JP2668010B2 - Sludge filtration and concentration equipment - Google Patents

Sludge filtration and concentration equipment

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Publication number
JP2668010B2
JP2668010B2 JP6129509A JP12950994A JP2668010B2 JP 2668010 B2 JP2668010 B2 JP 2668010B2 JP 6129509 A JP6129509 A JP 6129509A JP 12950994 A JP12950994 A JP 12950994A JP 2668010 B2 JP2668010 B2 JP 2668010B2
Authority
JP
Japan
Prior art keywords
sludge
valve
air
section
filtrate
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
JP6129509A
Other languages
Japanese (ja)
Other versions
JPH0768107A (en
Inventor
寛 本橋
康弘 三井
真一郎 江川
正徳 衛藤
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.)
Ebara Corp
Original Assignee
Ebara 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 Ebara Corp filed Critical Ebara Corp
Priority to JP6129509A priority Critical patent/JP2668010B2/en
Publication of JPH0768107A publication Critical patent/JPH0768107A/en
Application granted granted Critical
Publication of JP2668010B2 publication Critical patent/JP2668010B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は、上水処理,産業用水処
理,下水処理,し尿処理,産業排水処理などで発生する
汚泥をろ過濃縮するための装置に関するもので、特に汚
泥を天日乾燥床や、加圧脱水機,遠心脱水機,凍結融解
機等で脱水する場合の前処理として使用する汚泥ろ過濃
縮装置に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an apparatus for filtering and condensing sludge generated in water treatment, industrial water treatment, sewage treatment, human waste treatment, industrial waste water treatment, etc. The present invention relates to a sludge filtration / concentration apparatus used as a pretreatment for dehydration using a bed, a pressure dehydrator, a centrifugal dehydrator, a freeze-thaw machine, or the like.

【従来の技術】[Prior art]

【0002】従来、上水処理,産業用水処理,下水処
理,し尿処理,産業排水処理などで発生する汚泥を脱水
する場合、汚泥に鉄塩等の無機凝集剤,石灰、または高
分子凝集剤等の脱水助剤を添加し、水中造粒脱水機,真
空ろ過機,加圧ろ過機,遠心脱水機,ベルトプレス型脱
水機等の脱水機で脱水処理していた。近年、特に上水処
理,産業用水処理等の分野で、薬注なしの天日乾燥床や
加圧脱水機で脱水処理するケースが増えてきている。こ
のような脱水処理をする場合、天日乾燥床や、加圧脱水
機へ供給する際の汚泥の濃度が非常に重要であり、汚泥
濃度が薄いと天日乾燥床や、加圧脱水機での処理効率が
著しく低下する。従来、汚泥の前濃縮にはシックナーな
どの沈降法(沈殿法)が用いられてきたが、最近では汚
泥中に有機物や水酸化アルミニウム等の濃縮しにくい成
分の割合が増加し、沈降法では十分に濃縮できないこと
が多くなってきた。
Conventionally, when dewatering sludge generated in water treatment, industrial water treatment, sewage treatment, human waste treatment, industrial wastewater treatment, etc., an inorganic coagulant such as iron salt, lime, or a polymer coagulant is added to the sludge. And a dewatering aid such as an underwater granulation dehydrator, a vacuum filter, a pressure filter, a centrifugal dehydrator, and a belt press dehydrator. In recent years, in particular in the fields of water treatment, industrial water treatment, and the like, the number of cases of dehydration using a sun-dry bed or a pressure dehydrator without chemical injection has been increasing. When performing such a dehydration treatment, the concentration of sludge when supplying to a solar drying bed or a pressure dehydrator is very important. The efficiency drops significantly. Conventionally, the sedimentation method (sedimentation method) such as thickener has been used for pre-concentration of sludge. However, recently, the ratio of components that are difficult to concentrate, such as organic substances and aluminum hydroxide, has increased in the sludge. Have not been able to be concentrated.

【0003】そのため、従来では図5に示すようなろ過
濃縮装置が用いられていた。即ち、密閉槽1内に水平の
仕切板2によって汚泥濃縮部3とその上部にろ液を集め
る集液部4が区画形成され、汚泥濃縮部3には汚泥流入
弁5を備えた汚泥流入管6が連設され、集液部4にはろ
液弁7を備えたろ液流出管8と空気抜弁9を備えた空気
抜管10が連設されている。さらに、汚泥濃縮部3内に
は、支持体の外周にろ布を巻き付け、一端を開放し他端
を閉鎖した筒状フィルターエレメント(以下単にエレメ
ントという)11が配設され、各開放端部付近が仕切板
2に固定され、エレメント11内に透過したろ液がその
開放端を経て集液部4内に流れるようになっている。ま
た、密閉槽1内下方部は濃縮汚泥排出部12が形成さ
れ、濃縮汚泥排出弁13を備えた濃縮汚泥排出管14が
連設されている。
For this reason, conventionally, a filtration and concentration device as shown in FIG. 5 has been used. That is, a sludge thickening part 3 and a liquid collecting part 4 for collecting a filtrate on the sludge thickening part 3 are formed in the closed tank 1 by a horizontal partition plate 2, and the sludge thickening part 3 is provided with a sludge inlet pipe provided with a sludge inlet valve 5. A filtrate outlet pipe 8 having a filtrate valve 7 and an air vent pipe 10 having an air vent valve 9 are connected to the liquid collecting part 4. Further, in the sludge concentrating unit 3, a tubular filter element (hereinafter simply referred to as an element) 11 having a filter cloth wrapped around the outer periphery of the support and having one end opened and the other end closed is provided. Is fixed to the partition plate 2, and the filtrate permeated into the element 11 flows into the liquid collecting section 4 via its open end. A concentrated sludge discharge portion 12 is formed in a lower part in the closed tank 1, and a concentrated sludge discharge pipe 14 provided with a concentrated sludge discharge valve 13 is continuously provided.

