JPH0857489A - Water purifying method and device in shallow water region - Google Patents

Water purifying method and device in shallow water region

Info

Publication number
JPH0857489A
JPH0857489A JP19854994A JP19854994A JPH0857489A JP H0857489 A JPH0857489 A JP H0857489A JP 19854994 A JP19854994 A JP 19854994A JP 19854994 A JP19854994 A JP 19854994A JP H0857489 A JPH0857489 A JP H0857489A
Authority
JP
Japan
Prior art keywords
water
oyster
shallow
shallow water
oxygen
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
JP19854994A
Other languages
Japanese (ja)
Inventor
Michio Makino
道男 牧野
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.)
Kaiyo Kogyo KK
Original Assignee
Kaiyo Kogyo KK
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kaiyo Kogyo KK filed Critical Kaiyo Kogyo KK
Priority to JP19854994A priority Critical patent/JPH0857489A/en
Publication of JPH0857489A publication Critical patent/JPH0857489A/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

  • Biological Treatment Of Waste Water (AREA)
  • Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)

Abstract

PURPOSE: To efficiently purify contaminated matters under water by providing oystershells in a shallow water region and forcibly causing water to flow in the neighborhood thereof so that oxygen is supplied to microorganisms attached to the oystershells to activate them. CONSTITUTION: A great number of oyster shelves 3 each supporting many oystershells are installed at regular intervals at proper locations in a shallow water region 1. An intermittent air lift device 4 is provided at the middle point of each oyster shelf 3. Further, in the device 4, a large number of water lift cylinders are parallelly provided and a common floating room 6 is engaged with the upper parts of the cylinders and an air room 7 is engaged with a lower bubble collecting cylinder. Air bubbles are discharged from the room 7 to lift the water near the bottom 39 of the water so that the water 27 lifted is mixed with the water near the surface 28 of the water to diffuse it and the mixed water is caused to flow against the the seashore 30 and flow reversely so as to flow near the shelves 3 and then the water is lifted. As a result, microorganisms attached to the oystershells are activated, thereby efficiently purifying contaminated matters under water.

Description

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

【0001】[0001]

【産業上の利用分野】この発明は、比較的浅い海水域又
は湖・沼水域(例えば水深数m程度)における浄水を目
的とした浅水域における浄水方法及び装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a shallow water purification method and device for purifying relatively shallow seawater or lake / marsh water (for example, a water depth of about several meters).

【0002】[0002]

【従来の技術】従来浅水域における浄水方法について
は、間欠空気揚水装置を用いて水流を生成する方法及び
装置が提案されている(特開平6−7768号)。また
酸欠の激しい水域には、高酸素水を供給し、拡散する技
術も提案されている(特開平3−109997号)。
2. Description of the Related Art Conventionally, as a water purification method in a shallow water area, a method and an apparatus for generating a water flow using an intermittent air pumping apparatus have been proposed (JP-A-6-7768). In addition, a technique has been proposed in which high oxygen water is supplied to and diffused in a water area with severe oxygen deficiency (Japanese Patent Laid-Open No. 3-109997).

【0003】[0003]

【発明により解決すべき課題】前記従来の技術によれ
ば、比較的に汚濁進行の遅い水域においては、相当の効
果を揚げ、魚貝類の棲息に不適格の場所を良好な漁場域
に好転させている。
According to the above-mentioned prior art, in a water area where the progress of pollution is relatively slow, a considerable effect is brought about, and a place unfit for the habitation of fish and shellfish is turned into a good fishing area. ing.

【0004】然し乍ら生活排水の流入が多い場所、又は
水深が浅い為に水流の生成が不十分な水域においては、
酸素の供給だけでは十分の浄化が出来ない(例えば浄水
速度を上回る汚濁流入の為)問題点があった。
However, in a place where a large amount of domestic wastewater flows in, or in a water area where the generation of water flow is insufficient due to the shallow water depth,
There was a problem that sufficient purification could not be achieved only by supplying oxygen (for example, due to pollution inflow exceeding the water purification rate).

