JPH03280821A - Purifier for fish culture water - Google Patents
Purifier for fish culture waterInfo
- Publication number
- JPH03280821A JPH03280821A JP2078860A JP7886090A JPH03280821A JP H03280821 A JPH03280821 A JP H03280821A JP 2078860 A JP2078860 A JP 2078860A JP 7886090 A JP7886090 A JP 7886090A JP H03280821 A JPH03280821 A JP H03280821A
- Authority
- JP
- Japan
- Prior art keywords
- pipe
- fish
- water
- tank
- fish culture
- 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
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 50
- 241000251468 Actinopterygii Species 0.000 title abstract description 58
- 239000012528 membrane Substances 0.000 claims abstract description 43
- 244000052616 bacterial pathogen Species 0.000 claims abstract description 14
- 238000000926 separation method Methods 0.000 claims abstract description 11
- 238000001914 filtration Methods 0.000 claims abstract description 9
- 238000011282 treatment Methods 0.000 claims description 16
- 238000009372 pisciculture Methods 0.000 claims description 15
- 238000000746 purification Methods 0.000 claims description 11
- 238000003860 storage Methods 0.000 abstract description 22
- 238000000034 method Methods 0.000 abstract description 19
- 244000005700 microbiome Species 0.000 abstract description 6
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 abstract description 3
- 239000004576 sand Substances 0.000 abstract description 2
- 238000000108 ultra-filtration Methods 0.000 abstract description 2
- 229910052799 carbon Inorganic materials 0.000 abstract 1
- 230000001717 pathogenic effect Effects 0.000 abstract 1
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 14
- 229910021529 ammonia Inorganic materials 0.000 description 7
- 238000004140 cleaning Methods 0.000 description 7
- 238000005273 aeration Methods 0.000 description 6
- 239000007788 liquid Substances 0.000 description 6
- 230000007423 decrease Effects 0.000 description 5
- 230000004907 flux Effects 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 239000005416 organic matter Substances 0.000 description 4
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 3
- 238000011001 backwashing Methods 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 229910052760 oxygen Inorganic materials 0.000 description 3
- 239000001301 oxygen Substances 0.000 description 3
- 241000894006 Bacteria Species 0.000 description 2
- 238000009395 breeding Methods 0.000 description 2
- 230000001488 breeding effect Effects 0.000 description 2
- 239000012141 concentrate Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 230000001546 nitrifying effect Effects 0.000 description 2
- 244000052769 pathogen Species 0.000 description 2
- 239000013049 sediment Substances 0.000 description 2
- 238000004062 sedimentation Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 239000011550 stock solution Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- IOVCWXUNBOPUCH-UHFFFAOYSA-M Nitrite anion Chemical compound [O-]N=O IOVCWXUNBOPUCH-UHFFFAOYSA-M 0.000 description 1
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 244000053095 fungal pathogen Species 0.000 description 1
- 239000012510 hollow fiber Substances 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 238000010907 mechanical stirring Methods 0.000 description 1
- 238000001471 micro-filtration Methods 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 238000011403 purification operation Methods 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 238000001223 reverse osmosis Methods 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 235000015170 shellfish Nutrition 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Farming Of Fish And Shellfish (AREA)
- Biological Treatment Of Waste Water (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
Abstract
Description
【発明の詳細な説明】
[発明の目的]
(産業上の利用分野)
本発明は、魚介類を飼育する槽、池、河川中の水を循環
浄化する養魚水浄化技術に関する。DETAILED DESCRIPTION OF THE INVENTION [Object of the Invention] (Industrial Application Field) The present invention relates to a fish farming water purification technique for circulating and purifying water in tanks, ponds, and rivers in which fish and shellfish are raised.
(従来の技術)
第3図は、従来の養魚水浄化装置の概略構成を示してい
る。(Prior Art) FIG. 3 shows a schematic configuration of a conventional fish farming water purification device.
養魚槽1内の下部には散気管2が配置され、空気源3か
ら管4.前記散気管2を順に介して養魚槽1内に空気が
供給される。一方、補給水5は管6を介して養魚槽1内
に供給され、魚7の飼育がされる。A diffuser pipe 2 is arranged at the lower part of the fish tank 1, and a pipe 4. Air is supplied into the fish tank 1 through the aeration pipe 2 in order. On the other hand, makeup water 5 is supplied into the fish tank 1 through a pipe 6, and fish 7 are raised therein.
