JPS6296027A - Breeding of dojo - Google Patents

Breeding of dojo

Info

Publication number
JPS6296027A
JPS6296027A JP60235045A JP23504585A JPS6296027A JP S6296027 A JPS6296027 A JP S6296027A JP 60235045 A JP60235045 A JP 60235045A JP 23504585 A JP23504585 A JP 23504585A JP S6296027 A JPS6296027 A JP S6296027A
Authority
JP
Japan
Prior art keywords
wastewater
aeration tank
tank
loaches
breeding
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP60235045A
Other languages
Japanese (ja)
Inventor
尾関 和三
石川 速夫
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.)
IURA YUUTEIRITEII KK
Original Assignee
IURA YUUTEIRITEII KK
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by IURA YUUTEIRITEII KK filed Critical IURA YUUTEIRITEII KK
Priority to JP60235045A priority Critical patent/JPS6296027A/en
Publication of JPS6296027A publication Critical patent/JPS6296027A/en
Pending 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)

Abstract

(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。
(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は淡水魚の1種であるどじようの養殖法に関する
ものである。
DETAILED DESCRIPTION OF THE INVENTION (Field of Industrial Application) The present invention relates to a method for cultivating locust, which is a type of freshwater fish.

(従来の技術) どじょうの養殖には普通、水田や池沼をそのま\利用す
るとか、水田、池沼等に人工的な工作を施して養殖池と
したり、あるいは、専用の養殖池を築造し定シして行わ
れている。
(Conventional technology) Loach farming usually involves using rice paddies and ponds as they are, artificially modifying rice paddies, ponds, etc. to create aquaculture ponds, or constructing and establishing dedicated aquaculture ponds. This is done in a similar manner.

(発明が解決しようとする問題点) ところで、池沼等をそのま\利用しての養殖は管理が難
かしく、一般的ではなく、また水田の利用にあっても、
水田をそのま\利用したのではどしょうが飼育中に水田
から逃げ出してしまう事故が多く、どじようの養殖にお
いて最も難かしい条件の1つとして、どじようの逃げを
防止することが挙げられている、−ffに池沼や水田利
用による歩留りは最高75%と、いわれている。
(Problems to be solved by the invention) By the way, aquaculture using ponds and marshes as is is difficult to manage and is not common, and even when using rice fields,
If rice paddies are used as they are, there are many accidents in which the locusts escape from the rice paddies during breeding, and one of the most difficult conditions in cultivating locusts is to prevent them from escaping. , -ff is said to have a maximum yield of 75% by using ponds and paddy fields.

それ故、どじようの逃げを防止するためには水田等にあ
っては人工的な工作を施して養殖池とし几り、あるいは
、専用の養殖池を築造する等のことが要求されるから、
これに対して多額の費用を必要とすることになる。
Therefore, in order to prevent loach from escaping, it is necessary to use artificial techniques to create aquaculture ponds in rice fields, or to construct dedicated aquaculture ponds.
This will require a large amount of expense.

またどじようを飼育するためには、水温、水量、溶存酸
素量等の水質の管理が難かしく、また冬季には温度低下
によって休眠越冬するため、この間は生産性は零となる
ものである。これらの問題点の個々については、これを
解決する手段はあるが、生産原価に影響し、頴調に飼育
されたとしても、非常に高価などじょうとなってしまう
心配がある。
In addition, in order to raise locusts, it is difficult to control water quality such as water temperature, water volume, and dissolved oxygen content, and in winter, the locusts go dormant and overwinter due to the temperature drop, so productivity is zero during this period. Although there are ways to solve each of these problems, there is a concern that this will affect the production cost and result in very expensive locusts even if they are bred in good condition.

(問題点を解決するための手段) 本発明者等はこれらの点に鑑み、どじようが養殖中に逃
げることがなく、また養殖に使用される水質が適当であ
り、休眠越冬することなく、周年飼育が可能である養殖
法を得るべく鋭意研究した結果、活性汚泥法による排水
処理中間工程における曝気槽を養魚槽として、こXにお
いてどじょうを養殖することにLつて、工くその目的を
達することができ、本発明を得たものである。
(Means for Solving the Problems) In view of these points, the present inventors have determined that the locusts do not escape during cultivation, that the water quality used for cultivation is appropriate, and that they do not go dormant over the winter. As a result of intensive research into an aquaculture method that would allow year-round rearing, we decided to use the aeration tank in the intermediate process of wastewater treatment using the activated sludge method as a fish tank, and to cultivate loaches in Ko-X, achieving our goal. This is the result of the present invention.