【0005】[0005]

【課題を解決するための手段】前記問題点は、微生物を
活性化しその繁殖を盛にすると共に、汚濁水と微生物と
の接触酸化を促進することにより、改善することに成功
したのである。
The above-mentioned problems have been successfully solved by activating the microorganisms to promote their reproduction and promoting the catalytic oxidation of polluted water and the microorganisms.

【0006】また従来廃棄されていたかき殻を微生物床
に使用することにより、微生物の活性化とその繁殖促進
と、汚濁水の接触の機会を助長し、全体として効率の向
上を達成したのである。しかもかき殻は廃物利用にもな
る。
[0006] Further, by using the conventionally discarded wasted husks in the microbial bed, the activation of the microorganisms, the promotion of their reproduction, and the opportunity of contact with polluted water were promoted, and the efficiency as a whole was improved. Moreover, oyster shells can also be used as waste.

【0007】即ち方法の発明は浅水域内へ所定間隔でか
き殻を配置し、該かき殻配置付近の水を強制流動させ
て、かき殻に付着した微生物に酸素を供給することによ
り微生物を活性化し、これにより水中の汚濁物を処理す
ることを特徴とした浅水域における浄水方法であり、浅
水域内へ所定間隔でかき殻を配置し、該かき殻配置付近
の水を強制流動させ、流水中に高酸素水を供給し、かき
殻に付着した微生物に酸素を供給することにより微生物
を活性化し、これにより水中の汚濁物を処理することを
特徴とした浅水域における浄水方法である。
That is, the invention of the method is to activate the microorganisms by arranging the oyster shells at a predetermined interval in a shallow water area, forcibly flowing water near the oyster shell arrangement, and supplying oxygen to the microorganisms attached to the oyster shells. , This is a method of water purification in shallow water characterized by treating pollutants in water, arranging oyster shells at a predetermined interval in the shallow water area, forcing the water near the oyster shell arrangement to flow into running water. This is a water purification method in shallow water characterized by supplying high-oxygen water and activating oxygen by supplying oxygen to microorganisms adhering to the chaff, thereby treating contaminants in the water.

【0008】また強制流動は間欠空気揚水装置により生
成したものである。
The forced flow is generated by an intermittent air pumping device.

【0009】次に装置の発明は浅水域の水中へかき殻床
を所定間隔で配置し、前記かき殻床の付近に間欠空気揚
水装置を設置したことを特徴とする浅水域の浄水装置で
あり、浅水域の水中へかき殻床を所定間隔で配置し、前
記かき殻床の付近に間欠空気揚水装置を設置すると共
に、高酸素水の供給装置を付設したことを特徴とする浅
水域における浄水装置である。またかき殻床は、かき殻
を保持するかき棚又は網篭としたものである。
Next, the invention of the device is a water purifying device in a shallow water area, characterized in that the underwater rake shell bed in the shallow water area is arranged at a predetermined interval, and an intermittent air pumping device is installed in the vicinity of the above-mentioned oyster shell bed. , Purifying water in a shallow water area by arranging underwater rake shell beds in a shallow water area at a predetermined interval, installing an intermittent air pumping device near the aforementioned hack shell bed, and additionally installing a high oxygen water supply device It is a device. Further, the oyster shell is an oyster shelf or net basket for holding oyster shells.

【0010】前記におけるかき殻の表面には、アンモニ
ア性窒素酸化細菌(以下硝化菌という)が付着している
ことが知られており、産業廃棄物(かき殻)の有効利用
として、汚濁海域の浄化につき基礎実験(水槽内)が行
われていた。
It is known that the ammoniacal nitrogen-oxidizing bacteria (hereinafter referred to as nitrifying bacteria) are attached to the surface of the above-mentioned oyster shell, and as an effective use of industrial waste (oyster husk), A basic experiment (in a water tank) was being conducted for purification.

