JP2000117003A - Upward and downward counter-current concentrator - Google Patents

Upward and downward counter-current concentrator

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Publication number
JP2000117003A
JP2000117003A JP10331832A JP33183298A JP2000117003A JP 2000117003 A JP2000117003 A JP 2000117003A JP 10331832 A JP10331832 A JP 10331832A JP 33183298 A JP33183298 A JP 33183298A JP 2000117003 A JP2000117003 A JP 2000117003A
Authority
JP
Japan
Prior art keywords
sludge
pipe
water
floated
tank
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP10331832A
Other languages
Japanese (ja)
Inventor
Minoru Tsuchiya
実 土屋
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP10331832A priority Critical patent/JP2000117003A/en
Publication of JP2000117003A publication Critical patent/JP2000117003A/en
Pending legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To treat the precipitable sludge having the same specific gravity as water by a gravity type and to treat the floatable sludge having the specific gravity lower than that of water by a floating type with a single device by arranging a partition cylinder, a partition conical part, a floated sludge discharge plate and a floated sludge discharge passage, mounting an arm and a floated sludge scraper at a driving shaft and disposing an air dispersing pipe in a water introducing pipe. SOLUTION: In this concentrator 1, the sludge is made to flow from a raw water inflow pipe 8 into the introducing pipe 15 providing with the air dispersing pipe and in which air bubbles are brought into contact and combined with sludge floc, and the precipitable sludge having the specific gravity more than 1 is deposited on a bed board 10 by the gravity and collected in a sludge pit 12 with the driving shaft 18 and the scraper 11 and discharged to the outside of system through a sludge transfer pipe 13. The sludge floated by the upward stream at the water introducing pipe 15 and a contaminated water tank 3 is collected on the water surface of a water tank and transferred with a floated sludge discharge plate 5 and a floated sludge scraper 20 via floated sludge passage 21. A separated liq. from which the sludge is separated at the contaminated water tank 3 is transported from a separated liq. passage 7 via a separated water tank 6. In this way, the device enables to cope with the single concentrator 1 according to the precipitable sludge or the floatable sludge due to quality change and the value of the gravity.

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】この発明は、下水、農業集落
排水、産業排水等の流入汚水の一次処理、および二次処
理より発生する汚泥の濃縮に関するもので、水処理技術
分野に属する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to the primary treatment of incoming sewage such as sewage, agricultural settlement drainage, and industrial wastewater, and the concentration of sludge generated from secondary treatment, and belongs to the field of water treatment.

【0002】[0002]

【従来の技術】従来、汚水の一次処理、二次処理より発
生する汚泥の濃縮方法には、重力式、機械式(遠心濃縮
機)、浮上式の3方式がある。 (1)重力式は、最も一般的な方法であり、自然の重力
により汚泥を沈降させるもので、汚泥の比重が1より大
きい場合に有効であり、特にエネルギーを使用しない利
点がある。しかし、沈降分離を行うためには時間を要
し、濃縮槽を大きくする必要がある。また、汚泥の比重
が1より小さいときは沈降しないので処理が不可能とな
る。近年、下水等では処理方式によるもの、または汚泥
の質が有機質となるものが多く、発生汚泥は浮遊性のも
のが多い傾向にある。 (2)機械式は、主として遠心濃縮法であり、汚泥の比
重については1より大きいものは当然として、1より小
さいものでも濃縮効果がよいので使用される例が多い
が、本法はエネルギイー消費が大きく高速回転をするの
で騒音、振動などの二次公害の予防措置が必要である。
また、凝集剤を使用する例もある。 (3)浮上式は、主として比重1より小さい浮上性汚泥
を効率よく浮上させるものであり、加圧式、常圧式があ
るが、いずれも空気の微細気泡を汚泥と接触させ結合し
て浮力を増して浮上させ回収すものである。
2. Description of the Related Art Conventionally, there are three methods for concentrating sludge generated from primary treatment and secondary treatment of wastewater: gravity type, mechanical type (centrifugal concentrator), and floating type. (1) The gravity method is the most general method, and is used to settle sludge by natural gravity. It is effective when the specific gravity of the sludge is greater than 1, and has an advantage of not using energy. However, it takes time to perform sedimentation and separation, and it is necessary to enlarge the concentration tank. When the specific gravity of the sludge is smaller than 1, no settling is performed, so that the treatment becomes impossible. In recent years, in the case of sewage and the like, there are many cases in which the quality of sludge is organic, and the generated sludge tends to be floating. (2) The mechanical method is mainly a centrifugal concentration method, and the specific gravity of sludge is naturally larger than 1, and even smaller than 1 is often used because of its good concentration effect. Since it consumes a lot and rotates at high speed, it is necessary to take measures to prevent secondary pollution such as noise and vibration.
In some cases, a coagulant is used. (3) The levitation type is mainly for efficiently raising buoyant sludge having a specific gravity of less than 1, and there are a pressurization type and a normal pressure type, but both increase the buoyancy by contacting fine air bubbles with the sludge and combining them. And lift it up for recovery.

