JP2015024371A - Extraction equipment - Google Patents

Extraction equipment Download PDF

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JP2015024371A
JP2015024371A JP2013155125A JP2013155125A JP2015024371A JP 2015024371 A JP2015024371 A JP 2015024371A JP 2013155125 A JP2013155125 A JP 2013155125A JP 2013155125 A JP2013155125 A JP 2013155125A JP 2015024371 A JP2015024371 A JP 2015024371A
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sludge
separator
fiber
tank
extraction device
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JP6112475B2 (en
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山下 学
Manabu Yamashita
学 山下
康隆 末次
Yasutaka Suetsugu
康隆 末次
敦 柳井
Atsushi Yanai
敦 柳井
亮介 玉内
Ryosuke Tamauchi
亮介 玉内
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Ishigaki Co Ltd
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Ishigaki Co Ltd
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Priority to JP2013155125A priority Critical patent/JP6112475B2/en
Application filed by Ishigaki Co Ltd filed Critical Ishigaki Co Ltd
Priority to CA2917488A priority patent/CA2917488C/en
Priority to DK14829186.7T priority patent/DK3026026T3/en
Priority to CA2970289A priority patent/CA2970289C/en
Priority to PCT/JP2014/066435 priority patent/WO2015012039A1/en
Priority to EP16157337.3A priority patent/EP3059015A1/en
Priority to EP14829186.7A priority patent/EP3026026B1/en
Priority to TW103121710A priority patent/TWI636019B/en
Publication of JP2015024371A publication Critical patent/JP2015024371A/en
Priority to US14/989,362 priority patent/US9975798B2/en
Priority to US14/989,065 priority patent/US10974982B2/en
Application granted granted Critical
Publication of JP6112475B2 publication Critical patent/JP6112475B2/en
Priority to US15/951,716 priority patent/US11401188B2/en
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  • Crushing And Grinding (AREA)
  • Disintegrating Or Milling (AREA)
  • Separation Of Solids By Using Liquids Or Pneumatic Power (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide extraction equipment continuously separating and recovering a specified stock from sludge generated in a sewage treatment process.SOLUTION: Provided is extraction equipment including: a grinding machine of sub-dividing sludge; a separation machine of separating a hardly-decomposable organic matter and an easily-decomposable organic matter from the ground prepared sludge; and a recovery device of extracting a hardly-decomposable organic matter, in which a prescribed hardly-decomposable organic matter is continuously separated and recovered, where only the one useful as a dewatering aid from sludge made to flow into a sewage disposal plant is selectively recovered, and it can be effectively utilized for the dewatering of hardly-dewatered sludge in the latter stage.

Description

本発明は、汚泥から特定の素材を分離回収する装置において、下水処理場に流入した汚泥から脱水助剤として適切な繊維状物のみを選択して分離回収する抽出装置に関する。 The present invention relates to an apparatus for separating and collecting a specific material from sludge and selecting and separating and collecting only a suitable fibrous material as a dehydrating aid from sludge flowing into a sewage treatment plant.

従来、下水処理場で発生する難脱水汚泥は脱水性が悪い。汚泥処理では、汚泥中の有機物(繊維分等)を細菌の働きによって分解した汚泥(難脱水汚泥)を脱水している。そのため、脱水前の汚泥は繊維分が減少している。汚泥中の繊維分は凝集の核として機能するため、繊維分が減少している汚泥は、適切な凝集を行うことができず、脱水性が悪くなる。 Conventionally, hardly dewatered sludge generated in a sewage treatment plant has poor dewaterability. In the sludge treatment, sludge (hardly dewatered sludge) obtained by decomposing organic matter (fiber content, etc.) in the sludge by the action of bacteria is dehydrated. Therefore, fiber content is reduced in the sludge before dehydration. Since the fiber content in the sludge functions as the core of aggregation, the sludge in which the fiber content is reduced cannot perform proper aggregation, resulting in poor dewaterability.

難脱水汚泥に繊維状物又はおがくずや籾殻等の植物素材を脱水助剤として混合して脱水する方法は古くから知られており、多くの処理場で実施されている。繊維状物を脱水助剤として用いると低含水率の脱水ケーキが得られ、且つ加圧脱水の場合には脱水ケーキの剥離性が改善する。しかし、大量の脱水助剤を用意し供給しなければならないためランニングコストが増大し、また、脱水助剤の備蓄・供給設備も設置しなければならないという問題があった。 A method of dehydrating by mixing a fiber material or a plant material such as sawdust or rice husk as a dehydrating aid with a hardly dehydrated sludge has been known for a long time and has been practiced in many treatment plants. When a fibrous material is used as a dehydration aid, a dehydrated cake having a low water content can be obtained, and in the case of pressure dehydration, the peelability of the dehydrated cake is improved. However, since a large amount of dehydration aid has to be prepared and supplied, running costs have increased, and there has been a problem that storage and supply facilities for the dehydration aid have to be installed.

そこで、汚泥処理プロセスの最初沈殿池から発生する生汚泥中の繊維分を分離回収し、余剰汚泥または消化汚泥等の難脱水汚泥に繊維分を添加する技術が引用文献1に開示されている。 Therefore, a technique for separating and collecting the fiber content in raw sludge generated from the first sedimentation basin of the sludge treatment process and adding the fiber content to hardly dewatered sludge such as excess sludge or digested sludge is disclosed in Citation 1.

また、引用文献2には多層材の異なる構成物を相対回転する対向ディスクで小片に破砕し、開孔ドラムでパルプ化できる素材を分離しつつ、後段のドラム内のスクリューフィーダによりドラムの一端から残小片を排出する回収装置が開示されている。 In the cited document 2, different components of the multi-layer material are crushed into small pieces with a counter-rotating opposing disk, and a material that can be pulped with an open drum is separated from one end of the drum by a screw feeder in a subsequent drum. A collection device for discharging the remaining small pieces is disclosed.

特開昭61−268400号公報JP-A 61-268400 特表2000−513267号公報Special Table 2000-513267

引用文献1の技術は、処理場内の汚泥から繊維分を回収するので、別途脱水助剤を準備する必要がなく、ランニングコスト、設備共に通常の処理と変わりはない。しかし、明細書内に開示されているような、スクリーンや振動ふるいのメッシュによる分離装置では、繊維分(難分解性有機物)に絡まり合った食品残渣由来の易分解性有機物等の脱水助剤として適切でないものを分離できず、繊維分と共に回収してしまう。従って、大部分が水分である易分解性有機物が絡まった繊維を脱水助剤として添加すると、脱水ケーキの含水率が増加し、処理費用が高騰する。易分解性有機物は腐敗するため、添加前の脱水助剤および添加後の脱水ケーキを長期間保存することができない。脱水助剤として有効な繊維分のみを回収する具体的な方法が開示されていないため、必要な繊維分のみを回収することは困難であった。 Since the technology of the cited document 1 collects the fiber from the sludge in the treatment plant, it is not necessary to prepare a dehydration aid separately, and the running cost and equipment are the same as those in normal treatment. However, as disclosed in the specification, in a separation apparatus using a screen or a vibrating screen mesh, as a dehydration aid for easily degradable organic substances derived from food residues entangled with fiber components (persistent organic substances) Inappropriate things cannot be separated and collected together with the fiber content. Therefore, when fibers entangled with easily decomposable organic substances, most of which are moisture, are added as a dehydration aid, the moisture content of the dehydrated cake increases and the processing cost increases. Since the readily decomposable organic matter rots, the dehydration aid before addition and the dehydrated cake after addition cannot be stored for a long period of time. Since a specific method for recovering only the fiber component effective as a dehydrating aid has not been disclosed, it has been difficult to recover only the necessary fiber component.

引用文献2の技術は、紙、プラスチック、アルミホイルから成る多層材内の多様な構成物を回収するもので、パルプ化(泥状化)できる紙繊維とパルプ化できないアルミニウム、プラスチック等の固形物とを分離回収する装置である。前段での回転ディスクでは多層構造を小片に破砕する作用だけでなく、小片を懸濁液とともに分離機へ搬送するポンプ搬送する作用を奏している。本発明の処理対象物は、汚水中の繊維分に絡まり合った極めて小さい食品残渣由来の有機物をすり潰しながら細分化するため、ディスク間のギャップを極狭に設定する必要があるが、狭く設定すると分離機へポンプ搬送できない。 The technique of Cited Document 2 collects various components in a multilayer material composed of paper, plastic, and aluminum foil. Paper fibers that can be pulped (muddy) and solids such as aluminum and plastic that cannot be pulped. Is a device for separating and recovering. The rotating disk in the previous stage has not only the action of crushing the multilayer structure into small pieces, but also the action of pumping the small pieces together with the suspension to the separator. The object to be treated of the present invention is to subdivide while crushing organic substances derived from extremely small food residues entangled with fibers in sewage, so it is necessary to set the gap between the disks extremely narrow, The pump cannot be transferred to the separator.

後段の多孔ドラムでは懸濁液内でほぐれて分散した紙繊維を多孔よりドラム外に分離し、ドラム内の残小片(アルミニウム、プラスチック等)を他端まで搬送して排出している。懸濁液にて浸漬させた際に、泥状化しないある程度の大きさを有した小片(アルミニウム、プラスチック等)が存在するため成立する。本技術では、下水処理場の汚泥に含まれる繊維分と、それに絡まり合った食品残渣由来の微細な易分解性有機物について、繊維分と易分解性有機物を分離することは困難である。また、繊維分を脱水助剤として使用する際には、懸濁液から繊維分のみを抽出する工程が別途必要となる。 In the latter porous drum, the paper fibers loosened and dispersed in the suspension are separated from the drum outside the drum, and the remaining small pieces (aluminum, plastic, etc.) in the drum are conveyed to the other end and discharged. This is established because there are small pieces (aluminum, plastic, etc.) having a certain size that does not become mud when immersed in the suspension. In this technique, it is difficult to separate the fiber and the easily decomposable organic matter from the fiber contained in the sludge of the sewage treatment plant and the fine easily decomposable organic matter derived from the food residue entangled with the fiber. Moreover, when using a fiber part as a dehydration auxiliary agent, the process of extracting only a fiber part from suspension is needed separately.

