JPH07222995A - Aeration facility for river - Google Patents
Aeration facility for riverInfo
- Publication number
- JPH07222995A JPH07222995A JP3907794A JP3907794A JPH07222995A JP H07222995 A JPH07222995 A JP H07222995A JP 3907794 A JP3907794 A JP 3907794A JP 3907794 A JP3907794 A JP 3907794A JP H07222995 A JPH07222995 A JP H07222995A
- Authority
- JP
- Japan
- Prior art keywords
- river
- air
- aeration
- water
- holes
- 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.)
- Granted
Links
- 238000005273 aeration Methods 0.000 title claims abstract description 34
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 29
- 238000009792 diffusion process Methods 0.000 abstract description 5
- 230000002093 peripheral effect Effects 0.000 description 9
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 4
- 229910052760 oxygen Inorganic materials 0.000 description 4
- 239000001301 oxygen Substances 0.000 description 4
- 238000004140 cleaning Methods 0.000 description 3
- 238000000746 purification Methods 0.000 description 3
- 230000000630 rising effect Effects 0.000 description 3
- 230000006866 deterioration Effects 0.000 description 2
- BZHJMEDXRYGGRV-UHFFFAOYSA-N Vinyl chloride Chemical compound ClC=C BZHJMEDXRYGGRV-UHFFFAOYSA-N 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000000470 constituent Substances 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 239000010840 domestic wastewater Substances 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000003911 water pollution Methods 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
- Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は、河川を流れる水に溶存
酸素(DO)を供給することによって浄化作用を促す河
川の曝気施設に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an aeration facility for a river, which promotes a purification action by supplying dissolved oxygen (DO) to water flowing in the river.
【0002】[0002]
【従来の技術】産業の発達や生活様式の変化にともな
い、多くの河川、湖沼、貯水池などの水系域水質汚濁が
問題になっている。本来、自浄作用により浄化されてい
た河川域、特に、都市周辺域の河川では産業及び生活廃
水の流入が増大し、自浄能力以上の汚濁物質が流入する
ため、COD(化学的酸素要求量)及びBOD(生物化
学的酸素要求量)の自浄作用が不足し、水質悪化が問題
視されている。このような状況下において、近年、汚濁
された河川水の浄化を図るために各種の浄化措置が採ら
れている。図6は、曝気により河川の浄化を図る従来の
曝気施設を示す正面図である。本図に示した曝気施設
は、河川の底部へ幅方向に散気管10を配設し、空気供
給源11から送られてきた空気を、この散気管10から
河川水中に放出して、河川水の曝気を行なうものであ
る。このため、散気管10には、縦軸方向に10〜10
0cmの間隔をおいて散気孔12(ディフューザのことも
ある)が一列に設けてある。2. Description of the Related Art Along with the development of industry and changes in lifestyle, water pollution of many rivers, lakes and reservoirs has become a problem. Originally, rivers that had been purified by self-cleaning action, especially in rivers around urban areas, increased inflow of industrial and domestic wastewater, and pollutants in excess of the self-cleaning ability flow in, so COD (chemical oxygen demand) and The self-cleaning action of BOD (biochemical oxygen demand) is insufficient, and deterioration of water quality is a problem. Under such circumstances, in recent years, various purification measures have been taken to purify polluted river water. FIG. 6 is a front view showing a conventional aeration facility for purifying a river by aeration. In the aeration facility shown in this figure, the diffuser pipe 10 is arranged in the width direction to the bottom of the river, and the air sent from the air supply source 11 is discharged from the diffuser pipe 10 into the river water to generate the river water. Aeration. Therefore, the air diffuser 10 has 10 to 10 in the longitudinal direction.
Air diffuser holes 12 (which may be a diffuser) are provided in a line at intervals of 0 cm.
