JPS60248292A - Method and apparatus for purifying water of river and lake and seawater - Google Patents

Method and apparatus for purifying water of river and lake and seawater

Info

Publication number
JPS60248292A
JPS60248292A JP59035731A JP3573184A JPS60248292A JP S60248292 A JPS60248292 A JP S60248292A JP 59035731 A JP59035731 A JP 59035731A JP 3573184 A JP3573184 A JP 3573184A JP S60248292 A JPS60248292 A JP S60248292A
Authority
JP
Japan
Prior art keywords
water
air
pipe
lakes
lake
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
JP59035731A
Other languages
Japanese (ja)
Inventor
Yoshinori Matsuki
義則 松木
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP59035731A priority Critical patent/JPS60248292A/en
Publication of JPS60248292A publication Critical patent/JPS60248292A/en
Pending legal-status Critical Current

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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)

Abstract

PURPOSE:To reduce energy in water purification by utilizing the fluidizing force due to the density difference between water and air, and reducing the delivery pressure of air. CONSTITUTION:In water purification by aeration, the vicinity of an air ejection port is formed of a double structure, the ejection port is located at a position higher than the inflow port of water, and the fluidizing force due to the density difference between water and air is utilized. Consequently, the delivery pressure of air is decreased because the density is reduced due to the bubbles which are formed in the pipe several minutes after the supply of air is started and the necessary stress is simultaneously reduced. Accordingly, water is purified, and the energy is reduced.

Description

【発明の詳細な説明】 近年河川、湖沼(ダムを含む)海にて工場排水や生活排
水により、水質が非常に悪化し上水道原水に悪臭が発生
したり、魚介類が生息出来ない状態となっている。
[Detailed Description of the Invention] In recent years, the quality of water in rivers, lakes, marshes (including dams) and the sea due to industrial wastewater and domestic wastewater has deteriorated significantly, causing bad odors in raw water and making it impossible for fish and shellfish to live. ing.

その原因としてまず河川の場合は主に(1)工場排水に
よりBODが高くなり、停滞にほぼ近い流水量の少ない
河川などは酸素の供給が不足し酸欠状況となる。 その
時点で嫌気性バクテリアの活動によりメタンガス(CH
4)。
The reasons for this are: (1) In the case of rivers, the BOD becomes high due to industrial wastewater, and in rivers with a low flow rate that is almost stagnant, there is a lack of oxygen supply, resulting in an oxygen-deficient situation. At that point, methane gas (CH
4).

アンモニア(NH4+)、硫化水素(H2S)。Ammonia (NH4+), hydrogen sulfide (H2S).

メルカプタンなどが発生し悪臭を発生させる。Mercaptans are generated and produce a bad odor.

つまり死の川となる。In other words, it becomes a river of death.

(2)有機性(N、P等)生活排水の流入により水中の
溶存酸素を消費して、これも嫌気性状態となる。
(2) The inflow of organic (N, P, etc.) domestic wastewater consumes dissolved oxygen in the water, which also becomes anaerobic.

また、停滞した湖沼及び海域の場合は(1)河川と同じ
<N、P等の有機物を多く含む自然又は生活排水の流入
により酸欠状態を引き起し悪臭を発生するのであるが、
そこで有機物の分解にて栄養塩類が出来兄。このような
栄養分の多い状態を富栄養化現象と言う。そこで栄養塩
類が要因となりプランクトンや藻類が異状発生し、(海
の赤潮はこの時に起る。)水中の酸素消費が増大して酸
欠状態となり、水道水は悪臭化し、魚介類はへい死する
In addition, in the case of stagnant lakes and sea areas, (1) the inflow of natural or domestic wastewater containing a large amount of organic matter such as N and P, which is the same as in rivers, causes an oxygen deficiency and generates a foul odor;
Nutrient salts are produced through the decomposition of organic matter. This state of high nutrient content is called eutrophication. Nutrient salts then cause abnormal growth of plankton and algae (this is when red tide occurs in the ocean), increasing oxygen consumption in the water and creating an oxygen-deficient state, causing tap water to become foul-smelling and causing fish and shellfish to rot and die.

