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JPH0753750Y2 - Floating separation type purification device - Google Patents

Floating separation type purification device

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Publication number
JPH0753750Y2
JPH0753750Y2 JP40640190U JP40640190U JPH0753750Y2 JP H0753750 Y2 JPH0753750 Y2 JP H0753750Y2 JP 40640190 U JP40640190 U JP 40640190U JP 40640190 U JP40640190 U JP 40640190U JP H0753750 Y2 JPH0753750 Y2 JP H0753750Y2
Authority
JP
Japan
Prior art keywords
water
separation type
purification device
overflow port
type purification
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.)
Expired - Lifetime
Application number
JP40640190U
Other languages
Japanese (ja)
Other versions
JPH0487791U (en
Inventor
清之 北野
稔 生田
寛 有馬
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.)
Komatsu Ltd
Original Assignee
Komatsu 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 Komatsu Ltd filed Critical Komatsu Ltd
Priority to JP40640190U priority Critical patent/JPH0753750Y2/en
Publication of JPH0487791U publication Critical patent/JPH0487791U/ja
Application granted granted Critical
Publication of JPH0753750Y2 publication Critical patent/JPH0753750Y2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Description

【考案の詳細な説明】[Detailed description of the device]

【産業上の利用分野】本考案は、汚濁物分離を高効率で
行える浮上分離式浄化装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a flotation separation type purification device capable of separating pollutants with high efficiency.

【従来の技術】浮上分離式浄化装置は、原水に気泡を混
入させることにより、気泡の表面に汚濁物を付着させる
か、また微細気泡が汚濁物に付着して該汚濁物を浮上さ
せ、浮上汚濁物(以下、汚濁泡とする)を水から分離し
て外部に排出する浄化装置であり、これには各種形式が
ある(例えば、特開昭55年−49185号、実開昭6
0年63491号)。汚濁物が浮上して一旦集まる汚濁
物分離部での分離方法には強制分離式と自然分離式とが
ある。前者強制分離式は後者自然分離式の構成におい
て、掻き取り機等をその汚濁物分離部付近に備え、汚濁
泡を掻き取り、外部への排出を支援するものである。そ
こで後者自然分離式についての具体的構成を、第6図
(同図(a)は同図(b)の上視図)を参照して説明す
る。浮上分離式浄化装置は、本体31と、本体内上部に
設けられた汚濁物分離部32と、本体内下部に設けられ
た原水流入口33、散気部34(尚、図示しないが、原
水流入配管の内部に設置される空気供給装置もある)及
び処理水出口35と、この処理水出口35に取り付けら
れて水位調整部361を備えた水位調整堰36と(本例
では、上部に螺状係合された筒361を上下動すること
により、水位を調整している)、この水位調整堰36か
ら溢れ出た処理水を次段へ導く還流管37と、さらに汚
濁物分離部32で分離された汚濁泡Dを外部へ排出する
排出管38とから大略構成される。
2. Description of the Related Art A floating separation type purifying apparatus deposits bubbles on the surface of bubbles by mixing bubbles into the raw water, or fine bubbles attach to the contaminants to levitate the contaminants and float them. This is a purifying device that separates pollutants (hereinafter referred to as polluted bubbles) from water and discharges them to the outside, and there are various types (for example, JP-A-55-49185 and JP-A-6-1956).
Year 0, 63491). There are a forced separation type and a natural separation type as a separation method in the contaminant separation section where the contaminants float and gather once. In the former forced separation type, in the latter natural separation type configuration, a scraping machine or the like is provided in the vicinity of the pollutant separation section to scrape polluted bubbles and support discharge to the outside. Therefore, a specific configuration of the latter natural separation type will be described with reference to FIG. 6 (FIG. 6A is a top view of FIG. The levitation separation type purification device includes a main body 31, a contaminant separating section 32 provided in an upper part of the main body, a raw water inlet 33 and an aeration section 34 provided in a lower part of the main body (not shown, but raw water inflow). There is also an air supply device installed inside the pipe) and the treated water outlet 35, and a water level adjusting weir 36 attached to the treated water outlet 35 and provided with a water level adjusting portion 361 (in this example, a screw-shaped upper portion). The water level is adjusted by moving the engaged cylinder 361 up and down), and the treated water overflowing from the water level adjusting weir 36 is separated into the reflux pipe 37 and the contaminant separating unit 32. A discharge pipe 38 for discharging the polluted foam D thus formed is generally configured.

