JP2008307535A - Apparatus for dewatering sludge - Google Patents

Apparatus for dewatering sludge Download PDF

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JP2008307535A
JP2008307535A JP2008160255A JP2008160255A JP2008307535A JP 2008307535 A JP2008307535 A JP 2008307535A JP 2008160255 A JP2008160255 A JP 2008160255A JP 2008160255 A JP2008160255 A JP 2008160255A JP 2008307535 A JP2008307535 A JP 2008307535A
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sludge
filter cylinder
tank
supply pipe
supplied
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JP4887335B2 (en
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Kiyohiro Tozawa
清浩 戸澤
Kaoru Yasutake
馨 安竹
Kazutomo Yoshida
和睦 吉田
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Okumura Corp
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Abstract

<P>PROBLEM TO BE SOLVED: To provide an apparatus for dewatering sludge which enables flocculated sludge to be formed into a dewatered cake at high efficiency without being finely grained when supplied to a filter cylinder. <P>SOLUTION: In the apparatus A for dewatering the sludge, the sludge and a flocculating agent are mixed under stirring in a flocculation reactor 5 to form the flocculated sludge. The flocculated sludge is supplied into a filter cylinder 71 of a vertical type screw press 7 through a receiving port 76 provided on the lower part of the filter cylinder 71, and is dewatered by squeezing, while being conveyed upward in the filter cylinder 71 by the rotation of a screw 72 disposed in the filter cylinder 71. The flocculation reactor 5 is disposed above the receiving port 76. A supply pipe 6 is provided for supplying the flocculated sludge from the flocculation reactor 5 to the receiving port 76. The flocculated sludge is supplied into the filter cylinder 71 under pressure, while a state, where the flocculated sludge is accumulated in the supply pipe 6, is maintained. <P>COPYRIGHT: (C)2009,JPO&INPIT

Description

本発明は、主としてダム湖・港湾・河川の浚渫工事、トンネル掘削工事等で発生する汚泥の脱水処理装置に関する。   The present invention relates to a dewatering apparatus for sludge generated mainly during dredging work for dam lakes, harbors and rivers, tunnel excavation work, and the like.

ダム湖・港湾・河川の浚渫工事、トンネル掘削工事等で発生した水、粘土、シルトなどの混合物(以下、「汚泥」という。)は、脱水処理装置によって水が分離され脱水ケーキとされる。凝集反応槽にて汚泥と凝集剤とが攪拌混合されて凝集汚泥(フロック)が生成され、スクリュープレスの濾筒内に供給され、該濾筒内に配設されたスクリューの回転により当該濾筒内を搬送されつつ圧搾脱水されて脱水ケーキとなる。   The mixture of water, clay, silt, etc. (hereinafter referred to as “sludge”) generated during dredging work in dam lakes, harbors and rivers, tunnel excavation work, etc., is separated into water by a dehydration processing device to form dehydrated cake. The sludge and flocculant are stirred and mixed in the agglomeration reaction tank to produce agglomerated sludge (floc), which is supplied into the filter cylinder of the screw press, and the filter cylinder is rotated by rotation of the screw disposed in the filter cylinder. It is pressed and dehydrated while being transported inside to form a dehydrated cake.

スクリュープレスには、濾筒を水平方向に長手とした横型のものと、濾筒を上下方向に長手とした縦型のものとがある。ダム湖の浚渫工事の現場となる山間地やトンネル掘削工事の現場となる都市部では、スクリュープレスの設置スペースを広く確保することが困難な場合が多く、狭い場所にも設置できる縦型スクリュープレスが好適に使用される。   The screw press includes a horizontal type in which the filter cylinder is elongated in the horizontal direction and a vertical type in which the filter cylinder is elongated in the vertical direction. Vertical screw presses that can be installed in confined spaces are often difficult in mountainous areas where dredging works are performed on dam lakes and in urban areas where tunnel excavation works. Are preferably used.

縦型スクリュープレスでは、濾筒の下部に設けた受入口から当該濾筒内に供給された凝集汚泥をスクリューの回転により当該濾筒内を上方に搬送しつつ圧搾脱水して、濾筒内の上端の排出口から上方に押し出される被圧搾物(脱水ケーキ)を外部に排出している(例えば、特許文献1参照)。凝集汚泥は、ポンプにて加圧されて濾筒内に供給される。
特開2005−74384号公報
In the vertical screw press, the coagulated sludge supplied into the filter tube from the receiving port provided at the lower part of the filter tube is squeezed and dehydrated while being conveyed upward in the filter tube by the rotation of the screw. An object to be pressed (dehydrated cake) pushed upward from the discharge port at the upper end is discharged to the outside (see, for example, Patent Document 1). The agglomerated sludge is pressurized by a pump and supplied into the filter cylinder.
JP 2005-74384 A

しかしながら、凝集汚泥をポンプにて加圧して濾筒内に供給すると、ポンプを通過する際に凝集汚泥が粉砕され細粒分が生じる。この汚泥の細粒分は、濾筒の網目を通過(リーク)して濾液と共に排出されるため、脱水ケーキの生成効率が低下するという問題がある。   However, when the coagulated sludge is pressurized with a pump and supplied into the filter cylinder, the coagulated sludge is pulverized and fine particles are produced when passing through the pump. Since the fine sludge fraction passes through (leaks) the mesh of the filter cylinder and is discharged together with the filtrate, there is a problem that the production efficiency of the dehydrated cake is lowered.

本発明は、上記事情に鑑み、濾筒に供給される際に凝集汚泥が細粒化されることなく、脱水ケーキ生成の高効率化を図ることが可能な汚泥の脱水処理装置を提供することを目的とする。   In view of the above circumstances, the present invention provides a sludge dewatering apparatus capable of increasing the efficiency of dewatered cake generation without agglomerating sludge when supplied to a filter tube. With the goal.

