JP2010005520A - Floatation separation apparatus - Google Patents

Floatation separation apparatus Download PDF

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JP2010005520A
JP2010005520A JP2008166759A JP2008166759A JP2010005520A JP 2010005520 A JP2010005520 A JP 2010005520A JP 2008166759 A JP2008166759 A JP 2008166759A JP 2008166759 A JP2008166759 A JP 2008166759A JP 2010005520 A JP2010005520 A JP 2010005520A
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water
treated
levitation
chamber
floating
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JP4885169B2 (en
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Kazuhiko Shimizu
和彦 清水
Tomoaki Miyanoshita
友明 宮ノ下
Yuichiro Toba
裕一郎 鳥羽
Toshiaki Kunito
俊朗 國東
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Organo Corp
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Organo Corp
Japan Organo Co Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a floatation separation apparatus which enables high-speed treatment by small-scale equipment. <P>SOLUTION: The floatation separation apparatus makes air bubbles adhere to substances to be treated in water to be treated to separate the substances to be treated as floating substances. The apparatus has a floatation chamber 16, an inflow portion 12 for allowing the water to be treated to flow into the floatation chamber 16, and a water collecting portion 22 having water collecting openings 22a for collecting treated water, from which the substances to be treated have been separated. The floatation chamber 16 is vertically divided into upper and lower portions 28a and 28b by the water collecting portion 22, and has a water passing portion for allowing the treated water to pass between the upper portion 28a and the lower portion 28b. The multiple water collecting openings 22a installed in the water collecting portion 22 are formed from the peripheral wall to the center of the floatation chamber 16. The inflow portion 12 opens in the upper portion 28a to allow the water to be treated to flow into the upper portion 28a from the opening. <P>COPYRIGHT: (C)2010,JPO&INPIT

Description

本発明は、被処理水中の被処理物質に気泡を付着させ、被処理物質を浮上物として分離する浮上分離装置の技術に関する。   The present invention relates to a technique of a levitation separation device that attaches bubbles to a substance to be treated in water to be treated and separates the substance to be treated as a floating substance.

従来、被処理水中に含まれるSS成分、油分等の被処理物質を除去する方法として、被処理水と気泡とを混合して、浮上槽に供給し、被処理物質に気泡を付着させて浮上槽の水面に浮上させ、被処理物質を分離する浮上処理が知られている。なお、処理効率を上げるために、被処理水を浮上槽に供給する前に、凝集剤を添加して、被処理水中に含まれる被処理物質をフロック化させることも行われている。   Conventionally, as a method of removing SS components, oils, and other substances to be treated contained in the water to be treated, the water to be treated and bubbles are mixed and supplied to the levitation tank. A levitation process is known that floats on the surface of a tank and separates a substance to be treated. In addition, in order to raise processing efficiency, before supplying to-be-processed water to a levitation tank, a flocculant is added and the to-be-processed substance contained in to-be-processed water is made to flock.

図11は、従来の浮上分離装置の構成を示す模式図である。この浮上分離装置5において、浮上槽70には、槽体を構成する外周壁72の内側には、下端が槽内中間部に至る内周壁74が外周壁72の内周に沿って設けられている。外周壁72及び内周壁74は円筒形である。外周壁72と内周壁74との間は、内周壁74によって浮上物が進入するのが防止され、処理水が集水される処理水室76が形成されている。浮上槽70内の中央部分には、上部および下部が開放されたガイド筒78が設けられ、このガイド筒78内には、浮上槽70の底部70aの中央から延設され、ガイド筒78内で開口する導入管80が設けられている。導入管80には、浮上槽70外にて被処理水流入管82が接続されている。また、被処理水流入管82には、加圧水流入管84が接続され、ここから加圧タンク等で高圧下で空気が溶解した加圧水が供給されている。   FIG. 11 is a schematic diagram showing a configuration of a conventional floating separation apparatus. In the levitation separation device 5, the floating tank 70 is provided with an inner peripheral wall 74, which has a lower end reaching the intermediate portion in the tank, along the inner periphery of the outer peripheral wall 72, inside the outer peripheral wall 72 constituting the tank body. Yes. The outer peripheral wall 72 and the inner peripheral wall 74 are cylindrical. Between the outer peripheral wall 72 and the inner peripheral wall 74, the inner peripheral wall 74 prevents a levitated material from entering, and a treated water chamber 76 in which treated water is collected is formed. A guide cylinder 78 having an open upper and lower part is provided in the central portion of the levitation tank 70. The guide cylinder 78 extends from the center of the bottom 70 a of the levitation tank 70, and is provided in the guide cylinder 78. An opening introducing pipe 80 is provided. A treated water inflow pipe 82 is connected to the introduction pipe 80 outside the floating tank 70. Further, a pressurized water inflow pipe 84 is connected to the treated water inflow pipe 82, and pressurized water in which air is dissolved under high pressure is supplied from here through a pressurized tank or the like.

浮上分離装置5の運転方法を説明する。例えば、加圧水流入管84を介して、処理水に高圧下おいて空気を溶解させた加圧水を被処理水流入管82に供給し、加圧水と被処理水が混合された混合液が被処理水流入管82を通り、導入管80を介し、浮上槽70のガイド筒78内に供給される。浮上槽70内では、加圧水中に溶解していた気体が気泡として析出し、被処理水中に含まれる被処理物質に付着し、被処理物質が浮上分離される。被処理物質が除去された処理水は、処理水室76の下端部76aから処理水室76を通り、浮上槽70の外周壁72の上端の越流堰をオーバーフローして調整槽86に供給され、ここに接続されている処理水排出管88により系外に排出される。   A method for operating the levitation separator 5 will be described. For example, via the pressurized water inflow pipe 84, pressurized water in which air is dissolved under high pressure in the treated water is supplied to the treated water inflow pipe 82, and a mixed liquid in which the pressurized water and the to-be-treated water are mixed is treated water inflow pipe 82. And is supplied into the guide cylinder 78 of the levitation tank 70 through the introduction pipe 80. In the levitation tank 70, the gas dissolved in the pressurized water is precipitated as bubbles and adheres to the material to be treated contained in the water to be treated, and the material to be treated is floated and separated. The treated water from which the material to be treated has been removed passes from the lower end 76 a of the treated water chamber 76 through the treated water chamber 76, overflows the overflow weir at the upper end of the outer peripheral wall 72 of the floating tank 70, and is supplied to the adjusting tank 86. The treated water discharge pipe 88 connected here discharges the outside of the system.

ここで、図11に示す浮上分離装置5では、導入管80、ガイド筒78を通って浮上槽70内に流入した被処理水は、浮上槽70の内周壁74に向かって流れ、内周壁74に達すると、内周壁74に沿って、下降する。この下降流の流速が速いと、浮力が十分でない被処理物質が、下降流に伴い内周壁74の下端を越え処理水室76に流れ込んで、処理水の水質を悪化させる。このように、内周壁74に沿った下降流が早くなるのは、浮上槽70内に、浮上分離処理に使用されていない部分(例えば、図11に示す網掛け部)が、多く存在するからであり、被処理物質の除去において、浮上槽70全体を有効に使用することができないと、浮上分離が効率的に行えないという問題がある。   Here, in the levitation separation apparatus 5 shown in FIG. 11, the water to be treated that flows into the levitation tank 70 through the introduction pipe 80 and the guide cylinder 78 flows toward the inner peripheral wall 74 of the levitation tank 70, and the inner peripheral wall 74. , It descends along the inner peripheral wall 74. When the flow rate of the downward flow is high, the material to be treated having insufficient buoyancy flows into the treated water chamber 76 over the lower end of the inner peripheral wall 74 along with the downward flow, thereby deteriorating the quality of the treated water. As described above, the reason why the downward flow along the inner peripheral wall 74 is accelerated is that there are many portions (for example, the shaded portions shown in FIG. 11) that are not used for the floating separation process in the floating tank 70. In the removal of the material to be treated, there is a problem that the floating separation cannot be performed efficiently unless the entire floating tank 70 can be used effectively.

図11に示す浮上分離装置5の一般的な水面積負荷(浮上槽70の水平断面積に対する処理水量(線速度LV))は、5〜10m/hである。図11に示す浮上分離装置5では、LVを上記範囲より高くすると、処理水の水質が悪化しやすい。   The general water area load (the amount of treated water (linear velocity LV) with respect to the horizontal sectional area of the levitation tank 70) of the levitation separator 5 shown in FIG. 11 is 5 to 10 m / h. In the levitation separator 5 shown in FIG. 11, when the LV is higher than the above range, the quality of the treated water tends to deteriorate.

また、特許文献1には、図11に示す浮上分離装置5より、LVを高くすることが可能な浮上分離装置が提案されている。図12は、特許文献1の浮上分離装置の構成を示す模式図である。図12に示す浮上分離装置6において、浮上槽90の周壁90aは矩形であり、浮上槽90内は、上部開放の隔壁92a、下部開放の隔壁92bにより、被処理水が縦方向に迂回して流れる三つの室、第1の室94、第2の室96、第3の室98に区画されている。また、第2の室96の隔壁92aと隔壁92bとの間には、整流板100が水平に設置されている。整流板100には、複数の整流孔100aが形成されており、第2の室96から第3の室98に至る水は整流板100を通過する。第1の室94には、被処理水流入管102に接続されている。また、加圧水流入管104の一端は第1の室94に接続され、他端は空気溶解タンク105の出口に接続されている。第3の室98には、処理水排出管106が接続されている。空気溶解タンク105と処理排出管106との間には、ポンプ110を介して連通管111が接続され、処理水排出管106を通る処理水の一部が連通管111を通り、空気溶解タンク105に供給される。空気溶解タンク105では、処理水に空気を溶解させ、加圧水が製造される。   Further, Patent Document 1 proposes a levitation separator that can increase the LV compared to the levitation separator 5 shown in FIG. FIG. 12 is a schematic diagram showing the configuration of the flotation separation device of Patent Document 1. As shown in FIG. In the levitation separator 6 shown in FIG. 12, the peripheral wall 90a of the levitation tank 90 is rectangular, and in the levitation tank 90, the water to be treated is detoured in the vertical direction by the upper open partition 92a and the lower open partition 92b. It is divided into three chambers that flow, a first chamber 94, a second chamber 96, and a third chamber 98. A rectifying plate 100 is horizontally installed between the partition wall 92a and the partition wall 92b of the second chamber 96. A plurality of rectifying holes 100 a are formed in the rectifying plate 100, and water from the second chamber 96 to the third chamber 98 passes through the rectifying plate 100. The first chamber 94 is connected to the treated water inflow pipe 102. One end of the pressurized water inflow pipe 104 is connected to the first chamber 94, and the other end is connected to the outlet of the air dissolution tank 105. A treated water discharge pipe 106 is connected to the third chamber 98. A communication pipe 111 is connected between the air dissolution tank 105 and the treatment discharge pipe 106 via a pump 110, and part of the treated water passing through the treatment water discharge pipe 106 passes through the communication pipe 111, and the air dissolution tank 105. To be supplied. In the air dissolution tank 105, air is dissolved in the treated water to produce pressurized water.

