JPS5889995A - Treatment for night soil - Google Patents

Treatment for night soil

Info

Publication number
JPS5889995A
JPS5889995A JP56188129A JP18812981A JPS5889995A JP S5889995 A JPS5889995 A JP S5889995A JP 56188129 A JP56188129 A JP 56188129A JP 18812981 A JP18812981 A JP 18812981A JP S5889995 A JPS5889995 A JP S5889995A
Authority
JP
Japan
Prior art keywords
treatment
centrifugal
night soil
tank
specified time
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
JP56188129A
Other languages
Japanese (ja)
Other versions
JPH0474077B2 (en
Inventor
Shigeru Inami
茂 稲見
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.)
Nishihara Environment Co Ltd
Original Assignee
Nishihara Environmental Sanitation Research Corp
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 Nishihara Environmental Sanitation Research Corp filed Critical Nishihara Environmental Sanitation Research Corp
Priority to JP56188129A priority Critical patent/JPS5889995A/en
Publication of JPS5889995A publication Critical patent/JPS5889995A/en
Publication of JPH0474077B2 publication Critical patent/JPH0474077B2/ja
Granted 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)

Abstract

PURPOSE:To improve the workability in a night soil treatment by subjecting a liquid mixture after an aerating treatment of high concn. org. waste water to a centrifugal filtration treatment only for the specified time, adding flocculating agents to the separated liquid thereof then subjecting the liquid to centrifugal sepn. only for the specified time. CONSTITUTION:After night soil is charged into a temporally receiving tank 1 and is removed of sand, etc. by a settling treatment, the night soil is fed into a storage tank 2. From the tank 2, the night soil is pumped to a screen 3 by which extraneous materials are removed. Said pump is operated only for the specified time. The night soil is further supplied to an aerating tank 4, and the liquid mixture after the aeration is fed to a centrifugal filter 5, by which the greater part of solids are separated. Polymer flocculating agents are added to the separated liquid after the sepn. to flocculate the solids; thereafter, the SS are removed with a decanter type centrifugal separator 6. If the filter 5 and the separator 6 are both operated only for the specified time of 9-17hr, workability is improved.

Description

【発明の詳細な説明】 この発明はし尿処理において遠心r過工程および遠心分
離工程を用い、しかもこれらの運転を一定時間,例えば
昼間のみに行うし尿処理方法の改良に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an improvement in a human waste processing method that uses a centrifugal filtration step and a centrifugal separation step and performs these operations only during a certain period of time, for example, during the daytime.

従来のし尿処理方法として、例えば第1図に示す処理方
法が実施されている。このような方法を実施している処
理場では、最終沈殿池での処理が良好に行なわれている
か否かが間勉となる。特に小規模の処理場では夜間に放
流水質が悪化した場合等に朝まで全く対処策が講じられ
ず、水質の悪い処理水を放流したり、処理機能が害され
ることもあった。
As a conventional human waste treatment method, for example, the treatment method shown in FIG. 1 has been implemented. At treatment plants implementing such methods, it is important to check whether the treatment in the final sedimentation tank is being carried out properly. Particularly in small-scale treatment plants, when the quality of discharged water deteriorated during the night, no countermeasures were taken until the morning, resulting in poor quality treated water being discharged and treatment functions being impaired.

この発明は上記欠点を解消し、し尿処理において遠心P
過工程と遠心分離工程とを用い、処理を効果的に行い、
しかもこれらの運転を一定時間、例えば昼間のみに行い
し尿処理の作業性の向上を図るし尿処理方法を提供する
ことを目的とする。
This invention solves the above-mentioned drawbacks and uses a centrifugal P
The process is effectively carried out using a filtration process and a centrifugation process,
Moreover, it is an object of the present invention to provide a human waste disposal method in which these operations are performed for a certain period of time, for example, only during the daytime, in order to improve the workability of human waste disposal.

以下、この発明の一実施例についてm2図から第6図を
参照して説明する。
An embodiment of the present invention will be described below with reference to FIGS. m2 to 6.