本発明は、下水処理場に流入する汚泥から難脱水汚泥の脱水時に脱水助剤として有用な所定性状の繊維分のみを選択的に分離回収する抽出装置に関する。 The present invention relates to an extraction apparatus that selectively separates and recovers only a fiber having a predetermined property useful as a dehydration aid when dewatering sludge from sludge flowing into a sewage treatment plant.

本発明の抽出装置は、下水処理プロセスで発生する汚泥から特定の素材を抽出する装置において、汚泥を細分化するすり潰し機と、すり潰した調製汚泥から難分解性有機物と易分解性有機物とを分離する分離機と、難分解性有機物を抽出する回収装置を備え、連続的に所定の難分解性有機物を分離回収するもので、下水処理場に流入した汚泥から脱水助剤として有用なもののみを選択的に回収し、後段の難脱水汚泥の脱水に有効活用できる。 The extraction apparatus of the present invention is an apparatus for extracting a specific material from sludge generated in a sewage treatment process, and a pulverizer that subdivides sludge and a hardly decomposable organic substance and an easily decomposable organic substance separated from the ground prepared sludge. And a recovery device that extracts persistent organic substances, and separates and recovers predetermined persistent organic substances continuously. Only those that are useful as dehydration aids from sludge flowing into the sewage treatment plant It can be selectively collected and used effectively for the dewatering of difficult-to-dehydrate sludge in the later stage.

分離機の下方に易分解性有機物を収集する分離槽を設け、易分解性有機物を下水処理場の生物処理槽に返送する返送管を分離槽に連結したので、処理場内の生物処理工程での反応期間を短縮でき、処理場全体の処理効率の向上に寄与する。 A separation tank that collects readily degradable organic substances is provided below the separator, and a return pipe that returns the easily degradable organic substances to the biological treatment tank of the sewage treatment plant is connected to the separation tank. The reaction period can be shortened and it contributes to the improvement of the processing efficiency of the whole treatment plant.

すり潰し機を、回転ディスクと固定ディスクを対向させて構成するとともに、回転ディスクの中心部に開口した供給口に供給管を連結し、対向ディスクの外周端に所定の隙間を設けると、連続的に汚泥を細分化し、易分解性有機物からも脱水助剤として有用な素材を抽出できる。 When the grinding machine is configured with a rotating disk and a fixed disk facing each other, a supply pipe is connected to a supply port opened at the center of the rotating disk, and a predetermined gap is provided at the outer peripheral end of the facing disk, Sludge can be subdivided and materials useful as dehydration aids can be extracted from readily decomposable organic substances.

また、すり潰し機を、一方が閉塞された筒状のケーシングに円筒スクリーンを内挿し、円筒スクリーンの内壁に摺接する摺接部材を回転自在に内設させて構成するとともに、円筒スクリーンの開口部中央に供給管と、ケーシングに移送管を設けてもよい。 Further, the crusher is configured by inserting a cylindrical screen into a cylindrical casing closed on one side, and rotatably installing a sliding contact member that is in sliding contact with the inner wall of the cylindrical screen, and at the center of the opening of the cylindrical screen. In addition, a supply pipe and a transfer pipe may be provided in the casing.

分離機を、回転自在に配設した円筒型のスクリーンで構成するとともに、回収装置を、スクリーン内に内設した螺旋状に掛け回したスクリュー羽根で構成すると、連続的に難分解性有機物を分離回収できる。分離機の抽出部近傍を円錐状に漸減すると、繊維間内部に付着しているわずかな夾雑物又は回収範囲以下の小さな繊維分について、水と共に分離槽へ重力分離する作用を高めることができる。 When the separator is configured with a cylindrical screen that is rotatably arranged, and the recovery device is configured with screw blades hung around in the screen, it separates persistent organic substances continuously. Can be recovered. When the vicinity of the extraction part of the separator is gradually reduced in a conical shape, the effect of gravity separation into the separation tank together with water can be enhanced with respect to slight impurities adhering to the inside of the fibers or small fibers below the recovery range.

また、分離機を、複数のロールに走行自在に巻き掛け、多数の細孔を有した無端ベルト構成し、回収装置を、ろ過面後方に配設したスクレーパで構成してもよい。 Further, the separator may be wound around a plurality of rolls so as to run freely, and may be configured as an endless belt having a large number of pores, and the recovery device may be configured by a scraper disposed behind the filtration surface.

分離機の供給部を含むろ過面を、分離槽に浸漬水を貯水して浸漬させると、分離工程で絡み付いている各素材をほぐしながら分散させるので分離効果が向上する。分離機のろ過面を高圧水で噴射する噴射装置を設けて高圧水を噴射しながら分離を行ってもよい。 When the filtration surface including the supply part of the separator is immersed in the separation tank by storing immersion water, each material entangled in the separation step is dispersed while being dispersed, so that the separation effect is improved. You may isolate | separate, providing the injection apparatus which injects the filtration surface of a separator with high pressure water, and injecting high pressure water.

分離機に複数の転動体を混入し、転動体を回収する転動体槽と、転動体槽から循環管を経て分離機の供給部に返送するための返送手段を備えると、分離工程での素材同士の絡み付きを防止するとともに、調製汚泥をほぐす作用を奏するので分離効率が向上する。 A material in the separation process is provided with a rolling element tank that mixes a plurality of rolling elements in the separator and collects the rolling elements, and a return means for returning from the rolling element tank to the supply unit of the separator through a circulation pipe. While preventing the entanglement between each other and the effect of loosening the prepared sludge, the separation efficiency is improved.

難脱水性有機物は繊維状物であり、回収する所定性状の繊維分を、繊維長さ0.1mm〜5mm、繊維径1μm〜50μmとすると、難脱水汚泥と混合させることで強固な凝集フロックを形成させることができ、後段での脱水機で低含水率の脱水ケーキを生成できる。 The hard-to-dehydrate organic material is a fibrous material, and when the fiber content having a predetermined property to be collected is made to have a fiber length of 0.1 mm to 5 mm and a fiber diameter of 1 μm to 50 μm, a strong coagulated floc can be obtained by mixing with the hardly dewatered sludge. It can be formed, and a dehydrated cake with a low water content can be produced by a dehydrator at a later stage.

本発明の抽出装置は、汚泥の調製・分離・回収工程までを連続的に処理でき、各機器を一体化すると非常にコンパクトとなる。汚泥中の難脱水性有機物を脱水助剤として処理系内の汚泥処理に有効活用し、易分解性有機物を生物処理槽に返送するので、低含水率の脱水ケーキを生成できるとともに、処理場内の生物処理工程での反応期間を短縮できる。処理場全体の処理効率の向上に寄与できるものである。別途脱水助剤を購入するランニングコストが不要で、脱水助剤の備蓄・供給設備も必要ない。また、脱水助剤として抽出する難脱水性有機物は、易分解性有機物を含んでいないので長期保存が可能である。 The extraction apparatus of the present invention can continuously process the sludge preparation / separation / recovery process, and becomes very compact when the devices are integrated. The dewatering organic matter in the sludge is effectively used for the sludge treatment in the treatment system as a dehydrating aid, and the easily degradable organic matter is returned to the biological treatment tank. The reaction period in the biological treatment process can be shortened. It can contribute to the improvement of the processing efficiency of the entire treatment plant. There is no need to purchase separate dehydration aids, and there is no need to store and supply dehydration aids. In addition, the hardly dehydrated organic substance extracted as a dehydrating aid does not contain an easily decomposable organic substance and can be stored for a long period of time.

本発明に係る汚泥処理方法のフロー図である。It is a flowchart of the sludge processing method which concerns on this invention. 同じく、トイレットペーパーと抽出装置で回収した繊維を比較するグラフである。Similarly, it is the graph which compares the fiber collect | recovered with the toilet paper and the extraction apparatus. 同じく、抽出装置で得られた繊維を示す参考顕微鏡写真である。Similarly, it is the reference micrograph which shows the fiber obtained with the extraction apparatus. 同じく、抽出装置のチャート図である。Similarly, it is a chart diagram of the extraction device. 本発明の実施例に係る汚泥処理方法のフロー図である。It is a flowchart of the sludge processing method which concerns on the Example of this invention. 同じく、抽出装置の詳細図である。Similarly, it is a detailed view of the extraction device. 同じく、他の実施例の抽出装置の説明図である。Similarly, it is explanatory drawing of the extraction apparatus of another Example. 同じく、他の実施例1の抽出装置の詳細図である。Similarly, it is a detailed view of the extraction device of another embodiment 1. 同じく、他の実施例2の抽出装置の詳細図である。Similarly, it is detail drawing of the extraction apparatus of other Example 2. FIG. 同じく、他の実施例3の抽出装置の詳細図である。Similarly, it is detail drawing of the extraction apparatus of other Example 3. FIG. 同じく、他の実施例1の汚泥処理方法で、OD法を採用した際のフロー図である。Similarly, it is a flowchart at the time of employ | adopting OD method by the sludge treatment method of the other Example 1. FIG. 同じく、他の実施例2の汚泥処理方法で、MBRを採用した際のフロー図である。Similarly, it is a flowchart at the time of employ | adopting MBR with the sludge processing method of the other Example 2. FIG. 同じく、他の実施例3の汚泥処理方法で、混合生汚泥の処理に採用した際のフロー図である。Similarly, it is a flowchart at the time of employ | adopting for the process of mixed raw sludge by the sludge processing method of the other Example 3. FIG.

