に旋回流
を生じさせ、全ての浮遊物質を槽中心部に集める。
The swirling flow water pipe 3 has an injection nozzle, and by discharging the tank water supplied by the pump 5 from the injection nozzle in the tangential direction of the tank 1 in the form of a shower, a swirling flow is generated in the tank, which also serves as aeration. , all suspended solids are collected in the center of the tank.

ジェット噴流管4は先端部を水槽底部付近まで延出させ
ており、かつ端部は架橋2の長手方向に対し水槽外壁に
むかい30度の開きを持つ数本の管に分割した噴射ノズ
ルを有し、ポンプ5により供給された槽内水の一部を砂
層15表面に向は噴出させる。
The jet stream pipe 4 has a tip extending to near the bottom of the water tank, and the end has an injection nozzle divided into several pipes having an opening of 30 degrees toward the outer wall of the water tank in the longitudinal direction of the bridge 2. Then, a part of the tank water supplied by the pump 5 is spouted onto the surface of the sand layer 15.

またタイマー設定による電磁弁16を設は旋回流水管3
への流入を停止させ、全量をジェット噴流水管4より噴
射可能に設計されている。
In addition, the solenoid valve 16 is set by the timer setting to the swirling water pipe 3.
It is designed to be able to stop the flow into the jet water pipe 4 and inject the entire amount from the jet water pipe 4.

ポンプ5の吸入口17は架台9の下部に設けられており
、水流に応じて架台9に設けられた水処理部分6を通じ
て槽内水を吸出するか又は換水時には排水口18に排出
される。
The suction port 17 of the pump 5 is provided at the lower part of the pedestal 9, and depending on the water flow, the water in the tank is sucked out through the water treatment part 6 provided in the pedestal 9, or is discharged to the drain port 18 during water change.

さらにポンプ5はパイプ23により新鮮な海水を導入す
ることも可能である。
Furthermore, the pump 5 can also introduce fresh seawater via a pipe 23.

水処理部分6には合成樹脂等で作られた単位容積当りの
表面積がioo〜200 m’/yの廃水処理に使用さ
れる接触酸化材24を充填している。
The water treatment section 6 is filled with a catalytic oxidizing material 24 made of synthetic resin or the like and having a surface area per unit volume of ioo to 200 m'/y and used for wastewater treatment.

7はプロワ−で槽内水を循環させる配管途中に設けたエ
ジェクター8を通じて空気を混入し槽内へ噴射させるも
のである。
Reference numeral 7 designates a blower for mixing air into the tank through an ejector 8 installed in the middle of the piping for circulating the water in the tank and injecting it into the tank.

但しブロワ−7は槽内に設けた溶存酸素計14と制御盤
19を通じて連動するもので、溶存酸素量の一定数値を
下回った時点でのみ作動する構造としている。
However, the blower 7 is linked to a dissolved oxygen meter 14 provided in the tank through a control panel 19, and is designed to operate only when the amount of dissolved oxygen falls below a certain value.

制御盤19は、自動給餌器13、電磁弁16、駆動モー
ター11を制御するもので、これらの電源および溶存酸
素計14から送られる信号は、架台9内に設置したスリ
ップリングボックス20を通じて制御盤と連結している
The control panel 19 controls the automatic feeder 13, the solenoid valve 16, and the drive motor 11. Signals sent from these power sources and the dissolved oxygen meter 14 are sent to the control panel through a slip ring box 20 installed in the frame 9. It is connected with.

更に架台9側面の水処理部分6には網21が取り付けら
れ網21の目づまりを防止するクリーニングブラシ22
が架橋2に付設されている。
Furthermore, a net 21 is attached to the water treatment portion 6 on the side of the pedestal 9, and a cleaning brush 22 is installed to prevent the net 21 from clogging.
is attached to the bridge 2.

