JP2003080299A - Method of treating sludge - Google Patents

Method of treating sludge

Info

Publication number
JP2003080299A
JP2003080299A JP2001273087A JP2001273087A JP2003080299A JP 2003080299 A JP2003080299 A JP 2003080299A JP 2001273087 A JP2001273087 A JP 2001273087A JP 2001273087 A JP2001273087 A JP 2001273087A JP 2003080299 A JP2003080299 A JP 2003080299A
Authority
JP
Japan
Prior art keywords
sludge
wastewater
screen
sewage
fiber component
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP2001273087A
Other languages
Japanese (ja)
Inventor
Yoshio Nakayama
善雄 中山
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Hitachi Kiden Kogyo Ltd
Original Assignee
Hitachi Kiden Kogyo Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Hitachi Kiden Kogyo Ltd filed Critical Hitachi Kiden Kogyo Ltd
Priority to JP2001273087A priority Critical patent/JP2003080299A/en
Publication of JP2003080299A publication Critical patent/JP2003080299A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Abstract

PROBLEM TO BE SOLVED: To provide a method of treating sludge by which the load in a water treatment system for performing a biological treatment of organic sewage can be reduced, dehydration effect can be improved even if it is the surplus sludge difficult to dehydration and the volume of the surplus sludge can be reduced. SOLUTION: In the method of treating the sludge by separating the sludge produced in a treating vessel for the organic sewage and dehydrating the sludge, cellulosic fiber components are recovered from the sewage flowing into the treating vessel and the sludge is dehydrated by adding these fiber components to the sludge.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【発明の属する技術分野】本発明は、汚泥の処理方法に
関し、特に、有機性汚水を生物処理する水処理系での負
荷を軽減するとともに、脱水性の悪い余剰汚泥であって
も脱水効率を上げ、余剰汚泥を大幅に減容化することが
できる汚泥の処理方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a sludge treatment method, and more particularly, to reduce the load on a water treatment system for biologically treating organic wastewater and to improve the dehydration efficiency even with excess sludge having poor dehydration property. The present invention relates to a sludge treatment method that can raise and reduce the volume of surplus sludge significantly.

【0002】[0002]

【従来の技術】従来、下水等の有機性汚水を活性汚泥に
より生物処理する場合、図3に示すように、流入汚水を
まず沈砂池に導き、汚水中の砂、石などを重力沈降にて
除去した後、スクリーンにて有機物を含む夾雑物を除去
し、この後、最初沈殿池、反応タンク、最終沈殿池を経
て上澄水を消毒後放流する。一方、最終沈殿池で重力沈
降により分離された余剰汚泥は濃縮され、所定の含水率
になるよう脱水され、焼却、埋め立て、或いは緑農地利
用等により処分している。この下水処理場に流入する汚
水中には、浮遊物として10%程度のセルロース系の繊
維分(本明細書においてセルロースを含む)が含まれて
おり、この浮遊物は難分解性の繊維分であるとともに、
従来の有機物を含む夾雑物除去用のスクリーンでは除去
されないため、通常水処理系で常に汚泥に伴って移動
し、最終的には余剰汚泥として処分されている。
2. Description of the Related Art Conventionally, when biologically treating organic sewage such as sewage with activated sludge, as shown in FIG. 3, the influent sewage is first guided to a sand basin and sand, stones, etc. in the sewage are gravity settled. After the removal, impurities including organic substances are removed by a screen, and then the supernatant water is disinfected and discharged through the first settling tank, the reaction tank, and the final settling tank. On the other hand, the excess sludge separated by gravity settling in the final settling tank is concentrated and dehydrated to a predetermined water content, and then incinerated, landfilled, or disposed of by using green farmland. The wastewater flowing into the sewage treatment plant contains about 10% of cellulosic fiber components (including cellulose in the present specification) as suspended matter, and this suspended matter is a persistent fiber component. Along with
Since it is not removed by the conventional screen for removing contaminants containing organic matter, it is usually moved along with sludge in the water treatment system, and is finally disposed of as excess sludge.