養魚槽1の越流水は管8を介して固定床9に注入され、
この固定床9で生物処理・ろ過された水は管10を介し
て沈澱槽11に供給される。沈澱槽11内の液はポンプ
12を作動することによって管13を介して養魚槽1内
に返送され、これらの処理により養魚水が、循環浄化さ
れる。Overflow water from the fish culture tank 1 is injected into a fixed bed 9 via a pipe 8,
Water that has been biologically treated and filtered in this fixed bed 9 is supplied to a settling tank 11 via a pipe 10. The liquid in the sedimentation tank 11 is returned to the fish culture tank 1 through the pipe 13 by operating the pump 12, and the fish culture water is circulated and purified through these treatments.
(発明が解決しようとする課題)
しかしながら、このような従来の養魚水浄化装置におい
ては、養魚槽1内に病原菌やかびが混入し増殖した場合
、病原菌やかびは固定床9ては捕獲されず沈澱槽11内
に浮遊し、さらに養魚槽1に返送される。この状態で浄
化運転を行っても、常に養魚槽1内には病原菌、かびが
存在して繁殖し、魚7が病気になって死滅するといった
問題が生じた。(Problem to be Solved by the Invention) However, in such a conventional fish farming water purification device, if pathogenic bacteria or mold gets mixed into the fish tank 1 and grows, the pathogenic bacteria or mold cannot be captured by the fixed bed 9. It floats in the sedimentation tank 11 and is further returned to the fish culture tank 1. Even if the purification operation was carried out in this state, pathogenic bacteria and mold were always present in the fish culture tank 1 and multiplied, causing problems such as the fish 7 becoming sick and dying.
このように養魚槽1が病原菌、かびに汚染された場合、
養魚槽1や固定床9.配管系をすべて殺菌して再稼働し
なければならず、飼育のランニングコストは極めて大き
いものとなった。If the fish tank 1 is contaminated with pathogenic bacteria or mold in this way,
Fish culture tank 1 and fixed bed 9. All the piping systems had to be sterilized and restarted, making the running costs of breeding extremely high.
さらに、病原菌、かびは増殖によって養魚槽1内液の溶
存酸素を消費するので、魚7が生育していく上で必要な
溶存酸素濃度が低下し、魚7が死滅するという問題もあ
った。Furthermore, as pathogenic bacteria and molds multiply and consume dissolved oxygen in the liquid in the fish culture tank 1, the dissolved oxygen concentration necessary for the growth of the fish 7 decreases, causing the problem that the fish 7 die.
本発明は上記欠点を解決するためになされたもので、そ
の目的とするところは、水に含まれる病原菌、かびを除
去し、魚の飼育を正常に行うことが可能な信頼性の高い
養魚水浄化装置を提供することにある。The present invention has been made to solve the above-mentioned drawbacks, and its purpose is to provide highly reliable fish farming water purification that removes pathogenic bacteria and mold contained in the water and allows normal fish breeding. The goal is to provide equipment.
[発明の構成]
(課題を解決するための手段)
上記の目的を達成するために鋭意検討したところ、養魚
水を循環浄化する養魚水浄化装置において、浄化プロセ
スに生物膜処理槽と圧力駆動分離膜モジュールを配設し
、養魚水を生物膜処理槽で生物処理したのち、圧力駆動
分離膜でろ過することにより、養魚水中の病原菌、かび
を除去し正常に魚が飼育できる養魚水が得られることが
判明した。[Structure of the Invention] (Means for Solving the Problems) In order to achieve the above object, we have conducted intensive studies and found that in a fish farming water purification device that circulates and purifies fish farming water, a biofilm treatment tank and pressure-driven separation are used in the purification process. By installing a membrane module and biologically treating fish culture water in a biofilm treatment tank, and then filtering it with a pressure-driven separation membrane, pathogenic bacteria and mold can be removed from the fish culture water, resulting in fish culture water that can be used to raise fish normally. It has been found.
(作用)
すなわち、養魚水を生物膜処理槽で生物処理することに
より、養魚水中のアンモニア、有機物等の魚類生育阻害
物質が除去され、さらに圧力駆動分離膜でろ過すること
により病原菌、がびが除去される。このろ過水を例えば
養魚槽に返送し循環浄化すれば、養魚水中には病原菌、
かびが存在せず、魚が正常に生育できる良好な水質が維
持される。(Function) In other words, by biologically treating the fish culture water in a biofilm treatment tank, substances that inhibit fish growth such as ammonia and organic matter in the fish culture water are removed, and by filtration with a pressure-driven separation membrane, pathogenic bacteria and fungi are removed. removed. For example, if this filtered water is returned to the fish tank and circulated and purified, pathogenic bacteria and
There is no mold and good water quality is maintained where fish can grow normally.