【0011】然し乍ら浅水域の浄化については、厖大な
水量を強制流動させる手段がなく、かつ酸素不足の場合
の有効な補給手段もないので、実用的には未だ採用し難
いものであった。
However, for the purification of shallow water areas, there is no means for forcibly flowing an enormous amount of water, and there is no effective replenishment means in the case of oxygen shortage, so that it has not been practically adopted yet.

【0012】前記発明においては、かき殻床を用いるこ
とにより硝化菌を繁殖させたが、他の貝殻その他であっ
ても、かき殻と同様の着床効果のあるものは使用するこ
とができる。
In the above invention, nitrifying bacteria were propagated by using a oyster shell, but other shells and the like having the same implantation effect as oyster shells can be used.

【0013】またかき棚を設けると共に、かき殻を水底
に散布して使用することもできる(所定地域へ全面散
布)。
It is also possible to dispose the oyster shells on the bottom of the water and to use the oyster racks (spreading all over a predetermined area).

【0014】実験の結果によれば、かき殻とヘドロとの
併用により硝化菌の繁殖及び活性化を一層向上させるこ
とができるとされているので、水底へ適宜量を散布する
ことは有効である。前記において、かき棚、かき網篭
と、かき殻の散布とを併用することもできる。更にかき
棚及び網篭は魚床或いは海藻の着床にも有効である。
According to the results of the experiment, it is possible to further improve the reproduction and activation of nitrifying bacteria by using the combined use of oyster shell and sludge, so it is effective to spray an appropriate amount on the water bottom. . In the above, it is also possible to use an oyster rack, an oyster basket and a spray of oyster shells together. Further, the oyster rack and the net cage are also effective for the implantation of fish beds or seaweed.

【0015】現在かき殻は産業廃棄物となって大量の有
効利用はないが、この発明により、有効な利用をするこ
とができる。
At present, the husks are industrial wastes and are not effectively used in a large amount, but the present invention enables them to be effectively used.

【0016】前記における浅水域とは、例えば平均水深
5〜6m以下を考慮しているが、水深10mであっても
かき殻床の設置高さを適切にすれば同様の効果がある。
The shallow water area mentioned above is, for example, an average water depth of 5 to 6 m or less. However, even if the water depth is 10 m, the same effect can be obtained by appropriately setting the installation height of the oyster shell bed.

【0017】[0017]

【作用】この発明は、浅水域へかき殻を配置すると共
に、水流を起させたので、かき殻の微生物は酸素を供給
されて繁殖し、効率よく水流中の有機物を分解すること
ができる。また散布したかき殻はヘドロとの共同で、硝
化菌の繁殖を一層活発にすることができる。
According to the present invention, since the oysters are placed in the shallow water area and the water flow is caused, the microorganisms of the oyster shells are supplied with oxygen to reproduce and efficiently decompose organic substances in the water flow. In addition, the sprayed oyster shells, in cooperation with sludge, can further promote the reproduction of nitrifying bacteria.

【0018】[0018]

【実施例1】浅水域1の適所に、かき殻2、2を支承す
るかき棚3、3を所定間隔で設置する。例えば図2のよ
うに、平面10m×5mのかき棚3、3(かき殻床のこ
と)を、50m間隔で4台配置し、各かき棚3に、2cm
程度に破砕したかき殻2を夫々500kg宛積み込む。
[Embodiment 1] Shaft shelves 3 and 3 for supporting shaved shells 2 and 2 are installed at predetermined intervals in appropriate places in a shallow water area 1. For example, as shown in FIG. 2, 4 oyster shelves 3 and 3 (meaning oyster shell floors) having a flat surface of 10 m × 5 m are arranged at intervals of 50 m, and each oyster rack 3 has a length of 2 cm
The shredded husks 2 are loaded to 500 kg each.

【0019】前記かき棚3、3の中央部には間欠空気揚
水装置4を設置する。
An intermittent air pumping device 4 is installed in the central portion of the racks 3 and 3.