本発明の抽出装置2は、下水処理場等で使用することを前提としており、処理場の前段で汚泥(汚水含む)から所定の繊維状物を抽出し、処理場の後段で発生する難脱水汚泥を脱水する際に、繊維状物を脱水助剤として添加し、難脱水汚泥の脱水性を向上させることを目的としている。
難脱水汚泥とは、生物処理等によって凝集の核となる繊維分が大幅に減少し、脱水性の悪くなった汚泥のことである。例えば消化槽で生成された消化汚泥や、OD法の反応槽で生成されたOD汚泥等が難脱水汚泥にあたる。
The extraction device 2 of the present invention is premised on use in a sewage treatment plant or the like, extracts a predetermined fibrous material from sludge (including sewage) at the front stage of the treatment plant, and hardly dehydrates generated after the treatment plant. When dewatering sludge, it aims at adding the fibrous material as a dehydrating aid and improving the dehydrating property of the hardly dewatered sludge.
The hardly dewatered sludge is sludge whose fiber content that is the core of aggregation has been greatly reduced by biological treatment or the like, resulting in poor dewaterability. For example, digested sludge produced in a digestion tank, OD sludge produced in a reaction tank of the OD method, etc. are hardly dehydrated sludge.

図1は本発明に係る汚泥処理方法のフロー図である。汚泥を生物処理する生物処理槽1と、下水道から流れ込んだ汚水中の繊維分を選択的に回収する抽出装置2と、生物処理槽1で処理された汚泥と抽出装置2で回収した繊維分を混合する混合槽3と、混合槽3で繊維分を混合した汚泥に凝集剤を添加する凝集混和槽4と、凝集混和槽4で生成した凝集汚泥を固液分離する脱水機5からなる。
なお、破線で示すように、抽出装置2で分離した繊維分を凝集混和槽4に送り、高分子凝集剤と同時に添加してもよい。脱水機5はスクリュープレス、ベルトプレス、遠心脱水機等の公知の脱水機を使用できる。
FIG. 1 is a flowchart of the sludge treatment method according to the present invention. The biological treatment tank 1 for biologically treating sludge, the extraction device 2 for selectively collecting the fiber content in the sewage flowing from the sewer, the sludge treated in the biological treatment tank 1 and the fiber content recovered by the extraction device 2 It comprises a mixing tank 3 for mixing, an agglomeration mixing tank 4 for adding a flocculant to the sludge mixed with fibers in the mixing tank 3, and a dehydrator 5 for solid-liquid separation of the agglomerated sludge generated in the agglomeration mixing tank 4.
In addition, as shown with a broken line, the fiber part isolate | separated with the extraction apparatus 2 may be sent to the coagulation mixing tank 4, and you may add simultaneously with a polymer flocculant. As the dehydrator 5, a known dehydrator such as a screw press, a belt press, or a centrifugal dehydrator can be used.

本発明では、汚水中の繊維分を脱水助剤として利用するため、下水処理場に流入した汚水中の繊維分を抽出装置2で回収している。回収した繊維分は、凝集前の難脱水汚泥等に添加され、凝集の核として機能する。汚泥に対して適切な性状の脱水助剤を添加すれば、強固な凝集フロックを形成し、脱水性が向上する。よって脱水助剤の性状は、事前に被処理汚泥に適したものを選定している。
本発明では、予め定められた性状の繊維分のみを回収し、脱水助剤とすることで、脱水性を向上させている。
In the present invention, since the fiber content in the sewage is used as a dehydration aid, the fiber content in the sewage that has flowed into the sewage treatment plant is recovered by the extraction device 2. The recovered fiber is added to the hardly dehydrated sludge before aggregation and functions as a nucleus of aggregation. If a dehydrating aid having an appropriate property is added to the sludge, a strong coagulated floc is formed and the dehydrating property is improved. Therefore, the nature of the dehydrating aid is selected in advance to be suitable for the treated sludge.
In the present invention, only the fiber having a predetermined property is collected and used as a dehydrating aid, thereby improving the dehydrating property.

ここで、本発明者らが試行錯誤と実験とを繰り返してきた結果、脱水助剤として植物繊維で構成されたトイレットペーパーを用いることで、脱水ケーキの含水率を大幅に低減できるという成果が得られた。そこでトイレットペーパーの繊維の性状に着目し、トイレットペーパーと同等の性状の繊維分を脱水助剤として利用することで、含水率の低減を図ることに成功した。 Here, as a result of repeating trial and error and experiments by the present inventors, the use of toilet paper composed of plant fibers as a dehydrating aid has resulted in a significant reduction in the moisture content of the dehydrated cake. It was. Therefore, focusing on the properties of the toilet paper fibers, we succeeded in reducing the moisture content by using the same fiber content as the toilet paper as a dehydrating aid.

図2は、トイレットペーパーと抽出装置2で回収した繊維を比較するグラフである。グラフは、横軸を繊維の長さ、縦軸を繊維の個体数とした時の、トイレットペーパーから得られた繊維分と、本発明の抽出装置2に送られた汚泥を100メッシュのふるいで分離して得られた繊維分と、同じく抽出装置2に送られた汚泥をΦ650μmの孔径を有する回転円筒型のスクリーンで分離して得られた繊維分とを比較している。トイレットペーパーは浸漬撹拌後に顕微鏡にて調査を行った。 FIG. 2 is a graph comparing the toilet paper and the fibers collected by the extraction device 2. In the graph, the horizontal axis represents the length of the fiber, and the vertical axis represents the number of fibers. The sludge sent from the toilet paper and the sludge sent to the extraction device 2 of the present invention was sieved with 100 mesh. A comparison is made between the fiber obtained by separation and the fiber obtained by separating the sludge sent to the extraction device 2 with a rotating cylindrical screen having a pore diameter of Φ650 μm. The toilet paper was examined with a microscope after immersion stirring.

比較結果より、下水汚泥中の繊維分布(繊維長さ、個体数)がトイレットペーパーと酷似していることが判明した。また、回収する繊維の性状として、繊維長さ0.1mm〜5mmとしておくことが、汚泥への添加、混合また脱水時の作業性の点からも好ましいことが分かる。 From the comparison results, it was found that the fiber distribution (fiber length, number of individuals) in the sewage sludge is very similar to that of toilet paper. Moreover, it turns out that it is preferable from the point of workability | operativity at the time of the addition to sludge, mixing, and dehydration to set the fiber length as 0.1 mm-5 mm as a property of the fiber collect | recovered.

図3は抽出装置2で回収した繊維の参考顕微鏡写真であって、トイレットペーパーと同様で繊維径にばらつきは無く、1μm〜50μmの範囲に収まっていることが判明した。 FIG. 3 is a reference micrograph of the fiber collected by the extraction device 2, and it was found that the fiber diameter was not different and was in the range of 1 μm to 50 μm, similar to toilet paper.

これらのことから、抽出装置2で回収した繊維分の性状分布は、トイレットペーパーの繊維性状と非常に酷似しており、本発明の抽出装置2で回収した繊維分はトイレットペーパーの繊維分と同等の性状を有するもので、脱水助剤として好ましいことが分かる。 From these, the property distribution of the fiber recovered by the extraction device 2 is very similar to the fiber property of the toilet paper, and the fiber content recovered by the extraction device 2 of the present invention is equivalent to the fiber content of the toilet paper. It can be seen that it is preferable as a dehydrating aid.

なお、トイレットペーパーは水に浸漬させても溶解することが無く、シート状に構成している繊維がほどけて分散するのみである。したがって、下水汚泥中には多量のトイレットペーパー由来の繊維が存在すると考えられる。 Note that toilet paper does not dissolve even when immersed in water, and only the fibers constituting the sheet are unwound and dispersed. Therefore, it is considered that a large amount of fibers derived from toilet paper are present in the sewage sludge.

図4は抽出装置のチャート図であって、本発明で用いられる抽出装置2は、連続的に繊維分と粒状固形物をほぐしつつ粒状固形物をすり潰して細分化する調製工程6と、繊維分以外の固形物を分離する分離工程7と、脱水助剤として使用する繊維分を回収する回収工程8を備える。 FIG. 4 is a chart of the extraction device. The extraction device 2 used in the present invention comprises a preparation step 6 for continuously crushing and subdividing the granular solids while loosening the fibers and the granular solids, and the fiber content. The separation process 7 which isolate | separates solids other than these, and the collection | recovery process 8 which collect | recovers the fiber components used as a dehydration adjuvant are provided.

<調製工程>
下水処理場に流入した汚水中の固形物には、脱水助剤として回収するトイレットペーパーの主成分である難分解性有機物の植物性繊維分以外にも、食品残渣由来の易分解性有機物を主成分とした夾雑物、SSが混在しており、それらが繊維分と絡み合っている場合がある。従って調製工程6において、繊維分の絡まりをほどくと共に、回収範囲以上の繊維分の長さを整え、夾雑物又はSSを細かく破砕するなどして、汚泥を調製する必要がある。調製工程6時に希釈水を注水して、汚泥濃度を低くした状態で細分化してもよい。
<Preparation process>
The solid matter in the sewage that has flowed into the sewage treatment plant is mainly composed of easily degradable organic matter derived from food residues, in addition to the vegetable fiber component of the hardly decomposable organic matter that is the main component of toilet paper collected as a dehydrating aid. Contaminants and SS as components are mixed, and they may be intertwined with the fiber. Therefore, in the preparation step 6, it is necessary to prepare sludge by untangling the fiber, adjusting the length of the fiber beyond the recovery range, and finely crushing the foreign matter or SS. You may subdivide in the state which poured the dilution water at the time of the preparation process 6, and made the sludge density | concentration low.

調製工程6では、回収対象の繊維分を含む夾雑物及びSSをすり潰し機9で細分化してもよい。繊維分の多くは、繊維分同士又は夾雑物と絡み合っているため、そのままでは分離機10で回収範囲下限以下の小さな夾雑物を除去することが困難である。そこで、繊維分をすり潰し機9で細分化し、繊維分と夾雑物を容易に分離できるようにする。主な夾雑物が食品残渣である場合、すり潰すことにより食品残渣内部の繊維分を抽出できると共に、その他の有機物を細分化できる。 In the preparation step 6, the impurities and SS containing the fiber to be collected may be subdivided by the grinding machine 9. Since most of the fiber components are entangled with each other or with impurities, it is difficult to remove small impurities below the lower limit of the recovery range with the separator 10 as they are. Therefore, the fiber component is subdivided by the grinding machine 9 so that the fiber component and the impurities can be easily separated. When the main impurities are food residues, the fiber content inside the food residues can be extracted by grinding and other organic matters can be subdivided.

