JPH0468040B2 - - Google Patents

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Publication number
JPH0468040B2
JPH0468040B2 JP60111158A JP11115885A JPH0468040B2 JP H0468040 B2 JPH0468040 B2 JP H0468040B2 JP 60111158 A JP60111158 A JP 60111158A JP 11115885 A JP11115885 A JP 11115885A JP H0468040 B2 JPH0468040 B2 JP H0468040B2
Authority
JP
Japan
Prior art keywords
sludge
value
capillary suction
time
cst
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
JP60111158A
Other languages
Japanese (ja)
Other versions
JPS61268399A (en
Inventor
Akio Okada
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.)
NGK Insulators Ltd
Original Assignee
NGK Insulators 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 NGK Insulators Ltd filed Critical NGK Insulators Ltd
Priority to JP60111158A priority Critical patent/JPS61268399A/en
Publication of JPS61268399A publication Critical patent/JPS61268399A/en
Publication of JPH0468040B2 publication Critical patent/JPH0468040B2/ja
Granted legal-status Critical Current

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  • Treatment Of Sludge (AREA)

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は都市下水汚泥のような有機性汚泥をフ
イルタープレス脱水機やベルトプレス脱水機等に
よつて脱水処理するに先立つて行われる有機性汚
泥の調質方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION (Field of Industrial Application) The present invention relates to an organic sludge treatment process that is performed prior to dewatering organic sludge such as municipal sewage sludge using a filter press dehydrator, belt press dehydrator, etc. This relates to a method for refining sludge.

(従来の技術) 有機性汚泥の脱水処理場においては、脱水工程
の前工程として有機性汚泥に高分子凝集剤を加え
て攪拌し、フロツクを形成させる調質工程が置か
れている。従来、このような調質工程において
は、フロツクを急速に凝集させるために例えば周
速0.6〜1.3m/s程度の高速度で攪拌羽根を回転
させる急速攪拌が行われているが、凝集完了後、
脱水機へ送られるまでの時間が長い場合には一旦
形成されたフロツクが破壊され、汚泥の濾過性が
著しく阻害されて脱水処理が困難化するという問
題があつた。またフロツクの破壊を防止するため
に周速0.4m/s程度の低速度で緩速攪拌を行う
とフロツクの凝集完了までに時間がかかり、脱水
処理場全体の能率を低下させるという問題があつ
た。
(Prior Art) In a dewatering treatment plant for organic sludge, as a pre-process to the dewatering process, there is a refining process in which a polymer flocculant is added to organic sludge and stirred to form flocs. Conventionally, in such a refining process, rapid stirring is performed by rotating stirring blades at a high circumferential speed of, for example, 0.6 to 1.3 m/s in order to rapidly agglomerate the flocs. ,
If it takes a long time to send the sludge to the dehydrator, the flocs once formed are destroyed, which significantly impedes the filterability of the sludge and makes dewatering difficult. In addition, if slow stirring was performed at a peripheral speed of about 0.4 m/s to prevent floc destruction, it would take time for the flocs to coagulate, reducing the efficiency of the entire dehydration treatment plant. .

(発明が解決しようとする問題点) 本発明はこのような従来の問題点を解決して、
フロツクの凝集を急速に完了させることができ、
しかも一旦形成されたフロツクの破壊を生ずるこ
とのない有機性汚泥の調質方法を目的として完成
されたものである。
(Problems to be solved by the invention) The present invention solves these conventional problems,
The flocculation can be completed rapidly,
Moreover, it was completed with the aim of providing a method for refining organic sludge that does not cause the destruction of flocs once formed.

(問題点を解決するための手段) 本発明は、有機性汚泥に高分子凝集剤を加えて
凝集させた凝集汚泥を毛細管吸引時間測定装置に
供試し、瀘紙に滴下したときの湿潤域が所定地点
まで拡大するに要にする時間によつて表される毛
細管吸引時間値を測定し、その毛細管吸引時間値
がほぼ最小値となるまで急速攪拌し、その後凝集
フロツクが沈降しない程度の緩速攪拌を継続的に
行うことを特徴とするものである。
(Means for Solving the Problems) The present invention provides flocculated sludge obtained by adding a polymer flocculant to organic sludge and flocculating it to a capillary suction time measuring device. The capillary suction time value, expressed as the time required for expansion to a predetermined point, is measured, and the capillary suction time value is rapidly stirred until it reaches approximately the minimum value, and then stirred at a slow speed that does not allow the flocs to settle. It is characterized by continuous stirring.

