JPH05277498A - Sea water purification device - Google Patents

Sea water purification device

Info

Publication number
JPH05277498A
JPH05277498A JP4081781A JP8178192A JPH05277498A JP H05277498 A JPH05277498 A JP H05277498A JP 4081781 A JP4081781 A JP 4081781A JP 8178192 A JP8178192 A JP 8178192A JP H05277498 A JPH05277498 A JP H05277498A
Authority
JP
Japan
Prior art keywords
water
algae
aquarium
module
mineral
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
JP4081781A
Other languages
Japanese (ja)
Inventor
Keiko Nakanishi
圭子 中西
Masao Maki
正雄 牧
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.)
Panasonic Holdings Corp
Original Assignee
Matsushita Electric Industrial Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Matsushita Electric Industrial Co Ltd filed Critical Matsushita Electric Industrial Co Ltd
Priority to JP4081781A priority Critical patent/JPH05277498A/en
Publication of JPH05277498A publication Critical patent/JPH05277498A/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
    • 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

Landscapes

  • Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
  • Physical Water Treatments (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Farming Of Fish And Shellfish (AREA)
  • Biological Treatment Of Waste Water (AREA)

Abstract

PURPOSE:To prevent algae from sticking to the wall surface of an aquarium or pebble and thereby dispense with the trouble to clean the aquarium periodically by providing a nitrification module consisting of a mineral based on oceanic nitrifying bacteria, a basic substance and a sterilization/algae extermination module with a specified ultra-violet beam lamp, and an injector in the forced circulation flow path of the aquarium. CONSTITUTION:Water in an aquarium 1 is forcibly circulated using a pump 2, entering a nitrification module filled with a mineral 3 based on a basic substance. As this mineral 3 has a large amount of oceanic nitrifing bacteria proliferating on the surface, ammonia excreted by fish is oxidized as nitric acid efficiently. Next, the water rendered harmless has pathogenes and algae in the water exterminated by sterilization effects using an ultraviolet lamp 6, in a sterilization/algae extermination module 5, which is capable of generating an ultraviolet dosage of more than 1.6X10<4>W.s/day. After that, air is supplied into the water using an ejector 7, and the water returns to the aquatic tank 1 passing through a pipe 8.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、観賞魚用水槽の水、魚
の養殖用水などの海水を浄化し水中の病原菌や藻類を殺
菌殺藻する家庭用もしくは業務用海水浄化装置に関する
ものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a domestic or commercial seawater purification apparatus for purifying seawater such as water in an aquarium for ornamental fish and water for aquaculture of fish to sterilize and kill pathogens and algae in the water.

【0002】[0002]

【従来の技術】一般に、観賞魚水槽において、水槽中に
は魚の代謝作用と食べ残しの餌の分解と排泄物等が原因
でアンモニアや汚れの発生、病原菌の繁殖等の課題があ
った。
2. Description of the Related Art Generally, in an aquarium fish tank, there have been problems such as generation of ammonia and dirt, propagation of pathogenic bacteria, etc. due to the metabolic action of fish, decomposition of uneaten food and excrement.

【0003】これらの問題点を改善する目的で従来から
提案されているオーバーフロータイプの海水浄化装置を
図8に基づいて説明する。図8において水槽9内の水は
オーバーフローパイプ10を経由して、海水浄化槽11
でカキの貝殻、サンゴ砂等のろ材12によってアンモニ
アを除去し、紫外線ランプ13で病原菌を殺菌し、ポン
プ14で水槽9に戻される。酸素の補給は、水槽水にエ
アーポンプ15でエアレーションを行っている。
An overflow type seawater purifying apparatus which has been conventionally proposed for the purpose of improving these problems will be described with reference to FIG. In FIG. 8, the water in the water tank 9 is passed through the overflow pipe 10 to the seawater purification tank 11
Then, ammonia is removed by the filter medium 12 such as oyster shells and coral sand, the pathogen is sterilized by the ultraviolet lamp 13, and the water is returned to the water tank 9 by the pump 14. The oxygen is supplied by aerating the aquarium water with the air pump 15.

