JPH0691283A - Water area cleaning method - Google Patents

Water area cleaning method

Info

Publication number
JPH0691283A
JPH0691283A JP4270867A JP27086792A JPH0691283A JP H0691283 A JPH0691283 A JP H0691283A JP 4270867 A JP4270867 A JP 4270867A JP 27086792 A JP27086792 A JP 27086792A JP H0691283 A JPH0691283 A JP H0691283A
Authority
JP
Japan
Prior art keywords
water
ozone
water area
filtered
area
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
JP4270867A
Other languages
Japanese (ja)
Inventor
Teruhisa Yoshida
輝久 吉田
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.)
Hitachi Kiden Kogyo Ltd
Original Assignee
Hitachi Kiden Kogyo 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 Hitachi Kiden Kogyo Ltd filed Critical Hitachi Kiden Kogyo Ltd
Priority to JP4270867A priority Critical patent/JPH0691283A/en
Publication of JPH0691283A publication Critical patent/JPH0691283A/en
Pending legal-status Critical Current

Links

Abstract

PURPOSE:To effectively clean the water area polluted with phytoplanktons and make the size of a filtration apparatus compact. CONSTITUTION:Water in the water area P of such as lakes and marshes, moats, ponds, etc. is pumped, filtered through a filration cloth/filtration material and then ozone-containing air is injected into the filtered water 12 to sterilize the microbes such as phytoplanktons which remain in the filtered water 12. The water area P is cleaned by returning the water 14 treated with ozone to the water area P.

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、湖沼、城の堀、池など
の閉鎖性水域の浄化に係り、特に富栄養化して植物プラ
ンクトンの増殖により汚濁した水域浄化方法に関するも
のである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to the purification of closed water areas such as lakes, castle moats, and ponds, and more particularly to a method for cleaning water areas contaminated by eutrophication and growth of phytoplankton.

【0002】[0002]

【従来の技術】従来、汚濁した水域の浄化に対しては、
曝気撹拌装置を設けて水域内を好気化したり、水域内の
水を揚水して濾過装置等により濾過した水を水域に返還
するなどの方法を用いていた。
2. Description of the Related Art Conventionally, for purification of polluted water,
A method of aerating and aerating the inside of the body of water by providing an aeration stirring device, or pumping water in the body of water and returning the water filtered by a filter device to the body of water has been used.

【0003】[0003]

【発明が解決しようとする課題】しかし、前者の場合は
植物プランクトンが豊富な水域では、植物プランクトン
量を減らすことはできず、また後者の場合は、ある程度
植物プランクトンの量を減らすことができるものの、そ
の効果には限界があり、濾過槽を通過した微細なプラン
クトンが水域に戻されると、増殖によって再び数が増す
ため、大量に濾過しなければ効果が得られないという欠
点があった。
However, in the former case, the amount of phytoplankton cannot be reduced in a water area rich in phytoplankton, and in the latter case, the amount of phytoplankton can be reduced to some extent. However, there is a limit to the effect, and when the fine plankton that have passed through the filter tank are returned to the water area, the number increases again due to proliferation, and there is a drawback that the effect cannot be obtained unless a large amount of filtration is performed.

【0004】本発明は植物プランクトンによって汚濁し
た水域を効果的に浄化する方法を提供することにある。
The present invention is to provide a method for effectively purifying water contaminated with phytoplankton.

【0005】[0005]

【課題を解決するための手段】本発明は上記目的を達成
するためになしたもので、湖沼、堀、池等の水域の水を
揚水し、濾布・濾材を用いて濾過を行った後、濾過水に
オゾン含有空気を注入して濾過水に残留する植物プラン
クトン等の微生物を殺菌し、オゾン処理した水を水域に
戻すことにより水域を浄化することを要旨とする。
Means for Solving the Problems The present invention has been made in order to achieve the above-mentioned object, and after water in a water area such as a lake, a moat, or a pond is pumped and filtered using a filter cloth / filter material. The gist of the present invention is to purify a water area by injecting ozone-containing air into the filtered water to sterilize microorganisms such as phytoplankton remaining in the filtered water and returning the ozone-treated water to the water area.

