JP2007021413A - Apparatus and method for treating sludge - Google Patents

Apparatus and method for treating sludge Download PDF

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JP2007021413A
JP2007021413A JP2005208973A JP2005208973A JP2007021413A JP 2007021413 A JP2007021413 A JP 2007021413A JP 2005208973 A JP2005208973 A JP 2005208973A JP 2005208973 A JP2005208973 A JP 2005208973A JP 2007021413 A JP2007021413 A JP 2007021413A
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sludge
crusher
tank
dehydrator
residue
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JP4537282B2 (en
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Nobuyuki Tatemitsu
伸行 立光
Akira Saito
彰 斉藤
Koji Murakoshi
浩二 村越
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Shinko Pantec Co Ltd
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Kobelco Eco Solutions Co Ltd
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

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  • Treatment Of Sludge (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide an apparatus for treating sludge capable of preventing the sludge inflow port of a centrifugal dewatering machine from being clogged with screenings in screenings containing sludge. <P>SOLUTION: The apparatus for treating the sludge 1' comprises a first crusher 6 for crushing a solid substance in the screenings containing sludge into a smaller particle, the centrifugal dewatering machine 8 for receiving the screenings containing sludge crushed by the first crusher 6 to concentrate it, a second crusher 9 for receiving the screenings containing sludge dewatered by this centrifugal dewatering machine 8 to crush it, a pretreatment tank 11 for receiving the screenings containing sludge crushed by the second crusher 9 to easily digest it, and a digestion tank 12 for fermenting a pre-treated liquid pre-treated in this pretreatment tank 11 to generate methane. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は、汚泥処理設備および汚泥処理方法に係り、より詳しくは、下水処理場等の最初沈殿槽から排出されるし渣含有汚泥を処理するに際して、し渣含有汚泥を濃縮する脱水機のし渣含有汚泥が流入する汚泥流入口の目詰まりを防止することにより稼動率の向上を可能ならしめると共に、後段の前処理および消化処理の安定運転を可能ならしめるようにした汚泥処理設備および汚泥処理方法に関する。   The present invention relates to a sludge treatment facility and a sludge treatment method. More specifically, the present invention relates to a dehydrator for concentrating sludge containing sludge discharged from a first settling tank such as a sewage treatment plant and processing sludge containing sludge. Sludge treatment equipment and sludge treatment that can improve the operating rate by preventing clogging of the sludge inlet into which sludge containing sludge flows, and also enable stable operation of pretreatment and digestion in the subsequent stage. Regarding the method.

下水や廃水等の汚水を曝気槽により活性汚泥処理し、活性汚泥処理した被処理水の上澄みを河川等に放流する一方、し渣含有汚泥を濃縮し、調整した後に加熱、かつ加水分解すると共に、消化槽で発酵させてメタンガスを得た後に、脱水して脱水ケーキとするようにした汚泥処理設備がある。このような汚泥処理設備としては、例えば後述する構成になるものが公知である。以下、従来例1に係る汚泥処理設備を、添付図面を参照しながら説明する。   Sewage such as sewage and wastewater is treated with activated sludge in an aeration tank, and the supernatant of treated water that has been treated with activated sludge is discharged to rivers, while the sludge containing sludge is concentrated, adjusted, heated and hydrolyzed. There is a sludge treatment facility that is fermented in a digestion tank to obtain methane gas and then dehydrated into a dehydrated cake. As such a sludge treatment facility, for example, one having a configuration described later is known. Hereinafter, the sludge treatment facility according to Conventional Example 1 will be described with reference to the accompanying drawings.

従来例1に係る汚泥処理設備は、その概略図の図2に示すとおりである。即ち、下水は、先ず、最初沈殿池(最初沈殿槽に相当する。)に導入され、この最初沈殿池でし渣等の固形物質を沈殿分離させた後に、曝気槽を経て最終沈殿池(最終沈殿槽に相当する。)に送られる、そして、最終沈殿池において静置され、上澄みPH調整などが施された後、放流水として排出される。一方、最初沈殿池、および最終沈殿池の底に沈殿した汚泥は回収されて汚泥濃縮槽に送られ、汚泥濃縮槽においてさらに凝縮される。次いで、汚泥消化槽で嫌気性発酵させることにより消化処理された後に、超音波発振器が取付けられてなる汚泥貯留槽に送られる。この汚泥貯留槽において、先ず、汚泥に対して時間、超音波を照射した後に、凝集剤を加えて凝集沈殿処理が行われる。凝集沈殿した汚泥は、汚泥脱水機に送られて脱水されことにより、脱水汚泥となる。次いで、この脱水汚泥はケーキホッパに送られ、このケーキホッパから外部に搬出されるように構成されている(例えば、特許文献1参照。)。   The sludge treatment facility according to Conventional Example 1 is as shown in FIG. That is, sewage is first introduced into a first sedimentation basin (corresponding to a first sedimentation tank), solid substances such as residue are settled and separated in this first sedimentation tank, and then passed through an aeration tank (final sedimentation basin (final). It is sent to a settling tank) and left in the final settling basin, and after adjusting the supernatant pH and the like, it is discharged as discharge water. On the other hand, the sludge deposited on the bottom of the first sedimentation basin and the final sedimentation basin is collected and sent to the sludge concentration tank, where it is further condensed in the sludge concentration tank. Next, after digestion by anaerobic fermentation in the sludge digestion tank, it is sent to a sludge storage tank to which an ultrasonic oscillator is attached. In this sludge storage tank, first, after irradiating the sludge with ultrasonic waves for a time, a flocculant is added to perform a coagulation sedimentation treatment. The coagulated sedimented sludge is sent to a sludge dewatering machine and dehydrated to become dehydrated sludge. Next, the dewatered sludge is sent to a cake hopper and is transported out of the cake hopper (see, for example, Patent Document 1).