次に本発明を図面を参照しつつ更に詳細に説明
すると、有機性汚泥は供給管1により凝集混和槽
2の内部へ供給され、凝集剤添加管3から例えば
分子量が70万以下のカチオン系の高分子凝集剤が
汚泥の固形分当り1.5%程度の比率で添加され、
急速攪拌羽根4によつて例えば32rpmの速度で急
速攪拌される。この攪拌中試料採取管5から凝集
汚泥サンプルが採取され、毛細管吸引時間測定装
置により毛細管吸引時間値(以下CST値と記す)
が一定時間間隔で測定される。
Next, the present invention will be described in more detail with reference to the drawings. Organic sludge is supplied to the inside of a coagulation mixing tank 2 through a supply pipe 1, and a cationic sludge with a molecular weight of 700,000 or less is supplied from a flocculant addition pipe 3. A polymer flocculant is added at a ratio of about 1.5% based on the solid content of the sludge,
Rapid stirring is performed by the rapid stirring blade 4 at a speed of, for example, 32 rpm. During this stirring, a flocculated sludge sample is collected from the sample collection tube 5, and the capillary suction time value (hereinafter referred to as CST value) is collected using a capillary suction time measuring device.
is measured at regular time intervals.

ここでCSTとはCapillary Suction Time(毛細
管吸引時間)の略であつて、汚泥を特定の瀘紙の
中心に滴下したときの湿潤域が中心点から30mmの
地点から45mmの地点まで拡大するに要する時間に
よつて汚泥の濾過特性を評価するものである。な
お、CST値についての詳細は、例えば下水道協
会誌、VOL.15、No.168、1978年6月号に掲載の
「汚泥濾過性の評価指標としてのCSTについて」
と題する笠倉、今泉等の論文に記載されている。
このCST値は小さいぼど濾過特性が優れたもの
であることを意味する。本発明者はこのCST値
について研究を重ねた結果、汚泥に高分子凝集剤
を添加したうえで攪拌を行うと、汚泥のCST値
はフロツクの凝集が進行するとともに次第に低下
するが、CST値の最小値及び最小値となるまで
の攪拌時間は攪拌速度によつて異なり、58rpm
(周速1.03m/秒)、32rpm(周速0.57m/秒)の急
速攪拌では20〜30分で最小値に達した後にCST
値が再び上昇するに対して、22rpm(周速0.39
m/秒)の緩速攪拌の場合には最小値となるまで
に90分以上を要し、その後も最小値が維持される
ことを知つた。
Here, CST is an abbreviation for Capillary Suction Time, and it is the time required for the moist area to expand from 30 mm to 45 mm from the center when sludge is dropped into the center of a specific filter paper. The filtration characteristics of sludge are evaluated based on time. For more information on CST values, see, for example, "About CST as an evaluation index for sludge filterability" published in the Journal of Japan Sewage Works Association, VOL.15, No.168, June 1978 issue.
It is described in a paper by Kasakura, Imaizumi et al.
Although this CST value is small, it means that the filtration properties are excellent. As a result of repeated research on this CST value, the present inventor found that when a polymer flocculant is added to sludge and then stirred, the CST value of the sludge gradually decreases as floc flocculation progresses; The minimum value and the stirring time to reach the minimum value vary depending on the stirring speed, 58 rpm
(peripheral speed 1.03 m/s), CST after reaching the minimum value in 20 to 30 minutes with rapid stirring at 32 rpm (peripheral speed 0.57 m/s)
22 rpm (peripheral speed 0.39) whereas the value increases again
It was found that in the case of slow stirring (m/sec), it takes more than 90 minutes to reach the minimum value, and that the minimum value is maintained even after that.

