JPS60143900A - Concentration device for sludge - Google Patents

Concentration device for sludge

Info

Publication number
JPS60143900A
JPS60143900A JP58248566A JP24856683A JPS60143900A JP S60143900 A JPS60143900 A JP S60143900A JP 58248566 A JP58248566 A JP 58248566A JP 24856683 A JP24856683 A JP 24856683A JP S60143900 A JPS60143900 A JP S60143900A
Authority
JP
Japan
Prior art keywords
sludge
layer
tank
centrifugal concentrator
water
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
JP58248566A
Other languages
Japanese (ja)
Inventor
Keiichi Kamio
神尾 恵一
Hiroto Haruki
春木 裕人
Koji Mishima
弘次 三嶋
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.)
Takuma Co Ltd
Takuma Research and Development Co Ltd
Original Assignee
Takuma Co Ltd
Takuma Research and Development Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Takuma Co Ltd, Takuma Research and Development Co Ltd filed Critical Takuma Co Ltd
Priority to JP58248566A priority Critical patent/JPS60143900A/en
Publication of JPS60143900A publication Critical patent/JPS60143900A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Activated Sludge Processes (AREA)
  • Treatment Of Sludge (AREA)

Abstract

PURPOSE:To concentrate excess sludge withdrawn from a final settling basin economically by feeding a layer of concentrated sludge by floatation and a layer of concentrated sludge by settling to a centrifugal concentrator, and feeding the mixture of the separated water and the excess sludge to the centrifugal concentrator. CONSTITUTION:A layer of floated solid matters is mixed or collected in a sludge collecting box 3d provided to an intermediate chamber Q, and then enters an external box 3e. On one hand, settled sludge is withdrawn by a pump 4 from the bottom 3c, combined with the sludge withdrawn by a pump 5 from the external box 3e and enters a tank 6. The sludge in the tank 6 is withdrawn by a pump 7 and fed to a centrifugal concentrator 8. On the other hand, an intermediate clear layer contg. only small amt. of solid matters interposed between the floated solid matters layer and the settled sludge layer is discharged through a conduit pipe 9 and fed back to a filthy water treatig facility. The solid matter content of the intermediate water in this stage is reduced to less amt. than the content of solid matter in the separated water immediately after it is discharged from the centrifugal concentrator 8.

Description

【発明の詳細な説明】 (技術分野) 本発明祉各穐活性汚泥法によシ汚水処理を行う際に生成
する余剰汚泥を濃縮する汚泥濃縮装置に関するものであ
る。
DETAILED DESCRIPTION OF THE INVENTION (Technical Field) The present invention relates to a sludge concentrator for concentrating surplus sludge generated during sewage treatment using the activated sludge method.

(背景技術) 活性汚泥法には種種の変形があるが、その典型的な例を
示すと第1図に示すように、被処理汚水は、普通、先づ
最初沈殿池Aに入り生汚泥を沈降分離した後、返送汚泥
が加えられ、次いで曝気槽Bに入り、空気(酸素)が吹
込まれ、好気性雰囲気が保たれ、また、汚水と汚泥とが
懸濁状態となって緊密に接触し、好気性微生物による汚
泥の生物分解が行われる。汚水は、さらに最終沈殿池C
に至り、静置されて汚泥を沈降分離するが、その一部は
返送汚泥として曝気槽Bに返送され、残部はいわゆる余
剰汚泥りとして引抜かれる。上澄水は処理水として放出
される(最初沈殿池Aを省略した処理装置もある。)。
(Background Art) There are various variations of the activated sludge method, but as shown in Figure 1, a typical example is that sewage to be treated usually first enters settling tank A to collect raw sludge. After sedimentation and separation, return sludge is added, then enters the aeration tank B, where air (oxygen) is blown in to maintain an aerobic atmosphere, and the sewage and sludge are in a suspended state and in close contact. , biodegradation of sludge by aerobic microorganisms takes place. The wastewater is further transferred to the final settling tank C.
The sludge is then allowed to stand still and the sludge is sedimented and separated, but a portion of it is returned to the aeration tank B as return sludge, and the remainder is pulled out as so-called surplus sludge. The supernatant water is discharged as treated water (some treatment devices omit the initial settling tank A).

本発明が関係するのは、余剰汚泥りの処理装置である。The present invention relates to an apparatus for treating excess sludge.

従来法では、余剰汚泥りを、第2図に例示するような遠
心濃縮機にかけて、脱水濃縮するのが普通であった。
In conventional methods, excess sludge is usually dehydrated and concentrated using a centrifugal thickener as illustrated in FIG.