従来例2に係る汚泥処理設備は、その概略図の図3、およびその浄化装置の概略図の図4に示すとおりである。即ち、汚水が供給される最初沈殿池51と、この最初沈殿池51から流出する汚水を活性汚泥処理するための曝気槽52と、この曝気槽52で活性汚泥処理された曝気処理液から活性汚泥を分離するための最終沈殿池53と、この最終沈殿池53から分離除去された汚泥を消化し易くするための前処理装置55と、前処理した汚泥を嫌気消化するための分解槽(消化槽)56と、この分解槽56の処理物を脱水処理するための脱水装置57と、この脱水装置57からの脱水液を最初沈殿池51に戻すための返送ライン61とを備えた汚泥処理設備において、後述する構成になる浄化装置59が、前記曝気槽52と返送ライン61との間に配設されている。このような汚泥処理設備における脱水装置57として、プレス式脱水機や遠心分離機(以下、遠心脱水機という。)等を使用することができる。なお、図3に示す符号54は汚泥を高濃度(例えば、汚泥濃度8〜15%)に濃縮するための濃縮装置であって、このような濃縮装置としてはプレス式脱水機や遠心脱水機等が用いられる。   The sludge treatment facility according to Conventional Example 2 is as shown in FIG. 3 of the schematic diagram and FIG. 4 of the schematic diagram of the purification device. That is, the first settling basin 51 to which the sewage is supplied, the aeration tank 52 for treating the sewage flowing out from the first settling basin 51 with the activated sludge, and the activated sludge from the aerated treatment liquid treated with the activated sludge in the aerated tank 52. A final sedimentation basin 53 for separating the sludge, a pretreatment device 55 for facilitating digestion of the sludge separated and removed from the final sedimentation basin 53, and a decomposition tank (digestion tank) for anaerobically digesting the pretreated sludge ) 56, a sludge treatment facility comprising a dehydrator 57 for dehydrating the processed material in the decomposition tank 56 and a return line 61 for returning the dehydrated liquid from the dewaterer 57 to the initial sedimentation tank 51. A purification device 59 configured as described later is disposed between the aeration tank 52 and the return line 61. As the dewatering device 57 in such a sludge treatment facility, a press-type dewatering device, a centrifugal separator (hereinafter referred to as a centrifugal dewatering device), or the like can be used. In addition, the code | symbol 54 shown in FIG. 3 is a concentration apparatus for concentrating sludge to high concentration (for example, sludge density | concentration 8-15%), As such a concentration apparatus, a press-type dehydrator, a centrifugal dehydrator, etc. Is used.

前記浄化装置59は、図4に示すように構成されている。即ち、脱水液を活性汚泥処理するための曝気部81と、曝気処理した液から活性汚泥を分離除去する液ろ過部82とを有する浄化槽80で構成されている。前記曝気部81には曝気用気体供給口83が槽底付近に設置されており、前記液ろ過部82には膜分離のためのユニット84が槽の中程度の高さに設置されている。そして、この液ろ過部82でろ過された液は返送ライン61を介して最初沈殿池51に戻される(例えば、特許文献2参照。)。   The purification device 59 is configured as shown in FIG. That is, it comprises a septic tank 80 having an aeration section 81 for treating the dehydrated liquid with activated sludge and a liquid filtration section 82 for separating and removing the activated sludge from the aerated liquid. The aeration unit 81 is provided with an aeration gas supply port 83 in the vicinity of the tank bottom, and the liquid filtration unit 82 is provided with a unit 84 for membrane separation at an intermediate height of the tank. And the liquid filtered with this liquid filtration part 82 is first returned to the settling basin 51 via the return line 61 (for example, refer patent document 2).