このような浮上分離装置6において、被処理水流入管102から第1の室94に流入した被処理水、空気溶解タンク105から加圧水流入管104を通り第1の室94に流入した加圧水は、液面に向かって上昇して、隣接する第2の室96に流入する。第2の室96では、被処理水中の被処理物質が浮上物として液面上に浮かび、下部に処理水が得られる。このような浮上分離処理された処理水は、整流板100の整流孔100aを通り、第3の室98から排出される。   In such a levitation separator 6, the water to be treated that has flowed into the first chamber 94 from the water to be treated 102 and the pressurized water that has flowed from the air dissolution tank 105 through the pressurized water inflow tube 104 into the first chamber 94 are liquid. It rises toward the surface and flows into the adjacent second chamber 96. In the second chamber 96, the substance to be treated in the water to be treated floats on the liquid surface as a floating substance, and treated water is obtained at the bottom. The treated water that has been subjected to the float separation process passes through the rectifying hole 100 a of the rectifying plate 100 and is discharged from the third chamber 98.

図12に示す浮上分離装置6でも、第2の室96の隔壁92bに沿って下降する被処理水の下降流の流速は速くなる。しかし、図12に示す浮上分離装置6には、整流板100が設けられているため、整流板100の整流効果により、隔壁92bに沿って下降する被処理水の下降流がそのままの勢いで、第3の室98側へ流れることが防止される。その結果、被処理物質が下降流と共に第3の室98側へ流れ込むこと等が抑制され、図12に示す浮上分離装置6は、図11に示す浮上分離装置5より高容積負荷での処理が可能となる。   Also in the floating separation apparatus 6 shown in FIG. 12, the flow rate of the downflow of the water to be treated that descends along the partition wall 92b of the second chamber 96 is increased. However, since the levitation separation device 6 shown in FIG. 12 is provided with the rectifying plate 100, due to the rectifying effect of the rectifying plate 100, the downflow of the water to be treated that falls along the partition wall 92b remains as it is, The flow to the third chamber 98 side is prevented. As a result, the material to be treated is prevented from flowing into the third chamber 98 side along with the downward flow, and the levitating separation device 6 shown in FIG. 12 is capable of processing at a higher volume load than the levitating separation device 5 shown in FIG. It becomes possible.

米国特許出願公開第2005/0115881号明細書US Patent Application Publication No. 2005/0115881

図12に示す浮上分離装置6は、浮上槽90の周壁90aが矩形であって、周壁90aの一端側に設けられる第1の室94から被処理水が供給され、他端側に設けられる第3の室98から処理水が排出される構造である。このような構造において、第1の室94から隔壁92bへ流れる被処理水の流れ(すなわち、浮上槽の液面を流れる被処理水の流れ)は、図11に示す浮上分離装置5において、ガイド筒78から内周壁74に向かって拡がりながら流れる被処理水の流れ(すなわち、浮上槽の液面を流れる被処理水の流れ)より速い流速となる。   In the levitation separation apparatus 6 shown in FIG. 12, the peripheral wall 90a of the levitation tank 90 is rectangular, the water to be treated is supplied from the first chamber 94 provided on one end side of the peripheral wall 90a, and the first is provided on the other end side. 3, the treated water is discharged from the third chamber 98. In such a structure, the flow of water to be treated flowing from the first chamber 94 to the partition wall 92b (that is, the flow of water to be treated flowing on the liquid surface of the levitation tank) is guided in the levitation separation device 5 shown in FIG. The flow rate of the water to be treated flowing while expanding from the cylinder 78 toward the inner peripheral wall 74 (that is, the flow of the water to be treated flowing on the liquid surface of the levitation tank) is higher.

また、浮上分離装置の負荷を上げれば、浮上槽90の液面を流れる被処理水の流速はさらに速くなると共に、隔壁92bに沿って下降する下降流の流速も速くなる。その結果、隔壁92b側の整流板100に、速い流速の下降流が衝突することになり、整流板100の整流効果を充分に得ることが難しくなり、被処理物質が下降流と共に第3の室98側へ流れ込むこと等を充分に抑制することができず、処理水の水質が悪化しやすくなる。したがって、図12に示すような浮上分離装置6でも、処理水の水質を悪化させることなく処理量を増加するには、装置を大型化する必要がある。   Further, when the load of the floating separation device is increased, the flow rate of the water to be treated flowing on the liquid surface of the floating tank 90 is further increased, and the flow rate of the descending flow descending along the partition wall 92b is also increased. As a result, a downward flow having a high flow velocity collides with the rectifying plate 100 on the side of the partition wall 92b, and it becomes difficult to sufficiently obtain the rectifying effect of the rectifying plate 100. It cannot suppress sufficiently that it flows into 98 side, etc., and the quality of treated water tends to deteriorate. Therefore, even in the floating separation apparatus 6 as shown in FIG. 12, it is necessary to enlarge the apparatus in order to increase the throughput without deteriorating the quality of the treated water.

そこで、本発明の目的は、小型な装置設備で高速処理が可能な浮上分離装置を提供することにある。   Accordingly, an object of the present invention is to provide a floating separation apparatus capable of high-speed processing with a small apparatus.

本発明は、被処理水中の被処理物質に気泡を付着させ、被処理物質を浮上物として分離する浮上分離装置であって、浮上室と、前記浮上室に被処理水を流入させる流入部と、前記被処理物質が分離された処理水を集水する集水口を有する集水部とを有し、前記浮上室は、前記集水部により垂直方向上部及び下部に区画されると共に、前記上部と前記下部との間を前記処理水が通水する通水部を有し、前記集水部に設けられる集水口は、前記浮上室の周壁から中央に亘って複数形成され、前記流入部は、前記上部で開口し、当該開口部から前記上部に被処理水を流入させる。   The present invention is a levitation separation device that attaches bubbles to a material to be treated in the water to be treated and separates the material to be treated as a levitated substance, and includes a floating chamber and an inflow portion for allowing the water to be treated to flow into the levitation chamber; And a water collection part having a water collection port for collecting treated water from which the material to be treated is separated, and the floating chamber is partitioned into an upper part and a lower part in the vertical direction by the water collection part, and the upper part And the lower part has a water flow part through which the treated water flows, and a plurality of water collection ports provided in the water collection part are formed from the peripheral wall of the floating chamber to the center, and the inflow part is The upper portion is opened, and water to be treated is allowed to flow into the upper portion from the opening.

また、前記浮上分離装置において、前記通水部の水平断面積/前記浮上室の水平断面積が0.24〜0.75の範囲であることが好ましい。   Moreover, in the said levitation separator, it is preferable that the horizontal cross-sectional area of the said water flow part / the horizontal cross-sectional area of the said levitation chamber is the range of 0.24-0.75.

また、前記浮上分離装置において、前記被処理物質のうち前記浮上室の底部に沈殿した沈殿物を掻き寄せる沈殿物掻き寄せ機を備えることが好ましい。   Moreover, it is preferable that the levitation separation apparatus further includes a sediment scraper that scrapes the sediment that has settled at the bottom of the levitation chamber among the substances to be treated.

また、前記浮上分離装置において、前記被処理物質のうち前記集水部上に沈殿した沈殿物を前記通水部から下方に排出する集水部スクレーパーを備えることが好ましい。   Moreover, it is preferable that the floating separation apparatus further includes a water collection unit scraper that discharges a sediment precipitated on the water collection unit out of the material to be treated from the water flow unit downward.

また、前記浮上分離装置において、前記浮上室は円筒状であり、前記流入部は、前記浮上室の中心を軸として回転可能に設けられ、前記沈殿物掻き寄せ機及び前記集水部スクレーパーは、前記流入部に取り付けられ、前記流入部と一体に回転されることが好ましい。   Further, in the levitation separation apparatus, the levitation chamber is cylindrical, and the inflow portion is provided to be rotatable about the center of the levitation chamber, and the sediment scraper and the water collecting portion scraper are It is preferable to attach to the inflow part and rotate integrally with the inflow part.

本発明の浮上分離装置では、小型な装置設備で高速処理が可能である。   In the floating separation apparatus of the present invention, high-speed processing is possible with small equipment.

本発明の実施の形態について以下説明する。本実施形態は本発明を実施する一例であって、本発明は本実施形態に限定されるものではない。   Embodiments of the present invention will be described below. This embodiment is an example for carrying out the present invention, and the present invention is not limited to this embodiment.

図1は、本実施形態に係る浮上分離装置の構成の一例を示す模式斜視図である。図2は、本実施形態に係る浮上分離装置の構成の一例を示す模式断面図である。図1に示す浮上分離装置1は、浮上槽10、流入部12、排出部14、集水部22を備える。   FIG. 1 is a schematic perspective view showing an example of the configuration of the levitation separation apparatus according to the present embodiment. FIG. 2 is a schematic cross-sectional view showing an example of the configuration of the levitation separator according to this embodiment. A levitation separation apparatus 1 shown in FIG. 1 includes a levitation tank 10, an inflow portion 12, a discharge portion 14, and a water collection portion 22.

図1及び図2に示すように、浮上槽10の周壁10aは円筒形とされ、浮上槽10の底部10bは中央に向かって低位となるホッパ状とされている。浮上槽10内は、流入部12から供給された被処理水の浮上分離処理が行われる浮上室16となる。また、底部10bの中央には、被処理物質のうちの沈殿物を溜めるピット18が設けられている。ピット18には、不図示の沈殿物排出口が設けられ、沈殿物排出管19が接続されている。浮上槽10の周壁10aは、矩形とされてもよい。しかし、浮上槽10の周壁10aを円筒形とすることにより、浮上室16の中心部に配置される流入部12の開口部(開口部については後述する)から周壁10aまで、被処理水が拡がりながら流れることになる。従って、流入部12から出るときの流速は比較的速いが、周壁10aに当たる際の表面部の流れは比較的遅くなる。その結果、周壁10aのある一部分で急速な下降流が生じることもなく、急速な下降流により生じる処理水の水質の悪化を効果的に抑制することができる。   As shown in FIGS. 1 and 2, the peripheral wall 10a of the levitation tank 10 has a cylindrical shape, and the bottom 10b of the levitation tank 10 has a hopper shape that becomes lower toward the center. The inside of the levitation tank 10 is a levitation chamber 16 in which levitation separation processing of water to be treated supplied from the inflow portion 12 is performed. A pit 18 is provided at the center of the bottom portion 10b to collect a deposit of the material to be treated. The pit 18 is provided with a sediment discharge port (not shown), and a sediment discharge pipe 19 is connected thereto. The peripheral wall 10a of the floating tank 10 may be rectangular. However, by forming the peripheral wall 10a of the levitation tank 10 into a cylindrical shape, the water to be treated spreads from the opening portion (the opening portion will be described later) of the inflow portion 12 disposed at the center of the levitation chamber 16 to the peripheral wall 10a. It will flow while. Therefore, although the flow velocity when exiting the inflow portion 12 is relatively fast, the flow of the surface portion when hitting the peripheral wall 10a is relatively slow. As a result, a rapid downward flow does not occur in a part of the peripheral wall 10a, and the deterioration of the quality of the treated water caused by the rapid downward flow can be effectively suppressed.