【0004】従来から水中の病原菌を殺菌する目的で、
紫外線ランプは用いられてきたが、紫外線量は高々1.8
×103 W・s/日の水準で水中藻類の増殖防止には効果
はなかった。
Conventionally, for the purpose of sterilizing pathogenic bacteria in water,
UV lamps have been used, but the amount of UV light is at most 1.8.
At the level of × 10 3 W · s / day, there was no effect in preventing the growth of algae in water.

【0005】また殺藻技術としては、薬剤を用いる方
法、海水の電気分解による塩素処理を行う方法などが従
来から知られている。
Further, as algae killing technology, a method using a chemical agent, a method for performing chlorine treatment by electrolysis of seawater, etc. have been conventionally known.

【0006】[0006]

【発明が解決しようとする課題】しかしながら、従来の
ろ材では、海洋性硝化細菌の付着表面積が小さい為に、
海水浄化の効率が悪く、その結果海水浄化槽の大きさが
大きくなるという課題があった。
However, in the conventional filter medium, since the surface area of the marine nitrifying bacteria attached is small,
There was a problem that the efficiency of seawater purification was poor and, as a result, the size of the seawater purification tank became large.

【0007】また、浄化開始から2、3週間経過する
と、水中藻類が増殖し、水槽の壁面や敷石に藻類が付着
し、定期的な水槽掃除が必要となる。従来から知られて
いる殺藻技術は、薬剤を用いる方法、海水の電気分解に
よる塩素処理を行う方法などである。しかし、薬剤は観
賞魚などの水中飼育生物や、硝化細菌に悪影響を及ぼす
上に、耐久性がない。海水の電気分解による塩素処理
は、高濃度では観賞魚などの水中飼育生物や硝化細菌に
悪影響を及ぼし、低濃度では効果が認められず、濃度管
理が困難である。そこで観賞魚などの水中飼育生物や硝
化細菌に悪影響がなく、メンテナンスの簡単な殺藻技術
が求められてきたが、決定的に有効な技術は知られてい
なかった。
Also, a few weeks after the start of purification, algae in water grow and algae adheres to the wall surface and paving stones of the aquarium, which necessitates regular cleaning of the aquarium. Conventionally known algicidal techniques include a method of using a chemical agent and a method of chlorine treatment by electrolysis of seawater. However, the drug has an adverse effect on aquatic animals such as ornamental fish and nitrifying bacteria and is not durable. Chlorine treatment by electrolysis of seawater has a bad influence on aquatic animals such as ornamental fish and nitrifying bacteria at high concentration, and at low concentration, no effect is observed and concentration control is difficult. Therefore, there has been a demand for an algicidal technique that does not adversely affect underwater animals such as ornamental fish and nitrifying bacteria and is easy to maintain, but a decisively effective technique has not been known.

【0008】紫外線についても単に紫外線量を増大させ
れば、殺藻に有効となるかという点に関しては、従来明
確でなかった。
[0008] Regarding ultraviolet rays, it has hitherto not been clear as to whether or not simply increasing the amount of ultraviolet rays would be effective in killing algae.

【0009】本発明は、コンパクトな海水浄化装置を提
供することを第1の目的とする。また、本発明の水中の
藻類を殺藻することで、藻類の水槽壁面や敷石への付着
を防止し、定期的な水槽掃除をなくすことを目的とし
て、各種手段を検討する中から、ある臨界値以上の紫外
線照射が極めて有効なことを見出したものである。
The first object of the present invention is to provide a compact seawater purification device. Further, by killing algae in the water of the present invention, to prevent the adhesion of algae to the aquarium wall surface and paving stones, for the purpose of eliminating periodical aquarium cleaning, from among various means considered, a certain critical It has been found that the irradiation of ultraviolet rays above the value is extremely effective.

【0010】[0010]

【課題を解決するための手段】前記目的を達成するため
本発明の海水浄化装置は、海洋性硝化細菌と、塩基性物
質を主成分とした鉱物質を充填した硝化モジュルと、紫
外線量1.6×104 W・s/日以上となるような紫外線
ランプを備えた殺菌殺藻モジュルと、イジェクターを水
槽水の強制循環流路に配置する構成とする。
In order to achieve the above object, the seawater purification apparatus of the present invention comprises a marine nitrifying bacterium, a nitrification module filled with a mineral substance containing a basic substance as a main component, and an ultraviolet ray amount of 1. The sterilization and algaecide module equipped with an ultraviolet lamp capable of producing 6 × 10 4 W · s / day or more and the ejector are arranged in the forced circulation channel of the aquarium water.

