JP3114046B2 - Algae treatment equipment for ponds etc. - Google Patents

Algae treatment equipment for ponds etc.

Info

Publication number
JP3114046B2
JP3114046B2 JP16288594A JP16288594A JP3114046B2 JP 3114046 B2 JP3114046 B2 JP 3114046B2 JP 16288594 A JP16288594 A JP 16288594A JP 16288594 A JP16288594 A JP 16288594A JP 3114046 B2 JP3114046 B2 JP 3114046B2
Authority
JP
Japan
Prior art keywords
water
pond
tank
algae
daphnia
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 - Lifetime
Application number
JP16288594A
Other languages
Japanese (ja)
Other versions
JPH08126A (en
Inventor
直澄 山本
豊 小池
義教 黒崎
耕一 前田
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.)
Organo Corp
Original Assignee
Organo Corp
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 Organo Corp filed Critical Organo Corp
Priority to JP16288594A priority Critical patent/JP3114046B2/en
Publication of JPH08126A publication Critical patent/JPH08126A/en
Application granted granted Critical
Publication of JP3114046B2 publication Critical patent/JP3114046B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime 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
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本願発明は、池等、特に公園やリ
ゾート地における自然池や人口池の美感をそこねるアオ
コ等の微細藻類、および底生藻、大型浮遊藻等の大型藻
類を魚やミジンコ等動物プランクトンによって捕食処理
して水の浄化を行う装置に関する。
BACKGROUND OF THE INVENTION The present invention relates to the treatment of microalgae, such as blue-green algae, which disturb the beauty of natural ponds and artificial ponds in parks and resorts, and large algae, such as benthic algae and large floating algae, by fish and daphnia. The present invention relates to an apparatus for purifying water by performing predation processing by zooplankton.

【0002】[0002]

【従来の技術】自然界の湖沼においては、通常、底生藻
や大型浮遊藻等の大型藻類はコイやフナ等の魚によって
捕食され、魚が捕食しないで残留するアオコ等の微細藻
類はミジンコ等の動物プランクトンによって捕食される
ので、アオコが大量に発生することはない。しかし実際
には、これらミジンコ等動物プランクトンも魚によって
捕食される関係にあるため、これら動物プランクトンと
魚が共存する湖沼においては、ミジンコ等動物プランク
トンが魚に捕食されて著しく減少することがあり、その
ことが大量のアオコ発生を招く原因の1つと考えられて
いる。
2. Description of the Related Art In lakes and marshes in the natural world, macroalgae such as benthic algae and large floating algae are usually preyed by fish such as carp and crucian carp, and microalgae such as blue-green algae that remain without predation by fish are daphnia such as daphnia. Predation by zooplankton does not result in large numbers of blue-green algae. However, in practice, these zooplankton such as daphnia are also predated by fish, so in lakes and marshes where these zooplankton and fish coexist, zooplankton such as daphnia may be significantly reduced by fish predation, It is considered that this is one of the causes of the occurrence of a large amount of blue-green algae.

【0003】そこで、本出願人は、さきに、池等におけ
るアオコ等微細藻類および糸状藻等大型藻類を除去する
装置として、糸状藻等大型藻類を捕食すべき魚が放流さ
れている池と、上記池から該池内のアオコ等微細藻類お
よび捕食により生じた魚の代謝物等を含む水が給送され
る槽であって、微細藻類を捕食すべきミジンコ等動物プ
ランクトンが生育されているアオコ処理槽と、上記アオ
コ処理槽から前記捕食により生じた代謝物等を含む水が
給送される槽であって、好気性微生物を表面に着生させ
た充填材が充填された生物膜式浄化槽と、上記浄化槽の
処理水を上記池に循環させる手段とからなる処理装置を
提案した(実願平4−88550)。
[0003] The applicant of the present invention has proposed a device for removing microalgae such as blue-green algae and macroalgae such as filamentous algae in a pond, in which a fish from which macroalgae such as filamentous algae are to be eaten is released. A water treatment tank in which water containing microalgae such as blue water algae in the pond and metabolites of fish generated by predation is fed from the pond, and a water treatment tank in which zooplankton such as daphnia to be preyed on the microalgae are grown. A tank to which water containing metabolites and the like generated by the predation is fed from the water processing tank, and a biofilm-type septic tank filled with a filler that has grown aerobic microorganisms on its surface, A treatment device comprising means for circulating the treated water of the septic tank to the pond was proposed (Japanese Utility Model Application No. 4-88550).