本発明は、凝集反応槽にて汚泥と凝集剤とが攪拌混合されて凝集汚泥が生成され、該凝集汚泥が縦型スクリュープレスの濾筒内に当該濾筒の下部に設けた受入口から供給され、該濾筒内に配設されたスクリューの回転により凝集汚泥が当該濾筒内を上方に搬送されつつ圧搾脱水されるようにした汚泥の脱水処理装置において、前記受入口より上方に前記凝集反応槽が配設され、該凝集反応槽から前記受入口に凝集汚泥を供給する供給パイプを備え、当該供給パイプ内に凝集汚泥が滞留する状態を維持して、凝集汚泥を前記濾筒内に加圧供給することを特徴とする。   In the present invention, sludge and flocculant are stirred and mixed in a flocculation reaction tank to produce flocculated sludge, and the flocculated sludge is supplied from a receiving port provided at a lower portion of the filter cylinder in a filter cylinder of a vertical screw press. In the sludge dewatering apparatus, the aggregated sludge is compressed and dehydrated while being transported upward in the filter cylinder by the rotation of a screw disposed in the filter cylinder. A reaction tank is provided, and a supply pipe for supplying the coagulated sludge from the coagulation reaction tank to the receiving port is maintained, and the state in which the coagulated sludge stays in the supply pipe is maintained. It is characterized by supplying pressure.

本発明によれば、縦型スクリュープレスの濾筒への凝集汚泥の受入口より上方に配設された凝集反応槽から当該受入口に向けて凝集汚泥(フロック)を供給する供給パイプ内に凝集汚泥が滞留する状態を維持する。そして、供給パイプ内に滞留する凝集汚泥自体の自重によって、凝集汚泥を濾筒内に加圧供給する。そのため、凝集汚泥を加圧するためにポンプを用いる必要がないので、凝集反応槽から濾筒に至る間、凝集汚泥はほとんど細粒化されない。従って、脱水ケーキの生成効率を向上することが可能となる。   According to the present invention, flocculation is aggregated in a supply pipe for supplying flocculated sludge (floc) from a flocculation reaction tank disposed above a receiving port of the flocculated sludge to a filter tube of a vertical screw press toward the receiving port. Maintains sludge retention. Then, the coagulated sludge is pressurized and supplied into the filter cylinder by the own weight of the coagulated sludge itself staying in the supply pipe. Therefore, since it is not necessary to use a pump to press the coagulated sludge, the coagulated sludge is hardly finely divided from the coagulation reaction tank to the filter tube. Accordingly, it is possible to improve the production efficiency of the dehydrated cake.

また、本発明において、前記供給パイプ内に滞留する凝集汚泥の高さが所定範囲となる状態を維持することが好ましい。   In the present invention, it is preferable to maintain a state where the height of the coagulated sludge staying in the supply pipe is within a predetermined range.

この場合、凝集汚泥を濾筒内に加圧供給する際の圧力が所定範囲となる。そのため、凝集汚泥を濾筒内に適切な圧力で加圧供給することが可能となる。   In this case, the pressure when supplying the coagulated sludge under pressure into the filter cylinder is within a predetermined range. Therefore, it is possible to press and supply the coagulated sludge at an appropriate pressure in the filter cylinder.

本発明の一実施形態に係る汚泥の脱水処理装置について説明する。図1を参照して、この汚泥の脱水処理装置Aは、主として、汚泥貯留槽(原泥槽)1、ラインミキサー2、アニオン系凝集剤供給部3、カチオン系凝集剤供給部4、凝集反応槽5、供給パイプ6、縦型スクリュープレス7、及び濾液処理槽8から構成されている。   A sludge dewatering apparatus according to an embodiment of the present invention will be described. With reference to FIG. 1, this sludge dewatering apparatus A mainly includes a sludge storage tank (raw mud tank) 1, a line mixer 2, an anionic flocculant supply unit 3, a cationic flocculant supply unit 4, and an agglutination reaction. The tank 5 is composed of a supply pipe 6, a vertical screw press 7, and a filtrate treatment tank 8.

汚泥貯留槽1は、濃度調整された汚泥を貯留する。汚泥は、ダム湖・港湾・河川の浚渫工事、トンネル掘削工事等で発生した泥状物から礫や砂が除去された、水、粘土、シルトなどからなる混合物である。汚泥は、その含水率が80%程度となるように適宜水で希釈され濃度調整されている。また、固化や後述する凝集効果を高める観点から、汚泥の固形分の10%程度のフライアッシュを汚泥に混和しておくことが好ましい。汚泥貯留槽1に貯留される汚泥は、沈降防止のために、モータMにより回転駆動する攪拌翼により攪拌される。汚泥貯留槽1内に貯留される汚泥は、ポンプP1により吐出されて、管路11を介して凝集反応槽5に向けて圧送される。   The sludge storage tank 1 stores sludge whose concentration has been adjusted. Sludge is a mixture of water, clay, silt, etc., from which gravels and sand have been removed from sludge generated during dredging work in dam lakes, harbors and rivers, tunnel excavation work, etc. The sludge is appropriately diluted with water so that its moisture content is about 80% and the concentration is adjusted. Moreover, it is preferable to mix the fly ash of about 10% of sludge solid content in the sludge from the viewpoint of solidification and enhancing the coagulation effect described later. The sludge stored in the sludge storage tank 1 is stirred by a stirring blade that is rotationally driven by a motor M in order to prevent sedimentation. The sludge stored in the sludge storage tank 1 is discharged by the pump P <b> 1 and is pumped toward the agglomeration reaction tank 5 through the pipeline 11.

ラインミキサー2は、汚泥貯留槽1と凝集反応槽5との間を接続する管路11に介設されている。ラインミキサー2は、螺旋状の邪魔板をパイプ内に設けたスタティック型ミキサーであり、ポンプP1により汚泥貯留槽1から吐出され管路11を圧送される汚泥を攪拌する。   The line mixer 2 is interposed in a pipeline 11 that connects between the sludge storage tank 1 and the agglomeration reaction tank 5. The line mixer 2 is a static mixer in which a spiral baffle plate is provided in a pipe, and stirs the sludge discharged from the sludge storage tank 1 by the pump P1 and pumped through the pipeline 11.