(作用) 活性汚泥法による排水処理とは、よく知られる工うに下
水と活性汚泥とを混合攪拌し、これに空気を吹き込み酸
素を供給し、いわゆるエアーレーションすることに工っ
で、排水を生物学的に処理する方法であって、このエア
ーレーションによって排水中に好気性細菌が繁殖し、こ
の細菌にLつて排水中の酸化作用が促進される。このよ
うにして酸化分解を受けた有機物は細菌と共に沈下し、
上層には透明な排水を残すもので、この沈下物は泥状を
なしておシ、酸化力を多分に備えた好気性M菌を多量に
含んでいるので、これを、また新しい排水に加えて酸素
を供給し、前記し几工うな過程で排水の処理を行うもの
である。この活性汚泥法にあっては、排水が処理工程に
おける散水戸床で温められたり、さらに曝気槽に吹き込
まj、る空気は、空気圧縮機で圧縮された空気が吹き込
まれるが、空気圧縮機において空気が加温される結果と
なり、これが処理排水中に吹き込まれることに二って処
理排水は加温され友こととなり、東北地方、北海道等の
ような寒冷地では無理としても関東地方、東海地方以西
にあっては処理排水は冬季にあってもはソ20℃前後と
されるものである。
(Function) Wastewater treatment using the activated sludge method is a well-known process in which sewage and activated sludge are mixed and stirred, and air is blown into the mixture to supply oxygen, so-called aeration. This is a chemical treatment method, and this aeration causes aerobic bacteria to proliferate in the wastewater, and these bacteria promote oxidation in the wastewater. Organic matter that has undergone oxidative decomposition in this way sinks together with bacteria,
Clear drainage water is left in the upper layer, and this sediment is mud-like and contains a large amount of aerobic M bacteria with a large amount of oxidizing power, so it is added to the new drainage water. Oxygen is supplied to the plant, and wastewater is treated in the process described above. In this activated sludge method, the wastewater is heated in a sprinkler door in the treatment process, and the air that is blown into the aeration tank is compressed by an air compressor. As a result, the air is heated, and this air is blown into the treated wastewater, which in turn warms the treated wastewater and makes it more suitable for use in the Kanto and Tokai regions. To the west, treated wastewater is said to have a temperature of around 20°C even in winter.

この処理排水が冬季にあっても20℃前後であることは
、どじょうを養殖した時、どじようは水温の低下による
越冬休眠をしない環境におかnることとなシ、通年の養
殖が可能となることである。
The temperature of this treated wastewater is around 20℃ even in the winter, which means that when cultivating loaches, they must be placed in an environment where they will not go into hibernation over the winter due to a drop in water temperature, making it possible to farm them all year round. It is what happens.

また、曝気槽には好気性細菌の増殖を促すため王縮空気
が吹き込まれるため、排水中の溶存酸素が適量であって
どじようの養殖には好適な条件とされるし、さらに曝気
槽にはミジンコ等が相当量繁殖するので、これをどじょ
うの餌料とすることが出来、特別に餌を投与しないでも
充分な肥育が可能である等、活性汚泥法による排水処理
中間工程における曝気槽はどじようの養殖を行うについ
て他に類を見ない好条件を具備しているものということ
ができる。
In addition, condensed air is blown into the aeration tank to promote the growth of aerobic bacteria, so the amount of dissolved oxygen in the wastewater is appropriate, which is considered to be a suitable condition for cultivating locusts. Daphnia etc. breed in considerable quantities, which can be used as food for loaches, and sufficient fattening is possible without the need for special feed. It can be said that it has uniquely favorable conditions for cultivating oysters.

