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JP6103231B2 - Method and system for dewatering sewage sludge - Google Patents

Method and system for dewatering sewage sludge Download PDF

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JP6103231B2
JP6103231B2 JP2013189126A JP2013189126A JP6103231B2 JP 6103231 B2 JP6103231 B2 JP 6103231B2 JP 2013189126 A JP2013189126 A JP 2013189126A JP 2013189126 A JP2013189126 A JP 2013189126A JP 6103231 B2 JP6103231 B2 JP 6103231B2
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sludge
amount
dewatering
aid
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JP2015054286A (en
JP2015054286A5 (en
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山下 学
学 山下
片山 雅義
雅義 片山
康隆 末次
康隆 末次
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Ishigaki Co Ltd
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Ishigaki Co Ltd
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Priority to EP16157337.3A priority patent/EP3059015A1/en
Priority to CA2917488A priority patent/CA2917488C/en
Priority to EP14829186.7A priority patent/EP3026026B1/en
Priority to PCT/JP2014/066435 priority patent/WO2015012039A1/en
Priority to DK14829186.7T priority patent/DK3026026T3/en
Priority to CA2970289A priority patent/CA2970289C/en
Priority to TW103121710A priority patent/TWI636019B/en
Publication of JP2015054286A publication Critical patent/JP2015054286A/en
Publication of JP2015054286A5 publication Critical patent/JP2015054286A5/ja
Priority to US14/989,362 priority patent/US9975798B2/en
Priority to US14/989,065 priority patent/US10974982B2/en
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Publication of JP6103231B2 publication Critical patent/JP6103231B2/en
Priority to US15/951,716 priority patent/US11401188B2/en
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Description

本発明は、下水処理場に流入する流入水から脱水助材として適切な繊維状物のみを選択回収し、下水処理プロセスで発生する難脱水汚泥に回収した脱水助材を添加する下水汚泥の脱水方法及び脱水システムに関する。 The present invention selectively recovers only fibrous materials suitable as a dewatering aid from inflow water flowing into a sewage treatment plant, and adds the recovered dewatering aid to the hardly dewatered sludge generated in the sewage treatment process. The present invention relates to a method and a dehydration system.

従来、下水処理場で発生する難脱水汚泥は繊維分が少なく脱水性が悪い。嫌気消化汚泥処理では、汚泥中の有機物(繊維分等)を嫌気性細菌の働きによって分解した消化汚泥や微生物に転換した余剰汚泥等の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とともに脱水時の水路を形成する効果を有するため、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 a low fiber content and poor dewaterability. In anaerobic digestion sludge treatment, dewatered sludge such as digested sludge obtained by decomposing organic matter (fiber content, etc.) in sludge by the action of anaerobic bacteria and surplus sludge converted to microorganisms is dehydrated. Therefore, fiber content is reduced in the sludge before dehydration. Since the fiber content in the sludge functions as a core of coagulation and has the effect of forming a water channel during dehydration, sludge with a reduced fiber content cannot perform proper coagulation, 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材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。繊維状物を脱水助材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、大量の脱水助材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、脱水助材の備蓄・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 into a hardly dewatered sludge as a dehydrating aid 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 with 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 increase, and there is 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回収繊維を添加して脱水する技術が引用文献1に開示されている。 Thus, a technique for separating and recovering fibers in raw sludge generated from the first sedimentation basin of the sludge treatment process and adding the recovered fibers to hardly dewatered sludge such as excess sludge or digested sludge and dehydrating is disclosed in Citation 1. ing.

また、引用文献2には脱水設備に供給された汚泥に脱水補助材を添加して脱水する汚泥の脱水処理を管理する汚泥管理システムが開示されている。 Further, Cited Document 2 discloses a sludge management system that manages the dewatering treatment of sludge that is dehydrated by adding a dewatering auxiliary material to the sludge supplied to the dewatering equipment.

特開昭61−268400号公報JP-A 61-268400 特開2012−206018号公報JP 2012-206018 A

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、別途脱水助材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材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材として添加すると、脱水ケーキが増量して処理費用が高騰する。また、脱水後に易分解性有機物が分解して腐敗するため、添加前の脱水助材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。脱水助材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おらず、必要な繊維分のみを回収することは困難であった。 Since the technique of the cited document 1 collects fiber from the sludge in the treatment plant, it is not necessary to prepare a separate dehydration aid, and the running cost and equipment are the same as those in normal treatment. However, in a separation device using a screen or a vibrating screen mesh as disclosed in the specification, as a dehydration aid for easily decomposable 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 dehydrating aid, the amount of dehydrated cake increases and the processing cost increases. In addition, since the readily decomposable organic matter decomposes and decays after dehydration, the dehydration aid before addition and the dehydrated cake after addition cannot be stored for a long period of time. A specific method for recovering only the effective fiber as a dehydrating aid has not been disclosed, and it has been difficult to recover only the necessary fiber.

引用文献2の技術は、処理場の汚泥情報と、オフィス等に設置して不要な紙葉類から繊維化した脱水補助材を製造する補助材供給装置の製造情報に基づいて、脱水補助材を脱水設備に供給するための物流情報を管理し、適切な時期に適切な量の脱水補助材を脱水補助材供給装置から脱水設備に柔軟に供給するものである。しかし、紙葉類を溶解して脱水補助材を製造する補助材供給装置をオフィス等に設置する必要があり、脱水補助材の原料となる不要な紙葉類の排出量が一定でないため、複数のオフィスに補助材供給装置を設置しなければならない。また、脱水補助材をオフィスから処理場に輸送する物流手段が必要となる。 The technology of Cited Document 2 is based on the sludge information of the treatment plant and the manufacturing information of the auxiliary material supply device that manufactures the dehydration auxiliary material fiberized from unnecessary paper sheets installed in the office or the like. It manages logistics information for supplying to the dehydration facility, and flexibly supplies an appropriate amount of dehydration auxiliary material from the dehydration auxiliary material supply device to the dehydration facility at an appropriate time. However, it is necessary to install an auxiliary material supply device that dissolves paper sheets to produce dehydration auxiliary materials in offices, etc., and the amount of unnecessary paper sheets used as raw materials for dehydration auxiliary materials is not constant. An auxiliary material supply device must be installed in the office. In addition, a distribution means for transporting the dehydration auxiliary material from the office to the treatment plant is required.