【0003】[0003]

【発明が解決しようとする課題】ところで、水処理系で
最終的に回収した余剰汚泥は、通常は脱水機で脱水する
ことにより容積を減容するようにしているが、余剰汚泥
は脱水性が悪いために脱水効率が低く、その減容化にも
限度があるという問題があった。また、汚水中に含まれ
るセルロース系浮遊物の繊維分が難分解性であるため、
有機性汚水を活性汚泥により生物処理する水処理系で分
解処理するのが困難で、この水処理系での大きな負荷と
なっている。
The excess sludge finally recovered in the water treatment system is usually dehydrated by a dehydrator to reduce its volume. However, the excess sludge has a dewatering property. Since it was bad, the dehydration efficiency was low, and there was a problem that the volume reduction was limited. Also, since the fiber content of the cellulosic suspension contained in the wastewater is difficult to decompose,
It is difficult to decompose organic sewage in a water treatment system that biologically treats it with activated sludge, which is a heavy load on this water treatment system.

【0004】本発明は、上記従来の汚泥の処理方法が有
する問題点に鑑み、有機性汚水を生物処理する水処理系
での負荷を軽減するとともに、脱水性の悪い余剰汚泥で
あっても脱水効率を上げ、余剰汚泥を大幅に減容化する
ことができる汚泥の処理方法を提供することを目的とす
る。
In view of the problems of the above conventional sludge treatment methods, the present invention reduces the load on the water treatment system for biologically treating organic wastewater, and dehydrates even excess sludge having poor dehydration properties. An object of the present invention is to provide a sludge treatment method capable of increasing efficiency and significantly reducing the volume of excess sludge.

【0005】[0005]

【課題を解決するための手段】上記目的を達成するた
め、本発明の汚泥の処理方法は、有機性汚水の処理槽で
発生する汚泥を分離して脱水する汚泥の処理方法におい
て、処理槽に流入する汚水からセルロース系の繊維分を
回収するとともに、該繊維分を添加して汚泥を脱水する
ことを特徴とする。
In order to achieve the above object, the sludge treatment method of the present invention is a sludge treatment method in which sludge generated in a treatment tank of organic wastewater is separated and dehydrated. It is characterized by recovering a cellulosic fiber component from the inflowing wastewater and adding the fiber component to dehydrate the sludge.

【0006】この汚泥の処理方法は、汚水の処理槽に流
入する汚水からセルロース系の繊維分を回収するととも
に、該繊維分を添加して汚泥を脱水することから、有機
性汚水を生物処理する水処理系での負荷を軽減するとと
もに、脱水性の悪い余剰汚泥であっても脱水効率を上
げ、余剰汚泥を大幅に減容化することができる。
In this sludge treatment method, a cellulosic fiber component is recovered from the sewage flowing into the sewage treatment tank, and the fiber component is added to dehydrate the sludge, thereby biologically treating the organic sewage. It is possible to reduce the load on the water treatment system and increase the dehydration efficiency even for excess sludge having poor dehydration properties, and to significantly reduce the volume of the excess sludge.

【0007】この場合において、汚水中の繊維分の回収
を、目幅又は孔径が1〜2mmのスクリーンにより行う
ことができる。
In this case, the fibers in the waste water can be collected by using a screen having a mesh width or a hole diameter of 1 to 2 mm.

【0008】これにより、流入汚水中に含まれる繊維分
を、簡易な装置で確実に回収することができる。
This makes it possible to reliably collect the fiber component contained in the inflowing wastewater with a simple device.

【0009】[0009]

【発明の実施の形態】以下、本発明の汚泥の処理方法の
実施の形態を図面に基づいて説明する。
BEST MODE FOR CARRYING OUT THE INVENTION Embodiments of a sludge treatment method of the present invention will be described below with reference to the drawings.

【0010】図1に、本発明の汚泥の処理方法を含む水
処理工程のフローを示す。この水処理工程では、例え
ば、図1(a)に示すように、下水処理場に流入する汚
水Aを、まず沈砂池10に導入し、砂、石等を分離除去
した後、除塵機20を経て、本発明の繊維分回収装置X
を通過させ、汚水Aからセルロース系の繊維分を回収す
る。そして、汚水Aを最初沈殿池30から反応タンク4
0、最終沈殿池50へと順次導くようにし、この処理工
程を経て、処理後の上澄水Bを放流するとともに、水処
理工程で除去された汚泥C及び余剰汚泥Dを濃縮し、脱
水する。この場合、濃縮した汚泥C及び余剰汚泥Dに、
前記セルロース系の繊維分を添加して混合し、この繊維
分を添加した汚泥C及び余剰汚泥Dを汚泥脱水機70に
かけて脱水する。なお、脱水後の汚泥は、焼却、埋め立
て、或いは緑農地利用等により処分される。また、繊維
分回収装置Xの配設位置は、水処理工程前の最初沈殿池
30よりも前であればよく、例えば、図1(b)に示す
ように、沈砂池10の前段に配設することも可能であ
る。
FIG. 1 shows a flow of a water treatment process including the sludge treatment method of the present invention. In this water treatment process, for example, as shown in FIG. 1 (a), the wastewater A flowing into the sewage treatment plant is first introduced into the sand basin 10 to remove sand, stones, etc., and then the dust remover 20. After that, the fiber content recovery apparatus X of the present invention
And the cellulosic fibers are recovered from the wastewater A. Then, the wastewater A is first supplied from the settling tank 30 to the reaction tank 4
0, the sludge C and the excess sludge D removed in the water treatment step are concentrated and dehydrated, while the supernatant water B after the treatment is discharged through this treatment step. In this case, in the concentrated sludge C and the excess sludge D,
The cellulosic fiber components are added and mixed, and the sludge C and the excess sludge D to which the fiber components are added are dehydrated by a sludge dehydrator 70. The sludge after dehydration is disposed of by incineration, landfill, or use of green farmland. Further, the arrangement position of the fiber content collecting apparatus X may be before the first settling tank 30 before the water treatment step, and for example, as shown in FIG. It is also possible to do so.