【0003】[0003]
【発明が解決しようとする課題】通常、都市周辺域の河
川では、川岸に護岸ブロックを斜めに敷きつめて堤1が
構築されており、この堤1のために、河川の横幅は下方
に行くにしたがい狭くなり、川底にあって最も狭くなっ
ている。したがって、川底の全幅にわたり散気管10を
配設しても、河川の両脇部分Aは散気管10から放出さ
れる気泡の浮上範囲から外れることとなり、曝気されな
いままの水がこの両脇部分Aから通過してしまう。ま
た、従来の曝気施設に用いられていた散気管10には、
散気孔12を縦軸方向に一列のみ設けているに過ぎなか
ったので、これらの散気孔12から放出される各気泡帯
13相互の隙間Bが大きく、この隙間Bを曝気されない
まま多量の水が通過していた。以上のように、従来の曝
気施設では曝気効率が悪く、故に十分な曝気を行なうた
めには、散気量を増加するかあるいは河川流域に何本も
の散気管を配設しなければならず、運転または設備にコ
ストがかかるという課題を有していた。本発明はこのよ
うな課題を解決するためになされたもので、効率的に河
川の曝気ができ、経済的な河川の曝気施設を提供するこ
とを目的とする。Generally, in rivers around the city, a bank 1 is constructed by diagonally laying revetment blocks on the riverbank, and because of this bank 1, the lateral width of the river goes downward. Therefore, it becomes narrower and the narrowest at the bottom of the river. Therefore, even if the air diffuser 10 is arranged over the entire width of the river bottom, the portions A on both sides of the river will be out of the floating range of the bubbles discharged from the air diffuser 10, and the water that has not been aerated will remain on both sides A. Will pass through. In addition, in the air diffuser 10 used in the conventional aeration facility,
Since the air diffuser holes 12 were provided only in one row in the vertical axis direction, the gap B between the bubble bands 13 discharged from the air diffuser holes 12 was large, and a large amount of water was left in the gap B without being aerated. Was passing. As described above, in the conventional aeration facility, the aeration efficiency is poor, and therefore, in order to perform sufficient aeration, it is necessary to increase the aeration amount or arrange a number of air diffusers in the river basin. There was a problem that operation or equipment costly. The present invention has been made to solve such a problem, and an object of the present invention is to provide an economical aeration facility for a river that can efficiently aerate the river.
【0004】[0004]
【課題を解決するための手段】上記目的を達成するため
に、本発明の曝気施設は、河川の堤を一部切り欠いて川
底の横幅を拡大し、かつ周壁の全周または部分的周面に
多数の散気孔を備えた散気管を前記川底の全幅にわたり
配設するとともに、前記散気管を空気供給源と接続した
ことを特徴としている。In order to achieve the above-mentioned object, the aeration facility of the present invention has a structure in which a part of a river bank is cut out to expand the lateral width of the river bottom, and the entire or partial circumference of the peripheral wall. Further, an air diffusing tube having a large number of air diffusing holes is arranged over the entire width of the river bottom, and the air diffusing tube is connected to an air supply source.
【0005】[0005]
【作用】本発明は上記のように、河川の堤を一部切り欠
いて川底の横幅を拡大し、該川底の全幅にわたり散気管
を配設したので、河川の両脇部分にも散気管から放出さ
れた空気が行きわたり、効率的に曝気を行なうことが可
能となる。しかも、散気管の全周面または部分的周面に
多数の散気孔を備えているので、これらの散気孔から放
出された気泡の帯の隙間が小さく、流下してきた河川水
をもれなく曝気し得、一層効率的な曝気を実現できる。
なお、本発明の適用対象となる河川には、自然河川のみ
ならず、人工的に形成された水路をも含んでいる。As described above, according to the present invention, since the lateral width of the river bottom is enlarged by cutting out a part of the river bank and the air diffuser is arranged over the entire width of the river bottom, the diffusing pipes are provided on both sides of the river. It is possible to spread the released air and efficiently perform aeration. Moreover, since a large number of diffuser holes are provided on the entire or partial peripheral surface of the diffuser pipe, the gap of the band of bubbles discharged from these diffuser holes is small, and it is possible to aerate the flowing river water without fail. , More efficient aeration can be realized.
The rivers to which the present invention is applied include not only natural rivers but also artificially formed water channels.
【0006】[0006]
【実施例】以下、本発明の一実施例について図面を参照
して詳細に説明する。図1は、本発明の一実施例に係る
河川の曝気施設を示す正面断面図、図2は、同施設の外
観を示す斜視図である。本実施例では、河川両岸の堤
1、1において、それぞれ対向する位置に切欠き2、2
を設けている。これらの切欠き2、2は、堤1、1の傾
斜面を水面との境界線1aより外側の位置まで切除して
なり、切欠き側面1bは川底に対し鉛直面となってい
る。その結果、切欠き形成部分の川幅は、川底から水面
にかけて等しくなる。DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described in detail below with reference to the drawings. FIG. 1 is a front sectional view showing an aeration facility for a river according to an embodiment of the present invention, and FIG. 2 is a perspective view showing the appearance of the facility. In this embodiment, the notches 2 and 2 are provided at the opposite positions on the banks 1 and 1 on both banks of the river.
Is provided. These notches 2 and 2 are formed by cutting the inclined surface of the bank 1 to a position outside the boundary line 1a with the water surface, and the notch side surface 1b is a vertical plane with respect to the riverbed. As a result, the river width at the notch formation becomes equal from the river bottom to the water surface.