本発明は、下水処理プロセスから所定期間で分離回収する脱水助材の回収量を予測し、脱水助材の貯留量を最小限に保持しつつ、脱水処理される汚泥量を予測し、総汚泥量に脱水助材を分配供給する下水汚泥の脱水方法及び脱水システムを提供する。 The present invention predicts the amount of dewatering aid recovered and separated from a sewage treatment process in a predetermined period, predicts the amount of sludge to be dehydrated while keeping the amount of dewatering aid stored to a minimum, Provided is a dewatering method and a dewatering system for sewage sludge that distributes and supplies dewatering aids in an amount.

本発明の下水汚泥の脱水方法は、下水処理場に流入した流入水中の繊維分を回収し、脱水助材として下水処理プロセスから生じる難脱水汚泥に供給して脱水機で脱水処理する方法において、予め定めた所定期間で、脱水助材の実回収量と、季節や曜日、天候によって変動する流入水中の脱水助材の含有量についての情報である汚泥情報から脱水助材の予測総回収量を推定すると共に、下水処理場に流入する汚泥の実汚泥量と汚泥情報から脱水機で脱水処理する予測総汚泥量を推定し、予測総汚泥量に対して予測総回収量を分配供給するもので、貯留期間が短期間となり、供給量が極端に変動することがなく、安定した低含水率の脱水ケーキを生成できる。 The dewatering method of the sewage sludge of the present invention is a method of collecting fibers in the inflow water flowing into the sewage treatment plant, supplying the hardly dewatered sludge resulting from the sewage treatment process as a dewatering aid, and dehydrating with a dehydrator. Estimated total recovery amount of dewatering aid from the sludge information, which is information about the actual amount of dewatering aid collected in advance and the content of dewatering aid in the inflowing water that varies depending on the season, day of the week, and weather. The estimated total sludge amount to be dehydrated by the dehydrator is estimated from the actual sludge amount of sludge flowing into the sewage treatment plant and sludge information, and the predicted total recovered amount is distributed and supplied to the predicted total sludge amount. The storage period is short, the supply amount does not fluctuate extremely, and a stable dehydrated cake with a low water content can be generated.

本発明の下水汚泥の脱水システムは、脱水助材を回収する回収装置と、脱水助材の回収量を計測する計測装置と、脱水する汚泥量を計測する計測装置と、脱水助材を汚泥に供給する供給装置と、供給装置の供給量を調整する制御装置と、を備え、制御装置は、予め設定した所定期間で、脱水助材の実回収量と、季節や曜日、天候によって変動する流入水中の脱水助材の含有量についての情報である汚泥情報から、分離回収する脱水助材の予測総回収量を算出し、下水処理場に流入する汚泥の実汚泥量と汚泥情報から、所定の期間に脱水機で脱水処理する予測総汚泥量を算出し、予測総汚泥量に対して予測総回収量を分配するための供給量を算出するもので、所定期間の脱水助材の回収量を予測しつつ、予測回収量と脱水機の稼働時間から供給量を算出するので、回収量の変動に対応しつつ、安定した供給量を難脱水汚泥に供給できる。
The dewatering system for sewage sludge of the present invention includes a collection device for collecting dewatering aid, a measuring device for measuring the amount of dewatering aid collected, a measuring device for measuring the amount of sludge to be dehydrated, and dewatering aid as sludge. And a control device for adjusting the supply amount of the supply device. The control device has a predetermined period set in advance, and the actual recovery amount of the dehydration aid and the inflow that varies depending on the season, day of the week, and weather. Calculate the predicted total recovery amount of the dewatering aid to be separated and recovered from the sludge information, which is information on the content of the dewatering aid in the water, and calculate the predetermined amount from the actual sludge amount and sludge information of the sludge flowing into the sewage treatment plant. Calculate the predicted total sludge amount to be dehydrated by the dehydrator during the period and calculate the supply amount to distribute the predicted total recovery amount to the predicted total sludge amount. Supplied based on predicted recovery volume and dehydrator operating time while forecasting Since calculating the while with the variation of the recovery amount, a stable supply amount can be supplied to the flame dewatered sludge.

制御装置は、予測総汚泥量に対して予測総回収量を均等に分配するための供給量を算出するので、安定した低含水率の脱水ケーキの生成が可能である。また、実汚泥量に対して実回収量を均等に分配するための供給量を算出しても同様の効果を得ることができる。 Since the control device calculates the supply amount for evenly distributing the predicted total recovered amount with respect to the predicted total sludge amount, it is possible to generate a dehydrated cake having a stable low water content. Moreover, the same effect can be acquired even if the supply amount for distributing an actual collection amount equally with respect to an actual sludge amount is calculated.

本発明の下水処理場の脱水方法及び脱水システムは、下水処理プロセスから脱水助材を回収するため、別途脱水助材を購入する必要がなく、在庫管理、供給設備等も必要ない。下水処理プロセスの前段で脱水助材として難分解性有機物(繊維状物質)を回収するため、消化槽での分解効率が向上する。回収した脱水助材は脱水機の稼働時間に合わせて順次供給するので、貯留期間が短期間となり、脱水助材の貯留設備を縮小できるとともに、変質、腐敗、臭気の発生を防止できる。所定期間の脱水助材の回収量を予測しつつ、予測回収量と脱水機の稼働時間から供給量を算出するので、供給量が極端に変動することがなく、安定した低含水率の脱水ケーキを得ることができる。 The dewatering method and system of the sewage treatment plant of the present invention collects the dewatering aid from the sewage treatment process, so there is no need to purchase a dewatering aid separately, and no inventory management, supply facilities, etc. are required. Since the hardly decomposable organic substance (fibrous substance) is recovered as a dehydration aid in the previous stage of the sewage treatment process, the decomposition efficiency in the digester is improved. Since the collected dewatering aid is sequentially supplied in accordance with the operating time of the dehydrator, the storage period becomes short, the dewatering aid storage facility can be reduced, and alteration, decay, and odor generation can be prevented. Predicting the amount of dewatering aid collected for a given period, the supply amount is calculated from the predicted amount collected and the operating time of the dehydrator, so the dewatering cake has a stable and low water content without excessive fluctuation. Can be obtained.

本発明に係るシステムのフロー図である。It is a flowchart of the system which concerns on this invention. 同じく、回収装置以降のフロー図である。Similarly, it is a flowchart after a collection device. 同じく、某下水処理場での脱水助材の回収データである。Similarly, it is the collection data of the dewatering aid at the sewage treatment plant. 同じく、他の実施例1のフロー図である。Similarly, it is the flowchart of other Example 1. FIG. 同じく、他の実施例2のフロー図である。Similarly, it is the flowchart of other Example 2. FIG.