【0011】一方、繊維分回収装置Xは、図2に示すよ
うに、目幅1〜2mmの金網を用いたエンドレス状のス
クリーン1で構成し、これを汚水中で循環するように構
成する。スクリーン1は、両端に配設したスプロケット
3,3間に張架し、駆動装置2で一方のスプロケット3
を駆動させることより循環移動するようにし、これによ
り、汚水中のセルロース系の繊維分をスクリーン面に付
着させて回収するようにする。
On the other hand, as shown in FIG. 2, the fiber-content collecting apparatus X is composed of an endless screen 1 using a wire net having a mesh width of 1 to 2 mm, which is circulated in dirty water. The screen 1 is stretched between sprockets 3 and 3 arranged at both ends, and one sprocket 3 is driven by a drive unit 2.
Is circulated by driving so that the cellulosic fiber components in the wastewater are attached to the screen surface and collected.

【0012】この場合、スプロケット3,3は、スクリ
ーン1の構成に合わせて、図示のように多角形とするこ
とも、或いは円形のドラム型とすることもでき、これに
より、スプロケット3を駆動することによって、スクリ
ーン1は予め定めた汚水中の位置で循環して運行され
る。なお、このスクリーン1の循環は、連続的であって
も、間欠的であってもよい。
In this case, the sprockets 3 and 3 may be polygonal as shown in the drawing or may be a circular drum type depending on the configuration of the screen 1, whereby the sprockets 3 are driven. As a result, the screen 1 is circulated and operated at a predetermined position in the dirty water. The screen 1 may be circulated continuously or intermittently.

【0013】また、スクリーン1の付着物の回収側に
は、トラフ4を配設し、スプロケット3の回転によりス
クリーン1がトラフ4方向に移送され、該スクリーン1
に付着していた付着物が自然に或いは強制的にスクリー
ン面より剥離されたとき、この剥離付着物がトラフ4内
に落下し、集積されるようにする。このスクリーン1の
付着物の剥離をより確実に行うため、トラフ4の近傍で
上方位置にスプレーノズル5とブラシ6とを配設する。
スプレーノズル5は、スクリーン1の復路側で、背面に
スクリーン面に向かって洗浄水が噴射されるように配設
し、ブラシ6はスクリーン1の復路側表面に接するよう
にし、該ブラシで剥離された付着物は、トラフ4内に落
下するようにする。なお、このブラシ6とスプレーノズ
ル5は何れか一方のみでもよく、また、ブラシ6は駆動
装置により回転させることにより回収効率を上げること
もできる。また、繊維分回収装置Xとして、本発明の実
施例では、目幅1〜2mmの金網からなるスクリーン1
を使用しているが、このスクリーン1は、孔径が1〜2
mmのパンチングメタル等によっても構成することがで
きる。
Further, a trough 4 is provided on the side of the screen 1 on which the deposits are collected, and the screen 1 is transferred in the direction of the trough 4 by the rotation of the sprocket 3 and the screen 1
When the adhered matter adhered to the surface is naturally or forcibly separated from the screen surface, the separated adhered matter falls into the trough 4 and is accumulated. In order to more surely remove the deposits on the screen 1, the spray nozzle 5 and the brush 6 are arranged in the upper position near the trough 4.
The spray nozzle 5 is arranged on the return path side of the screen 1 so that the cleaning water is sprayed toward the screen surface on the back surface, and the brush 6 is brought into contact with the return path side surface of the screen 1 and is separated by the brush. The attached matter should fall into the trough 4. It should be noted that only one of the brush 6 and the spray nozzle 5 may be provided, and the brush 6 may be rotated by a driving device to improve the collection efficiency. Further, as the fiber content collecting device X, in the embodiment of the present invention, the screen 1 made of a wire mesh having a mesh width of 1 to 2 mm.
This screen 1 has a hole diameter of 1-2.
It can also be configured by a punching metal of mm or the like.