【0004】このようなろ過濃縮装置は、図6に示すよ
うに、汚泥流入管6を、吸込側が原汚泥貯槽15に連な
る汚泥ポンプ16の吐出側に連結し、原汚泥貯槽15に
貯留された原汚泥を、汚泥ポンプ16にて汚泥流入管6
を経て密閉槽1内の汚泥濃縮部3に供給するが、原汚泥
を汚泥ポンプ16によって圧入するか、あるいは集液部
4側を減圧することによって、エレメント11内外に生
じた差圧によりエレメント11の外側に汚泥が付着し濃
縮される一方、ろ液はエレメント11の内部に透過して
集液部4に集められ、ろ液流出管8から流出する。この
ような操作により、エレメント11の外側に付着し所定
濃度に汚泥が濃縮された時には、原汚泥の供給を停止
し、戻し弁17を開いて戻し管18から汚泥濃縮部3内
の未濃縮汚泥を原汚泥貯槽15に戻したのち戻し弁17
を閉じ、汚泥濃縮部3内を大気に開放したのち、エレメ
ント11内に圧力空気などをブローして外側に付着して
いる濃縮汚泥を剥離し、濃縮汚泥は濃縮汚泥排出部12
に落下し、濃縮汚泥排出弁13を開いて濃縮汚泥排出管
14から排出される。そして濃縮汚泥の剥離,排出工程
終了後は、濃縮汚泥排出弁13を閉じ、汚泥濃縮部3内
の大気開放を遮断し、再び汚泥ポンプ16にて原汚泥貯
槽15内の汚泥を汚泥濃縮部3に充満したのち、前述の
ようなろ過濃縮が行われる。
[0006] In such a filtration and concentration apparatus, as shown in FIG. 6, the sludge inflow pipe 6 is connected to the discharge side of a sludge pump 16 whose suction side is connected to the raw sludge storage tank 15, and is stored in the raw sludge storage tank 15. The raw sludge is fed to the sludge inflow pipe 6 by the sludge pump 16.
Is supplied to the sludge concentrating section 3 in the closed tank 1 through the sludge pump 16. The raw sludge is injected by the sludge pump 16 or the pressure in the liquid collecting section 4 is reduced, so that the differential pressure generated inside and outside the element 11 causes While the sludge adheres to the outside and is concentrated, the filtrate permeates into the inside of the element 11, is collected in the liquid collecting section 4, and flows out from the filtrate outflow pipe 8. When the sludge is attached to the outside of the element 11 and concentrated to a predetermined concentration by such an operation, the supply of the raw sludge is stopped, the return valve 17 is opened, and the unconcentrated sludge in the sludge concentration section 3 is returned from the return pipe 18. To the raw sludge storage tank 15, and then a return valve 17
Is closed, and the inside of the sludge thickening section 3 is opened to the atmosphere, and then the pressurized air or the like is blown into the element 11 to peel off the thickened sludge adhering to the outside.
And the concentrated sludge discharge valve 13 is opened to be discharged from the concentrated sludge discharge pipe 14. After the separation and discharge steps of the concentrated sludge, the concentrated sludge discharge valve 13 is closed, the opening of the sludge concentration section 3 to the atmosphere is shut off, and the sludge in the raw sludge storage tank 15 is again removed by the sludge pump 16. , And then filtration and concentration are performed as described above.

【0005】[0005]