本発明の下水汚泥の脱水方法及び脱水システムは、所定期間CP内に下水処理プロセスから発生する汚泥(汚水含む)から回収する脱水助材の総回収量11を予測するとともに、脱水処理する総汚泥量23を予測し、予測総汚泥量25に応じて予測総回収量13を分配添加し、汚泥の脱水性を向上させつつ脱水助材の貯留量を必要最小限に抑えることを目的としている。 The dewatering method and dewatering system for sewage sludge according to the present invention predicts the total recovered amount 11 of dewatering aid recovered from sludge (including sewage) generated from the sewage treatment process within a predetermined period CP, and total sludge to be dewatered. The purpose is to predict the amount 23 and distribute and add the predicted total recovery amount 13 according to the predicted total sludge amount 25 to improve the dewaterability of the sludge and minimize the storage amount of the dewatering aid.

図1は本発明に係るシステムのフロー図である。下水処理場に流れ込んだ流入水を分離する最初沈殿池1と、最初沈殿池1で分離した汚水中の有機物を浄化処理する反応タンク2と、最初沈殿池1で分離した生汚泥を濃縮する重力濃縮槽35と、重力濃縮槽35の前段で所定量の生汚泥を引き抜いて脱水助材を選択的に分離回収する回収装置3と、反応タンク2の混合液を分離する最終沈殿池20と、最終沈殿池20で分離した余剰汚泥を濃縮する機械濃縮槽36と、重力濃縮汚泥および機械濃縮汚泥を嫌気性消化する消化槽37と、難脱水性の消化汚泥を一時的に貯留する汚泥貯留槽27と、脱水助材と消化汚泥を混合した汚泥を固液分離する脱水機8からなる。 FIG. 1 is a flowchart of a system according to the present invention. First sedimentation basin 1 that separates the inflow water that has flowed into the sewage treatment plant, reaction tank 2 that purifies organic matter in the sewage separated in the first sedimentation basin 1, and gravity that concentrates the raw sludge separated in the first sedimentation basin 1 A concentration tank 35, a recovery device 3 for selectively separating and recovering the dewatering aid by drawing out a predetermined amount of raw sludge in the previous stage of the gravity concentration tank 35, a final sedimentation tank 20 for separating the mixed liquid in the reaction tank 2, Mechanical concentration tank 36 for concentrating excess sludge separated in final sedimentation basin 20, digestion tank 37 for anaerobically digesting gravity concentrated sludge and mechanical concentrated sludge, and sludge storage tank for temporarily storing non-dewaterable digested sludge 27 and a dehydrator 8 that separates sludge mixed with dewatering aid and digested sludge into solid and liquid.

なお、脱水助材を回収する汚泥を引き抜く位置は、最初沈殿池1あるいは最初沈殿池1の前後の流路等、重力濃縮槽35の前段であれば限定しない。また、脱水助材と消化汚泥を混合した汚泥に対し、必要に応じて高分子凝集剤を添加してもよい。脱水機8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。 The position for extracting the sludge for collecting the dewatering aid is not limited as long as it is the first stage of the gravity concentration tank 35 such as the first sedimentation tank 1 or the flow path before and after the first sedimentation tank 1. Moreover, you may add a polymer flocculent to the sludge which mixed the dehydration auxiliary material and digested sludge as needed. As the dehydrator 8, a known dehydrator such as a screw press, a belt press, or a centrifugal dehydrator can be used.

下水処理場には毎日24時間汚水の流入があるため、汚水を沈殿した汚泥を回収装置3に移送して汚泥中の脱水助材を回収する。予め定めた連続した所定期間CP内に回収する脱水助材の回収量を総回収量11とする。下水処理場への流入量は季節や曜日、天候によって変動し、汚泥に含まれる脱水助材の含有量も変動する。このような情報は汚泥情報26として過去情報も含めて処理場内で集積している。所定期間CPの初期数回の脱水助材の回収量の実測値や汚泥情報26から所定期間CP内に回収するであろう総回収量11を予測する。回収量の実測値を実回収量12、総回収量11の予測値を予測総回収量13とする。 Since sewage flows into the sewage treatment plant every day for 24 hours, the sludge precipitated with sewage is transferred to the recovery device 3 to recover the dewatering aid in the sludge. A collection amount of the dehydration aid collected within a predetermined continuous predetermined period CP is defined as a total collection amount 11. The amount of inflow to the sewage treatment plant varies depending on the season, day of the week, and weather, and the content of dewatering aid contained in the sludge also varies. Such information is accumulated as sludge information 26 in the treatment plant including past information. The total recovery amount 11 that will be recovered within the predetermined period CP is predicted from the measured value of the recovery amount of the dehydration aid several times during the predetermined period CP and the sludge information 26. The measured value of the collected amount is set as the actual collected amount 12, and the predicted value of the total collected amount 11 is set as the predicted total collected amount 13.

所定期間CP内に脱水助材を回収した後の残渣は、濃縮後、消化槽37に返送して嫌気性消化した後、脱水機8にて脱水処理する。ここで、下水処理場において脱水機8は毎日稼働しているわけではない。下水処理プロセスから発生する汚泥量に応じて脱水機8の稼働時間を随時決定している。汚泥量は変動するので、所定期間CPの初期の実測値や汚泥情報26から所定期間CP内に脱水処理するであろう総汚泥量23を予測する。汚泥量の実測値を実汚泥量24、総汚泥量23の予測値を予測総汚泥量25とする。一般的には予測総汚泥量25に応じて監視員が従事している予め定めた所定の日時のみ脱水機8を稼働している。 The residue after the dehydration aid has been collected within the predetermined period CP is concentrated, returned to the digestion tank 37 and subjected to anaerobic digestion, and then dehydrated by the dehydrator 8. Here, the dehydrator 8 is not operated every day in the sewage treatment plant. The operating time of the dehydrator 8 is determined as needed according to the amount of sludge generated from the sewage treatment process. Since the amount of sludge fluctuates, the total amount of sludge 23 that will be dehydrated within the predetermined period CP is predicted from the initial measured value of the predetermined period CP and the sludge information 26. The measured value of the sludge amount is the actual sludge amount 24, and the predicted value of the total sludge amount 23 is the predicted total sludge amount 25. In general, the dehydrator 8 is operated only at a predetermined date and time when a supervisor is engaged according to the predicted total sludge amount 25.