【0014】次に、本発明の汚水中の繊維分の回収処理
システムを、図1に示す水処理工程に基づいて詳細に説
明する。下水処理場に流入する汚水A中には、有機物、
汚泥分とともにセルロース系の繊維分が含まれている。
この繊維分は、流入する汚水の種類にもよるが、一般的
には汚水中に約10%程度、難分解性の浮遊物として含
まれている。そこで、図1(a)に示すように、流入す
る汚水Aをまず沈砂池10に導入し、ここで汚水A中に
含まれる石、砂、缶、瓶などのある程度の重力のある無
機物を重力沈降等にて分離除去した後、この汚水を次に
除塵機20、例えば、バースクリーン等の除塵機にて汚
水中に浮遊する枯れ草、木切れ、動物の死骸、紙、合成
樹脂製品、その他の粗大物を掻き揚げて除去する。
Next, the system for recovering and treating the fiber components in wastewater of the present invention will be described in detail based on the water treatment process shown in FIG. In the wastewater A flowing into the sewage treatment plant, organic matter,
It contains cellulosic fibers as well as sludge.
This fiber content is generally contained in the wastewater as about 10% as a hardly degradable suspended matter, although it depends on the type of the wastewater flowing in. Therefore, as shown in FIG. 1 (a), the inflowing wastewater A is first introduced into the sand basin 10, and the inorganic substances such as stones, sand, cans, and bottles contained in the wastewater A are gravitated. After being separated and removed by sedimentation or the like, this sewage is then removed by a dust remover 20, for example, a dust remover such as a bar screen. Scrape and remove coarse material.

【0015】この除塵機20にて粗大物が除去された汚
水は、次に繊維分回収装置Xを通過する。この場合、前
段階で石、砂、缶、瓶などの無機質及び浮遊する有機物
を除去しているが、繊維分回収装置Xに流入する汚水中
には、除塵機20でも除去されなかったセルロース系の
繊維分が、約10%程度の難分解性の浮遊物として含ま
れている。この繊維分は難分解性であるため、汚泥分と
共に水処理系へ流入させると、水処理系に大きな負荷と
なる。そこで、本実施例では、水処理系への入口となる
位置、例えば、最初沈殿池30や沈砂池10などの水処
理系の前段で回収するようにする。この流入汚水中の繊
維分の回収は、図2に示す繊維分回収装置Xのエンドレ
ス状に構成したスクリーン1の濾面を循環させて行う。
汚水をこの繊維分回収装置Xを通過させることにより、
難分解性の浮遊物であるセルロース系の繊維分が汚水中
から除去される。このように、水処理系への入口部で、
予めセルロース系の繊維分を回収することにより、水処
理系の負荷の低減を図ることができる。
The wastewater from which coarse particles have been removed by the dust remover 20 then passes through the fiber content recovery device X. In this case, although the inorganic substances such as stones, sand, cans, and bottles and floating organic substances were removed in the previous stage, the sewage flowing into the fiber content recovery device X was not removed by the dust remover 20. Fiber content of about 10% is contained as a persistent decomposition material. Since this fiber component is difficult to decompose, when it is made to flow into the water treatment system together with the sludge component, a large load is placed on the water treatment system. Therefore, in this embodiment, the water is collected at a position that is an inlet to the water treatment system, for example, at a stage before the water treatment system such as the first settling basin 30 and the sand basin 10. The fiber component in the inflowing wastewater is collected by circulating the filter surface of the endless screen 1 of the fiber component collector X shown in FIG.
By passing sewage through this fiber content recovery device X,
A cellulosic fiber component, which is a persistent biodegradable matter, is removed from wastewater. Thus, at the entrance to the water treatment system,
By preliminarily recovering the cellulose-based fiber component, the load on the water treatment system can be reduced.

