JPH09239400A - Sludge thickening device - Google Patents

Sludge thickening device

Info

Publication number
JPH09239400A
JPH09239400A JP8052184A JP5218496A JPH09239400A JP H09239400 A JPH09239400 A JP H09239400A JP 8052184 A JP8052184 A JP 8052184A JP 5218496 A JP5218496 A JP 5218496A JP H09239400 A JPH09239400 A JP H09239400A
Authority
JP
Japan
Prior art keywords
sludge
tank
floating
water
concentrated
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP8052184A
Other languages
Japanese (ja)
Other versions
JP3567392B2 (en
Inventor
Mamoru Minakata
護 皆方
Masaaki Yoshino
正章 吉野
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.)
Maezawa Industries Inc
Original Assignee
Maezawa Industries Inc
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 Maezawa Industries Inc filed Critical Maezawa Industries Inc
Priority to JP05218496A priority Critical patent/JP3567392B2/en
Publication of JPH09239400A publication Critical patent/JPH09239400A/en
Application granted granted Critical
Publication of JP3567392B2 publication Critical patent/JP3567392B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To provide a device which thickens the sludge in sewage, has a simple structure of the smaller number of apparatus parts, is capable of recovering the thickened sludge at a high concn., allows the simultaneous execution of a so-called deaeration treatment to remove the fine air bubbles in the thickened sludge and further, eliminates the need for frequently cleaning the inside walls of a sludge tank. SOLUTION: A sludge guide plate 8 which flocculates the floating sludge in a sludge tank 18 to be introduced with the sludge water contg. the water dissolved with pressurized air from an ejection port 10a in the sludge tank 18 is disposed into the sludge tank 18. The upper part of the sludge guide plate 8 is provided with rotary vanes 16 for splashing and deaerating the thickened and deposited sludge. The thickened sludge splashed by these vanes is recovered from a thickened sludge discharge pipe 9. The sludge tank 18 is composed to consist of two cylindrical settled sludge tank 2 and floated sludge tank 3. These sludge tanks are provided with scrapers 14 for the floating sludge, scrapers 15 for the settled sludge and scrapers 17 for the thickened sludge in order to scrape away the sludge stuck on the inside walls of these sludge tank.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は下水中の汚泥を濃縮
する装置に係り、特に汚泥に加圧微細気泡を付着させる
ことにより汚泥を加圧浮上させて濃縮する加圧浮上式汚
泥濃縮装置に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for concentrating sludge in sewage, and more particularly to a pressure-floating type sludge concentrating apparatus for concentrating the sludge under pressure by floating fine sludge on the sludge. It is a thing.

【0002】[0002]

【従来の技術】図7は従来の加圧浮上式汚泥濃縮装置の
一例を示すフロー説明図である。まず処理する原汚泥
が、原汚泥貯留タンク21からポンプにより流入管26
を通って汚泥濃縮装置23の汚泥槽24内に送り込まれ
る。このとき、流入管26途中に加圧空気溶解水タンク
22から圧縮空気を溶解した加圧空気溶解水が供給路2
7より送り込まれ、原汚泥と混合される。汚泥槽24内
において、汚泥には加圧空気溶解水中の微細気泡が付着
し、この微細気泡の浮力により浮上汚泥28となって浮
上する。浮上汚泥28は汚泥水面上部で堆積、濃縮し、
汚泥水面上部に設けられた、エンドレスチェーン等に取
り付けられた掻取り板25aを有する濃縮汚泥掻取り機
25によって矢印方向に定期的に掻き取られる。掻き取
られた浮上汚泥28は、脱気槽29に送られ、攪拌翼2
9aにより一定時間攪拌されて、付着した気泡を分離す
る、いわゆる脱気処理を行った後、濃縮汚泥として回収
される。微細気泡が付着しなかった汚泥や比重の大きい
汚泥は沈澱汚泥となって汚泥槽24の底部に設けた沈澱
汚泥掻き寄せ機30により掻き寄せられ、回収される。
また、これら浮上汚泥、沈澱汚泥から分離した加圧空気
溶解水は分離水として回収される。
2. Description of the Related Art FIG. 7 is a flow chart showing an example of a conventional pressure floating type sludge concentrating device. First, the raw sludge to be treated is pumped from the raw sludge storage tank 21 by an inflow pipe 26.
It is sent to the inside of the sludge tank 24 of the sludge concentrating device 23. At this time, the pressurized air-dissolved water obtained by dissolving the compressed air from the pressurized air-dissolved water tank 22 is supplied to the supply path 2 in the middle of the inflow pipe 26.
It is sent from 7 and mixed with raw sludge. In the sludge tank 24, fine air bubbles in the pressurized air-dissolved water adhere to the sludge, and due to the buoyancy of the fine air bubbles, the floating sludge 28 is floated. The floating sludge 28 is accumulated and concentrated on the upper surface of the sludge water surface,
The sludge is periodically scraped in the arrow direction by a concentrated sludge scraping machine 25 having a scraping plate 25a attached to an endless chain or the like provided on the upper surface of the sludge water surface. The floated sludge 28 scraped off is sent to the deaeration tank 29, and the stirring blade 2
After being stirred for a certain period of time by 9a to perform a so-called deaeration process for separating attached bubbles, the sludge is recovered as concentrated sludge. The sludge to which no fine air bubbles are attached or the sludge having a large specific gravity becomes a settled sludge and is collected and collected by the settled sludge scraper 30 provided at the bottom of the sludge tank 24.
Further, the pressurized air-dissolved water separated from the floating sludge and the settled sludge is collected as separated water.

【0003】[0003]

【発明が解決しようとする課題】上記の従来の汚泥濃縮
装置では、以下の課題を有していた。 (1)濃縮汚泥掻取り機25による濃縮汚泥の掻き取り
速度は濃縮汚泥に攪拌作用を起こさないような速度(例
えば60cm/分程度)でなければならない。なぜなら
汚泥水面上に堆積、濃縮された濃縮汚泥のうち、最も汚
泥濃度が高いのは最上部の濃縮汚泥であり、この最上部
の濃縮汚泥を掻き取るときに乱れが生じるとその下層の
濃度の低い濃縮汚泥と混合してしまい、回収する濃縮汚
泥の濃度が低くなってしまうからである。この掻き取り
速度を速くすると、汚泥の処理時間は短くなるが、掻き
取られる濃縮汚泥に乱れが生じ易くなり、回収される濃
縮汚泥の濃度は低くなり、逆に分離水中の汚泥濃度は高
くなってしまう。また、速度を遅くすると汚泥の処理時
間は長くなり、また浮上汚泥の堆積量が多くなるため装
置規模の大きいものが必要となる。その時々の原汚泥の
濃度、状態は異なるためこの掻き取り速度値の決定は非
常に困難なものとなっている。 (2)掻取り板25aの汚泥水面に対する高さ方向の位
置は、汚泥水面に近づけた方が一度に掻き取る濃縮汚泥
量が多くなり効率的であるが、大量の浮上汚泥を掻き取
る間に汚泥が攪拌されてしまうため、前記同様、回収さ
れる汚泥の濃度が低くなってしまう。この掻取り板25
aの位置設定も非常に困難なものとなる。 (3)浮上汚泥を掻き取った後に,攪拌、脱気処理工程
(29)に回すので,いわゆる汚泥の濃縮フロー効率が
悪いものとなっている。 (4)汚泥濃縮装置23内に流入した汚泥は、汚泥槽2
4の内壁に容易に付着、積層するために、頻繁に汚泥槽
24の内壁を清掃する必要があった。
The conventional sludge concentrating device described above has the following problems. (1) The scraping speed of the concentrated sludge by the concentrated sludge scraping machine 25 must be a speed (for example, about 60 cm / min) that does not cause a stirring action on the concentrated sludge. Because, of the concentrated sludge accumulated and concentrated on the water surface of the sludge, the highest concentration of sludge is the highest concentration sludge, and if turbulence occurs when scraping this highest concentration sludge, the concentration of the lower layer This is because the concentration of the concentrated sludge to be recovered will be low because it will be mixed with low concentrated sludge. If this scraping speed is increased, the sludge treatment time will be shortened, but the concentrated sludge to be scraped tends to be disturbed, the concentration of the recovered concentrated sludge will be low, and conversely the concentration of sludge in the separated water will be high. Will end up. Further, if the speed is slowed down, the sludge treatment time becomes long, and the amount of floating sludge accumulated increases, so that a large-scale device is required. It is very difficult to determine the scraping speed value because the concentration and state of the original sludge at that time are different. (2) As for the position of the scraping plate 25a in the height direction with respect to the water surface of sludge, it is more efficient to bring it closer to the water surface of sludge because the amount of concentrated sludge to be scraped at once increases, but while scraping a large amount of floating sludge. Since the sludge is agitated, the concentration of the recovered sludge becomes low as in the above. This scraping plate 25
Position setting of a is also very difficult. (3) Since the flotation sludge is scraped off and then passed to the stirring and degassing step (29), the so-called sludge concentration flow efficiency is poor. (4) The sludge that has flowed into the sludge concentrator 23 is the sludge tank 2
It was necessary to frequently clean the inner wall of the sludge tank 24 in order to easily attach and stack it on the inner wall of No. 4.