汚泥から抽出した脱水助材の貯留は必ず必要となるが、処理場内での配置やスペースを鑑みてできるだけ貯留容量を小さくすることが望ましい。そのため、下水処理プロセスで発生する汚泥から所定期間CPで分離回収する脱水助材の回収量と脱水機8で脱水処理する汚泥量を正確に予測し、脱水助材の貯留量29を一定以下に保持しつつ、総汚泥量23に応じて総回収量11を分配供給できるように供給量14を算出することが重要となる。 Although storage of the dewatering aid extracted from the sludge is indispensable, it is desirable to reduce the storage capacity as much as possible in view of the arrangement and space in the treatment plant. Therefore, the recovery amount of the dewatering aid separated and recovered from the sludge generated in the sewage treatment process in the predetermined period CP and the sludge amount dehydrated by the dehydrator 8 are accurately predicted, and the dewatering aid storage amount 29 is kept below a certain level. It is important to calculate the supply amount 14 so that the total recovery amount 11 can be distributed and supplied according to the total sludge amount 23 while being held.

下水汚泥から回収する脱水助材は植物性の繊維状物を主体とした難分解性有機物である。例えば汚水中に溶解したトイレットペーパーが難分解性有機物にあたる。また、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37で生成された消化汚泥や、OD法の反応タンク19で生成されたOD余剰汚泥等が難脱水汚泥にあたる。難分解性有機物を抽出した後の汚泥は主に易分解性有機物で構成されているが、食品残渣由来の易分解性有機物は腐敗しやすく長期間の保存はできないため、消化槽37に返送して嫌気性消化する。消化槽37では脱水助材の回収により難分解性有機物が減少しているので消化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。 The dewatering aid recovered from sewage sludge is a hardly decomposable organic substance mainly composed of plant-like fibrous materials. For example, toilet paper dissolved in sewage is a hardly decomposable organic substance. In addition, the hardly dewatered sludge is sludge whose fiber content which is a core of aggregation is greatly reduced by biological treatment or the like and the dewaterability is deteriorated. For example, digested sludge produced in the digestion tank 37, OD excess sludge produced in the reaction tank 19 of the OD method, and the like are hardly dewatered sludge. The sludge after extraction of the hard-to-decompose organic matter is mainly composed of easy-to-decompose organic matter, but the easy-to-decompose organic matter from the food residue is easily spoiled and cannot be stored for a long period of time. And anaerobic digestion. In the digestion tank 37, since the hardly decomposable organic substances are reduced due to the collection of the dehydration aid, the reaction period in the digestion process can be shortened, which contributes to the improvement of the treatment efficiency of the entire treatment plant.

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分が存在している。 Toilet paper does not dissolve even when dipped in water, and the fibers constituting the sheet form are only unwound and dispersed. Therefore, a large amount of fiber derived from toilet paper is present in the sewage sludge.

本発明では、汚泥中の繊維分を脱水助材として利用するため、下水処理場に流入した流入水中の繊維分を回収装置3で抽出している。回収した繊維分は、凝集前の難脱水汚泥等に添加し、凝集の核として機能させる。汚泥に対して適切な性状の脱水助材を添加すれば、強固な凝集フロックを形成し、脱水性が向上する。 In the present invention, since the fiber content in the sludge is used as a dehydration aid, the fiber content in the inflow water flowing into the sewage treatment plant is extracted by the recovery device 3. The recovered fiber is added to the hardly dehydrated sludge before agglomeration and functions as a nucleus of agglomeration. 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.

図2は本発明に係る回収装置以降のフロー図である。下水処理場に流入した汚水から沈殿分離された汚泥を引き抜いて回収装置3に移送する。回収装置3では汚泥中の難分解性有機物を選択的に分離し助材貯留槽4に排出する。助材貯留槽4回収されない易分解性有機物は回収装置3から重力濃縮槽35を介して消化槽37へ移送する。助材貯留槽4では重量計あるいはレベル計等の公知の計測装置15で脱水助材の回収量を計測する。回収した脱水助材の実回収量12の測定データは順次制御装置16に送信され、制御装置16にて所定期間CP内に回収すると予測される予測総回収量13を算出する。予測総回収量13は実回収量12の測定データが送信される度に補正をかけて修正される。 FIG. 2 is a flowchart after the collection device according to the present invention. The sludge precipitated and separated from the sewage flowing into the sewage treatment plant is drawn out and transferred to the recovery device 3. The recovery device 3 selectively separates the hardly decomposable organic matter in the sludge and discharges it to the auxiliary material storage tank 4. The easily decomposable organic matter that is not recovered in the auxiliary material storage tank 4 is transferred from the recovery device 3 to the digestion tank 37 via the gravity concentration tank 35. In the auxiliary material storage tank 4, the recovery amount of the dewatering auxiliary material is measured by a known measuring device 15 such as a weight meter or a level meter. The measurement data of the actual recovery amount 12 of the collected dewatering aid is sequentially transmitted to the control device 16, and the control device 16 calculates the predicted total recovery amount 13 predicted to be recovered within the predetermined period CP. The predicted total recovery amount 13 is corrected and corrected every time measurement data of the actual recovery amount 12 is transmitted.

消化汚泥は汚泥貯留槽27に一時的に貯留される。汚泥貯留槽27ではレベル計等の公知の計測装置28で汚泥量を計測する。貯留した実汚泥量24の測定データは順次制御装置16に送信され、制御装置16にて所定期間CP内に貯留すると予測される予測総汚泥量25を算出する。予測総汚泥量25は実汚泥量23の測定データが送信される度に補正をかけて修正される。なお、汚泥量を測定する計測装置28は、汚泥の移送管に配設してもよく、また、脱水機から排出される脱水ケーキから汚泥量を推測してもよい。 Digested sludge is temporarily stored in the sludge storage tank 27. In the sludge storage tank 27, the amount of sludge is measured by a known measuring device 28 such as a level meter. The stored measurement data of the actual sludge amount 24 is sequentially transmitted to the control device 16, and the control device 16 calculates a predicted total sludge amount 25 predicted to be stored within the predetermined period CP. The predicted total sludge amount 25 is corrected and corrected every time measurement data of the actual sludge amount 23 is transmitted. The measuring device 28 for measuring the amount of sludge may be disposed in the sludge transfer pipe, or the amount of sludge may be estimated from the dewatered cake discharged from the dehydrator 8 .