【0011】[0011]

【作用】本発明の海水浄化装置は、塩基性物質を主成分
とする鉱物質に海洋性硝化細菌を大量に繁殖させている
ため、海洋性硝化細菌の活性を高めることができる。
In the seawater purifying apparatus of the present invention, a large amount of marine nitrifying bacteria are propagated in a mineral substance containing a basic substance as a main component, so that the activity of the marine nitrifying bacteria can be enhanced.

【0012】水中の藻類として海水系に最も占有したナ
ビキュラ(Navicula sp.)を用いて増殖試
験を行った結果、1日で約4倍になることを把握した。
図4は増殖試験におけるクロロフィルaの時間変化を示
すものである。
[0012] As a result of a proliferation test using Navicula (Navicula sp.), Which is the most occupied by seawater as algae in water, it was found that the multiplication rate was about four times a day.
FIG. 4 shows the time change of chlorophyll a in the proliferation test.

【0013】ナビキュラ(Navicula sp.)
の増殖速度よりも殺藻速度を大きくするため、1日で藻
類の75%以上を死滅させることが有効と考えられる。
Navicula sp.
It is considered effective to kill 75% or more of the algae in one day in order to increase the algicidal rate higher than the growth rate.

【0014】紫外線出力15Wの紫外線ランプを用いて
藻類の殺藻試験を行った。藻類としては海水系に最も占
有したナビキュラ(Navicula sp.)を用い
た。図5は紫外線ランプによる殺藻試験におけるクロロ
フィルaの時間変化を示すものである。
An algae killing test was carried out using an ultraviolet lamp having an ultraviolet output of 15 W. As algae, Navicula sp., Which was the most occupied by the seawater system, was used. FIG. 5 shows the time change of chlorophyll a in the algaecide test using an ultraviolet lamp.

【0015】図5の結果に基づきナビキュラ(Navi
cula sp.)の75%を死滅させるのに要する紫
外線照射時間は18分となる。これより、藻類の75%
を死滅させるのに要する紫外線量は1.6×104 W・s
となる。
Based on the results shown in FIG.
cura sp. The ultraviolet irradiation time required to kill 75% of the) is 18 minutes. From this, 75% of algae
The amount of ultraviolet light required to kill the fish is 1.6 × 10 4 W ・ s
Becomes

【0016】本発明の海水浄化装置の殺菌殺藻モジュル
の紫外線量は1.6×104 W・s/日以上であるため水
中藻類の75%以上を死滅させることが出来る。藻類の
増殖速度よりも殺藻速度が大きくなるため水中の藻類は
増殖せず、水槽壁面や敷石への付着が防止できる。
Since the ultraviolet light amount of the germicidal algaecidal module of the seawater purifying apparatus of the present invention is 1.6 × 10 4 W · s / day or more, 75% or more of algae in water can be killed. Since the algae killing rate is higher than the algae growth rate, the algae in the water do not grow and it is possible to prevent the algae from adhering to the aquarium wall surface or the pavement.

【0017】[0017]

【実施例】本発明の実施例を図1に基づいて説明する。EXAMPLE An example of the present invention will be described with reference to FIG.

【0018】図1において水槽1の水はポンプ2によっ
て、強制循環し塩基性物質を主成分とする鉱物質3の充
填してある硝化モジュル4に入る。この鉱物質3には海
洋性硝化細菌が大量に繁殖しているので魚の排泄したア
ンモニアは、効率良く硝酸にまで酸化される。無害にな
った水は殺菌殺藻モジュル5で殺菌殺藻され、イジェク
ター7により、水中に空気を供給し、パイプ8を通って
水槽1に戻る。
In FIG. 1, the water in the water tank 1 is forcedly circulated by a pump 2 into a nitrification module 4 filled with a mineral substance 3 containing a basic substance as a main component. Since a large amount of marine nitrifying bacteria propagate in this mineral 3, ammonia excreted by fish is efficiently oxidized to nitric acid. The harmless water is sterilized and killed by the sterilizing and algae killing module 5, and the ejector 7 supplies air into the water, and returns to the aquarium 1 through the pipe 8.