【0016】セルロース系の繊維分が除去された汚水A
は、従来と同じく水処理工程へ導かれる。この水処理工
程は、特に限定されるものではないが、最初沈殿池3
0、生物処理槽などの反応タンク40、最終沈殿池50
を経て順次処理し、処理後の上澄水Bを直接、或いは消
毒した後放流する。一方、最初沈殿池30で沈降除去さ
れた汚泥Cと、最終沈殿池50で沈降除去された余剰汚
泥Dとを合流させ、汚泥濃縮槽60にて脱水可能な程度
まで濃縮し、その後、汚泥脱水機70へ供給する。
Sewage A from which cellulosic fibers have been removed
Is led to the water treatment process as in the past. This water treatment process is not particularly limited, but the first settling tank 3
0, reaction tank 40 such as biological treatment tank, final settling tank 50
Then, the treated supernatant water B is discharged directly or after being sterilized. On the other hand, the sludge C that has been first settled and removed in the settling tank 30 and the excess sludge D that has been settled and removed in the final settling tank 50 are combined and concentrated in a sludge thickening tank 60 to a degree that allows dewatering, and then sludge dewatering To the machine 70.

【0017】しかし、汚泥濃縮槽60にて汚泥を濃縮
し、これを直接脱水するようにしても、余剰汚泥は脱水
性が悪く、脱水効率(減容化効率)にも限度があるもの
となっている。そこで、本実施例では、この濃縮された
余剰汚泥の脱水効率を向上させるために、水処理工程前
にて回収した繊維分を余剰汚泥に添加し、混合する。こ
の場合、回収した繊維分は、汚泥脱水機70にかける前
の調整汚泥中、又はそれより前段の余剰汚泥中に添加す
る。
However, even if the sludge is concentrated in the sludge thickening tank 60 and directly dehydrated, the excess sludge has a poor dewatering property and the dewatering efficiency (volume reduction efficiency) is limited. ing. Therefore, in this example, in order to improve the dewatering efficiency of the concentrated excess sludge, the fiber component recovered before the water treatment step is added to the excess sludge and mixed. In this case, the recovered fiber component is added to the adjusted sludge before being applied to the sludge dehydrator 70, or to the excess sludge in the preceding stage.

【0018】このように、余剰汚泥と回収した繊維分と
を混合した後、汚泥脱水機70へ供給し、ここで予め定
めた含水率になるまで脱水する。この場合、余剰汚泥に
繊維分が混合されているので、脱水効率が向上し効果的
に脱水されるとともに、容積も減容される。その後、脱
水した余剰汚泥は、焼却や埋め立てにより処分するか、
或いは緑農地にて肥料或いは土壌改良材として利用され
る。
As described above, after the excess sludge and the recovered fiber component are mixed, the excess sludge is supplied to the sludge dewatering machine 70 and dehydrated until the moisture content determined in advance is reached. In this case, since the fiber component is mixed with the excess sludge, the dehydration efficiency is improved, the water is effectively dehydrated, and the volume is reduced. After that, the dehydrated excess sludge should be disposed of by incineration or landfill,
Alternatively, it is used as fertilizer or soil conditioner in green farmland.

【0019】なお、繊維分の回収は、生物処理槽である
反応タンク40の負荷低減から考えると、反応タンク4
0より前の最初沈殿池30や沈砂池10などの水処理系
前段で回収するのが望ましい。また、小規模水処理施設
等においては、沈砂池もしくは沈砂槽後段に設けられる
微細目除塵機の後段で繊維分を回収するのが望ましい。
The recovery of the fiber component is considered in consideration of the reduction of the load on the reaction tank 40 which is a biological treatment tank.
It is desirable to collect the water in the former stage of the water treatment system such as the first settling tank 30 and the sand settling tank 10 before 0. In small-scale water treatment facilities, it is desirable to recover the fiber content after the fine dust remover installed at the rear of the sand basin or sand basin.

【0020】なお、余剰汚泥の脱水性に問題がない場合
は、回収した繊維分を搬送し、余剰汚泥の脱水性が悪い
別の処理場において同様に利用することが可能である。
If there is no problem with the dehydration property of the excess sludge, the recovered fiber component can be transported and used in another treatment plant where the dehydration property of the excess sludge is poor.