【0020】前記間欠空気揚水装置4は、直径30cm、
長さ2.5mの揚水筒5a、5b、5c、5dを4本並
列固定し、その上部に共通の浮室6を嵌装固定すると共
に、下部の集泡筒8に空気室7を嵌装固定したものであ
る(図5)。
The intermittent air pumping device 4 has a diameter of 30 cm,
Four pumping cylinders 5a, 5b, 5c, 5d each having a length of 2.5 m are fixed in parallel, a common floating chamber 6 is fitted and fixed on the upper part thereof, and an air chamber 7 is fitted on a lower foam collecting cylinder 8. It is fixed (Fig. 5).

【0021】空気室7は、図5のように、集泡筒8の外
側へ内筒9、仕切筒10及び外筒11を順次所定間隔で
嵌装し、集泡筒8、内筒9、仕切筒10へ夫々通水孔1
2、13、14を穿設すると共に、頂板15、16と、
底板17で上下を閉鎖して構成したものである。
In the air chamber 7, as shown in FIG. 5, an inner cylinder 9, a partition cylinder 10 and an outer cylinder 11 are fitted to the outside of the foam collecting cylinder 8 in order at predetermined intervals, and the foam collecting cylinder 8, the inner cylinder 9, Water passage hole 1 to each partition 10
2, 13 and 14 are drilled, and top plates 15 and 16 are provided.
The bottom plate 17 is configured to be closed at the top and bottom.

【0022】前記実施例において、エアホース18から
矢示19のように加圧空気を送入すると、加圧空気は空
気室7の内側頂部から逐次たまり、空気室7内の水位を
押し下げる。水位20が通水孔13に達すると、空気室
7内の空気は矢示21、22、23のように通水孔1
2、13、14を通過して、大気泡24となり、集泡筒
8内を矢示25のように上昇し、ついで大気泡24は気
泡24aに分割されて、各揚水筒5a、5b、5c、5
d内を矢示26のように上昇し、各揚水筒の上端から矢
示27、27のように放出される(図1)。この放出さ
れた揚水は、水底39付近の水であるけれども、水面2
8付近の水と混合し、温度、比重(海水の場合)共に水
面付近の水と大差がなくなり矢示29のように水面28
に近接して拡散する。この拡散した水は、海岸30に衝
突して矢示31のように反転し、矢示32のようにかき
棚3付近を通過して、矢示33のように再び揚水筒5
a、5b、5c、5dにより揚水される。
In the above-mentioned embodiment, when pressurized air is fed from the air hose 18 as shown by the arrow 19, the pressurized air is accumulated from the inner top of the air chamber 7 successively and pushes down the water level in the air chamber 7. When the water level 20 reaches the water passage hole 13, the air in the air chamber 7 is moved to the water passage hole 1 as indicated by arrows 21, 22, and 23.
After passing through Nos. 2, 13 and 14, large bubbles 24 are formed and rise in the bubble collecting cylinder 8 as indicated by an arrow 25, and then the large bubbles 24 are divided into bubbles 24a, and the pumping cylinders 5a, 5b, 5c are separated. 5,
In d, it rises as shown by arrow 26 and is discharged from the upper end of each pump as shown by arrows 27, 27 (Fig. 1). This discharged pumped water is the water near the bottom 39 of the water, but the water level 2
When mixed with water around 8, the temperature and specific gravity (in the case of seawater) are almost the same as those near the water surface, and the water surface 28
Spread close to. This diffused water collides with the shore 30 and reverses as shown by the arrow 31, passes through the vicinity of the scraping shelves 3 as shown by the arrow 32, and again as shown by the arrow 33, the pumping cylinder 5 again.
Pumped by a, 5b, 5c and 5d.

【0023】前記揚水筒5a、5b、5c、5dにおけ
る揚水量は、流速1m/secとして、毎分17m3
度である。従って1時間に1020m3 、1日に約25
000m3 揚水できることになる。
The pumping amount in the pumping cylinders 5a, 5b, 5c and 5d is about 17 m 3 / min at a flow velocity of 1 m / sec. Therefore, 1020 m 3 per hour, about 25 per day
It will be able to 000m 3 pumping.