【考案が解決しようとする課題】ところで、上記従来の
自然分離式の浮上分離式浄化装置では汚濁泡Dを水から
効率的に分離できないのが現実である。汚濁泡Dを水か
ら効率よく分離して排出するには、本体31の水位を高
精度に(好ましくは2mm以内)制御する必要がある。
仮にこの制御が不完全であり、水位が低いと、汚濁物D
は排出されず、再溶解して処理水と共に還流管37から
還流される。逆に水位が高いと、汚濁物Dだけでなく清
浄な水までも排出管38から外部へ排出されてしまい、
頻繁な水の補給を余儀なくされる。上例構成(第6図)
での制御は水位調整堰36の筒361を上げ下げするこ
とによって行うが、かかる水位制御が必要となる水位の
変動原因は電圧等の変動によるポンプ20の流量の変
動、散気部34への空気供給量の変動、及び、第7図に
示すように、気泡による水位の持ち上げ等がある。かか
る不定変動要因に対して常時手作業で水位を制御すると
いうことは事実上不可能である。もっとも、浮上分離式
浄化装置を用い、排出物に多量の水が含まれていてもよ
い場合には当然にこのことは問題とならない。しかしな
がら、例えば魚介類を水槽で飼育し、養殖し又は生かし
たままで保存するような場合は、原水を濾過装置で濾過
して水槽へ還流させるような循環式(即ち、再利用式)
の浄化装置を用いる必要がある。ところがこの場合、濾
過装置の占める場積が大きくなることから、この場積を
半分以下程度にできる有効手段として、浮上分離式浄化
装置がある。これは、第5図に示すように、水槽10か
らポンプ20で吸引した原水を浮上分離式浄化装置30
で汚濁物Dと水とに強制分離し、汚濁物Dは外部へ排出
し、他方水はさらに濾過装置40で濾過して水槽10へ
還流させるものである。しかるに、上述のとおり、従来
の自然分離式の浮上分離式浄化装置では、浄化と共に水
までも排出され、減水するか、又は全く要を成さず汚濁
物が総て濾過装置40に至ってしまうことになる。これ
では、魚貝類の健康維持を図る上で、また経済上、由々
しき問題となる。殊に、魚介類の水槽の例では、その原
水は、汚濁物分離部32で広がる汚濁泡Dの粘性が高
く、このため、自然分離式はほぼ不可能である。そこで
かかる場合は、掻き取り機による強制分離式を行うこと
になる。しかるにこの強制分離式にしても、掻き取り機
の動力制御や保守等の手数の増加、泡掻き取り機自体に
発する水面の揺れによる掻き取り残し等の新たな問題が
生じている。本考案は、上記従来技術の問題点に着目
し、自然分離式であっても、高効率で汚濁物を分離し、
かつ、排出できる浮上分離式浄化装置を提供することを
目的とする。
By the way, it is a reality that the above-mentioned conventional natural separation type floating separation type purification device cannot efficiently separate the polluted foam D from water. In order to efficiently separate and discharge the polluted foam D from water, it is necessary to control the water level of the main body 31 with high accuracy (preferably within 2 mm).
If this control is incomplete and the water level is low, contaminant D
Is not discharged, but is redissolved and refluxed from the reflux pipe 37 together with the treated water. On the contrary, if the water level is high, not only the pollutant D but also clean water will be discharged from the discharge pipe 38 to the outside,
I am forced to replenish water frequently. Example configuration (Fig. 6)
Control is performed by raising and lowering the cylinder 361 of the water level adjusting weir 36. However, the cause of the water level change that requires such water level control is the change in the flow rate of the pump 20 due to the change in voltage or the like, and the air to the air diffuser 34. There are fluctuations in the supply amount, and as shown in FIG. 7, there is a rise in the water level due to bubbles. It is virtually impossible to always manually control the water level against such indefinite fluctuation factors. Of course, this does not cause a problem when the floating separation type purification device is used and the discharge may contain a large amount of water. However, for example, when seafood is raised in an aquarium, cultivated, or stored as it is kept alive, a circulation system (that is, a reusable system) in which raw water is filtered by a filtration device and returned to the aquarium
It is necessary to use the purification device of. However, in this case, since the field area occupied by the filtration apparatus becomes large, a flotation separation type purification apparatus is an effective means for reducing the field area to about half or less. As shown in FIG. 5, the raw water sucked by the pump 20 from the water tank 10 is floated and separated by the purification device 30.
In this case, the contaminant D is forcibly separated into water and the contaminant D is discharged to the outside, while the water is further filtered by the filter device 40 and returned to the water tank 10. However, as described above, in the conventional floating separation type purification apparatus of the natural separation type, even the water is discharged together with the purification, and the water is reduced or all the contaminants reach the filtering apparatus 40 without any need. become. This poses a serious problem in maintaining the health of fish and shellfish and in economic terms. In particular, in the case of an aquarium of seafood, the raw water has a high viscosity of the pollutant bubbles D spreading in the pollutant separation section 32, so that the natural separation method is almost impossible. Therefore, in such a case, a forced separation type using a scraping machine is used. However, even with this forced separation type, there are new problems such as an increase in the number of steps for power control and maintenance of the scraping machine, and an unscraped surface due to the shaking of the water surface generated by the foam scraping machine itself. The present invention focuses on the above-mentioned problems of the prior art, and even if it is a natural separation type, it separates pollutants with high efficiency,
Moreover, it aims at providing the floating separation type | formula purification apparatus which can be discharged | emitted.