【0006】[0006]

【作用】水域内の植物プランクトンを濾布を用いて濾過
したところ、植物プランクトンのうち5〜10ミクロン
以上ある比較的粒子径の大きいものは濾布によって除去
できるものの、5ミクロン以下のプランクトンは、ほと
んど除去することができず、除去率は通常50%程度で
ある。濾過槽で除去できなかった微小なプランクトン
は、水域内に返送されると水域内で増殖するため、水域
を浄化するためには水域の容量に対して、少なくとも1
週間以内に一循環するだけの量を濾過する必要がある。
そこで本発明は濾過した水に対してオゾンを含む空気で
曝気することにより、濾過水中に残留するプランクトン
の殺菌を行った後、水域に戻す。
When the phytoplankton in the water area is filtered using a filter cloth, the phytoplankton having a relatively large particle size of 5 to 10 microns or more can be removed by the filter cloth, but the plankton of 5 microns or less is It can hardly be removed, and the removal rate is usually about 50%. The minute plankton that could not be removed by the filtration tank will multiply in the water area when it is returned to the water area. Therefore, in order to purify the water area, at least 1
Only one cycle needs to be filtered within one week.
Therefore, in the present invention, the filtered water is aerated with air containing ozone to sterilize the plankton remaining in the filtered water and then return it to the water area.

【0007】[0007]

【実施例】以下、本発明の一実施例を図面に基づいて説
明する。Pは池など汚濁した水域で、窒素やリンなどの
栄養塩を多く溜め、植物プランクトンの増殖が活発な水
域である。水域内のデッドゾーン、または汚濁の激しい
ゾーンに、揚水ポンプ1を設けて植物プランクトンを含
む水を揚水し、濾過装置2に送水する。濾過装置2は濾
布や繊維状の濾材を等を用いた濾過装置で、一日当たり
200立方メートル程度で濾過する従来の砂濾過よりも
高速で濾過できる方式が好ましい。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described below with reference to the drawings. P is a polluted water area such as a pond, where many nutrient salts such as nitrogen and phosphorus are accumulated and phytoplankton is actively growing. A pump 1 is provided in a dead zone or a zone with severe pollution in the water area to pump water containing phytoplankton and send it to the filtering device 2. The filtration device 2 is a filtration device that uses a filter cloth, a fibrous filter material, or the like, and is preferably a system that can perform filtration at a higher speed than conventional sand filtration that filters approximately 200 cubic meters per day.

【0008】濾過水12に対してはオゾン反応槽3にお
いて、オゾンを含む空気を吹き込み、残留する植物プラ
ンクトン等の有機物と接触させる。オゾンはコンプレッ
サ4からの空気を乾燥機5により、空気中の水分を除去
してオゾン発生機6に送気して、無声放電等により酸素
の一部をオゾンに変換させた後、オゾン反応槽3に送気
する。ただし、オゾン含有空気の生成方法は、これに限
定されるものではない。
In the ozone reaction tank 3, air containing ozone is blown into the filtered water 12 to bring it into contact with residual organic matter such as phytoplankton. For ozone, the air from the compressor 4 is removed by a drier 5 to remove moisture in the air and sent to an ozone generator 6, where a part of oxygen is converted to ozone by silent discharge or the like, and then an ozone reaction tank. Insufflate to 3. However, the method of generating ozone-containing air is not limited to this.

【0009】またオゾン含有空気は散気管、散気板を用
いて曝気を行う方法が簡便であるが、必ずしもこれに限
定されるものではなく、機械式の曝気撹拌機と組み合わ
せたり、スタティックミキサーを用いて混合する方法等
も有効である。オゾン反応槽3も、散気塔を別に設けて
もよいが、濾過装置の濾過水槽を使用して濾過水槽にオ
ゾン含有空気を注入してもよい。オゾンと接触させた処
理水14は、水域内を撹拌するために設けた撹拌機、ま
たは曝気撹拌機7の前後に送水して、水域全体に拡散さ
せる。ただし撹拌機は水域の形状や大きさにより、省略
することも可能である。
The ozone-containing air is conveniently aerated by using an air diffuser or an air diffuser, but the method is not necessarily limited to this, and it may be combined with a mechanical aerator or a static mixer. A method of mixing by using is also effective. The ozone reaction tank 3 may also be provided with an air diffusing tower separately, but ozone-containing air may be injected into the filtered water tank by using the filtered water tank of the filtering device. The treated water 14 that has been brought into contact with ozone is sent to the front and rear of an agitator provided for agitating the inside of the water area or the aeration agitator 7, and diffused throughout the water area. However, the stirrer can be omitted depending on the shape and size of the water area.