この発明の一実施例の工程にはI42図に示すように,
バキュームカーからし尿を受は入れ、し尿中の砂等を除
去する仮受槽1と、この砂等の除去されたし尿を貯留す
る貯留槽2と、この貯留槽2からのし尿の夾雑物を除去
するスクリーン3と、夾雑物等が除去されたし尿を曝気
する曝気槽4と、この曝気処理されたし尿を遠心P過て
る遠心iF2過機5と、さらに遠心分離を行うスクリュ
ーデカンタ形の遠心分離機6とが配置され【いる。
As shown in Figure I42, the process of one embodiment of this invention includes the following steps:
A temporary storage tank 1 that receives human waste from a vacuum car and removes sand, etc. from the human waste, a storage tank 2 that stores the human waste from which sand and other substances have been removed, and removes impurities in the human waste from this storage tank 2. an aeration tank 4 for aerating the human waste from which impurities have been removed, a centrifugal iF2 filter 5 for passing the aerated human waste through a centrifugal P, and a screw decanter type centrifugal separator for further centrifugal separation. Machine 6 is located.

次にこの発明の動作について説明する。処理されるべき
し尿は、まず仮受槽1に投入され、沈殿処理によって砂
等が除去された後、貯留槽2へ送られる。
Next, the operation of this invention will be explained. Human waste to be treated is first put into a temporary storage tank 1, and after sand and the like are removed by sedimentation, it is sent to a storage tank 2.

その後、貯留槽2からポンプ(図示せず)によってスク
リーン3に送られ、夾雑物が除去されるか、このホン1
は一定時間(例えば昼間のみの9〜17時)のみ稼動す
る。
Thereafter, the storage tank 2 is sent to a screen 3 by a pump (not shown) to remove impurities.
operates only during certain hours (for example, from 9:00 to 17:00 only during the day).

次に夾雑物が除去されたし尿は、@気檜4に送られ、−
気処理を受ける(曝気処理工程)。この−気工程は単に
1つの曝気槽4であってもよいが、第3−に示すように
脱窒処理を含んでもよい。
Next, the human waste from which impurities have been removed is sent to @Kihino 4, and -
Receive air treatment (aeration treatment process). This aeration process may be performed in just one aeration tank 4, but may also include denitrification treatment as shown in the third aeration process.

さらに、この曝気工程は第5図に示すように@気槽4内
に生物付着用のP材を光填し付着−気槽としてもよい。
Furthermore, in this aeration step, as shown in FIG. 5, a P material for bioadhesion may be filled into the @air tank 4 to form an adhesion-air tank.

そしてwL2図に示すように上記曝気工程からの混合液
は遠心1過機5に送られ、ここで遠心濾過されて(遠心
r過工程)大部分の固形物が分離される。ここで、遠心
f’3m機5はそれ程目の細かいP布を使用韓ずに、あ
る程度の88分は通過してもよいこととすると、運転管
理が非常に容易となる◎ そしてこの遠心濾過工程で分離された伽紬液(固形分)
は上記曝気槽4へ返送され、査び曝気処理されることと
なるが、この返送によって曝気槽4内の微生物蓋が維持
できろ。
Then, as shown in Fig. wL2, the mixed liquid from the aeration step is sent to the centrifugal filter 5, where it is centrifugally filtered (centrifugal filtration step) to separate most of the solids. Here, if we assume that the centrifugal f'3m machine 5 does not use such fine-grained P cloth and that it can pass through for a certain amount of 88 minutes, operation management will be very easy.And this centrifugal filtration process Gapong liquid (solid content) separated by
The microorganisms are returned to the aeration tank 4 to be inspected and aerated, but the microorganisms in the aeration tank 4 can be maintained by this return.

他方、上記遠心e過工程で分離された分lIl液中には
、ある程度(例えば数百IR9/43 )のSSを含む
ので、高分子凝集剤を添加し、凝集した後にテカンタ形
遠心分離機6でSSを除去する(遠心分離工程)。
On the other hand, since the aliquot liquid separated in the centrifugation step contains a certain amount of SS (for example, several hundred IR9/43), a polymer flocculant is added and after flocculation, it is passed through a Tecanter type centrifuge 6. to remove SS (centrifugation step).