すり潰し機9としては、円板形、ローラー型、擂り粉木等、繊維分を連続的にすり潰して細分化できるものであればどのようなものでも構わないが、難分解性有機物(繊維分)および易分解性有機物粉ともに粉状に粉砕すると脱水助剤として有効な繊維分の分離が困難となるため、易分解性有機物である固形分のみをすり潰せるような装置が望ましい。 The crusher 9 may be any disk type, roller type, pulverized wood, etc., as long as it can continuously crush and subdivide the fiber, but it is a hardly decomposable organic substance (fiber). When both the easily decomposable organic powders are pulverized into powder, it is difficult to separate the fiber effective as a dehydrating aid. Therefore, an apparatus that can grind only the solids that are easily decomposable organic substances is desirable.

<分離工程>
分離工程7では、分離機10を用いて前工程で調製した繊維分をふるいに掛け、所定の繊維分と回収範囲下限以下の小さな夾雑物等とを分離する。
前工程で繊維分は調製され、繊維分と絡み合っていた夾雑物等はほどけている。よって、回収範囲内の繊維分が残るようにふるいに掛ければ、所定の性状の繊維分のみが回収できる。細分化した繊維分をふるいに掛けると、細分化する前には繊維分と絡み合っていた夾雑物等が取り除かれ、同時に回収範囲以下の小さな繊維分も取り除かれる。
<Separation process>
In the separation step 7, the fiber portion prepared in the previous step is sieved using the separator 10 to separate the predetermined fiber portion and small impurities below the lower limit of the recovery range.
The fiber is prepared in the previous step, and the foreign matter entangled with the fiber is unwound. Therefore, if it is sieved so that the fibers within the collection range remain, only the fibers with a predetermined property can be collected. When the subdivided fibers are sifted, the foreign matter entangled with the fibers before the subdivision is removed, and at the same time small fibers below the recovery range are also removed.

分離を行う際に、洗浄水を噴射して水圧により夾雑物を分離する分離補助や、浸漬させることにより繊維分と夾雑物をほどく分離補助、あるいは複数の転動体により分離時の繊維と夾雑物の絡まりを防止する分離補助を用いてもよい。 Separation aid that separates contaminants by spraying washing water when water is separated, separation aid that unwinds fibers and contaminants by dipping, or fibers and contaminants during separation by multiple rolling elements Separation aids that prevent entanglement may be used.

洗浄水を噴射することにより、繊維分に付着した、わずかな夾雑物又は回収範囲以下の小さな繊維分をさらに取り除くことができる。また、分離時に細分化された汚泥を浸漬させることにより、繊維間内部に付着した、わずかな夾雑物又は回収範囲以下の小さな繊維分を引き離し、確実に分離することができる。さらに、複数の転動体を細分化された汚泥に混入することにより、分離工程での繊維同士の絡み付きを防止するとともに、調製汚泥をほぐす作用を奏するので分離効率が向上する。 By spraying the washing water, it is possible to further remove a small amount of foreign matter adhering to the fiber content or a small fiber content below the recovery range. Moreover, by immersing the sludge that has been subdivided at the time of separation, it is possible to separate and reliably separate a small amount of foreign matter adhered to the inside of the fibers or a small fiber portion below the recovery range. Furthermore, by mixing a plurality of rolling elements into the subdivided sludge, the fibers are prevented from being entangled in the separation step, and the effect of loosening the prepared sludge is exhibited, so that the separation efficiency is improved.

なお、分離機10から排出される夾雑物を含む排水を清澄ろ過等で固液分離し、清澄水を洗浄水として再利用できる。 In addition, the waste water containing the impurities discharged | emitted from the separator 10 can be solid-liquid separated by clarification filtration etc., and clarified water can be reused as washing water.

分離機10としては、円筒型、ベルト型、振動ふるい型等、所定の性状の繊維分と細分化された夾雑物とを分離するものであればどのようなものでも構わない。 The separator 10 may be any type such as a cylindrical type, a belt type, a vibration sieve type, etc., as long as it separates the fiber component having a predetermined property and the finely divided impurities.

<回収工程>
回収工程8では、分離工程7により分離した所定の性状の繊維分を連続的に回収する。
回収装置11は分離機10の型式に適合したものを適宜選定する。例えば、分離機10が円筒型である場合、回収装置11は分離機に内挿したスクリューコンベア方式を採用する。また、分離機10がベルト型である場合、回収装置11はろ過面に押圧したスクレーパを採用する。分離機10から連続的に排出できるものであればどのようなものでも構わない。
<Recovery process>
In the recovery step 8, the fiber having a predetermined property separated in the separation step 7 is continuously recovered.
The recovery device 11 is appropriately selected to be suitable for the type of the separator 10. For example, when the separator 10 is cylindrical, the recovery device 11 employs a screw conveyor system inserted in the separator. Moreover, when the separator 10 is a belt type, the collection | recovery apparatus 11 employ | adopts the scraper pressed on the filtration surface. Any device that can continuously discharge from the separator 10 may be used.

回収した所定範囲内の繊維分は脱水助剤として混合槽3に送られ、凝集の核として難脱水汚泥と混合する。
なお、分離機7で分離された夾雑物等の固形物の大部分は易分解性有機物で構成されており、生物処理槽1に送れば長時間の生物処理を必要とせずに汚泥減容化に貢献できる。
The collected fiber within a predetermined range is sent to the mixing tank 3 as a dehydrating aid and mixed with the hardly dewatered sludge as the core of aggregation.
Note that most of the solids such as foreign matters separated by the separator 7 are composed of easily decomposable organic substances, and if sent to the biological treatment tank 1, sludge volume reduction can be achieved without requiring a long biological treatment. Can contribute.

<前処理工程>
また、下水処理場に流入した汚泥中に回収範囲上限以上の大きな夾雑物が混入している場合には、調製工程6の前段に以下の前処理工程12を追加してもよい。
前処理工程12では、下水処理場に流入した汚水中の大きな夾雑物を前処理装置13によって除去する。大きな夾雑物は脱水助剤として不適切であり、次工程の調製工程6において調製の妨げとなるため、この工程では回収範囲上限以上の大きな夾雑物と、回収対象の繊維分を含むSS及び小さな夾雑物とを分離し、大きな夾雑物を除去することを目的とする。従って前処理装置13としては、回収範囲上限以上の夾雑物を除去できるものであればどのようなものでもよく、バースクリーン、ふるい又はドラムスクリーンといったものでもよい。
<Pretreatment process>
Further, in the case where large contaminants exceeding the upper limit of the recovery range are mixed in the sludge flowing into the sewage treatment plant, the following pretreatment step 12 may be added before the preparation step 6.
In the pretreatment process 12, large contaminants in the sewage flowing into the sewage treatment plant are removed by the pretreatment device 13. Large contaminants are inappropriate as dehydration aids and hinder preparation in the preparation step 6 of the next step. In this step, large contaminants exceeding the upper limit of the recovery range, SS containing the fiber to be recovered, and small The purpose is to separate contaminants and remove large contaminants. Accordingly, the pretreatment device 13 may be any device as long as it can remove impurities exceeding the upper limit of the collection range, and may be a bar screen, a sieve, or a drum screen.

上述してきた調製工程6、分離工程7、回収工程8はユニット化して一つの装置で行うことができ、その装置の中に前処理工程12を含めてもよい。 The preparation process 6, the separation process 7, and the recovery process 8 described above can be unitized and performed in one apparatus, and the pretreatment process 12 may be included in the apparatus.

図5は下水処理場で消化汚泥を処理する際の汚泥処理方法のフロー図である。下水処理場に流れ込んだ汚水は最初沈殿池14へ流入する。最初沈殿池14では汚水が緩やかに流れ、繊維分を含む有機物等が沈殿する。沈殿物の主成分としては、繊維分が主にトイレットペーパーであり、固形分が食品残渣である。トイレットペーパーの繊維分の繊維長さは0.1〜30mmで、繊維径は1〜50μmである。沈殿物は、生汚泥として下方より引き抜き回収される。 FIG. 5 is a flow chart of a sludge treatment method when digested sludge is treated at a sewage treatment plant. The sewage that has flowed into the sewage treatment plant first flows into the settling basin 14. In the first settling basin 14, sewage flows gently, and organic matter containing fiber is precipitated. As the main component of the precipitate, the fiber content is mainly toilet paper, and the solid content is food residue. The fiber length of toilet paper is 0.1 to 30 mm, and the fiber diameter is 1 to 50 μm. The sediment is extracted and collected from below as raw sludge.

最初沈殿池14から引き抜いた生汚泥は、消化槽15で生物処理して減容化を行っている。最初沈殿池14から引き抜いた生汚泥の一部は抽出装置2に搬送し、所定の性状の繊維分を選択的に回収する。抽出装置2で分離した繊維分以外の夾雑物は消化槽15に返送し、消化槽での消化効率に寄与している。 The raw sludge withdrawn from the sedimentation tank 14 is biologically treated in the digestion tank 15 to reduce the volume. A part of the raw sludge withdrawn from the settling basin 14 is conveyed to the extraction device 2 and selectively collects fibers having a predetermined property. Contaminants other than the fibers separated by the extraction device 2 are returned to the digestion tank 15 and contribute to the digestion efficiency in the digestion tank.