なお、従来例に係る典型的な遠心脱水機としては、例えば、その断面図の図5に示すような構成になるものが公知である。この遠心脱水機は、一端側内周部が先細り状に傾斜させられた外形略円筒状をなして中心軸線O回りに回転可能に支持される回転ボール91を備えている。この回転ボール91内には、この回転ボール91と同軸的にスクリュコンベア97が配置されており、前記回転ボール91と差速をもって同方向に回転されるように構成されている。前記スクリュコンベア97と前記回転ボール91との間の環状空間C内に軸線O方向中央部から供給された被処理物(し渣含有汚泥)Pは、この回転ボール91の遠心力によって固液分離され、そして分離された固形分Sは環状空間Cの一端側に開口した固形分排出口94から排出されるように構成されている。さらに、この固形分排出口94に固形分Sの排出量を調整する弁体104が設けられると共に、分離液Lは軸線O方向他端側において環状空間Cの内周側に開口した分離液流路101から排出されるように構成されている。   As a typical centrifugal dehydrator according to the conventional example, for example, one having a configuration as shown in FIG. This centrifugal dehydrator is provided with a rotating ball 91 that is formed in a substantially cylindrical shape in which an inner peripheral portion on one end side is inclined in a tapered shape and is rotatably supported around a central axis O. In the rotating ball 91, a screw conveyor 97 is disposed coaxially with the rotating ball 91, and is configured to rotate in the same direction as the rotating ball 91 with a differential speed. The workpiece (sludge containing sludge) P supplied from the central portion in the axis O direction into the annular space C between the screw conveyor 97 and the rotating ball 91 is separated into solid and liquid by the centrifugal force of the rotating ball 91. The separated solid content S is discharged from a solid content discharge port 94 opened to one end of the annular space C. Further, a valve body 104 for adjusting the discharge amount of the solid content S is provided at the solid content discharge port 94, and the separation liquid L is opened to the inner peripheral side of the annular space C on the other end side in the axis O direction. It is configured to be discharged from the path 101.

なお、この遠心脱水機の長手方向(図における左右方向)の両端付近の符号92,93は略円筒状の軸端部であり、これら軸端部92,93に外嵌されてなる符合95は軸受であり、符号96はベルト96a、プーリ93aを介して回転ボール91を回転させるモータ等の回転手段である。また、これら軸端部92,93の内側に嵌合され、スクリュコンベア97の端部を支持してなるものは軸受98であり、このスクリュコンベア97の図における右側の端部に設けられてなるものは、このスクリュコンベア97を回転させるモータ等の回転手段である(例えば、特許文献3参照。)。
特開平11−19697号公報 特開2004−16969号公報 特開2002−336735号公報
Reference numerals 92 and 93 in the vicinity of both ends in the longitudinal direction (left and right direction in the figure) of the centrifugal dehydrator are substantially cylindrical shaft end portions, and reference numeral 95 formed by being externally fitted to the shaft end portions 92 and 93 is Reference numeral 96 denotes a rotating means such as a motor for rotating the rotating ball 91 via a belt 96a and a pulley 93a. Further, a bearing 98 that is fitted inside the shaft end portions 92 and 93 and supports the end portion of the screw conveyor 97 is provided at the right end portion of the screw conveyor 97 in the drawing. A thing is rotating means, such as a motor which rotates this screw conveyor 97 (for example, refer to patent documents 3).
Japanese Patent Laid-Open No. 11-19697 JP 2004-16969 A JP 2002-336735 A

脱水機には、ベルトプレス形脱水機、遠心脱水機、スクリュープレス、回転式加圧脱水機があるが、上記のような汚泥処理設備には、何れの形式の脱水機も採用することができる。ところで、脱水すべき汚泥や排水には、例えば、毛髪、ビニル片等の比較的長いし渣が含有されている場合がある。このようなし渣含有汚泥や汚水をベルトプレス形脱水機に供給した場合には問題がない。しかしながら、このようなし渣含有汚泥や汚水を遠心脱水機に供給すると、この遠心脱水機の本体の内部の径中心に配設され、先端部付近の外周に設けられ、外周方向にし渣含有汚泥や汚水を排出して脱水室に流入させる複数の汚泥流入口(直径40mm程度)がし渣で塞がれ、遠心脱水機によるし渣含有汚泥や汚水の脱水ができなくなるという問題が生じる。また、スクリュープレスや回転式加圧脱水機も同様の問題を有している。   The dehydrator includes a belt press type dehydrator, a centrifugal dehydrator, a screw press, and a rotary pressure dehydrator. Any type of dehydrator can be used for the sludge treatment equipment as described above. . By the way, the sludge to be dehydrated and the drainage may contain relatively long residues such as hair and vinyl pieces. There is no problem when such residue-containing sludge and sewage are supplied to a belt press type dehydrator. However, when such slag-containing sludge or sewage is supplied to the centrifugal dehydrator, it is disposed at the center of the diameter inside the main body of this centrifugal dehydrator, provided at the outer periphery near the tip, A plurality of sludge inlets (diameter of about 40 mm) for discharging the sewage and flowing into the dewatering chamber are blocked with scum, resulting in a problem that sewage-containing sludge and sewage cannot be dewatered by a centrifugal dehydrator. Screw presses and rotary pressure dehydrators have similar problems.