(実施例) 次に実施例によって本発明をさらに詳細に説明するにあ
たって活性汚泥法による排水処理の概要を添付図面に工
す説明すると、処理される排水は、中和槽A、調整槽B
を経て散水戸床C1から沈澱池D1で排水中の汚泥が沈
澱し排水はさらに散水戸床C2から沈澱池D2にて、さ
きの処理と同様の処理がされ、沈澱池D2からの排水は
曝気槽Bに至り、こXで排水は空気を吹き込まれ好気性
細菌は旺盛に繁殖される、この好気性細菌の繁殖は曝気
槽だけに限らず、散水戸床等、曝気槽に至るまでの間に
おいても繁殖することは説明するまでもない7曝気槽E
からの排水は沈澱池D3から凝集沈澱池Fに至り、これ
から活性炭吸着塔Gを経て滅菌池■(で滅菌され清浄水
となって放流される、これらの工程において排水が散水
P床から沈澱池を経る工程はCIからDIに、次いでC
2からD2にと2回縁シ返して処理されるが、これは2
回に限らず3回あるいはそれ以上であっても差支えない
。また、沈澱池DI、D2.D3.Ii”からの沈澱物
は汚泥濃縮槽Jで濃縮され、脱水、焼却されて廃棄さn
る6なお、沈澱物には酸化力を多分に備えた好気性細菌
を多量に含んでいるので、これの1部は新しい排水に加
えられ前記処理工程によって排水の処理が行はれる2 本発明であるどじようの養殖は前記処理工程中窒気王縮
機からの空気が空気管から槽中の排水中に吹き込まnる
ことによって曝気され、好気性細菌の繁殖が促進される
、この曝気槽においては排水の温度は冬季は約20℃前
後、夏季は約30℃前後となっている、これは夏季は別
として、冬季にあっても排水は、散水F床等を経てくる
ことによって若干昇温されで曝気槽に流入するが、この
曝気槽におけるエアレーションにLつで昇温されるもの
で、こね、は吹き込まれる空気が空気圧縮機の圧縮に工
す加温されるためである。それ故、20℃〜30℃とい
う水温はどじょうにとっての成育上最適な湿度であり、
またエアレーションに工って排水中には常に4〜5 P
PM  と充分な溶存酸素があるため、どじょうの成育
には適当である。
(Example) Next, in order to explain the present invention in more detail through Examples, an outline of wastewater treatment by the activated sludge method is shown in the attached drawings.
After that, the sludge in the waste water is precipitated from the sprinkler door bed C1 to the sedimentation tank D1, and the waste water is further processed in the same way as the previous treatment from the sprinkler door bed C2 to the settling tank D2, and the waste water from the settling tank D2 is aerated. The wastewater reaches tank B, where air is blown into the wastewater and aerobic bacteria are actively bred.This aerobic bacteria breeding is not limited to the aeration tank, but is also carried out in water spray doors and other areas up to the aeration tank. There is no need to explain that they also breed in 7 aeration tank E.
The wastewater flows from the sedimentation tank D3 to the coagulation and sedimentation tank F, and then passes through the activated carbon adsorption tower G and is sterilized in the sterilization pond (■), where it is discharged as clean water. The process is from CI to DI, then C
The process is repeated twice from 2 to D2, but this is 2
It is not limited to once, but may be three times or more. In addition, sedimentation pond DI, D2. D3. The sediment from ``Ii'' is concentrated in a sludge thickening tank J, dehydrated, incinerated, and disposed of.
6 Furthermore, since the precipitate contains a large amount of aerobic bacteria with a large amount of oxidizing power, a portion of this is added to the new wastewater and the wastewater is treated in the above treatment process.2 The present invention During the treatment process, the cultivation of loach is aerated by blowing air from the nitrogen compressor into the waste water in the tank through the air pipe, which promotes the growth of aerobic bacteria. The temperature of wastewater is around 20°C in winter and around 30°C in summer.This is because, apart from summer, even in winter, the temperature of wastewater rises slightly as it passes through the sprinkler floor, etc. The air is heated and flows into the aeration tank, but the temperature is raised by L during aeration in this aeration tank, and the kneading is because the air blown into the air is heated to be compressed by the air compressor. Therefore, a water temperature of 20℃ to 30℃ is the optimum humidity for loach growth.
Also, make sure to aerate and always use 4 to 5 points during drainage.
The presence of PM and sufficient dissolved oxygen makes it suitable for loach growth.