【課題を解決するための手段】上記目的を達成するた
め、本発明に係わる浮上分離式浄化装置は、第1図を参
照して説明すれば、浮上分離式浄化装置の汚濁物分離部
32において、該浮上分離式浄化装置の還流管37に合
流するオーバフロー口41を設け、このオーバフロー口
41の上方には、汚濁泡Dが該オーバフロー口41に流
入することを防ぐと共に該汚濁泡Dが排出側へ乗り越す
排出カバー42を設け、さらにこのオーバフロー口41
の下方には、下方からの上昇水流が該オーバフロー口4
1に直接流入することを防ぐ邪魔板43を備える構成と
した。
In order to achieve the above object, the flotation separation type purification apparatus according to the present invention will be described with reference to FIG. 1 in the contaminant separation section 32 of the flotation type purification apparatus. An overflow port 41 that joins the reflux pipe 37 of the floating separation type purification device is provided, and above the overflow port 41, the contamination bubble D is prevented from flowing into the overflow port 41 and the contamination bubble D is discharged. A discharge cover 42 that rides over to the side is provided.
The upward flow of water from the lower side of the overflow port 4
The baffle plate 43 for preventing the direct inflow to the No. 1 is provided.

【作用】本来、上記構成のように、汚濁物分離部32か
ら処理水を得るという発想はこの種の装置において常識
外とされていたものである。即ち上記構成によれば、第
3図に示すように、原水は上昇流となって汚濁物分離部
32に至る。このとき、オーバフロー口41の下方には
邪魔板43があるため、オーバフロー口41に直接流入
することがなくなる。汚濁物分離部32における汚濁水
は上部は汚濁泡Dとなり、下部は水となっている。この
ような下部の水に前記オーバフロー口41を水没し、前
記水の一部がオーバフロー水ωとなる。このオーバフロ
ー水ωの量は概ね水位調整堰36によって決定される
が、前述のとおり、不定の各種水位変動要因によって変
動する。排出カバー42は汚濁泡Dがオーバフロー口4
1に流入しようにするのを阻止する邪魔板の役目も果た
しているので、オーバフロー水ωは汚濁物分離部32か
らの水ではあるが、顕著な汚れはない。またその量も少
なく、還流管37の処理水と合流した時点で希釈され
る。他方汚濁泡Dは、下方からの上昇水流に押され、か
つ、オーバフロー水流に乗せられて排出カバー42の上
面を乗り越すようになり、排出管38から外部へ排出さ
れる。
Originally, the idea of obtaining treated water from the pollutant separation section 32 as in the above-mentioned configuration was not common knowledge in this type of apparatus. That is, according to the above-mentioned structure, as shown in FIG. 3, the raw water reaches the pollutant separation part 32 as an upward flow. At this time, since there is the baffle plate 43 below the overflow port 41, it does not flow directly into the overflow port 41. The upper part of the polluted water in the pollutant separation unit 32 is the polluted foam D, and the lower part is water. The overflow port 41 is submerged in such lower water, and a part of the water becomes overflow water ω. The amount of the overflow water ω is generally determined by the water level adjusting weir 36, but as described above, it varies due to various factors of varying water level. In the discharge cover 42, the contaminated foam D overflows the outlet 4
Since the overflow water ω is water from the pollutant separation section 32, it also has no remarkable dirt because it also serves as a baffle that prevents the water from flowing into the water 1. Further, the amount thereof is small, and when it joins the treated water in the reflux pipe 37, it is diluted. On the other hand, the polluted foam D is pushed by the rising water flow from below and is also carried on the overflow water flow to ride over the upper surface of the discharge cover 42 and is discharged to the outside from the discharge pipe 38.