[実施例] 第1図は本発明の一実施例を示している。[Example] FIG. 1 shows an embodiment of the invention.
養魚槽30内下部には、散気管31が配設され、その散
気管31は管32を介して空気源33と接続されている
。An aeration pipe 31 is disposed in the lower part of the fish culture tank 30, and the aeration pipe 31 is connected to an air source 33 via a pipe 32.
養魚槽30の上端部には管34が、底部には開閉弁35
を有する管36がそれぞれ配設されている。また、養魚
槽30の上部には越流壁37が設けられている。A pipe 34 is provided at the upper end of the fish tank 30, and an on-off valve 35 is provided at the bottom.
A tube 36 having a diameter is provided, respectively. Further, an overflow wall 37 is provided at the upper part of the fish culture tank 30.
越流壁37が位置する養魚槽3oの側面には、開閉弁3
8を有する管39か接続され、この管39は管40を介
して生物膜処理槽である固定床41の上端に接続され、
また管39は開閉弁42を有する管43を介して貯留槽
44の上端に接続されている。An on-off valve 3 is installed on the side of the fish tank 3o where the overflow wall 37 is located.
8 is connected to the pipe 39, and this pipe 39 is connected to the upper end of a fixed bed 41, which is a biofilm treatment tank, via a pipe 40.
Further, the pipe 39 is connected to the upper end of a storage tank 44 via a pipe 43 having an on-off valve 42 .
固定床41は、上部間隙部45とろ床46と支持材47
と下部間隙部48がら成り、ろ床46には活性炭、ゼオ
ライト、砂、セラミックス等のる材が充填されている。The fixed bed 41 includes an upper gap 45, a filter bed 46, and a support material 47.
and a lower gap 48, and the filter bed 46 is filled with a material such as activated carbon, zeolite, sand, or ceramics.
貯留槽44の側面の越流壁49の位置には管50が接続
されている。また、貯留槽44の底部には開閉弁51を
有する管52が接続されている。A pipe 50 is connected to the overflow wall 49 on the side surface of the storage tank 44 . Further, a pipe 52 having an on-off valve 51 is connected to the bottom of the storage tank 44 .
この貯留槽44の下部と前記固定床41の下部間隙部4
8側面とは開閉弁53を有する管54によって接続され
ている。The lower part of this storage tank 44 and the lower gap part 4 of the fixed bed 41
It is connected to the 8th side by a pipe 54 having an on-off valve 53.
また、貯留槽44の側面は、管55.ポンプ56、95
7. 同58. 同59. 同60. Hr14弁61
弁管12a、同62b、スポンジボール捕集器63、管
62cを順次介して圧力分離駆動膜の1つである限外ろ
過膜モジュール(以下、UF膜モジュールと略す)64
の入口側65と配管接続されている。Further, the side surface of the storage tank 44 is connected to a pipe 55. Pump 56, 95
7. 58. 59. 60. Hr14 valve 61
The ultrafiltration membrane module (hereinafter abbreviated as UF membrane module) 64, which is one of the pressure separation drive membranes, is passed through the valve pipes 12a, 62b, the sponge ball collector 63, and the pipe 62c in sequence.
It is connected by piping to the inlet side 65 of.
このUF膜モジュール64の濃縮液出口側66は、管7
0. スポンジボール捕集器71−2管72゜同73.
開閉弁74.管75.同76、調節弁77、管78.流
量計79.管80を順次介して、前記貯留槽44の底部
に配管接続されている。The concentrate outlet side 66 of this UF membrane module 64 is connected to the pipe 7
0. Sponge ball collector 71-2 pipe 72゜73.
Open/close valve 74. Tube 75. 76, control valve 77, pipe 78. Flow meter 79. Piping is connected to the bottom of the storage tank 44 via pipes 80 in sequence.
方、UF膜モジュール64のろ過酸出口側81は、流量
計82を有する管83と管84を順に介して前記養魚槽
30の上端に接続されている。On the other hand, the filtered acid outlet side 81 of the UF membrane module 64 is connected to the upper end of the fish culture tank 30 via a pipe 83 and a pipe 84 having a flow meter 82 in this order.
管57と管58の連結部は、開閉弁85を有する管86
を介して固定床41の底部に接続され、管58と管59
の連結部は管87.調節弁88゜管89.開閉弁90.