【0004】しかし、さきに提案した装置は、それぞれ
独立したアオコ処理槽および生物膜式浄化槽を備えるた
め装置全体が大型となり、設備費がかさむ欠点があり、
しかもアオコ処理槽は、槽内に水中培養材を設けること
なくミジンコを単に放流しているため、槽内のミジンコ
生育密度が低く、それに伴いアオコを処理する能力も低
いものであり、従って十分なアオコ処理能力をもたせる
ためには大型のアオコ処理槽が必要となり、装置大型化
の欠点がさらに助長されるのである。
[0004] However, the apparatus proposed above has a drawback that the entire apparatus becomes large and the equipment cost increases because it has an independent water treatment tank and a biofilm type septic tank.
Moreover, since the water-blowing tank is simply releasing daphnia without providing a submerged culture material in the tank, the density of the water flea in the tank is low, and the ability to treat blue-green algae is also low. In order to provide the water processing ability, a large water processing tank is required, and the drawback of increasing the size of the apparatus is further promoted.

【0005】また、上記アオコ処理槽においてミジンコ
を高密度で生育させる場合はミジンコの呼吸用の水中酸
素の濃度を大きくする必要があり、その方法として従来
は、アオコ処理槽の水中に空気を直接給送するいわゆる
直接バッキ方法が用いられているが、この方法では槽内
に気泡の上昇に伴う激しい水流が生じ、それが元来水の
流動にきわめて弱いミジンコの増殖を大幅に抑制し、槽
内のミジンコ生育密度をさらに低下させる難点もあっ
た。
In order to grow daphnia at a high density in the water treatment tank, it is necessary to increase the concentration of oxygen in the water for respiration of the water flea. Conventionally, air is directly introduced into the water of the water tank. The so-called direct backing method of feeding is used, but in this method, a violent water flow occurs due to the rise of bubbles in the tank, which significantly suppresses the growth of daphnia that is originally extremely weak to the flow of water, There was also a problem that the density of Daphnia in the inside was further reduced.

【0006】[0006]

【発明が解決しようとする課題および解決手段】本願第
1発明は、装置全体の小型化を課題とし、その解決手段
として、大型藻類を捕食すべき魚、貝、後生動物、甲か
く類等の1種または複数種が放流されている池と、上記
池において捕食されずに残留するアオコ等微細藻類およ
び代謝物による有機物等を含む水が該池から給送される
槽であって、該槽内に、多岐に交錯する微小間隙を有し
て水の流通を許す充填材が内装されると共に、上記アオ
コ等微細藻類を捕食すべきミジンコ等動物プランクトン
および上記有機物等を処理すべき好気性微生物が上記充
填材に共生しているアオコ等処理槽と、上記アオコ等処
理槽の処理水を上記池に循環させる手段とから構成され
る池等の藻類処理装置を提案する。
SUMMARY OF THE INVENTION The first invention of the present application aims at miniaturization of the entire apparatus, and as a means for solving the problem, there are fish, shellfish, metazoans, crustaceans and the like which should prey on large algae. A pond from which one or more species are released, and a tank to which water containing microalgae such as algae and organic matter due to metabolites remaining without being eaten in the pond is supplied from the pond. Inside, a filler is provided that has a wide variety of interspersed microscopic gaps to allow water to flow, and zooplankton such as daphnia to prey on microalgae such as blue water and aerobic microorganisms to treat the organic matter and the like Proposes an algae treatment apparatus such as a pond, which comprises a treatment tank for algae and the like coexisting with the filler and means for circulating the treated water of the treatment tank for algae and the like to the pond.

【0007】[0007]