消化槽15減容化された難脱水汚泥である消化汚泥は、混合槽3と凝集混和槽4でそれぞれ所定性状の繊維分(脱水助剤)と凝集剤とを添加されて強固な凝集フロックを形成した後、脱水機5で固液分離を行い、低含水率の脱水ケーキとなる。 Digested sludge, which is a difficult-to-dehydrate sludge whose volume has been reduced by digestion tank 15, is added with fiber components (dehydration aid) and a flocculant having predetermined properties in mixing tank 3 and agglomeration mixing tank 4, respectively. After the formation, solid-liquid separation is performed by the dehydrator 5 to obtain a dehydrated cake having a low water content.

図6は実施例における抽出装置の詳細図である。抽出装置2aは主に調製工程6と分離工程7および回収工程8とからなる。本実施例では、生汚泥を細分化するすり潰し機9aを対向ディスク16,17で構成し、回転円筒型のスクリーン18で構成した分離機10aの端部に内設している。すり潰し機9aから排出された調製汚泥は、スクリーン8内面に立設したスクリュー羽根19により他端に搬送されつつ、細分化された夾雑物等がスクリーン18の開孔より分離排出される。所定の性状の繊維分はスクリュー羽根19によりスクリーン18他端まで搬送されて回収される。 FIG. 6 is a detailed view of the extraction device in the embodiment. The extraction device 2a mainly includes a preparation step 6, a separation step 7, and a recovery step 8. In the present embodiment, a grinding machine 9a for subdividing raw sludge is constituted by opposing disks 16 and 17, and is provided at the end of a separator 10a constituted by a rotating cylindrical screen 18. The prepared sludge discharged from the pulverizer 9 a is conveyed to the other end by a screw blade 19 erected on the inner surface of the screen 8, and finely divided impurities and the like are separated and discharged from the opening of the screen 18. The fiber component having a predetermined property is conveyed to the other end of the screen 18 by the screw blade 19 and collected.

最初沈殿池14より送られてきた生汚泥は繊維分と夾雑物が絡み合っているため、調製工程6で絡み合った繊維分を繊維長さ0.1mm〜0.5mm、繊維径1μm〜50μmの繊維分に調製する。生汚泥を希釈水で希釈し、微細化は回転ディスク16と固定ディスク17を対向させたすり潰し機9aで行われる。対向させたディスク16,17内部に供給した生汚泥は、ディスク表面の粗く微小な凹凸によって微細化されながら外部に排出され、細分化された生汚泥は分離工程7に送られる。 Since the raw sludge sent from the first sedimentation basin 14 is entangled with fibers and impurities, the fibers entangled in the preparation step 6 are fibers having a fiber length of 0.1 mm to 0.5 mm and a fiber diameter of 1 μm to 50 μm. Prepare in minutes. The raw sludge is diluted with diluting water, and refinement is performed by a pulverizer 9a in which the rotating disk 16 and the fixed disk 17 are opposed to each other. The raw sludge supplied to the inside of the opposed disks 16 and 17 is discharged outside while being refined by rough minute irregularities on the disk surface, and the subdivided raw sludge is sent to the separation step 7.

具体的な構成について詳述すると、すり潰し機9aは外周部から中心に向かって内部に円錐状の凹部20を形成した円盤状のディスク16,17を回転可能に対向している。一方のディスクは固定ディスク17であり、外周部を他の部材に固定している。本実施例では放射状のリブ21で分離機と固定している。他方のディスクは回転ディスク16であり、中心部に有した供給口22に連結した供給管23から内部へ生汚泥が供給される。駆動機24からの動力はベルト等の動力伝達手段25を介して供給管23に伝達し、供給管23および回転ディスク16を回転させる。必要に応じて適所に軸受等で供給管23および回転ディスク16の支持を行う。 A specific configuration will be described in detail. In the grinding machine 9a, disk-shaped disks 16 and 17 each having a conical recess 20 formed therein are rotatably opposed from the outer periphery toward the center. One of the disks is a fixed disk 17, and the outer peripheral portion is fixed to another member. In this embodiment, radial ribs 21 are fixed to the separator. The other disk is a rotating disk 16 from which raw sludge is supplied from a supply pipe 23 connected to a supply port 22 provided at the center. The power from the drive unit 24 is transmitted to the supply pipe 23 via a power transmission means 25 such as a belt, and the supply pipe 23 and the rotary disk 16 are rotated. If necessary, the supply pipe 23 and the rotating disk 16 are supported by bearings or the like at appropriate positions.

対向するディスク16,17の中心部の容積は広く、外周に向かうほど容積が狭くなっている。外周端の隙間は1mm以下に設定し、中心部に供給された生汚泥は供給手段(図示せず)による圧入圧力と回転ディスク16の遠心作用により外周側に移送されながらディスクの内面で細分化される。細分化により、長さ0.1mm〜30mmであった繊維が、長さ0.1mm〜5mmに調製される。 The volume of the center part of the opposing disks 16 and 17 is large, and the volume is narrowed toward the outer periphery. The gap at the outer peripheral edge is set to 1 mm or less, and the raw sludge supplied to the center is subdivided on the inner surface of the disk while being transferred to the outer peripheral side by the press-fitting pressure by the supply means (not shown) and the centrifugal action of the rotating disk 16. Is done. By subdividing, fibers having a length of 0.1 mm to 30 mm are prepared to have a length of 0.1 mm to 5 mm.

本実施例では、生汚泥に希釈水を供給し、調製工程6での作用効果を増大させている。具体的には、生汚泥中の絡み合っていた繊維分と夾雑物は、希釈水中でのすり潰し作用によりほどけ、容易に分離できるようになる。大きな夾雑物は、細分化により除去しやすい大きさに砕かれる。 In the present embodiment, dilution water is supplied to the raw sludge to increase the effect in the preparation step 6. Specifically, the entangled fibers and contaminants in the raw sludge can be unwound by the crushing action in diluted water and easily separated. Large contaminants are crushed to a size that is easy to remove by fragmentation.

すり潰し機9aを分離機10に内設して一体化しているので、対向ディスク16,17外部に排出された調製汚泥は、回転円筒型スクリーン18で構成した分離機10aで連続的に分離が可能となる。 Since the grinding machine 9a is integrated in the separator 10, the prepared sludge discharged to the outside of the opposed disks 16 and 17 can be continuously separated by the separator 10a constituted by the rotating cylindrical screen 18. It becomes.

なお、処理量が多い場合は、対向ディスク16,17の径を大きくする、あるいは対向ディスク16,17を多段に併設する等、周知の技術で適宜対応できる。また、図7のように、すり潰し機9aを分離機10aの機外に設置する場合は、対向ディスク16,17をケーシング26で囲繞し、移送管27を介して調製汚泥を分離機10aに送れば、連続的に調製・分離工程が可能となる。 When the amount of processing is large, it can be appropriately handled by a known technique such as increasing the diameter of the opposing disks 16 and 17 or arranging the opposing disks 16 and 17 in multiple stages. Further, as shown in FIG. 7, when the grinding machine 9a is installed outside the separator 10a, the opposed disks 16 and 17 are surrounded by the casing 26, and the prepared sludge can be sent to the separator 10a via the transfer pipe 27. In this case, the preparation / separation process can be continuously performed.

本実施例の分離機10aは、回転円筒型のスクリーン18で構成している。スクリーン18端部の供給部28aに供給された調製汚泥は、スクリーン18内面に中心方向に向かって立設したスクリュー羽根19により他端に搬送されつつ、細分化された夾雑物等がろ過面52aを構成するスクリーン18に設けた多数の細孔より分離排出される。回転円筒型のスクリーン18のろ過面52aの下方には分離槽29を配設しており、スクリーン18の開口を通過した夾雑物等の易分解性有機物を集積している。 The separator 10a of the present embodiment is composed of a rotating cylindrical screen 18. The prepared sludge supplied to the supply unit 28a at the end of the screen 18 is conveyed to the other end by the screw blade 19 erected on the inner surface of the screen 18 in the center direction, and finely divided impurities and the like are filtered. Are separated and discharged from a large number of pores provided in the screen 18. A separation tank 29 is disposed below the filtration surface 52 a of the rotating cylindrical screen 18 and accumulates easily decomposable organic substances such as foreign substances that have passed through the opening of the screen 18.

スクリーン18の両端には軸30を延設しており、回転可能に軸支している。スクリーン18内部にすり潰し機9aを内設している場合、すり潰し機9aの供給管23を介してスクリーン18を回転可能に軸支する。駆動機31からの動力はベルト等の動力伝達手段32を介してスクリーン18に伝達し、スクリーン18を回転させる。 A shaft 30 extends from both ends of the screen 18 and is rotatably supported. When the grinding machine 9a is installed inside the screen 18, the screen 18 is rotatably supported through the supply pipe 23 of the grinding machine 9a. The power from the drive unit 31 is transmitted to the screen 18 through power transmission means 32 such as a belt, and the screen 18 is rotated.

本実施例では、分離槽29の壁板をスクリーン18に重複する程度まで高くして、内部に浸漬水を貯水することでスクリーン18の一部を浸漬させている。また、スクリーン18の抽出部33a近傍を円錐状に漸減させている。こうすることで、繊維間内部に付着しているわずかな夾雑物又は回収範囲以下の小さな繊維分について、浸漬水中でほぐしながら分散させ、水と共に分離槽へ重力分離する作用を高めることができる。なお、分離中の調製汚泥に高圧水を噴射する噴射装置34を設けても同等の効果が見込める。 In the present embodiment, the wall plate of the separation tank 29 is raised to the extent that it overlaps the screen 18, and a part of the screen 18 is immersed by storing immersion water therein. Further, the vicinity of the extraction portion 33a of the screen 18 is gradually reduced in a conical shape. By carrying out like this, it is possible to enhance the action of dispersing only a small amount of foreign substances adhering to the inside of the fiber or a small fiber content below the recovery range while loosening it in the immersion water and gravity separating it into the separation tank together with the water. An equivalent effect can be expected even if an injection device 34 for injecting high-pressure water to the prepared sludge being separated is provided.

