JP2004016163A - Method for resource-circulating treatment of culture residue by using useful invertebrate - Google Patents

Method for resource-circulating treatment of culture residue by using useful invertebrate Download PDF

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Publication number
JP2004016163A
JP2004016163A JP2002178443A JP2002178443A JP2004016163A JP 2004016163 A JP2004016163 A JP 2004016163A JP 2002178443 A JP2002178443 A JP 2002178443A JP 2002178443 A JP2002178443 A JP 2002178443A JP 2004016163 A JP2004016163 A JP 2004016163A
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invertebrate
fish
useful
breeding
aquaculture
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JP2002178443A
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Japanese (ja)
Inventor
Haruaki Honda
本田 晴朗
Kotaro Kikuchi
菊池 弘太郎
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Central Research Institute of Electric Power Industry
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Central Research Institute of Electric Power Industry
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  • Separation Of Solids By Using Liquids Or Pneumatic Power (AREA)
  • Filtration Of Liquid (AREA)
  • Farming Of Fish And Shellfish (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To recycle and reuse resources by treating a culture residue of fish and shellfish with a useful invertebrate. <P>SOLUTION: A culture residue composed mainly of the feces of fish and shellfish is supplied as a feed for a useful aqueous invertebrate such as lugworm to convert the residue into the lugworm body and the residue is recovered and reused as the feces of the invertebrate. The method is effective for converting the culture residue as a resource to the useful invertebrate, reducing the amount of sludge and usable as a resource-recycling method to reduce the environmental pollution load. <P>COPYRIGHT: (C)2004,JPO

Description

【0001】
【発明の属する技術分野】
本発明は、有用無脊椎動物の生物機能を用いた魚介類の残餌、糞などの養殖残渣(汚泥)処理と資源循環利用法に関するものである。
【0002】
【従来の技術】