管91.流量計92.管93、管84を順次介して養魚
槽3oの上端に接続されている。The connecting portion between the pipe 57 and the pipe 58 is a pipe 86 having an on-off valve 85.
are connected to the bottom of the fixed bed 41 via pipes 58 and 59
The connection part is the pipe 87. Control valve 88° pipe 89. Open/close valve 90.
Tube 91. Flowmeter 92. It is connected to the upper end of the fish tank 3o via a pipe 93 and a pipe 84 in this order.
管59と管60の連結部は、開閉弁94を有する管95
を介して管72と管73の連結部に接続され、管62a
と管62bの連結部は、管96゜開閉弁99.管100
を順次介して管75と管76の連結部に接続されている
。The connecting portion between the pipe 59 and the pipe 60 is a pipe 95 having an on-off valve 94.
is connected to the joint between pipe 72 and pipe 73 through pipe 62a.
The connecting portion between the pipe 62b and the pipe 62b is a pipe 96° opening/closing valve 99. tube 100
It is connected to the connecting portion of the pipe 75 and the pipe 76 through the pipe 75 and the pipe 76 in sequence.
なお、貯留槽44上部にはレベルコントローラ101が
配され、ポンプ56と電気的に接続されている。またス
ポンジボール捕集器71内にはUF膜洗浄用のスポンジ
ボール102が収納されている。Note that a level controller 101 is arranged above the storage tank 44 and is electrically connected to the pump 56. Further, a sponge ball 102 for cleaning the UF membrane is housed in the sponge ball collector 71.
また、図示はされていないが、開閉弁とポンプ56には
電気的に接続したタイマーが設けられている。Further, although not shown, a timer electrically connected to the on-off valve and the pump 56 is provided.
次に、本実施例の作用を■通常運転工程■UF膜運転工
程■UF膜洗浄工程■固定床洗浄工程の4つの工程に分
けて説明する。Next, the operation of this embodiment will be explained by dividing it into four steps: (1) normal operation process, (2) UF membrane operation process, (2) UF membrane cleaning process, and (2) fixed bed cleaning process.
■ 正常運転工程
養魚槽30内に補給水110を管34を介して供給し、
越流壁37から養魚水111を越流する。■ Normal operation process Supplying makeup water 110 into the fish tank 30 through the pipe 34,
The fish culture water 111 is overflowed from the overflow wall 37.
空気源33から管32.散気管31を順に介して養魚槽
30内に空気を吹き込み、溶存酸素濃度を飽和状態(8
1g/1以上)にする。この状態で養魚槽30内に魚1
12を投入し魚の飼育を行う。Air source 33 to tube 32. Air is blown into the fish tank 30 through the aeration pipe 31 in order to bring the dissolved oxygen concentration to a saturated state (8
1g/1 or more). In this state, there is one fish in the fish tank 30.
12 and raise the fish.
また、開閉弁38と同53を開け、その他の開閉弁をす
べて閉じることによって、越流水は管39、開閉弁38
.管40を順に介して固定床41に供給される。In addition, by opening on-off valves 38 and 53 and closing all other on-off valves, overflow water can be removed from pipe 39 and on-off valve 38.
.. A fixed bed 41 is supplied via a pipe 40 in turn.
上部間隙部45に注入された越流水は、ろ床46を通過
する過程で、ろ材表面の好気性微生物や硝化細菌によっ
て生物処理される。アンモニアは硝化細菌によって硝化
され、有機物も好気的に生物分解される。粒径の大きい
懸濁物質(以下、SSと略す)もろ床に保持される。The overflow water injected into the upper gap 45 is biologically treated by aerobic microorganisms and nitrifying bacteria on the surface of the filter medium while passing through the filter bed 46 . Ammonia is nitrified by nitrifying bacteria, and organic matter is also biodegraded aerobically. Suspended solids with large particle sizes (hereinafter abbreviated as SS) are also retained in the bed.
生物処理された水は、支持材47と下部間隙部48を下
降し、管54.開閉弁53を介して貯留槽44に供給さ
れる。The biologically treated water descends through the support member 47 and the lower gap 48, and passes through the pipe 54. It is supplied to the storage tank 44 via the on-off valve 53.
貯留槽44内の貯水が、管55を介して越流した時点で
、開閉弁90を開けてポンプ56を作動させる。これに
より、貯留槽44内液は管87゜調節弁88.管89.