【0004】本発明は上述の課題を解消するために創案
されたものであり、簡単な構造で、濃縮汚泥を高濃度で
回収でき、また濃縮汚泥中の微細気泡を取り除くいわゆ
る脱気処理を同時に行え、さらに頻繁に汚泥槽の内壁の
清掃を行う必要のない汚泥濃縮装置を提供することを目
的としている。
The present invention was devised to solve the above-mentioned problems and has a simple structure capable of collecting concentrated sludge at a high concentration, and at the same time performing so-called degassing treatment for removing fine bubbles in the concentrated sludge. It is an object of the present invention to provide a sludge concentrating device that can be performed and does not require frequent cleaning of the inner wall of the sludge tank.

【0005】[0005]

【課題を解決するための手段】本発明は前記の目的を達
成するために以下の手段を用いた。まず、濃縮汚泥を高
濃度で回収し、また同時に濃縮汚泥の脱気を行うための
手段として、加圧空気溶解水を混入した汚泥水を導入す
る汚泥槽と、加圧空気と混和され、浮上した汚泥を汚泥
槽内において凝集させる浮上汚泥凝集手段と、汚泥水の
液面上に配設され、濃縮、堆積した汚泥を撥ね飛ばし脱
気するための回転翼とを設けた。また、前記汚泥槽を、
有底円筒形状の沈殿汚泥槽と、この沈殿汚泥槽に内嵌さ
れる有蓋円筒形状の浮上汚泥槽とにより構成し、前記沈
殿汚泥槽には沈殿汚泥を排出するための沈殿汚泥排出管
を接続し、また、前記浮上汚泥槽には脱気された汚泥を
排出するための濃縮汚泥排出管を接続した。さらに、前
記浮上汚泥凝集手段を、上下部が開放された汚泥ガイド
板により構成し、この汚泥ガイド板は、その下端部を前
記濃縮汚泥排出管の下端部より下側に位置する汚泥槽の
内壁に固定、封止すると共に、その上端部を前記汚泥水
の液面レベルより上に位置する浮上汚泥槽の内部に配設
した。また、前記浮上汚泥槽の上部に、前記回転翼を回
転駆動させるためのモータを載置した。
The present invention uses the following means in order to achieve the above object. First, as a means for collecting concentrated sludge in high concentration and simultaneously deaerating the concentrated sludge, a sludge tank that introduces sludge water mixed with pressurized air-dissolved water, and mixed with pressurized air and floated. Floating sludge aggregating means for aggregating the sludge in the sludge tank, and rotary blades disposed on the liquid surface of the sludge water for splashing and degassing the sludge concentrated and accumulated. In addition, the sludge tank,
It is composed of a bottomed cylindrical sedimentation sludge tank and a lidded cylindrical floating sludge tank that is fitted in the sedimentation sludge tank, and a sedimentation sludge discharge pipe for discharging the sedimentation sludge is connected to the sedimentation sludge tank. Further, a concentrated sludge discharge pipe for discharging deaerated sludge was connected to the floating sludge tank. Further, the floating sludge aggregating means is constituted by a sludge guide plate whose upper and lower parts are opened, and the lower end of the sludge guide plate is located below the lower end of the concentrated sludge discharge pipe. Was fixed and sealed at the same time, and its upper end was placed inside the floating sludge tank located above the liquid level of the sludge water. Further, a motor for rotating and driving the rotary blade was placed on the upper part of the floating sludge tank.

【0006】また、汚泥槽内壁清掃の頻度低減のための
手段として、前記沈殿汚泥槽に、前記モータにより回転
駆動され、沈殿汚泥槽の内壁に沿って移動して、当該沈
殿汚泥槽に付着した沈殿汚泥を掻き取る沈殿汚泥用スク
レーパを設けた。また、前記浮上汚泥槽に、前記モータ
により回転駆動され、浮上汚泥槽の内壁に沿って移動し
て、当該浮上汚泥槽に付着した濃縮汚泥を掻き取る濃縮
汚泥用スクレーパを設けた。さらに、前記汚泥ガイド板
に、前記モータにより回転駆動され、汚泥ガイド板の内
壁に沿って移動して、当該汚泥ガイド板に付着した浮上
汚泥を掻き取る浮上汚泥用スクレーパを設けた。そし
て、装置全体を部品点数の少ない簡単な構造とするた
め、前記沈殿汚泥槽と浮上汚泥槽との間に、外部に分離
水を排出するための通路を形成するように構成した。さ
らに、前記回転翼、濃縮汚泥用スクレーパ、浮上汚泥用
スクレーパおよび沈澱汚泥用スクレーパを1台のモータ
の回転軸に取り付け、それぞれ異なる回転数で回転が可
能となるようにした。
As a means for reducing the frequency of cleaning the inner wall of the sludge tank, the settling sludge tank is driven to rotate by the motor, moves along the inner wall of the settling sludge tank, and adheres to the settling sludge tank. A scraper for settling sludge for scraping off settling sludge was provided. Further, a concentrated sludge scraper, which is driven to rotate by the motor and moves along the inner wall of the floating sludge tank to scrape the concentrated sludge adhering to the floating sludge tank, is provided in the floating sludge tank. Further, the sludge guide plate was provided with a scraper for floating sludge that was driven to rotate by the motor and moved along the inner wall of the sludge guide plate to scrape the floating sludge adhering to the sludge guide plate. Then, in order to make the entire apparatus a simple structure with a small number of parts, a passage for discharging separated water to the outside is formed between the sedimentation sludge tank and the floating sludge tank. Further, the rotary blade, the concentrated sludge scraper, the floating sludge scraper, and the settled sludge scraper are attached to the rotary shaft of one motor so that they can rotate at different rotational speeds.