先づ、第2図の遠心濃縮機について説明すると、中空円
筒形(右側1部は円錐形)ケーシングEの左端は中心部
に同心円状の開口部Fが設けられており、環状端板Gの
側端中心部は分離水出口i[Hを形成している。ケーシ
ングEの内部に、スクリューコンベヤー形式の回転体K
が同心回転自在に設けである。汚泥は、図の左端りから
、ケーシングE内に送入され、回転体Kにより回転運動
し、液面Mを形成する。中心部に近い、したがって、低
比重の分離水が堰Hを超えて細字矢印の方向に排出され
、ケーシングEの内面に近い濃縮された汚泥は、スクリ
ューNで、太字矢印で示す右方に送られ、右端から排出
される。本発明の遠心濃縮機が本例に限定されないのは
言うまでもない。この種円心製縮機の遠心効果は、経済
的な理由から、約800〜2000程度が望ましく、そ
の際分離した分離水中には、汚泥中の固形分の10〜2
0重量%が含まれるのが普通である。それゆえこの分離
水はそのまま放出する訳にいかず、従来、最初沈殿池A
または曝気槽Bへ返水するのが普通で、そのため、汚水
処理装置全体としての効率・能力を著しく減少させてい
た。
First, to explain the centrifugal concentrator shown in Fig. 2, the left end of the hollow cylindrical casing E (the right side part is conical) has a concentric opening F in the center, and the annular end plate G has a concentric opening F in the center. The center of the side end forms a separated water outlet i[H. Inside the casing E, there is a rotating body K in the form of a screw conveyor.
are provided for concentric rotation. The sludge is fed into the casing E from the left end of the figure, rotated by a rotating body K, and forms a liquid level M. Separated water near the center and therefore having a low specific gravity is discharged over the weir H in the direction of the thin arrow, and concentrated sludge near the inner surface of the casing E is sent by screw N to the right as shown by the bold arrow. and is ejected from the right end. It goes without saying that the centrifugal concentrator of the present invention is not limited to this example. For economical reasons, the centrifugal effect of this type of circular core shrinking machine is desirably about 800 to 2,000, and the separated water contains 10 to 2 of the solid content in the sludge.
Usually it contains 0% by weight. Therefore, this separated water cannot be released as it is, and conventionally, the first sedimentation tank A
Otherwise, the water is normally returned to the aeration tank B, which significantly reduces the efficiency and capacity of the sewage treatment system as a whole.

(発明の目的) 上記事情にかんがみ、本発明の目的は、活性汚泥法によ
る汚水処理装置の最終沈殿池から引抜かれる余剰汚泥の
、より経済的な濃縮装置tを提供することである。
(Object of the Invention) In view of the above circumstances, an object of the present invention is to provide a more economical thickening device t for excess sludge drawn out from the final settling tank of a sewage treatment device using an activated sludge method.

さらに具体的に言うと、本発明の目的は、汚泥濃縮機か
ら分離される分離水を余剰汚泥と混合することによシ、
汚泥の前濃縮を行い、かつ分離水の再処理を同時に行え
る。余剰汚泥の経済的濃縮装置を提供することである。
More specifically, it is an object of the present invention to achieve a
Sludge can be pre-concentrated and separated water can be reprocessed at the same time. The object of the present invention is to provide an economical thickening device for surplus sludge.

(発明の構成と作用) 本発明の実施例を示す第3図において、第1図に示した
余剰汚泥りは、導管(1)を通り、途中で、導管(2)
から送入される遠心濃縮機の分離水と混合したのち、分
離槽(3)に送入される。分離槽(3)は、水平断面が
、矩形、円形その他適宜の形状の槽で、隔壁3a 、3
bにより、下部開放状態で内室P、中間室Q1外室Rに
分かれている。
(Structure and operation of the invention) In FIG. 3 showing an embodiment of the present invention, the excess sludge shown in FIG.
After mixing with separated water from the centrifugal concentrator, the water is sent to the separation tank (3). The separation tank (3) is a tank with a rectangular, circular, or other appropriate shape in horizontal cross section, and has partition walls 3a, 3
b, it is divided into an inner chamber P, an intermediate chamber Q1, and an outer chamber R with the lower part open.