開閉弁90.管91.流量計92.管93.同84を順
次介して、養魚槽30に返送される。なお、レベルコン
トローラ101はポンプ56のインタロック用として機
能する。When the water in the storage tank 44 overflows through the pipe 55, the on-off valve 90 is opened and the pump 56 is activated. As a result, the liquid in the storage tank 44 is transferred to the pipe 87° regulating valve 88. Tube 89.
Open/close valve 90. Tube 91. Flowmeter 92. Tube 93. The fish are returned to the fish tank 30 through the same 84 in sequence. Note that the level controller 101 functions as an interlock for the pump 56.
以上の操作を繰り返して循環浄化が行われる。Circulating purification is performed by repeating the above operations.
この運転は第2図で示すようにt1時間行い、t1時間
経過後図示しないタイマーによって次工程のUF膜運転
工程に切り換わる。This operation is continued for t1 time as shown in FIG. 2, and after the t1 time has elapsed, a timer (not shown) switches to the next step, the UF membrane operation step.
この通常運転では、養魚槽30内の養魚水111のSS
とアンモニア濃度は第2図に示すように徐々に低下する
。SS濃度はCoから徐々に低下して一定値C1に維持
される。アンモニア濃度はAOから徐々に低下して一定
値A、に維持される。In this normal operation, the SS of the fish water 111 in the fish tank 30 is
and the ammonia concentration gradually decreases as shown in FIG. The SS concentration gradually decreases from Co and is maintained at a constant value C1. The ammonia concentration gradually decreases from AO and is maintained at a constant value A.
この一定値A1は魚112の成育阻害を起こさない限界
濃度である。また一定値CIは短期間では成育阻害を起
こさない濃度であるが、病原菌。This constant value A1 is the limit concentration that does not inhibit the growth of the fish 112. In addition, a constant value CI is a concentration that does not inhibit the growth of pathogenic bacteria in a short period of time.
かび等の微生物が存在する濃度であり、長期間の運転は
危険である。従って、この状態では次のUF膜運転工程
に移行することになる。The concentration is such that microorganisms such as mold are present, making long-term operation dangerous. Therefore, in this state, the next UF membrane operation step will be started.
■ UF膜運転工程
前記通常運転工程を長期間続けると、養魚水111を曝
気しているため、養魚水111中の病原菌、かび等の微
生物が多量に増殖してくる。また、微小SSは養魚水1
11中に残存するため曝気によって大きくなり、養魚水
111のSS濃度は徐々に高まってくる。本工程は、こ
れらの微生物。(2) UF membrane operating process If the normal operating process described above is continued for a long period of time, microorganisms such as pathogens and molds in the fish farming water 111 will proliferate in large quantities because the fish farming water 111 is aerated. In addition, micro SS is fish culture water 1
As the SS remains in the fish water 111, it becomes larger due to aeration, and the SS concentration in the fish culture water 111 gradually increases. This process uses these microorganisms.
微小SSを除去する工程である。This is a step of removing minute SS.
まず、タイマー動作によりポンプ56を停止し、開閉弁
90を閉じる。次に開閉弁61と同74を開けてポンプ
56を作動させる。貯留槽44内液は、管55.ポンプ
56.管57.同58.同59、同60.開閉弁61.
管62a、同62b。First, the pump 56 is stopped by a timer operation, and the on-off valve 90 is closed. Next, the on-off valves 61 and 74 are opened to operate the pump 56. The liquid in the storage tank 44 is transferred to the pipe 55. Pump 56. Tube 57. 58. 59, 60. Open/close valve 61.
Tubes 62a and 62b.
スポンジボール捕集器63.管62c、UF膜モジュー
ル64.管70.スポンジボール捕集器71、管72.
同73.開閉弁74.管75.同76、調節弁77、管
78.流量計79.管80を順次介して貯留槽44に返
送され循環する。Sponge ball collector 63. tube 62c, UF membrane module 64. Tube 70. Sponge ball collector 71, tube 72.
Same 73. Open/close valve 74. Tube 75. 76, control valve 77, pipe 78. Flow meter 79. It is returned to the storage tank 44 through the pipe 80 and circulated therein.
UF膜モジュール64でクロスフローろ過され、除菌さ
れた水が管83.流量計82.管84を順に介して養魚
槽30内に返送され、UF膜モジュール64の循環運転
を行う。The water that has been cross-flow filtered and sterilized by the UF membrane module 64 is sent to the pipe 83. Flow meter 82. The water is returned to the fish tank 30 through the pipe 84 in order, and the UF membrane module 64 is operated in circulation.
この循環運転は、第2図で示すようにt2時間行う。This circulation operation is performed for t2 hours as shown in FIG.