因みに、このような遠心脱水機では、24時間程度の運転で汚泥流入口が目詰まりしてしまい、24時間程度しか連続運転することができない。従って、汚泥流入口に目詰まりしたし渣を除去するために、脱水機の運転を停止すると共に、分解、組立て作業をしなければならないから、汚泥処理設備の稼動率が低下するばかりでなく、メンテナンスコストが嵩むという問題があった。また、上記のとおり、し渣含有汚泥の濃縮処理が連続的に行われなくなるため、後段の前処理および消化処理も不安定となり、し渣含有汚泥の処理能力も低下する恐れが生じるという問題もあった。   Incidentally, in such a centrifugal dehydrator, the sludge inlet is clogged after about 24 hours of operation, and can only be operated continuously for about 24 hours. Therefore, in order to remove clogs and residue from the sludge inlet, the operation of the dehydrator must be stopped and disassembly and assembly operations must be performed. There was a problem that maintenance cost increased. In addition, as described above, the concentration treatment of the sludge containing sludge is not continuously performed, so that the subsequent pretreatment and digestion treatment become unstable, and the treatment capacity of the sludge containing sludge may be reduced. there were.

従って、本発明の目的は、最初沈殿槽から排出されるし渣含有汚泥を処理するに際して、し渣含有汚泥中のし渣に起因する脱水機の汚泥流入口の目詰まりを防止することを可能ならしめる汚泥処理設備および汚泥処理方法を提供することである。   Therefore, the object of the present invention is to prevent clogging of the sludge inlet of the dehydrator caused by the residue in the residue-containing sludge when the residue-containing sludge discharged from the sedimentation tank is first processed. It is to provide a sludge treatment facility and a sludge treatment method.

本発明は、上記実情に鑑みてなされたものであって、従って課題を解決するために、本発明の請求項1に係る汚泥処理設備が採用した手段は、し渣含有汚泥中の固形物質をより小さな粒子に破砕する第1破砕機と、この第1破砕機で破砕されたし渣含有汚泥を受入れて濃縮する脱水機と、この脱水機で脱水された濃縮汚泥を受入れて破砕する第2破砕機と、この第2破砕機で破砕された濃縮汚泥を受入れて消化し易くする前処理槽と、この前処理槽で前処理された前処理液を発酵させてメタンを発生させる消化槽とを備えてなることを特徴とするもものである。   The present invention has been made in view of the above circumstances, and therefore, in order to solve the problem, the means employed by the sludge treatment facility according to claim 1 of the present invention is the solid substance in the sludge containing sludge. A first crusher that crushes into smaller particles, a dehydrator that accepts and concentrates sludge containing sludge crushed by this first crusher, and a second that accepts and crushes concentrated sludge dehydrated by this dehydrator A crusher, a pretreatment tank that accepts the concentrated sludge crushed by the second crusher for easy digestion, and a digester tank that ferments the pretreatment liquid pretreated in the pretreatment tank to generate methane. It is characterized by comprising.

本発明の請求項2に係る汚泥処理設備が採用した手段は、請求項1に記載の汚泥処理設備において、前記第1破砕機の上段側に、し渣含有汚泥を受入れる受入れ槽を設け、前記第1破砕機から前記受入れ槽に連通する汚泥戻しラインを設けたことを特徴とするものである。   Means employed by the sludge treatment facility according to claim 2 of the present invention is the sludge treatment facility according to claim 1, wherein a receiving tank for receiving the residue containing sludge is provided on the upper stage side of the first crusher, A sludge return line communicating from the first crusher to the receiving tank is provided.

本発明の請求項3に係る汚泥処理設備が採用した手段は、請求項2に記載の汚泥処理設備において、前記第2破砕機と前記前処理槽との間に、前記第2破砕機で破砕された濃縮汚泥中の固形物の濃度を均一にする調整槽を設け、この調整槽から前記第2破砕機に連通する汚泥戻しラインを設けたことを特徴とするものである。   The means adopted by the sludge treatment facility according to claim 3 of the present invention is the sludge treatment facility according to claim 2, wherein the second crusher crushes between the second crusher and the pretreatment tank. An adjustment tank that makes the concentration of the solid matter in the concentrated sludge uniform is provided, and a sludge return line that communicates from the adjustment tank to the second crusher is provided.

本発明の請求項4に係る汚泥処理方法が採用した手段は、前記請求項1乃至3のうちの何れか一つの項に記載の汚泥処理設備を用いて、し渣含有汚泥を処理することを特徴とするものである。   The means adopted by the sludge treatment method according to claim 4 of the present invention is to treat the sludge containing sludge using the sludge treatment facility according to any one of claims 1 to 3. It is a feature.

本発明の請求項1乃至3に係る汚泥処理設備では、脱水装置の前段側に、固体物質をより小さな粒子に破砕するための第1破砕機(例えば、マセレータポンプ)が配設されている。従って、本発明の請求項1乃至3に係る汚泥処理設備によれば、第1破砕機によるし渣含有汚泥中の毛髪やビニル片等のし渣の破砕により小さな粒子になるように破砕されて脱水機の汚泥流入口に供給されるから、この排水流入口がし渣により目詰まりするような恐れがない。よって、し渣含有汚泥が安定して連続的に濃縮されるため、後段側において濃縮汚泥は安定して前処理されると共に、消化処理されることとなる。   In the sludge treatment facility according to claims 1 to 3 of the present invention, a first crusher (for example, a macerator pump) for crushing the solid substance into smaller particles is disposed on the front side of the dehydrator. . Therefore, according to the sludge treatment facility according to claims 1 to 3 of the present invention, the sludge is crushed into small particles by crushing the residue such as hair and vinyl pieces in the residue containing sludge by the first crusher. Since it is supplied to the sludge inlet of the dehydrator, there is no fear that the drain inlet will be clogged with residue. Therefore, since the residue-containing sludge is stably and continuously concentrated, the concentrated sludge is stably pretreated and digested on the subsequent stage side.