【0024】然して揚水の拡散による影響は10倍以上
と考えられるので、約25万m3 の水に影響を与えるこ
とができる。
Since the influence of the diffusion of pumped water is considered to be 10 times or more, it is possible to affect about 250,000 m 3 of water.

【0025】次に揚水装置を中心とし、半径150mの
円柱内の水量(深さ3mとして)を計算すると、約27
万m3 となる。従って直径30cmの揚水筒4本の揚水量
による影響力は、1日25万m3 と予測されるので、水
深3mの海岸ならば、半径150mの円柱内の全水量に
影響を及ぼす可能性がある。そこで前記揚水装置を30
0m間隔で配置すれば、該水域内を高い効率で浄水が出
来る。尤も前記は揚水の10倍の影響力としたが、揚水
と同量の影響とした場合でも10日間で同様の浄水が可
能となる。
Next, when the amount of water in a cylinder with a radius of 150 m (with a depth of 3 m) is calculated centering on the pumping device, it is about 27.
It will be 10,000 m 3 . Therefore, the influence of the pumping capacity of four pumping cylinders with a diameter of 30 cm is estimated to be 250,000 m 3 a day, so if the coast is 3 m deep, it may affect the total amount of water in the cylinder with a radius of 150 m. is there. Therefore, 30
If they are arranged at 0 m intervals, water can be purified in the water area with high efficiency. Although the above-mentioned influence is 10 times as high as that of pumping, even if the same amount of influence as pumping is used, similar water purification will be possible within 10 days.

【0026】海岸等の汚濁進行度合により異なるが、浄
水能力と、汚濁進行予測とを確定することにより、揚水
装置の容量及び設置密度を決めることができる。
The capacity and installation density of the pumping equipment can be determined by confirming the water purification capacity and the pollution progress prediction, although it depends on the degree of pollution progress on the coast or the like.

【0027】前記のように水面側の水(溶存酸素量はほ
ぼ飽和状態)を水底側(汚濁水底は溶存酸素量は0に近
い)に導き、溶存酸素量を逐次増加させると、前記計算
によれば1日〜10日間で溶存酸素量を改善することが
できる。
As described above, when water on the water surface side (dissolved oxygen amount is almost saturated) is led to the water bottom side (dissolved oxygen amount is close to 0 in the polluted water bottom) and the dissolved oxygen amount is increased successively, the above calculation is performed. According to this, the dissolved oxygen amount can be improved in 1 to 10 days.

【0028】水流中の溶存酸素量が増加すると、かき殻
に付着していた硝化菌が急激に繁殖して汚濁水中の有機
物を分解するので、流水中の有機物は逐次減少する。ま
たヘドロ中の好気性菌も急激に繁殖し、ヘドロ内の有機
物を急激に分解するので、水底も浄化される。
When the amount of dissolved oxygen in the water stream increases, the nitrifying bacteria adhering to the oysters rapidly proliferate and decompose the organic matter in the polluted water, so that the organic matter in the running water gradually decreases. Further, aerobic bacteria in the sludge also rapidly propagate and rapidly decompose organic matters in the sludge, so that the water bottom is also purified.

【0029】従来湖・沼等における実験によれば、揚水
装置を水量に対応して十分能力を発揮できる数だけ設置
した場合には、ほぼ10日〜30日間で目的とする浄化
度に達することが知られている。
According to the experiments in conventional lakes and swamps, when the number of pumping equipment is set to a sufficient level corresponding to the amount of water, the desired degree of purification can be reached in about 10 to 30 days. It has been known.

【0030】この実施例においては、従来の浄水能力
に、かき殻による浄水能力を付加したので、永年かかっ
て汚濁して来た浅水域(例えば浅海域)においても急速
な水質の改善が期待できる。
[0030] In this embodiment, since the water purification capacity by the oyster shell is added to the conventional water purification capacity, rapid improvement in water quality can be expected even in shallow water areas (for example, shallow sea areas) that have been polluted for many years. .