以上のように本発明は水槽において旋回流水管及びジェ
ット噴流水管にてその水面上及び砂層面上に空気を含む
噴流を噴出させ、しかも噴流管を槽内で回転移動させ、
水槽内の有機物残渣を常に好気性に維持しながら攪乱し
、浮遊状態にするため有機物残渣の停滞、腐敗、ヘドロ
化への移行を防止してクルマエビの主たる棲息場所であ
る底砂層の環境悪化を防ぎ、底面全域がこの状態に維持
される。
As described above, the present invention jets a jet containing air onto the water surface and sand layer surface using a swirling water pipe and a jet jet water pipe in an aquarium, and furthermore, rotates and moves the jet pipe within the tank.
The organic residue in the aquarium is constantly maintained in an aerobic state while being disturbed and suspended, preventing organic residue from stagnation, decay, and turning into sludge, thereby preventing environmental deterioration of the bottom sand layer, which is the main habitat of prawns. The entire bottom surface is maintained in this state.

又、浮遊、攪乱された有機物残渣は旋回流の働きで槽中
央部に集められ、水処理部分に充填しである接触酸化材
に自然に付着したバクテリヤ、酵母、原生動物、微細藻
類により分解され、植物プランクトンの栄養塩に転化さ
れ、これら植物プランクトンの一部は餌料として直接利
用され、また一部は動物プランクトン等に捕食され、動
物プランクトンの増殖が行われるが、これら動物群もま
た餌料として利用されるもので、いわゆる生物サイクル
を利用した自然浄化が行えるものである。
In addition, floating and disturbed organic residues are collected in the center of the tank by the action of swirling flow, and are decomposed by bacteria, yeast, protozoa, and microalgae that naturally adhere to the contact oxidizing material filled in the water treatment section. , are converted into nutritional salts for phytoplankton, and some of these phytoplankton are used directly as food, and some are eaten by zooplankton, etc., resulting in the proliferation of zooplankton, but these animal groups are also used as food. It is used for natural purification using the so-called biological cycle.

更に有機物残渣等の微細物質の水中浮遊により太陽光線
の透過を妨げ、枯死、ヘドロ化の速いアオサ、シオグサ
等の槽壁、底面への発生を防止する効果を有する。
Furthermore, the suspension of fine substances such as organic residues in the water obstructs the penetration of sunlight, and has the effect of preventing the growth of Ulva, Urticaria, etc., which quickly die and turn into sludge, on the tank walls and bottom.

なお、上記運転中において底面に硫化物質0.05〜/
1湿泥以上の蓄積が認められた場合は、ジェット噴流水
管より全量の水を吐出し、これを水中に拡散させるとと
もに、飼育水中のアンモニア態窒素濃度が600μ?/
13または亜硝酸態窒素濃度が100μt711以上に
なった場合には、30%を限度として換水を行うもので
ある。
In addition, during the above operation, 0.05~/
If an accumulation of 1 wet mud or more is observed, discharge the entire amount of water from the jet water pipe, diffuse it into the water, and raise the ammonia nitrogen concentration in the breeding water to 600μ? /
13 or when the nitrite nitrogen concentration reaches 100 μt711 or more, water should be replaced to a maximum of 30%.

以上の作用効果が期待できるものであるが、更に以下に
クルマエビの放流用種苗の中間育成結果は第1表のとお
りであり、従来は囲い網による5001f/m程度の放
流密度で0.3F/尾程度まで中間育成することが一般
的であるが、現実には自然条件や施設的条件に支配され
充分な中間育成ができず、その歩留りは50%以下であ
るが、本発明によると2000尾/ m2の放養密度で
あるにもかかわらず76%の歩留りが得られた。
The above-mentioned effects can be expected, but Table 1 shows the intermediate growth results of Kuruma shrimp seedlings for stocking. Generally, it is common to raise the fish to about the size of a tail, but in reality, sufficient intermediate growth is not possible due to natural and institutional conditions, and the yield is less than 50%, but according to the present invention, the yield is less than 50%. A yield of 76% was obtained despite the cultivation density of /m2.