制御装置16では予測総回収量13と予測総汚泥量25に基づいて脱水助材の供給量14を算出する。算出された供給量14に応じて脱水助材の供給装置5を制御する。この時、助材貯留槽4への貯留量29は予め定めた範囲内に制限するように予め制御装置16にインプットしている。 The control device 16 calculates the dehydration aid supply amount 14 based on the predicted total recovery amount 13 and the predicted total sludge amount 25. The dehydration aid supply device 5 is controlled according to the calculated supply amount 14. At this time, the storage amount 29 in the auxiliary material storage tank 4 is input to the control device 16 in advance so as to be limited within a predetermined range.

脱水助材を供給装置5にて難脱水汚泥に供給する際に、希釈水17を注入すると脱水助材の移送が容易となる。 When the dehydration aid is supplied to the hardly dehydrated sludge by the supply device 5, if the dilution water 17 is injected, the dehydration aid is easily transferred.

図3は某下水処理場での脱水助材の回収データである。下水処理場には毎日24時間に亘って有機物を含有する汚水の流入があり、最初沈殿池1から予め定めた汚泥量を引き抜いて回収装置3に移送している。しかし、季節や日時により汚泥濃度が大きく異なり、特に、土、日曜日の休日は汚泥濃度が低く、固形物量が月〜金曜日の平日と比べて半減していることがわかる。したがって、難分解性有機物である繊維分を主とした脱水助材の回収量も減少している。 FIG. 3 shows the collection data of the dewatering aid at the sewage treatment plant. There is an inflow of sewage containing organic matter every day for 24 hours in the sewage treatment plant, and a predetermined amount of sludge is first extracted from the settling basin 1 and transferred to the recovery device 3. However, it can be seen that the sludge concentration varies greatly depending on the season and date and time, especially on Saturday and Sunday holidays, the sludge concentration is low, and the amount of solids is halved compared to the weekdays from Monday to Friday. Therefore, the recovery amount of the dehydration aid mainly composed of fiber, which is a hardly decomposable organic substance, is also decreasing.

本処理場では脱水助材に適さない易分解性有機物を消化槽37にて嫌気性消化した後、消化汚泥を脱水機8で脱水処理している。本処理場では、土、日曜日は流入量が少なく脱水機の稼働を最小限に抑えるため、消化槽37から消化汚泥を引き抜いていない。したがって、土、日曜日の発生消化汚泥量はデータ上0となっている。 In this treatment plant, an easily decomposable organic substance that is not suitable as a dehydration aid is anaerobically digested in the digestion tank 37, and then the digested sludge is dehydrated by the dehydrator 8. In this treatment plant, the digested sludge is not drawn out from the digestion tank 37 in order to minimize the amount of inflow on Saturday and Sunday so as to minimize the operation of the dehydrator. Therefore, the amount of digested sludge generated on Saturday and Sunday is 0 in the data.

本処理場では汚泥量と脱水機8の処理能力から、平日は各8時間のみの稼働で、休日は運転を停止している。所定期間CPに総汚泥量23に応じて均等に回収量11の脱水助材を供給できるように脱水助材の供給量14を算出する。本データでは1週間で回収した脱水助材の総回収量11を、その1週間で脱水処理する総汚泥量23に均等な添加率で供給するようにしている。 In this treatment plant, due to the amount of sludge and the processing capacity of the dehydrator 8, the operation is only 8 hours each on weekdays, and the operation is stopped on holidays. The supply amount 14 of the dewatering aid is calculated so that the total recovered amount 11 of the dewatering aid can be supplied uniformly in accordance with the total sludge amount 23 during the predetermined period CP. In this data, the total recovery amount 11 of the dewatering aid recovered in one week is supplied to the total sludge amount 23 to be dehydrated in that week at an equal addition rate.

<回収量>
本提案の実施例を図3のデータに沿って詳述する。脱水助材を回収する所定期間CPを以下のように設定した。
所定期間 :土曜日から翌週金曜日までの7日間
<Amount collected>
The proposed embodiment will be described in detail with reference to the data of FIG. A predetermined period CP for collecting the dehydration aid was set as follows.
Predetermined period: 7 days from Saturday to Friday

水処理プロセスで発生する汚泥について、下水処理場の最初沈殿池1から生汚泥を引き抜いて回収装置3に移送する。一定時間ごとに所定量を引き抜く作業を数回行ってもよいし、連続的に全量を引き抜いてもよい。 About the sludge generated in the water treatment process, the raw sludge is extracted from the first settling basin 1 of the sewage treatment plant and transferred to the recovery device 3. The operation of pulling out a predetermined amount every certain time may be performed several times, or the entire amount may be pulled out continuously.

回収された難分解性有機物は脱水助材として助材貯留槽4に貯留する。助材貯留槽4に貯留する脱水助材の回収量を公知の計測装置15でリアルタイムに計測し、実回収量12の測定データを制御装置16に送信する。助材貯留槽4には脱水助材の実回収量12に応じて希釈水17を注水してもよい。本実施例では、濃度が3%となるまで希釈水17を注水している。 The recovered hardly decomposable organic matter is stored in the auxiliary material storage tank 4 as a dehydrating auxiliary material. A recovery amount of the dewatering aid stored in the auxiliary material storage tank 4 is measured in real time by a known measuring device 15, and measurement data of the actual recovery amount 12 is transmitted to the control device 16. Diluent water 17 may be poured into the auxiliary material storage tank 4 in accordance with the actual recovery amount 12 of the dehydrating auxiliary material. In this embodiment, the dilution water 17 is poured until the concentration becomes 3%.

制御装置16では実回収量12と過去の測定情報や天候情報等の汚泥情報26も参考にして、所定期間CPに回収できる脱水助材の予測総回収量13を算出する。予測総回収量13を正確に予測するため、随時、実回収量12の測定データを制御装置16に送信し、制御装置16で予測総回収量13を補正しつつ算出する。 The control device 16 calculates the predicted total recovery amount 13 of the dewatering aid that can be recovered in the predetermined period CP with reference to the actual recovery amount 12 and the sludge information 26 such as past measurement information and weather information. In order to accurately predict the predicted total recovery amount 13, measurement data of the actual recovery amount 12 is transmitted to the control device 16 at any time, and the control device 16 calculates the predicted total recovery amount 13 while correcting it.