凝集した分離液が供給された遠心分離機6はスクリュー
デカンタ形のものがよいが固形物量が少なく、分離液量
が大きくなるために、遠心分離機6のプールの深さを大
きく取り、ケーキ排出口を軸に非常に近い位置とし、低
G(例えば1000G以下)で差速も小さくして運転す
るとよい。
The centrifugal separator 6 to which the flocculated separated liquid is supplied should preferably be of a screw decanter type, but since the amount of solids is small and the amount of separated liquid is large, the pool of the centrifugal separator 6 should be made deep enough to drain the cake. It is best to operate with the outlet located very close to the axis, with low G (for example, 1000 G or less) and with a small differential speed.

ここで上記遠心を過機5および遠心分離機6の運転は両
者共一定時間(例えば9〜17時)のみとすれば作業性
が非常に良(、しかも、その作動状態を常に監視できる
ので、し尿処理状態を常に良好に保つことができる◎ 尚、し尿の搬入は昼間のみなので、放流も昼間のみで全
く問題はない。
Here, if the centrifuge 5 and the centrifuge 6 are operated only for a certain period of time (for example, from 9 o'clock to 17 o'clock), the workability is very good (and since their operating status can be constantly monitored, The human waste treatment condition can always be kept in good condition◎ Furthermore, since human waste is only brought in during the day, it can also be discharged only during the day, so there is no problem at all.

第61は他の実施例の70−シートを示し、し尿の投入
、曝気処理工程、遠心濾過機5の稼動を各々別個に行っ
た実施例である。
No. 61 shows a 70-sheet of another example, and is an example in which the inputting of human waste, the aeration process, and the operation of the centrifugal filter 5 were performed separately.

例えば、−気は24時間連続で行い、遠心1過機5の稼
動は8〜12時の間に行い、ここで分離したam汚泥を
曝気槽4へ返送しく引抜)、他方分離液は高分子凝集剤
を添加後、遠心分離機6で処理を行う。そして上記濃縮
汚泥の曝気槽4への返送が終了した後に12〜14時の
間に新たなし尿の投入を行う。
For example, the aeration is carried out continuously for 24 hours, the operation of the centrifuge 1 filtration machine 5 is carried out between 8 o'clock and 12 o'clock, and the am sludge separated here is drawn out to be returned to the aeration tank 4), while the separated liquid is a polymer flocculant. After adding, processing is performed using a centrifuge 6. After the return of the thickened sludge to the aeration tank 4 is completed, fresh human waste is added between 12:00 and 14:00.

従って、投入されたし尿は、いわゆる引抜きが始まるま
での関必ず曝気されるので短絡することがない。
Therefore, the input human waste is always aerated until the so-called extraction begins, so there is no possibility of short circuit.

またし尿投入前に槽内は濃縮され、微生物濃度が高くな
っているのでF/M比を保ち易<、シかも投入直後は曝
気を連続していても、豊富な有機物の存在によって、嫌
気的条件となり投入開始前までに生成された硝#態窒素
の脱窒が活発に起こる。そして投入開始前までに硝化が
進行している。
In addition, the inside of the tank is concentrated before the human waste is added, and the microbial concentration is high, so it is easy to maintain the F/M ratio. Under these conditions, denitrification of the nitrate-nitrogen generated before the start of charging occurs actively. Nitrification has progressed by the time the input begins.

尚、し尿の投入、引抜きは昼間のみに行うので、作業性
がよく、しかも、し尿処理状態を監視することができる
Incidentally, since the human waste is put in and taken out only during the daytime, the workability is good and the human waste disposal state can be monitored.