また、浮上槽10には、被処理物質のうち、液面に浮上した浮上物23(いわゆるスカム)を排出するための浮上物ポット24(図2においては不図示)が設けられている。浮上槽10には、液面に浮上した浮上物23を掻き寄せる浮上物スキマー20が設けられている。浮上物スキマー20は、モータ26のシャフトに固定され、モータ26が駆動することにより、浮上物スキマー20が回転される。浮上物スキマー20は、羽根、螺旋羽根等のスクレーパー部を有しており、水面の流れ及びスクレーパー部の移動により浮上物23が半径方向外側に移動させられ、浮上物ポット24に集められる。また、浮上物ポット24は、掻き寄せられてくる浮上物23が水面上から浮上物ポット24内に落下するように、その浮上槽10側の境界部分に水面下から水面上に至るスロープを有することが好適である。   The levitation tank 10 is provided with a levitation object pot 24 (not shown in FIG. 2) for discharging the levitation substance 23 (so-called scum) that has floated on the liquid surface among the substances to be treated. The levitation tank 10 is provided with a levitated skimmer 20 that scrapes the levitated substance 23 that has levitated to the liquid surface. The levitated skimmer 20 is fixed to the shaft of the motor 26, and the levitated skimmer 20 is rotated by driving the motor 26. The levitated skimmer 20 has scraper portions such as blades and spiral vanes, and the levitated matter 23 is moved radially outward by the flow of the water surface and the movement of the scraper portion, and is collected in the levitated matter pot 24. Further, the levitated pot 24 has a slope extending from the lower surface to the upper surface of the water at the boundary portion of the levitating tank 10 side so that the levitated object 23 that is scraped down falls into the levitated pot 24 from the water surface. Is preferred.

図3は、本発明の実施形態に係る浮上分離装置の構成の一例を示す模式上面図である。図3では、集水部22の構造を明らかにするため、モータ26、浮上物スキマー20、浮上物ポット24等を不図示としている。図2及び図3に示すように、浮上室16(浮上槽10内)は、集水部22により垂直方向上部28a及び下部28bに区画されると共に、図3に示すように上部28aと下部28bとの間を処理水が通水する通水部33を有している。集水部22には、処理水を集水する集水口22aが形成されている。本実施形態における集水口22aは、下部28b側に形成されている。また、集水部22は排出部14を構成する処理水取出管38に接続されている。   FIG. 3 is a schematic top view showing an example of the configuration of the floating separation apparatus according to the embodiment of the present invention. In FIG. 3, the motor 26, the levitated skimmer 20, the levitated pot 24, and the like are not shown in order to clarify the structure of the water collecting unit 22. As shown in FIGS. 2 and 3, the levitation chamber 16 (in the levitation tank 10) is partitioned into a vertical upper part 28a and a lower part 28b by the water collecting part 22, and as shown in FIG. 3, the upper part 28a and the lower part 28b. A water passage 33 through which treated water flows. A water collection port 22 a for collecting treated water is formed in the water collection unit 22. The water collection port 22a in the present embodiment is formed on the lower portion 28b side. Further, the water collection unit 22 is connected to a treated water discharge pipe 38 that constitutes the discharge unit 14.

集水部22は、浮上室16を上部28a及び下部28bで通水可能なように区画する構造である。例えば、図3に示すように、集水部22は、下部28b側に形成された集水口22aを有する環状の集水管29を浮上室16の径方向に所定の間隔をあけて複数配置させることにより、形成される。集水管29同士の隙間、集水管29と周壁10aとの隙間、集水管29とガイド筒30との隙間が、上部28aと下部28bとの間を処理水が通水する通水部33となる。図4は、本発明の他の実施形態に係る浮上分離装置の構成の一例を示す模式上面図である。図4に示すように、下部28b側に形成された集水口22aを有する直線上の集水管29を所定の間隔をあけて複数配置させることにより、集水部22が形成されてもよい。図3,4に示す集水管29は処理水取出管38と連通しており、集水口22aから集水された処理水は、集水管29内を通り、処理水取出管38へ排出される。   The water collecting section 22 has a structure that partitions the floating chamber 16 so that water can flow through the upper portion 28a and the lower portion 28b. For example, as shown in FIG. 3, the water collecting section 22 has a plurality of annular water collecting pipes 29 each having a water collecting port 22 a formed on the lower portion 28 b side and arranged in the radial direction of the floating chamber 16 at a predetermined interval. Is formed. The gap between the water collecting pipes 29, the gap between the water collecting pipe 29 and the peripheral wall 10a, and the gap between the water collecting pipe 29 and the guide cylinder 30 serve as a water passage portion 33 through which treated water flows between the upper portion 28a and the lower portion 28b. . FIG. 4 is a schematic top view showing an example of the configuration of a levitation separation apparatus according to another embodiment of the present invention. As shown in FIG. 4, the water collecting part 22 may be formed by arranging a plurality of straight water collecting pipes 29 having a water collecting port 22a formed on the lower portion 28b side with a predetermined interval. The water collecting pipe 29 shown in FIGS. 3 and 4 communicates with the treated water outlet pipe 38, and the treated water collected from the water collection port 22 a passes through the water collecting pipe 29 and is discharged to the treated water outlet pipe 38.

ここで、集水部22を形成するために使用される集水管29の形状は特に制限されるものではない。図5(A)〜(C)は、集水部を構成する集水管の径方向断面の形状の一例を示す模式図である。図5(A),(B)に示すように、集水部22を構成する集水管29の径方向断面の形状は、円形、三角形等の多角形等が挙げられる。また、図5(C)に示すように、集水部22を構成する集水管29の上部、すなわち浮上室16の上部28a側には、集水管29上に被処理物質が堆積することを防止する堆積防止板32を設けてもよい。堆積防止板32は、集水管29上に被処理物質が堆積し難い形状となっていればよく、例えば、図5(C)に示すように、浮上室の下部28b側に向けてテーパ状に広がっている形状等が挙げられる。   Here, the shape of the water collecting pipe 29 used for forming the water collecting portion 22 is not particularly limited. FIGS. 5A to 5C are schematic views showing an example of the shape of the radial cross section of the water collecting pipe constituting the water collecting portion. As shown in FIGS. 5A and 5B, the shape of the radial cross section of the water collecting pipe 29 constituting the water collecting portion 22 may be a polygon such as a circle or a triangle. In addition, as shown in FIG. 5C, the material to be treated is prevented from depositing on the water collection pipe 29 on the upper side of the water collection pipe 29 constituting the water collection section 22, that is, on the upper portion 28a side of the floating chamber 16. An accumulation prevention plate 32 may be provided. The deposition preventing plate 32 only needs to have a shape that makes it difficult for the material to be treated to deposit on the water collection pipe 29. For example, as shown in FIG. 5C, the deposition preventing plate 32 is tapered toward the lower portion 28b of the levitation chamber. Examples include the expanding shape.

上記説明したように集水部22により、浮上室16は上部28a及び下部28bに区画されるが、集水部22が液面付近に設置されると、液面に浮上した浮上物23が処理水と共に集水口22aから取り込まれ、処理水の水質を悪化させる虞がある。また、集水部22が浮上室16の底部(浮上槽10の底部10b)付近に設置されると、底部に沈殿した沈殿物が処理水と共に集水口22aから取り込まれ、処理水の水質を悪化させる虞がある。したがって、集水部22は、浮上物23及び沈殿物が集水口22aから取り込まれない位置に設置されることが好ましい。   As described above, the floating chamber 16 is divided into the upper part 28a and the lower part 28b by the water collecting part 22, but when the water collecting part 22 is installed near the liquid level, the levitated object 23 that has floated to the liquid level is treated. The water is taken in from the water collection port 22a together with the water, and there is a risk of deteriorating the quality of the treated water. Moreover, when the water collection part 22 is installed in the bottom part of the floating chamber 16 (bottom part 10b of the levitation tank 10), the sediment which settled on the bottom part will be taken in from the water collection port 22a with treated water, and the quality of treated water will deteriorate. There is a risk of causing it. Therefore, it is preferable that the water collection part 22 is installed in the position where the levitated material 23 and the sediment are not taken in from the water collection port 22a.

図2〜4に示すように、集水部22に形成される集水口22aは、浮上室16の周壁から中央(浮上槽10の周壁10aから中央)に亘って複数設けられている。上記構成によって、浮上室16の上部28aから下部28bへ流れる処理水の下降流は、浮上室16の周壁(浮上槽10の周壁10a)に沿って流れる下降流だけでなく、周壁10a上方から浮上室16の中央下方に向かって流れる下降流も形成されるため、浮上室16全体を浮上処理に使用することが可能となる。   As shown in FIGS. 2 to 4, a plurality of water collection ports 22 a formed in the water collection unit 22 are provided from the peripheral wall of the floating chamber 16 to the center (from the peripheral wall 10 a to the center of the floating tank 10). With the above configuration, the downflow of the treated water flowing from the upper portion 28a to the lower portion 28b of the levitation chamber 16 is not only the downward flow flowing along the peripheral wall of the levitation chamber 16 (the peripheral wall 10a of the levitation tank 10), but also levitated from above the peripheral wall 10a. Since the downward flow flowing toward the lower center of the chamber 16 is also formed, the entire levitation chamber 16 can be used for the levitation process.

また、集水口22aの開口方向は、浮上室16の上部28a側、下部28b側等いずれの方向であってもよい。しかし、集水口22aの開口方向を上部28a側にすると、集水部22上に沈殿する沈殿物が、集水口22aから取り込まれ易くなり、処理水の水質を悪化させる虞がある。したがって、集水口22aの開口方向は、浮上室16の下部28b側であることが好ましい。集水口22aの形状は、処理水を集水することができれば特に制限されるものではなく、例えば、円形、多角形、スリット状等が挙げられる。   The opening direction of the water collecting port 22a may be any direction such as the upper 28a side and the lower 28b side of the floating chamber 16. However, when the opening direction of the water collection port 22a is set to the upper part 28a side, the sediment that precipitates on the water collection unit 22 is likely to be taken in from the water collection port 22a, which may deteriorate the quality of the treated water. Therefore, the opening direction of the water collection port 22a is preferably on the lower portion 28b side of the floating chamber 16. The shape of the water collection port 22a is not particularly limited as long as the treated water can be collected, and examples thereof include a circular shape, a polygonal shape, and a slit shape.