【0007】また、浮上汚泥の浮上効率を上げる目的の
ため、加圧空気溶解水を作用させた汚泥水を汚泥槽内に
噴出させる噴出口近傍に、前記汚泥水の流れを上部方向
に導くための流れ方向規制部材を設けた。特に、この流
れ方向規制部材を前記噴出口を囲む、上部が開口し、周
側面および底面が閉塞された円筒形状の部材とした。
Further, in order to improve the floating efficiency of the floating sludge, in order to guide the sludge water flow upward in the vicinity of the jet port for jetting the sludge water to which the pressurized air-dissolved water acts into the sludge tank. The flow direction regulating member of No. 1 is provided. In particular, the flow direction regulating member is a cylindrical member that surrounds the jet outlet and has an open upper portion and closed peripheral side surfaces and bottom surface.

【0008】[0008]

【発明の実施の形態】本発明の実施の形態を図面を参照
して説明する。図1の(a)および(b)は本発明に係
る汚泥濃縮装置の上面図および側面図、図2は図1にお
けるA−A断面図、図3は図1におけるB−B断面図、
図4は図1におけるC−C断面図、図5は汚泥濃縮装置
の全体斜視図、図6の(a)は同要部説明図であり、
(b)は他の実施形態における一部説明図である。これ
らの図中,符号1は汚泥濃縮装置を示す。この汚泥濃縮
装置1は、処理する原汚泥を圧縮空気を水に溶解した加
圧空気溶解水と共に噴出口10aから取り込み、汚泥槽
18内部で汚泥を浮上、濃縮させ、その濃縮汚泥を濃縮
汚泥排出管9へ、沈澱汚泥は沈澱汚泥排出管4へ、浮上
または沈澱した汚泥から分離した分離水を分離水排出管
7へ、それぞれ排出させるものである。
BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of the present invention will be described with reference to the drawings. 1A and 1B are a top view and a side view of a sludge concentrating apparatus according to the present invention, FIG. 2 is a sectional view taken along line AA in FIG. 1, and FIG. 3 is a sectional view taken along line BB in FIG.
4 is a sectional view taken along line CC in FIG. 1, FIG. 5 is an overall perspective view of the sludge concentrating device, and FIG.
(B) is a partial explanatory view in other embodiments. In these figures, reference numeral 1 indicates a sludge concentrator. This sludge concentrating device 1 takes in raw sludge to be treated together with pressurized air dissolved water in which compressed air is dissolved in water from a jet port 10a, floats sludge in a sludge tank 18 and concentrates the sludge, and discharges the concentrated sludge. The settling sludge is discharged to the pipe 9 to the settling sludge discharge pipe 4, and the separated water separated from the floated or settled sludge to the separated water discharge pipe 7.

【0009】汚泥槽18は、2つの筐体部材である沈澱
汚泥槽2および浮上汚泥槽3により構成される。沈澱汚
泥槽2は上部が開口した有底円筒形状の部材で、その下
方部において下部が狭まったテーパ形状を成し、底部に
おいて再び径の小さい円筒形状を形成している。この底
部円筒部の側壁には沈澱汚泥を排出させるための孔2a
が穿設され、沈澱汚泥排出管4が接続されている。沈澱
汚泥槽2の上縁周囲には、分離水がその上縁から溢れ出
たときの受けとして、断面L字状の分離水受枠5が全周
にわたって取り付けられている。この分離水受枠5の一
部は筐体6を形成しており、その底部には孔6aが穿設
され、分離水排出管7が接続されている。
The sludge tank 18 is composed of two housing members, a settling sludge tank 2 and a floating sludge tank 3. The settling sludge tank 2 is a bottomed cylindrical member having an open upper portion, and has a tapered shape in which a lower portion is narrowed at a lower portion thereof, and a cylindrical shape having a smaller diameter is again formed at a bottom portion. The side wall of the bottom cylindrical portion has a hole 2a for discharging the settled sludge.
And a settling sludge discharge pipe 4 is connected. Around the upper edge of the settling sludge tank 2, a separated water receiving frame 5 having an L-shaped cross section is attached over the entire circumference as a receiver when the separated water overflows from the upper edge. A part of the separated water receiving frame 5 forms a housing 6, and a hole 6a is formed in the bottom portion of the housing 6 to which a separated water discharge pipe 7 is connected.

【0010】浮上汚泥槽3は、下部が開口した有蓋円筒
形状の部材であり、その外径は分離水の通路19を形成
する程度に沈澱汚泥槽2の内径よりも小さい寸法で、固
定部材(図示せず)により、沈澱汚泥槽2の内側に同心
円状に内嵌、固定されている。浮上汚泥槽3の側壁に
は、脱気された汚泥を排出するための孔3aが穿設さ
れ、濃縮汚泥排出管9が接続されている。濃縮汚泥排出
管9は、沈澱汚泥槽2の側壁に穿設された孔2bを貫通
し(その接触部位は溶接等により封止され)、次処理工
程に続いている。
The floating sludge tank 3 is a cylindrical member with a lid whose bottom is opened, and the outer diameter of the floating sludge tank 3 is smaller than the inner diameter of the settling sludge tank 2 to the extent that a passage 19 for separated water is formed. (Not shown) is fitted and fixed concentrically inside the settling sludge tank 2. The side wall of the floating sludge tank 3 is provided with a hole 3a for discharging the degassed sludge, and a concentrated sludge discharge pipe 9 is connected to the hole 3a. The concentrated sludge discharge pipe 9 penetrates the hole 2b formed in the side wall of the settled sludge tank 2 (the contact portion is sealed by welding or the like), and is continued to the next treatment step.

【0011】そして、浮上汚泥槽3の内部には、浮上汚
泥凝集手段としての上下部が開放された円錐台形状の汚
泥ガイド板8が配設される。この汚泥ガイド板8は、浮
上汚泥を上方向に導き凝集させるため、および後述する
回転翼16により撥ね飛ばされ、脱気された濃縮汚泥と
前記浮上汚泥とを隔離させるためのものであり、その下
端部は濃縮汚泥排出管9の下端部より下側に位置する浮
上汚泥槽3の内壁に固定、封止されている。汚泥ガイド
板8の上部は、その全周にわたって鉛直に立ち上がるつ
ば部8aを形成している。このつば部8aは、図2およ
び図6(a)に示すように汚泥濃縮装置1内に流入され
た汚泥水の液面レベル(W.L.)よりやや上に位置す
るように立ち上げてあり、液面上に凝集された浮上汚泥
を堆積、濃縮させておくためのものである。
Inside the floating sludge tank 3, there is provided a sludge guide plate 8 having a truncated cone shape with open upper and lower portions as floating sludge aggregating means. The sludge guide plate 8 is for guiding the flotation sludge upward and causing the flocculation to agglomerate, and for separating the degassed concentrated sludge blown off by a rotary blade 16 described later from the flotation sludge. The lower end is fixed and sealed to the inner wall of the floating sludge tank 3 located below the lower end of the concentrated sludge discharge pipe 9. The upper portion of the sludge guide plate 8 forms a brim portion 8a that stands vertically over the entire circumference thereof. As shown in FIGS. 2 and 6 (a), the brim portion 8a is set up so that it is located slightly above the liquid level (W.L.) of the sludge water that has flowed into the sludge concentrating device 1. It is for depositing and concentrating flocculated floating sludge on the liquid surface.