本実施例では脱水助材の回収を土曜日から開始する。図3に示すように、土、日曜日の休日は脱水助材の回収量が減少する。これは、本データを抽出した某下水処理場の流入域に多数のオフィス街があり、土、日曜日は一般のオフィスが休みでオフィス街からの汚泥流入量が減少するためである。逆に住宅街を中心とする流入域を持つ下水処理場は、土、日曜日に流入汚泥の濃度が高くなり、脱水助材の回収量が増加することが予測される。 In this embodiment, the collection of the dehydration aid is started from Saturday. As shown in FIG. 3, the amount of dewatering aid collected decreases on Saturday and Sunday holidays. This is because there are many office districts in the inflow area of the dredged sewage treatment plant from which this data was extracted, and the amount of sludge inflow from the office district is reduced on Saturdays and Sundays when ordinary offices are closed. Conversely, in sewage treatment plants with inflow areas centering on residential areas, the concentration of inflow sludge is expected to increase on Saturdays and Sundays, and the amount of dewatering aid recovered will increase.

回収装置3では引き抜いた汚泥中の難分解性有機物のみを分離回収して助材貯留槽4に貯留する。難分解性有機物を抽出した残渣(主に易分解性有機物)は、最初沈殿池1の後段に配している重力濃縮槽35を介して消化槽37に返送し、下水処理プロセスに従って嫌気性消化する。 In the recovery device 3, only the hardly decomposable organic matter in the extracted sludge is separated and recovered and stored in the auxiliary material storage tank 4. The residue (mainly easily decomposable organic matter) extracted from the hardly decomposable organic matter is returned to the digestion vessel 37 through the gravity concentration tank 35 disposed at the first stage of the settling basin 1 and anaerobic digestion according to the sewage treatment process. To do.

<汚泥量>
本実施例では、脱水する汚泥は汚泥貯留槽27に貯留している。汚泥貯留槽27に貯留されている汚泥量を公知の計測装置28でリアルタイムに計測し、実汚泥量24の測定データを制御装置16に送信する。
<Sludge volume>
In this embodiment, the sludge to be dewatered is stored in the sludge storage tank 27. The amount of sludge stored in the sludge storage tank 27 is measured in real time by a known measuring device 28, and the measurement data of the actual sludge amount 24 is transmitted to the control device 16.

制御装置16では実汚泥量24と過去の測定情報や天候情報等の汚泥情報26も参考にして、所定期間CPに発生する予測総汚泥量25を算出する。予測総汚泥量25を正確に予測するため、随時、実回収量12の測定データを制御装置16に送信し、制御装置16で予測総汚泥量25を補正しつつ算出する。 The control device 16 calculates the predicted total sludge amount 25 generated in the predetermined period CP with reference to the actual sludge amount 24 and the sludge information 26 such as past measurement information and weather information. In order to accurately predict the predicted total sludge amount 25, the measurement data of the actual recovery amount 12 is transmitted to the control device 16 as needed, and the control device 16 calculates the predicted total sludge amount 25 while correcting it.

回収量と同様に、土、日曜日の汚泥発生量が少ないので、月〜金曜日までの5日間のみ脱水機8にて脱水処理を行っている。脱水機8は連続的に脱水処理できるスクリュープレス18を用いている。 Similar to the recovered amount, the amount of sludge generation on the soil and Sunday is small, so the dehydrator 8 performs the dehydration process only for 5 days from Monday to Friday. The dehydrator 8 uses a screw press 18 that can be continuously dehydrated.

<供給量算出>
制御装置16で算出した予測総回収量13の脱水助材を、制御装置16で算出した予測総汚泥量25の汚泥に均等に分配供給するべく、制御装置16にて脱水助材の供給量14を算出する。本実施例では、脱水助材を回収する期間と汚泥を貯留する期間が完全に一致しているため、常に最新データの予測総回収量13と予測総汚泥量25を基に、脱水助材の供給量14を随時算出する。脱水助材の供給量14を算出後、制御装置16は脱水助材の供給装置5を調整して、所定の量だけ難脱水汚泥に混合する。
<Calculation of supply amount>
In order to evenly distribute and supply the dewatering aid of the predicted total recovery amount 13 calculated by the control device 16 to the sludge of the predicted total sludge amount 25 calculated by the control device 16, the supply amount 14 of the dehydration aid by the control device 16 Is calculated. In this embodiment, since the period for collecting the dewatering aid and the period for storing the sludge are completely the same, the dewatering aid is always based on the predicted total recovery amount 13 and the predicted total sludge amount 25 of the latest data. The supply amount 14 is calculated at any time. After calculating the dehydration aid supply amount 14, the control device 16 adjusts the dehydration aid supply device 5 to mix the dehydration aid supply device 5 with the predetermined amount of the hardly dehydrated sludge.

なお、所定期間CPに脱水処理する実汚泥量24に対して、実回収量12を均等に分配供給してもよい。
The actual recovered amount 12 may be evenly distributed and supplied to the actual sludge amount 24 to be dehydrated during the predetermined period CP.

下水処理場に流入する固形物量が増加すれば、そこから回収できる脱水助材の回収量も増加する。この時、脱水助材に適さない易分解性有機物も増加しているため、脱水機8で脱水処理すべき汚泥量も増加する。助材貯留槽4で回収する脱水助材の予測総回収量13は増加傾向となるが、脱水処理する予測総汚泥量25も増加傾向となり、脱水助材の供給量も増加する。したがって、助材貯留槽4の貯留量29は極端な貯留量増加がないため、助材貯留槽に大きなスペースは必要としない。 If the amount of solids flowing into the sewage treatment plant increases, the amount of dewatering aid that can be recovered from it also increases. At this time, since easily decomposable organic substances that are not suitable for the dewatering aid are also increasing, the amount of sludge to be dewatered by the dehydrator 8 is also increased. Although the predicted total recovery amount 13 of the dewatering aid collected in the auxiliary material storage tank 4 tends to increase, the predicted total sludge amount 25 to be dehydrated also tends to increase, and the supply amount of the dehydration aid also increases. Therefore, since the storage amount 29 of the auxiliary material storage tank 4 does not increase extremely, the auxiliary material storage tank does not require a large space.