現在、わが国で行われている魚介類養殖のほとんどは、イケスや掛流し式といった開放系システムで行われており、システムから発生する養殖残渣は、ほとんど未処理のまま、海や河川に放流されている。
【0003】
【発明が解決しようとする課題】
このため、養殖施設からの養殖残渣を含む排水が公共水域への栄養塩汚濁負荷源となる可能性が指摘されている。一部、沈殿槽、沈殿池やスクリーンフィルターなどを付設している陸上養殖システムもあるが、これら物理的手法で集めた養殖残渣の処理法は確立されていない。とくに、魚類の糞は崩れやすく再び水に懸濁しやすい性質を有しており、取り扱いが容易ではない。
本発明は、これら処理しにくい養殖システムにおける魚介類の糞、残餌などの養殖残渣の有効利用および効率的な除去方法を提供することを目的とするものである。
【0004】
【課題を解決するための手段】
本発明は、魚介類を主体とした養殖施設における養殖残渣を水棲有用無脊椎動物に摂餌させ動物体に転換するとともに、無脊椎動物の糞粒として回収・再利用する資源循環型の養殖残渣処理方法および、このための処理システムに関するものである。
【0005】
本発明者らは資源循環型の養殖残渣処理に利用できる水棲有用無脊椎動物(以下、単に無脊椎動物という)について種々検討した結果、ゴカイ、クルマエビ、ナマコの仲間が魚介類の養殖時に生じる残餌(配合飼料等)はもちろんのこと、直接魚介類の糞を摂餌することを見出した。本発明の養殖残渣処理方法は、そのままでは水域への汚濁負荷源となる養殖残渣を、資源として無脊椎動物に転換することを特徴とする。本発明において利用できる無脊椎動物としては、上記以外にカニ、ザリガニ類などが挙げられる。
【0006】
上記で検討した無脊椎動物のうち、ゴカイ、イソゴカイなどのゴカイ類、クルマエビなどのエビ類の糞は粒状(糞粒)沈降性で網やサイフォンなどを用いた取り扱いに耐えられる強度があり、養殖施設から容易に除去できることを見出した。
養殖魚介類の飼料はほぼ同様なものが用いられてはいるが、使用する無脊椎動物は養殖すべき魚介類の種類に応じて選択すると良い。選択すべき無脊椎動物には上記のとおり、残餌をもっぱら食餌として生育するものと、後処理が容易な糞を排泄するものと、これらの両者を備えるものとがあることから、目的に応じて1種または2種以上を飼育すると良い。
【0007】
養殖残渣処理方法および処理装置を設計するのには、無脊椎動物の魚介類糞摂餌量、糞粒排泄量などと対象となる魚介類の糞排泄量等を知ることが必要である。
処理方法、すなわち魚介類の養殖および無脊椎動物の飼育方法としては、▲1▼養殖魚介類と無脊椎動物とを仕切りの無い同一養殖水槽で行う方法、▲2▼仕切りを設けた養殖水槽で飼育する方法、更には▲3▼魚介類の養殖水槽と無脊椎動物の飼育水槽とを別個に設けて飼育する方法等が考えられ,これらに応じて処理装置が設計される。
上記▲1▼の方法は無脊椎動物が養殖水槽の槽底の砂、土等の中で棲息する生物であって魚介類に損傷を与えずに共存できるものの場合に適用できる。▲2▼の方法は、カニ、エビ等の無脊椎動物のように養殖魚介類によっては同じ水槽内での飼育が好ましくないものの場合に適用される。例えば、網イケスを用いたり、スノコ、仕切り等で上下に水槽を仕切り、上部を魚介類の養殖部とし、下部を無脊椎動物の飼育部とする。▲3▼の方法は、魚介類の養殖水槽からの水を無脊椎動物の飼育水槽に循環させて処理する方法である。
例えば、無脊椎動物としてクルマエビを用いる場合には飼育床は砂利の代わりに砂を用いるとよく、ナマコでは何も敷かなくてもよいことから、処理方法に応じて無脊椎動物と処理槽の構造を選択するとよい。
【0008】
無脊椎動物が養殖魚介類の残餌および排泄物(糞)を餌として充分に消化し、無脊椎動物からの排泄量(糞量)が著しく少なくなる場合には、常法に従って飼育水を濾過または沈殿処理して養殖水槽に循環させるか系外に排出させても良い。無脊椎動物が取扱が容易な粒状物として糞を排泄する場合には、飼育部の底をスノコまたは目皿状の仕切り板として糞粒が槽底に落下するようにするとか、または飼育部の底に溜まった糞粒をジェット水流で一方の端に吹き寄せてサイホン等で吸い取るなどの方法で除去する。
無脊椎動物の排泄する糞を処理しやすい程度の固形物とするために、必要に応じて、養殖魚介類の養殖残渣のほかに更に無脊椎動物用の餌を与えても良い。無脊椎動物の糞粒とは、球状、短い棒状など取扱い容易で崩れない形の物を言う。
【0009】
【発明の実施の形態】
以下、養殖残渣処理方法および処理装置の一例として、無脊椎動物としてイソゴカイを、汚濁負荷(糞)を出す養殖魚介類としてヒラメを組み合わせた場合の設計例について記述する。他の魚介類の糞を処理する場合にはその糞排泄量、他の無脊椎動物を用いる場合にはその魚介類糞摂餌量、糞粒排泄量などについての情報を用い、同様にして養殖残渣処理方法および処理装置を設計することができる。