アニオン系凝集剤供給部3は、主に、アニオン系凝集剤溶解槽31と2つの連通するアニオン系凝集剤貯留槽32とから構成されている。アニオン系凝集剤溶解槽31は、フィーダ(図示せず)から供給されるアニオン系凝集剤と、清水槽33から供給される清水とを、モータMにより回転駆動する攪拌翼により混合攪拌して、アニオン系凝集剤を溶解する。この溶解されたアニオン系凝集剤(以下、アニオン系溶解凝集剤という。)は、ポンプP2により吐出されて、アニオン系凝集剤貯留槽32に供給される。アニオン系凝集剤貯留槽32は、その槽内にアニオン系溶解凝集剤を、モータMにより回転駆動する攪拌翼によって攪拌しながら貯留する。   The anionic flocculant supply unit 3 mainly includes an anionic flocculant dissolution tank 31 and two communicating anionic flocculant storage tanks 32. The anionic flocculant dissolution tank 31 mixes and stirs the anionic flocculant supplied from a feeder (not shown) and the fresh water supplied from the fresh water tank 33 with a stirring blade that is rotationally driven by a motor M, Dissolve anionic flocculants. The dissolved anionic flocculant (hereinafter referred to as an anionic flocculant) is discharged by the pump P2 and supplied to the anionic flocculant reservoir 32. The anionic flocculant storage tank 32 stores the anionic dissolution flocculant in the tank while being stirred by a stirring blade that is rotationally driven by the motor M.

一方のアニオン系凝集剤貯留槽32内に貯留するアニオン系溶解凝集剤は、ポンプP3により吐出されて、ラインミキサー2より上流側の管路11の部分に設けた投入口(第1の投入口)12から管路11内に投入され、ラインミキサー2で汚泥と攪拌されて混合される。汚泥にアニオン系凝集剤を混合すると粘度が高くなる。そのため、アニオン系溶解凝集剤を投入口12から過度に投入すると、汚泥を凝集反応槽5まで圧送できなくなる。そこで、投入口12からのアニオン系溶解凝集剤の投入量は凝集反応槽5まで汚泥をポンプ圧送可能な程度の量とする。他方のアニオン系凝集剤貯留槽32内に貯留するアニオン系溶解凝集剤は、ポンプP4により吐出されて、凝集反応槽5に設けた投入口(第2の投入口)51から凝集反応槽5内に投入される。投入口51からのアニオン系溶解凝集剤の投入量は、汚泥の凝集効果を高くするために必要なアニオン系溶解凝集剤の量より投入口12からのアニオン系溶解凝集剤の投入量を差し引いた量に設定する。   The anionic flocculating agent stored in one anionic flocculating agent storage tank 32 is discharged by the pump P3 and is provided at the inlet (first inlet) provided in the portion of the pipe line 11 upstream from the line mixer 2. ) Is introduced into the pipe line 11 from 12 and is agitated and mixed with sludge by the line mixer 2. When an anionic flocculant is mixed with sludge, the viscosity increases. For this reason, if the anionic dissolution flocculant is excessively charged from the inlet 12, the sludge cannot be pumped to the aggregation reaction tank 5. Therefore, the amount of the anionic dissolution flocculant charged from the charging port 12 is set to such an amount that the sludge can be pumped to the aggregation reaction tank 5. The anionic dissolution flocculant stored in the other anionic flocculant storage tank 32 is discharged by the pump P4 and enters the aggregation reaction tank 5 from the input port (second input port) 51 provided in the aggregation reaction tank 5. It is thrown into. The input amount of the anionic dissolution flocculant from the input port 51 was obtained by subtracting the input amount of the anionic dissolution flocculant from the input port 12 from the amount of the anionic dissolution flocculant required to increase the sludge aggregation effect. Set to quantity.

カチオン系凝集剤供給部4は、主に、カチオン系凝集剤溶解槽41とカチオン系凝集剤貯留槽42とから構成されている。カチオン系凝集剤溶解槽41は、フィーダ(図示せず)から供給されるカチオン系凝集剤と、清水槽33から供給される清水とを、モータMにより回転駆動する攪拌翼により混合攪拌して、カチオン系凝集剤を溶解する。この溶解されたカチオン系凝集剤(以下、カチオン系溶解凝集剤という。)は、ポンプP5により吐出されて、カチオン系凝集剤貯留槽42に供給される。カチオン系凝集剤貯留槽42は、その槽内にカチオン系溶解凝集剤を、モータMにより回転駆動する攪拌翼によって攪拌しながら貯留する。   The cationic flocculant supply unit 4 is mainly composed of a cationic flocculant dissolution tank 41 and a cationic flocculant storage tank 42. The cationic flocculant dissolution tank 41 mixes and stirs the cationic flocculant supplied from a feeder (not shown) and the fresh water supplied from the fresh water tank 33 with a stirring blade that is rotationally driven by the motor M, Dissolve the cationic flocculant. The dissolved cationic flocculant (hereinafter referred to as “cationic flocculant”) is discharged by the pump P5 and supplied to the cationic flocculant reservoir 42. The cationic flocculant storage tank 42 stores the cationic dissolved flocculant in the tank while being stirred by a stirring blade that is rotationally driven by the motor M.

カチオン系凝集剤貯留槽42内に貯留するカチオン系溶解凝集剤は、ポンプP6により吐出されて、凝集反応槽5の投入口51より下流側に設けた投入口52から凝集反応槽5内に投入される。投入口52からは、汚泥の凝集効果を高くするために必要な量のカチオン系溶解凝集剤を投入する。   The cationic dissolution flocculant stored in the cationic flocculant storage tank 42 is discharged by the pump P6 and charged into the agglomeration reaction tank 5 from the charging port 52 provided downstream from the charging port 51 of the aggregation reaction tank 5. Is done. From the inlet 52, an amount of a cationic dissolution flocculant necessary for increasing the sludge aggregation effect is charged.