第2図に示すように、本工程で養魚水111のSS濃度
は、徐々に値C1から値C2に減少し一定となる。また
アンモニア濃度はほとんど変化しない。値C2は、SS
濃度検出限界以下でかつ病原菌、かび等の微生物はほと
んど含有しない値である。このため、養魚槽30内の魚
112は、この濃度では病気にかかることもなく極めて
正常に成育できる。As shown in FIG. 2, in this step, the SS concentration of the fish culture water 111 gradually decreases from the value C1 to the value C2 and becomes constant. Also, the ammonia concentration hardly changes. The value C2 is SS
The concentration is below the detection limit and contains almost no microorganisms such as pathogenic bacteria and mold. Therefore, at this concentration, the fish 112 in the fish culture tank 30 can grow extremely normally without getting sick.
さらに、このUF膜運転工程を終了すると前記通常運転
工程に戻り、この2つの運転を交互に行う。Furthermore, when this UF membrane operation step is completed, the process returns to the normal operation step, and these two operations are performed alternately.
第2図に示すように、交互運転によってアンモニア濃度
は魚112の成育阻害を起こさないA1値、SS濃度は
C2〜C1値に維持でき、魚112の飼育を断続的に行
うことができる。As shown in FIG. 2, by alternate operation, the ammonia concentration can be maintained at the A1 value that does not inhibit the growth of the fish 112, and the SS concentration can be maintained at the C2 to C1 value, so that the fish 112 can be reared intermittently.
■ UF膜洗浄工程
前記UF膜運転工程におけるクロスクローろ過にともな
って、UF膜の原液側では原液中の固形物が堆積しケー
キ層を形成する。このケーキ層によりろ過のフラックス
が減少し、ろ過動率が低下する。本工程はフラックスの
回復を目的としたものである。(2) UF membrane cleaning step With the cross-claw filtration in the UF membrane operating step, solids in the stock solution accumulate on the stock solution side of the UF membrane to form a cake layer. This cake layer reduces the filtration flux and reduces the filtration rate. This process is aimed at recovering flux.
まず、前記UF膜運転工程を終了後、タイマー動作によ
り、開閉弁61.同74.同90を閉じ、同94.同9
9を開けてポンプ56を作動する。First, after the UF membrane operation step is completed, the on-off valve 61. Same 74. Closing 90, 94. Same 9
9 to operate the pump 56.
この操作によりUF膜モジュール64内の水流は、逆転
して濃縮液出口側が今度は入口側となる。この流れによ
りスポンジボール捕集器71に収納されていたスポンジ
ボール102がUF膜モジュール64内を流通して、ケ
ーキ層を剥離させる。スポンジボール102は再びスポ
ンジボール捕集器63に収まる。ここで、ポンプ56を
停止し、開閉弁94と同99を閉じ、開閉弁61.同7
4を開いてポンプ56を作動すると、再度流れが逆転し
、スポンジボール102がスポンジボール捕集器63か
ら同71に移動する。この操作を5〜20回程度程度返
すことによってフラックスが回復する。By this operation, the water flow inside the UF membrane module 64 is reversed, and the concentrate outlet side now becomes the inlet side. This flow causes the sponge balls 102 stored in the sponge ball collector 71 to flow through the UF membrane module 64, thereby peeling off the cake layer. The sponge ball 102 is placed in the sponge ball collector 63 again. Here, the pump 56 is stopped, the on-off valves 94 and 99 are closed, and the on-off valves 61. Same 7
4 is opened to operate the pump 56, the flow is reversed again and the sponge balls 102 move from the sponge ball collector 63 to the same 71. The flux is restored by repeating this operation about 5 to 20 times.
この工程はタイマーにより1〜3回/日の頻度で行う。This step is performed with a timer at a frequency of 1 to 3 times/day.
また、貯留槽44内下部の沈殿物は、開閉弁51を開け
、管52を介して定期的に排泥する。Further, the sediment in the lower part of the storage tank 44 is periodically drained through the pipe 52 by opening the on-off valve 51.
■ 固定床洗浄工程
本工程は、固定床41のろ床46と支持材47上に付着
した過剰生物膜を剥離・洗浄し、固定床41の通過流量
、すなわち管54の水量を回復する工程である。■ Fixed bed cleaning process This process is a process of peeling off and cleaning excess biofilm adhering to the filter bed 46 and support material 47 of the fixed bed 41, and restoring the flow rate passing through the fixed bed 41, that is, the amount of water in the pipe 54. be.