【0010】
(養殖残渣処理装置の設計例)
ヒラメの糞を用い、イソゴカイの1日当たりの魚類糞摂餌量と糞粒排泄量を求めた。図1に示すように、体重0.2〜0.7gのイソゴカイは1日に乾燥重量で10〜25mgのヒラメ糞を摂餌し(図1(A))、糞粒として1〜6mg/日の量を排泄する(図1(B))。すなわち、イソゴカイは摂餌したヒラメ糞の10〜43%(平均22.4%)程度を糞粒(乾燥重量)として排泄する(図1(C))。
【0011】
上記に対し、図2に示したように、一度に体重の0.4〜2.1%(平均0.5%)のヒラメ用配合飼料を摂餌したヒラメ(体重35〜1020g)は、摂餌後24〜72時間以内に合計で摂餌配合飼料の7〜23%(平均12.7%)の重量(乾燥重量)の糞を排泄する。配合飼料は魚用の市販のものを用いた。
【0012】
今、体重1000gのヒラメが体重の0.5%の配合飼料を毎日摂餌し、その重量の12.7%を24時間後までに排泄すると、排泄される糞は635mg(乾燥重量)となる。イソゴカイのヒラメ糞摂餌量を1日に15mgとすると、必要なイソゴカイは約42尾となる。イソゴカイの最適な生息密度はこれまでの飼育実験から0.1尾/cm2 程度である。したがって、処理装置の面積は420cm  となる。
【0013】
イソゴカイはヒラメ糞を摂餌して成長し、そのタンパク質効率はヒラメ用やゴカイ用の配合飼料と変わらないことを見出した。したがって、淡水魚も含め魚介類の糞はイソゴカイの養殖・飼育飼料または飼料原料として利用できる。
【0014】
イソゴカイの糞粒は、約3%の窒素を含んでいるので、他の無脊椎動物の飼料として再利用できる。また、イソゴカイは排泄直後は摂餌しないが、ある程度時間経過した自分の糞粒を摂餌することを見出した。イソゴカイの糞粒をイソゴカイに摂餌させることにより、ヒラメの糞は最初の重量の5%のイソゴカイ糞に減量される。
【0015】
(飼育・養殖残渣処理装置)
従来のイソゴカイの養殖・飼育装置は、飼育水槽の底部に集水管を付設し、その上に砂や砂利を敷く方式であり、糞粒が除去されにくく、そのため糞粒が分解され嫌気層ができ、飼育環境が低下する場合があった。
本発明では、無脊椎動物の飼育水槽(処理水槽)の槽底の上方にスノコまたは目皿状の有隙または多孔仕切り板を設置して水槽底と仕切り板との間に空間を設け、仕切り板の上に砂利などの無脊椎動物飼育床を設け、無脊椎動物の糞粒が水流により仕切り板の下方に除去される構造とした。また、処理水槽底は一方の端または中央部に向けて傾斜させ(傾斜度:1/10から1/20)、糞粒が糞粒溜1箇所に集まる構造とした。処理水槽からの排水は集めた糞粒を連行しないように、水槽上部から溢流させるか、あるいは立ち上がりパイプを用いて行う。この構造は他の無脊椎動物を用いる場合も同様とする。
【0016】
処理水槽の糞粒溜に集められた糞粒は、排水管によって処理水槽から取りだして廃棄処理するか、あるいはポンプにより処理水槽に返送し、再び無脊椎動物の飼料として用いるか、または他の無脊椎動物を含む処理水槽に供給して処理する。処理水槽の上部から排出される糞粒を含まない処理水はバイオフィルター等を介して魚介類の養殖水槽に循環させる。
【0017】
無脊椎動物の飼育床には対象生物により、砂、砂利、沈降性の木炭粒(ペレット)を用いる。木炭粒を用いた場合には、砂、砂利より軽く、水流または吹き込みエアーなどによって動かすことができるので糞粒との分離が容易で、作業性がよくなる。また、循環濾過飼育の場合には、難分解性有機物(黄色物質)の吸着除去も行えるなどの利点を有する。
無脊椎動物の飼育水槽(処理水槽)は、底面をスノコなどの多孔板とした箱に砂、砂利等を入れて飼育床を形成した飼育箱を別途作成し、この飼育箱を水槽内に懸架するようにしてもよい。飼育床の下面から水流またはエアーを間歇的に吹き上げて飼育床の砂等を流動させて堆積した糞粒をスノコの下に落下させるてもよく、また上記飼育箱を振動させるように構成してもよい。
特に、イソゴカイの糞粒は比重が大きく沈降性で、かつ堅固で壊れにくい特徴を持っているため分離が容易である。
【0018】
【実施例】
以下、本発明を循環濾過養殖システム(特公平7−55116号公報、特許第2035885号)に組み込んだ一実施例を図面に基づき説明するが、本発明はこの実施例に限定されるものではない。
【0019】
実施例
本例は、魚介類の飼育水槽と無脊椎動物の飼育水槽(養殖残渣処理槽)とを別個に設けた処理装置の例を示す。