【0012】濃縮汚泥排出管9と対向する側で汚泥ガイ
ド板8の下端部から下に位置する沈澱汚泥槽2および浮
上汚泥槽3の側壁には、それぞれ孔2c、3b(図2)
が穿設され、これらの孔2c、3bに、加圧空気溶解水
が混合された原汚泥が流れる汚泥流入管10が貫通し
(その接触部位は溶接等により封止され)、汚泥濃縮装
置1内部中央付近まで延出し、その先端を噴出口10a
としている。この汚泥流入管10は、原汚泥が貯留され
ている原汚泥タンク(図示せず)からポンプによって原
汚泥を送る原汚泥流入管10bと、これに分岐接続さ
れ、原水に圧縮空気を高濃度で溶解した加圧空気溶解水
をポンプにより送る加圧空気溶解水流入管10cとから
なる。
Holes 2c and 3b (FIG. 2) are formed in the side walls of the settling sludge tank 2 and the floating sludge tank 3 located below the lower end of the sludge guide plate 8 on the side facing the concentrated sludge discharge pipe 9, respectively.
The sludge inflow pipe 10 through which the raw sludge mixed with the compressed air-dissolved water flows is penetrated through these holes 2c and 3b (the contact portion is sealed by welding or the like), and the sludge concentrating device 1 It extends to near the center of the inside, and its tip is the jet outlet 10a.
And The sludge inflow pipe 10 is connected to a raw sludge inflow pipe 10b for sending the raw sludge by a pump from a raw sludge tank (not shown) in which the raw sludge is stored, and is branched and connected to the raw water so that compressed air can be highly concentrated in the raw water. It comprises a pressurized air-dissolved water inflow pipe 10c for sending the dissolved pressurized air-dissolved water by a pump.

【0013】沈澱汚泥槽2の内部には、汚泥流入管10
の噴出口10aから噴出する汚泥水の流れを上方向に導
く流れ方向規制部材11を配設する。流れ方向規制部材
11は、沈澱汚泥槽2と同一軸線上に設けた,上部が開
口し,周側面および底面が閉塞された有底円筒形状の部
材であり、その内方に噴出口10aが臨むように、側壁
に穿設された孔に汚泥流入管10を貫通しており、その
接触部位は溶接等により封止、固定されている。また、
流れ方向規制部材11の底面中央には後述するモータ1
2に取り付けられたシャフト12aが貫通できるように
孔が穿設されている。
Inside the settling sludge tank 2, a sludge inflow pipe 10 is provided.
A flow direction regulating member 11 that guides the flow of sludge water ejected from the ejection port 10a of the above is provided. The flow direction control member 11 is a bottomed cylindrical member provided on the same axis as the settling sludge tank 2 with an open top and closed peripheral side and bottom surfaces, and the jet outlet 10a faces the inside thereof. As described above, the sludge inflow pipe 10 penetrates the hole formed in the side wall, and the contact portion is sealed and fixed by welding or the like. Also,
A motor 1 described later is provided at the center of the bottom surface of the flow direction regulating member 11.
A hole is formed so that the shaft 12a attached to the No. 2 can penetrate.

【0014】浮上汚泥槽3の上面の中心部にはモータ1
2が載置され、このモータ12に、図示しない変速機に
よってそれぞれ回転数を調整し得る第1、第2および第
3の3つのシャフト12a、12b、12cを取り付け
る。第1のシャフト12aは下方に伸び、前述の流れ方
向規制部材11の底面に穿設された孔を貫通して沈澱汚
泥槽2の底面に支承された軸受13に挿嵌している。こ
れら回転数の異なる3つのシャフトにはそれぞれの目的
を持った羽状の部材が取り付けられている。
The motor 1 is provided at the center of the upper surface of the floating sludge tank 3.
2 is mounted, and three first, second and third shafts 12a, 12b, 12c whose rotation speeds can be adjusted by a transmission (not shown) are attached to the motor 12. The first shaft 12a extends downward and penetrates through the hole formed in the bottom surface of the flow direction regulating member 11 and is fitted into the bearing 13 supported on the bottom surface of the settling sludge tank 2. Feather-shaped members having different purposes are attached to the three shafts having different rotational speeds.

【0015】まず、第1のシャフト12aには上側と下
側にそれぞれ複数本、本形態では4本のブラケット14
a、15aがシャフト12aに対して直角に、そして互
いに同一角度となるように放射状に取り付けられてい
る。上側のブラケット14aの先端には、それぞれ汚泥
ガイド板8の内壁に沿う形状および長さ寸法の板状部材
からなる浮上汚泥用スクレーパ14が、また、下側のブ
ラケット14bの先端には、それぞれ沈澱汚泥槽2のテ
ーパ部の内壁に沿う形状および長さ寸法の板状部材から
なる沈澱汚泥用スクレーパ15が取り付けられている。
第1のシャフト12aを回転させることにより、浮上汚
泥用スクレーパ14は汚泥ガイド板8の内壁に付着した
浮上汚泥をその回転により汚泥ガイド板8の内壁に沿っ
て移動し掻き取る。この浮上汚泥用スクレーパ14は図
3に示すように、その回転方向側を汚泥ガイド板8の内
壁に接するか、僅かの間隙(数mm程度)を形成するよ
うに近接して、汚泥ガイド板8の横断面円の接線方向に
対して所定角度を成すようにブラケット14aに取り付
けられている。一方、沈澱汚泥用スクレーパ15は沈澱
汚泥槽2のテーパの形成された内壁に付着した沈澱汚泥
をその回転により内壁に沿って移動し掻き取る。この沈
澱汚泥用スクレーパ15は、浮上汚泥用スクレーパ14
と同様に、回転方向側を沈澱汚泥槽2のテーパ内壁に接
するか,僅かの間隙を形成するように近接して、テーパ
内壁の横断面円接線方向に対して所定角度を成すように
ブラケット15aに取り付けられている。シャフト12
aの周辺速度は高速にすると浮上汚泥用スクレーパ14
および沈澱汚泥用スクレーパ15によって掻き取られた
汚泥が槽内で攪乱してしまうので適切ではなく、およそ
2〜3m/分以下の低速回転が望ましい。本形態では、
浮上汚泥用スクレーパおよび沈澱汚泥用スクレーパを同
じシャフトに取り付けたが、もちろんシャフトをもう1
つ設けて、別々の回転数とした仕様にしてもよい。
First, the first shaft 12a has a plurality of brackets 14 on each of the upper side and the lower side, and four brackets 14 in this embodiment.
a and 15a are attached at right angles to the shaft 12a and radially so as to form the same angle with each other. A floating sludge scraper 14 made of a plate-like member having a shape and a length dimension along the inner wall of the sludge guide plate 8 is provided at the tip of the upper bracket 14a, and sedimentation is provided at the tip of the lower bracket 14b. The sludge scraper 15 for sedimentation, which is a plate-like member having a shape and a length along the inner wall of the tapered portion of the sludge tank 2, is attached.
By rotating the first shaft 12a, the floating sludge scraper 14 moves and scrapes the floating sludge adhered to the inner wall of the sludge guide plate 8 along the inner wall of the sludge guide plate 8 by the rotation thereof. As shown in FIG. 3, the floating sludge scraper 14 contacts the rotation direction side of the sludge guide plate 8 with the inner wall of the sludge guide plate 8 or is close to the sludge guide plate 8 to form a slight gap (about several mm). Is attached to the bracket 14a so as to form a predetermined angle with respect to the tangential direction of the cross section circle. On the other hand, the settled sludge scraper 15 moves and scrapes the settled sludge attached to the tapered inner wall of the settled sludge tank 2 along the inner wall by its rotation. The sludge scraper 15 for sedimentation sludge is the scraper 14 for floating sludge.
Similarly, the rotation direction side is in contact with the taper inner wall of the settling sludge tank 2 or is close to the taper inner wall so as to form a slight gap, and the bracket 15a is formed so as to form a predetermined angle with respect to the tangential direction of the cross section of the taper inner wall. Is attached to. Shaft 12
When the peripheral speed of a is set to a high speed, the scraper 14 for floating sludge
Further, sludge scraped off by the sludge for settling sludge 15 is disturbed in the tank and is not appropriate. It is desirable to rotate at a low speed of about 2 to 3 m / min or less. In this form,
I attached the scraper for flotation sludge and the scraper for sedimentation sludge to the same shaft.
Alternatively, the number of rotations may be one and the number of rotations may be different.