流入部12は、ガイド筒30と、ガイド筒30内に設けられる導入管31と有する。導入管31には、被処理水流入管34が接続され、導入管31は浮上槽10の底部10bの中央に形成されたピット18から浮上槽10内に延設されている。被処理水流入管34には加圧水流入管36が接続されている。浮上槽10内に設けられるガイド筒30は、底部10bや、周壁10aにフレームなどで固定される。また、ガイド筒30を上方から吊り下げてもよい。ガイド筒30を設けることにより、導入管31から供給される被処理水及び加圧水を浮上槽10の中央部分から均一に流入させることができる。   The inflow portion 12 includes a guide cylinder 30 and an introduction pipe 31 provided in the guide cylinder 30. A treated water inflow pipe 34 is connected to the introduction pipe 31, and the introduction pipe 31 extends from the pit 18 formed in the center of the bottom 10 b of the levitation tank 10 into the levitation tank 10. A pressurized water inflow pipe 36 is connected to the treated water inflow pipe 34. The guide cylinder 30 provided in the floating tank 10 is fixed to the bottom 10b and the peripheral wall 10a with a frame or the like. Further, the guide tube 30 may be suspended from above. By providing the guide tube 30, the water to be treated and the pressurized water supplied from the introduction pipe 31 can be uniformly introduced from the central portion of the levitation tank 10.

本実施形態の流入部12は、浮上室16の上部28aで開口し、当該開口部から浮上室16の上部28aに(加圧水を混合させた)被処理水を供給させる。ここで、本実施形態のように流入部12が、ガイド筒30と導入管31とから構成されている場合、少なくともガイド筒30の開口部30aが上部28aで開口していればよい。本実施形態の流入部12は、必ずしもガイド筒30を備える必要はない。例えば、流入部12が導入管31のみから構成されていてもよい。この場合、導入管31の開口部31aが上部28aで開口している必要がある。   The inflow portion 12 of the present embodiment opens at the upper portion 28a of the levitation chamber 16, and supplies water to be treated (mixed with pressurized water) from the opening to the upper portion 28a of the levitation chamber 16. Here, when the inflow part 12 is comprised from the guide cylinder 30 and the introductory pipe 31 like this embodiment, the opening part 30a of the guide cylinder 30 should just open at the upper part 28a. The inflow part 12 of this embodiment does not necessarily need to be provided with the guide cylinder 30. For example, the inflow portion 12 may be configured only from the introduction pipe 31. In this case, the opening 31a of the introduction pipe 31 needs to open at the upper part 28a.

流入部12の開口部(図1ではガイド筒30の開口部30a)の位置は、浮上室16の上部28a、すなわち集水部22より垂直方向上方であれば特に制限されるものではない。しかし、流入部12の開口部の位置が液面付近にあると、流入部12の開口部から供給される被処理水が液面に噴き上げて、液面を乱し、液面に浮上した浮上物23の再沈降を招く虞がある。   The position of the opening of the inflow portion 12 (in FIG. 1, the opening 30a of the guide tube 30) is not particularly limited as long as it is vertically above the upper portion 28a of the levitation chamber 16, that is, the water collection portion 22. However, if the position of the opening of the inflow portion 12 is near the liquid level, the water to be treated supplied from the opening of the inflow portion 12 spouts up to the liquid surface, disturbs the liquid surface, and floats to the liquid surface. There is a risk of re-sedimentation of the object 23.

排出部14は、処理水取出管38、水位調整槽40、処理水排出管42を備える。処理水取出管38の一端は、集水部22に接続されており、処理水取出管38の他端は、水位調整槽40の入口に接続されている。また、水位調整槽40の出口には処理水排出管42が接続されている。   The discharge unit 14 includes a treated water extraction pipe 38, a water level adjustment tank 40, and a treated water discharge pipe 42. One end of the treated water outlet pipe 38 is connected to the water collecting section 22, and the other end of the treated water outlet pipe 38 is connected to the inlet of the water level adjusting tank 40. A treated water discharge pipe 42 is connected to the outlet of the water level adjustment tank 40.

次に、本実施形態に係る浮上分離装置による運転方法の一例を説明する。まず、被処理水流入管34から被処理水を流入させると共に、加圧水流入管36から高圧下で気体を溶解させた加圧水を流入させる。加圧水は、処理水の一部を加圧タンクに導入し、ここにおいて高圧下で空気を溶解させて生成する。   Next, an example of the operation method by the levitation separator according to the present embodiment will be described. First, water to be treated is caused to flow in from the water to be treated inflow pipe 34 and pressurized water in which a gas is dissolved under high pressure from the pressure water inflow pipe 36. Pressurized water is generated by introducing a portion of treated water into a pressurized tank, where air is dissolved under high pressure.

加圧水流入管36を通る加圧水は、被処理水流入管34を通る被処理水に混合される。被処理水及び加圧水からなる混合液は被処理水流入管34から、導入管31に供給される。被処理水及び加圧水は導入管31を介し、導入管31の開口部31aからガイド筒30内に供給される。ガイド筒30内に供給された(浮上室16の液面に向かって上昇する)被処理水及び加圧水は、ガイド筒30の開口部30aから浮上室16の上部28aに流入する。浮上室16の上部28a(及びガイド筒30内)は、大気圧状態であるため、加圧水に溶解していた気体が気泡として析出し、被処理水中の被処理物質(SS成分、油分等)に付着し、被処理物質が浮上分離される。このようにして浮上した被処理物質(浮上物23)は、浮上物スキマー20により浮上物ポット24に収集される。浮上物ポット24に収集された浮上物23は、浮上物ポット24の排出口に接続された浮上物排出管44(図1に示す)から排出される。気泡の発生方法としては、上記のように加圧水を用いる方法に制限されるものではなく、その他に、例えば、界面活性剤等の気泡発生剤を被処理水に添加する方法等であってもよい。また、被処理水自体を空気溶解タンクに導入し、ここで被処理水に直接空気を溶解する全量加圧方式を採用してもよい。   The pressurized water that passes through the pressurized water inflow pipe 36 is mixed with the treated water that passes through the treated water inflow pipe 34. A mixed liquid comprising treated water and pressurized water is supplied from the treated water inflow pipe 34 to the introduction pipe 31. The water to be treated and the pressurized water are supplied into the guide tube 30 from the opening 31 a of the introduction pipe 31 through the introduction pipe 31. The treated water and pressurized water supplied into the guide cylinder 30 (ascending toward the liquid level of the levitation chamber 16) flow into the upper portion 28a of the levitation chamber 16 from the opening 30a of the guide cylinder 30. Since the upper part 28a of the levitation chamber 16 (and in the guide cylinder 30) is in an atmospheric pressure state, the gas dissolved in the pressurized water is precipitated as bubbles, and becomes a substance to be treated (SS component, oil, etc.) in the treated water. It adheres and the material to be treated floats and is separated. The material to be treated (the levitated material 23) that has floated in this manner is collected in the levitated material pot 24 by the levitated material skimmer 20. The float 23 collected in the float pot 24 is discharged from a float discharge pipe 44 (shown in FIG. 1) connected to the discharge port of the float pot 24. The method of generating bubbles is not limited to the method using pressurized water as described above, but may be a method of adding a bubble generating agent such as a surfactant to the water to be treated. . Alternatively, a whole-pressure method may be employed in which the water to be treated itself is introduced into an air dissolution tank and air is directly dissolved in the water to be treated.

ガイド筒30の開口部30aから浮上槽10の上部28aに供給された被処理水が、浮上室16の周壁(浮上槽10の周壁10a)に達すると、周壁10aに沿って流れる下降流となる。そこで、本実施形態では、ガイド筒30の開口部30aを浮上室16の上部28aの中心部において垂直方向上方に開口させるとともに、周壁10aを円筒状にすることが好ましい。上記構成によって、被処理水は放射状に拡がりながら流れる分散流れとなって、周壁10aに達する。その結果、開口部30aから供給された被処理水の流れは、浮上槽10の周壁10aに到達するまでに緩やかになり、周壁10aに沿って流れる被処理水の下降流も緩やかになる。したがって、急速な下降流によって生じる処理水の水質の悪化は抑制される。   When the water to be treated supplied from the opening 30a of the guide cylinder 30 to the upper portion 28a of the levitation tank 10 reaches the peripheral wall of the levitation chamber 16 (the peripheral wall 10a of the levitation tank 10), it becomes a downward flow that flows along the peripheral wall 10a. . Therefore, in the present embodiment, it is preferable that the opening 30a of the guide cylinder 30 is opened vertically upward at the center of the upper portion 28a of the floating chamber 16, and the peripheral wall 10a is cylindrical. With the above configuration, the water to be treated becomes a dispersed flow that flows while spreading radially and reaches the peripheral wall 10a. As a result, the flow of the water to be treated supplied from the opening 30a becomes gentle before reaching the peripheral wall 10a of the levitation tank 10, and the downward flow of the water to be treated flowing along the peripheral wall 10a also becomes gentle. Therefore, deterioration of the quality of the treated water caused by the rapid downward flow is suppressed.

ここで、流入部12の開口部(図1ではガイド筒30の開口部30a)の形状は特に制限されるものではないが、流入部12の開口部から供給される被処理水が放射状に分散し易くなる点で、その上部において上方に向けてテーパ状に広がっていることが好ましい。また、流入部12の開口部の水平断面積は、特に制限されるものではないが、流入部12を流れる被処理水の流速を適切に制御することができる点で、好ましくは浮上室16の水平断面積の1/30〜1/3の範囲、より好ましくは浮上室16の水平断面積の1/20〜1/8の範囲とするのがよい。流入部12の開口部の水平断面積が浮上室16の水平断面積の1/30より小さいと、流入部12から出る際の被処理水の流速が速くなるため、被処理水は浮上室16の表層部を流れ、開口部から周壁10aに向かって流れる被処理水の流速も速くなり、浮上室16の液面に乱れが生じやすく、液面に浮上した浮上物23の再沈降を招く虞がある。また、流入部12の開口部の水平断面積が浮上室16の水平断面積の1/3より大きいと、浮上室16の面積を確保することが難しくなり、浮上分離装置の水面積負荷が大きくなり、効率的な浮上処理が行えなくなる。   Here, the shape of the opening of the inflow portion 12 (in FIG. 1, the opening 30a of the guide tube 30) is not particularly limited, but the water to be treated supplied from the opening of the inflow portion 12 is dispersed radially. From the viewpoint of facilitating this, it is preferable that the upper portion of the upper portion spreads in a tapered shape. In addition, the horizontal cross-sectional area of the opening of the inflow portion 12 is not particularly limited, but is preferably a floating chamber 16 in that the flow rate of water to be treated flowing through the inflow portion 12 can be appropriately controlled. It is good to set it as the range of 1 / 20-1 / 8 of the horizontal cross-sectional area of the horizontal cross-sectional area of the horizontal cross-sectional area of the horizontal chamber of the floating chamber 16 more preferably. When the horizontal cross-sectional area of the opening of the inflow portion 12 is smaller than 1/30 of the horizontal cross-sectional area of the levitation chamber 16, the flow rate of the water to be treated when exiting the inflow portion 12 is increased. The flow rate of the water to be treated flowing from the opening toward the peripheral wall 10a is also increased, the liquid level of the floating chamber 16 is likely to be disturbed, and the floating object 23 that has floated on the liquid level may be re-settling. There is. Moreover, if the horizontal cross-sectional area of the opening of the inflow portion 12 is larger than 1/3 of the horizontal cross-sectional area of the floating chamber 16, it becomes difficult to secure the area of the floating chamber 16, and the water area load of the floating separator is large. Therefore, efficient levitation processing cannot be performed.