図3は、養殖用の魚介類飼育水槽に本発明の養殖残渣処理装置を組み込んだ処理システムの概略図である。図3において、1は魚介類飼育水槽、3は養殖残渣処理装置を示す。魚介類飼育水槽1は円形、または四角、六角、八角などの多角形の槽などいずれの形状の水槽を用いることができる。水槽1の底部は1/10から1/20程度の傾斜を持ち、飼育水槽への注水の流れにより糞や残餌の養殖残渣が自動的に水槽中央部に集められ、水槽底部より排出される構造とする。
【0020】
魚介類飼育水槽1の底部より排出された養殖残渣は、散水管2より無脊椎動物飼育水槽3の無脊椎動物生息床6に供給される。図2に示すように、無脊椎動物生息床6は、飼育水槽3の底面より上方に設けられたスノコ板4と仕切板5で区画、形成されている。散水管2の散水孔は,飼育魚介類によって異なるが、残餌により目詰まりを起こさないように直系5〜8mm以上とするとよい。また、無脊椎動物生息床6には、処理生物(無脊椎動物)の種類によって異なるが、粒径2〜5mm程度の砂、6〜12mm程度の砂利、または3〜5mm程度の沈降性木炭粒を、単独または併せて、厚さ5〜10cm程度に敷く。無脊椎動物生息床6の水位(水面7)は、処理生物の種類により異なるが水が流れている状態において生息床6の上面より0〜10cm高くなるようにし、水面7の調整は立ち上がり排水パイプ8の高さにより調節する。
【0021】
養殖残渣を摂餌した処理生物の糞粒は水流によりスノコ板4から無脊椎動物飼育水槽3の底に流下し、底の傾斜と水流により糞粒溜9に集まる。
糞粒溜9に集まった糞粒は、糞粒採取用コック10を開くことにより採取し、他の飼育システムで飼育している無脊椎動物の飼料として利用するか、返送ポンプ14により無脊椎動物生息床6に返送する。
立ち上がり排水パイプ8からの処理水はバイオフィルター11にて水中の溶存アンモニア等を除去した後、水温調節装置13で温度調節して魚介類飼育水槽1に循環させる。
【0022】
本発明の養殖残渣処理装置を、水量550Lの循環濾過養殖システムに組込みヒラメの養殖実験を行い、無脊椎動物(イソゴカイ)を用い糞粒を返送しない場合の汚泥発生量を計測することにより、養殖残渣処理効果について検討した。その結果、終了時の累積汚泥発生量は配合飼料投餌量から計算されるヒラメ糞重量(乾燥重量)の約24%であり、かつその性状は糞粒の形態を示していた。また、この糞粒を、返送し再度摂餌させた場合には、汚泥発生量はヒラメ糞重量の5%と計算され、本装置の設計方法と性能が実証された。
【0023】
【発明の効果】
本発明は、以上説明したように、これまで未処理でまたは活性汚泥槽等で処理して公共水域に排出されていた養殖残渣を資源として有用無脊椎動物に転換し、汚泥の発生量をこれまでより大幅に少なくすることができ、資源循環型の環境汚濁負荷低減法として利用できる。また、釣り餌や直接食用生物として活用できる有用無脊椎動物といった副産物を得ることができる。
【図面の簡単な説明】
【図1】イソゴカイのヒラメ糞摂餌量と排泄量を示すグラフである。
【図2】ヒラメの配合飼料摂餌量と糞排泄量との関係を示すグラフである。
【図3】本発明にかかわる養殖残渣処理装置の一実施例を示す構成図である。
【図4】本発明にかかわる養殖残渣処理装置の概略図である。
【符号の説明】
1 魚介類飼育水槽
2 散水管
3 無脊椎動物飼育槽
4 スノコ板(目皿)
5 仕切り版
6 無脊椎動物生息床
7 水面
8 立ち上がり排水パイプ
9 糞粒溜
10 糞溜採取用コック
11 バイオフィルター
12 ポンプ
13 温度調節装置
[0001]
TECHNICAL FIELD OF THE INVENTION
TECHNICAL FIELD The present invention relates to a method for treating aquaculture residues (sludge) such as fish and shellfish residual food and feces using useful invertebrate biological functions, and a resource recycling method.
[0002]
[Prior art]
Currently, most of the seafood cultivation in Japan is carried out in open systems such as ikesu and floating systems, and the farming residues generated from the system are discharged to the sea and rivers almost untreated. ing.