(2)秋から冬にかけては湖沼等の水面付近の水温は外
気の低い温度により冷却されるため。
(2) From autumn to winter, the water temperature near the water surface in lakes and marshes is cooled by the low temperature of the outside air.

湖底の暖い水温部との置換すなわち対流現象(冷却され
た密度の大きい水は沈降し、暖い密度の小さい水は一ト
昇する)を起し、湖水等の溶存酸素は均等化する。しか
し春から夏にかけては水面付近の水温が湖底等の水温よ
り高いため湖水内の置換(対流)現象が起らない。従っ
て湖水等の中〜下層部の水は酸欠状態となる。この状況
下にても嫌気性バクテリアの活動によりCH、NI−T
、+、H2S等が発生し悪臭が発生ずる。
Displacement with warmer water at the bottom of the lake, or a convection phenomenon (cooled, denser water sinks, warmer, less dense water rises), equalizes dissolved oxygen in lake water, etc. However, from spring to summer, the water temperature near the water surface is higher than the water temperature at the lake bottom, so the phenomenon of displacement (convection) within the lake water does not occur. Therefore, water in the middle to lower layers such as lake water becomes oxygen-deficient. Even under this situation, CH, NI-T due to the activity of anaerobic bacteria
, +, H2S, etc. are generated and a bad odor is generated.

以−1−の事から分かるように湖沼等の水質を悪化させ
る原因は工場排水、生活排水等にて起こる水中の酸素不
足の結果である。従って水中のDo(酸素溶存量)をな
んらかの方法で多くずれば問題解決につながって行く。
As can be seen from the following, the cause of the deterioration of water quality in lakes and marshes is the result of oxygen deficiency in water caused by industrial wastewater, domestic wastewater, etc. Therefore, if the Do (dissolved amount of oxygen) in water is increased by some method, the problem will be solved.

従来はそのDo(溶存酸素)を増加したり均等化するた
め次の方法を実施したり計画されている。
Conventionally, the following methods have been implemented or planned in order to increase or equalize the Do (dissolved oxygen).

(1)単純なエアーレーイション方法:この方法は湖沼
等の底へ等間隔にエアーの噴出]1を取付けた゛エアー
管を配列して、コンプレッサーにてエアーをエアー管を
通してエアー噴出口から中水へ放出し2強制的に水中の
Doを増加したり、エアーと水のもつ密度差による流動
エネルギーを利用して湖沼等の対流を計る方法である。
(1) Simple aeration method: In this method, air is ejected at equal intervals to the bottom of lakes, marshes, etc.] Arrange the air pipes with 1 installed, and use a compressor to pass the air through the air pipes to the gray water from the air spout. This is a method of measuring convection in lakes and marshes by forcibly increasing Do in the water by releasing air into the water, and by using flow energy due to the density difference between air and water.

しかし、この方法の場合常時エアー吐き出し口の水圧に
相当した圧力のエアーを送る必要がある。 従ってエア
ーを送るのには多大なエネルギーが必要となり不経済で
ある。
However, in this method, it is necessary to constantly send air at a pressure equivalent to the water pressure at the air outlet. Therefore, sending air requires a large amount of energy, which is uneconomical.

(2)容器へエアーを一時的に貯溜し一気に放出する方
法:この方法は湖沼等の底へ必要に応じた容器をエアー
パイプを取付は設置し次にその容器内へエアーを充填す
る。次に容器の口を一気に開放して、湖沼等の水を対流
置換しようとするものである。しかしこの方法も湖沼等
の水を完全に近い状態までに置換するのには多量のエア
ー量と圧力が必要であり非常に不経済である1、さらに
多量のエアーを一気に水の中で開放した場合は、湖沼等
の水は水面から数1− m以I−噴き七がったり、非常
に大きい爆発音と振動を発生する可能性があり2周辺に
大きな被害を与える事が考えられる。
(2) Method of temporarily storing air in a container and releasing it all at once: In this method, an appropriate container is installed at the bottom of a lake or pond, with an air pipe attached, and then air is filled into the container. Next, the mouth of the container is opened all at once to attempt to replace the water in lakes and marshes by convection. However, this method also requires a large amount of air and pressure to completely replace the water in lakes, marshes, etc., and is extremely uneconomical. In such a case, the water in lakes and marshes may spray several meters above the water surface, and there is a possibility that extremely loud explosion sounds and vibrations will be generated, causing great damage to the surrounding area.