【実施例】以下実施例は図面を参照して説明する。第1
実施例は、第1図(同図(a)は同図(b)の上視図)
及び第1図の部分拡大図である第2図に示すとおり、自
然分離式である浮上分離式浄化装置30の汚濁物分離部
32は、従来技術における汚濁物分離部32の水位決定
堰412と共に、水位決定堰411を備えている。この
水位決定堰411は水位決定堰412よりも低く備えら
れている。そしてこの水位決定堰411の液側下方に邪
魔板43を備え、さらに液側反対側に該水位決定堰41
1からのオーバフロー水ωを該浮上分離式浄化装置30
本来の還流管37へ合流させる副還流管44を備えてい
る。さらにこの水位決定堰411の上方に汚濁泡Dが乗
り越す排出カバー42を備えている。この排出カバー4
2の液側端は邪魔板43の液側端よりも該水位決定堰4
11側に位置すると共に邪魔板43の上位まで水没し、
該排出カバー42の液側端部に通水口41を備えた構成
となっている。上記構成において、オーバフロー口41
は邪魔板43と排出カバー42の液側端との隙間と、水
位決定堰側411と排出カバー42の下面との隙間と、
副還流管44とから構成される。従って分離された水も
この順で流れて還流管37に至り、ここで通常の処理水
と合流する。他方汚濁泡Dは下方からの上昇水流に押さ
れると共に、オーバフロー水の水流に乗せられて排出カ
バー42の上面を乗り越して排出管38から外部に排出
される。第2実施例は、第4図に示す。これは上記第1
実施例における主要部分を一体構成したものである。即
ち、オーバフロー口41と、排出カバー42と、邪魔板
43とを一体化して構成してある。他の実施例を項目列
挙すれば、次の通りである。(1)第1実施例では、従
来技術における水位決定堰412を存続させたが、オー
バフロー流量、不定の各種水位変動要因の程度に応じて
水位決定堰412を無くし、総てを水位決定堰411す
ること必要もある。 (2)第2実施例では、第4図に示したように、箱形と
したが、例えばオーバフロー口41を曲線状にしてその
上下にこれも曲面である排出カバー42と邪魔板43と
を配置する等の自在形状としてもよい。 (3)第2実施例では、一体式としたが、例えば、オー
バフロー41と排出カバー42との一体化又はオーバフ
ロー口41と邪魔板43との一体化等の部分的一体化で
もよい。 以下上記実施例の実験成績及び実験から得られた留意点
を述べる。 (成績)実施例は、容量800リットルの浮上分離式浄
化装置で全水量5mの平目の養殖用海水を浄化処理し
たところ、1日当たり約20lの汚濁泡Dを排出した。
その化学的酸素要求量(COD)は約600ppmであ
る(排除した総CODは一日当たり12gとなる)。こ
れは、従来装置の同様の試験結果の2〜10倍の値であ
る。次に、水槽の10分の1の容量の本発明装置と、水
槽の3分の1の容量の濾過装置とを用いて平目の養殖を
6か月間行ったところ、海水の補充は微々たるものとな
った(本出願人の知る限り、かかる好結果の養殖の報告
例は無い)。 (留意点) (1)水位調整堰36との関連について述べれば、汚濁
泡Dの種類にもよるが、水位調整堰36の水位高さは排
出カバー42の汚濁物乗り越え面の高さと、オーバフロ
ー口41水位との中間がよく、上記第1実施例では、排
出カバー42の汚濁物乗り越え面高さから2〜30mm
下方がよいという効果を得た。これより高いと、排出カ
バー42の上面から純粋な水が流出するようになり、逆
にこれより低いと、汚濁泡Dが排出されにくくなり、掻
き取り機等による強制分離が必要となってしまう。 (2)邪魔板43の位置は基本的に設定水位より(即
ち、排出カバー42の汚濁物乗り越え面高さより)も低
ければ効果を発揮する。しかし設定水位より5mm〜3
00mm程度下方が理想的である。仮に邪魔板43の位
置が高すぎると、水面上の汚濁泡Dが邪魔板43に接し
て移動しにくくなり、しかもこの接触部分での水平方向
の乱流にして汚濁泡Dの成長に支障をきたす。従って汚
濁泡Dの排出がスムーズにいかなくなる。逆に邪魔板4
3の位置が低すぎると、邪魔板43を回って気泡が上昇
するようになり、邪魔板43の本考案における効果を半
減化してしまう。
Embodiments will be described below with reference to the drawings. First
The embodiment is shown in Fig. 1 (Fig. 1 (a) is a top view of Fig. 1 (b)).
Further, as shown in FIG. 2 which is a partially enlarged view of FIG. 1, the contaminant separation unit 32 of the flotation separation type purification device 30 which is a natural separation type together with the water level determination weir 412 of the contaminant separation unit 32 in the prior art. A water level determination weir 411 is provided. The water level determination weir 411 is provided lower than the water level determination weir 412. A baffle plate 43 is provided below the water level determining weir 411 on the liquid side, and the water level determining weir 41 is provided on the opposite side to the liquid side.
The levitation separation type purification device 30 for overflow water ω from 1
An auxiliary reflux pipe 44 is provided to join the original reflux pipe 37. Further, above the water level determining weir 411, there is provided a discharge cover 42 over which the polluted foam D rides. This discharge cover 4
The liquid side end of 2 is closer to the water level determining weir 4 than the liquid side end of the baffle plate 43.
Located on the 11 side and submerged to the upper level of the baffle plate 43,
The water outlet 41 is provided at the liquid side end of the discharge cover 42. In the above configuration, the overflow port 41
Is a gap between the baffle plate 43 and the liquid side end of the discharge cover 42, a gap between the water level determining weir side 411 and the lower surface of the discharge cover 42,
It is composed of an auxiliary reflux pipe 44. Therefore, the separated water also flows in this order to reach the reflux pipe 37, where it joins the normal treated water. On the other hand, the polluted foam D is pushed by the rising water flow from below, and is also carried on the water flow of the overflow water to pass over the upper surface of the discharge cover 42 and is discharged to the outside from the discharge pipe 38. The second embodiment is shown in FIG. This is the first