凝集反応槽5は、詳細は図示されていないが、攪拌翼が形成された回転軸がモータMにより回転駆動することにより内部に滞留する滞留物を攪拌すると共に、滞留物を上流側から下流側に移送する二軸のパドルミキサーである。尚、この凝集反応槽5内に送り翼が形成された回転軸を設け、これをモータMにより回転駆動することにより滞留物を移送するようにしてもよい。凝集反応槽5は、架台53によって縦型スクリュープレス7の上部と同じ程度の高さに位置して配設されている。   Although the details of the agglomeration reaction tank 5 are not shown, the rotating shaft on which the stirring blades are formed is driven to rotate by the motor M to stir the staying matter staying inside, and the staying matter is moved from the upstream side to the downstream side. It is a two-shaft paddle mixer that is transported to. In addition, a rotating shaft having a feeding blade formed in the agglomeration reaction tank 5 may be provided, and the staying material may be transferred by rotating the shaft by a motor M. The agglomeration reaction tank 5 is disposed at the same height as the upper part of the vertical screw press 7 by the gantry 53.

ラインミキサー2にてアニオン系凝集剤と攪拌混合されてある程度凝集し粘度が高まった状態の汚泥が、受入口54から凝集反応槽5内に供給される。凝集反応槽5内に供給された汚泥は、滞留物として攪拌翼により攪拌されると共に送り翼により下流側に移送されながら、投入口51から投入されたアニオン系溶解凝集剤、及びその下流側の投入口52から投入されたカチオン系溶解凝集剤と順次混合されて反応することにより、さらに凝集が進行して凝集汚泥(フロック)となる。   Sludge that has been agitated and mixed with the anionic flocculant in the line mixer 2 and has agglomerated to some extent to increase the viscosity is supplied into the agglomeration reaction tank 5 from the receiving port 54. The sludge supplied into the agglomeration reaction tank 5 is agitated by the stirring blade as a stagnant substance and is transferred to the downstream side by the feed blade, and the anionic dissolution flocculant charged from the inlet 51 and the downstream side thereof. By sequentially mixing and reacting with the cationic dissolving flocculant charged from the charging port 52, the agglomeration further proceeds to become agglomerated sludge (floc).

攪拌翼及び必要に応じて送り翼が回転する槽の下流側の側壁が堰55となっており、堰55を越えて溢れ出た凝集汚泥が、凝集反応槽5の底部に設けた排出口56から下方に落下する。排出口56の直下には、傾斜スクリーン57が配設されている。この傾斜スクリーン57は、細かい網目が多数形成された水切り用のスクリーンであり、受箱の上に傾斜して設置されている。傾斜スクリーン57の網目を通過した液体や微粒子は受箱を介して濾液処理槽8に送られる。一方、傾斜スクリーン57の網目を通過できない凝集汚泥は、供給パイプ6内に落下する。   The side wall on the downstream side of the tank where the stirring blade and the feed blade rotate as necessary is a weir 55, and the aggregated sludge overflowing the weir 55 is provided at the discharge port 56 provided at the bottom of the aggregation reaction tank 5. Falls downward from An inclined screen 57 is disposed immediately below the discharge port 56. The inclined screen 57 is a screen for draining in which a lot of fine meshes are formed, and is inclined on a receiving box. The liquid and fine particles that have passed through the mesh of the inclined screen 57 are sent to the filtrate treatment tank 8 through a receiving box. On the other hand, the coagulated sludge that cannot pass through the mesh of the inclined screen 57 falls into the supply pipe 6.

供給パイプ6は、凝集反応槽5から縦型スクリュープレス7に凝集汚泥を供給するパイプであり、主として上下方向に伸びており、凝集反応槽5の排出口56から排出された凝集汚泥をその上部から内部に受け入れる。供給パイプ6又は凝集反応槽5には、その上部に外部と連通する開口(図示せず)が設けられており、この開口から空気が自由に行き来し、供給パイプ6内の圧が大気圧と等しくなるようになっている。   The supply pipe 6 is a pipe for supplying the coagulated sludge from the coagulation reaction tank 5 to the vertical screw press 7 and extends mainly in the vertical direction. The coagulation sludge discharged from the discharge port 56 of the coagulation reaction tank 5 is the upper part thereof. Accept from the inside. The supply pipe 6 or the agglomeration reaction tank 5 is provided with an opening (not shown) communicating with the outside at the upper portion thereof, and air freely passes through this opening, and the pressure in the supply pipe 6 is changed to the atmospheric pressure. It is supposed to be equal.