【0003】[0003]

【発明が解決しようとする課題】本案は、一次処理と二
次処理において発生する如何ような汚泥に対しても対応
できる濃縮装置を提供するものである。即ち、一つの装
置を使用して、比重1より大きい沈降性汚泥は重力式に
て対処し、比重1より小さい浮遊性若しくは浮上性汚泥
については浮上式で対処することを課題とする。
SUMMARY OF THE INVENTION The object of the present invention is to provide a concentrating apparatus which can cope with any sludge generated in the primary treatment and the secondary treatment. That is, it is an object of the present invention to use one apparatus to deal with settling sludge having a specific gravity of more than 1 by a gravity method, and to deal with floating or floating sludge having a specific gravity of less than 1 by using a floating method.

【0004】[0004]

【課題を解決するための手段】重力式濃縮槽1におい
て、仕切円筒2、仕切円錐部4、浮上汚泥排出板5を設
け、駆動軸18にアーム19、浮上汚泥スクレーパ20
を取付け、浮上汚泥排水路21を設置する。つぎに、導
水管15内に散気管16を設け空気源と接続する。
Means for Solving the Problems In the gravity type concentration tank 1, a partition cylinder 2, a partition cone portion 4, and a floating sludge discharge plate 5 are provided, and a drive shaft 18 has an arm 19 and a floating sludge scraper 20.
And a floating sludge drainage channel 21 is installed. Next, an air diffuser 16 is provided in the water pipe 15 and connected to an air source.

【0005】[0005]

【発明の実施の形態】本案は、沈降する汚泥を床盤10
に受けて集積しつつ濃縮し、スクレーパ11により汚泥
ピット12に集め系外に移送する重力式濃縮槽1におい
て、浮遊性または浮上性汚泥を導水管15内および汚濁
水槽3内にて上向流にて浮上させ、水面近くに集積し、
この汚泥を浮上汚泥スクレーパ20にて浮上汚泥排出板
5を経て汚泥水路21に投入し系外に移送するもので、
沈降性、浮上性いずれの汚泥も処理可能である。また、
浮遊汚泥または浮上汚泥の浮上性を改善するために、空
気気泡と汚泥フロックを接触させて結合させる方法とし
て、導水管15内に散気管16を設けて散気する。ま
た、空気を原水流入管8に直接流入して汚泥と混合する
方法が採用されている。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention relates to
In the gravity type concentrating tank 1, which collects and accumulates in a sludge pit 12 by a scraper 11 and transfers the collected sludge to the outside of the system, floating or buoyant sludge flows upward in a water pipe 15 and a polluted water tank 3. Float, accumulate near the water surface,
This sludge is introduced into the sludge channel 21 via the floating sludge discharge plate 5 by the floating sludge scraper 20 and transferred out of the system.
Both settling and floating sludge can be treated. Also,
As a method of bringing air bubbles and sludge flocs into contact and combining them in order to improve the floating property of the suspended or floating sludge, an air diffuser 16 is provided in the water pipe 15 to diffuse air. Further, a method is employed in which air is directly introduced into the raw water inflow pipe 8 and mixed with sludge.