【0031】前記かき棚の配置によって流水中の酸素量
が不足するおそれのある場合には、高濃度酸素水の発生
装置34、34を揚水装置4の付近に設置し、不足酸素
量を補充することができる。
When there is a possibility that the amount of oxygen in the running water will be insufficient due to the arrangement of the racks, the high-concentration oxygen water generators 34, 34 are installed near the pumping device 4 to supplement the insufficient oxygen amount. be able to.

【0032】[0032]

【実施例2】図3、4の実施例は、実施例1のかき棚3
に代えて、網篭35にかき殻を入れて、これを枠体36
に吊下し、枠体36を浮体37で浮遊可能に設置したも
のである。この場合には吊索38の長さを調節して網篭
35の下端を水底39に圧着すれば、枠体36を定置で
きる。吊索38を短くして網篭35を吊り上げることに
より、網篭35を矢示40、40のように揚水装置と共
に移動すれば、移動浄水システムを完成することができ
る。
[Embodiment 2] The embodiment shown in FIGS.
In place of this, put a oyster shell in the net basket 35 and put it in the frame 36
The frame body 36 is suspended by a floating body 37 so that the frame body 36 can be floated. In this case, the frame 36 can be placed by adjusting the length of the hanging rope 38 and crimping the lower end of the net cage 35 to the water bottom 39. The moving water purification system can be completed by moving the net cage 35 together with the pumping device as indicated by arrows 40 and 40 by shortening the hanging rope 38 and hoisting the net cage 35.

【0033】前記枠体36も、実施例1のかき棚のよう
に揚水装置の前後左右に配置することにより、かき殻に
付着した硝化菌によって、水流中の有機物を急速に処理
することができる。
By arranging the frame 36 also in the front, rear, left and right of the pumping apparatus like the oyster rack of the first embodiment, the organic substances in the water stream can be rapidly treated by the nitrifying bacteria adhering to the oyster shell. .

【0034】[0034]

【実施例3】図6、7の実施例は、実施例2の網篭35
を水面付近へ浮上させた場合である。即ち筏46にかき
殻を詰めた網篭35を所定間隔で吊下すると共に、筏4
6に必要な浮体41を固定する。また筏46の中央部は
空間とし、その下方に揚水筒42の上端を臨ませてあ
る。図中43は揚水筒42の上部外側に固定した浮子で
ある。
[Embodiment 3] The embodiment shown in FIGS.
This is the case when is raised near the water surface. That is, a net raft 35 in which a raft 46 is filled with an oyster shell is hung at a predetermined interval, and a raft 4
The floating body 41 required for 6 is fixed. In addition, the central portion of the raft 46 is a space, and the upper end of the pumping cylinder 42 is exposed below it. Reference numeral 43 in the figure denotes a float fixed outside the upper part of the pumping cylinder 42.

【0035】前記筏46は例えば50m×50mとし、
その中央部へ直径30cmの揚水筒42の上端を臨ませ
る。揚水筒42の下方には空気室47が嵌装され、公知
のように気泡弾44を間欠的に上昇させ、揚水する。
The raft 46 is, for example, 50 m × 50 m,
The upper end of the pumping cylinder 42 having a diameter of 30 cm is exposed to the center thereof. An air chamber 47 is fitted below the pumping cylinder 42 to intermittently raise the bubble bullets 44 to pump water, as is known.

【0036】この場合に揚水は、水面28付近の水と混
合すると共に、矢示45、45のように拡散する。この
場合に、拡散水がかき殻と接触するので、かき殻に付着
している硝化菌の働により有機物等を分解する。
In this case, the pumped water mixes with the water near the water surface 28 and diffuses as shown by arrows 45 and 45. In this case, since the diffused water comes into contact with the oyster shell, organic substances and the like are decomposed by the action of nitrifying bacteria adhering to the oyster shell.

【0037】前記揚水筒は単筒について説明したが、複
合筒(例えば直径30cmの単筒を4本結束)としても同
様である。
The pumping cylinder has been described as a single cylinder, but the same applies to a composite cylinder (for example, four single cylinders having a diameter of 30 cm are bundled).