【0016】次に、第2のシャフト12bには複数枚、
本形態では4枚の矩形板状部材の回転翼16がシャフト
12bに対して直角に、そして互いに同一角度となるよ
うに放射状に取り付けられている。第2のシャフト12
bを回転させることにより、この回転翼16は回転し、
汚泥ガイド板8のつば部8a内に堆積された濃縮汚泥を
浮上汚泥槽3の内壁に向かって撥ね飛ばして、脱気する
ものである。浮上汚泥を効率よく撥ね飛ばし、脱気する
ために、回転翼16の先端から、180度反対に位置す
る回転翼16の先端までの寸法(図6(a)におけるL
寸法)はつば部8aの径と略同一寸法であり、また回転
翼16の下縁とつば部8aの上縁の間隙寸法(図6
(a)におけるH寸法)は0〜数mm程度である。また
気泡の付着している濃縮汚泥の脱気は、回転翼16との
衝突力、および回転翼16の回転に対して接線方向に跳
ねとばされたときの浮上汚泥槽3の内壁に対する衝突力
により左右されるので、その衝突力を大きくすべくシャ
フト12bの回転速度は100rpm以上の高速回転が
望ましい。
Next, a plurality of sheets are attached to the second shaft 12b,
In the present embodiment, four rectangular blade-shaped rotary blades 16 are mounted at right angles to the shaft 12b and radially so as to form the same angle. Second shaft 12
By rotating b, this rotary blade 16 rotates,
The concentrated sludge accumulated in the collar portion 8a of the sludge guide plate 8 is splashed toward the inner wall of the floating sludge tank 3 to be deaerated. The dimension from the tip of the rotary blade 16 to the tip of the rotary blade 16 positioned 180 degrees opposite (L in FIG. 6A) in order to efficiently splash the floating sludge and deaerate it.
The dimension is approximately the same as the diameter of the collar 8a, and the gap between the lower edge of the rotary blade 16 and the upper edge of the collar 8a (see FIG. 6).
(H dimension in (a)) is about 0 to several mm. Further, deaeration of the concentrated sludge with bubbles adheres to the rotary blade 16 and the collision force against the inner wall of the flotation sludge tank 3 when it is bounced tangentially to the rotation of the rotary blade 16. The rotation speed of the shaft 12b is preferably 100 rpm or more in order to increase the collision force.

【0017】第3のシャフト12cには複数本、本形態
では4本のブラケット17aがシャフト12cに対して
直角に、そして互いに直角に放射状に取り付けられてい
る。ブラケット17aの先端には、それぞれ浮上汚泥槽
3の内壁に沿う形状で、かつ、浮上汚泥槽3の内壁上端
から既述の濃縮汚泥排出管9の開口部上縁近傍までの長
さ寸法の矩形板状部材からなる濃縮汚泥用スクレーパ1
7が取り付けられている。第3のシャフト12cを回転
することにより、この濃縮汚泥用スクレーパ17は、浮
上汚泥槽3の上部内壁に付着した濃縮汚泥(前記回転翼
16により脱気された汚泥)をその回転により浮上汚泥
槽3の内壁に沿って移動し掻き取る。図4に示すよう
に、濃縮汚泥用スクレーパ17は回転方向側を浮上汚泥
槽3の内壁に接するか,僅かの間隙(数mm程度)を形
成するように近接して、浮上汚泥槽3の横断面円の接線
方向に対して所定角度を成すようにブラケット17aに
取り付けられている。濃縮汚泥用スクレーパ17は濃縮
汚泥を掻き落とすだけなので高速回転である必要はな
く、回転翼16により撥ね飛ばされ浮上汚泥槽3に付着
する濃縮汚泥の量にもよるが、シャフト12cの周辺速
度は2〜3m/分以下の低速回転が望ましい。
A plurality of, in the present embodiment, four brackets 17a are radially attached to the third shaft 12c at right angles to the shaft 12c and at right angles to each other. At the tip of the bracket 17a, a rectangle having a shape along the inner wall of the floating sludge tank 3 and having a length from the upper end of the inner wall of the floating sludge tank 3 to the vicinity of the upper edge of the opening of the concentrated sludge discharge pipe 9 described above Scraper for concentrated sludge 1 consisting of plate-shaped members
7 is attached. By rotating the third shaft 12c, the concentrated sludge scraper 17 causes the concentrated sludge adhered to the upper inner wall of the floating sludge tank 3 (sludge degassed by the rotary blade 16) to float in the floating sludge tank. Move along the inner wall of 3 and scrape. As shown in FIG. 4, the concentrated sludge scraper 17 contacts the inner wall of the flotation sludge tank 3 on the rotation direction side or is close to form a slight gap (about several mm), and traverses the flotation sludge tank 3. The bracket 17a is attached so as to form a predetermined angle with respect to the tangential direction of the face circle. Since the concentrated sludge scraper 17 only scrapes the concentrated sludge off, it does not need to rotate at a high speed, and the peripheral speed of the shaft 12c depends on the amount of concentrated sludge that is splashed off by the rotor blades 16 and adheres to the floating sludge tank 3. A low speed rotation of 2 to 3 m / min or less is desirable.