【作用】上記第1発明の、特にアオコ等処理槽について
みると、ミジンコ等が正常密度に生息しているときは、
ミジンコ等によるアオコ等処理と微生物による有機物等
処理とがほぼ平衡して行われるが、ミジンコ等が異常に
増殖すると、アオコ等処理が活発に行われる反面、ミジ
ンコ等が微生物を捕食し、その結果有機物等処理が低下
することとなる。しかし有機物等処理の低下により有機
物等の濃度が高くなると、ミジンコの活動が低下し、そ
の増殖が抑制され、その結果微生物が増殖して有機物等
処理を活発化する。有機物等濃度が減少していくと、ミ
ジンコ等が再び正常密度に復し、それによりミジンコ等
によるアオコ等処理と微生物による有機物等処理とがほ
ぼ平衡状態に戻るのである。
According to the first invention of the present invention, in particular, regarding the treatment tank for water blooms and the like, when daphnia and the like are inhabiting at a normal density,
The treatment of water moss and the like by water flea is almost in equilibrium with the treatment of organic matter and the like by microorganisms.If the water larva etc. proliferate abnormally, the treatment of water larva etc. is actively performed, but the water flea etc. prey on the microorganisms, and as a result Processing of organic substances and the like will be reduced. However, when the concentration of the organic substance or the like increases due to the decrease in the treatment of the organic substance or the like, the activity of daphnia decreases, and the proliferation of the daphnia is suppressed. As a result, the microorganisms proliferate to activate the treatment of the organic substance or the like. As the concentration of the organic matter and the like decreases, the density of the daphnia and the like returns to the normal density, whereby the treatment of the water maggot and the like with the daphnia and the like and the treatment of the organic matter and the like with the microorganism return to an almost equilibrium state.

【0008】本願第2発明は、上記第1発明のアオコ等
処理槽において、ミジンコ等が異常に減少したとき、ア
オコ等が異常増殖したとき等にミジンコ等を充填材に補
給するためにミジンコ等の予備の安全生息域を確保する
ことを課題とし、その解決手段として、上記第1発明に
おけるアオコ等処理槽の上端に溢流セキを設け、該溢流
セキからの溢流処理水を上記池に循環させると共に、上
記アオコ等処理槽内の水面に、ミジンコ等動物プランク
トンが生息し易い糸状部を有する浮漂植物を浮遊させ
た、池等の藻類処理装置を提案する。
[0008] The second invention of the present application is directed to the water tank of the first invention for replenishing the daphnia or the like to the filler when the water or the like is abnormally decreased or when the water or the like grows abnormally. As a means for solving the problem, an overflow spill is provided at the upper end of the treatment tank for algae or the like in the first invention, and the overflow treated water from the overflow seki is supplied to the pond. The present invention proposes an apparatus for treating algae such as a pond, in which a floating plant having a thread-like portion where zooplankton such as daphnia is easily inhabited is floated on the water surface in the treatment tank such as a blue water.

【0009】本願第3発明は、ミジンコ等および好気性
微生物に対し、激しい水流の発生を抑制して安全に空気
を供給することを課題とし、その解決手段として、上記
第1発明における池の一側に溢流セキを介してバッキ槽
を設置し、上記池からバッキ槽内に溢流される水の中に
空気を直接圧送し、該空気を供給された水を上記アオコ
等処理槽に給送するようにした、池等の藻類処理装置を
提案する。
The third invention of the present application aims at safely supplying air to daphnia and the like and aerobic microorganisms by suppressing the generation of a violent water flow. A back tank is set up on the side via an overflow block, air is directly pumped from the above pond into the water overflowing into the back tank, and the water supplied with the air is supplied to the treatment tank for blue-green algae and the like. The present invention proposes an apparatus for treating algae such as a pond.

【0010】本願第1発明における上記大型藻類を捕食
すべき「魚」には、底生魚としてドジョウ、コリドラ
ス、ナマズ、オトシンクルス等、雑食魚としてコイ、フ
ナ、キンギョ等があり、「貝」にはアップルスネイル、
カワニナ、ヒメタニシ、モノアラガイ、カラスガイ、ヌ
マガイ、サカマキガイ等があり、「後生動物」にはイト
ミミズ、ゴカイ等があり、「甲かく類」にはエビ、カニ
等がある。
In the first invention of the present application, the "fish" to be preyed on by the macroalgae include loach, corydoras, catfish, otocinurus and the like as benthic fish, carp, crucian carp, goldfish and the like as omnivorous fish. Apple Snail,
There are Kawanina, Himetanishi, Monomurai, Raven mussel, Crab mussel, Smelt mussel and the like, "Metamorphic animals" include worms and creatures, and "Crustaceans" include prawns and crabs.

【0011】上記ミジンコ等動物プランクトンとして
は、ミジンコ類、ワムシ類等が用いられる。
As the zooplankton such as daphnia, daphnia and rotifers are used.