本発明の請求項2に係る汚泥処理装置では、第1破砕機の前段側に、し渣含有汚泥を受入れる受入れ槽が設けられ、第1破砕機から受入れ槽に連通する汚泥戻しラインが設けられている。従って、発明の請求項2に係る汚泥処理装置によれば、受入れ槽と第1破砕機との間でし渣含有汚泥を循環させて破砕したし渣を脱水機に供給することができるから、この第1破砕機によるし渣の小粒子化効率が向上し、脱水機の汚泥流入口の目詰まりをより確実に防止することができる。     In the sludge treatment apparatus according to claim 2 of the present invention, a receiving tank for receiving the sludge containing sludge is provided on the front stage side of the first crusher, and a sludge return line communicating from the first crusher to the receiving tank is provided. ing. Therefore, according to the sludge treatment apparatus according to claim 2 of the invention, since the residue-containing sludge is circulated between the receiving tank and the first crusher and crushed, the residue can be supplied to the dehydrator. The particle size reduction efficiency of the residue by the first crusher is improved, and clogging of the sludge inlet of the dehydrator can be more reliably prevented.

本発明の請求項3に係る汚泥処理設備では、第2破砕機と前処理槽との間に、第2破砕機で破砕された濃縮汚泥中の固形物の濃度を均一にする調整槽が設けられ、この調整槽から前記第2破砕機に連通する汚泥戻しラインが設けられている。従って、本発明の請求項3に係る汚泥処理設備によれば、第2破砕機と調整槽との間でし渣含有濃縮汚泥を循環させることにより、調整槽内におけるし渣含有濃縮汚泥の固形分濃度の均一性を向上させることができるから、後段においてし渣含有濃縮汚泥を安定して効率良く前処理および消化処理することができる。   In the sludge treatment facility according to claim 3 of the present invention, an adjustment tank is provided between the second crusher and the pretreatment tank to make the concentration of solids in the concentrated sludge crushed by the second crusher uniform. In addition, a sludge return line communicating from the adjustment tank to the second crusher is provided. Therefore, according to the sludge treatment facility according to claim 3 of the present invention, the residue-containing concentrated sludge is solidified in the adjustment tank by circulating the residue-containing concentrated sludge between the second crusher and the adjustment tank. Since the uniformity of the partial concentration can be improved, the residue-containing concentrated sludge can be stably and efficiently pretreated and digested in the subsequent stage.

本発明の請求項4に係る汚泥処理方法では、前記請求項1乃至3のうちの何れか一つの項に記載の汚泥処理設備を用いて、し渣含有汚泥が処理される。従って、本発明の請求項4に係る汚泥処理方法によれば、し渣含有汚泥は安定して効率良く前処理および消化処理される。   In the sludge treatment method according to claim 4 of the present invention, the residue-containing sludge is treated using the sludge treatment facility according to any one of claims 1 to 3. Therefore, according to the sludge treatment method of claim 4 of the present invention, the residue-containing sludge is stably and efficiently pretreated and digested.

以下、本発明の汚泥処理方法を実施する、本発明の形態に係る汚泥処理設備を、脱水機が遠心脱水機である場合を例として、添付図面を参照しながら説明する。図1は本発明の形態に係る汚泥処理設備の模式的構成説明図である。なお、遠心脱水機の構成については、段落番号〔0006〕において説明した従来例(特開2002−336735号公報)に係る遠心脱水機とほぼ同構成であるから、遠心脱水機の構成に係る説明については割愛する。   Hereinafter, a sludge treatment facility according to an embodiment of the present invention for carrying out the sludge treatment method of the present invention will be described with reference to the accompanying drawings, taking as an example the case where the dehydrator is a centrifugal dehydrator. FIG. 1 is a schematic explanatory diagram of a sludge treatment facility according to an embodiment of the present invention. The configuration of the centrifugal dehydrator is substantially the same as that of the conventional centrifugal dehydrator described in paragraph [0006] (Japanese Patent Laid-Open No. 2002-336735). I'll leave you out.

