JP2008006360A - Filtration concentration apparatus and filtration concentration method - Google Patents
Filtration concentration apparatus and filtration concentration method Download PDFInfo
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Description
本発明は、浄水場や下水処理場等における汚泥の濾過濃縮装置とその濾過濃縮方法に関する。 TECHNICAL FIELD The present invention relates to a sludge filtration and concentration device and a filtration and concentration method thereof in a water purification plant, a sewage treatment plant, and the like.
一般に、浄水場や下水処理場から排出される汚泥は、重力沈降槽で濃縮した後、機械脱水を行って含水率80%以下の濃縮汚泥とし、この濃縮汚泥を焼却、埋立て処分している。
従来の重力沈降槽による汚泥濃縮では、滞留時間が長く、汚泥の性状により含水率が大幅に変わるので、機械脱水を安定的に運転することが難しい問題点があった。そこで、重力沈降槽の代替手段として濾過濃縮装置が開発された。
従来の濾過濃縮装置を記載した文献として、特許文献1が挙げられるが、動作に記載不十分な点がある。そこで、従来の濾過濃縮装置の動作を補足しつつ、図14を用いて説明する。
In general, sludge discharged from a water purification plant or sewage treatment plant is concentrated in a gravity sedimentation tank and then mechanically dehydrated to a concentrated sludge with a water content of 80% or less. The concentrated sludge is incinerated and disposed of in landfills. .
In the conventional sludge concentration in the gravity settling tank, the residence time is long and the moisture content varies greatly depending on the properties of the sludge. Therefore, it is difficult to stably operate the mechanical dehydration. Therefore, a filtration and concentration device was developed as an alternative to the gravity sedimentation tank.
Patent Document 1 is cited as a document describing a conventional filtration and concentration device, but there is an insufficient description in the operation. Then, it demonstrates using FIG. 14, supplementing operation | movement of the conventional filtration concentration apparatus.
まず、装置構成について説明する。この濾過濃縮装置は、缶体22の内部を仕切板23により上室24と下室25に区画され、複数の濾過体26が、仕切板23から下室25内に垂設されている。上室24天蓋部には、空気導入管36を備えている。下室25上部には、給排気管37、同底部には、被処理液導入管27を備えている。濾液排出管28には、濾液弁29を備え、さらに、濾液弁29より上流に真空弁30を介して、貯留タンク32、エアーポンプ31を備えた真空ライン33が接続されており、貯留タンク32には排液弁34、吸気弁35を有するラインがそれぞれ接続されている。濾過体26の長さは、例えば1.5m程度である。 First, the apparatus configuration will be described. In this filtration concentration apparatus, the inside of the can 22 is partitioned into an upper chamber 24 and a lower chamber 25 by a partition plate 23, and a plurality of filter bodies 26 are suspended from the partition plate 23 into the lower chamber 25. An air introduction pipe 36 is provided in the upper chamber 24 canopy. A supply / exhaust pipe 37 is provided in the upper part of the lower chamber 25, and a liquid to be processed introduction pipe 27 is provided in the bottom part. The filtrate discharge pipe 28 is provided with a filtrate valve 29, and further connected with a storage tank 32 and a vacuum line 33 provided with an air pump 31 via a vacuum valve 30 upstream of the filtrate valve 29. Are connected to lines having a drain valve 34 and an intake valve 35, respectively. The length of the filter body 26 is, for example, about 1.5 m.
次に、動作について説明する。まず、はじめに加圧濾過を行う。給排気管37を閉じ、被処理液を被処理液導入管27を通して下室25内に導入し、濾過体26で濾過する。濾液は、上室24内に移動し、濾液排出管28、濾液弁29を介して所定の行き先へと排出される。この時、空気導入管36は、閉じられている。被処理液中の懸濁物は、濾過体26の表面に濾滓(本願の濃縮汚泥に相当する)として捕捉され付着する。 Next, the operation will be described. First, pressure filtration is performed first. The supply / exhaust pipe 37 is closed, and the liquid to be processed is introduced into the lower chamber 25 through the liquid inlet pipe 27 to be processed and filtered through the filter body 26. The filtrate moves into the upper chamber 24 and is discharged to a predetermined destination through the filtrate discharge pipe 28 and the filtrate valve 29. At this time, the air introduction pipe 36 is closed. The suspension in the liquid to be treated is captured and attached as filter cake (corresponding to the concentrated sludge of the present application) on the surface of the filter body 26.
次いで、上記加圧濾過を継続中にエアーポンプ31で上室24の減圧を開始する。すなわち、排液弁34、吸気弁35を閉じ、真空弁30を開け、エアーポンプ31を作動させる。
次いで、濾液弁29を閉じ、加圧濾過を停止する。そして、給排気管37を大気開放し、被処理液導入管27から下室25の未濃縮汚泥を排出する。この時、エアーポンプ31による減圧は継続中である。減圧を維持するためには、貯留タンク32の容積は、上室24と濾過体26の容積および付着した濃縮汚泥の水量の合計容積以上でなければならない。さもなければ、エアーポンプ31に濾液が流入してしまい不都合である。減圧を継続すると、濃縮汚泥の含水率はより低下し、暫くすると濃縮汚泥にクラックが発生し空気も上室24に流入するようになる。そして、上室24や濾過体26の2次側の濾液が吸引され除かれる。
Next, the pressure reduction of the upper chamber 24 is started by the air pump 31 while the pressure filtration is continued. That is, the drain valve 34 and the intake valve 35 are closed, the vacuum valve 30 is opened, and the air pump 31 is operated.
Next, the filtrate valve 29 is closed and the pressure filtration is stopped. Then, the air supply / exhaust pipe 37 is opened to the atmosphere, and unconcentrated sludge in the lower chamber 25 is discharged from the liquid inlet pipe 27 to be treated. At this time, the pressure reduction by the air pump 31 is continuing. In order to maintain the reduced pressure, the volume of the storage tank 32 must be equal to or greater than the total volume of the volume of the upper chamber 24 and the filter body 26 and the amount of water of the attached concentrated sludge. Otherwise, the filtrate flows into the air pump 31, which is inconvenient. If the pressure reduction is continued, the moisture content of the concentrated sludge is further reduced, and after a while, cracks are generated in the concentrated sludge and air also flows into the upper chamber 24. Then, the filtrate on the secondary side of the upper chamber 24 and the filter body 26 is sucked and removed.