【0012】上記アオコ等処理槽の「充填材」として
は、多数本の細い繊維を互にアトランダムに交錯させて
繊維相互間に多岐に交錯する微小間隙をもたせてなる繊
維交錯体(好ましくは繊維の太さが10〜80μ)、細
い繊維の不織布、細い繊維による荒目布、起毛布、網等
を巻いたもの、またはそれらの複数枚を重合したもの、
多数の細い繊維を芯棒に止着したもの、その他砂利、砕
石、合成樹脂製ハニカム等各種のものが使用される。こ
の場合、充填材の空隙率は約50%以上、好ましくは8
0%以上にするとよい。以下図面を参照して本願発明の
実施例について説明する。
As the "filler" for the processing tank for water bloom, etc., a fiber-interplex (preferably a fiber interlinkage) comprising a large number of fine fibers interspersed at random with each other so as to have fine gaps interspersed among the fibers. The thickness of the fiber is 10 to 80μ), a non-woven fabric of a thin fiber, a coarse cloth, a raised cloth, a net or the like wound with a thin fiber, or a polymer obtained by polymerizing a plurality of the sheets.
Various materials such as those obtained by fastening a large number of fine fibers to a core rod, gravel, crushed stone, and honeycombs made of synthetic resin are used. In this case, the porosity of the filler is about 50% or more, preferably 8%.
It is good to make it 0% or more. Hereinafter, embodiments of the present invention will be described with reference to the drawings.

【0013】[0013]

【実施例】図1において、人工の池(1)内に、底生魚
としてドジョウ、ナマズ、雑食魚としてコイ、フナ、キ
ンギョ、貝としてヒメタニシ、カラスガイ、ヌマガイ、
後生動物としてイトミミズ、ゴカイをそれぞれ放流し、
該池(1)の一側に溢流セキ(2)を介してバッキ槽
(3)を連設し、これら池(1)およびバッキ槽(3)
の各水中に、地上に設置されたブロア(4)から空気供
給管(5)、(6)をそれぞれ水中深く延長して空気を
直接供給している。
In FIG. 1, in an artificial pond (1), loach and catfish as benthic fish, carp, crucian carp, goldfish as omnivorous fish, and lime clam, mussel, numa mussel as shellfish.
Release earthworms and worms as metazoans, respectively.
A back tank (3) is connected to one side of the pond (1) via an overflow (2), and the pond (1) and the back tank (3) are connected.
In each of the waters, air supply pipes (5) and (6) are respectively extended deeply into the water from a blower (4) installed on the ground to directly supply air.

【0014】上記池(1)の一側に設けられた支持台
(7)上に、上端を開口した円筒状のアオコ等処理槽
(8)を軸心を垂直に設置してあり、該処理槽(8)
は、槽本体の上面より適宜下の位置および下面から適宜
上の位置にそれぞれ金網(9)、(10)を張設し、両
金網(9)、(10)の間に、本例では太さ約50μの
極細ポリエステル繊維を互にアトランダムに交錯させて
繊維相互間に多岐に交錯する微小間隙を有する繊維交錯
体からなる充填材(11)を水表面下約20cmを上限
として下方底部まで100%の充填率として、水と繊維
交錯体が十分に均等に通過接触するように充填する。こ
の充填材(11)の各微小間隙にミジンコを生息させる
と共に各繊維の表面に好気性微生物を着生させる。
On a support (7) provided on one side of the pond (1), a processing tank (8) having a cylindrical shape with an open upper end is vertically installed with its axis being vertical. Tank (8)
The wire meshes (9) and (10) are stretched at a position appropriately below the upper surface of the tank body and at a position appropriately above the lower surface, respectively. A filler (11) consisting of a fiber-cross-complex having micro gaps interspersed between fibers at random by intermingling ultra-fine polyester fibers with a size of about 50μ with each other at a distance of up to about 20 cm below the water surface up to the lower bottom. Filling is carried out at a filling factor of 100% so that the water and the fiber complex are brought into contact with each other in a sufficiently uniform manner. Daphnia inhabits each minute gap of the filler (11), and aerobic microorganisms grow on the surface of each fiber.

【0015】上記下側金網(10)の直下には原水デス
トリビューター(12)を配置し、該デストリビュータ
ー(12)に、上記バッキ槽(3)の水中に一端を挿入
された原水供給管(13)を原水供給用ポンプ(14)
およびストレーナー(15)を介して管他端において接
続してある。上記デストリビューター(12)の下方ス
ペースは沈澱室(16)とし、該沈澱室底部に排泥デス
トリビューター(17)を配置し、該デストリビュータ
ーに排泥管(18)を接続してある。
A raw water distributor (12) is disposed immediately below the lower wire mesh (10). The raw water supply pipe (1) having one end inserted into the water of the back tank (3) is disposed in the distributor (12). 13) is a raw water supply pump (14)
And the other end of the tube via a strainer (15). A space below the distributor (12) is a sedimentation chamber (16), and a sludge discharger (17) is arranged at the bottom of the sedimentation chamber. A sludge pipe (18) is connected to the distributor.