【0018】次に、本装置の作用について説明する。処
理する原汚泥が貯留された原汚泥タンクからポンプによ
って原汚泥が原汚泥流入管10b内を流れる。一方、原
水に圧縮空気が高濃度に溶解した加圧空気溶解水が貯留
された加圧空気溶解水タンクからポンプによって加圧空
気溶解水が空気溶解水流入管10c内を流れる。両者
は、両管の接続部で混合し、噴出口10aから汚泥水と
して汚泥濃縮装置1内部へと噴出する。噴出した汚泥水
はまず、流れ方向規制部材11の内壁に衝突する。流れ
方向規制部材11の下面は閉塞されているので汚泥水は
流れ方向規制部材11の内壁に沿って上方向へと流れを
変える。また、汚泥水中の原汚泥には、槽内において、
大気圧下で加圧空気溶解水から発生する微細気泡が付着
する。原汚泥は付着した微細気泡の浮力により浮上汚泥
となって浮上する。ここで微細気泡と付着しなかった汚
泥成分は沈澱汚泥となって沈降する。沈澱汚泥槽2のテ
ーパ内壁に沈降した沈澱汚泥は、テーパ内壁に沿って回
転移動する沈澱汚泥用スクレーパ15によって掻き取ら
れる。沈澱汚泥用スクレーパ15は低速度で掻き取りを
行うため、沈澱汚泥は汚泥水内で攪拌されることなく沈
澱汚泥槽2の底部へと沈澱していく。そして、沈澱汚泥
排出管4を介して沈澱汚泥処理工程へと搬送される。ま
た、浮上汚泥および沈澱汚泥が分離した後の余剰の加圧
空気溶解水は、分離水として、沈澱汚泥槽2の内壁と浮
上汚泥槽3の外壁との間に形成された通路19を通って
沈澱汚泥槽2の上縁から溢れ出て分離水受枠5内に流出
する。そして、分離水受枠5の一部に形成された筐体6
に流れて孔6aから分離水排出管7を介して分離水処理
工程へと排出される。
Next, the operation of this apparatus will be described. From the raw sludge tank in which the raw sludge to be treated is stored, the raw sludge flows in the raw sludge inflow pipe 10b by a pump. On the other hand, the pressurized air-dissolved water flows through the air-dissolved water inflow pipe 10c from the pressurized air-dissolved water tank in which the compressed air-dissolved water in which the compressed air is dissolved in the raw water at a high concentration is stored. Both are mixed at the connecting portion of both pipes and ejected as sludge water into the interior of the sludge concentrator 1 from the ejection port 10a. The ejected sludge water first collides with the inner wall of the flow direction regulating member 11. Since the lower surface of the flow direction regulating member 11 is closed, the sludge water changes its flow upward along the inner wall of the flow direction regulating member 11. In addition, for raw sludge in sludge water,
Under atmospheric pressure, fine bubbles generated from pressurized air-dissolved water adhere. The raw sludge floats as floating sludge due to the buoyancy of the adhered fine bubbles. Here, the sludge components that have not adhered to the fine bubbles are settled as settled sludge. The settled sludge settled on the tapered inner wall of the settled sludge tank 2 is scraped off by the settled sludge scraper 15 which rotates and moves along the tapered inner wall. Since the sludge scraper 15 for scraping sludge scrapes at a low speed, the sludge settles down to the bottom of the sludge sludge tank 2 without being stirred in the sludge water. Then, it is conveyed to the settling sludge treatment step via the settling sludge discharge pipe 4. Further, the excess pressurized air-dissolved water after the separation of the floating sludge and the settling sludge passes as a separated water through a passage 19 formed between the inner wall of the settling sludge tank 2 and the outer wall of the floating sludge tank 3. It overflows from the upper edge of the settling sludge tank 2 and flows into the separated water receiving frame 5. Then, the housing 6 formed in a part of the separated water receiving frame 5
And is discharged to the separated water treatment step from the hole 6a through the separated water discharge pipe 7.

【0019】さて微細気泡の付着した浮上汚泥は、浮上
汚泥凝集手段としての汚泥ガイド板8の内側を浮上しな
がら次第に凝集され、つば部8a内において堆積する。
浮上途中、汚泥ガイド板8の内壁に付着した浮上汚泥
は、その内壁に沿って回転移動する浮上汚泥用スクレー
パ14によって掻き取られる。浮上汚泥用スクレーパ1
4は沈澱汚泥用スクレーパ15と同じ低速度で掻き取り
を行うため、浮上汚泥は汚泥水内で攪拌されることな
く、再びつば部8a付近の汚泥水面に向かって浮上し始
める。図6(a)に示すように、浮上汚泥の堆積量を多
くして汚泥を高濃度に濃縮させるため、汚泥水の液面レ
ベルはつば部8aの、つば部8a立ち上がり近傍に位置
している。この液面上まで浮上してきた浮上汚泥は堆積
し、次第に濃縮される。そして、この堆積した濃縮汚泥
のうち最も汚泥濃度の高い最上部の濃縮汚泥は高速度で
回転する回転翼16によってその回転方向に撥ね飛ばさ
れる。このとき汚泥は回転翼16との衝突による衝撃力
および浮上汚泥槽3の内壁との衝突による衝撃力により
容易に脱気される。浮上汚泥槽3の内壁に付着した濃縮
汚泥は、浮上汚泥槽3の内壁に沿って回転移動する濃縮
汚泥用スクレーパ17により随時掻き落とされるため壁
面で乾燥、固化することがない。そして、掻き取られた
濃縮汚泥は浮上汚泥槽3の壁面に穿設された孔3aを通
って濃縮汚泥排出管9へ排出、回収される。
The floating sludge to which the fine air bubbles are attached is gradually aggregated while floating inside the sludge guide plate 8 as the flocculation sludge aggregating means, and is accumulated in the collar portion 8a.
During the floating, the floating sludge adhered to the inner wall of the sludge guide plate 8 is scraped off by the floating sludge scraper 14 which rotates and moves along the inner wall. Scraper for floating sludge 1
Since No. 4 scrapes off at the same low speed as the settling sludge scraper 15, the floating sludge begins to float again toward the water surface of the sludge near the brim 8a without being stirred in the sludge water. As shown in FIG. 6A, the liquid level of sludge water is located near the rising edge of the brim portion 8a of the brim portion 8a in order to increase the deposition amount of the floating sludge and concentrate the sludge to a high concentration. . The floating sludge that has floated to the surface of the liquid accumulates and is gradually concentrated. The uppermost concentrated sludge having the highest sludge concentration among the accumulated concentrated sludge is repelled in the rotating direction by the rotary blades 16 rotating at a high speed. At this time, the sludge is easily deaerated by the impact force caused by the collision with the rotary blades 16 and the impact force caused by the collision with the inner wall of the floating sludge tank 3. The concentrated sludge adhering to the inner wall of the floating sludge tank 3 is scraped off by the concentrated sludge scraper 17 that rotates and moves along the inner wall of the floating sludge tank 3 at any time, so that it does not dry and solidify on the wall surface. Then, the scraped thickened sludge is discharged and collected into the thickened sludge discharge pipe 9 through the hole 3a formed in the wall surface of the floating sludge tank 3.

【0020】さて、以上説明した本発明に係る汚泥濃縮
装置では、モータに取り付けた各羽状部材、回転翼、濃
縮汚泥用スクレーパ、浮上汚泥用スクレーパおよび沈澱
汚泥用スクレーパを全て4枚ずつとしたが、もちろんこ
れに限られることなく、1枚としても構わない。通常は
2〜4枚である。なお、図6(b)に示すようにモータ
回転軸に対し角度θだけ傾斜させて回転翼をシャフトに
取り付ければ、回転翼に衝突した濃縮汚泥は水平方向よ
り常に上方に撥ね飛ばされるため、つば部8aに堆積し
た濃縮汚泥に戻されることなく、効率の良い脱気処理が
可能となる。
In the sludge concentrating apparatus according to the present invention described above, each of the blade-shaped members attached to the motor, the rotor, the scraper for the concentrated sludge, the scraper for the floating sludge, and the scraper for the settled sludge are four in number. However, the present invention is not limited to this, and one sheet may be used. Usually, it is 2-4 sheets. As shown in FIG. 6 (b), if the rotary blade is attached to the shaft by inclining it by an angle θ with respect to the motor rotary shaft, the concentrated sludge colliding with the rotary blade is always splashed upward from the horizontal direction. Efficient degassing can be performed without returning to the concentrated sludge accumulated in the portion 8a.