【0038】[0038]

【発明の効果】この発明によれば間欠空気揚水装置によ
って浅水域の厖大な水量を所定方向に流動させて水流を
発生させ、かき殻付近を通過させると共に、水中の溶存
酸素量を改善するので、従来不可能視されていたヘドロ
の堆積した浅水域の浄水を効率よく行うことができる効
果がある。
According to the present invention, the intermittent air pumping device causes a large amount of water in a shallow water region to flow in a predetermined direction to generate a water flow, which allows it to pass near the oyster shell and improve the amount of dissolved oxygen in water. There is an effect that it is possible to efficiently purify shallow water where sludge has accumulated, which was considered impossible in the past.

【0039】この発明の装置によれば、浅水域の水を有
効に流動させ汚水浄化能力の管理が容易となり、最少の
設備で最大の効果をあげることができる。また産業廃棄
物となっていたかき殻を有効に使用し、汚水の浄化のみ
ならず魚床及び水藻床として有効である。
According to the apparatus of the present invention, the water in the shallow water can be effectively flowed to facilitate the management of the sewage purification capacity, and the maximum effect can be obtained with the minimum equipment. In addition, by effectively using the oyster shell that had been industrial waste, it is effective not only for purification of sewage but also for a fish bed and an algae bed.

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

【図1】この発明の実施例の正面図。FIG. 1 is a front view of an embodiment of the present invention.

【図2】同じくかき棚の配置例を示す拡大平面図。FIG. 2 is an enlarged plan view showing an arrangement example of the scraping rack in the same manner.

【図3】同じく網篭を用いた実施例の拡大正面図。FIG. 3 is an enlarged front view of an embodiment using the same basket.

【図4】同じく網篭の配置例を示す拡大平面図。FIG. 4 is an enlarged plan view showing an arrangement example of a net basket.

【図5】同じく揚水装置の空気室部分の拡大断面図。FIG. 5 is an enlarged sectional view of an air chamber portion of the water pumping device.

【図6】同じく他の実施例の一部拡大正面図。FIG. 6 is a partially enlarged front view of another embodiment of the present invention.

【図7】同じく一部を省畧した平面図。FIG. 7 is a plan view in which a part is also omitted.

【符号の説明】[Explanation of symbols]

1 浅水域 2 かき殻 3 かき棚 4 間欠空気揚水装置 5a、5b、5c、5d 揚水筒 6 浮室 7 空気室 8 集泡筒 9 内筒 10 仕切筒 11 外筒 12、13、14 通水孔 15、16 頂板 17 底板 18 エアホース 20 水位 24 大気泡 24a 気泡 28 水面 30 海岸 35 網篭 36 枠体 37 浮体 38 吊索 39 水底 41 浮体 42 揚水筒 43 浮子 44 気泡弾 46 筏 1 Shallow water 2 Shaft 3 Shaking rack 4 Intermittent air pumping device 5a, 5b, 5c, 5d Pumping cylinder 6 Floating chamber 7 Air chamber 8 Foam collecting cylinder 9 Inner cylinder 10 Partition cylinder 11 Outer cylinder 12, 13, 14 Water passage hole 15, 16 Top plate 17 Bottom plate 18 Air hose 20 Water level 24 Large air bubble 24a Air bubble 28 Water surface 30 Coast 35 Net gauze 36 Frame 37 Float 38 Suspension 39 Water bottom 41 Float 42 Pumping cylinder 43 Float 44 Rape 46 Raft