(3)ポンプの汲み揚げによる置換方法:この方法は湖
沼等の底近くまでポンプを下げ、ポンプにて水を汲み揚
げ水面へ放流し、湖沼等内の水を置換する方法である。
(3) Replacement method by pumping: In this method, the pump is lowered to near the bottom of the lake, etc., and the water is pumped up by the pump and discharged to the water surface to replace the water in the lake, etc.

この場合数多くのポンプが必要であり、従って機材費が
莫大でポンプを作動する動力源も多大で不経済である。
In this case, a large number of pumps are required, and therefore the cost of equipment is enormous and the power source for operating the pumps is also large, making it uneconomical.

(4)機械的攪拌方法:攪拌方法には概ね2種類あり「
一つは」(1)で述べた湖沼等で放出したエアーの上昇
エネルギーをタービン(水車)に回収し、タービンを回
転させ湖沼等の水を攪拌均質化する方法である。
(4) Mechanical stirring method: There are roughly two types of stirring methods.
One is the method described in ``(1)'', in which the rising energy of air released in lakes, etc. is collected in a turbine (waterwheel), and the turbine is rotated to agitate and homogenize the water in lakes, marshes, etc.

「一つは」攪拌器をモーター等の動力にて回転し水質を
均質化する方法である。
One method is to homogenize the water quality by rotating a stirrer using the power of a motor or the like.

01f者については、放出したエネルギーを利用する事
からタービンの回転エネルギー単独に考えた場合は非常
に経済的であるが。
Regarding the 01f type, since the released energy is utilized, it is very economical when considering the rotational energy of the turbine alone.

エネルギー源のエアー送圧力にはなんの低減効果は期待
出来ない。後者については。
No effect of reducing the air supply force of the energy source can be expected. Regarding the latter.

攪拌器を回転させるエネルギーは莫大に必要であり非常
に不経済である。
The energy required to rotate the stirrer is enormous and is very uneconomical.

※ 本発明は(1)同様エアーパイソヨンによる水質浄
化方法であるがエアー噴出口付近を2重構造、または噴
出口を水の流入1−■より高い位置とし、水とエアーと
の密度差による流動力をその機構で利用するため、エア
ーの送り圧力はエアーを送り始めてから数分後にパイプ
内に出来る泡沫(空水と水の混合)により密度が低下す
るため必要圧力は小さくなる。よって本装置とその機構
は水質の浄化とエネルギー低減方法として最適装置であ
る1、 以下図面にて本発明の説明する。
*The present invention is a water purification method using air python similar to (1), but the area near the air outlet has a double structure, or the outlet is located higher than the inflow of water (1-■), and the difference in density between water and air is Because the mechanism uses fluid force, the required pressure becomes smaller because the density of the air is reduced by the foam (mixture of air and water) that forms inside the pipe several minutes after the air is started. Therefore, this device and its mechanism are optimal as a water purification and energy reduction method.1 The present invention will be explained below with reference to the drawings.