【0010】次に本発明の動作・作用を説明する。図1
1において、揚水した水11は、濾過装置2に送水さ
れ、水中の浮遊物質が濾材によって除去される。濾材に
付着した浮遊物は、連続的にまたは一定時間間隔で逆洗
することにより、濾材から剥離させて少量の逆洗配水1
3として濾過装置から排出される。この逆洗排水13は
下水道等に放流するか、または濃縮・脱水等を行って汚
泥として系外に搬出する。一方濾過装置は、通常5〜1
0ミクロン以上の粒子に対しては濾材によって阻止して
除去できるが、これよりも小さい粒子のプランクトンは
濾材を通過するため、次のオゾン反応槽3においてオゾ
ン含有空気と接触させ、プランクトンを殺菌した後、処
理水14を水域に返送する。水域内には撹拌機7を設け
ているため、処理水が水域全体に拡散され、水域全体が
徐々に浄化されていく。
Next, the operation and action of the present invention will be described. Figure 1
In 1, the pumped water 11 is sent to the filtering device 2, and the suspended matter in the water is removed by the filter medium. The suspended solids adhering to the filter medium are backwashed continuously or at regular time intervals so as to be separated from the filter medium and a small amount of backwash water 1
It is discharged from the filtration device as 3. The backwash drainage 13 is discharged to a sewer or the like, or concentrated / dehydrated and carried out as sludge to the outside of the system. On the other hand, the filtration device is usually 5 to 1
Particles of 0 micron or larger can be blocked and removed by a filter medium, but since plankton having smaller particles passes through the filter medium, it is brought into contact with ozone-containing air in the next ozone reaction tank 3 to sterilize the plankton. After that, the treated water 14 is returned to the water area. Since the stirrer 7 is provided in the water area, the treated water is diffused throughout the water area, and the entire water area is gradually purified.

【0011】[0011]

【実施例1】約150立方メートルの汚濁した池を3つ
に仕切り、それぞれ約50立方メートルの水域に達し、
下記3つの方法で浄化を行った。ただし、池への流入管
を塞ぎ、池からの排水はオーバーフローのみとした。 (A)…本発明の方法で、50立方メートルの水域に対
し、一日当たり五立方メートルの水を濾過処理した後、
オゾン含有空気で曝気を行って処理水を池に戻した場
合。 (B)…オゾン処理は行わず、一日当たり5立方メート
ルの水を濾過処理のみ行って濾過水を池に戻した場合。 (C)…オゾン処理は行わず、一日当たり15立方メー
トルの水を濾過して濾過水を池に戻した場合。 これらの3方法により、約3ヶ月間運転を行った時の各
水域のSS(浮遊物質)濃度の経時変化を図2に示す。
池水量50立方メートルに対して、一日5立方メート
ル、すなわち、10日間で一循環する程度の濾過量で
は、池内で生産される植物プランクトン量に比べて除去
する量がわずかに大きい程度であるため、(B)に示す
ようにSSがわずかに低下する程度であり、一日15立
方メートル、約3.3日で一循環するように濾過量を大
きくした(C)では、水域内SSがかなり低下し、開始
時の、1リットル当たり56ミリグラムから、60日後
には、一リットル当たり24ミリグラムまで低下し、ほ
ぼ安定した。一方本発明の(A)は、濾過水量は(B)
と同じ、一日当たり5立方メートルと少ないものの、オ
ゾン処理を行って殺菌した水を水域に戻しているため、
濾過水量の大きい(C)よりも急激にSS濃度が低下
し、しかも安定時のSS濃度も低く、一リットル当たり
約11ミリグラムであった。
[Example 1] A polluted pond of about 150 cubic meters was partitioned into three parts, each reaching a water area of about 50 cubic meters,
Purification was performed by the following three methods. However, the inflow pipe to the pond was blocked and the drainage from the pond was limited to overflow. (A) ... By the method of the present invention, after filtering 50 cubic meters of water per day with 5 cubic meters of water,
When aeration is performed with ozone-containing air and the treated water is returned to the pond. (B) ... When ozone is not treated and only 5 cubic meters of water per day is filtered and the filtered water is returned to the pond. (C) ... When ozone treatment is not performed and 15 cubic meters of water are filtered per day and the filtered water is returned to the pond. FIG. 2 shows the time-dependent change in the SS (suspended substance) concentration in each water area when operating for about 3 months by these three methods.
For a volume of pond water of 50 cubic meters, a filtration volume of 5 cubic meters per day, that is, one circulation in 10 days, removes slightly more than the amount of phytoplankton produced in the pond. As shown in (B), SS was only slightly decreased, and when the filtration amount was increased so as to make one circulation of 15 cubic meters per day for about 3.3 days, (C) significantly decreased SS in the water area. From 60 mg per liter at the start to 24 mg per liter after 60 days, it was almost stable. On the other hand, in (A) of the present invention, the amount of filtered water is (B).
Same as the above, although it is as small as 5 cubic meters per day, it returns ozone-treated and sterilized water to the water area,
The SS concentration decreased more rapidly than that of the large amount of filtered water (C), and the SS concentration in the stable state was also low, which was about 11 mg per liter.