【0021】また、流れ方向規制部材11は上述した円
筒形状のものに限られるものでなく、汚泥槽内に流入し
てくる汚泥水の流れを上部方向に導く態様のものであれ
ばよい。
Further, the flow direction restricting member 11 is not limited to the above-mentioned cylindrical member, but may be any member that guides the sludge water flowing into the sludge tank in the upward direction.

【0022】[0022]

【発明の効果】上述の構成からなる本発明の汚泥濃縮装
置によれば、以下のような効果を奏する。 (1)汚泥水面に堆積、濃縮した汚泥のうち、十分な濃
縮がなされた最上部の濃縮汚泥のみを回転翼により高速
で撥ね飛ばすため、乱れが生じず、下層の濃度の低い汚
泥と混ざることなく、極めて高濃度の濃縮汚泥を回収す
ることができる。 (2)微細気泡の付着した濃縮汚泥の脱気処理を汚泥の
濃縮と同時に行うことができるので、脱気処理槽を別個
に設ける必要がなくなり、汚泥の濃縮フロー効率が向上
する。(3)汚泥槽内壁に付着した濃縮汚泥、浮上汚
泥、沈澱汚泥をそれぞれ掻き取るスクレーパを設けたの
で、汚泥槽内壁の清掃頻度が低減される。 (4)汚泥槽を略円筒形状として、上述の回転翼、各ス
クレーパを1台のモータにより回転駆動させる構造とし
たため、コンパクトかつ機器点数の少ない装置が実現さ
れる。 (5)汚泥槽内に流入する汚泥水の流れを上部方向に導
く流れ方向規制部材を設けたので、汚泥槽内の汚泥水に
乱れが生じることがなく、浮上汚泥の浮上効率が上が
る。
According to the sludge concentrating apparatus of the present invention having the above-mentioned structure, the following effects can be obtained. (1) Sludge Of the sludge accumulated and condensed on the surface of the water, only the uppermost concentrated sludge, which has been sufficiently concentrated, is repelled at high speed by the rotor blades, so it does not cause turbulence and mix with the lower concentration of sludge. It is possible to collect concentrated sludge of extremely high concentration. (2) Since the deaeration process of the concentrated sludge having fine air bubbles can be performed at the same time as the concentration of the sludge, it is not necessary to separately provide a deaeration treatment tank, and the sludge concentration flow efficiency is improved. (3) Since the scraper for scraping off the concentrated sludge, the floating sludge, and the settled sludge adhering to the inner wall of the sludge tank is provided, the frequency of cleaning the inner wall of the sludge tank is reduced. (4) Since the sludge tank has a substantially cylindrical shape and the rotary blades and the scrapers are driven to rotate by one motor, a compact device having a small number of devices can be realized. (5) Since the flow direction regulating member for guiding the flow of the sludge water flowing into the sludge tank to the upper direction is provided, the sludge water in the sludge tank is not disturbed and the floating efficiency of the floating sludge is improved.

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

【図1】(a)および(b)は本発明に係る汚泥濃縮装
置の上面図および側面図である。
FIG. 1 (a) and (b) are a top view and a side view of a sludge concentrating device according to the present invention.

【図2】図1におけるA−A断面図である。FIG. 2 is a sectional view taken along line AA in FIG.

【図3】図1におけるB−B断面図である。FIG. 3 is a sectional view taken along line BB in FIG.

【図4】図1におけるC−C断面図である。FIG. 4 is a sectional view taken along line CC in FIG.

【図5】汚泥濃縮装置の全体斜視図である。FIG. 5 is an overall perspective view of a sludge concentrating device.

【図6】(a)は要部説明図であり、(b)は他の実施
形態における要部説明図である。
6A is an explanatory view of a main part, and FIG. 6B is an explanatory view of a main part in another embodiment.

【図7】従来の加圧浮上式汚泥濃縮装置の一例を示すフ
ロー説明図である。
FIG. 7 is an explanatory flow diagram showing an example of a conventional pressure floating type sludge concentrating device.

【符号の説明】[Explanation of symbols]

1 汚泥濃縮装置 2 沈澱汚泥槽 3 浮上汚泥槽 4 沈澱汚泥排出管 5 分離水受枠 6 筐体 7 分離水排出管 8 汚泥ガイド板 9 濃縮汚泥排出管 10 汚泥流入管 10a 噴出口 10b 原汚泥流入管 10c 空気溶解水流入管 11 流れ方向規制部材 12 モータ 12a,12b,12c シャフト 13 軸受 14 浮上汚泥用スクレーパ 14a ブラケット 15 沈澱汚泥用スクレーパ 15a ブラケット 16 回転翼 17 濃縮汚泥用スクレーパ 17a ブラケット 18 汚泥槽 19 通路 1 Sludge Concentrator 2 Sedimentation Sludge Tank 3 Floating Sludge Tank 4 Sedimentation Sludge Discharge Pipe 5 Separation Water Receiving Frame 6 Housing 7 Separation Water Discharge Pipe 8 Sludge Guide Plate 9 Condensed Sludge Discharge Pipe 10 Sludge Inlet Pipe 10a Jet 10b Raw Sludge Inflow Pipe 10c Air-dissolved water inflow pipe 11 Flow direction regulating member 12 Motors 12a, 12b, 12c Shaft 13 Bearing 14 Floating sludge scraper 14a Bracket 15 Slag sludge scraper 15a Bracket 16 Rotor blades 17 Condensed sludge scraper 17a Bracket 18 Sludge tank 19 Passage

Claims (11)