【発明が解決しようとする課題】このような汚泥充満工
程,ろ過濃縮工程,未濃縮汚泥排出工程,濃縮汚泥剥
離,排出工程を1サイクルとした従来の装置では、次の
ような多くの問題点を有していた。 未濃縮汚泥排出工程における密閉槽1から原汚泥貯
槽15への未濃縮汚泥の返送は、動力費等の低減のため
にも自然流下方式が好ましく、そのために原汚泥貯槽1
5の高水位(HWL)は密閉槽1より低いことが必要
で、平地においては原汚泥貯槽15を埋設、あるいは密
閉槽1を高架にせねばならず、建設費が多くなる。 未濃縮汚泥が原汚泥貯槽15に返送されると、原汚
泥貯槽15の容量は最大返送量分を見込まなければなら
ず、非常に大きくなる。 ろ過濃縮工程が終了した時点での密閉槽1内の未濃
縮汚泥量は、密閉槽1内の集液部4とエレメント11内
ろ液部を除いた60〜80%程度と、非常に大きな量で
ある。このため、未濃縮汚泥排出工程及び次回のろ過濃
縮工程前の汚泥充満工程に要する時間、いわゆる雑時間
が増え、1サイクル当たりの所要時間も多くなる。さら
に、汚泥充満工程における汚泥ポンプ16の稼動によ
り、動力費も多くなる。 未濃縮汚泥排出工程により、密閉槽1内のエレメン
ト11が空気と接触することになる。さらに、空気ブロ
ー等にて濃縮汚泥の剥離を行うと、均等に剥離できない
ばかりかエレメント11内に残留又は付着しているろ液
等が酸化状態になる。そのため、原汚泥貯槽15におい
て、あるいはそれ以前に行われた濃縮操作等において、
還元状態でイオン化されていた鉄,マンガン等が酸化さ
れてエレメント11に付着し、その通気度の低下,ろ過
速度の低下ともなり、寿命も著しく短くなる。 本発明は、このような従来の問題点を解決し、従来の汚
泥充満工程,未濃縮汚泥排出工程を行うことなく、ろ過
濃縮装置内の汚泥濃縮部を汚泥で満杯にした状態のまま
で濃縮汚泥の剥離,排出を行い、雑時間,ランニングコ
ストの低減,設備の簡素化,エレメントの目詰まり防止
等を図ることができる汚泥ろ過濃縮装置を提供すること
を目的としている。
The conventional apparatus having such a sludge filling step, filtration and concentration step, unconcentrated sludge discharge step, concentrated sludge stripping and discharge step as one cycle has many problems as follows. Had. The return of the non-concentrated sludge from the closed tank 1 to the raw sludge storage tank 15 in the non-concentrated sludge discharge step is preferably performed by a natural flow method in order to reduce the power cost and the like.
The high water level (HWL) of No. 5 needs to be lower than that of the closed tank 1, and the raw sludge storage tank 15 must be buried or the closed tank 1 must be elevated on level ground, which increases construction costs. When the unconcentrated sludge is returned to the raw sludge storage tank 15, the capacity of the raw sludge storage tank 15 must be large enough to allow for the maximum amount of returned sludge, and becomes very large. The amount of unconcentrated sludge in the closed tank 1 at the end of the filtration / concentration step is a very large amount of about 60 to 80% excluding the liquid collecting section 4 in the closed tank 1 and the filtrate section in the element 11. Is. Therefore, the time required for the unconcentrated sludge discharge step and the sludge filling step before the next filtration and concentration step, that is, so-called miscellaneous time, increases, and the time required for one cycle also increases. Further, the operation of the sludge pump 16 in the sludge filling step increases the power cost. By the unconcentrated sludge discharging step, the element 11 in the closed tank 1 comes into contact with air. Further, if the concentrated sludge is peeled off by air blow or the like, not only the peeling cannot be carried out uniformly, but also the filtrate or the like remaining or adhering to the inside of the element 11 is in an oxidized state. Therefore, in the raw sludge storage tank 15, or in a concentration operation or the like performed before that,
Iron, manganese, etc., which have been ionized in the reduced state, are oxidized and adhere to the element 11, which lowers the air permeability and the filtration rate, resulting in a significantly shortened life. The present invention solves such a conventional problem and concentrates a sludge enrichment unit in a filtration concentrator while being filled with sludge without performing a conventional sludge filling process and an unconcentrated sludge discharging process. An object of the present invention is to provide a sludge filtration / concentration device capable of removing and discharging sludge, reducing rough time, running cost, simplifying equipment, and preventing element clogging.

【0006】[0006]

【課題を解決するための手段】本発明は、密閉槽1内に
汚泥濃縮部3と集液部4とを仕切板2で区画形成し、汚
泥濃縮部3内に一端を開放して他端を閉鎖した複数の筒
状フィルターエレメント11を仕切板2に垂下配設し、
その開放端部を集液部4に連通し、該集液部4にろ液弁
7のあるろ液流出管8を設け、前記密閉槽1の汚泥濃縮
部3内に汚泥流入弁5のある汚泥流入管6から汚泥を供
給し、前記筒状フィルターエレメント11内に透過した
ろ液を集液部4を経て槽外に流出させて汚泥のろ過濃縮
を行う装置において、前記汚泥濃縮部3内上部に連通す
る空気抜管20と、該空気抜管20に設けた空気抜弁1
9とを備え、前記集液部4に空気抜弁9を備えた空気抜
管10を設けると共に、空気流入弁21を備え、空気源
に連なる空気管22と、真空弁23を備え真空源に連な
る真空管24とを連通配備したものである。
According to the present invention, a sludge thickening section 3 and a liquid collecting section 4 are formed in a closed tank 1 by a partition plate 2, and one end is opened in the sludge thickening section 3 and the other end is opened. A plurality of tubular filter elements 11 having closed are suspended from the partition plate 2,
The open end communicates with the liquid collecting part 4, a filtrate outlet pipe 8 having a filtrate valve 7 is provided in the liquid collecting part 4, and a sludge inflow valve 5 is provided in the sludge concentrating part 3 of the closed tank 1. In an apparatus for supplying sludge from a sludge inflow pipe 6 and allowing the filtrate permeated into the tubular filter element 11 to flow out of the tank via a liquid collecting section 4 to perform filtration and concentration of the sludge, the sludge concentration section 3 An air bleeding pipe 20 communicating with the upper part, and an air bleeding valve 1 provided in the air bleeding pipe 20
A vacuum pipe provided with an air inflow valve 21 and connected to an air source, and a vacuum pipe provided with a vacuum valve 23 and connected to a vacuum source. 24 in communication with each other.

【0007】[0007]