図1に示す符号1は、本発明の形態に係る汚泥処理設備1′を組込んだ汚水処理設備である。この汚水処理設備1は、処理すべき下水等の汚水が流入する最初沈殿槽2、この最初沈殿槽2から流入する1次処理水を活性汚泥処理する曝気槽3を備えている。また、この曝気層3から流入する曝気処理された曝気処理液から活性汚泥を分離し、上澄みを処理水として放流する最終沈殿槽4を備えている。そして、汚泥処理設備1′は。前記最初沈殿槽2、および最終沈殿槽4の底に沈殿した毛髪、ビニル片等のし渣を含む汚泥(水分;94〜99wt%程度)、および最終沈殿槽4の底の微生物の汚泥(水分;94〜99wt%程度)を受入れる受入れ槽5を備えている。なお、水分を94〜99wt%程度含む汚泥にするために、最初沈殿槽2と受入れ槽5との間、および最終沈殿槽4と受入れ槽5との間のそれぞれに濃縮装置が設けられることがある。   The code | symbol 1 shown in FIG. 1 is the sewage treatment equipment incorporating the sludge treatment equipment 1 'which concerns on the form of this invention. The sewage treatment facility 1 includes an initial sedimentation tank 2 into which sewage such as sewage to be treated flows, and an aeration tank 3 for treating the activated sludge from the primary treatment water flowing in from the first sedimentation tank 2. In addition, a final sedimentation tank 4 is provided for separating activated sludge from the aeration-treated aerated liquid flowing in from the aeration layer 3 and discharging the supernatant as treated water. And sludge treatment equipment 1 '. Sludge (moisture; about 94 to 99 wt%) containing hair, vinyl pieces, and the like sedimented on the bottom of the first sedimentation tank 2 and the final sedimentation tank 4, and microorganism sludge (moisture content) at the bottom of the final sedimentation tank 4 ; About 94-99 wt%) is provided. In order to make sludge containing about 94 to 99 wt% of water, a concentrating device may be provided between the first settling tank 2 and the receiving tank 5 and between the final settling tank 4 and the receiving tank 5. is there.

また、前記受入れ槽5から排出された毛髪、ビニル片等のし渣を含有するし渣含有汚泥は、図示しない破砕刃を有する第1破砕機6で破砕されてポンプ7に供給されるようになっている。第1破砕機6とポンプ7は、破砕機能とポンプ機能を有するマセレータポンプに置換することが、設備の簡素化にとって好ましい。このようなマセレータポンプとしては、例えば、特開平6−154752号公報において開示されてなる公知の構成のものを使用することができる。   Further, the residue-containing sludge containing residue such as hair and vinyl pieces discharged from the receiving tank 5 is crushed by a first crusher 6 having a crushing blade (not shown) and supplied to the pump 7. It has become. The first crusher 6 and the pump 7 are preferably replaced with a macerator pump having a crushing function and a pump function for simplification of equipment. As such a macerator pump, for example, a known configuration disclosed in Japanese Patent Laid-Open No. 6-154752 can be used.

なお、前記第1破砕機6から受入れ槽5の上部に連通してなるものは、第1汚泥戻しライン6aであって、この第1汚泥戻しライン6aにより受入れ槽5と第1破砕機6との間でし渣含有汚泥を循環させて破砕することができる。従って、第1破砕機6によるし渣の小粒子化効率が向上するという効果を得ることができる。   In addition, what is connected to the upper part of the receiving tank 5 from the said 1st crusher 6 is the 1st sludge return line 6a, Comprising: With this 1st sludge return line 6a, the receiving tank 5 and the 1st crusher 6 and The residue-containing sludge can be circulated and crushed. Therefore, it is possible to obtain an effect that the efficiency of reducing the size of the residue by the first crusher 6 is improved.

前記第1破砕機6で小粒子化されたし渣を含有するし渣含有汚泥は、ポンプ7を介して上記従来例に係る遠心脱水機とほぼ同構成になる遠心脱水機8に供給される。そして、この遠心脱水機8で脱水されて、固形分が8〜20wt%程度、好ましくは10〜15wt%のし渣含有濃縮汚泥となって、前記第1破砕機6と同構成になる第2破砕機9に供給され、この第2破砕機9で破砕されたし渣含有濃縮汚泥は調整槽10に供給される。そして、この調整槽10に供給されたし渣含有濃縮汚泥は固形分濃度が均一になるように調整される。また、第2破砕機9もマセレータポンプとすることも可能である。   The sludge containing sludge that has been reduced in size by the first crusher 6 is supplied via a pump 7 to a centrifugal dehydrator 8 having substantially the same configuration as the centrifugal dehydrator according to the conventional example. . Then, it is dewatered by the centrifugal dehydrator 8 to form a sludge containing concentrated sludge having a solid content of about 8 to 20 wt%, preferably 10 to 15 wt%, and having the same configuration as the first crusher 6. The residue-containing concentrated sludge that is supplied to the crusher 9 and crushed by the second crusher 9 is supplied to the adjustment tank 10. And the residue containing concentrated sludge supplied to this adjustment tank 10 is adjusted so that solid content concentration may become uniform. The second crusher 9 can also be a macerator pump.

なお、前記調整槽10の下部から第2破砕機9に連通してなるものは、第2汚泥戻しライン9aであって、この第2汚泥戻しライン9aにより第2破砕機9と調整槽10との間でし渣含有濃縮汚泥を循環させることにより、調整槽10内におけるし渣含有濃縮汚泥の固形分濃度の均一性を向上させることができる。   In addition, what is connected to the 2nd crusher 9 from the lower part of the said adjustment tank 10 is the 2nd sludge return line 9a, Comprising: The 2nd crusher 9 and the adjustment tank 10 with this 2nd sludge return line 9a By circulating the residue-containing concentrated sludge between them, the uniformity of the solid content concentration of the residue-containing concentrated sludge in the adjustment tank 10 can be improved.