まず、開閉弁38と同42を開け、養魚水111を貯留
槽44内に供給する。貯留槽44内液が管50を介して
越流すると、開閉弁42と同85を開き、それ以外の開
閉弁を全て閉じポンプ56を作動させる。この操作によ
って貯留槽44内液が固定床41底部に供給され、これ
により、ろ床46内に上向流が発生する。この上向流と
生物膜の接触によって生物膜が剥離する。剥離した生物
膜は貯留槽44に送られその底部に沈殿する。First, the on-off valves 38 and 42 are opened, and the fish culture water 111 is supplied into the storage tank 44. When the liquid in the storage tank 44 overflows through the pipe 50, the on-off valves 42 and 85 are opened, all other on-off valves are closed, and the pump 56 is operated. By this operation, the liquid in the storage tank 44 is supplied to the bottom of the fixed bed 41, thereby generating an upward flow in the filter bed 46. The biofilm peels off due to contact between this upward flow and the biofilm. The detached biofilm is sent to the storage tank 44 and settles at the bottom thereof.
その後、開閉弁42と同85を閉じ、ポンプ56を停止
して開閉弁51を開けば、貯留槽44下部の沈殿物は排
泥される。Thereafter, by closing the on-off valves 42 and 85, stopping the pump 56, and opening the on-off valve 51, the sediment in the lower part of the storage tank 44 is drained.
さらに、開閉弁38.同53.同90を開いてポンプ5
6を作動し、前記通常運転工程に戻るか、開閉弁38.
同53.同61.同74を開いてポンプ56を作動し、
前記UF膜運転工程に戻り、運転を再開する。Furthermore, the on-off valve 38. Same 53. Open the same 90 and pump 5
6 and return to the normal operation process, or open/close valve 38.
Same 53. 61. Open the same 74 and operate the pump 56,
Return to the UF membrane operation step and restart the operation.
以上説明したように本実施例によれば、以下のような効
果が得られる。As explained above, according to this embodiment, the following effects can be obtained.
(1)生物膜処理槽として固定床41を用いたため、有
機物の除去とともに硝化も起こり魚の有害物質のアンモ
ニア、亜硝酸、有機物が除去できる。(1) Since the fixed bed 41 is used as the biofilm treatment tank, nitrification occurs as well as the removal of organic matter, making it possible to remove harmful substances such as ammonia, nitrite, and organic matter to fish.
また、3材間隙より大きい比較的目の粗いSSも除去で
きる。Moreover, relatively coarse SS which is larger than the gap between the three materials can also be removed.
(2) 圧力駆動分離膜として用いたUF膜モジュー
ル64はろ退部積が大きいため、フラックスを高く維持
でき効率的に病原菌を除去できる。(2) Since the UF membrane module 64 used as a pressure-driven separation membrane has a large filtration area, a high flux can be maintained and pathogens can be efficiently removed.
(3) 貯留槽44とポンプ56は、通常運転、UF
膜運転のみならず、固定床41とUF膜モジュール64
の逆洗用にも使用できるため、逆洗用の槽、ポンプを新
たに設置する必要がない。(3) The storage tank 44 and pump 56 are in normal operation, UF
In addition to membrane operation, fixed bed 41 and UF membrane module 64
It can also be used for backwashing, so there is no need to install a new tank or pump for backwashing.
(4) 開閉弁を自動開閉弁で構成したので、開閉の
制御が容易である。(4) Since the on-off valve is configured as an automatic on-off valve, it is easy to control opening and closing.
(5)UF膜モジュール64の洗浄にスポンジボール洗
浄を用いたので、長期にわたってろ退部は開基しない。(5) Since sponge ball cleaning is used to clean the UF membrane module 64, the filtration part will not open for a long period of time.
なお、本発明は第1図の実施例に限定されるものではな
く、次のような他の実施例も包含するものである。Note that the present invention is not limited to the embodiment shown in FIG. 1, but includes other embodiments as follows.
生物膜処理槽は固定床41に限定されず流動床。The biofilm treatment tank is not limited to the fixed bed 41, but may be a fluidized bed.
膨脂床でもよく、また好気、嫌気も問わない。さらにそ
の逆洗機構、剥離方法も第1図に限定されず、曝気法1
機械的撹拌等可能である。A swollen bed may be used, and it does not matter whether it is aerobic or anaerobic. Furthermore, the backwashing mechanism and peeling method are not limited to those shown in Fig. 1, and the aeration method 1
Mechanical stirring, etc. is possible.