本実施形態において、浮上室16の上部28aに存在する処理水は、浮上室16の周壁から中央に亘って形成された集水口22aに向かって流れる。そのため、上部28aから下部28bへ流れる処理水の下降流は、浮上室16の周壁(浮上槽10の周壁10a)に沿って流れる下降流だけでなく、周壁10a上方から中央下方に向かって流れる下降流も形成される。その結果、浮上室16の上部28a全体を浮上分離処理に使用することが可能となり、処理能力を向上させることができる。また、気泡が付着しても浮上することが出来ない比重の重い被処理物質(沈殿物)や、気泡が十分付着しなかった被処理物質が、周壁10a下方の底部に局所的に沈殿することがなく、底部全体に沈殿する。このように、被処理物質の除去において、浮上室16全体を有効に使用することができるため、装置の小型化、浮上分離装置の高速処理が可能となる。   In the present embodiment, the treated water existing in the upper portion 28a of the floating chamber 16 flows toward the water collection port 22a formed from the peripheral wall of the floating chamber 16 to the center. Therefore, the downflow of the treated water flowing from the upper portion 28a to the lower portion 28b is not only the downward flow flowing along the peripheral wall of the levitation chamber 16 (the peripheral wall 10a of the levitation tank 10), but also the downward flow flowing from the upper peripheral wall 10a toward the lower center. A flow is also formed. As a result, the entire upper portion 28a of the levitation chamber 16 can be used for the levitation separation process, and the processing capacity can be improved. In addition, a material to be treated (precipitate) having a high specific gravity that cannot float even if bubbles are attached, or a material to be treated to which bubbles are not sufficiently adhered are locally precipitated at the bottom below the peripheral wall 10a. And settles to the entire bottom. As described above, since the entire floating chamber 16 can be used effectively in removing the substance to be processed, the apparatus can be downsized and the high-speed processing of the floating separation apparatus can be performed.

浮上室16の上部28aの処理水が集水口22aから集水される際には、通水部33を通り、浮上室16の下部28bに供給される。なお、集水口22aが上部28a側に形成されている場合には、浮上室16の上部28aの処理水の一部は、通水部33を通過することなく、集水口22aから集水される。ここで、通水部33の水平断面積と通水部33が形成されている浮上室16の水平断面積との比(通水部33の水平断面積/浮上室16の水平断面積)は、0.24〜0.75の範囲であることが好ましく、0.4〜0.6の範囲であることがより好ましい。通水部33の水平断面積/浮上室16の水平断面積が、0.24より小さいと、浮上分離装置の水面積負荷を上げた場合、通水部33を通る処理水の流速が速くなりすぎるため、上部28a側の被処理物質が下部28b側へ流れ込み、集水口22aに取り込まれ、処理水の水質を悪化させる場合がある。また、通水部33の水平断面積/浮上室16の水平断面積が、0.75より大きいと、浮上分離装置の水面積負荷を上げた場合、上部28aから下部28bへ流れる処理水の下降流のうち、周壁10a上方から中央下方に向かって流れる下降流が形成され難くなるため、浮上室16全体を浮上分離処理に使用することが困難となり、処理能力が低下する場合がある。   When the treated water in the upper portion 28a of the floating chamber 16 is collected from the water collection port 22a, it passes through the water passage 33 and is supplied to the lower portion 28b of the floating chamber 16. In addition, when the water collection port 22a is formed in the upper part 28a side, a part of the treated water of the upper part 28a of the floating chamber 16 is collected from the water collection port 22a without passing the water flow part 33. . Here, the ratio of the horizontal cross-sectional area of the water flow portion 33 and the horizontal cross-sectional area of the floating chamber 16 where the water flow portion 33 is formed (the horizontal cross-sectional area of the water flow portion 33 / the horizontal cross-sectional area of the floating chamber 16) is , Preferably in the range of 0.24 to 0.75, and more preferably in the range of 0.4 to 0.6. If the horizontal cross-sectional area of the water flow portion 33 / the horizontal cross-sectional area of the levitation chamber 16 is smaller than 0.24, the flow rate of the treated water passing through the water flow portion 33 is increased when the water area load of the levitation separator is increased. Therefore, the material to be treated on the upper 28a side flows into the lower 28b side and is taken into the water collecting port 22a, which may deteriorate the quality of the treated water. Further, if the horizontal cross-sectional area of the water flow section 33 / the horizontal cross-sectional area of the levitation chamber 16 is larger than 0.75, when the water area load of the levitation separator is increased, the treated water flowing from the upper part 28a to the lower part 28b is lowered. Of the flow, it is difficult to form a downward flow that flows from the upper part of the peripheral wall 10a to the lower part of the center, so that it becomes difficult to use the entire floating chamber 16 for the floating separation process, and the processing capacity may be reduced.

集水口22aから集水された処理水は、集水管29内を通り、処理水取出管38に供給される。そして、処理水は、処理水取出管38を通り、水位調整槽40に供給される。水位調整槽40には可動堰41が設けられている。この可動堰41の高さを調整することで、浮上室16における水位を調整でき、浮上槽10の水位が浮上物23の浮上物ポット24への排出に適した水位に調整される。そして、処理水が水位調整槽40の出口から処理水排出管42へ排出される。なお、可動堰41を間欠的に上昇させ、これによって浮上室16の液面にある浮上物23を浮上物ポット24へオーバーフローさせることも可能である。   The treated water collected from the water collection port 22 a passes through the water collection pipe 29 and is supplied to the treated water extraction pipe 38. Then, the treated water passes through the treated water take-out pipe 38 and is supplied to the water level adjustment tank 40. A movable weir 41 is provided in the water level adjustment tank 40. By adjusting the height of the movable weir 41, the water level in the floating chamber 16 can be adjusted, and the water level in the floating tank 10 is adjusted to a water level suitable for discharging the floating material 23 to the floating material pot 24. Then, the treated water is discharged from the outlet of the water level adjustment tank 40 to the treated water discharge pipe 42. It is also possible to raise the movable weir 41 intermittently, thereby causing the floating material 23 on the liquid surface of the floating chamber 16 to overflow into the floating material pot 24.

図6は、本発明の他の実施形態に係る浮上分離装置の構成の一例を示す模式断面図である。図7は、本発明の他の実施形態に係る浮上分離装置の構成の一例を示す模式上面図である。図6に示す浮上分離装置2において、浮上槽50の周壁50aは矩形であり、浮上槽50内は、上部開放の隔壁50bにより、流入室52(流入部)、浮上室54に区画されている。図6に示すように、浮上室54は、集水部56により垂直方向上部28a及び下部28bに区画されると共に、図7に示すように上部28aと下部28bとの間を処理水が通水する通水部58を有する。流入室52には、被処理水流入管34が接続されている。浮上室54の底部には、被処理物質のうちの沈殿物を溜めるピット18が設けられており、ピット18の沈殿物排出口には沈殿物排出管19が接続されている。排出部14は、処理水取出管38、水位調整槽40、処理水排出管42を備えており、処理水取出管38の一端は、集水部56に接続され、処理水取出管38の他端は、水位調整槽40の入口に接続されている。また、水位調整槽40の出口には処理水排出管42が接続されている。   FIG. 6 is a schematic cross-sectional view showing an example of the configuration of a levitation separator according to another embodiment of the present invention. FIG. 7 is a schematic top view showing an example of the configuration of a flotation separation apparatus according to another embodiment of the present invention. In the levitation separation apparatus 2 shown in FIG. 6, the peripheral wall 50 a of the levitation tank 50 is rectangular, and the inside of the levitation tank 50 is partitioned into an inflow chamber 52 (inflow portion) and a levitation chamber 54 by an upper open partition 50 b. . As shown in FIG. 6, the levitation chamber 54 is partitioned into a vertical upper part 28a and a lower part 28b by a water collecting part 56, and treated water flows between the upper part 28a and the lower part 28b as shown in FIG. It has the water flow part 58 to do. The treated water inflow pipe 34 is connected to the inflow chamber 52. A pit 18 is provided at the bottom of the levitation chamber 54 to collect deposits of the material to be treated. A deposit discharge pipe 19 is connected to the deposit outlet of the pit 18. The discharge unit 14 includes a treated water extraction pipe 38, a water level adjustment tank 40, and a treated water discharge pipe 42, and one end of the treated water extraction pipe 38 is connected to the water collection unit 56. The end is connected to the inlet of the water level adjustment tank 40. A treated water discharge pipe 42 is connected to the outlet of the water level adjustment tank 40.

集水部56は、下部28b側に形成された集水口56aを有する直線上の集水管60を浮上室54の長手方向に所定の間隔をあけて複数配置させることにより、形成される。集水管60同士の隙間、集水管60と周壁50aとの隙間が、上部28aと下部28bとの間を処理水が通水する通水部58となる。集水部56は、集水管60内を通る処理水を集合させる集合管62を備えており、該集合管62に処理水取出管38が接続されている。集水管60は、浮上槽50外から浮上槽50内に延設され、浮上槽50外で集合管62に接続されているが、集合管62を浮上槽50内、すなわち浮上室54に設けて、浮上室54で集水管60と集合管62とが接続されていてもよい。なお、上記でも説明したように、集水部56は、浮上室54を上部28a及び下部28bで通水可能なように区画する構成であれば、集水部56の構成は上記に制限されるものではない。   The water collecting part 56 is formed by arranging a plurality of straight water collecting pipes 60 each having a water collecting port 56a formed on the lower part 28b side at predetermined intervals in the longitudinal direction of the floating chamber 54. A gap between the water collecting pipes 60 and a gap between the water collecting pipe 60 and the peripheral wall 50a serve as a water passing portion 58 through which treated water flows between the upper portion 28a and the lower portion 28b. The water collecting section 56 includes a collecting pipe 62 that collects treated water passing through the collecting pipe 60, and the treated water take-out pipe 38 is connected to the collecting pipe 62. The water collecting pipe 60 extends from the outside of the floating tank 50 into the floating tank 50 and is connected to the collecting pipe 62 outside the floating tank 50, but the collecting pipe 62 is provided in the floating tank 50, that is, in the floating chamber 54. The water collecting pipe 60 and the collecting pipe 62 may be connected to each other in the floating chamber 54. As described above, the configuration of the water collecting portion 56 is limited to the above as long as the water collecting portion 56 is configured to partition the floating chamber 54 so that water can be passed through the upper portion 28a and the lower portion 28b. It is not a thing.