したがって少い換水量で高い生残率の中間育成が可能で
ある。
Therefore, intermediate growth with a high survival rate is possible with a small amount of water exchange.

第2表は餌料効率の向上、及び高密度の生産が可能とな
ったことを示す実験結果で有機物残渣が餌料に転換され
、それを餌料の一部として摂取しながらクルマエビは成
長を行うため配合餌料で補うことのできない各種栄養源
が摂取されることも加わって大巾な餌代の節約が可能と
なる。
Table 2 shows the experimental results showing that the feed efficiency has been improved and high-density production has become possible.Organic residue is converted into feed, and the prawns grow while ingesting it as part of the feed. In addition to the fact that various nutritional sources that cannot be supplemented through feed are ingested, it is possible to save a large amount of feed costs.

以上本発明による水処理を行う増養殖方法および装置に
よれば、食物連鎖による再餌料化は浄化作用、抗菌作用
、餌料面、成長、歩留りに及ぼす影響は極めて大きく、
飼育水の自家汚染や近海域の汚染を防止すると同時にエ
ネルギーロスを複利的に縮少する効果を有するものであ
る。
As described above, according to the aquaculture method and apparatus for water treatment according to the present invention, re-feeding through the food chain has an extremely large effect on the purification effect, antibacterial effect, feed quality, growth, and yield.
This has the effect of preventing self-contamination of breeding water and contamination of nearby waters, and at the same time reducing energy loss in a compounded manner.

*

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は本発明の実施例を示す系統図。 第2図は同上一部(内部を示した装置)全体図。 1・・・円形水槽、2・・・架橋、3・・・旋回流水管
、4・・・ジェット噴流管、6・・・水処理部、9・・
・架台、15・・・砂層、17・・・吸入口、24・・
・接触酸化材。
FIG. 1 is a system diagram showing an embodiment of the present invention. FIG. 2 is an overall view of a part of the same as above (the device showing the inside). DESCRIPTION OF SYMBOLS 1...Circular water tank, 2...Bridging, 3...Swirling water pipe, 4...Jet jet pipe, 6...Water treatment section, 9...
- Frame, 15... Sand layer, 17... Inlet, 24...
- Contact oxidizing material.

Claims (1)

【特許請求の範囲】 1 底面に砂層を有する円形水槽において、槽内水を吸
出してその一部は上記砂層面へ噴射して砂層面上への有
機物残渣の堆積あるいは停滞を防ぎ、他は槽の接線方向
への噴射により槽内に旋回流を生じさせ、これにより浮
遊状態の有機物残渣を槽中央の槽内水吸出孔に移動させ
、そこに充填された接触酸化材に付着したバクテリヤ、
酵母、原生動物、微細藻類により有機物残渣を植物プラ
ンクトンの栄養塩に転化させるようにした底棲魚類の増
養殖方法。 2 円形水槽の底には砂を敷き、その中心に置く架台と
槽の外壁とを架橋してこの架橋は架台を中心支点として
水平に旋回し、架橋には旋回流水管、ジェット噴流水管
、自動給餌器を取付けて、旋回流水管は槽の接線方向の
、またジェット噴流水管は砂層表面に向く噴射ノズルを
有し、これらの水管は圧縮空気エゼクタを通じて槽内水
吸出しポンプにつながり、中心の架台下部には接触酸化
材を充填した水処理部をおき、そこを通じての槽内水吸
出孔を設けた底棲魚類の増養殖装置。
[Claims] 1. In a circular aquarium having a sand layer on the bottom, water in the tank is sucked out and a part of it is injected onto the surface of the sand layer to prevent organic residue from accumulating or stagnation on the surface of the sand layer. is injected in the tangential direction to create a swirling flow in the tank, which moves the suspended organic residue to the tank water suction hole in the center of the tank, and removes bacteria attached to the contact oxidizing material filled there.
A cultivation method for benthic fish that uses yeast, protozoa, and microalgae to convert organic residue into nutrients for phytoplankton. 2. Spread sand on the bottom of the circular water tank, bridge the pedestal placed in the center with the outer wall of the tank, and use the pedestal as a central fulcrum to pivot horizontally. When the feeder is installed, the swirl water pipe has an injection nozzle oriented tangentially to the tank, and the jet jet water pipe has an injection nozzle facing the sand layer surface, and these water pipes are connected to the water suction pump in the tank through a compressed air ejector, and are connected to the central pedestal. This is a demersal fish aquaculture device with a water treatment section filled with contact oxidizing material at the bottom, and a tank water suction hole through it.
JP56067429A 1981-05-04 1981-05-04 Method and equipment for breeding benthic fish Expired JPS5950289B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP56067429A JPS5950289B2 (en) 1981-05-04 1981-05-04 Method and equipment for breeding benthic fish