第1図は本装置設置の全体図である。第2図は本装置の
断面図で第3図は同しく本装置の立体模式図である。 
(1)はコンプレツ一部、 (2)エアーパイプ、(6
)は2重管構造の外側パイプで(4)はパイプ等を上向
へする浮子で(5)は土砂流入置市のフィルター(6)
エアーを噴出すパイプで2重管構造の内側パイプて(力
は泡沫の吐き出し口で(8)は湖沼等の底及び地盤面で
ある。(9)は湖沼等水である。
FIG. 1 is an overall diagram of the installation of this device. FIG. 2 is a sectional view of this device, and FIG. 3 is a three-dimensional schematic diagram of the same.
(1) is a complete part, (2) air pipe, (6
) is the outer pipe with a double pipe structure, (4) is the float that moves the pipe upwards, and (5) is the filter for the sediment inflow (6).
It is a pipe that blows out air, and is an inner pipe with a double pipe structure (the force is the outlet for foam, and (8) is the bottom and ground surface of lakes and marshes. (9) is water such as lakes and marshes.

まず(1)のコンプレッサーで作り圧縮されたエアーは
、(2−b)のエアーパイプを通り(6〜b)の2重管
の中に入っていた水を押し出しながら(6〜C)のエア
ー吐き出し[1まで達する。次にエアー圧力が(6〜C
)地点の水圧より高圧になった時に(6〜C)の吐き出
し口より(3〜b)の外側パイプ内に噴出る。その時点
で(3〜1〕)のパイプ内密度は低下する。(3〜b)
内の密度低下により密度の大きい(9)の湖沼等の水は
水中の密度差を均一化する力にて(5)のフィルター部
から(3〜b)のパイプ内に流入する。(5)のフィル
ターの位置は常に(6〜C)の吐き出口より低い条件が
必要である。(3〜b )へ噴出たエアーは水との密度
差及び水圧により単独に泡となり押し上げられたり、泡
沫となり上へと−上昇して(ハの噴出口から放出される
First, the air created and compressed by the compressor in (1) passes through the air pipe in (2-b), pushing out the water that was in the double pipe in (6-b), and air in (6-C). Exhale [reach 1. Next, the air pressure (6~C
) When the water pressure becomes higher than the water pressure at point (6 to C), it is ejected from the outlet at point (6 to C) into the outer pipe at point (3 to b). At that point, the density inside the pipe (3-1) decreases. (3-b)
Water from lakes and marshes (9), which has a high density due to a decrease in density within the water, flows from the filter section (5) into the pipes (3-b) with a force that equalizes the density difference in the water. The position of the filter in (5) must always be lower than the outlet in (6 to C). The air ejected to (3-b) may become bubbles independently due to the difference in density with water and water pressure and be pushed up, or it may become foam and rise upwards (emitted from the air outlet (c)).

(ハから放出された泡沫は空気との混合体であることか
ら水中のDOを増加させながら湖沼等の水を対流させD
oの均一化を進行させ、水質の浄化的役割をする。 さ
らに(5)のフィルターから流入した水も(6〜C)か
ら噴出したエアーと混合するため密度が低下する。その
ためコンプレッサーから送り出す圧力は(3〜b)のパ
イプ内圧力と同等もしくは僅か高い圧力で機能を果す。
(Since the foam released from Ha is a mixture with air, it causes convection of water in lakes and marshes while increasing DO in the water.
It promotes homogenization of water and plays a role in purifying water quality. Furthermore, since the water flowing in from the filter (5) also mixes with the air ejected from (6 to C), the density decreases. Therefore, the pressure sent out from the compressor is equivalent to or slightly higher than the pressure inside the pipe (3 to b).

以上までの本発明の特徴をまとめると、水中に鉛直方向
に設定しである両端開放のパイプ内に、エアーを送る事
によりパイプ内の密度は小さくなり2次に連続して送る
エアー圧力は小さくてすむ省エネ型水質浄化装置である
To summarize the features of the present invention as described above, by sending air into a pipe that is vertically set underwater and open at both ends, the density inside the pipe is reduced, and the pressure of the air that is continuously sent to the secondary pipe is reduced. This is an energy-saving water purification device.