そこで本発明においては、有機性汚泥に高分子
凝集剤を加えて凝集させた凝集汚泥を毛細管吸引
時間測定装置に供試し、CST値を測定する。そ
して第3に示すように、CST値がほぼ最小値と
なるまで急速攪拌を行い、次にオーバーフロー管
6を介して汚泥を凝集汚泥保持槽7へ移動させて
緩速攪拌羽根8により凝集フロツクが沈降しない
程度の例えば22rpmの速度で緩速攪拌を継続す
る。この緩速攪拌に移行した後は汚泥は脱水処理
に適した性状に保たれるから、排出管9から何時
でもフイルタープレス脱水機やベルトプレス脱水
機へ供給することができる。なお、急速攪拌と緩
速攪拌とを同一の槽内で行わせることもできるこ
とは言うまでもない。
Therefore, in the present invention, flocculated sludge obtained by adding a polymer flocculant to organic sludge and flocculating it is subjected to a capillary suction time measuring device to measure the CST value. Then, as shown in the third figure, rapid stirring is performed until the CST value reaches almost the minimum value, and then the sludge is transferred to the flocculated sludge holding tank 7 via the overflow pipe 6, and the flocculated flocs are stirred by the slow stirring blades 8. Slow stirring is continued at a speed of, for example, 22 rpm to prevent sedimentation. After shifting to this slow agitation, the sludge is maintained in a state suitable for dewatering treatment, so it can be supplied from the discharge pipe 9 to a filter press dehydrator or belt press dehydrator at any time. It goes without saying that rapid stirring and slow stirring can be performed in the same tank.

(実施例) 次に本発明の実施例を示す。(Example) Next, examples of the present invention will be shown.

1m×1m×1.5mの凝集混和槽2へ下水汚泥
1m3を入れ、予めジヤーテストで決定された適正
薬注率(汚泥固形分当り1.5%)で高分子凝集剤
を投入し、32rpmの急速攪拌を行つた。これとと
もに凝集汚泥を毛細管吸引時間測定装置に供試
し、CST値を測定した。そして急速攪拌を開始
してから約20分後にCST値が17.1秒の最小値に達
したので汚泥を凝集汚泥保持槽7へ移送し、
22rmpの緩速攪拌を継続的に行つた。その後の
CST値は第3図に示すように最小値を維持し、
フロツクの破壊は生じなかつた。緩速攪拌へ移行
した後30分を経過した汚泥をフイルタープレス
脱水機によつて濾過圧4Kg/cm2、濾過時間10分、
圧搾圧力15Kg/cm2、圧搾時間10分の条件で脱水し
たところ、水分70.2%のケーキが得られ、このと
きの濾過速度は2.73Kg・DS/m2・Hrであつた。
なお、32rpmの急速攪拌を同一時間にわたり継続
した場合には、CST値は18.5秒となり、これを同
一条件で脱水した結果、水分72.5%のケーキとな
り、濾過速度は2.13Kg・DS/m2・Hrであつた。
Pour 1 m 3 of sewage sludge into a 1 m x 1 m x 1.5 m flocculation mixing tank 2, add polymer flocculant at the appropriate chemical injection rate (1.5% per sludge solid content) determined in advance by a jar test, and rapidly stir at 32 rpm. I went there. At the same time, the flocculated sludge was subjected to a capillary suction time measuring device to measure the CST value. Approximately 20 minutes after starting rapid stirring, the CST value reached the minimum value of 17.1 seconds, so the sludge was transferred to the flocculated sludge holding tank 7.
Slow stirring at 22 rpm was performed continuously. after that
The CST value maintains the minimum value as shown in Figure 3,
No destruction of the flocs occurred. The sludge that has passed 30 minutes after shifting to slow stirring is filtered using a filter press dehydrator at a filtration pressure of 4 Kg/cm 2 and a filtration time of 10 minutes.
When dehydration was performed under conditions of a compression pressure of 15 Kg/cm 2 and a compression time of 10 minutes, a cake with a moisture content of 70.2% was obtained, and the filtration rate at this time was 2.73 Kg・DS/m 2・Hr.
In addition, when rapid stirring at 32 rpm is continued for the same time, the CST value is 18.5 seconds, and when dehydrated under the same conditions, a cake with a moisture content of 72.5% is obtained, and the filtration rate is 2.13 Kg・DS/m 2・It was Hr.

(発明の効果) 本発明は以上の説明から明らかなように、有機
性汚泥に高分子凝集剤を加えた後に急速攪拌を行
うのでフロツクを短時間内に凝集させることがで
き、またその後は緩速攪拌に移行させるので一旦
形成されたフロツクを破壊することなく汚泥性状
を濾過に適した状態に長時間維持することができ
る。しかも急速攪拌から緩速攪拌への切替え時期
を汚泥の濾過特性を正確に表わすCST値がほぼ
最小値となる時期としたので、従来のように勘や
経験に頼ることなく汚泥を濾過に最適の状態に的
確に調質することができるものである。なお、同
一性状の汚泥については、CST値の測定をその
都度行う必要のないこは言うまでもなく、タイマ
ーにより緩速攪拌への切替えを行わせることもで
きる。
(Effects of the Invention) As is clear from the above explanation, the present invention performs rapid stirring after adding a polymer flocculant to organic sludge, so flocs can be flocculated within a short time, and after that, the flocs can be flocculated slowly. By shifting to rapid agitation, the sludge properties can be maintained in a state suitable for filtration for a long period of time without destroying the flocs once formed. Furthermore, since the timing of switching from rapid agitation to slow agitation is set to the time when the CST value, which accurately represents the filtration characteristics of sludge, is almost at its minimum value, the sludge can be optimized for filtration without relying on intuition or experience as in the past. It is possible to precisely refine the condition. Note that for sludge with the same properties, it is needless to say that it is not necessary to measure the CST value each time, and it is also possible to switch to slow stirring using a timer.