前記混合汚泥水は導管(4)から、分シ准槽(3)の内
室Pに送入される。送入された汚泥水中の浮遊固形物の
一部は浮上して浮上固形分層となシ、一部は沈降して分
離汚泥層を形成し、底部(3c)に溜まる。浮上固形分
層は中間室Qに設けた集泥箱(3d)内に溢大または集
泥され、外函(3e)に入る。一方沈降した汚泥は底部
(3c)からポンプ(4)によシ引抜かれ、外函(3e
)からポンプ(5)により引抜かれた汚泥と合流して、
貯槽(6)に入る。このとき余剰汚泥りは1〜2重量%
となり減容されている。貯4(6)内の汚泥はポンプ(
7)により引抜かれ、遠心濃縮機(8)にかけられる。
The mixed sludge water is sent from the conduit (4) to the inner chamber P of the separation tank (3). Some of the suspended solids in the introduced sludge water float to the surface and form a floating solids layer, while some of them settle to form a separated sludge layer and accumulate at the bottom (3c). The floating solid layer overflows or collects mud in a mud collection box (3d) provided in the intermediate chamber Q, and enters the outer box (3e). On the other hand, the settled sludge is pulled out from the bottom (3c) by the pump (4) and placed in the outer box (3e).
) is combined with the sludge drawn out by the pump (5),
Enter the storage tank (6). At this time, the excess sludge is 1 to 2% by weight.
Therefore, the volume has been reduced. The sludge in storage 4 (6) is pumped (
7) and placed in a centrifugal concentrator (8).

一方、浮上固形分層と沈降汚泥層との中間の固形杯の少
ない中間清泄層は導管(9)を通って排出され、汚水処
理場へ返送される。このときの中間水は遠心濃縮機から
排出直後の分離水よりも固形分は除去減少されている。
On the other hand, the intermediate excretory layer between the floating solids layer and the settled sludge layer, which has few solids, is discharged through the conduit (9) and returned to the sewage treatment plant. The intermediate water at this time has less solid content removed than the separated water immediately after being discharged from the centrifugal concentrator.

この実施例の場合、例えば、固形分0.12〜0.13
重量%を含む分離水が先づ余剰汚泥と混合して前述の処
理を受ける。一方、余剰汚泥中の固形分は約0.5〜0
.6重量%であるが、上記処理によシ、遠心濃縮機(8
)K供給される汚泥中の固形分はz1〜2..2重量%
に殖え、導管(9)からの中間水は固形分0.03〜0
.1重量%で、その量は全余剰汚泥の約84〜89重量
%である。
In the case of this example, for example, the solid content is 0.12 to 0.13
The separated water containing % by weight is first mixed with excess sludge and subjected to the aforementioned treatment. On the other hand, the solid content in excess sludge is approximately 0.5 to 0.
.. 6% by weight, but due to the above treatment, a centrifugal concentrator (8%
) The solid content in the sludge supplied with K is z1 to 2. .. 2% by weight
The intermediate water from the conduit (9) has a solid content of 0.03 to 0.
.. 1% by weight, the amount is about 84-89% by weight of the total excess sludge.

余剰汚泥の主構成要素は、活性汚泥であって、この活性
汚泥が一種の吸着を起こすことが知られているが、他方
遠心製縮機分離水には溶解および取込まれた気l′6I
金多く含んでいる。分離槽(3)内で起こる固形物質の
浮上濃縮および沈降濃縮、および分離水側から見た分離
水中の固形物の除去減少は、この余剰汚泥の吸着作用と
、分離水中の気泡による凝集浮上作用の相乗効果による
と言える。
The main component of surplus sludge is activated sludge, and it is known that this activated sludge causes a kind of adsorption, but on the other hand, the centrifugal compressor separated water contains dissolved and incorporated air l'6I.
Contains a lot of gold. The flotation concentration and sedimentation concentration of solid substances that occur in the separation tank (3), and the reduction in removal of solids in the separated water as seen from the separated water side, are due to the adsorption effect of this excess sludge and the coagulation and flotation effect due to air bubbles in the separated water. This can be said to be due to the synergistic effect of

遠心濃縮機(8)の+p縮汚泥は、例えば、固形分4−
′6チの組成を持ち、貯槽QOで貯蔵し、または直接、
適宜処置される。
For example, the +p reduced sludge from the centrifugal concentrator (8) has a solid content of 4-
'6-chi composition, stored in storage tank QO or directly,
Appropriate treatment will be taken.