【0016】上記処理槽(8)の上端部には環状の溢水
セキ(19)を介して環状溢水溝(20)を形成し、該
溢水溝(20)に一端を接続された処理水供給管(2
1)の他端を、コーラル石、石灰石、貝ガラ等を充填し
たPH等調整槽(22)の下部に接続し、該調整槽(2
2)の上部に接続された調整処理水リターン管(23)
を上記池(1)上にのぞませている。
At the upper end of the treatment tank (8), an annular overflow groove (20) is formed via an annular overflow ring (19), and a treated water supply pipe having one end connected to the overflow groove (20). (2
The other end of 1) is connected to the lower part of a pH adjustment tank (22) filled with coral stone, limestone, shellfish, etc., and the adjustment tank (2) is connected.
2) Adjusted treated water return pipe (23) connected to the upper part of
In the pond (1).

【0017】さらに、上記アオコ等処理槽(8)内の水
面には、多数の細い糸状根を有する浮漂植物ウォルフィ
ア(24)を浮遊させ、その糸状根にミジンコを生息さ
せて予備のミジンコ安全生息域を形成してある。
Further, a floating plant Wolfia (24) having a large number of fine thread-like roots is floated on the water surface in the water tank (8), and daphnia is inhabited in the thread-like roots to provide a reserve safe water habitat for Daphnia magna. An area is formed.

【0018】上例の作用を次に説明する。底生藻、大型
浮遊藻およびアオコの発生した池(1)において、底生
藻はドジョウ等底生魚、ヒメタニシ等貝およびイトミミ
ズ等後生動物が捕食し、大型浮遊藻はコイ等雑食魚が捕
食する。ここで、水中のN、P成分は上記各藻類に吸収
され、ついで各水中動物の代謝物等は有機化合物として
水中に排出される。ポンプ(14)の駆動によりバッキ
槽(3)の水を原水供給管(13)を経てアオコ等処理
槽(8)内に圧送し、ついで溢水溝(20)から処理水
供給管(21)、PH等調整槽(22)、調整処理水リ
ターン管(23)を経て池(1)内に水を循環させる
と、池内で捕食されずに残ったアオコおよび上記各動物
の代謝物に起因するアンモニア性窒素等の有機物を含む
原水が溢流セキ(2)からバッキ槽(3)内に溢流し、
そこで空気供給管(6)から空気が直接供給され、この
空気を付与された原水が原水供給管(13)を経てアオ
コ等処理槽(8)内下部に圧送され、充填材(11)の
繊維間微小間隙内を通って充填材内のミジンコおよび微
生物に空気を補給しながらゆっくりと上昇し、その間に
原水中のアオコはミジンコに捕食され、N、P等の有機
物は微生物により分解されてNO2、NO3、PO3とな
る。同時にミジンコの代謝物あるいはミジンコの死ガ
イ、ミジンコの脱皮した表皮なども微生物に分解され
る。このように充填材内にはミジンコ、微生物が付着し
生息しており、また該充填材は原水中の有機物、アオコ
や濁質などを十分に付着捕捉するのでそれらが互に平衡
を保ちながら原水を浄化していくのである。
The operation of the above example will now be described. In the ponds (1) where benthic algae, large floating algae and blue-green algae were generated, benthic algae are predated by benthic fish such as loach, metamorphosed fish such as clams and worms, and large floating algae are preyed by omnivorous fish such as carp. . Here, the N and P components in the water are absorbed by the algae, and the metabolites and the like of each underwater animal are discharged into the water as organic compounds. By driving the pump (14), the water in the back tank (3) is pumped into the treatment tank (8) through the raw water supply pipe (13) and into the treatment tank (8), and then the treated water supply pipe (21) from the overflow groove (20). When water is circulated in the pond (1) through the pH adjustment tank (22) and the adjusted treated water return pipe (23), ammonia that is not preyed in the pond and remains due to the metabolites of the above animals Raw water containing organic matter, such as nitrogen, overflows from the overflow seki (2) into the back tank (3),
Then, air is directly supplied from the air supply pipe (6), and the raw water to which the air has been supplied is pressure-fed to the lower part of the treatment tank (8) through the raw water supply pipe (13), and the fibers of the filler (11) are formed. The water slowly rises while supplying air to the daphnia and microorganisms in the filler through the small gaps, while the water in the raw water is eaten by the daphnia, and organic substances such as N and P are decomposed by the microorganisms and NO 2 , NO 3 and PO 3 . At the same time, metabolites of daphnia or dead clams of daphnia and the exterminated epidermis of daphnia are also decomposed by microorganisms. As described above, daphnia and microorganisms adhere to and inhabit the filler, and the filler sufficiently adheres and captures organic matter, watercress and turbidity in the raw water. It purifies.