以上のようKこの発明のし尿処理方法によれば、し尿処
理において曝気処理工程に加えて、遠心1過工程および
遠心分離工程を用い処理を効果的に行い、しかもこれら
の運転を一定時間、例えば昼間のみに行い、処理状態を
監視でき、作業性の向上が図れる。
As described above, according to the human waste treatment method of the present invention, in addition to the aeration process, the human waste treatment is effectively carried out using the centrifugation step and the centrifugation step, and these operations are continued for a certain period of time, e.g. It is carried out only during the day, and the processing status can be monitored, improving work efficiency.

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

第1図は従来のし尿処理方法の工程を示すフローシート
、第2図はこの発明方法の工程を示すフローシート、第
3図から第6図は他の実施例を示すフローシートを示す
。 1・・・仮受槽、2・φ・貯留槽、3・・・スクリーン
、4−・・曝気槽、5・・・遠心r過機、6・・・遠心
分離機。
FIG. 1 is a flow sheet showing the steps of a conventional human waste treatment method, FIG. 2 is a flow sheet showing the steps of the method of the present invention, and FIGS. 3 to 6 are flow sheets showing other embodiments. 1... Temporary receiving tank, 2-φ storage tank, 3... Screen, 4-... Aeration tank, 5... Centrifugal filtration machine, 6... Centrifugal separator.

Claims (1)

【特許請求の範囲】[Claims] し腋等の高濃度有機性廃水を曝気処理する曝気処理工程
と、この曝気処理工程からの混合液を一定時間のみ1c
遠心f過処理する遠心f過処理工程と、この遠心1過工
鴨からの分離液に凝集剤を添加した後、一定時間のみに
デカンタ形の遠心分離する遠心分離工程とを備えたし尿
処理方法。
The aeration process involves aerating high-concentration organic wastewater such as underarms, and the mixed liquid from this aeration process is heated for a certain period of time to 1 c.
A method for treating human waste comprising a centrifugal f overtreatment step in which the centrifugal F overtreatment is carried out, and a centrifugation step in which a flocculant is added to the separated liquid from the centrifuged duck and then centrifuged in a decanter for a certain period of time. .
JP56188129A 1981-11-24 1981-11-24 Treatment for night soil Granted JPS5889995A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP56188129A JPS5889995A (en) 1981-11-24 1981-11-24 Treatment for night soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP56188129A JPS5889995A (en) 1981-11-24 1981-11-24 Treatment for night soil

Publications (2)

Publication Number Publication Date
JPS5889995A true JPS5889995A (en) 1983-05-28
JPH0474077B2 JPH0474077B2 (en) 1992-11-25

Family

ID=16218226

Family Applications (1)

Application Number Title Priority Date Filing Date
JP56188129A Granted JPS5889995A (en) 1981-11-24 1981-11-24 Treatment for night soil

Country Status (1)

Country Link
JP (1) JPS5889995A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100352243B1 (en) * 1999-12-10 2002-09-16 에스아이비(주) A Treatment Method for Livestock Wastewater
JP2019005687A (en) * 2017-06-22 2019-01-17 Jfeエンジニアリング株式会社 Method and device for treating organic sewage containing fibrous materials

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52135560A (en) * 1976-05-10 1977-11-12 Chiyoda Chem Eng & Constr Co Ltd Microbial treating method of waste water
JPS5518156A (en) * 1978-07-25 1980-02-08 Matsushita Electric Ind Co Ltd Speaker
JPS5638190A (en) * 1979-09-06 1981-04-13 Kubota Ltd Treatment of night soil

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS52135560A (en) * 1976-05-10 1977-11-12 Chiyoda Chem Eng & Constr Co Ltd Microbial treating method of waste water
JPS5518156A (en) * 1978-07-25 1980-02-08 Matsushita Electric Ind Co Ltd Speaker
JPS5638190A (en) * 1979-09-06 1981-04-13 Kubota Ltd Treatment of night soil

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100352243B1 (en) * 1999-12-10 2002-09-16 에스아이비(주) A Treatment Method for Livestock Wastewater
JP2019005687A (en) * 2017-06-22 2019-01-17 Jfeエンジニアリング株式会社 Method and device for treating organic sewage containing fibrous materials

Also Published As

Publication number Publication date
JPH0474077B2 (en) 1992-11-25

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