供給パイプ6は、凝集反応槽5と縦型スクリュープレス7とを連通する太い主パイプ61とは別に、主パイプ61から分岐して上下方向に伸びる細い副パイプ62を有している。この副パイプ62には、高低2つの界面センサ63,64が配設されている。界面センサ63,64は、凝集汚泥と水との界面の高さが、それぞれ所定高さを超えるか否かを検知する。このように高低2つの界面センサ63,64を設けることによって、供給パイプ6内に滞留する凝集汚泥の高さが所定範囲となる状態を維持することが可能となる。具体的には、供給パイプ6内に滞留する凝集汚泥の高さが上限を超えたことを高い位置の界面センサ63により検知した場合には、ポンプP1を停止して、汚泥貯留槽1からの汚泥の供給を停止する。一方、供給パイプ6内に滞留する凝集汚泥の高さが下限を下回ったことを低い位置の界面センサ64により検知した場合には、ポンプP1の出力を上げて、汚泥貯留槽1からの汚泥の供給量を増加させる。この供給パイプ6内に滞留する凝集汚泥の高さの上限及び下限の設定については後述する。   The supply pipe 6 has a thin sub pipe 62 that branches from the main pipe 61 and extends in the vertical direction separately from the thick main pipe 61 that communicates the aggregation reaction tank 5 and the vertical screw press 7. The sub-pipe 62 is provided with two high and low interface sensors 63 and 64. The interface sensors 63 and 64 detect whether or not the height of the interface between the coagulated sludge and water exceeds a predetermined height. By providing the two high and low interface sensors 63 and 64 in this way, it is possible to maintain a state where the height of the coagulated sludge staying in the supply pipe 6 is within a predetermined range. Specifically, when it is detected by the interface sensor 63 at a high position that the height of the coagulated sludge staying in the supply pipe 6 exceeds the upper limit, the pump P1 is stopped and the sludge storage tank 1 Stop supplying sludge. On the other hand, when it is detected by the interface sensor 64 at a low position that the height of the coagulated sludge staying in the supply pipe 6 is lower than the lower limit, the output of the pump P1 is increased and the sludge from the sludge storage tank 1 is increased. Increase supply. The setting of the upper limit and the lower limit of the height of the coagulated sludge staying in the supply pipe 6 will be described later.

縦型スクリュープレス7は、上下方向を長手とする濾筒71と、濾筒71内に回転自在に配設されたスクリュー72と、水平方向に隙間Sを設けて濾筒71の周囲を覆う覆筒73とを備え、濾筒71内に供給された凝集汚泥をスクリュー72にて上方に搬送させつつ圧搾脱水して、分離した水を濾筒71から隙間Sに排出する。   The vertical screw press 7 includes a filter cylinder 71 whose longitudinal direction is the longitudinal direction, a screw 72 rotatably disposed in the filter cylinder 71, and a gap S in the horizontal direction so as to cover the periphery of the filter cylinder 71. The aggregated sludge supplied to the filter cylinder 71 is compressed and dehydrated while being conveyed upward by the screw 72, and the separated water is discharged from the filter cylinder 71 into the gap S.

縦型スクリュープレス7は、柱や梁等で構成され上下方向を長手とする四角柱状の枠体74を有しており、枠体74の下部に底板75が横設されている。底板75には、パンチングメタル等で形成される円筒状の濾筒71が立設されている。覆筒73は、この枠体74を構成する縦柱間に下端が底板75に当接するように取り付けられたシールド板で構成されている。濾筒71の下部には受入口76が開設されており、供給パイプ6から供給される凝集汚泥が受入口76から濾筒71内に投入される。尚、濾筒71の外周面には補強枠が設けられている。   The vertical screw press 7 has a quadrangular columnar frame 74 composed of columns, beams, and the like and having a vertical direction as a longitudinal direction, and a bottom plate 75 is horizontally provided below the frame 74. On the bottom plate 75, a cylindrical filter tube 71 formed of punching metal or the like is erected. The cover cylinder 73 is composed of a shield plate attached so that the lower end is in contact with the bottom plate 75 between the vertical columns constituting the frame body 74. A receiving port 76 is provided at the lower portion of the filter cylinder 71, and the coagulated sludge supplied from the supply pipe 6 is introduced into the filter cylinder 71 from the receiving port 76. A reinforcing frame is provided on the outer peripheral surface of the filter cylinder 71.

濾筒71内にはスクリュー72が回転自在に挿通されている。スクリュー72は、濾筒71の下端側から上端側に向けて次第に拡径するテーパー状のスクリュー軸と、スクリュー軸の外周面に固定した螺旋状のスクリュー羽根とから構成されている。スクリュー72は、濾筒71の上方に設けられたモータMにより回転駆動される。   A screw 72 is rotatably inserted into the filter cylinder 71. The screw 72 includes a tapered screw shaft that gradually increases in diameter from the lower end side to the upper end side of the filter tube 71 and a helical screw blade fixed to the outer peripheral surface of the screw shaft. The screw 72 is rotationally driven by a motor M provided above the filter cylinder 71.

スクリュー72を回転させると、受入口76から受け入れた凝集汚泥がスクリュー羽根による送り作用で濾筒71の下方から上方に搬送される。濾筒71とスクリュー軸との間の空間は上方に向けて次第に狭くなっているため、凝集汚泥は濾筒71の上方に向けて搬送されつつ圧搾される。凝集汚泥の水分は濾筒71を通して搾り出され、濾液として隙間Sを落下して、底板75に形成された開口(図示せず)と集水枡77とを介して、濾液処理槽8に排出される。また、水を噴きかけて濾筒71の外表面を洗浄する散水管78が設けられており、この水も同様に濾液処理槽8に排出される。濾筒71の上端に連設された排出室79の底面には排出口79aが開設されている。脱水された凝集汚泥である脱水ケーキCは、排出口79aから排出室79に押し出され、排出口シュート79bを介して外部に排出される。また、排出口79aの上方には、エアシリンダ79cを介して邪魔板79dが排出口79a側に付勢された状態で設けられており、この邪魔板79dを押し上げながら脱水ケーキCが排出口79aより排出される。そして、この状態でのエアシリンダ79cのシリンダ圧を計測し、これを脱水ケーキCの強度や含水率を表す間接指標として汚泥の脱水処理装置A全体の運転管理に使用する。   When the screw 72 is rotated, the coagulated sludge received from the receiving port 76 is conveyed upward from below the filter cylinder 71 by the feeding action by the screw blades. Since the space between the filter cylinder 71 and the screw shaft is gradually narrowed upward, the coagulated sludge is squeezed while being conveyed upward of the filter cylinder 71. The moisture of the coagulated sludge is squeezed out through the filter cylinder 71, falls in the gap S as a filtrate, and is discharged to the filtrate treatment tank 8 through an opening (not shown) formed in the bottom plate 75 and a water collecting tank 77. Is done. Further, a water spray pipe 78 for spraying water to clean the outer surface of the filter cylinder 71 is provided, and this water is similarly discharged to the filtrate treatment tank 8. A discharge port 79 a is opened on the bottom surface of the discharge chamber 79 connected to the upper end of the filter cylinder 71. The dewatered cake C, which is the dewatered agglomerated sludge, is pushed out from the discharge port 79a to the discharge chamber 79 and discharged to the outside through the discharge port chute 79b. Further, a baffle plate 79d is provided above the discharge port 79a in a state of being biased toward the discharge port 79a via an air cylinder 79c, and the dehydrated cake C is pushed up while the baffle plate 79d is pushed up. More discharged. Then, the cylinder pressure of the air cylinder 79c in this state is measured, and this is used as an indirect index representing the strength and moisture content of the dewatered cake C for the operation management of the entire sludge dewatering apparatus A.