次いで、空気導入管36を開放して圧縮空気を上室24に導入する。すると、濾過体26は2次側から膨らみ、濾過体26の1次側に付着した濃縮汚泥が剥離される。
なお、上述の装置構成および動作によれば、濾液排出管28および排液弁34の配管には、ポンプなど動力を使った排液装置は記載されていない。
In addition, according to the above-mentioned apparatus configuration and operation, a drainage device using power such as a pump is not described in the piping of the filtrate discharge pipe 28 and the drainage valve 34.
貯留タンク32の容積は、上室24と濾過体26の容積および付着した濃縮汚泥の水量の合計容積以上でなければならないため、装置規模が大きくなった場合、貯留タンク32が大型化してしまう問題点があった。
そこで、本発明は、貯留タンクの容量を小さくでき、高濃度の濃縮汚泥が効率的に得られる濾過濃縮装置、および濾過濃縮方法を提供するものである。
The volume of the storage tank 32 must be equal to or greater than the total volume of the volume of the upper chamber 24 and the filter body 26 and the amount of water of the attached concentrated sludge, so that the storage tank 32 is enlarged when the apparatus scale is increased. There was a point.
Therefore, the present invention provides a filtration and concentration apparatus and a filtration and concentration method that can reduce the capacity of a storage tank and efficiently obtain concentrated sludge having a high concentration.
本発明の課題は、エアーポンプ作動中に貯留タンク内の濾液を排出することによって解決される。
すなわち、本発明の特徴は、汚泥槽と、前記汚泥槽に汚泥を供給する汚泥供給手段と、前記汚泥槽内に設置して前記汚泥を濾過する濾過部と、前記濾過部から前記汚泥槽外部に引き出した濾液排出管と、未濃縮汚泥排出手段と、前記濾過部に付着した濃縮汚泥を剥離する剥離手段と、剥離した濃縮汚泥を前記汚泥槽から排出する濃縮汚泥排出手段と、前記濾液排出管の途中に設置した貯留タンクと、前記貯留タンクへ気体を吐出および前記貯留タンク内の気体を吸引できるエアーポンプと、前記貯留タンクと前記エアーポンプを連通する気体通流管と、前記汚泥供給手段と前記汚泥槽を連通する汚泥供給管とを備えた濾過濃縮装置において、前記貯留タンクの圧力を測定する圧力計と、前記貯留タンク内部の水位を測定する水位測定手段と、前記貯留タンクより下流の前記濾液排出管に連通させた液体ポンプと、前記汚泥供給手段,前記未濃縮汚泥排出手段,前記剥離手段,前記濃縮汚泥排出手段,前記濾液排出管,および前記気体通流管の流体流路にそれぞれ設けた弁と、制御装置とを備えることにある。
The problem of the present invention is solved by discharging the filtrate in the storage tank during the operation of the air pump.
That is, the features of the present invention are a sludge tank, a sludge supply means for supplying sludge to the sludge tank, a filtration unit installed in the sludge tank to filter the sludge, and the sludge tank outside the sludge tank. A filtrate discharge pipe drawn into the filter, a non-concentrated sludge discharging means, a peeling means for peeling the concentrated sludge adhering to the filtration part, a concentrated sludge discharging means for discharging the peeled concentrated sludge from the sludge tank, and the filtrate discharging. A storage tank installed in the middle of the pipe, an air pump capable of discharging gas to the storage tank and sucking the gas in the storage tank, a gas flow pipe connecting the storage tank and the air pump, and the sludge supply In a filtration and concentration device comprising a means and a sludge supply pipe communicating with the sludge tank, a pressure gauge that measures the pressure of the storage tank, and a water level measurement means that measures the water level inside the storage tank, A liquid pump communicating with the filtrate discharge pipe downstream from the storage tank, the sludge supply means, the unconcentrated sludge discharge means, the stripping means, the concentrated sludge discharge means, the filtrate discharge pipe, and the gas flow The object is to include a valve provided in each of the fluid flow paths of the pipe and a control device.
そして、請求項2の発明は、請求項1に記載の濾過濃縮装置において、前記貯留タンク内部と大気とを連通または遮断させる大気開放弁を備えることにある。
また、請求項3の発明の特徴は、汚泥供給工程と、エアーポンプ濾過工程と、未濃縮汚泥排出工程とを備え、前記汚泥供給工程と前記エアーポンプ濾過工程と前記未濃縮汚泥排出工程とが全て終了した後に濃縮汚泥剥離工程を実行する濾過濃縮方法において、前記貯留タンク内の液体水位を所定範囲内に制御する前記液体ポンプ濾過工程と、前記貯留タンク内の気体を吸引するエアーポンプ濾過工程とを同時に実行することにある。
そして、請求項4の発明の特徴は、請求項3に記載の濾過濃縮方法において、前記エアーポンプ濾過工程と、前記未濃縮汚泥排出工程とを同時に行うことにある。
そして、請求項5の発明の特徴は、請求項3または4に記載の濾過濃縮方法において、前記濃縮汚泥剥離工程前に、前記貯留タンクおよび前記濾液排出管の液体を排出する濾液流路排水工程を実行することにある。
そして、請求項6の発明の特徴は、請求項3から5のいずれか一項に記載の濾過濃縮方法において、前記エアーポンプ濾過工程において、前記圧力計の測定値と所定圧力値とを比較し、前記圧力計の測定値が前記所定圧力値より大きい時に前記エアーポンプの作動を継続させ、前記圧力計の測定値が前記所定圧力値以下の時に前記エアーポンプの作動を停止することにある。
そして、請求項7の発明の特徴は、請求項3から6のいずれか一項に記載の濾過濃縮方法において、前記エアーポンプ濾過工程の前記エアーポンプは、該エアーポンプの作動から所定時間経過後、停止することにある。
そして、請求項8の発明の特徴は、請求項3から7のいずれか一項に記載の濾過濃縮方法において、前記液体ポンプと前記エアーポンプとが同時に作動する時に、前記貯留タンク内の気体圧力を前記液体ポンプの作動圧力許容範囲内とすることにある。
According to a second aspect of the present invention, in the filtration and concentration apparatus according to the first aspect of the present invention, an atmosphere release valve is provided for communicating or blocking the interior of the storage tank and the atmosphere.