The main part in the embodiment is integrally configured. That is, the overflow port 41, the discharge cover 42, and the baffle plate 43 are integrally formed. Items of other examples are listed as follows. (1) In the first embodiment, the water level determining weir 412 in the prior art was kept alive, but the water level determining weir 412 is eliminated according to the overflow flow rate and the degree of various uncertain factors of water level variation, and all the water level determining weirs 411. There is also a need to do. (2) In the second embodiment, as shown in FIG. 4, the box shape is used. However, for example, the overflow port 41 is formed into a curved shape, and the discharge cover 42 and the baffle plate 43, which are also curved surfaces, are provided above and below the overflow port 41. It may be arranged freely, for example. (3) In the second embodiment, the integral type is used, but the overflow 41 and the discharge cover 42 may be integrated or the overflow port 41 and the baffle plate 43 may be integrated partially. The experimental results of the above-mentioned examples and points to be noted from the experiments will be described below. (Results) In the example, when the floating separation type purification device having a capacity of 800 liters was used to purify the flat culture seawater having a total water amount of 5 m 3 , about 20 l of the polluted foam D was discharged per day.
Its chemical oxygen demand (COD) is about 600 ppm (total COD excluded is 12 g per day). This is a value that is 2 to 10 times higher than the similar test result of the conventional device. Next, when the flat culture was carried out for 6 months using the device of the present invention having a capacity of 1/10 of the water tank and the filtration device having a capacity of 1/3 of the water tank, supplementation of seawater was insignificant. (As far as the applicant is aware, there are no reports of such successful aquaculture). (Points to be noted) (1) Speaking of the relation with the water level adjusting weir 36, the water level height of the water level adjusting weir 36 depends on the type of the pollution bubble D, but the height of the surface of the discharge cover 42 overcoming the contaminants and the overflow. It is close to the water level of the mouth 41, and in the first embodiment, it is 2 to 30 mm from the height of the surface of the discharge cover 42 over which contaminants pass.
The effect is that the lower part is good. If it is higher than this, pure water comes to flow out from the upper surface of the discharge cover 42, and if it is lower than this, the polluted foam D becomes difficult to be discharged and forced separation by a scraper or the like becomes necessary. . (2) Basically, the position of the baffle plate 43 is effective if it is lower than the set water level (that is, the height of the surface of the discharge cover 42 over which the contaminants pass). However, from the set water level 5 mm to 3
Ideally, the lower part is about 00 mm. If the position of the baffle plate 43 is too high, it becomes difficult for the dirty bubbles D on the surface of the water to come into contact with the baffle plate 43, and it becomes difficult to move the horizontal direction turbulent flow at this contact portion to hinder the growth of the dirty bubbles D. Come here. Therefore, the discharge of the polluted foam D does not go smoothly. On the contrary, baffle plate 4
If the position of 3 is too low, air bubbles will rise around the baffle plate 43 and the effect of the baffle plate 43 in the present invention will be halved.