また、圧力駆動分離膜は、UF膜に限定されず、マイク
ロろ過膜である中空糸膜、逆浸透膜(RO膜)の適用も
可能である。Further, the pressure-driven separation membrane is not limited to the UF membrane, and hollow fiber membranes and reverse osmosis membranes (RO membranes), which are microfiltration membranes, can also be applied.
さらに、上記生物膜処理槽および圧力駆動分離膜はそれ
ぞれ1体ずつとは限らない。並列あるいは直列的に複数
組み合わせることもできる。Furthermore, the number of the biofilm treatment tank and the pressure-driven separation membrane is not limited to one each. A plurality of them can be combined in parallel or in series.
加えて、上記生物膜処理槽および圧力駆動分離膜と、他
の処理技術を併用することも可能である。In addition, it is also possible to use the above biofilm treatment tank and pressure-driven separation membrane in combination with other treatment techniques.
つまりこの2つの処理と、オゾンあるいは紫外線処理あ
るいは土壌処理等の処理と組み合わせることも可能であ
る。In other words, it is also possible to combine these two treatments with treatments such as ozone, ultraviolet rays, or soil treatment.
[発明の効果]
以上説明したように本発明によれば、養魚水中の病原菌
、かびを除去し、魚が正常に成育できる信頼性の高い養
魚水浄化装置を提供することができる。[Effects of the Invention] As described above, according to the present invention, it is possible to provide a highly reliable fish farming water purification device that can remove pathogenic bacteria and mold from fish farming water and allow fish to grow normally.
第1図は本発明による養魚水浄化装置の一実施例を示す
構成図、第2図は同実施例における運転工程を示す作用
説明図、第3図は従来の養魚水浄化装置の一例を示す概
略構成図である。
30・・・養魚槽
41・・・生物膜処理槽(固定床)
64・・・圧力駆動分離膜(UF膜モジュール)111
・・・養魚水Fig. 1 is a configuration diagram showing an embodiment of a fish farming water purification device according to the present invention, Fig. 2 is an explanatory diagram showing the operation process in the same embodiment, and Fig. 3 shows an example of a conventional fish farming water purification device. It is a schematic block diagram. 30... Fish culture tank 41... Biofilm treatment tank (fixed bed) 64... Pressure-driven separation membrane (UF membrane module) 111
...Fish water
Claims (1)
する圧力駆動分離膜モジュールと、を備えて成る養魚水
浄化装置。[Scope of Claim] A fish farming water purification device comprising: a biological treatment tank for biologically treating fish farming water; and a pressure-driven separation membrane module for filtering pathogenic bacteria, mold, etc. contained in the fish farming water after biological treatment.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2078860A JPH03280821A (en) | 1990-03-29 | 1990-03-29 | Purifier for fish culture water |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2078860A JPH03280821A (en) | 1990-03-29 | 1990-03-29 | Purifier for fish culture water |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH03280821A true JPH03280821A (en) | 1991-12-11 |
Family
ID=13673583
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2078860A Pending JPH03280821A (en) | 1990-03-29 | 1990-03-29 | Purifier for fish culture water |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH03280821A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2017201935A (en) * | 2016-05-12 | 2017-11-16 | タイワン ウォーター リサイクル テクノロジー カンパニー リミテッドTaiwan Water Recycle Technology Co., Ltd. | Method and system for combining aquaculture with plant cultivation |
WO2020095800A1 (en) * | 2018-11-06 | 2020-05-14 | ダイセン・メンブレン・システムズ株式会社 | System for managing quality of rearing water for land-based recirculating aquaculture and method for operating same |
JP2020074761A (en) * | 2018-11-06 | 2020-05-21 | ダイセン・メンブレン・システムズ株式会社 | Breeding water quality management system for circulation type on-land culture and operation method |
-
1990
- 1990-03-29 JP JP2078860A patent/JPH03280821A/en active Pending
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2017201935A (en) * | 2016-05-12 | 2017-11-16 | タイワン ウォーター リサイクル テクノロジー カンパニー リミテッドTaiwan Water Recycle Technology Co., Ltd. | Method and system for combining aquaculture with plant cultivation |
WO2020095800A1 (en) * | 2018-11-06 | 2020-05-14 | ダイセン・メンブレン・システムズ株式会社 | System for managing quality of rearing water for land-based recirculating aquaculture and method for operating same |
JP2020074761A (en) * | 2018-11-06 | 2020-05-21 | ダイセン・メンブレン・システムズ株式会社 | Breeding water quality management system for circulation type on-land culture and operation method |
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