【作用】汚泥流入管6より汚泥を密閉槽1に供給してろ
過濃縮するには、空気抜弁19,空気流入弁21,真空弁
23,濃縮汚泥排出弁13を閉として、汚泥流入弁5,ろ
液弁7,空気抜弁9を開とし、汚泥ポンプ16を稼動し
て汚泥濃縮部3内に汚泥を押込むと、汚泥濃縮部3内に
貯留されている汚泥に圧力がかかり、フィルターエレメ
ント11によってろ過されてフィルターエレメント11
の外側には汚泥が付着して濃縮され、ろ液はフィルター
エレメント11内を経て集液部4に貯留され、ろ液弁7
から流出する。この時、集液部4内のろ液はHWLに保
たれる。このようなろ過濃縮工程終了後は、フィルター
エレメント11の外側に付着している濃縮汚泥の剥離,
排出工程に移るが、ろ過濃縮工程終了後、汚泥濃縮部3
内の汚泥を排出することなく、そのままとし、汚泥ポン
プ16を停止し、汚泥流入弁5,ろ液弁7,空気抜弁9
を閉にし、真空弁23,空気抜弁19を開にし、集液部
4を真空状態とし、ろ液のレベルをHWLに保つ。次
に、真空弁23を閉、空気抜弁9を開にすると、集液室
4内の真空状態が破壊され、集液室4内のろ液がフィル
ターエレメント11内へ逆流し、フィルターエレメント
11の外側に付着している濃縮汚泥が剥離されると同時
にフィルターエレメント11は洗浄される。この時、エ
レメント11が伸縮自在のものを使用しているときはフ
ィルターエレメント11は伸びるから、濃縮汚泥の剥離
は物理的力により、より効果的となる。この剥離した濃
縮汚泥は密閉槽(1)内下方部に沈降し、再び汚泥ポン
プ16を作動してろ過工程に入る。
In order to supply sludge from the sludge inflow pipe 6 to the closed tank 1 for filtration and concentration, the air release valve 19, the air inflow valve 21, the vacuum valve 23, and the concentrated sludge discharge valve 13 are closed, and the sludge inflow valve 5, When the filtrate valve 7 and the air release valve 9 are opened and the sludge pump 16 is operated to push the sludge into the sludge concentration section 3, pressure is applied to the sludge stored in the sludge concentration section 3, and the filter element 11 is pressed. Filtered by the filter element 11
The sludge adheres to the outside of the filter and is concentrated, and the filtrate is stored in the liquid collecting section 4 through the inside of the filter element 11.
Spill out of. At this time, the filtrate in the liquid collecting section 4 is kept at HWL. After completion of the filtration and concentration step, the concentrated sludge adhering to the outside of the filter element 11 is peeled off,
Move to the discharge step, but after the filtration and concentration step, the sludge concentration section 3
The sludge inside is not discharged but left as it is, the sludge pump 16 is stopped, and the sludge inflow valve 5, the filtrate valve 7, and the air vent valve 9
Is closed, the vacuum valve 23 and the air bleeding valve 19 are opened, the liquid collecting part 4 is brought into a vacuum state, and the level of the filtrate is kept at HWL. Next, when the vacuum valve 23 is closed and the air vent valve 9 is opened, the vacuum state in the liquid collecting chamber 4 is broken, and the filtrate in the liquid collecting chamber 4 flows back into the filter element 11 and the filter element 11 At the same time as the concentrated sludge adhering to the outside is removed, the filter element 11 is washed. At this time, when the element 11 is of an elastic type, the filter element 11 expands, so that the separation of the concentrated sludge becomes more effective by physical force. The peeled concentrated sludge settles in the lower part of the closed tank (1), and the sludge pump 16 is operated again to start the filtration step.

【0008】[0008]

【実施例】本発明の実施例を図1及び図2の例で説明す
ると、密閉槽1内に汚泥濃縮部3と集液部4とを仕切板
2で区画形成し、汚泥濃縮部3内に一端を開放して他端
を閉鎖した複数の筒状フィルターエレメント11を仕切
板2に垂下配設し、その開放端部を集液部4に連通し、
該集液部4にろ液弁7のあるろ液流出管8を設け、前記
密閉槽1の汚泥濃縮部3内に汚泥流入弁5のある汚泥流
入管6から汚泥を供給し、前記筒状フィルターエレメン
ト11内に透過したろ液を集液部4を経て槽外に流出さ
せて汚泥のろ過濃縮を行う装置において、前記汚泥濃縮
部3内上部に連通する空気抜管20と、該空気抜管20
に設けた空気抜弁19とを備え、前記集液部4に空気抜
弁9を備えた空気抜管10を設けると共に、空気流入弁
21を備え、空気源に連なる空気管22と、真空弁23
を備え真空源に連なる真空管24とを連通配備した構成
の汚泥ろ過濃縮装置としてある。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS An embodiment of the present invention will be described with reference to FIGS. 1 and 2. In FIG. 1, a sludge thickening section 3 and a liquid collecting section 4 are partitioned by a partition plate 2 in a closed tank 1. A plurality of tubular filter elements 11 having one end opened and the other end closed are disposed hanging on the partition plate 2, and the open ends thereof are communicated with the liquid collecting section 4.
A filtrate outflow pipe 8 having a filtrate valve 7 is provided in the liquid collecting section 4, and sludge is supplied from a sludge inflow pipe 6 having a sludge inflow valve 5 into the sludge enrichment section 3 of the closed tank 1. An apparatus for draining the filtrate permeated into the filter element 11 to the outside of the tank via the liquid collecting part 4 to filter and concentrate the sludge, comprising: an air vent pipe 20 communicating with the upper part inside the sludge concentrating part 3;
, An air bleeding pipe 10 provided with the air bleeding valve 9 in the liquid collecting part 4, an air pipe 22 provided with an air inflow valve 21 and connected to an air source, and a vacuum valve 23.
And a sludge filtration / concentration apparatus configured to communicate with a vacuum tube 24 connected to a vacuum source.