[0003]
[Problems to be solved by the invention]
For this reason, it has been pointed out that wastewater containing aquaculture residues from aquaculture facilities may be a source of nutrient pollution load to public waters. There are some onshore aquaculture systems equipped with sedimentation tanks, sedimentation ponds, screen filters, etc., but the method of treating farming residues collected by these physical methods has not been established. In particular, fish dung is easily broken and easily suspended in water, and is not easy to handle.
It is an object of the present invention to provide a method for effectively utilizing and efficiently removing a culture residue such as fish and shellfish dung and remaining food in a culture system that is difficult to treat.
[0004]
[Means for Solving the Problems]
The present invention relates to a resource-recycling culture residue that feeds aquatic useful invertebrates in an aquaculture facility mainly composed of fish and shellfish to convert them into an animal body and collects and reuses them as feces of the invertebrates. The present invention relates to a processing method and a processing system for this.
[0005]
The present inventors have conducted various studies on useful aquatic invertebrates (hereinafter, simply referred to as invertebrates) that can be used for resource-recycling-type farming residue treatment. They found that they feed directly on fish and shellfish feces as well as feed (mixed feeds, etc.). The method for treating a culture residue of the present invention is characterized in that a culture residue that is a pollutant load source in water bodies as it is is converted into an invertebrate as a resource. Invertebrates that can be used in the present invention include crabs and crayfishes in addition to the above.
[0006]
Among the invertebrates examined above, the droppings such as moss and shrimp, and the shrimp such as prawns are sedimentable in granular form (fecal grain) and have the strength to withstand handling using nets and siphons. It has been found that it can be easily removed from the facility.
Although almost the same feed is used for cultured fish and shellfish, invertebrates to be used are preferably selected according to the type of fish and shellfish to be cultured. Depending on the purpose, invertebrates to be selected include those that grow only as diet as described above, those that excrete faeces that can be easily post-processed, and those that have both. It is good to breed one or more species.
[0007]
In order to design a method and an apparatus for treating aquaculture residues, it is necessary to know the amount of fish and shellfish excretion of invertebrates, the amount of excretion of feces, and the amount of excretion of the target fish and shellfish.
The treatment method, namely, the cultivation of fish and shellfish and the breeding method of invertebrates are as follows: (1) a method in which cultured fish and shellfish and an invertebrate are carried out in the same aquaculture tank without partitions; and (2) a method in which aquaculture tanks with partitions are provided. A method of rearing, and (3) a method of separately cultivating a tank for cultivating fish and shellfish and a tank for breeding invertebrates may be considered, and a processing apparatus is designed according to these.
The method (1) can be applied to the case where the invertebrates are living organisms in the sand or soil at the bottom of the aquaculture tank and can coexist without damaging the fish and shellfish. The method (2) is applied to a case where it is not desirable to rear in the same aquarium depending on the cultured fish and shellfish, such as invertebrates such as crab and shrimp. For example, a net tank is used, or a tank is divided up and down with a mushroom, a partition, etc., and the upper part is a fish and fish cultivation part, and the lower part is an invertebrate breeding part. The method (3) is a method of circulating water from an aquarium for cultivating fish and shellfish into a breeding aquarium for invertebrates.
For example, when prawns are used as invertebrates, it is better to use sand instead of gravel on the breeding floor, and it is not necessary to lay anything in sea cucumber, so the structure of the invertebrates and the treatment tank according to the treatment method You should select
[0008]
If the invertebrate has sufficiently digested the remaining food and excrement (feces) of the cultured fish and shellfish and the amount of excretion (feces) from the invertebrate is significantly reduced, filter the breeding water according to a conventional method. Alternatively, it may be settled and circulated to the aquaculture tank or discharged out of the system. If invertebrates excrete faeces as easy-to-handle particulate matter, the bottom of the breeding section should be a mushroom or perforated partition plate so that the stool drops to the bottom of the tank, or The fecal particles collected at the bottom are removed by a method such as blowing it to one end with a jet water stream and sucking it with a siphon or the like.
If necessary, invertebrate food may be provided in addition to the cultured fish and shellfish residues in order to make the excrement excreted by the invertebrates into a solid matter that can be easily processed. Invertebrate droppings are those that are easy to handle and do not collapse, such as spheres or short rods.