ここで、上記した供給パイプ6内に滞留する凝集汚泥の高さの上限及び下限は、フライアッシュの添加割合、凝集剤の添加割合や凝集汚泥の濃度といったスクリュープレス7に供給される凝集汚泥の性状や縦型スクリュープレス7の運転条件(スクリュー72の回転速度)に従って、所定範囲の強度若しくは含水率の脱水ケーキCを得ることができる範囲として設定される。   Here, the upper limit and the lower limit of the height of the coagulated sludge staying in the supply pipe 6 described above are those of the coagulated sludge supplied to the screw press 7 such as the fly ash addition ratio, the coagulant addition ratio, and the coagulated sludge concentration. According to the properties and the operating conditions of the vertical screw press 7 (rotational speed of the screw 72), the range is set as a range where a dehydrated cake C having a predetermined range of strength or moisture content can be obtained.

凝集汚泥は、濾筒71内を上方移動する際、下方からの加圧により上方移動される液体的性状からスクリュー羽根による機械的作用により上方移動される固体的性状に徐々に移行する。凝集汚泥の供給パイプ6内での高さが濾筒71内において液体的性状を有する高さの範囲内であると供給パイプ6内での凝集汚泥の高さより上方へ凝集汚泥を移送することが困難になる。このため、供給パイプ6内に滞留する凝集汚泥の高さの下限は、この濾筒71内において液体的性状を有する高さの範囲より上方に位置させる必要がある。   When the agglomerated sludge moves upward in the filter cylinder 71, it gradually shifts from a liquid property that is moved upward by pressurization from below to a solid property that is moved upward by a mechanical action by a screw blade. If the height of the coagulated sludge in the supply pipe 6 is within the range having a liquid property in the filter cylinder 71, the coagulated sludge can be transferred above the height of the coagulated sludge in the supply pipe 6. It becomes difficult. For this reason, the lower limit of the height of the coagulated sludge staying in the supply pipe 6 needs to be positioned above the range of the height having liquid properties in the filter cylinder 71.

一方、上限は、脱水ケーキCが過度に圧搾され濾筒71内で閉塞することのないように、脱水ケーキCの強度や含水率及びこれを間接的に表す邪魔板79dを付勢するエアシリンダ79cのシリンダ圧やスクリュー72の回転トルクなどの指標を基に設定する。   On the other hand, the upper limit is an air cylinder that energizes the strength and moisture content of the dewatered cake C and the baffle plate 79d that indirectly represents the dewatered cake C so that the dewatered cake C is not excessively compressed and blocked in the filter cylinder 71. It is set based on indices such as the cylinder pressure of 79c and the rotational torque of the screw 72.

濾液処理槽8は、縦型スクリュープレス7から排出された濾液及び傾斜スクリーン57の網目を通過した液体からなる排水を処理する。排水には、濾筒71や傾斜スクリーン57に形成された細かな孔を通過した汚泥の細粒分も若干残存する。   The filtrate treatment tank 8 treats the wastewater comprising the filtrate discharged from the vertical screw press 7 and the liquid that has passed through the mesh of the inclined screen 57. In the drainage, a small amount of fine sludge particles that have passed through the fine holes formed in the filter cylinder 71 and the inclined screen 57 also remain.

濾液処理槽8は、沈殿槽81と排水槽82とを備える。沈殿槽81は、排水を受け入れる。排水中に含まれる汚泥の細粒分は、時間経過に伴い沈殿し、沈殿槽81の底部に堆積する。尚、凝集剤を添加して汚泥の細粒分を凝集させ沈殿を促進させてもよい。沈殿槽81の底部に沈殿した汚泥の細粒分は、ポンプP7により吐出されて、ラインミキサー2と凝集反応槽5との間の部分の管路11内に送り返される。尚、汚泥貯留槽1とラインミキサー2との間の部分の管路11内や、汚泥貯留槽1内に送り返してもよい。   The filtrate treatment tank 8 includes a precipitation tank 81 and a drain tank 82. The sedimentation tank 81 receives drainage. The fine particles of sludge contained in the waste water are precipitated with the passage of time and are deposited at the bottom of the settling tank 81. A flocculant may be added to agglomerate the sludge fine particles to promote precipitation. Sludge fine particles settled on the bottom of the settling tank 81 are discharged by the pump P7 and sent back into the pipe line 11 in the portion between the line mixer 2 and the agglomeration reaction tank 5. In addition, you may send back in the pipe line 11 of the part between the sludge storage tank 1 and the line mixer 2, or in the sludge storage tank 1. FIG.

沈殿槽81と排水槽82との間には堰83が設けられており、沈殿槽81に貯留された水分の上澄みが堰83を越えて排水槽82に放出されるようになっている。排水槽82に貯留された排水は、ポンプP8により吐出されて、雑排水槽9に送られる。   A weir 83 is provided between the settling tank 81 and the drainage tank 82, and the supernatant of water stored in the settling tank 81 passes through the weir 83 and is discharged to the drainage tank 82. The wastewater stored in the drainage tank 82 is discharged by the pump P8 and sent to the miscellaneous drainage tank 9.