【0019】鉱物質3は、高炉水砕を原料として用い
た。この高炉水砕は、製鉄所の溶鉱炉から溶鉄1トン当
たり0.5トン発生するスラグを急冷して製造され、主に
セメントの原料や土壌改良材として使用されているもの
である。高炉水砕は、多孔質のガラス質に焼成され(表
1)に示すようにCaO、SiO2 、Al2 3 、Mg
Oなどが主成分である。
Mineral material 3 was prepared by using granulated blast furnace as a raw material. This granulated blast furnace is produced by rapidly cooling slag generated in a blast furnace of an iron mill at a rate of 0.5 ton per ton of molten iron, and is mainly used as a raw material for cement and a soil improving material. Granulated blast furnace is fired into a porous glassy material (Table 1), and CaO, SiO 2 , Al 2 O 3 , Mg
O is the main component.

【0020】[0020]

【表1】 [Table 1]

【0021】酸化カルシウムなどが主成分である鉱物質
3の表面には、水中でカルシウムなど2価のプラスイオ
ンが多く存在する。一方、微生物は、マイナスに荷電さ
れているので海水を浄化する海洋性硝化細菌が鉱物質3
に付着しやすく、鉱物質3は海洋性硝化細菌の固定床と
して最適である。
A large amount of divalent positive ions such as calcium are present in water on the surface of the mineral substance 3 containing calcium oxide as a main component. On the other hand, since microorganisms are negatively charged, the marine nitrifying bacteria that purify seawater are minerals 3
The mineral 3 is most suitable as a fixed bed of marine nitrifying bacteria.

【0022】図2は、本発明の殺菌殺藻モジュル5の1
実施例を示すものである。図3は図2のa−b断面図で
ある。殺菌殺藻モジュル5は、直径5.5cm、高さ40cm
の容器に、253.7nmを中心波長とする紫外線を照射
する13w出力の防水型紫外線ランプ6を1本配置し
た。水は、紫外線ランプ6により水中の病原菌や藻類が
殺菌殺藻された後、パイプ8を通って水槽1に戻る。
FIG. 2 shows one of the bactericidal and algal killing modules 5 of the present invention.
An example is shown. FIG. 3 is a sectional view taken along the line ab of FIG. The sterilizing and algae killing module 5 has a diameter of 5.5 cm and a height of 40 cm.
In this container, one 13w output waterproof type ultraviolet lamp 6 for irradiating ultraviolet rays having a central wavelength of 253.7 nm was arranged. After the germs and algae in the water are sterilized and killed by the ultraviolet lamp 6, the water returns to the aquarium 1 through the pipe 8.

【0023】殺菌殺藻モジュルの紫外線量は13Wの紫
外線ランプ、50l水槽で2.5l/minの循環流量、
換水率は72回/日、殺菌殺藻モジュル内の滞留時間は
18sより、1.68×104 W・s/日となり水中藻類
の75%以上を死滅させることが出来る。次に、本発明
の海水浄化装置の効果を下記の実験で判定した。
The ultraviolet light amount of the germicidal algaecide module is a 13 W ultraviolet lamp, a circulation flow rate of 2.5 l / min in a 50 l water tank,
The water exchange rate is 72 times / day, and the residence time in the bactericidal / algicidal module is 18 s, which is 1.68 × 10 4 W · s / day, and 75% or more of algae in water can be killed. Next, the effect of the seawater purification device of the present invention was determined by the following experiment.

【0024】実験に用いた水槽は、内容積50lで、水
温はヒーターとサーモスタットで26±1℃に保つよう
にした。硝化モジュル4は海洋性硝化細菌を繁殖させた
鉱物質3を2l充填し、殺菌殺藻モジュル5は直径5.5
cm、高さ40cmの容器に、253.7nmを中心波長とす
る紫外線を照射する13w出力の防水型紫外線ランプ6
を1本配置したものを用いた。
The water tank used in the experiment had an internal volume of 50 l, and the water temperature was kept at 26 ± 1 ° C. by a heater and a thermostat. Nitrification module 4 is filled with 2 liters of mineral matter 3 in which marine nitrifying bacteria have been propagated, and bactericidal and algicidal module 5 has a diameter of 5.5.
13w output waterproof UV lamp 6 that irradiates UV light with a central wavelength of 253.7nm in a container of cm and height of 40cm.
One was used.