【0021】[0021]

【発明の効果】本発明の汚泥の処理方法によれば、汚水
の処理槽に流入する汚水からセルロース系の繊維分を回
収するとともに、該繊維分を添加して汚泥を脱水するこ
とから、有機性汚水を生物処理する水処理系での負荷を
軽減するとともに、脱水性の悪い余剰汚泥であっても脱
水効率を上げ、余剰汚泥を大幅に減容化することができ
る。
According to the sludge treatment method of the present invention, the cellulosic fiber component is recovered from the sewage flowing into the sewage treatment tank, and the fiber component is added to dehydrate the sludge. It is possible to reduce the load on the water treatment system that biologically treats sewage, and to improve the dehydration efficiency even for excess sludge with poor dehydration properties, and to significantly reduce the volume of the excess sludge.

【0022】また、汚水中の繊維分の回収を、目幅又は
孔径が1〜2mmのスクリーンにより行うことにより、
流入汚水中に含まれる繊維分を、簡易な装置で確実に回
収することができる。
By collecting the fiber component in the wastewater with a screen having a mesh width or a hole diameter of 1 to 2 mm,
The fiber component contained in the inflowing wastewater can be reliably recovered with a simple device.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明の汚泥の処理方法を含む汚水処理のフロ
ー図である。
FIG. 1 is a flow diagram of wastewater treatment including a sludge treatment method of the present invention.

【図2】繊維分回収装置の説明図である。FIG. 2 is an explanatory diagram of a fiber content recovery device.

【図3】従来の汚水処理のフロー図である。FIG. 3 is a flow chart of conventional wastewater treatment.

【符号の説明】[Explanation of symbols]

A 汚水 B 処理後の上澄水 C 最初沈殿池で沈降除去した汚泥 D 余剰汚泥 X 繊維分回収装置 1 スクリーン(繊維分回収装置) 2 駆動装置 3 スプロケット 4 トラフ 5 スプレーノズル 6 ブラシ 10 沈砂池 20 除塵機 30 最初沈殿池 40 反応タンク(生物処理槽) 50 最終沈殿池 60 汚泥濃縮槽 70 汚泥脱水機 A dirty water B Clear water after treatment C Sludge settled and removed in the first settling tank D surplus sludge X fiber recovery device 1 screen (fiber collection device) 2 drive 3 sprockets 4 troughs 5 spray nozzles 6 brushes 10 sand basin 20 dust remover 30 First settling tank 40 Reaction tank (biological treatment tank) 50 final settling tank 60 sludge thickening tank 70 Sludge dehydrator

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 有機性汚水の処理槽で発生する汚泥を分
離して脱水する汚泥の処理方法において、処理槽に流入
する汚水からセルロース系の繊維分を回収するととも
に、該繊維分を添加して汚泥を脱水することを特徴とす
る汚泥の処理方法。
1. A method for treating sludge in which sludge generated in a treatment tank for organic wastewater is separated and dehydrated, and a cellulosic fiber component is recovered from the wastewater flowing into the treatment tank and the fiber component is added. A method for treating sludge, which comprises dewatering the sludge.
【請求項2】 汚水中の繊維分の回収を、目幅又は孔径
が1〜2mmのスクリーンにより行うことを特徴とする
請求項1記載の汚泥の処理方法。
2. The sludge treatment method according to claim 1, wherein the fiber component in the wastewater is collected by a screen having a mesh width or a pore diameter of 1 to 2 mm.
JP2001273087A 2001-09-10 2001-09-10 Method of treating sludge Pending JP2003080299A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2001273087A JP2003080299A (en) 2001-09-10 2001-09-10 Method of treating sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2001273087A JP2003080299A (en) 2001-09-10 2001-09-10 Method of treating sludge

Publications (1)

Publication Number Publication Date
JP2003080299A true JP2003080299A (en) 2003-03-18

Family

ID=19098353

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2001273087A Pending JP2003080299A (en) 2001-09-10 2001-09-10 Method of treating sludge

Country Status (1)

Country Link
JP (1) JP2003080299A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2016140006A1 (en) * 2015-03-03 2016-09-09 株式会社日立製作所 Sludge volume reduction device and sewage treatment system comprising same
JP2016190188A (en) * 2015-03-31 2016-11-10 株式会社石垣 Sludge dehydration apparatus, and sludge dehydration method
JP2016190190A (en) * 2015-03-31 2016-11-10 株式会社石垣 Sludge treatment system and sludge treatment method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2016140006A1 (en) * 2015-03-03 2016-09-09 株式会社日立製作所 Sludge volume reduction device and sewage treatment system comprising same
JP2016190188A (en) * 2015-03-31 2016-11-10 株式会社石垣 Sludge dehydration apparatus, and sludge dehydration method
JP2016190190A (en) * 2015-03-31 2016-11-10 株式会社石垣 Sludge treatment system and sludge treatment method

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