分離槽29には返送管35を連結しており、分離槽29に分離排出された易分解性有機物を主とする夾雑物は生物処理槽1に返送される。生物処理槽1の前段で難分解性有機物である植物繊維を主とした繊維分を抽出しており、生物処理槽1では食品残渣由来の易分解性有機物の割合が高くなる。したがって、生物処理に要する反応時間が短時間で済み、下水処理場全体の処理効率が向上する。 A return pipe 35 is connected to the separation tank 29, and impurities mainly composed of easily decomposable organic substances separated and discharged to the separation tank 29 are returned to the biological treatment tank 1. The fiber part which mainly consists of the vegetable fiber which is a hardly decomposable organic substance is extracted in the front | former stage of the biological treatment tank 1, and the ratio of the easily decomposable organic substance derived from a food residue becomes high in the biological treatment tank 1. FIG. Therefore, the reaction time required for biological treatment is short, and the treatment efficiency of the entire sewage treatment plant is improved.

スクリーン18の開孔から分離されずにスクリーン18内部に残留する所定の性状の繊維分は、スクリュー羽根19によりスクリーン18他端まで搬送される。 A fiber having a predetermined property that remains in the screen 18 without being separated from the opening of the screen 18 is conveyed to the other end of the screen 18 by a screw blade 19.

本実施例の回収装置11aは、回転円筒型のスクリーン18に適合するように、スクリーン18内部の繊維分を搬送するスクリュー羽根19を回収装置として使用している。スクリーン18内面にスクリュー羽根19を螺旋状に掛け回して立設し、スクリーン18の回転に伴って残留繊維分を抽出部33まで搬送して回収槽36に貯留する。
なお、円筒型のスクリーン18の場合、軸にスクリュー羽根を掛け回したスクリュー軸を内挿して回収装置として使用してもよい。
The recovery device 11a of the present embodiment uses a screw blade 19 that conveys the fiber content inside the screen 18 as the recovery device so as to fit the rotating cylindrical screen 18. Screw blades 19 are spirally wound around the inner surface of the screen 18, and the residual fibers are conveyed to the extraction unit 33 as the screen 18 rotates and stored in the collection tank 36.
In the case of the cylindrical screen 18, a screw shaft in which a screw blade is wound around the shaft may be inserted and used as a recovery device.

回収された繊維分は、短時間で腐敗する食品残渣由来の易分解性有機物がないので、特別な処理および装置を必要とせず、長時間の保管が可能となる。 Since the recovered fiber has no readily decomposable organic matter derived from food residues that rot in a short time, it does not require special treatment and equipment and can be stored for a long time.

図8は他の実施例1の抽出装置の詳細図であって、抽出部33bを上方に傾斜した状態で抽出装置2bを配設している。抽出装置2bのすり潰し機9bから排出された調製汚泥は、浸漬水でほぐされて分散し、分離機10bのスクリーン18で小さな夾雑物を分離排出しつつ、所定の性状の繊維分をスクリュー羽根19で抽出部33bへ搬送し、回収槽36に集積する。 FIG. 8 is a detailed view of the extraction device of another embodiment 1, in which the extraction device 2b is disposed with the extraction portion 33b inclined upward. The prepared sludge discharged from the pulverizer 9b of the extraction device 2b is loosened and dispersed with immersion water, and small impurities are separated and discharged by the screen 18 of the separator 10b. Then, it is conveyed to the extraction unit 33b and accumulated in the collection tank 36.

分離機10bが傾斜しているためスクリーン18の抽出部33b近傍が浸漬されておらず、浸漬による洗浄・分散効果と、抽出部33b近傍での重力分離作用によって、図5の抽出装置2と同様の効果が得られる。
その他の部品構成は、図6に示す実施例と同様である。
Since the separator 10b is inclined, the vicinity of the extraction unit 33b of the screen 18 is not immersed, and the same effect as the extraction device 2 of FIG. 5 is obtained due to the washing / dispersing effect by the immersion and the gravity separation action near the extraction unit 33b. The effect is obtained.
Other component configurations are the same as those of the embodiment shown in FIG.

図9は他の実施例2の抽出装置の詳細図であって、回転円筒型のスクリーン18の内部に複数の転動体37…を混入している。抽出装置2cはスクリーン18の内部ですり潰し機9cから排出された調製汚泥と混合し、分離工程7での繊維同士の絡み付きを防止するとともに、調製汚泥をほぐす作用を奏するので分離効率が向上する。 FIG. 9 is a detailed view of the extraction device of another embodiment 2, in which a plurality of rolling elements 37 are mixed inside a rotating cylindrical screen 18. The extraction device 2c mixes with the prepared sludge discharged from the crusher 9c inside the screen 18 to prevent the fibers from being entangled in the separation step 7 and also has an effect of loosening the prepared sludge, so that the separation efficiency is improved.

転動体37は金属、合成ゴム、樹脂等の重量物であれば材質は限定しないが、スクリーン18内部で搬送されながら転がるため、振動や騒音の観点から衝撃・振動吸収性に優れた低反発ゴムが望ましい。 The material of the rolling element 37 is not limited as long as it is a heavy object such as metal, synthetic rubber, and resin. However, the rolling element 37 is rolled while being conveyed inside the screen 18, and therefore has low impact resistance and vibration absorption from the viewpoint of vibration and noise. Is desirable.

分離機10cは、所定の性状の繊維分を回収する抽出部33cをスクリーン18の円筒面に設け、抽出部33cの開孔を繊維分より大きく、且つ転動体37の径より小さくすることで繊維分のみを抽出できる。転動体37は抽出部33cからさらに搬送され、スクリーン18端部より転動体槽38に排出される。転動体槽38に貯留された転動体37は、公知の返送手段39により循環管42を経て、すり潰し機9c側のスクリーン18端部に供給される。必要に応じて、転動体37を洗浄してもよい。
その他の部品構成は、図6に示す実施例と同様である。
The separator 10c is provided with an extraction portion 33c for collecting a fiber having a predetermined property on the cylindrical surface of the screen 18, and the opening of the extraction portion 33c is made larger than the fiber and smaller than the diameter of the rolling element 37. Only minutes can be extracted. The rolling element 37 is further conveyed from the extraction unit 33 c and discharged from the end of the screen 18 to the rolling element tank 38. The rolling elements 37 stored in the rolling element tank 38 are supplied to the end of the screen 18 on the side of the grinding machine 9c via the circulation pipe 42 by a known return means 39. The rolling element 37 may be washed as necessary.
Other component configurations are the same as those of the embodiment shown in FIG.

図10は他の実施例3の抽出装置の詳細図であって、円筒スクリーン40の内壁に摺接しながら回転するローラー41で構成したすり潰し機9dで汚泥を細分化し、調製汚泥をベルト型の分離機10dに供給し、抽出部33dに搬送する間に夾雑物を分離し、抽出部33dでスクレーパ43により所定の繊維分を抽出する抽出装置2dである。 FIG. 10 is a detailed view of the extraction device of another embodiment 3, wherein the sludge is subdivided by a grinding machine 9d composed of a roller 41 that rotates while sliding on the inner wall of the cylindrical screen 40, and the prepared sludge is separated into a belt type. This is an extraction device 2d that separates contaminants while being supplied to the machine 10d and conveyed to the extraction unit 33d, and a predetermined fiber component is extracted by the scraper 43 in the extraction unit 33d.

すり潰し機9dは、一方が閉塞された筒状のケーシング44に、径方向に所定の間隔を設けて円筒スクリーン40を内挿し、円筒スクリーン40の内壁に摺接部材41を押圧しながら摺接回転させている。本実施例では、摺接部材としてローラー41を用い、複数のローラー41…を回転させている。円筒スクリーン40の開口部中央には供給管23を連結し汚泥を供給する。駆動機46からの動力はベルト等の動力伝達手段47を介してローラー41に伝達し、ローラー41を回転させる。 The crusher 9d inserts the cylindrical screen 40 into a cylindrical casing 44, one of which is closed, with a predetermined interval in the radial direction, and rotates while sliding while pressing the sliding member 41 against the inner wall of the cylindrical screen 40. I am letting. In this embodiment, a roller 41 is used as a sliding contact member, and a plurality of rollers 41 are rotated. A supply pipe 23 is connected to the center of the opening of the cylindrical screen 40 to supply sludge. The power from the driving machine 46 is transmitted to the roller 41 via power transmission means 47 such as a belt, and the roller 41 is rotated.

供給管23から円筒スクリーン40内に供給された汚泥は、ローラー41の押圧作用と遠心作用によりすり潰されながら細分化され、円筒スクリーン40の細孔を通過する。円筒スクリーン40とケーシング44間に移送された調製汚泥は、ケーシング44に設けた移送管48を経て分離機10dへ供給される。
なお、本実施例はローラー41を円筒スクリーン40の内壁に摺設させているが、同様の効果を得るものであれば摺接部材を限定しない。
The sludge supplied from the supply pipe 23 into the cylindrical screen 40 is subdivided while being ground by the pressing action and centrifugal action of the roller 41, and passes through the pores of the cylindrical screen 40. The prepared sludge transferred between the cylindrical screen 40 and the casing 44 is supplied to the separator 10 d through a transfer pipe 48 provided in the casing 44.
In this embodiment, the roller 41 is slid on the inner wall of the cylindrical screen 40, but the sliding contact member is not limited as long as the same effect is obtained.