【0025】実験は、水槽(50l)に海水魚(デバス
ズメ)20匹をいれて、2.5l/minの循環流量で循
環し、アンモニア態窒素濃度、亜硝酸態窒素濃度、硝酸
態窒素濃度、壁面付着藻類量を測定した。
In the experiment, 20 seawater fish (Debas sparrows) were placed in a water tank (50 l) and circulated at a circulation flow rate of 2.5 l / min to obtain ammonia nitrogen concentration, nitrite nitrogen concentration, nitrate nitrogen concentration, The amount of algae adhering to the wall surface was measured.

【0026】本発明の海水浄化装置を用いた場合のアン
モニア態窒素濃度、亜硝酸態窒素濃度、硝酸態窒素濃度
の変化を図6に示す。図6より本発明の海水浄化装置
は、海洋性硝化細菌の活性が高く、アンモニアを効率良
く硝酸にまで分解する。
FIG. 6 shows changes in the concentration of ammonia nitrogen, the concentration of nitrite nitrogen, and the concentration of nitrate nitrogen when the seawater purifying apparatus of the present invention is used. From FIG. 6, the seawater purifying apparatus of the present invention has high activity of marine nitrifying bacteria and efficiently decomposes ammonia into nitric acid.

【0027】本発明の海水浄化装置の殺菌殺藻モジュル
を用いた場合(紫外線量1.6×10 4 W・s/日)は、
17週間経過後も壁面及び敷石付着藻類は計数不可能で
あった。
Sterilizing and algae killing module of the seawater purifying apparatus of the present invention
When using (UV amount 1.6 × 10 FourWs / day) is
Even after 17 weeks, the algae attached to the walls and paving stones cannot be counted.
there were.

【0028】従来の海水浄化装置を用いた場合(紫外線
量1.8×103 W・s/日)の壁面付着藻類量の変化を
図7に示す。
FIG. 7 shows changes in the amount of algae adhering to the wall surface when the conventional seawater purifying apparatus was used (ultraviolet ray amount 1.8 × 10 3 W · s / day).

【0029】従来の海水浄化装置を用いた場合は、2週
間目から壁面付着藻類が増加し始め、5週間目には壁面
は藻類で覆われた。
When the conventional seawater purifying apparatus was used, the algae adhering to the wall surface started to increase from the second week and the wall surface was covered with algae at the fifth week.

【0030】また、観賞魚などの水中飼育生物や海洋性
硝化細菌にも、異常はなかった。
There were no abnormalities in aquatic animals such as ornamental fish and marine nitrifying bacteria.

【0031】[0031]

【発明の効果】以上説明したように本発明の海水浄化装
置によれば、塩基性物質を主成分とする鉱物質を海洋性
硝化細菌の固定床に使用しているので、小型コンパクト
にすることが出来る。また、殺菌殺藻モジュルは1.6×
104 W・s/日以上の紫外線量を照射することがで
き、水中の病原菌や藻類を殺菌殺藻するので、藻類の水
槽壁面や敷石への付着を防止することができる。また、
観賞魚などの水中飼育生物や海洋性硝化細菌にも、異常
は発生せず、極めて安全度が高い。
As described above, according to the seawater purifying apparatus of the present invention, since the mineral substance containing the basic substance as the main component is used for the fixed bed of marine nitrifying bacteria, it should be small and compact. Can be done. In addition, the germicidal algaecide module is 1.6 ×
It is possible to irradiate with an amount of ultraviolet rays of 10 4 W · s / day or more, and sterilize and kill pathogenic bacteria and algae in the water, so that it is possible to prevent the algae from adhering to the aquarium wall surface or paving stones. Also,
No abnormalities occur in aquatic animals such as ornamental fish and marine nitrifying bacteria, and the safety is extremely high.

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

【図1】本発明の一実施例における海水浄化装置の構成
断面図
FIG. 1 is a sectional view showing the configuration of a seawater purification device according to an embodiment of the present invention.

【図2】本発明の海水浄化装置の殺菌殺藻モジュル断面
FIG. 2 is a cross-sectional view of the bactericidal and algae killing module of the seawater purification apparatus of the present invention.