排水槽82には、フロートスイッチ(図示せず)が設けられている。このフロートスイッチは、排水槽82の水位が所定範囲にあるか否かを検知するレベルセンサであり、その水位が所定範囲の上限を超えた場合には、ポンプP1を停止して、汚泥貯留槽1からの汚泥の供給を停止する。一方、水位が所定範囲の下限を下回った場合には、ポンプP8を停止して、排水槽82からの雑排水槽9への排水の移送を停止する。   The drain tank 82 is provided with a float switch (not shown). This float switch is a level sensor that detects whether or not the water level of the drainage tank 82 is within a predetermined range. When the water level exceeds the upper limit of the predetermined range, the pump P1 is stopped and the sludge storage tank Stop the supply of sludge from 1. On the other hand, when the water level falls below the lower limit of the predetermined range, the pump P8 is stopped, and the transfer of drainage from the drainage tank 82 to the miscellaneous drainage tank 9 is stopped.

ところで、縦型スクリュープレス7では、凝集汚泥が濾筒71内で上方に移動することをアシストするため、濾筒71に凝集汚泥を加圧供給する必要がある。ここで、凝集反応槽5が地面に設置されている場合には、凝集反応槽5から濾筒71に凝集汚泥をポンプ圧送することが必要となる。そして、ポンプにより凝集汚泥が粉砕されて細粒分が生じる。汚泥の細粒分は、濾筒71を通過して濾液処理槽8に排出されるため、送り返して再度処理を行う必要があり、脱水ケーキの生成効率が劣ることになる。   By the way, in the vertical screw press 7, in order to assist the agglomerated sludge to move upward in the filter cylinder 71, it is necessary to pressurize and supply the agglomerated sludge to the filter cylinder 71. Here, when the flocculation reaction tank 5 is installed on the ground, it is necessary to pump the flocculated sludge from the flocculation reaction tank 5 to the filter tube 71. And agglomerated sludge is grind | pulverized with a pump, and a fine particle part arises. Since the fine sludge content passes through the filter cylinder 71 and is discharged to the filtrate treatment tank 8, it is necessary to send it back and perform the treatment again, resulting in poor dewatered cake production efficiency.

これに対し、本実施形態に係る汚泥の脱水処理装置Aでは、凝集反応槽5は架台53によって縦型スクリュープレス7の上部と同じ程度の高さに位置させているので、凝集反応槽5底部の排出口56と濾筒71の下部に設けた受入口76とを連通する供給パイプ6は上下方向に長いものとなっている。そして、供給パイプ6内に凝集汚泥が滞留する状態を維持することによって、当該凝集汚泥の自重により凝集汚泥を縦型スクリュープレス7の濾筒71内に加圧供給している。すなわち、凝集反応槽5の排出口56から供給パイプ6内に落下した凝集汚泥は、自重及びその後に落下してくる凝集汚泥により濾筒71に向けて送られる。そのため、ポンプ圧送する場合と異なり、汚泥の細粒分はほとんど生じず、脱水ケーキの生成効率が向上する。   In contrast, in the sludge dewatering apparatus A according to the present embodiment, the agglomeration reaction tank 5 is positioned at the same height as the upper part of the vertical screw press 7 by the gantry 53, so the bottom of the agglomeration reaction tank 5 The supply pipe 6 that communicates the discharge port 56 and the receiving port 76 provided at the lower part of the filter cylinder 71 is long in the vertical direction. By maintaining the state in which the aggregated sludge stays in the supply pipe 6, the aggregated sludge is pressurized and supplied into the filter cylinder 71 of the vertical screw press 7 by its own weight. That is, the coagulated sludge that has fallen into the supply pipe 6 from the discharge port 56 of the coagulation reaction tank 5 is sent toward the filter cylinder 71 by its own weight and the coagulated sludge that falls thereafter. Therefore, unlike the case of pumping, almost no sludge fine particles are produced, and the production efficiency of the dehydrated cake is improved.

さらに、汚泥の脱水処理装置Aでは、供給パイプ6内に滞留する凝集汚泥の高さが所定範囲となる状態を界面センサ63,64を用いて維持して、凝集汚泥を濾筒71内に適切な圧力で供給できるようにしている。界面センサ63,64の検知結果によるポンプP1の操作は、CPU等からなる制御手段を用いて自動化してもよいし、検知結果を報知する警告音を聞いたなどした作業員が行ってもよい。   Further, in the sludge dewatering apparatus A, the state where the height of the coagulated sludge staying in the supply pipe 6 is within a predetermined range is maintained using the interface sensors 63 and 64, and the coagulated sludge is appropriately stored in the filter cylinder 71. It can be supplied at a reasonable pressure. The operation of the pump P1 based on the detection results of the interface sensors 63 and 64 may be automated using a control means including a CPU or the like, or may be performed by a worker who has heard a warning sound for notifying the detection results. .

本発明の一実施形態に係る汚泥の脱水処理装置を示す説明図。BRIEF DESCRIPTION OF THE DRAWINGS Explanatory drawing which shows the sludge dehydration processing apparatus which concerns on one Embodiment of this invention.

