JPS61171598A - Treatment of separated solution from digestion tank - Google Patents

Treatment of separated solution from digestion tank

Info

Publication number
JPS61171598A
JPS61171598A JP59154913A JP15491384A JPS61171598A JP S61171598 A JPS61171598 A JP S61171598A JP 59154913 A JP59154913 A JP 59154913A JP 15491384 A JP15491384 A JP 15491384A JP S61171598 A JPS61171598 A JP S61171598A
Authority
JP
Japan
Prior art keywords
tank
sludge
concn
digestion
liquid
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
JP59154913A
Other languages
Japanese (ja)
Inventor
Kunihiko Karashima
辛島 邦彦
Hironari Takabayashi
高林 宏成
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.)
Yaskawa Electric Corp
Original Assignee
Yaskawa Electric Manufacturing 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 Yaskawa Electric Manufacturing Co Ltd filed Critical Yaskawa Electric Manufacturing Co Ltd
Priority to JP59154913A priority Critical patent/JPS61171598A/en
Publication of JPS61171598A publication Critical patent/JPS61171598A/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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • 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 reduce the concn. of the org. substance of return water, by returning the separated solution separated from digested sludge in a digestion tank to a gravitational concn. tank along with the withdrawn sludge from a first sedimentation basin. CONSTITUTION:The separated solution of a digestion tank 15 is charged in a gravitational concn. tank along with the withdrawn sludge 8 from a first sedimentation basin 6. The high concn. separated solution of the digestion tank 15 is diluted to concn. receiving no sedimentation interference by the withdrawn sludge 11 from the first sedimentation basin 4 being the inflow sludge of the gravitational concn. tank 12 and excessive sludge 10. Flocs of sludge are formed so as to be grown on the solids contained in the separated solution as nuclei to promote the solid-liquid separation of the gravitational concn. tank 12. Therefore, the generation amount of digestion gas is increased to promote digestion.

Description

【発明の詳細な説明】 (産業上の利用分野〕 本発明は、汚泥処理に消化方式を採用している下水処理
設備における消化槽脱離液の処理方法に関するものであ
る。
DETAILED DESCRIPTION OF THE INVENTION (Industrial Field of Application) The present invention relates to a method for treating a digester separated liquid in a sewage treatment facility that employs a digestion method for sludge treatment.

〔従来の技術〕[Conventional technology]

一般的に、汚泥処理に消化方式を採用している下水処理
場が多い、その代表的フローは第2図に示すようなもの
である。これについて説明すると、流入水(1)と汚泥
処理系よりの返流水(2)が合流し、最初沈殿池流入水
(3)として最初沈殿池(4)に流入する。最初沈殿池
(4)で固液分離が行なわれ液相はエアレーションタン
ク(5)へ送られ、固相が最初沈殿池引抜汚泥(11)
として排出される。液相はエアレーーションタンク(5
1で活性汚泥法により生物処理され最終沈殿池(6)で
固液分離される。この液相は滅菌され放流水(7)とし
て場外へ排出する。固相は最終沈殿池引抜汚泥(8)と
して排出し、エアレーションタンク(5)への返送汚泥
(9)と余剰汚泥(10)に分けられる。最初沈殿池引
抜汚泥(11)と余剰汚泥(10)は重力濃縮槽(12
)で固液分離され、液相は重力濃縮槽越流水(13)と
して水処理系へ返流する。固相は重力濃縮汚泥(14)
として排出され、消化槽(15)へ投入され、汚泥の無
機化と固液分離が行なわれる。その固液分離後の液相が
脱離液(16)として水処理系へと返流され、固相が消
化汚泥(17)として排出される。このlη泥はその後
、脱水、乾燥、焼却等の処理がなされる。
In general, many sewage treatment plants use the digestion method for sludge treatment, and a typical flow is shown in Figure 2. To explain this, the inflow water (1) and the return water (2) from the sludge treatment system are combined and flow into the first settling tank (4) as the first settling tank inflow water (3). Solid-liquid separation is performed in the first settling tank (4), the liquid phase is sent to the aeration tank (5), and the solid phase is transferred to the first settling tank drawn sludge (11).
It is discharged as. The liquid phase is stored in an aeration tank (5
In step 1, it is subjected to biological treatment using an activated sludge method, and solid-liquid separation is carried out in the final settling tank (6). This liquid phase is sterilized and discharged outside the facility as effluent water (7). The solid phase is discharged as sludge drawn from the final settling tank (8) and divided into sludge (9) returned to the aeration tank (5) and surplus sludge (10). The sludge drawn from the initial settling tank (11) and the excess sludge (10) are stored in the gravity thickening tank (12).
), and the liquid phase is returned to the water treatment system as gravity thickener overflow water (13). The solid phase is gravity thickened sludge (14)
The sludge is discharged as sludge and put into the digestion tank (15), where the sludge is mineralized and solid-liquid separated. The liquid phase after the solid-liquid separation is returned to the water treatment system as a desorbed liquid (16), and the solid phase is discharged as digested sludge (17). This lη mud is then subjected to treatments such as dewatering, drying, and incineration.