[0009]
BEST MODE FOR CARRYING OUT THE INVENTION
Hereinafter, as an example of a method and an apparatus for treating a farming residue, a design example in which a sea creature is combined as an invertebrate and a flounder is used as a cultured fish and shell which emits a pollutant load (feces) will be described. When processing other fish and shellfish feces, use the information on the amount of feces excreted, and when using other invertebrates, use the information on the amount of fish and shellfish feces fed and fecal particles excreted. Residue treatment methods and treatment equipment can be designed.
[0010]
(Example of design of aquaculture residue treatment equipment)
Using the flounder feces, the amount of fish faeces per day and the amount of fecal particles excreted per day were determined. As shown in FIG. 1, a sea squid weighing 0.2 to 0.7 g feeds on flounder feces in a dry weight of 10 to 25 mg per day (FIG. 1 (A)), and 1 to 6 mg / day as fecal particles. Is excreted (FIG. 1 (B)). That is, Isogokai excretes about 10 to 43% (average 22.4%) of the fed flounder feces as fecal particles (dry weight) (FIG. 1 (C)).
[0011]
On the other hand, as shown in FIG. 2, flounder (weight 35 to 20 g), which ate a mixed feed for flounder at a time of 0.4 to 2.1% (average 0.5%) of the body weight, Within 24 to 72 hours after feeding, a total of 7 to 23% (average 12.7%) weight (dry weight) of feces of the feed formula is eliminated. The commercial feed for the fish was used.
[0012]
Now, when a flounder weighing 1000 g ingests a combined feed of 0.5% of body weight every day and excretes 12.7% of its weight by 24 hours, the excreted feces becomes 635 mg (dry weight). . If the feeding amount of flounder feces of the sea lion is 15 mg per day, the required sea lion is about 42 fish. The optimum population density of the sea lion is about 0.1 fish / cm 2 based on the past breeding experiments. Therefore, the area of the processing apparatus is 420 cm 2   It becomes.
[0013]
It was found that L. japonicum grew by feeding on Japanese flounder feces, and its protein efficiency was no different from that of the compound diets for Japanese flounder and Japanese silkworm. Therefore, the faeces of fish and shellfish including freshwater fish can be used as feed or feed materials for cultivation and breeding of sea lions.
[0014]
The mosquitoes contain about 3% nitrogen and can be reused as feed for other invertebrates. In addition, they found that they did not feed immediately after excretion, but did feed their own feces after some time. By feeding the mosquito grains to the mosquitoes, the flounder stool is reduced to 5% of its original weight.
[0015]
(Breeding and aquaculture residue treatment equipment)
Conventional cultivation and breeding equipment for sea bream is a method in which a collecting pipe is attached to the bottom of the breeding aquarium and sand or gravel is laid on it, making it difficult for fecal particles to be removed, so that the fecal particles are decomposed and an anaerobic layer is formed. In some cases, the breeding environment deteriorated.
According to the present invention, a space is provided between the bottom of the aquarium and the partition plate by providing a mushroom or perforated gap or a porous partition plate above the bottom of the invertebrate breeding aquarium (treatment tank). An invertebrate breeding bed such as gravel was provided on the plate, and the structure was such that fecal particles of the invertebrate were removed below the partition plate by water flow. Further, the bottom of the treated water tank was inclined toward one end or the center (inclination degree: 1/10 to 1/20), so that the dung particles were collected in one dung container. Drainage from the treated water tank is performed by overflowing from the upper part of the water tank or by using a rising pipe so as not to carry the collected fecal particles. This structure is the same when other invertebrates are used.
[0016]
The dung collected in the dung tank of the aquarium is taken out of the aquarium by a drain pipe and disposed of, or returned to the aquarium by a pump and used again as feed for invertebrates, or used for other invertebrates. The water is supplied to a treatment tank containing vertebrates for treatment. Treated water containing no fecal particles discharged from the upper part of the treated water tank is circulated through a biofilter or the like to a fish and shellfish aquaculture tank.