【0019】この場合、多数繊維の広い表面積にミジン
コが高密度に付着生息しており、このミジンコの生息し
ている同じ繊維表面にアオコが付着し、大量に蓄積され
ていくので、ミジンコによるアオコ捕食が容易に行わ
れ、しかもアオコ濃度が高くなるとミジンコの捕食速度
がきわめて高くなる傾向がある(濃度により数百倍にも
達する)ので、速かなアオコ処理が行われる。それ故処
理槽(8)の容積を小さくすることが可能となる。
In this case, daphnia adheres and inhabits the large surface area of a large number of fibers at a high density, and a large amount of blue water adheres to the surface of the same fiber where the daphnia lives and accumulates in a large amount. Predation is easily carried out, and as the concentration of blue-green algae increases, the predation rate of daphnia tends to be extremely high (several hundred times depending on the concentration). Therefore, the volume of the processing tank (8) can be reduced.

【0020】また、上記空気を付与された原水は処理槽
(8)内をゆっくり上昇するから、水の流動に弱いミジ
ンコに対し悪影響を与えることはない。
Since the raw water supplied with the air slowly rises in the treatment tank (8), there is no adverse effect on daphnia which is weak in water flow.

【0021】上記充填材(11)におけるミジンコの量
が減少したとき、アオコが異常増殖したとき等には、上
記浮漂植物(24)に生息しているミジンコが充填材
(11)に補充される。
When the amount of daphnia in the filler (11) is reduced, or when blue-green algae grows abnormally, etc., the daphnia inhabiting the floating plant (24) is replenished to the filler (11). .

【0022】上記処理槽(8)で処理された水は溢流セ
キ(19)、溢流溝(20)、処理水供給管(21)を
経てPH等調整糟(22)内に送られ、ここで処理水中
のNO2、NO3、PO3はコーラル石等に中和結合され
る。なお、上記コーラル石等からはカルシウムが溶出
し、上記池(1)内の水中動物に栄養塩を与える。
The water treated in the treatment tank (8) is sent through an overflow tank (19), an overflow groove (20) and a treated water supply pipe (21) into an adjustment tank (22) such as a PH. Here, NO 2 , NO 3 , and PO 3 in the treated water are neutralized and bonded to coral stone and the like. Calcium is eluted from the coral stone or the like, and gives nutrients to the underwater animals in the pond (1).

【0023】[0023]

【発明の効果】本願第1発明の池等の藻類処理装置によ
れば、従来のミジンコによるアオコ等処理槽と好気性微
生物による浄化槽との2槽を備えた藻類処理装置と比較
し、1つの処理槽内の充填材にミジンコ等動物プランク
トンと好気性微生物とを共生させ、該処理槽でアオコ等
微細藻類および有機物等の処理を行うようにしたから、
装置全体の小型化および設備費の削減が実現できるので
ある。
According to the apparatus for treating algae such as a pond of the first invention of the present application, compared with a conventional apparatus for treating algae such as water flea and a septic tank using an aerobic microorganism, which is one tank, Since zooplankton such as daphnia and aerobic microorganisms coexist in the filler in the treatment tank, and microalgae such as blue-green algae and organic matter are treated in the treatment tank,
This makes it possible to reduce the size of the entire apparatus and reduce equipment costs.

【0024】本願第2発明の池等の藻類処理装置によれ
ば、上記第1発明の効果に加え、処理槽の充填材内のミ
ジンコ等動物プランクトンが異常に減少したとき、アオ
コ等微細藻類が異常増殖してミジンコ等がさらに必要に
なったとき等に、浮漂植物に生息するミジンコ等を補給
することができ、それによりアオコ等微細藻類の処理を
安定して行うことができる。
According to the apparatus for treating algae such as a pond of the second aspect of the present invention, in addition to the effects of the first aspect, when zooplankton such as daphnia in the filler in the treatment tank is abnormally reduced, microalgae such as blue-green algae are reduced. Daphnia and the like that inhabit floating plants can be replenished when, for example, Daphnia has become more necessary due to abnormal growth, whereby the treatment of microalgae such as blue-green algae can be performed stably.