【0009】前記フィルターエレメント11としては、
公知の多孔管等の支持体の外周にろ布を巻き付けたも
の、中空糸,多孔質セラミックスろ過筒,多孔質の樹脂
系ろ過筒等を使用することができるが、コイルスプリン
グ等の弾性支持体で筒状ろ布を支持した伸縮自在の構造
のフィルターエレメント11を使用するのが好ましい。
また、図2のように前記密閉槽1は、汚泥流入管6を、
吸込側が原汚泥貯槽15に連なる汚泥ポンプ16の吐出
側に連結し、原汚泥貯槽15に貯留された原汚泥を、汚
泥ポンプ16にて汚泥流入管6を経て密閉槽1内の汚泥
濃縮部3に供給するが、原汚泥を汚泥ポンプ16によっ
て圧入するか、あるいは集液部4がっわを減圧すること
によって、フィルターエレメント11内外に生じた差圧
によりフィルターエレメント11の外側に汚泥が付着し
濃縮される一方、ろ液はフィルターエレメント11の内
部に透過して集液部4に集められ、ろ液流出管8から流
出するようにしてある。
As the filter element 11,
A known support such as a perforated tube with a filter cloth wrapped around it, a hollow fiber, a porous ceramics filter tube, a porous resin filter tube, or the like can be used, but an elastic support such as a coil spring can be used. It is preferable to use a filter element 11 having a stretchable structure supporting a cylindrical filter cloth.
In addition, as shown in FIG.
The suction side is connected to the discharge side of a sludge pump 16 connected to the raw sludge storage tank 15, and the raw sludge stored in the raw sludge storage tank 15 is passed through the sludge inflow pipe 6 by the sludge pump 16 and the sludge concentration section 3 in the closed tank 1 When the raw sludge is injected by the sludge pump 16 or the pressure of the liquid collecting part 4 is reduced, sludge adheres to the outside of the filter element 11 due to the differential pressure generated inside and outside the filter element 11. While being concentrated, the filtrate permeates into the filter element 11, is collected in the liquid collecting part 4, and flows out from the filtrate outlet pipe 8.

【0010】なお、濃縮汚泥をフィルターエレメント1
1から剥離する際に、前述のように集液室4を真空状態
にしてから剥離を行うと均等に剥離できるので好ましい
が、真空状態にせずにいきなり空気抜弁19を開放する
だけでも剥離できる。この際には、真空弁23,空気抜
弁9の操作は必要ではなく閉にしておく。また、前述の
集液室4の真空破壊後に空気抜弁9を閉にし、空気流入
弁21を開にして集液部4内に圧力空気又は他から圧力
水を導いて逆流するろ液を加圧すれば、濃縮汚泥の剥離
が一層効果的に行われる。また、真空弁23が閉,空気
抜弁9が閉の状態で、空気管22の空気流入弁21を開
にすると、減圧状態から一気に加圧状態になり、ろ液が
フィルターエレメント11内に急激に逆流するため、最
も効率の良い濃縮汚泥の剥離とフィルターエレメント1
1の洗浄が行われる。
The concentrated sludge is supplied to the filter element 1
As described above, it is preferable that the liquid collecting chamber 4 is evacuated and then peeled off when the liquid is collected from the substrate 1. Since it is possible to perform uniform peeling, it is also possible to release the air vent valve 19 without opening the vacuum state. At this time, the operation of the vacuum valve 23 and the air vent valve 9 is not necessary and is kept closed. Further, after the above-described vacuum break of the liquid collecting chamber 4, the air vent valve 9 is closed, the air inflow valve 21 is opened, and pressurized air or pressure water is introduced into the liquid collecting part 4 to pressurize the filtrate flowing backward. If it does, stripping of concentrated sludge will be performed more effectively. When the air inflow valve 21 of the air pipe 22 is opened while the vacuum valve 23 is closed and the air vent valve 9 is closed, the pressure is changed from the reduced pressure state to the pressurized state at a stretch, and the filtrate is rapidly injected into the filter element 11. The most efficient separation of concentrated sludge and the filter element 1
Washing 1 is performed.

【0011】剥離された濃縮汚泥は、濃縮汚泥排出部1
2に沈降するが、一旦濃縮された汚泥はその形状が壊れ
ることなく未濃縮汚泥中を沈降し、またフィルターエレ
メント11内に逆流し、流出するろ液は微々たる量であ
るから、未濃縮汚泥をわずかに希釈する程度であり、濃
縮汚泥はほとんど希釈されることなく濃縮汚泥排出部1
2の底部に堆積し、堆積した濃縮汚泥は、濃縮汚泥排出
弁13を開にし、場合によってはポンプを使用すること
によって濃縮汚泥排出管14から排出される。なお、濃
縮汚泥排出用のポンプとしてはスネークポンプあるいは
その他の容積形ポンプを使用すると良い。この濃縮汚泥
剥離,排出工程としては、濃縮汚泥排出管14から排出
される汚泥の濃度を測定して、所定濃度以下になった時
あるいは所定時間経過後に終了し、再びろ過濃縮行程に
切換えるが、排出汚泥濃度を自動的に測定し自動停止及
び切換を可能にすれば便利である。かくて、再びろ過濃
縮工程が行われるが、汚泥濃縮部3内は、濃縮汚泥の剥
離に使われた僅かなろ液と未濃縮汚泥とでほとんど満杯
状態となっており、従来のような汚泥充満工程はほとん
ど必要ない。
The stripped concentrated sludge is supplied to the concentrated sludge discharge section 1
The sludge that has once concentrated is sedimented in the non-concentrated sludge without breaking its shape, and flows back into the filter element 11 so that the amount of filtrate flowing out is only a small amount. Is slightly diluted, and the concentrated sludge is hardly diluted.
The concentrated sludge that has been deposited and deposited at the bottom of 2 is discharged from the concentrated sludge discharge pipe 14 by opening the concentrated sludge discharge valve 13 and possibly using a pump. As a pump for discharging the concentrated sludge, a snake pump or another positive displacement pump may be used. In this concentrated sludge stripping and discharging process, the concentration of sludge discharged from the concentrated sludge discharge pipe 14 is measured, and when the concentration falls below a predetermined concentration or after a lapse of a predetermined time, the process is switched to the filtration concentration process again. It is convenient if the discharged sludge concentration is automatically measured to enable automatic stop and switching. Thus, the filtration and concentration step is performed again. However, the inside of the sludge concentration section 3 is almost full of the small amount of filtrate used for stripping the concentrated sludge and the unconcentrated sludge, and the sludge is filled as in the conventional case. Almost no steps are required.