さらに曝気槽中の排水には、エアレーションにエラ排水
中の有機物を栄養源として微生物が繁殖し、さらにこれ
を栄養源としてミジンコ等が繁殖し、これらがどじょう
の餌料としてそのま\利用される。この曝気槽における
どじょうの養殖にあ之つでは、曝気槽の中にどじ工うを
そのま\放流飼育することと、篭、網等に入れ、これを
飼育容器として曝気槽中に浸漬して飼育することに大別
されるが、曝気槽中にそのま\放流飼育する時は、排水
の流入口、排出口等を金網等で覆い、どじようが逃げ出
さない工うにすべきである。曝気槽での飼育にあ几って
は次のような留意が望ましい。すなわち、どじょうのみ
ならず魚類全般について言えることであるが、放流にあ
たって、放流前と放流後の水温の差をなるべく生じさせ
ないこと、ならびに水質の激変を避けることが望ましく
、水温、水質等の環境の変化を余り生じさせないことが
よいもので、どじょうは環境の激変によって/ヨノタ死
することがあるものである。この之め水温と水質とを適
整した水槽で2〜5日間程度の馴し飼いをした後、曝気
槽に放流するのが工い。
Furthermore, in the waste water in the aeration tank, microorganisms breed using the organic matter in the gill waste water as a nutrient source, and Daphnia and the like use this as a nutrient source, and these are used as they are as food for the loaches. There are two methods for cultivating loaches in an aeration tank: one is to raise the loaches as they are in the aeration tank, and the other is to put them in cages, nets, etc. and use them as breeding containers and immerse them in the aeration tank. When rearing them directly in an aeration tank, the inlet and outlet of waste water should be covered with wire mesh, etc., to prevent the moths from escaping. When rearing in an aeration tank, it is recommended to keep the following in mind. In other words, this applies not only to loaches but also to fish in general, but when stocking, it is desirable to minimize differences in water temperature before and after release, and to avoid drastic changes in water quality. It is best not to allow too much change; loaches can die due to drastic changes in their environment. For this reason, it is best to tame the fish for 2 to 5 days in an aquarium with the appropriate water temperature and water quality, and then release the fish into an aeration tank.

本発明者等による飼育実験に工れば、どじょうの稚魚3
,500 ?を網篭に入れ、曝気槽中に吊し100日後
に重量を測定した処8,750 ?となり、飼育当初の
体重の2.5倍となった。この間特別な餌の投与は行は
れず、曝気槽中の自然増殖のミジンコ等を栄養源として
いたものであり、このどじようの肉質は工くしまり高品
質のどじLうが得られた。なお、この飼育は4月から7
月までの100日間であった、 (発明の効果) 本発明は、す、上に詳細に説明したように活性汚泥法に
よる排水処理工程を行う際の曝気槽にあっては、コンク
リート等の構築物からなっている之め、槽内で直接飼育
しても排水の流出入口を処置するだけで、どじようの槽
からの逃亡を容易に防止できることから逃亡による歩留
りの低下の心配がないこと、および曝気槽の水温は冬季
にあっても、どじょうの飼育適温L−、1.下に下り難
いことから、どじょうの冬季越冬休眠を招来する心配が
なく、周年飼育が可能であること、さらにはエアレーン
ヨンにLる充分な溶存酸素が水中に含有され、また排水
中の有機物を栄養源としてどじょうの飼のま5利用でき
る等どじよう養殖における難点を解消した画期的な発明
であり、どじょうの国内生産が昭和56年の867トン
から昭和57年に781トン、同58年には712トン
、同59年には647トンと年々減少しこれとは逆に韓
国、中国、台湾、香港等海外に依存する度合が増大して
いる現状からも本発明の童義は極めて大きいものがある
If the breeding experiment by the present inventors is carried out, loach fry 3
,500? 8,750? The weight was 2.5 times the weight at the time of breeding. During this period, no special feed was administered, and the naturally growing Daphnia in the aeration tank were the source of nutrients. This breeding is carried out from April to July.
(Effects of the Invention) As explained in detail above, the present invention provides that the aeration tank used in the wastewater treatment process using the activated sludge method is constructed of concrete, etc. Therefore, even if you raise the locusts directly in the tank, you can easily prevent the locusts from escaping from the tank by simply treating the wastewater inlet and outlet, so there is no need to worry about a drop in yield due to escape. The water temperature in the aeration tank is the optimum temperature for raising loaches, L-, even in winter.1. Since it is difficult to go down, there is no need to worry about causing the loaches to go into winter dormancy, and year-round breeding is possible.Furthermore, the water contains enough dissolved oxygen to nourish the organic matter in the wastewater. This is an epoch-making invention that solved the difficulties in loach farming, such as the ability to use loach farms as a source of food, and the domestic production of loaches increased from 867 tons in 1980 to 781 tons in 1981, and to 781 tons in 1981. 712 tons, decreasing year by year to 647 tons in 1959, and on the contrary, the current situation is that the degree of dependence on overseas countries such as South Korea, China, Taiwan, and Hong Kong is increasing, and the fairy tale of this invention is extremely significant. There is.

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

添付図面は本発明の方法が実施される活性汚泥法による
排水処理の一例を示す工程図である。
The accompanying drawings are process diagrams showing an example of wastewater treatment by an activated sludge method in which the method of the present invention is implemented.