上記実施例の説明から明らかなように、本発明では、導
管(9)から引抜いた中間水水量と導管(2)からの分
離液量との差だけ、遠心濃縮機(8)にかかる容積負荷
が減るのが、その主要効果である。そのほか、最終的に
下水処理場へ返送される固形物も、従来法のi−1に減
少し、回収固形物(濃縮工程で分離液または中間水とし
て排出される固形物を差引いた、濃縮汚泥として正味排
出される固形物)を当シの消費動力は、余剰汚泥濃度を
0,6重id %とすると、従来法1871(支)Vt
に対して拳法では45餡■セ′tとなシ、大IIIを省
エネルギー効果が認められる。
As is clear from the description of the above embodiments, in the present invention, the volumetric load applied to the centrifugal concentrator (8) is equal to the difference between the amount of intermediate water drawn out from the conduit (9) and the amount of separated liquid from the conduit (2). Its main effect is to reduce In addition, the solids ultimately returned to the sewage treatment plant have been reduced to i-1 of the conventional method, and the recovered solids (thickened sludge, minus the solids discharged as separated liquid or intermediate water in the concentration process) Assuming that the excess sludge concentration is 0.6%, the power consumption of this system is as follows: conventional method 1871 (support) Vt
On the other hand, in Kempo, it is recognized that the energy saving effect is 45 陡■se't and Nasi, Dai III.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は、汚水処理装置の一般的な構成を示す工程図。 第2図は、遠心濃縮機の構造の1例を示す断面図。第3
図は、本発明の構成を示す工程図である。 A・・・最初沈殿池 B・・・曝気槽 C・・・最終沈殿池− E・・・遠心濃縮機のケーシング K・・・遠心濃縮機の回転体 M・・遠心濃縮機内の液面 N・・・遠心製縮機回転体のスクリュ 3・・・−分離槽 6・・・貯槽 8・・遠心濃縮機 10・・・貯槽 出 願 人 株式会社タ クマ
FIG. 1 is a process diagram showing the general configuration of a sewage treatment device. FIG. 2 is a sectional view showing an example of the structure of a centrifugal concentrator. Third
The figure is a process diagram showing the configuration of the present invention. A... Initial settling tank B... Aeration tank C... Final settling tank - E... Casing of centrifugal concentrator K... Rotating body of centrifugal concentrator M... Liquid level N in centrifugal concentrator ...Screw of centrifugal compressor rotor 3...-Separation tank 6...Storage tank 8...Centrifugal concentrator 10...Storage tank Applicant: Takuma Co., Ltd.

Claims (1)

【特許請求の範囲】 1、汚水を、曝気槽で、酸素の存在の下で生物分解し、
次に(最終)沈殿池で、汚泥を沈降分離し、1部を曝気
槽に返送し、残部を余剰汚泥として取出し遠心濃縮機で
処理する工程を含む汚水処理法において: ・ 該余剰汚泥を、遠心濃縮機へ送入する前に遠心#縮
機から生ずる分離水と混合した後、分離槽で、浮上濃縮
汚泥層と、沈殿濃縮汚泥層と、中間静澄槽とに層別し、
中間静澄ノーを系外に排出し、浮上濃縮汚泥層と沈殿濃
縮汚泥層とを前記遠心濃縮機に送入し、この分離水(前
記分離水と同じ)を余剰汚泥と混合して遠心濃縮機に送
入し、遠心濃縮した汚泥層1へ 出する構造を含む汚泥濃縮装置。
[Claims] 1. Biodegrading wastewater in the presence of oxygen in an aeration tank,
Next, in a sewage treatment method that includes a step of separating the sludge by sedimentation in a (final) settling tank, returning one part to the aeration tank, and taking out the remaining part as surplus sludge and treating it with a centrifugal thickener: - The surplus sludge is Before being sent to the centrifugal thickener, it is mixed with separated water produced from the centrifugal compressor, and then stratified in a separation tank into a floating thickened sludge layer, a settled thickened sludge layer, and an intermediate clarification tank.
The intermediate clarified water is discharged out of the system, the floated thickened sludge layer and the sedimented thickened sludge layer are sent to the centrifugal thickener, and this separated water (same as the separated water) is mixed with excess sludge and centrifugally concentrated. A sludge thickening device that includes a structure for sending sludge into a sludge machine and discharging it to a centrifugally concentrated sludge layer 1.
JP58248566A 1983-12-28 1983-12-28 Concentration device for sludge Pending JPS60143900A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58248566A JPS60143900A (en) 1983-12-28 1983-12-28 Concentration device for sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58248566A JPS60143900A (en) 1983-12-28 1983-12-28 Concentration device for sludge

Publications (1)

Publication Number Publication Date
JPS60143900A true JPS60143900A (en) 1985-07-30

Family

ID=17180045

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58248566A Pending JPS60143900A (en) 1983-12-28 1983-12-28 Concentration device for sludge

Country Status (1)

Country Link
JP (1) JPS60143900A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6422399A (en) * 1987-07-20 1989-01-25 Nishihara Om Tech Co Ltd Automatic sludge thickening device
JPH0390700U (en) * 1989-12-28 1991-09-17

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6422399A (en) * 1987-07-20 1989-01-25 Nishihara Om Tech Co Ltd Automatic sludge thickening device
JPH0390700U (en) * 1989-12-28 1991-09-17

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