【0012】また、剥離されて濃縮汚泥排出部12の底
部に沈降,堆積した濃縮汚泥の排出にはフィルターエレ
メント11の濃縮汚泥の剥離,洗浄を行ったのち、剥離
された濃縮汚泥を排出することなく、そのまま各弁を開
閉を行い、汚泥ポンプ16を稼動してろ過濃縮工程を再
開する。この時、汚泥濃縮部3内に圧力がかかり、ろ過
濃縮が行われると同時に、濃縮汚泥排出弁13を開にす
ることによって、汚泥濃縮部3内の圧力あるいは必要に
よりポンプを使用して、沈降,堆積している濃縮汚泥が
所定時間連続的に排出させて、1サイクル当たりの所要
時間がさらに短縮されるようにすることもできる。この
場合の濃縮汚泥の排出も、排出汚泥濃度が所定濃度以下
になった時に自動停止できるようにすることが好まし
い。なお、前述したようなフィルターエレメント11へ
の酸化物付着による機能低下を防ぐためには、濃縮汚泥
剥離排出工程においてフィルターエレメント11を空気
と接触させないようにすることが必要であり、そのため
には、該工程中ろ液が常に集液部4内に残っているよう
に集液部4の容量を設定することが好ましい。多くの実
験結果によれば、濃縮汚泥の剥離に必要なろ液量は2〜
15l/m2−エレメント程度であり、また空気圧併用
の場合の空気圧は0.5〜2kgf/cm2 程度が最適
であった。
In order to discharge the concentrated sludge that has settled and settled at the bottom of the concentrated sludge discharge section 12 that has been separated, the concentrated sludge of the filter element 11 is separated and washed, and then the separated concentrated sludge is discharged. Instead, the valves are opened and closed as they are, and the sludge pump 16 is operated to restart the filtration and concentration step. At this time, pressure is applied to the sludge thickening section 3 and filtration and concentration are performed. At the same time, the concentrated sludge discharge valve 13 is opened to settle the sedimentation using the pressure in the sludge thickening section 3 or a pump as necessary. The accumulated sludge accumulated can be continuously discharged for a predetermined time so that the time required for one cycle can be further shortened. In this case, it is preferable that the discharge of the concentrated sludge can be automatically stopped when the discharged sludge concentration becomes equal to or lower than the predetermined concentration. In addition, in order to prevent the function deterioration due to the adhesion of the oxide to the filter element 11 as described above, it is necessary to prevent the filter element 11 from coming into contact with air in the concentrated sludge peeling and discharging step. It is preferable to set the volume of the liquid collecting section 4 so that the filtrate during the process always remains in the liquid collecting section 4. According to many experimental results, the amount of filtrate required for stripping concentrated sludge is 2 to 2.
15l / m 2 - is about elements, also the air pressure in the case of air pressure combination was optimally about 0.5~2kgf / cm 2.

【0013】さらに、フィルターエレメント11を空気
と接触させないための手段としては、図3に示すよう
に、集液部4に水位計25を設け、ろ液水位が集液部4
内LWLで空気流入弁21を閉にし、大気開放とするこ
とができるようにすると良い。また、図4に示すよう
に、集液部4上部に弾性あるダイヤフラム26を張設し
て空気室27を形成し、この空気室27に空気源から所
定圧力の空気を導くようにすることもでき、その時の空
気抜管10はろ液流出管8から分岐させる。
Further, as a means for preventing the filter element 11 from coming into contact with air, as shown in FIG. 3, a water level gauge 25 is provided in the liquid collecting section 4, and the water level of the filtrate is set in the liquid collecting section 4.
It is preferable that the air inflow valve 21 be closed at the inner LWL so that the air can be opened to the atmosphere. Further, as shown in FIG. 4, an elastic diaphragm 26 may be stretched over the liquid collecting part 4 to form an air chamber 27, and air of a predetermined pressure may be introduced into the air chamber 27 from an air source. At that time, the air vent tube 10 is branched off from the filtrate outflow tube 8.

【0014】次に、本発明の装置を使用した場合におい
て、従来例との実験比較をすると、原汚泥としてN浄水
場の沈殿池から排泥された表−1の如き性状の汚泥を、
表−2に示すろ過濃縮装置を使用してろ過濃縮を行っ
た。
Next, when the apparatus of the present invention is used, an experimental comparison with the conventional example shows that sludge having the properties shown in Table 1 discharged from the sedimentation basin of the N water treatment plant as raw sludge is obtained as follows.
Filtration and concentration were performed using the filtration and concentration devices shown in Table-2.

【0015】[0015]

【表1】 [Table 1]

【0016】[0016]

【表2】 [Table 2]

【0017】また1サイクル当たりの各工程時間は表−
3の通りとした。
Table 3 shows each process time per cycle.
It was set as 3.

【0018】[0018]

【表3】 [Table 3]

【0019】以上の実験結果を表−4に示す。Table 4 shows the results of the above experiments.