The invention of claim 3 includes a sludge supply step, an air pump filtration step, and an unconcentrated sludge discharge step, wherein the sludge supply step, the air pump filtration step, and the unconcentrated sludge discharge step are In the filtration and concentration method in which the concentrated sludge separation step is executed after all the steps are completed, the liquid pump filtration step for controlling the liquid water level in the storage tank within a predetermined range, and the air pump filtration step for sucking the gas in the storage tank Is to execute simultaneously.
According to a fourth aspect of the present invention, in the filtration and concentration method according to the third aspect, the air pump filtration step and the unconcentrated sludge discharge step are performed simultaneously.
And the characteristic of invention of Claim 5 is the filtration flow path drainage process which discharges | emits the liquid of the said storage tank and the said filtrate discharge pipe before the said concentration sludge peeling process in the filtration concentration method of Claim 3 or 4 Is to execute.
According to a sixth aspect of the present invention, in the filtration and concentration method according to any one of the third to fifth aspects, the measured value of the pressure gauge is compared with a predetermined pressure value in the air pump filtration step. The operation of the air pump is continued when the measured value of the pressure gauge is larger than the predetermined pressure value, and the operation of the air pump is stopped when the measured value of the pressure gauge is less than the predetermined pressure value.
A seventh aspect of the present invention is the filtration and concentration method according to any one of the third to sixth aspects, wherein the air pump in the air pump filtration step is after a predetermined time has elapsed since the operation of the air pump. , To stop.
The invention according to claim 8 is characterized in that, in the filtration and concentration method according to any one of claims 3 to 7, when the liquid pump and the air pump operate simultaneously, the gas pressure in the storage tank is Is within the allowable operating pressure range of the liquid pump.
請求項1の発明によれば、貯留タンクの容積を小さくできる。また、汚泥槽を気密容器にする必要がないので、規模が大きくなっても製作が容易な構造である。
請求項2の発明によれば、貯留タンク内部と大気とを連通させる大気開放弁を備え、濾過中は大気開放弁を閉じ、エアーポンプで気体を濾過部に供給して濃縮汚泥を剥離させる前には貯留タンク内部と大気とを連通させて濾液排出管および貯留タンクの濾液を除去することで濾液排出管および貯留タンク内部の濾液が濾過部に逆流して濃縮汚泥の濃度を低下させることを防止できる。
請求項3の発明によれば、汚泥供給工程と、エアーポンプ濾過工程と、未濃縮汚泥排出工程とを備え、前記汚泥供給工程と前記エアーポンプ濾過工程と前記未濃縮汚泥排出工程とが全て終了した後に濃縮汚泥剥離工程を実行する濾過濃縮方法において、前記貯留タンク内の液体水位を所定範囲内に制御する前記液体ポンプ濾過工程と、前記貯留タンク内の気体を吸引するエアーポンプ濾過工程とを同時に実行することによって、貯留タンクの容積を小さくできる。
請求項4の発明によれば、前記エアーポンプ濾過工程と、前記未濃縮汚泥排出工程とを同時に行うことによって、前記未濃縮汚泥排出工程時に未濃縮汚泥と共に濾過板表面の濃縮汚泥が脱落することを防止できる。すなわち、サイフォン濾過工程時にできた半固形状の濃縮汚泥は、エアーポンプ濾過により含水率をさらに低下させられ、濾過板表面に付着したままの状態で維持される。
請求項5の発明によれば、前記濃縮汚泥剥離工程前に、前記貯留タンクおよび前記濾液排出管の液体を排出する濾液流路排水工程を実行することによって、前記貯留タンクおよび前記濾液排出管の液体が濾過部に逆流して濃縮汚泥の濃度を低下させることを防止できる。
請求項6の発明によれば、前記エアーポンプ濾過工程において、前記圧力計の測定値と所定圧力値とを比較し、前記圧力計の測定値が前記所定圧力値より大きい時に前記エアーポンプの作動を継続させ、前記圧力計の測定値が前記所定圧力値以下の時に前記エアーポンプの作動を停止することによって、エアーポンプの過剰減圧を防止でき、省エネルギーに濃縮濾過を実行できる。
請求項7の発明によれば、前記エアーポンプ濾過工程の前記エアーポンプは、該エアーポンプの作動から所定時間経過後、停止することによって、圧力計が故障していた場合でも確実に濃縮濾過を進行でき、障害耐性が向上する。
請求項8の発明によれば、前記液体ポンプと前記エアーポンプとが同時に作動する時に、前記貯留タンク内の気体圧力を前記液体ポンプの作動圧力許容範囲内とすることによって、前記液体ポンプに過負荷がかかることを防止でき、液体ポンプの故障リスクを低減できる。
According to invention of Claim 1, the volume of a storage tank can be made small. Further, since it is not necessary to make the sludge tank an airtight container, the structure is easy to manufacture even when the scale is increased.
According to the second aspect of the present invention, the air release valve that allows the inside of the storage tank to communicate with the atmosphere is provided. During the filtration, the air release valve is closed, and before the concentrated sludge is peeled off by supplying the gas to the filtration unit with an air pump. In order to reduce the concentration of concentrated sludge, the filtrate inside the storage tank and the storage tank are removed by removing the filtrate from the filtrate discharge pipe and the storage tank. Can be prevented.