逆に、下水処理場に流入する固形物量が減少すれば、そこから回収できる脱水助材の回収量も減少する。この時、脱水助材に適さない易分解性有機物も減少しているため、脱水機8で脱水処理すべき汚泥量も減少する。助材貯留槽4で回収する脱水助材の予測総回収量13は減少傾向となるが、脱水処理する予測総汚泥量25も減少傾向となり、脱水助材の供給量も減少する。したがって、助材貯留槽4の貯留量29は極端な貯留量減少がないため、脱水助材が不足して含水率が不安定な脱水処理となることがない。 Conversely, if the amount of solids flowing into the sewage treatment plant decreases, the amount of recovered dewatering aid that can be recovered therefrom also decreases. At this time, since easily decomposable organic substances that are not suitable as a dewatering aid have also decreased, the amount of sludge to be dewatered by the dehydrator 8 also decreases. Although the predicted total recovery amount 13 of the dewatering aid collected in the auxiliary material storage tank 4 tends to decrease, the predicted total sludge amount 25 to be dehydrated also tends to decrease, and the supply amount of the dehydration aid also decreases. Therefore, since the storage amount 29 of the auxiliary material storage tank 4 does not cause an extreme decrease in the storage amount, there is no shortage of dehydration auxiliary material and the dehydration process with an unstable moisture content is not caused.

図4は他の実施例1のフロー図であって、下水処理場に最初沈殿池を設置していない場合のフロー図である。具体的にはOD法やMBR(膜分離活性汚泥法)を採用した際の処理方法が該当する。処理場に流入する流入水は、反応タンク19に流入し微生物の作用により浄化される。流入水の一部は、反応タンク流入路から分岐した固液分離機21に導入されて、汚水中の懸濁物質を分離する。洗浄排水は回収装置3へ移送する。また、ろ過水は反応タンク19前段の流入側に返送する。回収装置3へ移送された懸濁物質等の排水からは、脱水助材が選択的に分離回収される。重力濃縮槽35は最終沈殿池20から移送される余剰汚泥と、回収装置3から返送される易分解性有機物等の残渣を濃縮する。重力濃縮槽35の上澄液は反応タンク19前段の流入側へ送られる。回収装置3で排出される残渣は反応タンク19へ返送してもよい。重力濃縮槽35で濃縮された難脱水性の余剰汚泥等は、回収装置3で回収した脱水助材を混合され、必要に応じて高分子凝集剤を添加して、脱水機8にて脱水処理を行う。
なお、MBRを採用した場合は、最終沈殿池20が不要となり、反応タンク19の上澄液を処理水として排出し、汚泥を重力濃縮槽35に移送する。
FIG. 4 is a flowchart of another embodiment 1, and is a flowchart when the first settling basin is not installed in the sewage treatment plant. Specifically, the treatment method when employing the OD method or MBR (membrane separation activated sludge method) is applicable. The inflow water flowing into the treatment plant flows into the reaction tank 19 and is purified by the action of microorganisms. A part of the inflow water is introduced into the solid-liquid separator 21 branched from the reaction tank inflow passage to separate suspended substances in the sewage. The washing waste water is transferred to the recovery device 3. The filtered water is returned to the inflow side of the front stage of the reaction tank 19. The dewatering aid is selectively separated and recovered from the wastewater such as suspended substances transferred to the recovery device 3. The gravity concentration tank 35 concentrates surplus sludge transferred from the final sedimentation tank 20 and residues such as easily decomposable organic substances returned from the recovery device 3. The supernatant liquid of the gravity concentration tank 35 is sent to the inflow side before the reaction tank 19. The residue discharged from the recovery device 3 may be returned to the reaction tank 19. The dewatering surplus sludge and the like concentrated in the gravity concentration tank 35 is mixed with the dewatering aid recovered by the recovery device 3, and if necessary, a polymer flocculant is added, and the dehydrator 8 performs the dewatering treatment. I do.
In addition, when MBR is employ | adopted, the final sedimentation tank 20 becomes unnecessary, the supernatant liquid of the reaction tank 19 is discharged | emitted as treated water, and sludge is transferred to the gravity concentration tank 35. FIG.

図5は他の実施例2のフロー図であって、最初沈殿池の生汚泥と最終沈殿池の余剰汚泥を混合した混合生汚泥を処理する際のフロー図である。具体的には図1の消化槽を除いたフローが該当する。一般的に、夜間は昼間よりも汚水の流入量が減少するため、最初沈殿池1から引き抜かれる汚泥の量が減少する。従って、最終沈殿池20から送られる余剰汚泥の割合が増えるため、混合汚泥は難脱水性となる。よって、混合生汚泥の脱水に本発明の脱水システムを採用することで脱水効率が向上する。
脱水助材に関するフローは図1と同様で、最初沈殿池1から引き抜いた生汚泥から回収装置3により脱水助材を抽出する。回収装置3から排出された易分解性有機物等の残渣は重力濃縮槽35に返送され、重力濃縮汚泥(生汚泥)および機械濃縮汚泥(余剰汚泥)を混合して脱水機8にて脱水処理される。脱水機8の前段で混合生汚泥に脱水助材を添加する。
FIG. 5 is a flowchart of another embodiment 2, and is a flowchart for processing mixed raw sludge obtained by mixing raw sludge from the first sedimentation basin and excess sludge from the final sedimentation basin. Specifically, the flow excluding the digester shown in FIG. In general, since the amount of inflow of sewage is reduced at night than in the daytime, the amount of sludge withdrawn from the settling basin 1 is reduced. Therefore, since the ratio of the excess sludge sent from the final sedimentation basin 20 increases, the mixed sludge becomes difficult to dehydrate. Therefore, the dewatering efficiency is improved by employing the dewatering system of the present invention for dewatering the mixed raw sludge.
The flow relating to the dewatering aid is the same as in FIG. 1, and the dewatering aid is extracted from the raw sludge drawn out from the settling basin 1 by the recovery device 3. Residues such as readily decomposable organic matter discharged from the recovery device 3 are returned to the gravity concentration tank 35 and mixed with gravity concentrated sludge (raw sludge) and mechanically concentrated sludge (excess sludge) and dehydrated by the dehydrator 8. The A dehydrating aid is added to the mixed raw sludge before the dehydrator 8.