分離機10dの構成は、複数のロール50…に多数の細孔を有した無端ベルト51を掛け回し、上部のろ過面52に調製汚泥を供給する。ロール50を駆動して小さな夾雑物を分離しながら無端ベルト51を走行させる。ろ過面52dの下方には分離槽29を配設しており、濾過された小さな夾雑物が貯留される。分離槽29には返送管35を連結しており、分離槽29に分離排出された易分解性有機物を主とする夾雑物を生物処理槽1に返送する。必要に応じてろ過面52dを再生する洗浄装置53を適所に配設する。洗浄水は、分離槽29から清澄ろ過等で夾雑物を分離したろ液を用いてもよい。調製汚泥の供給部28dには越流防止用のカバー54を設け、調製汚泥を浸漬させるようにしてもよい。 The separator 10d has a configuration in which an endless belt 51 having a large number of pores is wound around a plurality of rolls 50, and the prepared sludge is supplied to the upper filtration surface 52. The endless belt 51 is made to travel while driving the roll 50 to separate small impurities. A separation tank 29 is disposed below the filtration surface 52d, and small filtered impurities are stored. A return pipe 35 is connected to the separation tank 29, and contaminants mainly composed of easily decomposable organic substances separated and discharged to the separation tank 29 are returned to the biological treatment tank 1. If necessary, a cleaning device 53 for regenerating the filtration surface 52d is disposed at an appropriate position. As the washing water, a filtrate obtained by separating impurities from the separation tank 29 by clarification filtration or the like may be used. The prepared sludge supply unit 28d may be provided with a cover 54 for preventing overflow, and the prepared sludge may be immersed therein.

回収装置11dとして、無端ベルト51の抽出部33dにスクレーパ43を押圧し、無端ベルト51上面に残留した所定の繊維分をスクレーパ43で掻き取る。掻き取られた繊維分は、回収槽36に貯留される。 As the recovery device 11 d, the scraper 43 is pressed against the extraction unit 33 d of the endless belt 51, and predetermined fiber remaining on the upper surface of the endless belt 51 is scraped off by the scraper 43. The scraped fibers are stored in the collection tank 36.

抽出装置2のすり潰し機、分離機、回収装置は様々な組み合わせで使用することが可能で、仕様や処理場に応じて適宜選択できる。 The crusher, the separator, and the recovery device of the extraction device 2 can be used in various combinations, and can be appropriately selected according to the specifications and the processing site.

図11は下水処理場にOD法を採用した際のフロー図である。下水道から流入する汚水は、流路を経てOD法を行う反応槽55へ送られ、一部を抽出装置2へ送る。抽出装置2へ送られた汚泥は繊維分が回収され、排出される夾雑物や水分などは反応槽55へ送られる。汚水から難分解性有機物の繊維分を回収しているため、反応槽55へ送る夾雑物等は易分解性有機物を多く含む。従って、易分解性有機物を反応槽55へ送ると、生物処理を行うための反応期間が短くなる。
反応槽55では活性汚泥処理が行われ、活性汚泥は最終沈澱池56へ送られる。
最終沈殿池56では汚泥を沈殿させ、上澄水は図示しない消毒タンクへ送り、消毒後に放流する。沈殿した汚泥は混合槽3へ送り、抽出装置2で回収された繊維分と混合される。
繊維分が添加された汚泥は凝集混和槽4へ送られ、凝集剤を添加して凝集汚泥を生成する。凝集汚泥は脱水機5へ送られ、脱水される。
FIG. 11 is a flowchart when the OD method is adopted in the sewage treatment plant. The sewage flowing from the sewer is sent to the reaction tank 55 that performs the OD method through the flow path, and a part thereof is sent to the extraction device 2. The sludge sent to the extraction device 2 collects the fiber content, and the discharged contaminants and moisture are sent to the reaction tank 55. Since the fiber content of the hardly decomposable organic matter is recovered from the sewage, the contaminants sent to the reaction tank 55 contain a large amount of easily decomposable organic matter. Therefore, when an easily decomposable organic substance is sent to the reaction tank 55, the reaction period for performing biological treatment is shortened.
In the reaction tank 55, activated sludge treatment is performed, and the activated sludge is sent to the final sedimentation basin 56.
In the final sedimentation basin 56, sludge is precipitated, and the supernatant water is sent to a disinfection tank (not shown) and discharged after disinfection. The precipitated sludge is sent to the mixing tank 3 and mixed with the fiber collected by the extraction device 2.
The sludge to which the fiber is added is sent to the coagulation / mixing tank 4, and a coagulant is added to produce the coagulated sludge. The agglomerated sludge is sent to the dehydrator 5 and dehydrated.

図12は下水処理場にMBR(膜分離活性汚泥法)を採用した際のフロー図である。下水道から流入した汚水は、流路に配設した微細目の流入スクリーン57で分離され、固形物を抽出装置2へ送り、その他の汚水を調製タンク58へ送る。流入スクリーン57で分離した回収物は、微細目の流入スクリーン57で分離しているので、繊維分の他、夾雑物等が混入している。
抽出装置2へ送られた固形物は、回収範囲内の繊維分が回収され、その他の夾雑物や水分等が調製タンク58へ送られる。調製タンク58へ送られた汚水は膜分離活性汚泥法を行う反応槽55へ送られる。抽出装置2では汚水から難分解性有機物の繊維分を回収しているため、調製タンク58へ送る夾雑物等は易分解性有機物を多く含む。従って、調製タンク58から反応槽55へ易分解性有機物を送ると、生物処理を行うための反応期間が短くなる。
反応槽55の生物膜を透過したろ液は、図示しない消毒タンクへ送り、消毒後に放流する。
反応槽55から引き抜いた汚泥は混合槽3へ送られ、抽出装置2で回収した繊維分と混合される。繊維分が添加された汚泥は凝集混和槽4へ送られ、凝集剤を添加して凝集汚泥を生成する。凝集汚泥は脱水機5へ送られ、脱水される。
FIG. 12 is a flow chart when MBR (membrane separation activated sludge method) is adopted in the sewage treatment plant. The sewage flowing from the sewer is separated by a fine inflow screen 57 disposed in the flow path, the solid matter is sent to the extraction device 2, and the other sewage is sent to the preparation tank 58. Since the recovered material separated by the inflow screen 57 is separated by the fine inflow screen 57, impurities and the like are mixed in addition to the fibers.
The solids sent to the extraction device 2 are collected with the fiber content within the collection range, and other impurities, moisture, etc. are sent to the preparation tank 58. The sewage sent to the preparation tank 58 is sent to the reaction tank 55 that performs the membrane separation activated sludge method. Since the extraction device 2 collects the fiber of the hardly decomposable organic matter from the sewage, the foreign matter to be sent to the preparation tank 58 contains a lot of easily decomposable organic matter. Therefore, when an easily decomposable organic substance is sent from the preparation tank 58 to the reaction tank 55, the reaction period for performing biological treatment is shortened.
The filtrate that has passed through the biofilm in the reaction tank 55 is sent to a disinfection tank (not shown) and discharged after disinfection.
The sludge extracted from the reaction tank 55 is sent to the mixing tank 3 and mixed with the fiber recovered by the extraction device 2. The sludge to which the fiber is added is sent to the coagulation / mixing tank 4, and a coagulant is added to produce the coagulated sludge. The agglomerated sludge is sent to the dehydrator 5 and dehydrated.

図13は下水処理場で混合生汚泥を処理する際のフロー図である。ここで、夜間は昼間よりも一般的に汚水の発生量が減少するため、最初沈殿池14から引き抜かれる汚水の量が減少する。従って、混合生汚泥は最終沈殿池56から送られる余剰汚泥の割合が増えるため、難脱水性となる。よって、混合生汚泥の脱水に本発明の汚泥処理方法を採用することで、脱水効率が向上する。
下水道から流入した汚水は最初沈殿池14へ送られる。最初沈殿池14では緩やかに汚水が流れており、沈殿物が生汚泥として引き抜かれ、抽出装置2と混合槽3へ送られる。また、最初沈殿池14の上澄水は反応槽55へ送る。抽出装置2で繊維分を回収し、回収した繊維分は混合槽3へ送られる。また、抽出装置2から排出された夾雑物等を反応槽55へ送る。抽出装置2は生汚泥から難分解性有機物の繊維分を回収しているため、抽出装置2から排出した夾雑物等は易分解性有機物を多く含む。従って、易分解性有機物が反応槽55へ送られると、生物処理を行うための反応期間が短くなる。
反応槽55で分解された汚泥は最終沈殿池56へ送られる。最終沈殿池56では汚泥を沈殿させ、上澄水は図示しない消毒タンクへ送り、消毒後に放流する。沈殿した汚泥は混合槽3へ送られ、最初沈殿池14から引き抜かれた生汚泥と混合することで混合生汚泥となる。また、抽出装置2で回収した繊維分も混合槽3へ送られ、混合生汚泥に添加されている。
繊維分を添加した混合生汚泥は凝集混和槽4へ送られ、凝集剤を添加して凝集汚泥を生成する。凝集汚泥は脱水機5へ送られ、脱水される。
FIG. 13 is a flowchart when processing mixed raw sludge in a sewage treatment plant. Here, since the amount of generated sewage generally decreases at night compared to the daytime, the amount of sewage that is initially withdrawn from the settling basin 14 decreases. Accordingly, the mixed raw sludge becomes difficult to dehydrate because the proportion of excess sludge sent from the final sedimentation basin 56 increases. Therefore, the dewatering efficiency is improved by employing the sludge treatment method of the present invention for dewatering the mixed raw sludge.
The sewage flowing from the sewer is first sent to the settling basin 14. In the first sedimentation basin 14, sewage flows gently, and the sediment is extracted as raw sludge and sent to the extraction device 2 and the mixing tank 3. In addition, the supernatant water of the first sedimentation tank 14 is sent to the reaction tank 55. The extractor 2 collects the fiber and the recovered fiber is sent to the mixing tank 3. Further, the foreign matter discharged from the extraction device 2 is sent to the reaction tank 55. Since the extraction device 2 collects the fiber of the hardly decomposable organic matter from the raw sludge, the impurities and the like discharged from the extraction device 2 contain a lot of easily decomposable organic matter. Therefore, when an easily decomposable organic substance is sent to the reaction tank 55, the reaction period for performing biological treatment is shortened.
The sludge decomposed in the reaction tank 55 is sent to the final sedimentation tank 56. In the final sedimentation basin 56, sludge is precipitated, and the supernatant water is sent to a disinfection tank (not shown) and discharged after disinfection. The precipitated sludge is sent to the mixing tank 3 and mixed with the raw sludge drawn out from the settling tank 14 first to become mixed raw sludge. Moreover, the fiber part collect | recovered with the extraction apparatus 2 is also sent to the mixing tank 3, and is added to mixing raw sludge.
The mixed raw sludge to which the fibers are added is sent to the flocculation mixing tank 4, and a flocculating agent is added to generate the flocculated sludge. The agglomerated sludge is sent to the dehydrator 5 and dehydrated.