手続補正書 昭和 年 月 日 1 事件の表示 昭和59年 特許願第35731号2
 発明の名称 エアーレイジョンによる河川、湖沼、海水の水質浄化方
法とその装置 3 補正をする者 事件との関係 特許出願人 4 補正命令の日付 昭和59年5月9日5 補正の対
象 HB 鋼+1 jt 17′N)J B日ノ詳WII 
yA−君d 1111 n m k−) rに]ヅ面6
 補正の内容 1、明細書第1頁第8行目と第9行目の間に13、発明
の詳細な説明」を挿入する。
Procedural amendment document Showa year, month, day 1 Indication of case 1982 Patent Application No. 35731 2
Name of the invention Method and device for purifying the quality of rivers, lakes, and seawater by air rays 3 Relationship with the case of the person making the amendment Patent applicant 4 Date of amendment order May 9, 1980 5 Target of amendment HB Steel + 1 jt 17'N) J B Hino detailed WII
yA-kun d 1111 nm k-) r]ㅅ面6
Contents of amendment 1: Insert 13, Detailed description of the invention, between lines 8 and 9 on page 1 of the specification.

2、明細書箱8頁15行目の後に14、図面の簡単な説
明」と以下の文を加入する。
2. On page 8 of the specification box, after line 15, add the following sentence: 14. "Brief explanation of the drawings."

前記l、2を補正して、書面を別紙の通り添付する。Amend items 1 and 2 above and attach the documents as attached.

の簡単な説明の欄 [発明の詳細な説明の記載もれを」「発明の詳細な説明
」と記載して補正する。
[Omissions in the detailed description of the invention] should be amended by writing ``Detailed description of the invention'' in the brief description column.

「図面の簡単な説明した正確に記載した書面が不備であ
ったので」記載したものを「図面の簡単な説明」で補正
する。
``Because the document that accurately described the drawing was incomplete,'' the statement was amended with a ``brief explanation of the drawing.''

3、発明の詳細な説明 4、図面の簡単な説明 第1図は全体の機構模式図 第2図は本装置の断面図 第3図は本装置の立体模式図 (1) コンプレッサー (2) エアーパイプ (3)2重管構造の外側パイプ (4)パイプ等を上向へする浮子 (5)土砂流入防止用のフィルター (6) エアーを噴出するパイプで2重管構造の内側パ
イプ (7)泡沫の吐き出し口 (8)湖沼等の底及び地盤面
3. Detailed description of the invention 4. Brief description of the drawings Figure 1 is a schematic diagram of the overall mechanism Figure 2 is a sectional view of this device Figure 3 is a three-dimensional schematic diagram of this device (1) Compressor (2) Air Pipe (3) Outer pipe with double pipe structure (4) Float to move the pipe upwards (5) Filter to prevent the inflow of earth and sand (6) Inner pipe with double pipe structure that blows out air (7) Foam outlet (8) Bottom and ground surface of lakes, marshes, etc.

Claims (1)

【特許請求の範囲】[Claims] 水質浄化に伴つエアーレーイションのエアー圧力を水と
エアーとの密度差を利用して低減する装置と機構
Device and mechanism that reduces the air pressure of aeration during water purification by using the density difference between water and air
JP59035731A 1984-02-27 1984-02-27 Method and apparatus for purifying water of river and lake and seawater Pending JPS60248292A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59035731A JPS60248292A (en) 1984-02-27 1984-02-27 Method and apparatus for purifying water of river and lake and seawater

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59035731A JPS60248292A (en) 1984-02-27 1984-02-27 Method and apparatus for purifying water of river and lake and seawater

Publications (1)

Publication Number Publication Date
JPS60248292A true JPS60248292A (en) 1985-12-07

Family

ID=12449978

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59035731A Pending JPS60248292A (en) 1984-02-27 1984-02-27 Method and apparatus for purifying water of river and lake and seawater

Country Status (1)

Country Link
JP (1) JPS60248292A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH07222995A (en) * 1994-02-14 1995-08-22 Aqua Tec Kk Aeration facility for river

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH07222995A (en) * 1994-02-14 1995-08-22 Aqua Tec Kk Aeration facility for river

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