【考案の効果】以上説明したように、本考案に係わる浮
上分離式浄化装置によれば、汚濁物分離部に、還流管と
合流するオーバフロー口と、その上方の排出カバー42
と、下方の邪魔板43とを適宜配置したので、自然分離
式の浮上分離式浄化装置であっても、高効率で汚濁物を
分離し、かつ、排出することができるようになる。例え
ば、従来技術において、従来技術の浮上分離式浄化装置
の適用が困難であった養魚用水の浄化システムであって
も、本考案の浮上分離式浄化装置を付設すれば、魚貝類
の健康維持の増進、用水の補充の軽減、強制排出機構の
省略及び濾過装置の小型化等を容易に達成するこができ
るようになる。
As described above, according to the flotation separation type purification apparatus of the present invention, the contaminant separation section is provided with an overflow port which joins the reflux pipe, and a discharge cover 42 above the overflow port.
Since the lower baffle plate 43 is appropriately arranged, the contaminant can be separated and discharged with high efficiency even in the case of the natural separation type floating separation type purification device. For example, in the conventional technology, even if it is a purification system for water for fish farming, to which it was difficult to apply the floatation separation type purification apparatus of the prior art, if the floatation separation type purification apparatus of the present invention is attached, it is possible to maintain the health of fish and shellfish. It is possible to easily achieve enhancement, reduction of replenishment of water, omission of the forced discharge mechanism, downsizing of the filtering device, and the like.