【0007】各切欠き2、2間の川底には、散気管3が
全幅にわたって配設されている。散気管3の先端は閉塞
端となっており、基端側が配管4を介して空気供給源5
と接続されている。空気供給源5としては電動式の圧送
ポンプ等、河川曝気に必要な空気量を散気管3の中空部
全体に供給できるものであればよい。この空気供給源5
は、通常、散気管3の配設箇所近くの河川敷に設置され
る。また、散気管3と配管4との接続部には、空気の供
給停止中に、後述する散気孔7から散気管3内に流入し
てきた水が配管4側へ流入することを阻止するために、
逆止弁6を設けてもよい。An air diffuser 3 is provided over the entire width at the river bottom between the notches 2 and 2. The tip of the air diffuser 3 is a closed end, and the base end side is connected to the air supply source 5 via the pipe 4.
Connected with. The air supply source 5 may be an electric pressure pump or the like as long as it can supply the air amount necessary for river aeration to the entire hollow portion of the air diffuser 3. This air source 5
Is usually installed on the riverbed near the location of the diffuser pipe 3. In addition, in order to prevent the water flowing into the diffuser pipe 3 from the diffuser hole 7 described later from flowing into the pipe 4 side at the connecting portion between the diffuser pipe 3 and the pipe 4 while the air supply is stopped. ,
The check valve 6 may be provided.
【0008】散気管3の周壁には、図3及び図4に示す
ごとく多数の散気孔7が穿設されている。これらの散気
孔7は、周壁の全周面にわたって形成してもよく、また
周壁の部分的周面、例えば上部半周面のみに穿設しても
よい。ここで、散気孔7の形状や配置等穿設形態は任意
でよく、少なくとも散気管3の周方向に分散して穿設さ
れていればよく、特に制限されることはない。好ましく
は、散気管3より上昇する気泡が平面を形成するごとく
なり、気泡が上昇しない水空間がないようにするのがよ
い。例えば、図に示す実施例では、縦軸方向に任意、で
きるだけ狭い間隔で散気孔7を穿設したもので、縦軸方
向に連なり各列8を形成する各散気孔7は、上下列で互
いに穿設箇所を同方向に僅かずつずらして穿設され、散
気管周面を縦軸方向にらせん状に細かいピッチで散気孔
7が形成されるように底部を除き穿設したものである。
このように形成することにより、各散気孔7から排出さ
れ水面へと上昇する気泡の帯間隔を一層狭小に、例えば
5mm間隔程度にすることができ、気泡が流通水を面状
に横切るように水中を上昇するため、曝気されないまま
水が通過することをなくすことができる。散気管3の横
断面形状は、多角形、円形等任意に選択することができ
る。また、散気管3の相当直径も任意であり、空気を流
通させることができ、かつ後述するごとく穿設される散
気孔7を通して空気を噴出できるものであればよい。散
気管3の材質も特に制限されるものでなく、被浄化河川
水中において、腐食等劣化せずに長期間形態等を保持で
きるものであればよい。一般には、塩化ビニル製管体を
用いることができる。A large number of air diffusion holes 7 are formed in the peripheral wall of the air diffusion pipe 3 as shown in FIGS. These air diffusing holes 7 may be formed over the entire peripheral surface of the peripheral wall, or may be formed only on a partial peripheral surface of the peripheral wall, for example, the upper half peripheral surface. Here, the shape and arrangement of the air diffuser holes 7 may be arbitrary, as long as they are distributed and provided at least in the circumferential direction of the air diffuser pipe 3, and are not particularly limited. It is preferable that the bubbles rising from the air diffuser 3 form a flat surface so that there is no water space in which the bubbles do not rise. For example, in the embodiment shown in the drawing, the air diffuser holes 7 are bored in the vertical axis direction at an arbitrary and as narrow interval as possible, and the air diffuser holes 7 that are continuous in the vertical axis direction and form each row 8 are arranged in the upper and lower rows. The perforated portions are perforated by slightly shifting in the same direction, and the peripheral surface of the air diffuser is bored except for the bottom so that the air diffuser holes 7 are spirally formed in a fine pitch in the vertical axis direction.
By forming in this way, the band interval of the bubbles discharged from each air diffuser 7 and rising to the water surface can be made narrower, for example, about 5 mm, so that the bubbles cross the circulating water in a plane shape. Since it rises in the water, it is possible to prevent water from passing through without being aerated. The cross-sectional shape of the air diffuser 3 can be arbitrarily selected such as polygonal or circular. Further, the equivalent diameter of the air diffusing tube 3 is also arbitrary, and it is sufficient that air can be circulated and air can be ejected through the air diffusing holes 7 that are formed as described later. The material of the air diffuser 3 is not particularly limited as long as it can maintain its shape in the river water to be purified without deterioration such as corrosion for a long time. Generally, a vinyl chloride tube can be used.