Claims (1)

【特許請求の範囲】[Claims] 活性汚泥法による排水処理中間工程における曝気槽を養
魚槽として、どじょうを飼育することを特徴とするどじ
ょうの養殖法
A loach cultivation method characterized by raising loaches in an aeration tank used as a fish tank in the intermediate process of wastewater treatment using the activated sludge method.
JP60235045A 1985-10-21 1985-10-21 Breeding of dojo Pending JPS6296027A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP60235045A JPS6296027A (en) 1985-10-21 1985-10-21 Breeding of dojo

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60235045A JPS6296027A (en) 1985-10-21 1985-10-21 Breeding of dojo

Publications (1)

Publication Number Publication Date
JPS6296027A true JPS6296027A (en) 1987-05-02

Family

ID=16980264

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60235045A Pending JPS6296027A (en) 1985-10-21 1985-10-21 Breeding of dojo

Country Status (1)

Country Link
JP (1) JPS6296027A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6385842B1 (en) 2000-01-14 2002-05-14 Delaware Capital Formation, Inc. Tube feeder having a zone on which components can pivot
JP2010194426A (en) * 2009-02-24 2010-09-09 Ebara Engineering Service Co Ltd Biological treatment method and apparatus utilizing fishes

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5298189A (en) * 1976-02-13 1977-08-17 Battelle Institut E V Method of rearing and accommodating aquztic animals
JPS52107990A (en) * 1976-03-05 1977-09-10 Mitsubishi Heavy Ind Ltd Method of rearing fishes with use of excess sludge

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5298189A (en) * 1976-02-13 1977-08-17 Battelle Institut E V Method of rearing and accommodating aquztic animals
JPS52107990A (en) * 1976-03-05 1977-09-10 Mitsubishi Heavy Ind Ltd Method of rearing fishes with use of excess sludge

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6385842B1 (en) 2000-01-14 2002-05-14 Delaware Capital Formation, Inc. Tube feeder having a zone on which components can pivot
US6478533B2 (en) 2000-01-14 2002-11-12 Davis, Iii Maurice M. Method of using a tube feeder for circuit board components
JP2010194426A (en) * 2009-02-24 2010-09-09 Ebara Engineering Service Co Ltd Biological treatment method and apparatus utilizing fishes

Similar Documents

Publication Publication Date Title
CN104255632B (en) The intelligent organic prawn ecology rearing device of totally-enclosed full impregnated light
WO2014190571A1 (en) System combining aquaculture and soil-less agricultural planting
CN106508762A (en) Method for indoor recirculating aquaculture of crayfish
JP2017148007A (en) Cultivation system of fish seedling
CN108967085A (en) A kind of rice field-Penaeus Vannmei dystopy ecological cultivation system
CN104082253B (en) Leech and snail, pasture and water commensalism enclosure fence high-yield cultivation method
CN201393474Y (en) Parent circulating water cultivation device of blue crab
CN109892232A (en) Aggregate species cultivating system and its application in scale animal and poultry cultivation treatment for cow manure
CN209135151U (en) A kind of chimeric Greenhouse System of the intensive circulating water cultivation light and shade of Ecology
CN109122531A (en) A kind of light and shade of the intensive circulating water cultivation of Ecology is fitted into Greenhouse System and cultural method
CN1219430C (en) Youngling of large sea horse and artificial cultivating method of commodity sea horse and its equipment
CN215559753U (en) Artificial wetland system for treating aquaculture tail water and circulating water aquaculture system
CN216452710U (en) Brocade carp and vegetable symbiotic recirculating aquaculture system
TWI604787B (en) Wisdom aquarium fish tank
CN206100999U (en) Agricultural cyclic utilization system
CN112352715A (en) Facility and method for large-scale culture of perinereis aibuhitensis by using prawn culture wastewater
CN108911146B (en) Ecological treatment system for domestic sewage
JP2002239573A (en) Method for cleaning water
CN116098109A (en) Industrial pond culture system
CN100503484C (en) Method of preparing biological activity water by fecaluria of livestock and poultry and application thereof
TW200847920A (en)
JPS6296027A (en) Breeding of dojo
CN213881396U (en) Annual large-scale aquaculture system for snail and shellfish aquatic products
CN108164006A (en) Utilize the method for the food chain purification biogas slurry of planktonic organism-water plant-fish
CN209964992U (en) A seed field that is used for carp fry production of northern area