【0020】[0020]

【表4】 [Table 4]

【0021】次に、濃縮汚泥の排出をろ過濃縮工程中に
行った場合、1サイクル当たりの各工程時間を表−5の
通りとし、その実験結果は表−6の通りであった。
Next, when the concentrated sludge was discharged during the filtration and concentration step, the process times per cycle were as shown in Table 5, and the experimental results were as shown in Table 6.

【0022】[0022]

【表5】 [Table 5]

【0023】[0023]

【表6】 [Table 6]

【0024】上述したように、本発明では、濃縮汚泥の
剥離,排出に当たって装置内の未濃縮汚泥を原汚泥貯槽
に返送することなく、そのまま濃縮汚泥を適確に剥離す
るものであるから、原汚泥貯槽の容量は従来より大幅に
小さくなり、またろ過濃縮に当たって原汚泥を装置内に
満杯にする汚泥充満工程も必要なく、濃縮汚泥の排出を
ろ過濃縮工程中に行うことによりほぼ連続的処理が可能
となり、ろ過速度も大幅に向上する。さらに、従来法に
おける未濃縮汚泥返送時には、真空によってフィルター
エレメント上の濃縮汚泥の剥離や亀裂が発生しないよう
に、濃縮汚泥を厚くしておかねばならず、ろ過速度が極
端に悪くなるが、本発明では未濃縮汚泥を返送しないの
で、濃縮汚泥の厚さが薄くても操作可能であり、ろ過速
度をさらに早めることができる。
As described above, in the present invention, the concentrated sludge is appropriately separated without removing the unconcentrated sludge from the apparatus to the raw sludge storage tank when separating and discharging the concentrated sludge. The capacity of the sludge storage tank is much smaller than before, and there is no need for a sludge filling step to fill the raw sludge into the device during filtration and concentration, and almost continuous treatment is achieved by discharging the concentrated sludge during the filtration and concentration step. Possible, and the filtration speed is greatly improved. Furthermore, when returning the non-condensed sludge in the conventional method, the thickened sludge must be thickened so that the vacuum does not cause separation or cracking of the thickened sludge on the filter element, and the filtration speed becomes extremely poor. Since the present invention does not return unconcentrated sludge, it can be operated even if the thickness of the concentrated sludge is small, and the filtration speed can be further increased.

【0025】[0025]

【発明の効果】本発明によれば、従来の密閉槽内の未濃
縮汚泥の排出を行うことなく、そのままろ液によるフィ
ルターの濃縮汚泥の剥離を均等で効率良く行い、従来必
要とされていた雑時間を大幅に短縮し、実質のろ過時間
を短縮し、消費電力その他のランニングコストが低減さ
れ、付属する原汚泥貯槽の容量が小さくなり、さらに筒
状フィルターエレメントからの濃縮汚泥の剥離時に真空
状態にしてから汚泥濃縮部を大気に開放しさらに圧力ガ
ス又は圧力水を併用することにより一層効果的な剥離を
可能にすることができ、エレメントに付着した濃縮汚泥
の空気による酸化を避けることができて、フィルターエ
レメントの寿命も大巾に長くすることができる顕著なる
効果を奏するものである。
According to the present invention, the concentrated sludge of the filter can be uniformly and efficiently separated from the filter by the filtrate without discharging the unconcentrated sludge in the conventional closed tank, which has been conventionally required. Significantly shortens the time required for filtration, reduces the actual filtration time, reduces power consumption and other running costs, reduces the capacity of the attached sludge storage tank, and reduces the vacuum when removing the concentrated sludge from the cylindrical filter element. After the state, the sludge thickening section is opened to the atmosphere, and furthermore, the combined use of pressure gas or pressure water enables more effective peeling, thereby avoiding oxidation of the concentrated sludge attached to the element by air. In addition, the service life of the filter element can be greatly extended, and a remarkable effect can be obtained.

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

【図1】本発明の実施例を示す縦断面図である。FIG. 1 is a longitudinal sectional view showing an embodiment of the present invention.

【図2】図1の例の一使用状態の系統説明図である。FIG. 2 is a system explanatory diagram of one use state of the example of FIG. 1;

【図3】本発明の他の実施例の一部の縦断面図である。FIG. 3 is a partial longitudinal sectional view of another embodiment of the present invention.

【図4】本発明のさらに他の例の一部の縦断面図であ
る。
FIG. 4 is a partial longitudinal sectional view of still another example of the present invention.

【図5】従来のろ過濃縮装置例の縦断面図である。FIG. 5 is a longitudinal sectional view of an example of a conventional filtration and concentration device.

【図6】図5の例の一使用状態の系統説明図である。FIG. 6 is an explanatory diagram of a system in one use state of the example of FIG. 5;

【符号の説明】[Explanation of symbols]

1 密閉槽 2 仕切板 3 汚泥濃縮部 4 集液部 5 汚泥流入弁 6 汚泥流入管 7 ろ液弁 8 ろ液流出管 9 空気抜弁 10 空気抜管 11 筒状フィルターエレメント 12 濃縮汚泥排出部 13 濃縮汚泥排出弁 14 濃縮汚泥排出管 15 原汚泥貯槽 16 汚泥ポンプ 17 戻し弁 18 戻し管 19 空気抜弁 20 空気抜管 21 空気流入弁 22 空気管 23 真空弁 24 真空管 25 水位計 26 ダイヤフラム 27 空気室 DESCRIPTION OF SYMBOLS 1 Closed tank 2 Partition plate 3 Sludge thickening part 4 Liquid collecting part 5 Sludge inflow valve 6 Sludge inflow pipe 7 Filtrate valve 8 Filtrate outflow pipe 9 Air vent valve 10 Air vent pipe 11 Cylindrical filter element 12 Thickened sludge discharge part 13 Thickened sludge Discharge valve 14 Condensed sludge discharge pipe 15 Raw sludge storage tank 16 Sludge pump 17 Return valve 18 Return pipe 19 Air release valve 20 Air release pipe 21 Air inflow valve 22 Air pipe 23 Vacuum valve 24 Vacuum pipe 25 Water level gauge 26 Diaphragm 27 Air chamber