[0017]
Depending on the target organism, sand, gravel and sedimentary charcoal grains (pellets) are used for the invertebrate breeding floor. When charcoal particles are used, they are lighter than sand or gravel and can be moved by a water flow or blown air, so that separation from fecal particles is easy and workability is improved. Further, in the case of circulating filtration rearing, there is an advantage that it is possible to adsorb and remove hardly decomposable organic substances (yellow substances).
For invertebrate breeding aquariums (treatment aquariums), a separate breeding box is created, in which sand and gravel are placed in a box with a perforated plate such as a mushroom to form a breeding floor, and this breeding box is suspended in the aquarium. You may make it. Water or air may be intermittently blown up from the lower surface of the breeding floor to allow the sand and the like on the breeding floor to flow and the accumulated feces to fall under the snowboard, and the breeding box may be configured to vibrate. Is also good.
In particular, the scabs of Isogokai have a large specific gravity, are sedimentable, and are firm and hard to break, so that separation is easy.
[0018]
【Example】
Hereinafter, an embodiment in which the present invention is incorporated into a circulation filtration culture system (Japanese Patent Publication No. 7-55116, Japanese Patent No. 2035885) will be described with reference to the drawings, but the present invention is not limited to this embodiment. .
[0019]
EXAMPLE This example shows an example of a processing apparatus in which a fish tank for raising fish and shellfish and a tank for raising invertebrates (a tank for treating aquaculture residues) are separately provided.
FIG. 3 is a schematic diagram of a processing system in which the culture residue processing apparatus of the present invention is incorporated in a fish and shellfish breeding aquarium for aquaculture. In FIG. 3, reference numeral 1 denotes a fish and shellfish breeding aquarium, and reference numeral 3 denotes a culture residue treatment device. As the fish and shellfish breeding aquarium 1, any shape of aquarium such as a circular, or a polygonal tank such as a square, hexagon, or octagon can be used. The bottom of the aquarium 1 has an inclination of about 1/10 to 1/20, and due to the flow of water into the breeding aquarium, the cultivation residue of feces and remaining food is automatically collected in the center of the aquarium and discharged from the aquarium bottom. Structure.
[0020]
The culture residue discharged from the bottom of the fish breeding aquarium 1 is supplied to the invertebrate habitat 6 of the invertebrate breeding aquarium 3 from the watering pipe 2. As shown in FIG. 2, the invertebrate habitat 6 is divided and formed by a veneer board 4 and a partition plate 5 provided above the bottom of the breeding aquarium 3. The sprinkling hole of the sprinkling pipe 2 varies depending on the breeding fish and shellfish, but is preferably 5 mm to 8 mm or more in direct line so as not to cause clogging due to the remaining food. In the invertebrate habitat 6, depending on the type of treated organism (invertebrate), sand having a particle size of about 2 to 5 mm, gravel of about 6 to 12 mm, or sedimentary charcoal particles of about 3 to 5 mm Are spread alone or in combination to a thickness of about 5 to 10 cm. The water level (water surface 7) of the invertebrate habitat 6 varies depending on the type of the treated organism, but is set to be 0 to 10 cm higher than the upper surface of the habitat 6 in a state where water is flowing. Adjust according to the height of 8.
[0021]
The feces of the treated organism that has fed the farming residues flow down from the vampire board 4 to the bottom of the invertebrate breeding aquarium 3 by the water flow, and are collected in the feces reservoir 9 by the inclination of the bottom and the water flow.
The dung collected in the dung collection 9 is collected by opening the dung collection cock 10 and used as feed for invertebrates bred in other breeding systems, or by the return pump 14. Return to habitat 6.
The treated water from the rising drainage pipe 8 is used to remove dissolved ammonia and the like in the water by the biofilter 11, and then temperature-controlled by the water temperature control device 13 and circulated to the fish breeding aquarium 1.
[0022]
The aquaculture is carried out by incorporating the aquaculture residue treatment apparatus of the present invention into a 550 L circulating filtration aquaculture system and conducting flounder aquaculture experiments, and measuring the amount of sludge generated when fecal particles are not returned using an invertebrate. The effect of residue treatment was studied. As a result, the cumulative amount of sludge generated at the end was about 24% of the weight (dry weight) of flounder feces calculated from the feed amount of the mixed feed, and the properties showed the form of fecal particles. When the feces were returned and fed again, the sludge generation was calculated to be 5% of the weight of flounder feces, demonstrating the design method and performance of this device.