According to the invention of claim 3, a sludge supply step, an air pump filtration step, and an unconcentrated sludge discharge step are provided, and the sludge supply step, the air pump filtration step, and the unconcentrated sludge discharge step are all completed. In the filtration and concentration method for performing the concentrated sludge stripping process after the process, the liquid pump filtration process for controlling the liquid water level in the storage tank within a predetermined range, and the air pump filtration process for sucking the gas in the storage tank By executing simultaneously, the volume of the storage tank can be reduced.
According to the invention of claim 4, by simultaneously performing the air pump filtration step and the non-concentrated sludge discharge step, the concentrated sludge on the filter plate surface is dropped together with the non-concentrated sludge during the non-concentrated sludge discharge step. Can be prevented. That is, the semi-solid concentrated sludge produced during the siphon filtration step is further reduced in water content by air pump filtration and is maintained in a state of adhering to the filter plate surface.
According to the invention of claim 5, before the concentrated sludge stripping step, a filtrate channel draining step for draining the liquid in the storage tank and the filtrate discharge pipe is performed, so that the storage tank and the filtrate discharge pipe are It is possible to prevent the liquid from flowing back to the filtration part and reducing the concentration of the concentrated sludge.
According to the invention of claim 6, in the air pump filtration step, the measured value of the pressure gauge is compared with a predetermined pressure value, and the operation of the air pump is performed when the measured value of the pressure gauge is larger than the predetermined pressure value. And by stopping the operation of the air pump when the measured value of the pressure gauge is equal to or lower than the predetermined pressure value, excessive pressure reduction of the air pump can be prevented, and concentration filtration can be executed with energy saving.
According to the seventh aspect of the present invention, the air pump in the air pump filtration step is stopped after a predetermined time from the operation of the air pump, so that the concentration filtration can be reliably performed even when the pressure gauge is broken. Can progress and improve fault tolerance.
According to the eighth aspect of the present invention, when the liquid pump and the air pump are operated simultaneously, the gas pressure in the storage tank is set within the allowable operating pressure range of the liquid pump, so It is possible to prevent the load from being applied and to reduce the risk of failure of the liquid pump.
まず、本発明の濾過濃縮装置の構成について説明する。図1は、本発明の実施形態にかかる濾過濃縮装置の構成図である。
図1の濾過濃縮装置は、底部がテーパー状に細くなっている汚泥槽1と、汚泥槽1への汚泥供給手段および未濃縮汚泥排出手段である汚泥供給兼排出ポンプ2と、汚泥槽1に原汚泥を供給する際に汚泥供給兼排出ポンプ2を作動させて所定の水位まで汚泥を入れるために汚泥水位を検出する水位計18と、汚泥槽1内に設置して汚泥を濾過する濾過部3と、濾過部から汚泥槽1の外部に引き出した濾液排出管4と、弁10,38と、濾過して濃縮された濃縮汚泥を汚泥槽1から排出する濃縮汚泥排出手段である濃縮汚泥ポンプ39と、濃縮汚泥排出管42と、弁9と、水位計20と、濾液排出管4の途中の弁10と弁38の間に設置した貯留タンク5と、貯留タンク5へ気体を吐出および貯留タンク5内の気体を吸引でき濾過部3に付着した濃縮汚泥を剥離する剥離手段の一部となるエアーポンプ7と、弁13と、貯留タンク5とエアーポンプ7を連通する気体通流管40と、汚泥供給兼排出ポンプ2と汚泥槽1を連通する汚泥供給管41と、弁8とを備えた濾過濃縮装置において、貯留タンク5の圧力を測定する圧力計17と、貯留タンク5内部の水位を測定する水位計19と、貯留タンク5より下流の濾液排出管4に連通させた液体ポンプ16および弁11と、貯留タンク5に水を供給する水道水供給管6および弁12と、貯留タンク5に溜まった空気を排出する大気開放管43および弁14と、図示していない制御装置とを備えた構成としている。
First, the structure of the filtration concentration apparatus of this invention is demonstrated. FIG. 1 is a configuration diagram of a filtration and concentration apparatus according to an embodiment of the present invention.
1 includes a sludge tank 1 having a tapered bottom, a sludge supply / discharge pump 2 which is a sludge supply means and an unconcentrated sludge discharge means to the sludge tank 1, and a sludge tank 1. When supplying the raw sludge, the sludge supply / discharge pump 2 is operated to enter the sludge to a predetermined water level, and a water level meter 18 for detecting the sludge water level and a filtration unit installed in the sludge tank 1 for filtering the sludge. 3, a filtrate discharge pipe 4 drawn from the filtration unit to the outside of the sludge tank 1, valves 10 and 38, and a concentrated sludge pump which is a concentrated sludge discharge means for discharging concentrated sludge filtered and concentrated from the sludge tank 1 39, the concentrated sludge discharge pipe 42, the valve 9, the water level gauge 20, the storage tank 5 installed between the valve 10 and the valve 38 in the middle of the filtrate discharge pipe 4, and the gas is discharged and stored in the storage tank 5. The gas in the tank 5 can be sucked and adhered to the filtration unit 3 The air pump 7 which is a part of the stripping means for stripping the reduced sludge, the valve 13, the gas flow pipe 40 which communicates the storage tank 5 and the air pump 7, the sludge supply / discharge pump 2 and the sludge tank 1 are communicated. In the filtration and concentration apparatus including the sludge supply pipe 41 and the valve 8, the pressure gauge 17 that measures the pressure of the storage tank 5, the water level gauge 19 that measures the water level inside the storage tank 5, and the downstream of the storage tank 5 A liquid pump 16 and a valve 11 communicated with the filtrate discharge pipe 4, a tap water supply pipe 6 and a valve 12 for supplying water to the storage tank 5, an air release pipe 43 for discharging the air accumulated in the storage tank 5, and The valve 14 and a control device (not shown) are provided.