図6に示す浮上分離装置2には、浮上室54の底部に沈殿した沈殿物を掻き寄せる沈殿物掻き寄せ機63、不図示であるが集水部上に沈殿した沈殿物を掻き取り通水部から下方に排出する集水部スクレーパー、浮上物スキマーが設けられる。   In the levitation separating apparatus 2 shown in FIG. 6, a sediment squeezing machine 63 that squeezes the sediment deposited on the bottom of the levitation chamber 54, and scrapes the sediment deposited on the water collecting unit (not shown). A water collecting unit scraper and a levitated skimmer are provided to discharge downward from the unit.

図6に示すように、沈殿物掻き寄せ機63は、浮上室54の底部で所定の間隔を隔てて配置される2つのローラ65a,65bと、これらのローラ65a,65bに掛けられる無端ベルト66と、無端ベルト66上に形成される羽根等のスクレーパー部とを備える。また、2つのローラ65a,65bのうちの一方のローラには、不図示のモータが接続される。モータが駆動することにより、ローラ65a,65b、無端ベルト66が回転される。そして、無端ベルト66上に形成されたスクレーパー部により、浮上室54の底部に沈殿した沈殿物が、ピット18に掻き寄せされる。不図示の集水部スクレーパー、浮上物スキマーは、上記説明した沈殿物掻き寄せ機63と同様の構成を有するものが、それぞれ集水部上、浮上室の液面上に設置されている。なお、沈殿物掻き寄せ機63は、浮上室54の底部を掻き寄せることができるもの、集水部スクレーパーは、集水部56上の沈殿物を掻き寄せ、通水部58から下方に排出することができるもの、浮上物スキマーは、浮上物を掻き寄せることができるものであれば、必ずしも上記構成に制限されるものではない。   As shown in FIG. 6, the sediment scraper 63 includes two rollers 65a and 65b arranged at a predetermined interval at the bottom of the floating chamber 54, and an endless belt 66 hung on these rollers 65a and 65b. And a scraper portion such as a blade formed on the endless belt 66. A motor (not shown) is connected to one of the two rollers 65a and 65b. When the motor is driven, the rollers 65a and 65b and the endless belt 66 are rotated. Then, by the scraper portion formed on the endless belt 66, the sediment deposited on the bottom of the floating chamber 54 is scraped to the pit 18. A water collecting unit scraper and a float skimmer (not shown) having the same configuration as the above-described sediment scraper 63 are installed on the water collecting unit and the liquid level of the floating chamber, respectively. The sediment scraper 63 can scrape the bottom of the floating chamber 54, and the water collecting unit scraper scrapes the sediment on the water collecting unit 56 and discharges it downward from the water flow unit 58. The float skimmer is not necessarily limited to the above configuration as long as the float skimmer can scrape the float.

従来は、沈殿物を清掃するため定期的なメンテナンスが必要であったが、沈殿物掻き寄せ機63、不図示の集水部スクレーパーを備えることにより、浮上室54の底部、集水部56上に沈殿した沈殿物を清掃するためのメンテナンス回数を減らし、装置の長期連続運転が可能となる。   Conventionally, periodic maintenance is required to clean the sediment. However, by providing the sediment scraper 63 and a water collecting unit scraper (not shown), the bottom of the floating chamber 54 and the water collecting unit 56 are provided. This reduces the number of maintenance operations for cleaning the sediment that has settled on the surface, and enables long-term continuous operation of the apparatus.

次に、本実施形態に係る浮上分離装置による運転方法の一例を説明する。浮上分離装置2において、被処理水流入管34から流入室52に流入した加圧水及び被処理水は、液面に向かって上昇して、流入室52の開口部52aから、隣接する浮上室54の上部28aに流入する。浮上室54の上部28aでは、被処理水中の被処理物質が浮上物として液面上に浮かび、浮上物が除去された処理水は集水部56に設けられた集水口56aに向かって流れる。   Next, an example of the operation method by the levitation separator according to the present embodiment will be described. In the levitation separator 2, the pressurized water and the water to be treated that have flowed into the inflow chamber 52 from the to-be-treated water inflow pipe 34 rise toward the liquid surface, and the upper portion of the adjacent floating chamber 54 from the opening 52 a of the inflow chamber 52. It flows into 28a. In the upper part 28 a of the levitation chamber 54, the substance to be treated in the treated water floats on the liquid surface as a floating substance, and the treated water from which the floating substance has been removed flows toward the water collection port 56 a provided in the water collection unit 56.

浮上室54の上部28aに存在する処理水は、浮上室54の周壁(浮上槽50の周壁50a)から中央に亘って形成された集水口56aに向かって流れる。そのため、上部28aから下部28bへ流れる処理水の下降流は、隔壁50bと反対側の周壁50aに沿って流れる下降流だけでなく、隔壁50bと反対側の周壁50a上方から中央下方、周壁50a上方から隔壁50b下方に向かって流れる下降流も形成される。その結果、浮上室54の上部28a全体を浮上分離処理に使用すること、沈殿物を下部28bの底部全体に沈殿させることができることにより、被処理物質の除去において、浮上槽50全体を有効に使用することができるため、装置の小型化、浮上分離装置の高速処理が可能となる。   The treated water present in the upper part 28a of the floating chamber 54 flows from the peripheral wall of the floating chamber 54 (the peripheral wall 50a of the floating tank 50) toward the water collection port 56a formed from the center. Therefore, the downflow of the treated water flowing from the upper part 28a to the lower part 28b is not only a downward flow flowing along the peripheral wall 50a opposite to the partition wall 50b, but also from the upper part of the peripheral wall 50a opposite to the partition wall 50b to the lower center and upper part of the peripheral wall 50a. A downward flow that flows downward from the partition wall 50b is also formed. As a result, the entire upper part 28a of the levitation chamber 54 can be used for the levitation separation process, and the sediment can be settled on the entire bottom part of the lower part 28b. Therefore, it is possible to downsize the apparatus and perform high-speed processing of the floating separation apparatus.

図8は、本発明の他の実施形態に係る浮上分離装置の構成の一例を示す模式断面図である。図8に示す浮上分離装置3は、図1に示す浮上分離装置1に沈殿物掻き寄せ機64、集水部スクレーパー68を設けたものである。図8に示す浮上分離装置3において、図1に示す浮上分離装置1と同様の構成については、同一の符合を付し、その説明を省略する。   FIG. 8 is a schematic cross-sectional view showing an example of the configuration of a flotation separation apparatus according to another embodiment of the present invention. The floating separator 3 shown in FIG. 8 is obtained by providing the sediment separator 64 and the water collecting unit scraper 68 in the floating separator 1 shown in FIG. In the levitation separator 3 shown in FIG. 8, the same components as those of the levitation separator 1 shown in FIG.

沈殿物掻き寄せ機64は、浮上室16の底部(浮上槽10の底部10b)に沈殿した沈殿物を掻き寄せるためのものである。沈殿物掻き寄せ機64はガイド筒30に取り付けられると共に、支持体69により沈殿物掻き寄せ機64の角度調整、補強がなされている。そして、ガイド筒30は、モータ26のシャフトに取り付けられ、モータ26の駆動により回転される。すなわち、沈殿物掻き寄せ機65はモータ26の駆動により、ガイド筒30と一体に回転される。沈殿物掻き寄せ機64が回転することにより、底部10bに沈殿した沈殿物が掻き寄せられ、ピット18に集められ、沈殿物排出管19から排出される。なお、この沈殿物掻き寄せ機64は、羽根、螺旋羽根等のスクレーパー部を有しており、このスクレーパー部によって内側方向に沈殿物を掻き寄せる。   The sediment scraper 64 is for scraping the sediment deposited on the bottom portion of the floating chamber 16 (the bottom portion 10b of the floating tank 10). The sediment scraper 64 is attached to the guide cylinder 30, and the angle of the sediment scraper 64 is reinforced by the support 69. The guide cylinder 30 is attached to the shaft of the motor 26 and is rotated by driving the motor 26. That is, the sediment scraper 65 is rotated integrally with the guide cylinder 30 by driving the motor 26. As the sediment scraper 64 rotates, the sediment deposited on the bottom 10 b is scraped, collected in the pit 18, and discharged from the sediment discharge pipe 19. In addition, this sediment scraper 64 has scraper parts, such as a blade | wing and a spiral blade, and scrapes a sediment inward by this scraper part.

ここで、従来は、沈殿物を清掃するため定期的なメンテナンスが必要であったが、沈殿物掻き寄せ機64を設けることにより、沈殿物を効率的に排出することができるため、メンテナンス回数を減らし、装置の長期連続運転が可能となる。   Here, in the past, periodic maintenance was required to clean the sediment. However, by providing the sediment scraper 64, the sediment can be efficiently discharged, so the number of maintenance times is reduced. The system can be operated continuously for a long time.

集水部スクレーパー68は、集水部22上に沈殿した沈殿物を掻き取り、通水部から下方に落下排出するためのものである。集水部スクレーパー68は、ガイド筒30に取り付けられており、モータ26の駆動により、ガイド筒30と一体に回転される。集水部スクレーパー68が回転することにより、集水部22上に沈殿した沈殿物が掻き取られ、通水部から沈殿物が排出される。集水部スクレーパー68を設けることにより、集水部22を清掃するためのメンテナンス回数を減らし、装置の長期連続運転が可能となる。集水部スクレーパー68も羽根等を有するが、この羽根は、沈殿物を半径方向に輸送する必要はない。なお、浮上物スキマー20、沈殿物掻き寄せ機64、集水部スクレーパー68の回転数は同一でなく、それぞれ異ならせてもよい。しかし、同一回転数とすれば、減速機構等が不要で、駆動機構を簡単にできる。特に、対象物に応じて、羽根の傾斜を適切なものに設定することが好適である。   The water collection unit scraper 68 is for scraping the sediment precipitated on the water collection unit 22 and dropping it downward from the water flow unit. The water collecting unit scraper 68 is attached to the guide cylinder 30 and is rotated integrally with the guide cylinder 30 by driving of the motor 26. As the water collecting unit scraper 68 rotates, the sediment deposited on the water collecting unit 22 is scraped off and discharged from the water passing unit. By providing the water collecting unit scraper 68, the number of maintenance operations for cleaning the water collecting unit 22 is reduced, and the apparatus can be operated continuously for a long time. The catchment scraper 68 also has blades or the like, but the blades do not have to transport sediment in the radial direction. Note that the rotational speeds of the levitated skimmer 20, the sediment scraper 64, and the water collecting unit scraper 68 are not the same, and may be different from each other. However, if the rotation speed is the same, a speed reduction mechanism or the like is unnecessary, and the drive mechanism can be simplified. In particular, it is preferable to set the blade inclination to an appropriate value according to the object.