本発明に係る繊維の抽出装置は下水処理場に流入した汚泥中の繊維分を脱水助剤として有効活用するもので、処理場内の不要物から脱水助剤を調達できるものである。脱水助剤を購入、備蓄する必要がないため、ランニングコストが低減するだけでなく、設備の小型化を図ることができる。
汚泥中の難脱水性有機物を脱水助剤として処理系内の汚泥処理に有効活用し、易分解性有機物を生物処理槽に返送するので、低含水率の脱水ケーキを生成できるとともに、処理場内の生物処理工程での反応期間を短縮できる。処理場全体の処理効率の向上に寄与できるものである。
The fiber extraction apparatus according to the present invention effectively utilizes the fiber content in the sludge that has flowed into the sewage treatment plant as a dehydration aid, and can procure the dehydration aid from unnecessary materials in the treatment plant. Since it is not necessary to purchase and store dehydration aids, not only the running cost is reduced, but also the equipment can be downsized.
The dewatering organic matter in the sludge is effectively used for the sludge treatment in the treatment system as a dehydrating aid, and the easily degradable organic matter is returned to the biological treatment tank. The reaction period in the biological treatment process can be shortened. It can contribute to the improvement of the processing efficiency of the entire treatment plant.

9 すり潰し機
10 分離機
11 回収装置
16 回転ディスク
17 固定ディスク
18 スクリーン
19 スクリュー羽根
22 供給口
23 供給管
29 分離槽
33 抽出部
28 供給部
34 噴射装置
35 返送管
37 転動体
38 転動体槽
39 返送手段
40 円筒スクリーン
41 摺接部材,ローラー
42 循環管
43 スクレーパ
44 ケーシング
48 移送管
50 ロール
51 無端ベルト
52 ろ過面
DESCRIPTION OF SYMBOLS 9 Crusher 10 Separator 11 Recovery device 16 Rotating disk 17 Fixed disk 18 Screen 19 Screw blade 22 Supply port 23 Supply pipe 29 Separation tank 33 Extraction part 28 Supply part 34 Injection apparatus 35 Return pipe 37 Rolling body 38 Rolling body tank 39 Return Means 40 Cylindrical screen 41 Sliding member, roller 42 Circulating pipe 43 Scraper 44 Casing 48 Transfer pipe 50 Roll 51 Endless belt 52 Filtration surface

Claims (11)

下水処理プロセスで発生する汚泥から特定の素材を抽出する装置において、
汚泥を細分化するすり潰し機(9)と、
すり潰した調製汚泥から難分解性有機物と易分解性有機物とを分離する分離機(10)と、
難分解性有機物を抽出する回収装置(11)を備え、
連続的に所定の難分解性有機物を分離回収する
ことを特徴とする抽出装置。
In a device that extracts specific materials from sludge generated in the sewage treatment process,
A grinding machine (9) for subdividing sludge;
A separator (10) for separating a hardly decomposable organic substance and an easily decomposable organic substance from the ground prepared sludge;
Equipped with a recovery device (11) for extracting persistent organic matter,
An extraction apparatus characterized by continuously separating and recovering a predetermined hardly decomposable organic substance.
前記分離機(10)の下方に易分解性有機物を収集する分離槽(29)を設け、
易分解性有機物を下水処理場の生物処理槽に返送する返送管(35)を分離槽(29)に連結した
ことを特徴とする請求項1に記載の抽出装置。
A separation tank (29) for collecting easily decomposable organic substances is provided below the separator (10),
The extraction apparatus according to claim 1, wherein a return pipe (35) for returning easily decomposable organic matter to a biological treatment tank of a sewage treatment plant is connected to the separation tank (29).
前記すり潰し機(9)を、
回転ディスク(16)と固定ディスク(17)を対向させて構成するとともに、
回転ディスク(16)の中心部に開口した供給口(22)に供給管(23)を連結し、
対向ディスク(16,17)の外周端に所定の隙間を設けた
ことを特徴とする請求項1または2に記載の抽出装置。
The crusher (9),
The rotating disk (16) and the fixed disk (17) are configured to face each other,
The supply pipe (23) is connected to the supply port (22) opened at the center of the rotating disk (16),
3. The extraction device according to claim 1, wherein a predetermined gap is provided at the outer peripheral end of the opposing disk (16, 17).
前記すり潰し機(9)を、
一方が閉塞された筒状のケーシング(44)に円筒スクリーン(40)を内挿し、
円筒スクリーン(40)の内壁に摺接する摺接部材(41)を回転自在に内設して構成するとともに、
円筒スクリーン(40)の開口部中央に供給管(23)と、
ケーシング(44)に移送管(48)を設けた
ことを特徴とする請求項1または2に記載の抽出装置。
The crusher (9),
A cylindrical screen (40) is inserted into a cylindrical casing (44) closed on one side,
The sliding contact member (41) that is in sliding contact with the inner wall of the cylindrical screen (40) is configured to be rotatably provided,
A supply pipe (23) in the center of the opening of the cylindrical screen (40);
3. Extraction device according to claim 1 or 2, characterized in that a transfer pipe (48) is provided in the casing (44).
前記分離機(10)を、
回転自在に配設した円筒型のスクリーン(18)で構成するとともに、
前記回収装置(11)を、
スクリーン(18)内に内設した螺旋状に掛け回したスクリュー羽根(19)で構成した
ことを特徴とする請求項1〜4の何れか1項に記載の抽出装置。
Said separator (10),
It is composed of a cylindrical screen (18) arranged rotatably,
The recovery device (11)
The extraction device according to any one of claims 1 to 4, wherein the extraction device comprises a screw blade (19) wound in a spiral shape provided in a screen (18).
前記分離機(10)の抽出部(33)近傍を円錐状に漸減した
ことを特徴とする請求項5に記載の抽出装置。
The extraction device according to claim 5, wherein the vicinity of the extraction section (33) of the separator (10) is gradually reduced in a conical shape.
前記分離機(10)を、
複数のロール(50…)に走行自在に巻き掛け、多数の細孔を有した無端ベルト(51)構成し、
前記回収装置(11)を、
ろ過面後方に配設したスクレーパ(43)で構成した
ことを特徴とする請求項1〜4の何れか1項に記載の抽出装置。
Said separator (10),
A plurality of rolls (50...) Are wound around freely to form an endless belt (51) having a large number of pores.
The recovery device (11)
The extraction device according to any one of claims 1 to 4, comprising a scraper (43) disposed behind the filtration surface.
前記分離機(10)の供給部(28)を含むろ過面(52)を、分離槽(29)に浸漬水を貯水して浸漬させた
ことを特徴とする請求項1〜6の何れか1項に記載の抽出装置。
The filtration surface (52) including the supply part (28) of the separator (10) is stored in immersion tank (29) and immersed in the immersion tank (29). The extraction device according to item.
前記分離機(10)のろ過面(52)を高圧水で噴射する噴射装置(34)を設けた
ことを特徴とする請求項1〜8の何れか1項に記載の抽出装置。
The extraction device according to any one of claims 1 to 8, further comprising an injection device (34) for injecting the filtration surface (52) of the separator (10) with high-pressure water.
前記分離機(10)に複数の転動体(37…)を混入し、
転動体(37…)を回収する転動体槽(38)と、
転動体槽(38)から循環管(42)を経て分離機(10)の供給部(28)に返送するための返送手段(39)を備えた
ことを特徴とする請求項1〜9の何れか1項に記載の抽出装置。
A plurality of rolling elements (37 ...) are mixed in the separator (10),
A rolling element tank (38) for collecting the rolling elements (37 ...);
The return means (39) for returning to the supply part (28) of the separator (10) from the rolling element tank (38) through the circulation pipe (42) is provided. The extraction device according to claim 1.
前記難脱水性有機物は繊維状物であり、
回収する所定性状の繊維分を、
繊維長さ0.1mm〜5mm、繊維径1μm〜50μmとする
ことを特徴とする請求項1〜10の何れか1項に記載の抽出装置。
The hardly dehydrating organic material is a fibrous material,
The fiber of the predetermined property to collect
The extraction apparatus according to any one of claims 1 to 10, wherein the fiber length is 0.1 mm to 5 mm, and the fiber diameter is 1 µm to 50 µm.
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CA2970289A CA2970289C (en) 2013-07-26 2014-06-20 Recovery device and recovery method for recovering specific material from sludge
PCT/JP2014/066435 WO2015012039A1 (en) 2013-07-26 2014-06-20 Recovery device and recovery method for recovering specific material from sludge, sludge dehydration system, and sludge dehydration method
EP16157337.3A EP3059015A1 (en) 2013-07-26 2014-06-20 Sludge dehydration system and sludge dehydration method
EP14829186.7A EP3026026B1 (en) 2013-07-26 2014-06-20 Recovery device and recovery method for recovering specific material from sludge
CA2917488A CA2917488C (en) 2013-07-26 2014-06-20 Sludge dehydration system and sludge dehydration method
TW103121710A TWI636019B (en) 2013-07-26 2014-06-24 Recovery device for recovering specific materials from sludge, recovery method, sludge dewatering system, and sludge dewatering method
US14/989,362 US9975798B2 (en) 2013-07-26 2016-01-06 Sludge dehydration system and sludge dehydration method
US14/989,065 US10974982B2 (en) 2013-07-26 2016-01-06 Recovery device and recovery method for recovering specific material from sludge
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