そして、濾液排出管4の出口高さは、濾過部3下端より下になるようにしている。また、濾過部3は、濾液と汚泥を隔離する袋状の濾過膜3aと、濾過膜3aを支持する濾枠3bから成っている。濾過膜3aの内側上部には、濾液の吸引や濃縮汚泥を剥離するための空気分配管15が設けられている。この空気分配管15は、金属や塩化ビニールなどの丸型や角型パイプを水平方向に設置し、パイプの下部に鉛直下方向に小孔を複数設けている。小孔は、濾過部3内部の濾液を吸引するためや、濃縮汚泥を濾過膜3aから剥離させる加圧空気を供給するために設けられている。空気分配管15の濾液排出管4と接続していない側の端は、封止されている。 The outlet height of the filtrate discharge pipe 4 is set to be lower than the lower end of the filtration unit 3. Moreover, the filtration part 3 consists of the bag-shaped filtration membrane 3a which isolates a filtrate and sludge, and the filter frame 3b which supports the filtration membrane 3a. An air distribution pipe 15 for sucking the filtrate and peeling the concentrated sludge is provided on the inner upper part of the filtration membrane 3a. The air distribution pipe 15 is a round or square pipe made of metal, vinyl chloride, or the like installed in the horizontal direction, and a plurality of small holes are provided vertically downward in the lower part of the pipe. The small holes are provided for sucking the filtrate in the filtration unit 3 and for supplying pressurized air for separating the concentrated sludge from the filtration membrane 3a. The end of the air distribution pipe 15 that is not connected to the filtrate discharge pipe 4 is sealed.
本発明に係る濾過濃縮装置の制御装置の入出力図を図2に示す。制御装置は、少なくとも水位計18,19,20の水位信号と、圧力計17の圧力信号と、サイフォン濾過設定時間と、液体ポンプ濾過設定時間と、エアーポンプ濾過設定時間とが入力される。そして、同制御装置は、弁8〜14,38と、汚泥供給兼排出ポンプ2と、エアーポンプ7と、液体ポンプ16と、濃縮汚泥ポンプ39とを制御する信号を出力する。 An input / output diagram of the control device of the filtration concentration apparatus according to the present invention is shown in FIG. At least the water level signals of the water level gauges 18, 19, and 20, the pressure signal of the pressure gauge 17, the siphon filtration setting time, the liquid pump filtration setting time, and the air pump filtration setting time are input to the control device. The control device outputs signals for controlling the valves 8 to 14 and 38, the sludge supply / discharge pump 2, the air pump 7, the liquid pump 16, and the concentrated sludge pump 39.
次に、濾過濃縮装置の運転方法を説明する。
本発明に係る濾過濃縮方法の運転フロー図を図3に示す。制御装置は、濾過濃縮開始信号を受信すると、汚泥供給工程A、続いてサイフォン形成工程を実行する。
次に、サイフォン濾過工程と、汚泥供給工程Bが平行して実行される。サイフォン濾過工程の途中で貯留タンク5に気体が溜って圧力が上昇した場合は、サイフォン濾過工程を中断してサイフォン形成工程を実行して貯留タンク5内部の気体を除去した後、サイフォン濾過工程に復帰させる。
Next, the operation method of the filtration concentration apparatus will be described.
FIG. 3 shows an operation flowchart of the filtration concentration method according to the present invention. When the control device receives the filtration and concentration start signal, the control device executes the sludge supply step A and then the siphon formation step.
Next, the siphon filtration process and the sludge supply process B are performed in parallel. When gas accumulates in the storage tank 5 during the siphon filtration process and the pressure rises, the siphon filtration process is interrupted and the siphon formation process is executed to remove the gas inside the storage tank 5 and then the siphon filtration process. Return.
サイフォン濾過工程を所定時間実行した後、エアーポンプ濾過工程と、液体ポンプ濾過工程と、未濃縮汚泥排出工程とを平行して実行する。エアーポンプ濾過工程終了後、濾液流路排水工程、濃縮汚泥剥離工程、濃縮汚泥排出工程をこの順に実行し、濾過濃縮の一連の動作を終了する。
以下に、各工程を更に詳細に説明する。
After the siphon filtration step is executed for a predetermined time, the air pump filtration step, the liquid pump filtration step, and the unconcentrated sludge discharge step are executed in parallel. After the air pump filtration process is completed, the filtrate flow path draining process, the concentrated sludge peeling process, and the concentrated sludge discharging process are executed in this order, and the series of filtration and concentration operations is completed.
Below, each process is demonstrated in detail.
汚泥供給工程AおよびBのフロー図を図4に示す。開始時には、弁8〜14,38は、すべて閉じている。汚泥供給工程AおよびBでは、まず弁8を開き、汚泥供給兼排出ポンプ2を作動させて、汚泥槽1に設置した濾過板3が水没する所定水位まで汚泥を供給する。この所定水位は、水位計18の水位Hに達したかどうかで判断される。汚泥供給工程Bにおいては、サイフォン濾過工程中に汚泥水位が所定水位を維持するために、上述のように汚泥供給兼排出ポンプ2と弁8とを作動および停止させる。 A flow chart of the sludge supply steps A and B is shown in FIG. At the start, valves 8-14, 38 are all closed. In the sludge supply steps A and B, first, the valve 8 is opened and the sludge supply / discharge pump 2 is operated to supply the sludge to a predetermined water level where the filter plate 3 installed in the sludge tank 1 is submerged. This predetermined water level is determined by whether or not the water level H of the water level gauge 18 has been reached. In the sludge supply process B, the sludge supply / discharge pump 2 and the valve 8 are operated and stopped as described above in order to maintain the sludge water level at a predetermined level during the siphon filtration process.
次に、サイフォン形成工程のフロー図を図5,6に示す。弁12,14を開いて貯留タンク5が所定水位になるまで水を供給後、弁12,14を閉じる。この所定水位は、水位計19の水位Hに達したかどうかで判断される。
エアーポンプ7を用いてサイフォン形成工程を実施する場合は、弁13を開き、エアーポンプ7で気体を吸引して貯留タンク5内部を減圧させて、貯留タンク5の水位が所定水位になるまで吸引した後、弁13を閉じる。この場合、水道水供給管6,大気開放管43,弁12,14を設置しなくてもよい。
Next, flow charts of the siphon forming process are shown in FIGS. After the valves 12 and 14 are opened and water is supplied until the storage tank 5 reaches a predetermined water level, the valves 12 and 14 are closed. This predetermined water level is determined by whether or not the water level H of the water level gauge 19 has been reached.