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

第1図及び第2図は本考案の第1実施例なる浮上分離式
浄化装置の図であって、第1図(a)は上視図、(b)
は正面図、第2図は一部拡大図、第3図は本考案の作用
を説明する図、第4図は第2実施例なる浮上分離式浄化
装置の一部拡大図、第5図は魚貝類の養殖等において浮
上分離式浄化装置を設置した場合の循環式の浄化システ
ム図、第6図は従来の浮上分離式浄化装置例の図であっ
て、(a)は上視図、(b)は正面図、第7図は従来の
作用を説明する図である。 30……浮上分離式浄化装置 31……本体 32……汚濁物分離部 33……原水流入口 34……散気部 35……処理水出口 36……水位調整堰 37……還流管 38……排出管 41……オーバフロー口 42……排出カバー 43……邪魔板 D……汚濁泡
1 and 2 are views of a floating separation type purification apparatus according to a first embodiment of the present invention, wherein FIG. 1 (a) is a top view and FIG.
Is a front view, FIG. 2 is a partially enlarged view, FIG. 3 is a diagram for explaining the operation of the present invention, FIG. 4 is a partially enlarged view of the flotation type purification apparatus according to the second embodiment, and FIG. FIG. 6 is a diagram of a circulation type purification system when a flotation type purification device is installed in fish and shellfish aquaculture, etc. FIG. 6 is a diagram of an example of a conventional flotation type purification device, (a) is a top view, ( b) is a front view, and FIG. 7 is a view for explaining the conventional operation. 30 ...... Floating separation type purification device 31 ...... Main body 32 …… Contaminant separation part 33 …… Raw water inlet 34 …… Aeration part 35 …… Treatment water outlet 36 …… Water level adjusting weir 37 …… Recirculation pipe 38 ・ ・ ・… Discharge pipe 41 …… Overflow port 42 …… Discharge cover 43 …… Baffle plate D …… Contaminated foam

Claims (1)

【実用新案登録請求の範囲】[Scope of utility model registration request] 【請求項1】浮上分離式浄化装置の汚濁物分離部32に
おいて、該浮上分離式浄化装置の還流管37に合流する
オーバフロー口41を設け、このオーバフロー口41の
上方には、汚濁泡Dが該オーバフロー口41に流入する
ことを防ぐと共に該汚濁泡Dが排出側へ乗り越す排出カ
バー42を設け、さらにこのオーバフロー口41の下方
には、下方からの上昇水流が該オーバフロー口41に直
接流入することを防ぐ邪魔板43を備えた構成を特徴と
する浮上分離式浄化装置。
1. An overflow port 41, which joins a reflux pipe 37 of the flotation type purification device, is provided in a pollutant separation part 32 of the flotation type purification device, and a polluted bubble D is provided above the overflow port 41. A discharge cover 42 is provided to prevent the polluted foam D from flowing into the overflow port 41 and to pass over to the discharge side. Further, below the overflow port 41, a rising water flow from below directly flows into the overflow port 41. A flotation separation type purification device characterized by a structure including a baffle plate 43 for preventing such a situation.
JP40640190U 1990-12-14 1990-12-14 Floating separation type purification device Expired - Lifetime JPH0753750Y2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP40640190U JPH0753750Y2 (en) 1990-12-14 1990-12-14 Floating separation type purification device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP40640190U JPH0753750Y2 (en) 1990-12-14 1990-12-14 Floating separation type purification device

Publications (2)

Publication Number Publication Date
JPH0487791U JPH0487791U (en) 1992-07-30
JPH0753750Y2 true JPH0753750Y2 (en) 1995-12-13

Family

ID=31883661

Family Applications (1)

Application Number Title Priority Date Filing Date
JP40640190U Expired - Lifetime JPH0753750Y2 (en) 1990-12-14 1990-12-14 Floating separation type purification device

Country Status (1)

Country Link
JP (1) JPH0753750Y2 (en)

Also Published As

Publication number Publication date
JPH0487791U (en) 1992-07-30

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