【0025】本願第3発明の池等の藻類処理装置によれ
ば、上記第1発明または第2発明の効果に加え、バッキ
槽で予め空気を供給された水をアオコ等処理槽に給送
し、該水をゆっくりと槽内に流通させて空気を補給する
から、水の流動にきわめて弱いミジンコ等に何ら悪影響
を与えることがなく、順調な成育を維持することができ
る。
According to the apparatus for treating algae such as a pond of the third invention of the present application, in addition to the effects of the first invention or the second invention, water supplied with air in advance in a back tank is supplied to a treatment tank for a blue moss. Since the water is slowly circulated in the tank to replenish the air, smooth growth can be maintained without any adverse effect on daphnia or the like which is extremely weak in the flow of water.

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

【図1】本装置全体の一部省略縦断正面図である。FIG. 1 is a partially omitted longitudinal front view of the entire apparatus.

【符号の説明】[Explanation of symbols]

1 池 2 溢流セキ 3 バッキ槽 6 空気供給管 8 アオコ等処理槽 11 充填材 13 原水供給管 19 溢流セキ 21 処理水供給管 24 浮漂植物ウォルフィア Reference Signs List 1 pond 2 overflow overflow 3 back tank 6 air supply pipe 8 treatment tank for blue water etc. 11 filling material 13 raw water supply pipe 19 overflow flood 21 treated water supply pipe 24 floating plant Wolfia

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI A01K 67/033 A01K 67/033 C02F 3/06 ZAB C02F 3/06 ZAB (72)発明者 前田 耕一 東京都文京区本郷5丁目5番16号 オル ガノ株式会社内 (56)参考文献 特開 平3−290130(JP,A) (58)調査した分野(Int.Cl.7,DB名) A01K 63/00 - 63/04 ────────────────────────────────────────────────── ─── Continued on the front page (51) Int.Cl. 7 Identification code FI A01K 67/033 A01K 67/033 C02F 3/06 ZAB C02F 3/06 ZAB (72) Inventor Koichi Maeda 5-Chome Hongo, Bunkyo-ku, Tokyo No. 5-16 Organo Corporation (56) References JP-A-3-290130 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) A01K 63/00-63/04

Claims (3)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 大型藻類を捕食すべき魚、貝、後生動
物、甲かく類等の1種または複数種が放流されている池
と、 上記池において捕食されずに残留するアオコ等微細藻類
および代謝物による有機物等を含む水が該池から給送さ
れる槽であって、該槽内に、多岐に交錯する微小間隙を
有して水の流通を許す充填材が内装されると共に、上記
アオコ等微細藻類を捕食すべきミジンコ等動物プランク
トンおよび上記有機物等を処理すべき好気性微生物が上
記充填材に共生しているアオコ等処理槽と、 上記アオコ等処理槽の処理水を上記池に循環させる手段
とから構成される池等の藻類処理装置。
1. A pond in which one or more species of fish, shellfish, metazoans, crustaceans, etc., which are to prey on macroalgae are released, microalgae such as blue-green algae remaining without predation in the pond, A tank to which water containing organic substances and the like due to metabolites is fed from the pond.In the tank, a filler that allows the flow of water with minute gaps intersecting variously is provided, and Water treatment tank in which zooplankton such as daphnia to prey on microalgae such as blue water and aerobic microorganisms to treat the above organic matter coexist in the filler, and treated water in the water treatment tank for blue water in the pond. An algae treatment device such as a pond, which is configured to circulate.
【請求項2】 上記アオコ等処理槽の上端に溢流セキを
設け、該溢流セキからの溢流処理水を上記池に循環させ
ると共に、上記アオコ等処理槽内の水面に、ミジンコ等
動物プランクトンが生息し易い糸状部を有する浮漂植物
を浮遊させた、請求項1に記載の池等の藻類処理装置。
2. An overflow spill is provided at an upper end of the tank for treating water bloom and the like, and the spilled water from the overflow seki is circulated to the pond. The algae treatment device for a pond or the like according to claim 1, wherein a floating plant having a thread-like portion in which plankton easily lives is floated.
【請求項3】 上記池の一側に溢流セキを介してバッキ
槽を設置し、上記池からバッキ槽内に溢流される水の中
に空気を直接圧送し、該空気を供給された水を上記アオ
コ等処理槽に給送するようにした、請求項1または2に
記載の池等の藻類処理装置。
3. A backing tank is installed on one side of the pond via an overflow baffle, and air is directly pressure-fed into water overflowing from the pond into the backing tank. The algae treatment device for pond or the like according to claim 1 or 2, wherein the algae is fed to the treatment tank for blue water and the like.
JP16288594A 1994-06-22 1994-06-22 Algae treatment equipment for ponds etc. Expired - Lifetime JP3114046B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP16288594A JP3114046B2 (en) 1994-06-22 1994-06-22 Algae treatment equipment for ponds etc.