【0012】[0012]

【発明の効果】本発明によれば、濾過装置とオゾン発生
機を組み合わせ、水域から揚水した水を濾過処理した
後、オゾン含有空気を濾過水と接触させて、濾過水中に
含まれる植物プランクトン等の微生物を殺菌して水域に
返送するため、濾過装置単独で処理する場合よりも濾過
装置を小さくできる上、浄化の効果も大きく、またオゾ
ン含有空気を直接水域に注入する場合のように、オゾン
によって魚が死亡するというような事故の恐れもなく、
あらかじめSSの大部分を除去した濾過水に対してオゾ
ンを注入するため、少量のオゾンて効果的な処理を行う
ことができるという効果を有する。
According to the present invention, a filter device and an ozone generator are combined, the water pumped from the water area is filtered, and then ozone-containing air is brought into contact with the filtered water to contain phytoplankton contained in the filtered water. Since the microorganisms are sterilized and returned to the water area, the size of the filtration apparatus can be made smaller than in the case where the filtration apparatus is used alone, and the effect of purification is great, and the ozone-containing air is directly injected into the water area. There is no fear of accidents such as death of fish due to
Since ozone is injected into the filtered water from which most of SS has been removed in advance, there is an effect that a small amount of ozone can be effectively treated.

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

【図1】本発明水域の浄化方法の実施例を示す説明図で
ある。
FIG. 1 is an explanatory view showing an embodiment of a method for purifying a water area of the present invention.

【図2】本発明による水域の浮遊物質濃度の経時変化を
示すグラフ図である。
FIG. 2 is a graph showing changes over time in the concentration of suspended solids in water according to the present invention.

【符号の説明】[Explanation of symbols]

P 水域 1 揚水ポンプ 2 濾過装置 3 オゾン反応槽 4 コンプレッサ 6 オゾン発生機 7 曝気撹拌機 P Water area 1 Pumping pump 2 Filtration device 3 Ozone reaction tank 4 Compressor 6 Ozone generator 7 Aeration stirrer

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 湖沼、堀、池等の水域の水を揚水し、濾
布・濾材を用いて濾過を行った後、濾過水にオゾン含有
空気を注入して濾過水に残留する植物プランクトン等の
微生物を殺菌し、オゾン処理した水を水域に戻すことに
より水域を浄化することを特徴とする水域の浄化方法。
1. A phytoplankton or the like remaining in the filtered water obtained by pumping water from water bodies such as lakes, moats, and ponds, filtering it using a filter cloth / filter material, and then injecting ozone-containing air into the filtered water. The method for purifying a water body, which comprises purifying the water body by sterilizing the microorganisms described above and returning the ozone-treated water to the water body.
JP4270867A 1992-09-14 1992-09-14 Water area cleaning method Pending JPH0691283A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4270867A JPH0691283A (en) 1992-09-14 1992-09-14 Water area cleaning method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4270867A JPH0691283A (en) 1992-09-14 1992-09-14 Water area cleaning method

Publications (1)

Publication Number Publication Date
JPH0691283A true JPH0691283A (en) 1994-04-05

Family

ID=17492079

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4270867A Pending JPH0691283A (en) 1992-09-14 1992-09-14 Water area cleaning method

Country Status (1)

Country Link
JP (1) JPH0691283A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001024604A1 (en) * 1999-10-01 2001-04-12 Universidade De Santiago De Compostela Closed and energetically integrated process (cei process for the treatment of animal wastes (purines)
WO2005077833A1 (en) * 2004-02-13 2005-08-25 Mitsubishi Heavy Industries, Ltd. Method of liquid detoxification and apparatus therefor
JP2008149215A (en) * 2006-12-14 2008-07-03 Sharp Corp Cleaning apparatus

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001024604A1 (en) * 1999-10-01 2001-04-12 Universidade De Santiago De Compostela Closed and energetically integrated process (cei process for the treatment of animal wastes (purines)
ES2160518A1 (en) * 1999-10-01 2001-11-01 Univ Santiago Compostela Closed and energetically integrated process (cei process for the treatment of animal wastes (purines)
WO2005077833A1 (en) * 2004-02-13 2005-08-25 Mitsubishi Heavy Industries, Ltd. Method of liquid detoxification and apparatus therefor
KR100814658B1 (en) * 2004-02-13 2008-03-18 미츠비시 쥬고교 가부시키가이샤 Method of liquid detoxification and apparatus therefor
CN100393632C (en) * 2004-02-13 2008-06-11 三菱重工业株式会社 Method of liquid detoxification and apparatus therefor
NO337935B1 (en) * 2004-02-13 2016-07-11 Mitsubishi Heavy Ind Ltd Process for detoxifying ballast water and apparatus for carrying out the process.
JP2008149215A (en) * 2006-12-14 2008-07-03 Sharp Corp Cleaning apparatus

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