【特許請求の範囲】[Claims] 【請求項1】 加圧空気溶解水を混入した汚泥水を導入
する汚泥槽と、加圧空気と混和され、浮上した汚泥を汚
泥槽内において凝集させる浮上汚泥凝集手段と、汚泥水
の液面上に配設され、濃縮、堆積した汚泥を撥ね飛ばし
脱気するための回転翼とを備えることを特徴とする汚泥
濃縮装置。
1. A sludge tank for introducing sludge water mixed with pressurized air-dissolved water, a floating sludge aggregating means for aggregating sludge that is mixed with pressurized air and floated in the sludge tank, and a liquid surface of the sludge water. A sludge concentrating device, which is provided on the upper side of the sludge and has rotary blades for repelling and degassing concentrated and accumulated sludge.
【請求項2】 前記汚泥槽を、有底円筒形状の沈殿汚泥
槽と、この沈殿汚泥槽に内嵌される有蓋円筒形状の浮上
汚泥槽とにより構成し、前記沈殿汚泥槽には沈殿汚泥を
排出するための沈殿汚泥排出管を接続し、また、前記浮
上汚泥槽には脱気された汚泥を排出するための濃縮汚泥
排出管を接続してなる請求項1に記載の汚泥濃縮装置。
2. The sludge tank is constituted by a bottomed cylindrical sedimentation sludge tank and a lidded cylindrical floating sludge tank fitted in the sedimentation sludge tank, and the sedimentation sludge tank is filled with the sedimentation sludge. The sludge concentrating device according to claim 1, wherein a sedimentation sludge discharge pipe for discharging is connected, and a concentrated sludge discharge pipe for discharging deaerated sludge is connected to the floating sludge tank.
【請求項3】 前記浮上汚泥凝集手段を、上下部が開放
された汚泥ガイド板により構成し、この汚泥ガイド板
は、その下端部を前記濃縮汚泥排出管の下端部より下側
に位置する汚泥槽の内壁に固定、封止すると共に、その
上端部を前記汚泥水の液面レベルより上に位置する浮上
汚泥槽の内部に配設してなる請求項1または請求項2に
記載の汚泥濃縮装置。
3. The floating sludge aggregating means is constituted by a sludge guide plate whose upper and lower parts are opened, and the lower end of the sludge guide plate is located below the lower end of the concentrated sludge discharge pipe. The sludge concentrate according to claim 1 or 2, wherein the sludge is fixed and sealed to the inner wall of the tank, and the upper end thereof is arranged inside the floating sludge tank located above the liquid level of the sludge water. apparatus.
【請求項4】 前記浮上汚泥槽の上部に、前記回転翼を
回転駆動させるためのモータを載置してなる請求項1な
いし請求項3のいずれかに記載の汚泥濃縮装置。
4. The sludge concentrating device according to claim 1, wherein a motor for rotating and driving the rotary blade is mounted on an upper portion of the floating sludge tank.
【請求項5】 前記沈殿汚泥槽に、前記モータにより回
転駆動され、沈殿汚泥槽の内壁に沿って移動して、当該
沈殿汚泥槽に付着した沈殿汚泥を掻き取る沈殿汚泥用ス
クレーパを設けてなる請求項2ないし請求項4のいずれ
かに記載の汚泥濃縮装置。
5. The settled sludge scraper, which is driven to rotate by the motor and moves along the inner wall of the settled sludge tank to scrape the settled sludge adhering to the settled sludge tank, is provided in the settled sludge tank. The sludge concentrating device according to any one of claims 2 to 4.
【請求項6】 前記浮上汚泥槽に、前記モータにより回
転駆動され、浮上汚泥槽の内壁に沿って移動して、当該
浮上汚泥槽に付着した濃縮汚泥を掻き取る濃縮汚泥用ス
クレーパを設けてなる請求項2ないし請求項4のいずれ
かに記載の汚泥濃縮装置。
6. The sludge scraper for concentrated sludge, which is driven to rotate by the motor and moves along the inner wall of the floating sludge tank to scrape the concentrated sludge adhering to the floating sludge tank, is provided in the floating sludge tank. The sludge concentrating device according to any one of claims 2 to 4.
【請求項7】 前記汚泥ガイド板に、前記モータにより
回転駆動され、汚泥ガイド板の内壁に沿って移動して、
当該汚泥ガイド板に付着した浮上汚泥を掻き取る浮上汚
泥用スクレーパを設けてなる請求項2ないし請求項4の
いずれかに記載の汚泥濃縮装置。
7. The sludge guide plate is driven to rotate by the motor and moved along the inner wall of the sludge guide plate,
The sludge concentrating device according to any one of claims 2 to 4, further comprising a floating sludge scraper for scraping the floating sludge adhered to the sludge guide plate.
【請求項8】 前記沈殿汚泥槽と浮上汚泥槽との間に、
外部に分離水を排出するための通路を形成してなる請求
項2ないし請求項7のいずれかに記載の汚泥濃縮装置。
8. Between the settling sludge tank and the floating sludge tank,
The sludge concentrator according to any one of claims 2 to 7, wherein a passage for discharging separated water is formed outside.
【請求項9】 前記回転翼、濃縮汚泥用スクレーパ、浮
上汚泥用スクレーパおよび沈澱汚泥用スクレーパは1台
のモータの回転軸に取り付けられ、それぞれ異なる回転
数で回転が可能となっていることを特徴とする請求項2
ないし請求項7のいずれかに記載の汚泥濃縮装置。
9. The rotary blade, the concentrated sludge scraper, the floating sludge scraper, and the settled sludge scraper are attached to a rotary shaft of a single motor, and can rotate at different rotational speeds. Claim 2
The sludge concentrating device according to claim 7.
【請求項10】 加圧空気溶解水を作用させた汚泥水を
汚泥槽内に噴出させる噴出口近傍に、前記汚泥水の流れ
を上部方向に導くための流れ方向規制部材を設けたこと
を特徴とする請求項1ないし請求項9のいずれかに記載
の汚泥濃縮装置。
10. A flow direction restricting member for guiding the flow of the sludge water upward is provided in the vicinity of an ejection port for ejecting the sludge water to which the pressurized air-dissolved water is applied into the sludge tank. The sludge concentrating device according to any one of claims 1 to 9.
【請求項11】 前記流れ方向規制部材は前記噴出口を
囲む、上部が開口し、周側面および底面が閉塞された円
筒形状の部材であることを特徴とする請求項1ないし請
求項9のいずれかに記載の汚泥濃縮装置。
11. The flow direction restricting member is a cylindrical member that surrounds the jet outlet, is open at an upper portion, and is closed at a peripheral side surface and a bottom surface, according to any one of claims 1 to 9. The sludge concentrating device described in Crab.
JP05218496A 1996-03-11 1996-03-11 Sludge thickener Expired - Fee Related JP3567392B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP05218496A JP3567392B2 (en) 1996-03-11 1996-03-11 Sludge thickener

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP05218496A JP3567392B2 (en) 1996-03-11 1996-03-11 Sludge thickener

Publications (2)

Publication Number Publication Date
JPH09239400A true JPH09239400A (en) 1997-09-16
JP3567392B2 JP3567392B2 (en) 2004-09-22

Family

ID=12907724

Family Applications (1)

Application Number Title Priority Date Filing Date
JP05218496A Expired - Fee Related JP3567392B2 (en) 1996-03-11 1996-03-11 Sludge thickener

Country Status (1)

Country Link
JP (1) JP3567392B2 (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100374442B1 (en) * 2001-08-02 2003-03-08 인효석 Circular settling tank
KR100906310B1 (en) * 2009-03-31 2009-07-07 가람환경기술(주) Integrated type waste water treating apparatus using a minute bubble generator
CN103833196A (en) * 2014-02-20 2014-06-04 镇江市水业总公司 supermatant discharge system and sludge condensation method
US20160185639A1 (en) * 2014-12-31 2016-06-30 ClearCove Systems, Inc. Method and apparatus for optimization of a conventional waste water treatment plant
CN107935357A (en) * 2017-12-27 2018-04-20 北京东方园林环境股份有限公司 A kind of Dredged bed mud treatment in situ system and processing method
CN111661991A (en) * 2020-06-01 2020-09-15 湖北众堃科技股份有限公司 Integration sludge thickening pond

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100374442B1 (en) * 2001-08-02 2003-03-08 인효석 Circular settling tank
KR100906310B1 (en) * 2009-03-31 2009-07-07 가람환경기술(주) Integrated type waste water treating apparatus using a minute bubble generator
CN103833196A (en) * 2014-02-20 2014-06-04 镇江市水业总公司 supermatant discharge system and sludge condensation method
US20160185639A1 (en) * 2014-12-31 2016-06-30 ClearCove Systems, Inc. Method and apparatus for optimization of a conventional waste water treatment plant
CN107935357A (en) * 2017-12-27 2018-04-20 北京东方园林环境股份有限公司 A kind of Dredged bed mud treatment in situ system and processing method
CN107935357B (en) * 2017-12-27 2023-12-05 北京东方园林环境股份有限公司 On-site dredging sediment treatment system and treatment method
CN111661991A (en) * 2020-06-01 2020-09-15 湖北众堃科技股份有限公司 Integration sludge thickening pond
CN111661991B (en) * 2020-06-01 2022-04-12 湖北众堃科技股份有限公司 Integration sludge thickening pond

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