【0006】[0006]

【実施例】図1は、本案の実施例を示すもので、濃縮槽
1において、原水流入管8より導水管15内に汚泥を流
入して比重1より大きい沈降性汚泥は重力により床盤1
0上に沈積すると、駆動軸18、スクレーパ11により
汚泥ピット12に集められ汚泥移送管13により系外に
移送される。導水管15および汚濁水槽3内で浮上する
汚泥は水槽水面に集積し、浮上汚泥排出板5、浮上汚泥
スクレーパ20により浮上汚泥水路21に流入し移送す
る。汚濁水槽3で汚濁物と分離した分離液は分離水槽6
を経て分離液水路7に流入し搬出される。このようにし
て、単一槽において下向流と上向流による汚泥を排除す
るものである。図2は、上記濃縮槽において、浮上性を
向上させるための散気管を設けた例である。導水管15
内に散気管16を設け、空気管9と接続する。散気管1
6よりの気泡と原水流入管8よりの汚泥は導水管15内
で接触混合し、浮上性を増して上昇する。同時にエアリ
フト作用も伴って、導水管15内の汚水は全体的に浮上
し、導水管15の上端部を経て沈降することとなり、汚
濁水槽3内の水の流れが変化して浮上性汚泥中心となる
が、沈降性汚泥に対しても十分に対応できる。なを、散
気管16を設ける代替として原水流入管内に直接空気を
注入し混合する方法でもよい。
FIG. 1 shows an embodiment of the present invention. In a concentration tank 1, sludge flows from a raw water inflow pipe 8 into a water conveyance pipe 15, and settled sludge having a specific gravity of more than 1 is converted into a floor bed 1 by gravity.
When the sediment is deposited on the zero, it is collected in the sludge pit 12 by the drive shaft 18 and the scraper 11 and is transferred out of the system by the sludge transfer pipe 13. The sludge that floats in the water pipe 15 and the polluted water tank 3 accumulates on the water surface of the tank, flows into the floating sludge channel 21 by the floating sludge discharge plate 5 and the floating sludge scraper 20, and is transferred. The separated liquid separated from the pollutants in the polluted water tank 3 is separated from the separated water tank 6.
Flows into the separated liquid channel 7 and is carried out. In this way, sludge due to downward flow and upward flow is eliminated in a single tank. FIG. 2 shows an example in which an air diffuser for improving levitation is provided in the concentration tank. Water pipe 15
A diffuser tube 16 is provided in the inside, and is connected to the air tube 9. Diffuser 1
The bubbles from 6 and the sludge from the raw water inflow pipe 8 contact and mix in the water pipe 15 and rise with increasing buoyancy. At the same time, the sewage in the water pipe 15 floats as a whole, and sinks through the upper end of the water pipe 15 with the air lift action, and the flow of water in the polluted water tank 3 changes, and the sewage sludge becomes the center of the buoyant sludge. However, it can sufficiently cope with settling sludge. Instead of providing the air diffuser 16, a method of directly injecting air into the raw water inflow pipe and mixing the air may be used.

【0007】[0007]

【発明の効果】本発明によると、汚泥の質的変化、比重
の大小による沈降性、浮上性汚泥に対して対応が可能で
あり、本来の重力式濃縮槽としての特性を害なうことな
く、即ち簡易で省エネルギー的システムとして、流入汚
泥を受け入れることが可能である。また、流入量の変動
に対しても適応範囲が広い。
According to the present invention, it is possible to deal with qualitative changes in sludge, sedimentation due to the specific gravity, and floating sludge, without deteriorating the characteristics of the original gravity type thickening tank. That is, it is possible to receive the inflow sludge as a simple and energy-saving system. It also has a wide adaptation range for fluctuations in inflow.

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

【図1】上下向流濃縮槽の断面図FIG. 1 is a cross-sectional view of an up-down flow enrichment tank.

【符号の説明】[Explanation of symbols]

1 は、濃縮槽 2 は、仕切円筒 3 は、汚濁水槽 4 は、仕切円筒部 5 は、浮上汚泥排出板 6 は、分離水槽 7 は、分離液水路 8 は、原水流入管 9 は、空気管 10は、床盤 11は、スクレーパ 12は、汚泥ピット 13は、汚泥移送管 15は、導水管 16は、散気管 17は、駆動装置 18は、駆動軸 20は、浮上汚泥スクレーパ 21は、浮上汚泥水路 22は、ブリッジ 1 is a concentration tank 2, a partition cylinder 3, a polluted water tank 4, a partition cylinder part 5, a floating sludge discharge plate 6, a separation water tank 7, a separated liquid channel 8, a raw water inflow pipe 9, an air pipe 10, floor panel 11, scraper 12, sludge pit 13, sludge transfer pipe 15, water pipe 16, diffuser pipe 17, drive device 18, drive shaft 20, floating sludge scraper 21, floating Sludge channel 22 is a bridge