以下、実施例および比較例を挙げ、本発明をより具体的に詳細に説明するが、本発明は、以下の実施例に限定されるものではない。   Hereinafter, although an example and a comparative example are given and the present invention is explained more concretely in detail, the present invention is not limited to the following examples.

下記の実施例及び比較例で使用した試験装置の構成を説明する。図9は、実施例及び比較例で用いた試験装置の構成を示す模式断面図である。図10は、実施例及び比較例で用いた試験装置の構成を示す模式上面図である。図9,10に示す試験装置4の浮上室54、流入室52、集水部56、排出部14の構成は、図6,7に示す浮上分離装置2と同様の構成である。集水部56を構成する集水管60の数は、実施例及び比較例で異なるが、浮上室54の長手方向に沿って、等間隔で最大13本配置させることができる。   The configuration of the test apparatus used in the following examples and comparative examples will be described. FIG. 9 is a schematic cross-sectional view showing a configuration of a test apparatus used in Examples and Comparative Examples. FIG. 10 is a schematic top view showing the configuration of the test apparatus used in Examples and Comparative Examples. The structure of the floating chamber 54, the inflow chamber 52, the water collection part 56, and the discharge part 14 of the test apparatus 4 shown in FIGS. 9 and 10 is the same as that of the floating separation apparatus 2 shown in FIGS. Although the number of the water collecting pipes 60 constituting the water collecting portion 56 differs between the example and the comparative example, a maximum of 13 water collecting pipes 60 can be arranged at equal intervals along the longitudinal direction of the floating chamber 54.

(実施例1)
図9,10の試験装置4において、集水管60のNo.1,6,11(図10に示す)に集水管60を配置し、下記の条件で被処理水の浮上分離処理を行い、浮上分離後の処理水のSS濃度(mg/L)を測定した。浮上分離装置に供給する被処理水は、予め凝集処理槽(サイズ:1000L、1000mmΦ×高さ1400mm)で凝集処理したものを用いた。実施例1で使用した集水管の数、通水部の水平断面積/浮上室の水平断面積、各LVに基づくSS濃度の結果を表1にまとめた。
<浮上分離装置サイズ>
浮上室:長さ(D):1200mm、幅(W):500mm、高さ(H)1500mm
上部:高さ(H1)800mm、下部:高さ(H2)500mm
集水管:65A(外径=76mm)
集水口:10mmΦ (集水口の個数は集水口1個あたり0.75m/hrとなるように調整した)
<試験条件>
被処理水:戸田市工業用水にカオリンを10mg/L、フミンを1mg/L添加したもの
凝集処理時に用いた凝集剤:ポリ塩化アルミニウム(PAC)を30mg/L添加
凝集時の被処理水pH:7(pH調整剤としてHCl、NaOHを添加)
被処理水流量:6〜18m/hr
水平断面積に対する処理水量(線速度LV):10、20、30m/h
Example 1
In the test apparatus 4 of FIGS. 1, 6 and 11 (shown in FIG. 10), the water collecting pipe 60 was placed, the separation treatment of the water to be treated was performed under the following conditions, and the SS concentration (mg / L) of the treated water after the floating separation was measured. . The water to be treated supplied to the levitation separator was previously agglomerated in a flocculation tank (size: 1000 L, 1000 mmΦ × height 1400 mm). Table 1 summarizes the results of the SS concentration based on the number of water collecting pipes used in Example 1, the horizontal cross-sectional area of the water flow section / the horizontal cross-sectional area of the floating chamber, and each LV.
<Floating separator size>
Floating chamber: Length (D): 1200 mm, Width (W): 500 mm, Height (H) 1500 mm
Upper part: Height (H1) 800mm, Lower part: Height (H2) 500mm
Catch pipe: 65A (outer diameter = 76mm)
Water collection port: 10 mmΦ (The number of water collection ports was adjusted to be 0.75 m 3 / hr per water collection port)
<Test conditions>
Water to be treated: Toda City industrial water added with 10 mg / L of kaolin and 1 mg / L of humin Coagulant used at the time of coagulation treatment: 30 mg / L of polyaluminum chloride (PAC) pH of water to be treated at the time of coagulation: 7 (Addition of HCl and NaOH as pH adjusters)
Water to be treated: 6-18m 3 / hr
Amount of treated water with respect to horizontal cross-sectional area (linear velocity LV): 10, 20, 30 m / h

(実施例2〜7)
実施例2は、集水管60のNo.2,5,8,11、実施例3は、集水管60のNo.1,3,5,7,9,11、実施例4は、集水管60のNo.1,3,5,7,8,9,11,12、実施例5は、集水管60のNo.1,3,5,6,7,8,9,10,11,12、実施例6は、集水管60のNo.1〜12、実施例7は、集水管60のNo.1〜13に集水管60を配置したこと以外は、実施例1と同様の条件で試験を行った。実施例2〜6で使用した集水管の数、通水部の水平断面積/浮上室の水平断面積、各LVに基づくSS濃度の結果を表1にまとめた。
(Examples 2 to 7)
In Example 2, the water collecting pipe 60 No. 2, 5, 8, 11 and Example 3, No. of the water collecting pipe 60. 1, 3, 5, 7, 9, 11, and Example 4, the No. 1, 3, 5, 7, 8, 9, 11, 12, and Example 5, No. 1, 3, 5, 6, 7, 8, 9, 10, 11, 12, and Example 6, No. 1 to 12 and Example 7 are Nos. The test was performed under the same conditions as in Example 1 except that the water collecting pipes 60 were disposed at 1 to 13. Table 1 summarizes the results of the SS concentration based on the number of water collecting pipes used in Examples 2 to 6, the horizontal cross-sectional area of the water flow portion / the horizontal cross-sectional area of the floating chamber, and the LVs.

(比較例1,2)
比較例1は、集水管60のNo.1、比較例2は、集水管60のNo.6に管を配置した試験装置を用いたいこと以外は、実施例1と同様の条件で試験を行った。
(Comparative Examples 1 and 2)
Comparative Example 1 is the No. of the water collecting pipe 60. No. 1 and Comparative Example 2 are No. The test was performed under the same conditions as in Example 1 except that the test apparatus in which the tube was arranged in 6 was used.

Figure 2010005520
Figure 2010005520

実施例1〜6のように、浮上室を垂直方向上部及び下部で通水可能なように区画し、集水口が浮上室の周壁(例えば、管No.1〜4、10〜13)から中央(例えば、管No.5〜9)に向かって複数形成されている装置の方が、比較例1,2のように、集水口が浮上室の周壁(管No.1)のみ又は中央(管No.6)のみに形成されている装置より、処理水のSS濃度を低下させることができた。通水部の水平断面積/浮上室の水平断面積の比が0.24〜0.75である実施例2〜6は、LVを増加させても、低いSS濃度を確保することができた。特に、通水部の水平断面積/浮上室の水平断面積の比が、0.49、0.62である実施例3,4は、LVを30に上げてもSS濃度を1未満に抑えることができた。   As in Examples 1 to 6, the floating chamber is partitioned so that water can flow through the upper and lower parts in the vertical direction, and the water collecting port is located in the center from the peripheral wall of the floating chamber (for example, pipes Nos. 1 to 4 and 10 to 13). (For example, in the case of a plurality of devices formed toward pipes Nos. 5 to 9, the water collecting port is only the peripheral wall (tube No. 1) of the floating chamber or the center (tube) as in Comparative Examples 1 and 2. The SS concentration of treated water could be reduced from the apparatus formed only in No. 6). In Examples 2 to 6 in which the ratio of the horizontal cross-sectional area of the water flow portion / the horizontal cross-sectional area of the floating chamber was 0.24 to 0.75, a low SS concentration could be secured even when the LV was increased. . In particular, in Examples 3 and 4 in which the ratio of the horizontal cross-sectional area of the water flow portion / the horizontal cross-sectional area of the floating chamber is 0.49 and 0.62, the SS concentration is suppressed to less than 1 even when the LV is increased to 30. I was able to.

下記の実施例及び比較例で使用した試験装置は、図9,10の試験装置4に図6に示す沈殿物掻き寄せ機63を設けたものである。   The test apparatus used in the following examples and comparative examples is the test apparatus 4 shown in FIGS. 9 and 10 provided with a sediment scraper 63 shown in FIG.

(実施例8〜14)
実施例8は、集水管60のNo.1,6,11、実施例9は、集水管60のNo.2,5,8,11、実施例10は、集水管60のNo.1,3,5,7,9,11、実施例11は、集水管60のNo.1,3,5,7,8,9,11,12、実施例12は、集水管60のNo.1,3,5,6,7,8,9,10,11,12、実施例13は、集水管60のNo.1〜12、実施例14は、集水管60のNo.1〜13に集水管60を配置し、沈殿部掻き寄せ機を稼働させ、浮上室の底部に沈殿した沈殿物を排出させたこと以外は、実施例1と同様の条件で試験を行った。実施例8〜14で使用した集水管の数、通水部の水平断面積/浮上室の水平断面積、各LVに基づくSS濃度の結果を表2にまとめた。
(Examples 8 to 14)
In Example 8, no. Nos. 1, 6 and 11 and Example 9 show the No. of the water collecting pipe 60. 2, 5, 8, 11 and 10th Embodiment, No. Nos. 1, 3, 5, 7, 9, 11, and Example 11 show the No. of the water collecting pipe 60. 1, 3, 5, 7, 8, 9, 11, 12, and Example 12 are Nos. 1, 3, 5, 6, 7, 8, 9, 10, 11, 12, and Example 13 are Nos. 1 to 12 and Example 14 are Nos. The test was performed under the same conditions as in Example 1 except that the water collecting pipe 60 was placed at 1 to 13 and the sedimentation part scraper was operated to discharge the sediment precipitated at the bottom of the floating chamber. Table 2 summarizes the results of the SS concentration based on the number of water collecting pipes used in Examples 8 to 14, the horizontal cross-sectional area of the water flow portion / the horizontal cross-sectional area of the floating chamber, and each LV.