符号の説明Explanation of symbols

1…汚泥貯留槽、2…ラインミキサー、3…アニオン系凝集剤供給部、4…カチオン系凝集剤供給部、5…凝集反応槽、6…供給パイプ、7…縦型スクリュープレス、8…濾液処理槽、9…雑排水処理槽、53…架台、61…主パイプ、62…副パイプ、63,64…界面センサ、71…濾筒、72…スクリュー、73…覆筒、76…受入口、A…汚泥の脱水処理装置 DESCRIPTION OF SYMBOLS 1 ... Sludge storage tank, 2 ... Line mixer, 3 ... Anionic flocculant supply part, 4 ... Cationic flocculant supply part, 5 ... Coagulation reaction tank, 6 ... Supply pipe, 7 ... Vertical screw press, 8 ... Filtrate Treatment tank, 9 ... miscellaneous wastewater treatment tank, 53 ... mount, 61 ... main pipe, 62 ... sub pipe, 63, 64 ... interface sensor, 71 ... filter tube, 72 ... screw, 73 ... cover tube, 76 ... receiving port, A ... Sludge dewatering equipment

Claims (2)

凝集反応槽にて汚泥と凝集剤とが攪拌混合されて凝集汚泥が生成され、該凝集汚泥が縦型スクリュープレスの濾筒内に当該濾筒の下部に設けた受入口から供給され、該濾筒内に配設されたスクリューの回転により凝集汚泥が当該濾筒内を上方に搬送されつつ圧搾脱水されるようにした汚泥の脱水処理装置において、
前記受入口より上方に前記凝集反応槽が配設され、該凝集反応槽から前記受入口に凝集汚泥を供給する供給パイプを備え、当該供給パイプ内に凝集汚泥が滞留する状態を維持して、凝集汚泥を前記濾筒内に加圧供給することを特徴とする汚泥の脱水処理装置。
The sludge and the flocculant are stirred and mixed in the flocculation reaction tank to produce agglomerated sludge, and the agglomerated sludge is supplied into the filter cylinder of the vertical screw press from the inlet provided at the lower part of the filter cylinder. In the sludge dewatering apparatus, the sludge is squeezed and dewatered while being transported upward in the filter cylinder by the rotation of the screw disposed in the cylinder.
The flocculation reaction tank is disposed above the receiving port, and includes a supply pipe that supplies the flocculated sludge from the flocculation reaction tank to the receiving port, maintaining a state in which the flocculated sludge stays in the supply pipe, An apparatus for dewatering sludge, wherein the coagulated sludge is pressurized and supplied into the filter cylinder.
前記供給パイプ内に滞留する凝集汚泥の高さが所定範囲となる状態を維持することを特徴とする請求項1記載の汚泥の脱水処理装置。   2. The sludge dewatering apparatus according to claim 1, wherein a state in which the height of the coagulated sludge staying in the supply pipe is within a predetermined range is maintained.
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Cited By (8)

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JP2010149093A (en) * 2008-12-26 2010-07-08 Sanki Eng Co Ltd Screw press dehydrator
JP2010284623A (en) * 2009-06-15 2010-12-24 Justec Co Ltd Flock supply equalization apparatus and solid-liquid separation system
JP2015000380A (en) * 2013-06-17 2015-01-05 水ing株式会社 Apparatus and method for coagulating sludge, and sludge treatment apparatus
JP5899340B1 (en) * 2015-01-30 2016-04-06 月島機械株式会社 Concentration method using a vertical filtration concentrator
JP2016140862A (en) * 2016-01-22 2016-08-08 月島機械株式会社 Vertical filtration concentrator, and concentration equipment and concentration method using the same
CN112010527A (en) * 2020-09-16 2020-12-01 山达玛 Basin water pollution administers and uses sludge dewatering device
CN113213725A (en) * 2021-06-16 2021-08-06 华电水务科技股份有限公司 Sludge solid-liquid separation equipment for sewage treatment and operation method thereof
CN114940575A (en) * 2022-05-27 2022-08-26 国投信开水环境投资有限公司 Device and method for conditioning sludge

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JP2006051458A (en) * 2004-08-13 2006-02-23 Tsukishima Kikai Co Ltd Sludge coagulation apparatus and method and chemical feed position controller
JP2007090264A (en) * 2005-09-29 2007-04-12 Kurita Water Ind Ltd Sludge concentration apparatus and method
JP2008036703A (en) * 2006-08-10 2008-02-21 Okumura Corp Vertical screw press

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JPH11254000A (en) * 1998-03-13 1999-09-21 Nagoya City Method and apparatus for concentrating dehydration
JP2003088896A (en) * 2001-09-18 2003-03-25 Kurita Water Ind Ltd Screw press type sludge dewatering apparatus
JP2003164899A (en) * 2001-09-18 2003-06-10 Kurita Water Ind Ltd Apparatus and method for concentrating sludge
JP2004121955A (en) * 2002-10-01 2004-04-22 Kurita Water Ind Ltd Sludge concentration apparatus and method for washing the same
JP2006051458A (en) * 2004-08-13 2006-02-23 Tsukishima Kikai Co Ltd Sludge coagulation apparatus and method and chemical feed position controller
JP2007090264A (en) * 2005-09-29 2007-04-12 Kurita Water Ind Ltd Sludge concentration apparatus and method
JP2008036703A (en) * 2006-08-10 2008-02-21 Okumura Corp Vertical screw press

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010149093A (en) * 2008-12-26 2010-07-08 Sanki Eng Co Ltd Screw press dehydrator
JP2010284623A (en) * 2009-06-15 2010-12-24 Justec Co Ltd Flock supply equalization apparatus and solid-liquid separation system
JP2015000380A (en) * 2013-06-17 2015-01-05 水ing株式会社 Apparatus and method for coagulating sludge, and sludge treatment apparatus
JP5899340B1 (en) * 2015-01-30 2016-04-06 月島機械株式会社 Concentration method using a vertical filtration concentrator
JP2016140790A (en) * 2015-01-30 2016-08-08 月島機械株式会社 Concentration method using vertical filtration concentrator
JP2016140862A (en) * 2016-01-22 2016-08-08 月島機械株式会社 Vertical filtration concentrator, and concentration equipment and concentration method using the same
CN112010527A (en) * 2020-09-16 2020-12-01 山达玛 Basin water pollution administers and uses sludge dewatering device
CN113213725A (en) * 2021-06-16 2021-08-06 华电水务科技股份有限公司 Sludge solid-liquid separation equipment for sewage treatment and operation method thereof
CN114940575A (en) * 2022-05-27 2022-08-26 国投信开水环境投资有限公司 Device and method for conditioning sludge

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