When the siphon forming process is performed using the air pump 7, the valve 13 is opened, the gas is sucked by the air pump 7, the inside of the storage tank 5 is decompressed, and suction is performed until the water level of the storage tank 5 reaches a predetermined water level. After that, the valve 13 is closed. In this case, the tap water supply pipe 6, the air release pipe 43, and the valves 12 and 14 need not be installed.
次に、サイフォン濾過工程のフロー図を図7に示す。弁10,38を開いて濾過を開始する。濾過膜3aに堆積する汚泥の厚さが、好ましくは10〜13mmになるまで汚泥供給工程Bによる汚泥の供給およびサイフォン濾過工程を継続する。濾過を継続する時間は、予め汚泥堆積厚さと濾過時間との関係を調べておき、その後は、汚泥堆積厚さが前記10〜13mmになる濾過時間を指標にして実施してもよい。具体的には、浄水汚泥の濾過濃縮の場合、例えば90分間濾過を行う。ここで発生される圧力は−30kPa程度である。 Next, a flow chart of the siphon filtration process is shown in FIG. Valves 10 and 38 are opened to begin filtration. The supply of sludge and the siphon filtration process in the sludge supply process B are continued until the thickness of the sludge deposited on the filtration membrane 3a is preferably 10 to 13 mm. The time for which the filtration is continued may be carried out by examining the relationship between the sludge deposition thickness and the filtration time in advance, and thereafter using the filtration time when the sludge deposition thickness is 10 to 13 mm as an index. Specifically, in the case of filtration concentration of purified water sludge, for example, filtration is performed for 90 minutes. The pressure generated here is about -30 kPa.
次に、未濃縮汚泥排出工程のフロー図を図8に示す。弁8を開け、汚泥供給兼排出ポンプ2を逆作動させて、濾過膜3a表面に付着されなかった未濃縮汚泥を汚泥槽1から排出する。水位計18の水位L信号を用いて未濃縮汚泥が汚泥槽1から排出されたかどうか制御装置が判断し、汚泥供給兼排出ポンプ2を止め、弁8を閉じる。
次に、液体ポンプ濾過工程のフロー図を図9に示す。弁10,11を開き、液体ポンプ16を作動させると同時に液体ポンプ作動経過時間の計測を開始する。液体ポンプ濾過の開始当初に貯留タンク内に発生する圧力は−80〜−90kPa程度である。そして、液体ポンプ作動経過時間が液体ポンプ濾過設定時間以上かどうかを比較する。液体ポンプ作動経過時間が液体ポンプ濾過設定時間より小さい場合は、さらに、水位計19の水位と貯留タンクの水位Lとを比較する。水位計19の水位が貯留タンク水位Lより高い場合は、液体ポンプ作動経過時間が液体ポンプ濾過設定時間以上かどうかを比較する処理に戻り、この処理ループを実行する。未濃縮汚泥排出工程は液体ポンプ濾過工程と同時に作動するので、未濃縮汚泥排出工程によって下がりつつある水位より上の濾過膜3a表面に付着した濃縮汚泥は、外気に触れる状態で液体ポンプ濾過が行われる。また、液体ポンプ作動経過時間が液体ポンプ濾過設定時間より大きい場合、および、液体ポンプ作動経過時間が液体ポンプ濾過設定時間より小さくかつ水位計19の水位が貯留タンク水位Lより低いの場合は、液体ポンプ16を停止し、弁11を閉じ、液体ポンプ作動経過時間の計測を終了する。
Next, a flow chart of the unconcentrated sludge discharging step is shown in FIG. The valve 8 is opened and the sludge supply / discharge pump 2 is reversely operated to discharge the unconcentrated sludge that has not adhered to the surface of the filtration membrane 3a from the sludge tank 1. The control device determines whether unconcentrated sludge is discharged from the sludge tank 1 using the water level L signal of the water level gauge 18, stops the sludge supply / discharge pump 2, and closes the valve 8.
Next, FIG. 9 shows a flowchart of the liquid pump filtration process. The valves 10 and 11 are opened and the liquid pump 16 is operated, and at the same time, measurement of the liquid pump operation elapsed time is started. The pressure generated in the storage tank at the beginning of liquid pump filtration is about −80 to −90 kPa. Then, it is compared whether or not the liquid pump operation elapsed time is longer than the liquid pump filtration set time. When the liquid pump operation elapsed time is smaller than the liquid pump filtration set time, the water level of the water level gauge 19 and the water level L of the storage tank are further compared. When the water level of the water level gauge 19 is higher than the storage tank water level L, the process returns to the process of comparing whether or not the liquid pump operation elapsed time is equal to or longer than the liquid pump filtration set time, and this process loop is executed. Since the unconcentrated sludge discharge process operates simultaneously with the liquid pump filtration process, the concentrated sludge adhering to the surface of the filtration membrane 3a above the water level that is falling by the unconcentrated sludge discharge process is subjected to liquid pump filtration while being in contact with the outside air. Is called. Further, when the liquid pump operation elapsed time is larger than the liquid pump filtration set time, and when the liquid pump operation elapsed time is smaller than the liquid pump filtration set time and the water level of the water level gauge 19 is lower than the storage tank water level L, the liquid The pump 16 is stopped, the valve 11 is closed, and the measurement of the liquid pump operation elapsed time is finished.