前記調整槽10により固形分が均一化された調整濃縮汚泥は前処理槽11に供給され、この前処理槽11内において、後段側の消化処理を促進し易くするために可溶化される。
前処理槽11で採用される調整濃縮汚泥の可溶化方法としては、例えば加熱、超音波、高電圧パルス印加、高圧気体導入、オゾン供給、粉砕、酸添加、アルカリ添加、または酵素添加等の種々の手段を挙げることができる。しかしながら、消化により発生するメタンを有効利用する観点からすると加熱することが好ましく、調整濃縮汚泥は120〜220℃(好ましくは、150〜180℃)、0.1〜6時間(好ましくは、0.2〜2時間)の条件で加熱・加水分解される。このような条件下で調整濃縮汚泥から生成された反応処理液は消化槽12に供給される。
The adjusted concentrated sludge whose solid content has been made uniform by the adjusting tank 10 is supplied to the pretreatment tank 11 and is solubilized in the pretreatment tank 11 in order to facilitate the subsequent digestion process.
Examples of the solubilization method of the adjusted concentrated sludge employed in the pretreatment tank 11 include various methods such as heating, ultrasonic waves, high voltage pulse application, high pressure gas introduction, ozone supply, pulverization, acid addition, alkali addition, or enzyme addition. Can be mentioned. However, from the viewpoint of effectively using methane generated by digestion, heating is preferable, and the adjusted concentrated sludge is 120 to 220 ° C. (preferably 150 to 180 ° C.) for 0.1 to 6 hours (preferably 0.1. It is heated and hydrolyzed under the condition of 2 to 2 hours. The reaction treatment liquid generated from the adjusted concentrated sludge under such conditions is supplied to the digestion tank 12.

前記消化槽12に供給された反応処理液は、この消化槽12内において発酵してメタンを発生する。発酵済みの処理液は、図示しない最終脱水機に供給されて脱水されて汚泥ケーキとなり、然るべき方法により処理されることとなる。そして、前記遠心脱水機8、前記最終脱水機により分離された分離液は、例えば図示しない分離液処理槽に集液されると共に、前記最初沈殿槽2に流入する下水に混入されるように構成されている。なお、前記消化槽12で発生したメタンの一部は、前記前処理槽11における調整濃縮汚泥を加熱するための燃料として活用される。   The reaction solution supplied to the digester 12 is fermented in the digester 12 to generate methane. The fermented processing liquid is supplied to a final dehydrator (not shown) and dehydrated to form a sludge cake, which is processed by an appropriate method. The separation liquid separated by the centrifugal dehydrator 8 and the final dehydrator is collected in, for example, a separation liquid treatment tank (not shown) and mixed into the sewage flowing into the first precipitation tank 2. Has been. A part of the methane generated in the digestion tank 12 is utilized as a fuel for heating the adjusted concentrated sludge in the pretreatment tank 11.

以下、上記構成になる汚泥処理設備1′の作用態様を説明する。即ち、この汚泥処理設備1′では、遠心脱水機8の前段側に、固体物質をより小さな粒子とする第1破砕機(例えば、マセレータポンプ)6が配設されている。従って、第1破砕機6の破砕刃によるし渣含有汚泥中の毛髪やビニル片等のし渣の破砕により小さな粒子になるように破砕されて遠心脱水機8の汚泥流入口に供給されるから、この汚泥流入口がし渣により目詰まりするような恐れがない。よって、し渣含有汚泥が安定して連続的に濃縮されるため、後段側において濃縮汚泥は安定して前処理されると共に、消化処理されることとなる。   Hereinafter, the operation mode of the sludge treatment facility 1 ′ having the above configuration will be described. That is, in the sludge treatment facility 1 ′, a first crusher (for example, a macerator pump) 6 that makes a solid substance smaller particles is disposed on the upstream side of the centrifugal dehydrator 8. Therefore, it is crushed into small particles by crushing the residue such as hair and vinyl pieces in the residue containing sludge by the crushing blade of the first crusher 6 and supplied to the sludge inlet of the centrifugal dehydrator 8. There is no fear that the sludge inlet will be clogged with residue. Therefore, since the residue-containing sludge is stably and continuously concentrated, the concentrated sludge is stably pretreated and digested on the subsequent stage side.