このように本発明は有機性汚泥を脱水処理する
ための前工程としての調質方法として好適なもの
であり、産業の発展に寄与するところは極めて大
である。
As described above, the present invention is suitable as a refining method as a pre-process for dehydrating organic sludge, and will greatly contribute to the development of industry.

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

第1図は本発明の実施に使用される調質装置の
概略的な断面図、第2図は攪拌速度によるCST
値の変化を示すグラフ、第3図は本発明の方法に
おけるCST値の変化を示すグラフである。 2:凝集混和槽、4:急速攪拌羽根、7:凝集
汚泥保持槽、8:緩速攪拌羽根。
Figure 1 is a schematic cross-sectional view of the tempering device used in the implementation of the present invention, and Figure 2 is a CST according to the stirring speed.
Graph showing changes in values. FIG. 3 is a graph showing changes in CST values in the method of the present invention. 2: coagulation mixing tank, 4: rapid stirring blade, 7: flocculating sludge holding tank, 8: slow stirring blade.

Claims (1)

【特許請求の範囲】[Claims] 1 有機性汚泥に高分子凝集剤を加えて凝集させ
た凝集汚泥を毛細管吸引時間測定装置に供試し、
瀘紙に滴下したときの湿潤域が所定地点まで拡大
するに要する時間によつて表される毛細管吸引時
間値を測定し、その毛細管吸引時間値がほぼ最小
値となるまで急速攪拌し、その後凝集フロツクが
沈降しない程度の緩速攪拌を継続的に行うことを
特徴とする有機性汚泥の調質方法。
1. Coagulated sludge obtained by adding a polymer flocculant to organic sludge and flocculating it was subjected to a capillary suction time measurement device.
The capillary suction time value, which is expressed by the time required for the wet area to expand to a predetermined point when dropped on filter paper, is measured, and the capillary suction time value is rapidly stirred until it reaches almost the minimum value, and then the flocculation is carried out. A method for refining organic sludge, which is characterized by continuously performing slow agitation to an extent that flocs do not settle.
JP60111158A 1985-05-23 1985-05-23 Method for conditioning organic sludge Granted JPS61268399A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP60111158A JPS61268399A (en) 1985-05-23 1985-05-23 Method for conditioning organic sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP60111158A JPS61268399A (en) 1985-05-23 1985-05-23 Method for conditioning organic sludge

Publications (2)

Publication Number Publication Date
JPS61268399A JPS61268399A (en) 1986-11-27
JPH0468040B2 true JPH0468040B2 (en) 1992-10-30

Family

ID=14553947

Family Applications (1)

Application Number Title Priority Date Filing Date
JP60111158A Granted JPS61268399A (en) 1985-05-23 1985-05-23 Method for conditioning organic sludge

Country Status (1)

Country Link
JP (1) JPS61268399A (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5382356A (en) * 1991-11-29 1995-01-17 Tokyo Metropolitan Method and apparatus for controlling sludge dewatering
JP3787970B2 (en) * 1997-08-08 2006-06-21 栗田工業株式会社 Sludge dewatering method
FR3030485B1 (en) * 2014-12-19 2019-08-09 Veolia Water Solutions & Technologies Support FLOATING REAGENT ASSISTED SLUDGE DEHYDRATION METHOD AND INSTALLATION FOR IMPLEMENTING SUCH A METHOD.

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5481558A (en) * 1977-12-12 1979-06-29 Hitachi Zosen Corp Method of adding and mixing coagulants in the treatment of sludge
JPS57102297A (en) * 1980-12-19 1982-06-25 Hitachi Plant Eng & Constr Co Ltd Pretreatment of sludge dehydration

Also Published As

Publication number Publication date
JPS61268399A (en) 1986-11-27

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