次に、エアーポンプ濾過工程のフロー図を図10に示す。弁10,13を開き、貯留タンク5内の圧力を減圧させるようにエアーポンプ7を作動させると同時にエアーポンプ作動経過時間の計測を開始する。液体ポンプ16とエアーポンプ7とが同時に作動する時に、貯留タンク5内の気体圧力を液体ポンプ16の作動圧力許容範囲内とする。
貯留タンク5の水位が水位H以上になると、弁10,13を閉じる。そして、濾液流路排水工程を実行する。エアーポンプ作動経過時間がエアーポンプ濾過設定時間以上になると、弁10,13を閉じ、エアーポンプを停止させてエアーポンプ濾過工程を終了する。
Next, the flowchart of an air pump filtration process is shown in FIG. The valves 10 and 13 are opened, and the air pump 7 is operated so as to reduce the pressure in the storage tank 5, and at the same time, the measurement of the elapsed time of the air pump operation is started. When the liquid pump 16 and the air pump 7 operate simultaneously, the gas pressure in the storage tank 5 is set within the allowable operating pressure range of the liquid pump 16.
When the water level of the storage tank 5 becomes equal to or higher than the water level H, the valves 10 and 13 are closed. And a filtrate flow path drainage process is performed. When the air pump operation elapsed time is equal to or longer than the air pump filtration set time, the valves 10 and 13 are closed, the air pump is stopped, and the air pump filtration process is ended.
次に、濾液流路排水工程のフロー図を図11に示す。まず、弁14を開ける。そして、貯留タンク5および濾液排出管4の濾液を除去するために、弁38を開け、貯留タンク5の濾液が排水された後に弁14,38を閉じる。前記の「弁38を開け、貯留タンク5の濾液が排水された後に弁14,38を閉じる」方法の代わりに弁11を開け、貯留タンク5の水位が水位Lになるまで液体ポンプ16を作動させた後、弁11,14を閉じて液体ポンプ16を停止させても良い。 Next, a flow chart of the filtrate flow path draining process is shown in FIG. First, the valve 14 is opened. And in order to remove the filtrate of the storage tank 5 and the filtrate discharge pipe 4, the valve 38 is opened, and after the filtrate of the storage tank 5 is drained, the valves 14 and 38 are closed. Instead of the above-described method of “opening the valve 38 and closing the valves 14 and 38 after the filtrate in the storage tank 5 is drained”, the valve 11 is opened and the liquid pump 16 is operated until the water level in the storage tank 5 reaches the water level L. Then, the valves 11 and 14 may be closed to stop the liquid pump 16.
次に、濃縮汚泥剥離工程のフロー図を図12に示す。弁10,13を開け、濾過膜3aの2次側に空気をエアーポンプ7で入れて加圧すると共に、剥離経過時間の計測を開始する。すると、袋状の濾過膜3aは膨らみ、濾過膜3aの1次側表面に付着した濃縮汚泥は濾過膜3aから剥離され、落下する。落下した濃縮汚泥は汚泥槽1の底に堆積する。剥離経過時間と剥離設定時間を比較し、剥離経過時間が剥離設定時間以上の場合、エアーポンプの動作を停止して弁10,13を閉じる。 Next, a flow chart of the concentrated sludge peeling step is shown in FIG. The valves 10 and 13 are opened, and air is introduced into the secondary side of the filtration membrane 3a with the air pump 7 to pressurize it, and the measurement of the elapsed peeling time is started. Then, the bag-like filtration membrane 3a swells, and the concentrated sludge adhering to the primary surface of the filtration membrane 3a is peeled off from the filtration membrane 3a and falls. The concentrated sludge that has fallen is deposited on the bottom of the sludge tank 1. The peeling elapsed time and the peeling set time are compared. If the peeling elapsed time is equal to or longer than the peeling set time, the operation of the air pump is stopped and the valves 10 and 13 are closed.
次に、濃縮汚泥排出工程のフロー図を図13に示す。弁9を開け、濃縮汚泥ポンプを作動させて濃縮汚泥を汚泥槽1から排出する。濃縮汚泥の水位と水位計20の水位を比較して濃縮汚泥の水位が水位計20の水位以下の場合、濃縮汚泥ポンプを停止し、弁9を閉じる。濃縮汚泥排出工程では、水位計20を用いる代わりに濃縮汚泥ポンプの作動時間をタイマーで予め設定しておき、設定時間になると濃縮汚泥ポンプが停止するようにしても良い。 Next, FIG. 13 shows a flowchart of the concentrated sludge discharging step. The valve 9 is opened, the concentrated sludge pump is operated, and the concentrated sludge is discharged from the sludge tank 1. When the water level of the concentrated sludge is compared with the water level of the water level meter 20 and the water level of the concentrated sludge is below the water level of the water level meter 20, the concentrated sludge pump is stopped and the valve 9 is closed. In the concentrated sludge discharging step, the operation time of the concentrated sludge pump may be set in advance with a timer instead of using the water level gauge 20, and the concentrated sludge pump may be stopped when the set time is reached.
本実施例では、各水位計を用いて水面の検知を行っているが、各ポンプの吐出または吸引体積と各タンク寸法とから演算することで、各タンクの水位を測定してもよい。
これらにより、サイフォン濾過工程では汚泥槽1へ入れた汚泥の初期濃度に対して約1.5倍の濃縮度であったものが、エアーポンプ濾過工程および液体ポンプ濾過工程後には更に約1.3倍の高濃度の濃縮汚泥が得られた。
In this embodiment, the water level is detected using each water level meter, but the water level of each tank may be measured by calculating from the discharge or suction volume of each pump and each tank size.
As a result, in the siphon filtration step, the concentration which was about 1.5 times the initial concentration of the sludge put into the sludge tank 1 was further increased to about 1.3 after the air pump filtration step and the liquid pump filtration step. Double concentration of concentrated sludge was obtained.