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 浅水域内へ所定間隔でかき殻を配置し、
該かき殻配置付近の水を強制流動させて、かき殻に付着
した微生物に酸素を供給することにより微生物を活性化
し、これにより水中の汚濁物を処理することを特徴とし
た浅水域における浄水方法。
1. Arranging oyster shells in shallow water at predetermined intervals,
Water purification method in shallow water characterized by forcibly flowing water near the arrangement of the oyster shells to activate oxygen by supplying oxygen to the microorganisms attached to the oyster shells, thereby treating contaminants in the water .
【請求項2】 浅水域内へ所定間隔でかき殻を配置し、
該かき殻配置付近の水を強制流動させ、流水中に高酸素
水を供給し、かき殻に付着した微生物に酸素を供給する
ことにより微生物を活性化し、これにより水中の汚濁物
を処理することを特徴とした浅水域における浄水方法。
2. Arranging oyster shells in shallow water at predetermined intervals,
To forcibly flow water near the arrangement of the oyster shell, supply high-oxygen water into running water, and activate oxygen by supplying oxygen to the microorganisms adhering to the oyster shell, thereby treating contaminants in the water. A method for water purification in shallow water.
【請求項3】 強制流動は間欠空気揚水装置により生成
した請求項1又は2記載の浅水域の浄水方法。
3. The shallow water purification method according to claim 1, wherein the forced flow is generated by an intermittent air pumping device.
【請求項4】 浅水域の水中へかき殻床を所定間隔で配
置し、前記かき殻床の付近に間欠空気揚水装置を設置し
たことを特徴とする浅水域の浄水装置。
4. A water purifier in a shallow water area, characterized in that the underwater shackle bed in the shallow water area is arranged at predetermined intervals, and an intermittent air pumping device is installed in the vicinity of the shackle bed.
【請求項5】 浅水域の水中へかき殻床を所定間隔で配
置し、前記かき殻床の付近に間欠空気揚水装置を設置す
ると共に、高酸素水の供給装置を付設したことを特徴と
する浅水域における浄水装置。
5. An underwater rake shell bed in a shallow water area is arranged at a predetermined interval, an intermittent air pumping device is installed near the hack shell bed, and a high oxygen water supply device is additionally provided. Water purification equipment in shallow water.
【請求項6】 かき殻床は、かき殻を保持するかき棚又
は網篭とした請求項4又は5記載の浅水域における浄水
装置。
6. The water purifying apparatus in shallow water according to claim 4, wherein the oyster shell is an oyster shelf or a net cage for holding oyster husks.
JP19854994A 1994-08-23 1994-08-23 Water purifying method and device in shallow water region Pending JPH0857489A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP19854994A JPH0857489A (en) 1994-08-23 1994-08-23 Water purifying method and device in shallow water region

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP19854994A JPH0857489A (en) 1994-08-23 1994-08-23 Water purifying method and device in shallow water region

Publications (1)

Publication Number Publication Date
JPH0857489A true JPH0857489A (en) 1996-03-05

Family

ID=16393025

Family Applications (1)

Application Number Title Priority Date Filing Date
JP19854994A Pending JPH0857489A (en) 1994-08-23 1994-08-23 Water purifying method and device in shallow water region

Country Status (1)

Country Link
JP (1) JPH0857489A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008238072A (en) * 2007-03-28 2008-10-09 Sohachi Kosugi Water cleaner and water cleanying system
JP2009095803A (en) * 2007-10-18 2009-05-07 Kaiyo Kensetsu Kk Water purification apparatus
GB2489037A (en) * 2011-03-17 2012-09-19 Biomatrix Water Technology Llp A floating integrated water treatment system
JP2015043740A (en) * 2013-08-29 2015-03-12 独立行政法人農業・食品産業技術総合研究機構 Production method of inorganic fertilizer

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008238072A (en) * 2007-03-28 2008-10-09 Sohachi Kosugi Water cleaner and water cleanying system
JP2009095803A (en) * 2007-10-18 2009-05-07 Kaiyo Kensetsu Kk Water purification apparatus
GB2489037A (en) * 2011-03-17 2012-09-19 Biomatrix Water Technology Llp A floating integrated water treatment system
GB2489037B (en) * 2011-03-17 2015-10-14 Biomatrix Water Technology Llp Integrated water treatment system
JP2015043740A (en) * 2013-08-29 2015-03-12 独立行政法人農業・食品産業技術総合研究機構 Production method of inorganic fertilizer

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