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP16288594A JP3114046B2 (en) 1994-06-22 1994-06-22 Algae treatment equipment for ponds etc.

Publications (2)

Publication Number Publication Date
JPH08126A JPH08126A (en) 1996-01-09
JP3114046B2 true JP3114046B2 (en) 2000-12-04

Family

ID=15763112

Family Applications (1)

Application Number Title Priority Date Filing Date
JP16288594A Expired - Lifetime JP3114046B2 (en) 1994-06-22 1994-06-22 Algae treatment equipment for ponds etc.

Country Status (1)

Country Link
JP (1) JP3114046B2 (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4685405B2 (en) * 2004-10-14 2011-05-18 喜暉 村山 Water purification equipment
US8845891B2 (en) * 2011-06-09 2014-09-30 T.F.H. Publications, Inc. Aquarium filter media including nanofibers
CN105325375B (en) * 2015-10-09 2017-11-24 南京新侨鑫环保科技有限公司 A kind of pillworm cultural method
CN105284740B (en) * 2015-10-27 2018-03-02 长江大学 Quick discriminating Daphnia magna children's Magna method for distinguishing
CN107624698A (en) * 2016-07-05 2018-01-26 林国义 Fish, dish, the organic plantation cultural method of earthworm symbiosis and device

Also Published As

Publication number Publication date
JPH08126A (en) 1996-01-09

Similar Documents

Publication Publication Date Title
CN109548720B (en) Compound prawn farming systems based on heterotopic biological flocculation is cultivated and normal position is nitrified
CN1105809C (en) Synthetic aouatic structure
GB2335835A (en) Fish feeder
US5466373A (en) Maintenance-free enhancement of aquatic biological filters using amphipods
JPH0771435B2 (en) Fish farming method
JP2002119169A (en) System and method for raising fish and shellfish
JP2012254412A (en) Method and apparatus for biologically treating organic wastewater
JP3114046B2 (en) Algae treatment equipment for ponds etc.
JP6860764B2 (en) Aquaculture method and aquaculture equipment
JP2009060830A (en) Circulating aquarium and method for breeding fish and shellfish using the same
CN110240362A (en) A kind of efficient cultivation tail water processing method
KR20190070152A (en) Method for Management of Fish-raising Farm Using Nano-bubble and Micro-bubble
WO2020122168A1 (en) Aquatic creature cultivation device, purification device, purification method, and molded article
Menasveta et al. A comparative study on larviculture techniques for the giant freshwater prawn, Macrobrachium rosenbergii (de Man)
JP2562528Y2 (en) Algae treatment equipment for ponds etc.
Holtje The biology of sewage sprinkling filters
JP3427091B2 (en) Fish water purification equipment
JP3360075B2 (en) Floating energy-saving water purifier
JPH10304789A (en) Bottom sand for culturing fish and shells, fish and shells culturing/rearing pipe using this and culturing device connecting many of the pipes
JP2001212569A (en) Method for controlling propagation of bacteria, fungi and algae in water
JP2618331B2 (en) Breeding of saltwater fish
JPH06125677A (en) Device for cleaning water for farming and raising fish
JP2020039334A (en) Culture apparatus
JP2002320427A (en) Fishes and shellfishes culturing equipment
JPH0581211B2 (en)

Legal Events

Date Code Title Description
R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

R250 Receipt of annual fees

Free format text: JAPANESE INTERMEDIATE CODE: R250

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080929

Year of fee payment: 8

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080929

Year of fee payment: 8

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090929

Year of fee payment: 9

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20090929

Year of fee payment: 9

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20100929

Year of fee payment: 10

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20110929

Year of fee payment: 11

FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20120929

Year of fee payment: 12