1 汚泥槽
2 汚泥供給兼排出ポンプ
3 濾過部
3a 濾過膜
3b 濾枠
4 濾液排出管
5 貯留タンク
6 水道水供給管
7 エアーポンプ
8〜14 弁
15 空気分配管
16 液体ポンプ
17 圧力計
18〜20 水位計
21 濾過濃縮装置
22 缶体
23 仕切板
24 上室
25 下室
26 濾過体
27 被処理液導入管
28 濾液排出管
29 濾液弁
30 真空弁
31 真空ポンプ
32 貯留タンク
33 真空ライン
34 排液弁
35 吸気弁
36 空気導入管
37 給排気管
38 弁
39 濃縮汚泥ポンプ
40 気体通流管
41 汚泥供給管
42 濃縮汚泥排出管
43 大気開放管
DESCRIPTION OF SYMBOLS 1 Sludge tank 2 Sludge supply and discharge pump 3 Filtration part 3a Filtration membrane 3b Filter frame 4 Filtrate discharge pipe 5 Storage tank 6 Tap water supply pipe 7 Air pump 8-14 Valve 15 Air distribution pipe 16 Liquid pump 17 Pressure gauge 18-20 Water level gauge 21 Filtration concentrator 22 Can body 23 Partition plate 24 Upper chamber 25 Lower chamber 26 Filter body 27 Processed liquid introduction pipe 28 Filtrate discharge pipe 29 Filtrate valve 30 Vacuum valve 31 Vacuum pump 32 Storage tank 33 Vacuum line 34 Drain valve 35 Intake valve 36 Air introduction pipe 37 Supply / exhaust pipe 38 Valve 39 Concentrated sludge pump 40 Gas flow pipe 41 Sludge supply pipe 42 Concentrated sludge discharge pipe 43 Atmospheric release pipe
Claims (8)
前記貯留タンクの圧力を測定する圧力計と、前記貯留タンク内部の水位を測定する水位測定手段と、前記貯留タンクより下流の前記濾液排出管に連通させた液体ポンプと、前記汚泥供給手段,前記未濃縮汚泥排出手段,前記剥離手段,前記濃縮汚泥排出手段,前記濾液排出管,および前記気体通流管の流体流路にそれぞれ設けた弁と、制御装置とを備えることを特徴とする濾過濃縮装置。 A sludge tank, a sludge supply means for supplying sludge to the sludge tank, a filtration unit installed in the sludge tank for filtering the sludge, a filtrate discharge pipe drawn out of the sludge tank from the filtration unit, Unconcentrated sludge discharging means, peeling means for peeling the concentrated sludge adhering to the filtration unit, concentrated sludge discharging means for discharging the peeled concentrated sludge from the sludge tank, and a storage tank installed in the middle of the filtrate discharge pipe An air pump capable of discharging gas to the storage tank and sucking the gas in the storage tank, a gas flow pipe communicating the storage tank and the air pump, and connecting the sludge supply means and the sludge tank. In a filtration and concentration device equipped with a sludge supply pipe,
A pressure gauge for measuring the pressure of the storage tank, a water level measuring means for measuring the water level inside the storage tank, a liquid pump communicating with the filtrate discharge pipe downstream from the storage tank, the sludge supply means, Filtration concentration characterized by comprising a control device and a valve provided in each of the fluid flow paths of the unconcentrated sludge discharging means, the peeling means, the concentrated sludge discharging means, the filtrate discharge pipe, and the gas flow pipe. apparatus.
前記貯留タンク内の液体水位を所定範囲内に制御する前記液体ポンプ濾過工程と、前記貯留タンク内の気体を吸引するエアーポンプ濾過工程とを同時に実行することを特徴とする濾過濃縮方法。 A sludge supply step, an air pump filtration step, and an unconcentrated sludge discharge step are provided, and the concentrated sludge stripping step is executed after all of the sludge supply step, the air pump filtration step, and the unconcentrated sludge discharge step are completed. In the filtration and concentration method,
A filtration and concentration method, wherein the liquid pump filtration step for controlling the liquid water level in the storage tank within a predetermined range and the air pump filtration step for sucking the gas in the storage tank are performed simultaneously.
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| JP2006177876A JP4677374B2 (en) | 2006-06-28 | 2006-06-28 | Filtration concentration apparatus and filtration concentration method |
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Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2007296455A (en) * | 2006-04-28 | 2007-11-15 | Fuji Electric Systems Co Ltd | Filtration concentrator |
| JP2009207982A (en) * | 2008-03-04 | 2009-09-17 | Metawater Co Ltd | Method of recovering phosphorus extract |
| CN117566997A (en) * | 2023-12-29 | 2024-02-20 | 中建三局绿色产业投资有限公司 | An environmentally friendly sludge dewatering device for dredging |
| CN119113798A (en) * | 2024-11-12 | 2024-12-13 | 安庆恩聚生物医药科技有限公司 | A concentration and filtration device for preparing penicillin |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN111282330A (en) * | 2020-03-14 | 2020-06-16 | 刘春焕 | Multi-pipeline press filtration type sewage treatment all-in-one machine |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2000342911A (en) * | 1999-06-08 | 2000-12-12 | Hitoshi Daido | Dynamic filter |
| JP2002001248A (en) * | 2000-06-20 | 2002-01-08 | Tenkou:Kk | Screen residue transfer apparatus |
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- 2006-06-28 JP JP2006177876A patent/JP4677374B2/en active Active
Patent Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2000342911A (en) * | 1999-06-08 | 2000-12-12 | Hitoshi Daido | Dynamic filter |
| JP2002001248A (en) * | 2000-06-20 | 2002-01-08 | Tenkou:Kk | Screen residue transfer apparatus |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2007296455A (en) * | 2006-04-28 | 2007-11-15 | Fuji Electric Systems Co Ltd | Filtration concentrator |
| JP2009207982A (en) * | 2008-03-04 | 2009-09-17 | Metawater Co Ltd | Method of recovering phosphorus extract |
| CN117566997A (en) * | 2023-12-29 | 2024-02-20 | 中建三局绿色产业投资有限公司 | An environmentally friendly sludge dewatering device for dredging |
| CN119113798A (en) * | 2024-11-12 | 2024-12-13 | 安庆恩聚生物医药科技有限公司 | A concentration and filtration device for preparing penicillin |
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| JP4677374B2 (en) | 2011-04-27 |
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