───────────────────────────────────────────────────── フロントページの続き (72)発明者 衛藤 正徳 東京都港区港南1丁目6番27号 荏原イ ンフィルコ株式会社内 (56)参考文献 特開 平1−288308(JP,A) ──────────────────────────────────────────────────続 き Continuation of front page (72) Inventor Masanori Eto 1-6-27 Konan, Minato-ku, Tokyo Ebara Infilco Co., Ltd. (56) References JP-A-1-288308 (JP, A)

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 密閉槽1内に汚泥濃縮部3と集液部4と
を仕切板2で区画形成し、汚泥濃縮部3内に一端を開放
して他端を閉鎖した複数の筒状フィルターエレメント1
1を仕切板2に垂下配設し、その開放端部を集液部4に
連通し、該集液部4にろ液弁7のあるろ液流出管8を設
け、前記密閉槽1の汚泥濃縮部3内に汚泥流入弁5のあ
る汚泥流入管6から汚泥を供給し、前記筒状フィルター
エレメント11内に透過したろ液を集液部4を経て槽外
に流出させて汚泥のろ過濃縮を行う装置において、前記
汚泥濃縮部3内上部に連通する空気抜管20と、該空気
抜管20に設けた空気抜弁19とを備え、前記集液部4
に空気抜弁9を備えた空気抜管10を設けると共に、空
気流入弁21を備え、空気源に連なる空気管22と、真
空弁23を備え真空源に連なる真空管24とを連通配備
したことを特徴とする汚泥ろ過濃縮装置。
1. A plurality of cylindrical filters in which a sludge thickening section 3 and a liquid collecting section 4 are partitioned by a partition plate 2 in a closed tank 1, and one end is opened in the sludge thickening section 3 and the other end is closed. Element 1
1 is suspended from a partition plate 2, the open end of which is communicated with a liquid collecting part 4, a filtrate outlet pipe 8 having a filtrate valve 7 is provided in the liquid collecting part 4, and the sludge of the closed tank 1 is provided. Sludge is supplied from the sludge inflow pipe 6 having the sludge inflow valve 5 into the concentration section 3, and the filtrate permeated into the cylindrical filter element 11 is discharged out of the tank through the liquid collection section 4 to filter and concentrate the sludge. An air vent pipe 20 communicating with an upper portion inside the sludge concentrating section 3 and an air vent valve 19 provided in the air vent pipe 20.
The air vent valve 10 provided with the air vent valve 9 is provided, and an air inlet valve 21 is provided, and an air tube 22 connected to an air source and a vacuum tube 24 provided with a vacuum valve 23 and connected to a vacuum source are provided in communication with each other. Sludge filter concentrator.
JP6129509A 1994-04-20 1994-04-20 Sludge filtration and concentration equipment Expired - Lifetime JP2668010B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6129509A JP2668010B2 (en) 1994-04-20 1994-04-20 Sludge filtration and concentration equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6129509A JP2668010B2 (en) 1994-04-20 1994-04-20 Sludge filtration and concentration equipment

Related Parent Applications (1)

Application Number Title Priority Date Filing Date
JP1271546A Division JP2581600B2 (en) 1989-10-20 1989-10-20 Method for overconcentration of sludge

Publications (2)

Publication Number Publication Date
JPH0768107A JPH0768107A (en) 1995-03-14
JP2668010B2 true JP2668010B2 (en) 1997-10-27

Family

ID=15011256

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6129509A Expired - Lifetime JP2668010B2 (en) 1994-04-20 1994-04-20 Sludge filtration and concentration equipment

Country Status (1)

Country Link
JP (1) JP2668010B2 (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4695107B2 (en) * 2007-02-28 2011-06-08 メタウォーター株式会社 Filtration concentration apparatus and filtration concentration method
WO2010150790A1 (en) * 2009-06-23 2010-12-29 メタウォーター株式会社 Suction filtration/concentration method and suction filtration/concentration device
CN101781077A (en) * 2010-02-11 2010-07-21 东华大学 System for vacuum drying sludge by adopting solar energy
CN102531322B (en) * 2011-12-28 2013-11-13 同济大学 Novel energy-saving sludge drying system
CN102531314B (en) * 2011-12-28 2013-11-20 北京科力丹迪技术开发有限责任公司 Sludge water heat drying treatment device and flashing reactor thereof
CN102531321B (en) * 2011-12-28 2013-11-20 北京科力丹迪技术开发有限责任公司 Sludge water heat drying treatment device and homogeneous reactor thereof
CN102531315B (en) * 2011-12-28 2013-11-20 北京科力丹迪技术开发有限责任公司 Sludge hydrothermal drying treating device and hydrothermal reactor thereof
CN108658429A (en) * 2017-03-31 2018-10-16 广州新致晟环保科技有限公司 Sludge condensation and modifying device and the method that sludge is handled using it
CN108465281B (en) * 2018-05-28 2023-09-19 浙江东瓯过滤机制造有限公司 Filtering and concentrating device and filtering and concentrating method thereof
CN110002700B (en) * 2019-03-21 2021-06-01 广州市永蓝环保科技有限公司 Resource recycling equipment for piling mud and working method thereof

Also Published As

Publication number Publication date
JPH0768107A (en) 1995-03-14

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