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 流入汚泥から沈降する汚泥を床盤(1
0)で受けて、スクレーパ(11)で汚泥ピット(1
2)に集めて排出し、分離液を分離液水路(7)より搬
出する重力式下向流の円形濃縮槽において、仕切円筒
(2)、仕切円錐部(4)、浮上汚泥排出板(5)を設
けて汚濁水槽(3)と分離水槽(6)に区分し、汚濁水
槽(3)内で沈降汚泥は下部床盤へ、浮上する汚濁物は
導水管(15)、仕切円筒円錐部(4)内側を経て浮上
汚泥排出板(5)、浮上汚泥スクレーパ(20)により
汚泥水路(21)より搬出することを特長とする上下向
流濃縮槽。
1. Sludge settling from inflow sludge is transferred to a floor (1).
0) and the sludge pit (1) with the scraper (11).
In a gravity-type downward-flow circular concentrating tank for collecting and discharging the separated liquid from the separated liquid channel (7), the partition cylinder (2), the partition cone (4), and the floating sludge discharge plate (5) ) Is provided to divide the tank into a polluted water tank (3) and a separated water tank (6). In the polluted water tank (3), the settled sludge is transferred to the lower floor, and the contaminants floating up are transferred to the water pipe (15) and the partitioning cylindrical cone ( 4) An up-down flow thickening tank characterized in that the sludge is discharged from the sludge channel (21) by the floating sludge discharge plate (5) and the floating sludge scraper (20) through the inside.
【請求項2】 請求項1の上下向流濃縮槽において、導
水管(15)内に散気管(16)を設け空気管(9)と
連結し、散気することを特長とする上下向流濃縮槽。
2. The up-down flow in the up-down flow enrichment tank according to claim 1, wherein a diffuser pipe (16) is provided in the water pipe (15) and connected to the air pipe (9) to diffuse air. Thickening tank.
JP10331832A 1998-10-19 1998-10-19 Upward and downward counter-current concentrator Pending JP2000117003A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP10331832A JP2000117003A (en) 1998-10-19 1998-10-19 Upward and downward counter-current concentrator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10331832A JP2000117003A (en) 1998-10-19 1998-10-19 Upward and downward counter-current concentrator

Publications (1)

Publication Number Publication Date
JP2000117003A true JP2000117003A (en) 2000-04-25

Family

ID=18248153

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10331832A Pending JP2000117003A (en) 1998-10-19 1998-10-19 Upward and downward counter-current concentrator

Country Status (1)

Country Link
JP (1) JP2000117003A (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
KR100391095B1 (en) * 2000-07-20 2003-07-12 제일유리공업 주식회사 A device using centrifuge for cooling water of processing glass
CN102805956A (en) * 2011-06-05 2012-12-05 赵峰 Vertical pipe type sludge-water separation treating device
CN103252115A (en) * 2013-05-31 2013-08-21 云南大红山管道有限公司 Dehydrating device for improving concentration of slurry
WO2019187355A1 (en) * 2018-03-28 2019-10-03 隆 玉城 Device for removing sediment/floating matter in water and on water surface
CN110606533A (en) * 2019-08-28 2019-12-24 北京国电龙源环保工程有限公司 Wet desulphurization clarification tank wastewater treatment structure and construction method thereof

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100391095B1 (en) * 2000-07-20 2003-07-12 제일유리공업 주식회사 A device using centrifuge for cooling water of processing glass
KR100374442B1 (en) * 2001-08-02 2003-03-08 인효석 Circular settling tank
CN102805956A (en) * 2011-06-05 2012-12-05 赵峰 Vertical pipe type sludge-water separation treating device
CN103252115A (en) * 2013-05-31 2013-08-21 云南大红山管道有限公司 Dehydrating device for improving concentration of slurry
WO2019187355A1 (en) * 2018-03-28 2019-10-03 隆 玉城 Device for removing sediment/floating matter in water and on water surface
CN110606533A (en) * 2019-08-28 2019-12-24 北京国电龙源环保工程有限公司 Wet desulphurization clarification tank wastewater treatment structure and construction method thereof

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