なお、以上の形態においては、第1破砕機6から受入れ槽5の上部に第1汚泥戻しライン6aを、また調整槽10の下部から第2破砕機9に第2汚泥戻しライン9aをそれぞれ連通させることにより、し渣含有汚泥、またはし渣含有濃縮汚泥を循環させる場合の例を説明した。しかしながら、第1汚泥戻しライン6aや第2汚泥戻しライン9aを設けなくてもそれなりの効果が得られ、また脱水機は遠心脱水機に限らず、例えばスクリュープレス(例えば、特開2004−195524に記載されたもの)や回転式加圧脱水機(例えば、特表2004−532733に記載されたもの)に対しても本発明の技術的思想を適用することができるので、上記形態に係る汚泥処理設備1′の構成に限定されるものではない。また、上記形態に係る汚泥処理設備1′は、本発明の1具体例に過ぎないから、本発明の技術的思想を逸脱しない範囲内における設計変更等は自由自在である。   In the above embodiment, the first sludge return line 6a communicates from the first crusher 6 to the upper part of the receiving tank 5, and the second sludge return line 9a communicates from the lower part of the adjustment tank 10 to the second crusher 9. The example in which the residue-containing sludge or the residue-containing concentrated sludge is circulated is described. However, even if the first sludge return line 6a and the second sludge return line 9a are not provided, a certain effect can be obtained, and the dehydrator is not limited to the centrifugal dehydrator. For example, a screw press (for example, Japanese Patent Application Laid-Open No. 2004-195524). The technical idea of the present invention can also be applied to a rotary pressure dehydrator (for example, those described in JP-T-2004-532733). The configuration is not limited to the equipment 1 '. Further, the sludge treatment facility 1 ′ according to the above embodiment is only one specific example of the present invention, and therefore, design changes and the like can be freely made without departing from the technical idea of the present invention.

本発明の形態に係る汚泥処理設備の模式的構成説明図である。It is typical structure explanatory drawing of the sludge processing equipment which concerns on the form of this invention. 従来例1に係る汚泥処理設備の概略図である。It is the schematic of the sludge processing equipment which concerns on the prior art example 1. 従来例2に係る汚泥処理設備の概略図である。It is the schematic of the sludge processing equipment concerning the prior art example 2. 従来例2に係る汚泥処理設備の浄化装置の概略図である。It is the schematic of the purification apparatus of the sludge treatment facility which concerns on the prior art example 2. 従来例に係る典型的な遠心脱水機の断面図である。It is sectional drawing of the typical centrifugal dehydrator which concerns on a prior art example.

符号の説明Explanation of symbols

1…汚水処理設備、1′…汚泥処理設備、2…最初沈殿槽、3…曝気槽、4…最終沈殿槽、5…受入れ槽、6…第1破砕機,6a…第1汚泥戻しライン、7…ポンプ、8…遠心脱水機。9…第2破砕機,9a…第2汚泥戻しライン、10…調整槽、11…前処理槽、12…消化槽。   DESCRIPTION OF SYMBOLS 1 ... Sewage treatment equipment, 1 '... Sludge treatment equipment, 2 ... First sedimentation tank, 3 ... Aeration tank, 4 ... Final sedimentation tank, 5 ... Receiving tank, 6 ... 1st crusher, 6a ... 1st sludge return line, 7 ... Pump, 8 ... Centrifugal dehydrator. DESCRIPTION OF SYMBOLS 9 ... 2nd crusher, 9a ... 2nd sludge return line, 10 ... Adjustment tank, 11 ... Pretreatment tank, 12 ... Digestion tank.

Claims (4)

し渣含有汚泥中の固形物質をより小さな粒子に破砕する第1破砕機と、この第1破砕機で破砕されたし渣含有汚泥を受入れて濃縮する脱水機と、この脱水機で脱水された濃縮汚泥を受入れて破砕する第2破砕機と、この第2破砕機で破砕された濃縮汚泥を受入れて消化し易くする前処理槽と、この前処理槽で前処理された前処理液を発酵させてメタンを発生させる消化槽とを備えてなることを特徴とする汚泥処理設備。   The 1st crusher which crushes the solid substance in the residue containing sludge into smaller particles, the dehydrator which accepts and concentrates the residue containing sludge crushed by this 1st crusher, and was dehydrated by this dehydrator Fermenting the second crusher that receives and crushes the concentrated sludge, the pretreatment tank that accepts the concentrated sludge crushed by the second crusher and facilitates digestion, and the pretreatment liquid pretreated in this pretreatment tank A sludge treatment facility characterized by comprising a digester for generating methane. 前記第1破砕機の上段側に、し渣含有汚泥を受入れる受入れ槽を設け、前記第1破砕機から前記受入れ槽に連通する汚泥戻しラインを設けたことを特徴とする請求項1に記載の汚泥処理設備。   2. The sludge return line communicating with the receiving tank from the first crusher is provided on the upper stage side of the first crusher, and a receiving tank is provided for receiving sludge containing sludge. Sludge treatment equipment. 前記第2破砕機と前記前処理槽との間に、前記第2破砕機で破砕された濃縮汚泥中の固形物の濃度を均一にする調整槽を設け、この調整槽から前記第2破砕機に連通する汚泥戻しラインを設けたことを特徴とする請求項2に記載の汚泥処理設備。   An adjustment tank is provided between the second crusher and the pretreatment tank to make the concentration of solids in the concentrated sludge crushed by the second crusher uniform from the adjustment tank to the second crusher. 3. The sludge treatment facility according to claim 2, further comprising a sludge return line communicating with the sludge. 前記請求項1乃至3のうちの何れか一つの項に記載の汚泥処理設備を用いて、し渣含有汚泥を処理することを特徴とする汚泥処理方法。   A sludge treatment method, comprising treating sludge containing sludge using the sludge treatment facility according to any one of claims 1 to 3.
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