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP56067429A JPS5950289B2 (en) 1981-05-04 1981-05-04 Method and equipment for breeding benthic fish

Publications (2)

Publication Number Publication Date
JPS57181626A JPS57181626A (en) 1982-11-09
JPS5950289B2 true JPS5950289B2 (en) 1984-12-07

Family

ID=13344652

Family Applications (1)

Application Number Title Priority Date Filing Date
JP56067429A Expired JPS5950289B2 (en) 1981-05-04 1981-05-04 Method and equipment for breeding benthic fish

Country Status (1)

Country Link
JP (1) JPS5950289B2 (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61132124A (en) * 1984-11-30 1986-06-19 三井海洋開発株式会社 Cleaning apparatus of aquatic tank for fishery breeding
JPS61135522A (en) * 1984-12-05 1986-06-23 三井海洋開発株式会社 Apparatus for cleaning aquatic tank
JPS61185139A (en) * 1985-02-09 1986-08-18 浦上 政治 Method and basin apparatus for breeding shrimps
JPH035246Y2 (en) * 1986-04-17 1991-02-12

Also Published As

Publication number Publication date
JPS57181626A (en) 1982-11-09

Similar Documents

Publication Publication Date Title
US5947057A (en) Open air mariculture system and method of culturing marine animals
JP5629288B2 (en) Seafood culture apparatus and method
CN107667938A (en) The intensive high density circulating water cultivation method of Penaeus Vannmei
JP6297816B2 (en) Abalone culture method and culture system
CN104322419A (en) Factorized totally-closed circulating aquaculture system of sea cucumbers
JP2010088315A (en) Water treatment apparatus for aquaculture pond
CN207411238U (en) The intensive high density circulating water culture system of Penaeus Vannmei
CN106719270B (en) A kind of aquaculture life-support system and its application method
KR20090051685A (en) Aquaculture system using ultra-mini century cannon
CN110352893B (en) Snakehead circulating water purification culture system
JP2016208890A (en) Abalone culturing method and system for same
KR101564807B1 (en) Automatic drainage for aquaculture tank
CN105684972A (en) Method for cultivating babylonia lutosa
JP5913717B1 (en) Sandy aquatic life culture equipment
CN110835206A (en) A kind of catfish high-level pond culture tail water treatment system
JPS5950289B2 (en) Method and equipment for breeding benthic fish
JP2006217822A (en) Seafood culture apparatus and method
CN213623716U (en) Ecological clean system of tail water breeds
CN104115778A (en) Circulating water high-density culturing system equipment
CN210974345U (en) Silurus meridionalis elevated pond culture tail water treatment system
CN212184747U (en) A hydroponic aquaponics system based on micro-nano bubble technology
CN207707068U (en) Efficient bait-laying device for fish in a kind of cultivating pool
CN216863750U (en) Biochemical Plant Combination Filter
CN115316331A (en) Land-based circulating water ecological fish culture system
CN109006648A (en) Water body is removed contamination system and its application