[0023]
【The invention's effect】
As described above, the present invention converts aquaculture residues, which have been untreated or treated in an activated sludge tank or the like and discharged into public waters, into useful invertebrates as resources, and reduces the amount of sludge generated. It can be used as a resource recycling type environmental pollution load reduction method. In addition, by-products such as useful invertebrates that can be used as fishing baits and direct edible organisms can be obtained.
[Brief description of the drawings]
BRIEF DESCRIPTION OF DRAWINGS FIG. 1 is a graph showing the amount of flounder feces fed and excreted by the sea lion.
FIG. 2 is a graph showing the relationship between the amount of feed mixed with flounder and the amount of feces excreted.
FIG. 3 is a configuration diagram showing one embodiment of a culture residue treatment device according to the present invention.
FIG. 4 is a schematic diagram of a culture residue treatment device according to the present invention.
[Explanation of symbols]
1 Fish and shellfish breeding tank 2 Watering pipe 3 Invertebrate breeding tank 4 Snowboard board (mesh plate)
Reference Signs List 5 Partition plate 6 Invertebrate habitat 7 Water surface 8 Standing drainage pipe 9 Dung collection 10 Dung collection cock 11 Biofilter 12 Pump 13 Temperature control device

Claims (7)

魚介類の糞、残餌などの養殖残渣を水棲有用無脊椎動物に摂餌させ、無脊椎動物の動物体および排泄される糞粒として魚介類養殖システムから回収除去する方法。A method of feeding aquaculture invertebrates such as fish droppings and bait to a useful aquatic invertebrate, and collecting and removing the invertebrate animal body and excreted feces from the fish culture system. 魚介類の糞、残餌などの養殖残渣を飼料として水棲有用無脊椎動物を飼育する方法。A method of breeding useful aquatic invertebrates by using farm residues such as fish droppings and bait as feed. 魚介類の養殖水槽の下流側に設けられた水棲有用無脊椎動物の飼育水槽と、養殖水槽からの養殖残渣を含む養殖水を飼育水槽に供給する手段と、飼育水槽から生じる無脊椎動物の糞粒を分離除去する手段とからなる魚介類の養殖残渣処理装置。An aquatic useful invertebrate breeding aquarium provided downstream of the fish and aquaculture aquarium, a means for supplying aquaculture water containing farming residues from the aquaculture aquarium to the breeding aquarium, and invertebrate feces generated from the breeding aquarium A fish and shellfish culture residue treatment device comprising means for separating and removing grains. 請求項3に記載の装置を組み込んだ魚介類養殖装置。A fish culture apparatus incorporating the apparatus according to claim 3. 請求項4に記載の装置を用い、魚介類を飼育する環境汚濁負荷の少ない養殖方法。An aquaculture method that uses the apparatus according to claim 4 and breeds fish and shellfish with a low environmental pollution load. 請求項3に記載の装置の飼育水槽の有用無脊椎動物生息床の底質に砂、砂利の代わりに、沈降性の木炭粒(ペレット)を用いる飼育方法。A breeding method using sedimentable charcoal granules (pellets) instead of sand or gravel on the bottom of the useful invertebrate habitat of the breeding aquarium of the apparatus according to claim 3. 有用無脊椎動物の排泄する糞粒を、同一または異なる有用無脊椎動物に再度給餌する養殖残渣処理法ならびに有用無脊椎動物の飼育方法。A method of treating a culture residue and feeding a useful invertebrate in which fecal particles excreted by the useful invertebrate are fed again to the same or different useful invertebrates.
JP2002178443A 2002-06-19 2002-06-19 Method for resource-circulating treatment of culture residue by using useful invertebrate Pending JP2004016163A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102295394A (en) * 2011-08-22 2011-12-28 大连海洋大学 Culture method of microbial film in biological-filtering pool for lobworm

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102295394A (en) * 2011-08-22 2011-12-28 大连海洋大学 Culture method of microbial film in biological-filtering pool for lobworm
CN102295394B (en) * 2011-08-22 2013-01-02 大连海洋大学 Culture method of microbial film in biological-filtering pool for lobworm

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