【0009】本発明は、上記のように構成されているた
め、空気供給源5から散気管3の中空部内に送られてき
た空気を、散気孔7を通して河川水中に放出する。散気
孔7から放出された空気は、図5に示すように連続的な
気泡の帯9を形成し、且つ、従来法で生じていた各気泡
帯間の間隙13が殆どないような形態、即ち、気泡平面
を形成して水面に向い上昇して行く。各散気孔7から放
出された空気は、一部が河川水に溶け込み、その溶存酸
素量を増加させる。これにより河川水の曝気浄化が実現
される。本実施例では、河川の堤1、1に形成した切欠
き2、2によって、河川の横幅が川底から水面にかけて
等しくなっているので、川底の全幅に配設された散気管
3からの気泡の帯が、河川の幅方向に隅々まで行きわた
り、曝気効率の向上が図られる。さらに、本実施例の散
気管3は、周壁の全周面または部分的周面において、周
方向及び縦軸方向に多数の散気孔7を形成しているの
で、各散気孔7から排出される気泡の帯が面状に河川水
中で高密度に形成されるため、一層曝気効率が向上す
る。Since the present invention is configured as described above, the air sent from the air supply source 5 into the hollow portion of the air diffusing pipe 3 is discharged into the river water through the air diffusing holes 7. The air discharged from the air diffuser 7 forms a continuous band 9 of bubbles as shown in FIG. 5, and there is almost no gap 13 between the respective bubble bands generated by the conventional method, that is, , Forming a bubble plane and rising toward the water surface. Part of the air released from each air diffuser 7 dissolves in the river water, increasing the amount of dissolved oxygen. As a result, aeration purification of river water is realized. In this embodiment, since the lateral width of the river is equalized from the river bottom to the water surface by the notches 2 and 2 formed in the river bank 1, 1, the bubbles from the air diffusing pipes 3 arranged in the entire width of the river bottom are prevented. The belt extends all over the width of the river, improving the aeration efficiency. Further, in the air diffuser 3 of this embodiment, a large number of air diffusers 7 are formed in the circumferential direction and the longitudinal direction on the entire circumferential surface or a partial circumferential surface of the circumferential wall, so that the air is discharged from each of the diffused holes 7. Since the band of bubbles is formed on the surface of the river water at high density, the aeration efficiency is further improved.
【0010】なお、本発明は上述した一実施例に限定さ
れるものではなく、要旨を変更しない範囲で種々の変形
または応用が可能である。例えば、上記実施例では、河
川の横幅を川底から水面にかけて等しくするような幅の
切欠きを堤に形成したが、この切欠きによって堤の耐水
圧性能が低下し安全基準を下回る等の場合には、該安全
基準を確保しつつ可能な限り川底の幅を拡大するように
適宜切欠き幅を設定すればよい。この場合であっても、
川底の幅が拡大された分、従来より散気曝気し得る範囲
が広がり、曝気効率向上という本発明の効果は達成され
る。また、散気管から放出された気泡の帯が浮上する水
面部分には、水中及び水面に浮遊するゴミが集まり易い
ため、その部分にゴミ取り施設や凝集剤散布施設等を併
設し、曝気と併せて河川を浄化することも可能である。The present invention is not limited to the above-described embodiment, but various modifications and applications are possible within the scope of the invention. For example, in the above embodiment, the notch having a width that makes the lateral width of the river equal from the river bottom to the water surface is formed in the bank, but due to this notch, the water pressure resistance performance of the bank decreases and falls below the safety standard. The cutout width may be set as appropriate so that the width of the riverbed is expanded as much as possible while ensuring the safety standards. Even in this case,
As the width of the riverbed is expanded, the range in which aeration and aeration can be performed is wider than in the past, and the effect of the present invention that the aeration efficiency is improved is achieved. In addition, since dust that floats in the water and on the water surface tends to collect on the surface of the water where the band of bubbles discharged from the air diffuser floats up, a garbage collection facility, a flocculant spraying facility, etc., will be installed along with the aeration. It is also possible to purify rivers.