以上述べた処理フローの下水処理場においては、−e的
に汚泥処理系よりの返流負荷が水処理系へ影響を及ぼし
、放流水質の悪化を起こすといわれている。
In a sewage treatment plant with the treatment flow described above, it is said that the return load from the sludge treatment system affects the water treatment system, causing deterioration of the quality of the effluent water.

ある下水処理場における放流水中有機物濃度の変動要因
について発明者らが調査した結果によれば、第1表のよ
うに汚泥処理系からの返流水によるものが約60%を占
めていた。中でも、消化槽脱離液の液量又はそれに含ま
れる固形物量の影響が極めて大きいことがわかった。
According to the results of an investigation by the inventors into the factors contributing to variations in organic matter concentration in effluent water at a certain sewage treatment plant, as shown in Table 1, approximately 60% of the variation was due to return water from the sludge treatment system. Among these, it was found that the influence of the amount of the digester desorbed liquid or the amount of solids contained therein is extremely large.

第1表 放流水中有機物濃度の変動要因〔発明が解決し
ようとする問題点〕 上述したように、従来の方法では、消化槽脱離液(16
)は、生物的難分解性(non−biodegrada
ble)物質を多く含むので、この脱離液(16)が最
初沈殿池(4)へ戻されることによって水処理系に大き
な負担がかかり、放流水質へ大きく影響を及ぼす結果と
なっている。
Table 1 Factors for variation in organic matter concentration in effluent water [Problems to be solved by the invention] As mentioned above, in the conventional method, the digester desorbed liquid (16
) are non-biodegradable
Since this desorbed liquid (16) is returned to the initial settling tank (4), it places a heavy burden on the water treatment system and has a large effect on the quality of the effluent water.

本発明は、汚泥処理に消化方式を採用している下水処理
設備において、返流水中のを機動濃度を軽減して、返流
負荷による放流水質への影響を防止することを目的とす
るものである。
The purpose of the present invention is to reduce the mobile concentration in return water in sewage treatment equipment that uses a digestion method for sludge treatment, and to prevent the impact of return load on the quality of effluent water. be.

〔問題点を解決するための手段〕[Means for solving problems]

本発明は、前記の下水処理設備において、消化槽脱離液
を最初沈殿池からの引抜汚泥と共に重力濃縮槽に投入す
るようにしたものであり、これにより重力濃縮槽の固液
分離を促進することができる・           
                    11〔実施
例〕 以下、本発明を第1図に示す実施例に基づいて説明する
0本発明と従来の処理方法との相違点は、消化槽(15
)の脱離液(16)を従来は直接、返流水(2)として
水処理系に戻しているが、本発明は消化槽(15)の脱
離液(16)を最初沈殿池(6)からの引抜汚泥(8)
と共に、重力濃縮槽(12)に投入していることである
。その他の処理フローは従来と同じである。
The present invention provides the aforementioned sewage treatment equipment in which the digester desorbed liquid is charged into the gravity thickening tank along with the sludge drawn from the initial settling tank, thereby promoting solid-liquid separation in the gravity thickening tank. be able to·
11 [Example] Hereinafter, the present invention will be explained based on the example shown in FIG. 1.The difference between the present invention and the conventional treatment method is that
Conventionally, the desorbed liquid (16) of the digester (15) is directly returned to the water treatment system as return water (2), but in the present invention, the desorbed liquid (16) of the digestion tank (15) is first returned to the sedimentation tank (6). Sludge extracted from (8)
At the same time, it is also put into the gravity concentration tank (12). Other processing flows are the same as before.

〔作用〕[Effect]

このように構成することにより、濃度の高い消化槽(1
5)の脱離液(16)が、重力濃縮槽(12)の流入l
η泥である最初沈殿池(4)からの引抜汚泥(11)、
余剰汚泥(10)により沈降干渉のない濃度に希釈され
、脱離液(16)中に含まれていた固形物、例えば無機
化物、土砂類が核となって汚泥のフロックを形成するこ
とにより、重力濃縮槽(12)の固液分離を促進するこ
とができる。
By configuring this way, a high-concentration digestion tank (1
The desorbed liquid (16) of 5) flows into the gravity concentration tank (12).
Sludge (11) drawn from the initial settling tank (4), which is η mud;
The excess sludge (10) is diluted to a concentration that does not interfere with sedimentation, and the solids contained in the desorbed liquid (16), such as minerals and sediment, become cores and form sludge flocs. Solid-liquid separation in the gravity concentration tank (12) can be promoted.

従って、重力濃縮汚泥濃度が高くなり、それが消化槽(
15)へ投入されることにより消化ガス発生■が増大す
ることになって消化が促進される。
Therefore, the concentration of gravity-thickened sludge increases, which increases in the digester (
15), the amount of digestive gas produced increases and digestion is promoted.