【図3】図2のa−b断面図3 is a sectional view taken along the line ab of FIG.

【図4】増殖試験におけるクロロフィルaの時間変化を
示す図
FIG. 4 is a view showing a time change of chlorophyll a in a proliferation test.

【図5】紫外線ランプによる殺藻試験におけるクロロフ
ィルaの時間変化を示す図
FIG. 5 is a diagram showing a time change of chlorophyll a in an algae killing test using an ultraviolet lamp.

【図6】本発明の海水浄化装置を用いた場合のアンモニ
ア、亜硝酸、硝酸濃度変化図
FIG. 6 is a diagram showing changes in the concentration of ammonia, nitrous acid, and nitric acid when the seawater purification device of the present invention is used.

【図7】従来の海水浄化装置を用いた場合の壁面付着藻
類の経時変化図
FIG. 7: Time-dependent change diagram of algae adhering to the wall surface when a conventional seawater purification device is used

【図8】従来の海水浄化装置の構成断面図FIG. 8 is a sectional view showing the configuration of a conventional seawater purification device.

【符号の説明】[Explanation of symbols]

1 水槽 2 ポンプ 3 鉱物質 4 硝化モジュル 5 殺菌殺藻モジュル 6 紫外線ランプ 7 イジェクター 1 Water Tank 2 Pump 3 Minerals 4 Nitrification Module 5 Bactericidal and Algicidal Module 6 Ultraviolet Lamp 7 Ejector

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.5 識別記号 庁内整理番号 FI 技術表示箇所 C02F 3/10 A 3/22 B 3/34 101 D ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 5 Identification code Internal reference number FI technical display location C02F 3/10 A 3/22 B 3/34 101 D

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】水槽の水を強制循環する強制循環流路に、
海洋性硝化細菌と塩基性物質を主成分とした鉱物質から
なる硝化モジュルと、紫外線ランプを備えた殺菌殺藻モ
ジュルと、循環流路の水に空気を供給するイジェクター
と、前記殺菌殺藻モジュルは紫外線量1.6×104 W・s
/日以上となる紫外線ランプを備えた海水浄化装置。
1. A forced circulation flow path for forcibly circulating water in a water tank,
Nitrification module consisting of marine nitrifying bacteria and minerals composed mainly of basic substances, germicidal algicidal module equipped with UV lamp, ejector for supplying air to water in circulation channel, and the germicidal algicidal module Is the amount of ultraviolet rays 1.6 × 10 4 W ・ s
/ A seawater purification device equipped with an ultraviolet lamp that can be used for more than a day.
JP4081781A 1992-04-03 1992-04-03 Sea water purification device Pending JPH05277498A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4081781A JPH05277498A (en) 1992-04-03 1992-04-03 Sea water purification device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4081781A JPH05277498A (en) 1992-04-03 1992-04-03 Sea water purification device

Publications (1)

Publication Number Publication Date
JPH05277498A true JPH05277498A (en) 1993-10-26

Family

ID=13756028

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4081781A Pending JPH05277498A (en) 1992-04-03 1992-04-03 Sea water purification device

Country Status (1)

Country Link
JP (1) JPH05277498A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR960034083A (en) * 1995-03-23 1996-10-22 사까모또 고오이찌 Method and apparatus for removing green algae and preventing abnormal occurrence
JP2004261698A (en) * 2003-02-28 2004-09-24 Ebara Corp Cleaning method for seawater and brackish water and apparatus therefor

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0349630A (en) * 1989-07-18 1991-03-04 Nabitsukusu Rain Kk Apparatus for transporting live fish
JPH0394888A (en) * 1989-09-05 1991-04-19 Matsushita Electric Ind Co Ltd Water sterilizing and purifying device

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0349630A (en) * 1989-07-18 1991-03-04 Nabitsukusu Rain Kk Apparatus for transporting live fish
JPH0394888A (en) * 1989-09-05 1991-04-19 Matsushita Electric Ind Co Ltd Water sterilizing and purifying device

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR960034083A (en) * 1995-03-23 1996-10-22 사까모또 고오이찌 Method and apparatus for removing green algae and preventing abnormal occurrence
JP2004261698A (en) * 2003-02-28 2004-09-24 Ebara Corp Cleaning method for seawater and brackish water and apparatus therefor

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