【0011】[0011]
【発明の効果】以上説明したように、本発明の河川曝気
施設によれば、従来施設では不十分であった河川両脇部
分でも十分な曝気を行え、しかも散気管から放出される
各気泡の帯を狭小間隔で形成できるので、従来に比べ少
ない散気量で効率的に河川の曝気ができ、運転及び設備
コスト面において経済的である。As described above, according to the river aeration facility of the present invention, sufficient aeration can be performed even on both sides of the river, which was not sufficient in the conventional facility, and each bubble emitted from the diffuser pipe is Since the bands can be formed at narrow intervals, the aeration of the river can be efficiently performed with a smaller amount of air diffusion than in the conventional case, which is economical in terms of operation and equipment costs.
【図1】本発明の一実施例に係る河川の曝気施設を示す
正面断面図である。FIG. 1 is a front sectional view showing an aeration facility for a river according to an embodiment of the present invention.
【図2】同施設の外観を示す斜視図である。FIG. 2 is a perspective view showing an appearance of the facility.
【図3】同施設の構成部材である散気管の一部を拡大し
て示す正面図である。FIG. 3 is an enlarged front view showing a part of an air diffuser which is a constituent member of the facility.
【図4】同じく側面断面図である。FIG. 4 is a side sectional view of the same.
【図5】同施設による河川の曝気状況を示す側面断面図
である。FIG. 5 is a side sectional view showing an aeration situation of a river by the facility.
【図6】従来の河川曝気施設を示す正面断面図である。FIG. 6 is a front cross-sectional view showing a conventional river aeration facility.
1 堤 2 切欠き 3 散気管 5 空気供給源 7 散気孔 1 Levee 2 Notch 3 Air diffuser 5 Air supply source 7 Air diffuser
Claims (1)
大し、かつ周壁の全周または部分的周面に多数の散気孔
を備えた散気管を前記川底の全幅にわたり配設するとと
もに、前記散気管を空気供給源と接続したことを特徴と
する河川の曝気施設。1. A river bank is partially cut away to increase the lateral width of the river bottom, and an air diffuser having a large number of air diffuser holes is provided on the entire circumference or partial circumference of the surrounding wall over the entire width of the river bottom. Also, an aeration facility for a river, characterized in that the air diffuser is connected to an air supply source.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3907794A JP2720287B2 (en) | 1994-02-14 | 1994-02-14 | River aeration facilities |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3907794A JP2720287B2 (en) | 1994-02-14 | 1994-02-14 | River aeration facilities |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH07222995A true JPH07222995A (en) | 1995-08-22 |
| JP2720287B2 JP2720287B2 (en) | 1998-03-04 |
Family
ID=12543054
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP3907794A Expired - Lifetime JP2720287B2 (en) | 1994-02-14 | 1994-02-14 | River aeration facilities |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2720287B2 (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2008545522A (en) * | 2005-05-16 | 2008-12-18 | リー,バ−ドゥ | Small river water purification system |
| JP2015085314A (en) * | 2013-09-26 | 2015-05-07 | 三菱レイヨン株式会社 | Air diffusion device and water treatment apparatus |
| CN108609771A (en) * | 2018-05-08 | 2018-10-02 | 福建省蓝深环保技术股份有限公司 | A kind of river regulation system |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS4846143A (en) * | 1971-10-15 | 1973-07-02 | ||
| JPS49108634U (en) * | 1973-01-11 | 1974-09-17 | ||
| JPS60248292A (en) * | 1984-02-27 | 1985-12-07 | Yoshinori Matsuki | Method and apparatus for purifying water of river and lake and seawater |
| JPS63229133A (en) * | 1986-10-02 | 1988-09-26 | Ube Ind Ltd | Gas-liquid contacting device |
-
1994
- 1994-02-14 JP JP3907794A patent/JP2720287B2/en not_active Expired - Lifetime
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS4846143A (en) * | 1971-10-15 | 1973-07-02 | ||
| JPS49108634U (en) * | 1973-01-11 | 1974-09-17 | ||
| JPS60248292A (en) * | 1984-02-27 | 1985-12-07 | Yoshinori Matsuki | Method and apparatus for purifying water of river and lake and seawater |
| JPS63229133A (en) * | 1986-10-02 | 1988-09-26 | Ube Ind Ltd | Gas-liquid contacting device |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2008545522A (en) * | 2005-05-16 | 2008-12-18 | リー,バ−ドゥ | Small river water purification system |
| JP2015085314A (en) * | 2013-09-26 | 2015-05-07 | 三菱レイヨン株式会社 | Air diffusion device and water treatment apparatus |
| CN108609771A (en) * | 2018-05-08 | 2018-10-02 | 福建省蓝深环保技术股份有限公司 | A kind of river regulation system |
Also Published As
| Publication number | Publication date |
|---|---|
| JP2720287B2 (en) | 1998-03-04 |
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