また脱離液(16)中の未分解有機物が上述の理由によ
り沈降しやす(なり、従来行われている消化槽(15)
の脱離液(16)を直接、水処理系へ返流する場合より
、未分解有機物の水処理系へ戻される割合が減少し、水
処理系への返流負荷が軽減され、放流水質が向上するこ
とになる。
In addition, undecomposed organic matter in the desorbed liquid (16) tends to settle due to the above-mentioned reasons.
Compared to the case where the desorbed liquid (16) is directly returned to the water treatment system, the proportion of undecomposed organic matter returned to the water treatment system is reduced, the return load to the water treatment system is reduced, and the quality of the effluent water is improved. It will improve.

また、このような処理フローの変更に伴って従来の下水
処理システムに変更をきたすような不都合は考えられな
い。
In addition, it is not conceivable that there would be any inconvenience caused by changing the conventional sewage treatment system due to such a change in the treatment flow.

〔発明の効果〕〔Effect of the invention〕

上述したように本発明によれば、下記のような効果を奏
する。
As described above, the present invention provides the following effects.

■ 最初沈殿池における固形物負荷が軽減される。■ Solids load in the initial settling tank is reduced.

■ 固形物濃度の高い脱離液が希釈され、本来沈降し易
い無機化物や土砂類が沈降し、それが核となってフロッ
クを形成し、重力濃縮槽の沈降性が増大する。
■ The desorbed liquid with a high concentration of solids is diluted, and inorganic substances and sediments, which are originally easy to settle, settle out, and these become cores to form flocs, increasing the sedimentation property of the gravity thickening tank.

■ 固形物濃度の高い脱離液が希釈されることにより未
分解有機物も沈降し易くなり、水処理、系への影響が軽
減され、放流水質が良好となる。
■ By diluting the desorbed liquid with a high concentration of solids, undecomposed organic matter becomes easier to settle, reducing the impact on water treatment and systems, and improving the quality of the effluent water.

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

第1図は本発明に係る方法の処理フローチャート、第2
図は従来・方法の処理フローチャートであ(1):流入
水 (2):返流水 (3):最初沈殿池への流入水 +4): Flt初沈殿池 (5):エアレーションタンク (6):最終沈殿池 (7):放流水 (8):最終沈殿池からの引抜汚泥 (9):返送汚泥 (10) :余剰汚泥 (11) :最初沈殿池からの引抜汚泥(12) :重
力濃縮槽 (13) : ’重力濃縮槽からの越流水(14) :
重力濃縮汚泥 (15) :消化槽 (16) :脱離液 (17) :消化汚泥
FIG. 1 is a processing flowchart of the method according to the present invention;
The figure is a processing flowchart of the conventional method (1): Inflow water (2): Return water (3): Inflow water to the primary sedimentation tank + 4): Flt primary sedimentation tank (5): Aeration tank (6): Final settling tank (7): Effluent water (8): Sludge drawn from the final settling tank (9): Returned sludge (10): Surplus sludge (11): Sludge drawn from the first settling tank (12): Gravity thickening tank (13): 'Overflow water from gravity thickener (14):
Gravity thickening sludge (15): Digestion tank (16): Desorption liquid (17): Digested sludge

Claims (1)

【特許請求の範囲】[Claims] 1、流入水を貯留する最初沈殿池と、同最初沈殿池から
の液相分を活性化汚泥法により生物処理するエアレーシ
ョンタンクと、同エアレーションタンクからの流入水を
固液分離する最終沈殿池と、前記最初沈殿池からの引抜
汚泥を濃縮する重力濃縮槽と、同濃縮槽で濃縮された重
力濃縮汚泥を消化処理する消化槽とを備えた下水処理設
備において、前記消化槽において消化汚泥から脱離され
た脱離液を、前記最初沈殿池からの引抜汚泥と共に重力
濃縮槽に返流することを特徴とする消化脱離液の処理方
法。
1. A primary sedimentation tank that stores inflow water, an aeration tank that biologically processes the liquid phase from the primary sedimentation tank using the activated sludge method, and a final sedimentation tank that separates solid-liquid inflow from the aeration tank. , in a sewage treatment facility equipped with a gravity thickening tank for concentrating the sludge drawn from the first settling tank, and a digestion tank for digesting the gravity thickened sludge concentrated in the thickening tank, the digested sludge is decomposed in the digestion tank. A method for treating digested and desorbed liquid, characterized in that the separated desorbed liquid is returned to a gravity thickening tank together with the sludge drawn from the initial settling tank.
JP59154913A 1984-07-24 1984-07-24 Treatment of separated solution from digestion tank Pending JPS61171598A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59154913A JPS61171598A (en) 1984-07-24 1984-07-24 Treatment of separated solution from digestion tank

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59154913A JPS61171598A (en) 1984-07-24 1984-07-24 Treatment of separated solution from digestion tank

Publications (1)

Publication Number Publication Date
JPS61171598A true JPS61171598A (en) 1986-08-02

Family

ID=15594693

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59154913A Pending JPS61171598A (en) 1984-07-24 1984-07-24 Treatment of separated solution from digestion tank

Country Status (1)

Country Link
JP (1) JPS61171598A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0719239A4 (en) * 1993-09-16 1998-07-29 Harold J Beard Mixed liquor wasting system and method

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0719239A4 (en) * 1993-09-16 1998-07-29 Harold J Beard Mixed liquor wasting system and method

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