Figure 2010005520
Figure 2010005520

実施例1〜7と実施例8〜14を比較すると、通水部の水平断面積/浮上室の水平断面積が同じでも、実施例8〜14のように沈殿物掻き寄せ機を設けることにより、さらに処理水のSS濃度を低下させることができた。   When Examples 1-7 are compared with Examples 8-14, even if the horizontal cross-sectional area of the water flow section / the horizontal cross-sectional area of the floating chamber are the same, by providing a sediment scraper as in Examples 8-14 Furthermore, the SS concentration of treated water could be lowered.

本実施形態に係る浮上分離装置の構成の一例を示す模式斜視図である。It is a model perspective view which shows an example of a structure of the floating separation apparatus which concerns on this embodiment. 本実施形態に係る浮上分離装置の構成の一例を示す模式断面図である。It is a schematic cross section which shows an example of a structure of the floating separation apparatus which concerns on this embodiment. 本発明の実施形態に係る浮上分離装置の構成の一例を示す模式上面図である。It is a schematic top view which shows an example of a structure of the floating separation apparatus which concerns on embodiment of this invention. 本発明の他の実施形態に係る浮上分離装置の構成の一例を示す模式上面図である。It is a schematic top view which shows an example of a structure of the floating separation apparatus which concerns on other embodiment of this invention. (A)〜(C)は、集水部を構成する集水管の径方向断面の形状の一例を示す模式図である。(A)-(C) are schematic diagrams which show an example of the shape of the radial direction cross section of the water collection pipe | tube which comprises a water collection part. 本発明の他の実施形態に係る浮上分離装置の構成の一例を示す模式断面図である。It is a schematic cross section which shows an example of a structure of the floating separation apparatus which concerns on other embodiment of this invention. 本発明の他の実施形態に係る浮上分離装置の構成の一例を示す模式上面図である。It is a schematic top view which shows an example of a structure of the floating separation apparatus which concerns on other embodiment of this invention. 本発明の他の実施形態に係る浮上分離装置の構成の一例を示す模式断面図である。It is a schematic cross section which shows an example of a structure of the floating separation apparatus which concerns on other embodiment of this invention. 実施例及び比較例で用いた試験装置の構成を示す模式断面図である。It is a schematic cross section which shows the structure of the test apparatus used by the Example and the comparative example. 実施例及び比較例で用いた試験装置の構成を示す模式上面図である。It is a model top view which shows the structure of the test apparatus used by the Example and the comparative example. 従来の浮上分離装置の構成を示す模式図である。It is a schematic diagram which shows the structure of the conventional floating separation apparatus. 特許文献1の浮上分離装置の構成を示す模式図である。It is a schematic diagram which shows the structure of the floating separation apparatus of patent document 1.

符号の説明Explanation of symbols

1,2,3,5,6 浮上分離装置、4 試験装置、10,50,70,90 浮上槽、10a,50a,90a 周壁、10b,70a 底部、12 流入部、14 排出部、16,54 浮上室、18 ピット、19 沈殿物排出管、20 浮上物スキマー、22,56 集水部、22a,56a 集水口、23 浮上物、24 浮上物ポット、26 モータ、28a 上部、28b 下部、29,60 集水管、30,78 ガイド筒、30a,31a,52a 開口部、31,80 導入管、32 堆積防止板、33,58 通水部、34,82,102 被処理水流入管、36,84,104 加圧水流入管、38 処理水取出管、40 水位調整槽、41 可動堰、42,88,106 処理水排出管、44 浮上物排出管、50b,92a,92b 隔壁、52 流入室、62 集合管、63,64 沈殿物掻き寄せ機、65a,65b ローラ、66 無端ベルト、68 集水部スクレーパー、69 支持体、72 外周壁、74 内周壁、76 処理水室、76a 下端部、86 調整槽、94 第1の室、96 第2の室、98 第3の室、100 整流板、100a 整流孔、105 空気溶解タンク、110 ポンプ、111 連通管。   1, 2, 3, 5, 6 Levitation separation device, 4 Test device, 10, 50, 70, 90 Levitation tank, 10a, 50a, 90a Perimeter wall, 10b, 70a Bottom portion, 12 Inflow portion, 14 Discharge portion, 16, 54 Floating chamber, 18 pits, 19 Sediment discharge pipe, 20 Floating matter skimmer, 22, 56 Water collecting part, 22a, 56a Water collecting port, 23 Floating object, 24 Floating substance pot, 26 Motor, 28a upper part, 28b lower part, 29, 60, water collecting pipe, 30, 78 guide tube, 30a, 31a, 52a opening, 31, 80 introduction pipe, 32 accumulation prevention plate, 33, 58 water passing part, 34, 82, 102 treated water inflow pipe, 36, 84, 104 Pressurized water inflow pipe, 38 Treated water take-out pipe, 40 Water level adjustment tank, 41 Movable weir, 42, 88, 106 Treated water discharge pipe, 44 Floating matter discharge pipe, 50b, 92a, 92b Partition wall, 52 Inflow chamber, 62 Collecting pipe, 63, 64 Sediment scraper, 65a, 65b Roller, 66 Endless belt, 68 Water collecting portion scraper, 69 Support, 72 Outer peripheral wall, 74 Inner peripheral wall, 76 Treated water chamber , 76a lower end, 86 adjustment tank, 94 first chamber, 96 second chamber, 98 third chamber, 100 rectifying plate, 100a rectifying hole, 105 air dissolution tank, 110 pump, 111 communication pipe.

Claims (5)

被処理水中の被処理物質に気泡を付着させ、被処理物質を浮上物として分離する浮上分離装置であって、
浮上室と、前記浮上室に被処理水を流入させる流入部と、前記被処理物質が分離された処理水を集水する集水口を有する集水部とを有し、
前記浮上室は、前記集水部により垂直方向上部及び下部に区画されると共に、前記上部と前記下部との間を前記処理水が通水する通水部を有し、
前記集水部に設けられる集水口は、前記浮上室の周壁から中央に亘って複数形成され、
前記流入部は、前記上部で開口し、当該開口部から前記上部に被処理水を流入させることを特徴とする浮上分離装置。
A levitation separation device that attaches bubbles to a material to be treated in water to be treated, and separates the material to be treated as a floating material
A levitation chamber, an inflow portion for allowing treated water to flow into the levitation chamber, and a water collection portion having a water collection port for collecting treated water from which the material to be treated is separated,
The levitation chamber is partitioned into a vertical upper part and a lower part by the water collecting part, and has a water flow part through which the treated water flows between the upper part and the lower part,
A plurality of water collection ports provided in the water collection unit are formed from the peripheral wall of the floating chamber to the center,
The inflow portion is opened at the upper portion, and the water to be treated is caused to flow into the upper portion from the opening portion.
請求項1記載の浮上分離装置であって、前記通水部の水平断面積/前記浮上室の水平断面積が0.24〜0.75の範囲であることを特徴とする浮上分離装置。   The levitation separator according to claim 1, wherein the horizontal cross-sectional area of the water flow portion / the horizontal cross-sectional area of the levitation chamber is in a range of 0.24 to 0.75. 請求項1記載の浮上分離装置であって、前記被処理物質のうち前記浮上室の底部に沈殿した沈殿物を掻き寄せる沈殿物掻き寄せ機を備えることを特徴とする浮上分離装置。   The levitation separation apparatus according to claim 1, further comprising a sediment squeezer that squeezes out the sediment that has settled at the bottom of the levitation chamber among the substances to be treated. 請求項3記載の浮上分離装置であって、前記被処理物質のうち前記集水部上に沈殿した沈殿物を前記通水部から下方に排出する集水部スクレーパーを備えることを特徴とする浮上分離装置。   The levitation separation apparatus according to claim 3, further comprising a water collection unit scraper that discharges a sediment precipitated on the water collection unit from the material to be treated downward from the water flow unit. Separation device. 請求項4に記載の浮上分離装置であって、前記浮上室は円筒状であり、前記流入部は、前記浮上室の中心を軸として回転可能に設けられ、
前記沈殿物掻き寄せ機及び前記集水部スクレーパーは、前記流入部に取り付けられ、前記流入部と一体に回転されることを特徴とする浮上分離装置。
The levitation separation apparatus according to claim 4, wherein the levitation chamber is cylindrical, and the inflow portion is provided to be rotatable about the center of the levitation chamber,
The sediment separator and the water collecting unit scraper are attached to the inflow part and rotated integrally with the inflow part.
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Cited By (6)

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Publication number Priority date Publication date Assignee Title
CN101811757A (en) * 2010-04-26 2010-08-25 中国科学院过程工程研究所 Air-assisted electro-coagulation algae water separation device and using method thereof
JP2012040509A (en) * 2010-08-19 2012-03-01 Kurita Water Ind Ltd Floatation separation apparatus
JP2012055829A (en) * 2010-09-09 2012-03-22 Japan Organo Co Ltd Floatation apparatus
JP2012066202A (en) * 2010-09-24 2012-04-05 Japan Organo Co Ltd Floatation separation apparatus
JP2014147854A (en) * 2013-01-31 2014-08-21 Kobelco Eco-Solutions Co Ltd Pressure floatation device
WO2021036459A1 (en) * 2019-08-30 2021-03-04 中清信益环境(南京)有限公司 Vertical-flow type precipitation and air floatation device for water treatment and working method therefor

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JP2000350983A (en) * 1999-06-09 2000-12-19 Masaharu Ishikawa Cleaning apparatus of sludge-containing sewage
JP2001300514A (en) * 2000-04-28 2001-10-30 Kurita Water Ind Ltd Pressure floatation device
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JPS4892566A (en) * 1972-03-15 1973-11-30
JPH03267190A (en) * 1990-03-15 1991-11-28 Masakatsu Ozawa Pressure floatation apparatus
JP2000350983A (en) * 1999-06-09 2000-12-19 Masaharu Ishikawa Cleaning apparatus of sludge-containing sewage
JP2001300514A (en) * 2000-04-28 2001-10-30 Kurita Water Ind Ltd Pressure floatation device
US20050115881A1 (en) * 2002-01-30 2005-06-02 Patrick Vion Installation for treating water by means of flotation

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101811757A (en) * 2010-04-26 2010-08-25 中国科学院过程工程研究所 Air-assisted electro-coagulation algae water separation device and using method thereof
JP2012040509A (en) * 2010-08-19 2012-03-01 Kurita Water Ind Ltd Floatation separation apparatus
JP2012055829A (en) * 2010-09-09 2012-03-22 Japan Organo Co Ltd Floatation apparatus
JP2012066202A (en) * 2010-09-24 2012-04-05 Japan Organo Co Ltd Floatation separation apparatus
JP2014147854A (en) * 2013-01-31 2014-08-21 Kobelco Eco-Solutions Co Ltd Pressure floatation device
WO2021036459A1 (en) * 2019-08-30 2021-03-04 中清信益环境(南京)有限公司 Vertical-flow type precipitation and air floatation device for water treatment and working method therefor

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