本発明に係る下水汚泥の脱水方法及び脱水システムは下水処理場に流入した汚水を沈殿分離した汚泥から繊維分を脱水助材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材を調達できるものである。ランニングコストが低減するだけでなく、脱水助材の回収量を予測しながら予測発生汚泥量に応じて脱水助材を使用するので、脱水助材の貯留槽等、設備の小型化を図ることができる。
汚泥中の難分解性有機物を脱水助材として処理系内の汚泥処理に有効活用し、その処理系で発生する難脱水汚泥に添加するもので、安定した低含水率の脱水ケーキを生成できるとともに、脱水ケーキの処理が安価で容易となる環境配慮型の脱水方法及び脱水システムとなる。
The dewatering method and dewatering system for sewage sludge according to the present invention is to effectively utilize the fiber content as dewatering aid from sludge obtained by settling and separating sewage flowing into the sewage treatment plant. It can be done. Not only will running costs be reduced, but because the amount of dewatering aid is used while predicting the amount of dewatering aid that is predicted, it is possible to reduce the size of equipment such as the storage tank for dewatering aid. it can.
Effectively used for sludge treatment in sludge system as a dewatering aid, and added to the hardly dewatered sludge generated in the treatment system, and can produce a stable low moisture content dehydrated cake. Thus, an environment-friendly dewatering method and dewatering system that makes dewatering cake processing inexpensive and easy can be obtained.

3 回収装置
5 供給装置
8 脱水機
12 実回収量
13 予測総回収量
14 供給量
15,28 計測装置
16 制御装置
24 実汚泥量
25 予測総汚泥量
26 汚泥情報
CP 所定期間
3 Recovery device 5 Supply device 8 Dehydrator 12 Actual recovery amount 13 Predicted total recovery amount 14 Supply amount 15, 28 Measuring device 16 Control device 24 Actual sludge amount 25 Predicted total sludge amount 26 Sludge information CP Predetermined period

Claims (4)

下水処理場に流入した流入水中の繊維分を回収し、脱水助材として下水処理プロセスから生じる難脱水汚泥に供給して脱水機(8)で脱水処理する方法において、
予め定めた所定期間(CP)で、
脱水助材の実回収量(12)と、季節や曜日、天候によって変動する流入水中の脱水助材の含有量についての情報である汚泥情報(26)から脱水助材の予測総回収量(13)を推定すると共に、
下水処理場に流入する汚泥の実汚泥量(24)と汚泥情報(26)から脱水機(8)で脱水処理する予測総汚泥量(25)を推定し、
予測総汚泥量(25)に対して予測総回収量(13)を分配供給する
ことを特徴とする下水汚泥の脱水方法。
In the method of recovering the fiber content of the inflow water flowing into the sewage treatment plant, supplying it to the hardly dewatered sludge resulting from the sewage treatment process as a dehydration aid, and dehydrating with the dehydrator (8),
At a predetermined period (CP),
From the actual recovery amount of dewatering aid (12) and the sludge information (26), which is information about the content of the dewatering aid in the inflowing water that varies depending on the season, day of the week, and weather, the predicted total recovery amount of dewatering aid (13 )
Estimate the predicted total sludge amount (25) to be dewatered by the dehydrator (8) from the actual sludge amount (24) and sludge information (26) of the sludge flowing into the sewage treatment plant,
A dewatering method of sewage sludge, characterized by distributing and supplying a predicted total recovery amount (13) to a predicted total sludge amount (25).
下水処理場に流入した流入水中の繊維分を回収し、脱水助材として下水処理プロセスから生じる難脱水汚泥に供給して脱水機(8)で脱水処理するシステムにおいて、
脱水助材を回収する回収装置(3)と、
脱水助材の回収量を計測する計測装置(15)と、
脱水する汚泥量を計測する計測装置(28)と、
脱水助材を汚泥に供給する供給装置(5)と、
供給装置(5)の供給量(14)を調整する制御装置(16)と、を備え、
制御装置は、
予め設定した所定期間(CP)で、
脱水助材の実回収量(12)と、季節や曜日、天候によって変動する流入水中の脱水助材の含有量についての情報である汚泥情報(26)から、分離回収する脱水助材の予測総回収量(13)を算出し、
下水処理場に流入する汚泥の実汚泥量(24)と汚泥情報(26)から、所定の期間に脱水機(8)で脱水処理する予測総汚泥量(25)を算出し、
予測総汚泥量(25)に対して予測総回収量(13)を分配するための供給量(14)を、算出する
ことを特徴とする下水汚泥の脱水システム。
In the system that collects the fiber content of the inflow water flowing into the sewage treatment plant, supplies it to the hardly dewatered sludge resulting from the sewage treatment process as a dehydration aid, and dehydrates it with the dehydrator (8).
A recovery device (3) for recovering the dehydration aid;
A measuring device (15) for measuring the amount of dewatering aid recovered;
A measuring device (28) for measuring the amount of sludge to be dehydrated;
A supply device (5) for supplying dewatering aid to sludge;
A control device (16) for adjusting the supply amount (14) of the supply device (5),
The control device
In a predetermined period (CP) set in advance,
The total amount of dewatering aid to be separated and recovered from the actual amount of dewatering aid (12) and the sludge information (26), which is information about the content of dewatering aid in the influent that varies depending on the season, day of the week, and weather. Calculate the recovery amount (13)
From the actual sludge amount (24) of the sludge flowing into the sewage treatment plant and the sludge information (26), the predicted total sludge amount (25) to be dehydrated by the dehydrator (8) during a predetermined period is calculated.
A dewatering system for sewage sludge, characterized in that a supply amount (14) for distributing a predicted total recovered amount (13) to a predicted total sludge amount (25) is calculated.
前記制御装置は、
予測総汚泥量(25)に対して予測総回収量(13)を均等に分配するための供給量(14)を算出する
ことを特徴とする請求項2に記載の下水汚泥の脱水システム。
The controller is
The sewage sludge dewatering system according to claim 2, wherein a supply amount (14) for uniformly distributing the predicted total recovery amount (13) to the predicted total sludge amount (25) is calculated.
前記制御装置は、
実汚泥量(24)に対して実回収量(12)を均等に分配するための供給量(14)を算出する
ことを特徴とする請求項3に記載の下水汚泥の脱水システム。
The controller is
The sewage sludge dewatering system according to claim 3, wherein a supply amount (14) for evenly distributing the actual recovery amount (12) to the actual sludge amount (24) is calculated.
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CA2917488A CA2917488C (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
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
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CA2970289A CA2970289C (en) 2013-07-26 2014-06-20 Recovery device and recovery method for recovering specific material from sludge
EP16157337.3A EP3059015A1 (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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