JPS60220194A - Anaerobic treatment apparatus - Google Patents

Anaerobic treatment apparatus

Info

Publication number
JPS60220194A
JPS60220194A JP59078020A JP7802084A JPS60220194A JP S60220194 A JPS60220194 A JP S60220194A JP 59078020 A JP59078020 A JP 59078020A JP 7802084 A JP7802084 A JP 7802084A JP S60220194 A JPS60220194 A JP S60220194A
Authority
JP
Japan
Prior art keywords
reaction tank
sludge
anaerobic
pipe
gas
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
JP59078020A
Other languages
Japanese (ja)
Inventor
Mikio Kitagawa
幹夫 北川
Motoyuki Yoda
依田 元之
Atsushi Watanabe
敦 渡辺
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.)
Kurita Water Industries Ltd
Original Assignee
Kurita Water Industries 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 Kurita Water Industries Ltd filed Critical Kurita Water Industries Ltd
Priority to JP59078020A priority Critical patent/JPS60220194A/en
Publication of JPS60220194A publication Critical patent/JPS60220194A/en
Pending legal-status Critical Current

Links

Classifications

    • Y02W10/12

Abstract

PURPOSE:To make the titled apparatus compact and to perform the stable operation thereof for a long period of time, by providing a means, which floats and separates sludge by using the digestion gas of an anaerobic reaction tank, in said reaction tank provided above a reaction part. CONSTITUTION:Raw water enters a reaction tank 1 from an introducing pipe 2 and stayed in a sludge blanket 5 to receive anaerobic treatment and org. substances are gradually decomposed to digestion gas based on methane and carbon dioxide. The treated solution comes out from the sludge blanket 5 and gradually rises in the tank 1 to enter a separation chamber 6 while sludge contained in the solution is floated and separated by gas blown from an air diffusion pipe 9 to be converted to scum 15 which is, in turn, returned to the sludge blanket 5 through a bell mouth 12, a pipeline 11 and a pump 13. The treated water after separation is discharged from a pipe 3 and a part of the generated digestion gas is pressurized to be utilized as floating and separaing gas.

Description

【発明の詳細な説明】 [発明の利用分野] 本発明は嫌気性処理装置に係り、特に嫌気性反応槽処理
水中の汚泥を反応槽の消化ガスを用いて加圧浮上分離し
て嫌気性反応部に返送するように構成された嫌気性処理
装置に関するものである。
[Detailed Description of the Invention] [Field of Application of the Invention] The present invention relates to an anaerobic treatment device, and in particular, sludge in treated water of an anaerobic reaction tank is subjected to pressure flotation separation using the digestion gas of the reaction tank to perform an anaerobic reaction. The present invention relates to an anaerobic treatment device configured to be returned to the department.

[発明の背景] 嫌気性処理は、周知の如く、産業廃水、ド水汚泥などの
被処理液(以下原水という。)に含まれる有機物を嫌気
性細菌によって分解するものであり、原木中の有機物は
最終的にはメタン、二酸化炭素、アンモニア、硫化水素
などのカス(消化カス)に分解される。
[Background of the invention] As is well known, anaerobic treatment is a process in which organic matter contained in a liquid to be treated (hereinafter referred to as raw water), such as industrial wastewater or water sludge, is decomposed by anaerobic bacteria. Eventually, it is decomposed into scum (digested scum) such as methane, carbon dioxide, ammonia, and hydrogen sulfide.

この嫌気性処理を行なう嫌気性処理装置においては、嫌
気性反応槽中の汚泥量を十分なものとすることが安定し
た処理を行なう上に重要である。
In an anaerobic treatment apparatus that performs this anaerobic treatment, it is important to ensure a sufficient amount of sludge in the anaerobic reaction tank in order to perform stable treatment.

そこで反応槽の外に加圧浮上槽を設は嫌気性反応槽から
の流出混合液を加圧浮上分離処理し、分離した汚泥を反
応槽に返送しようとする提案がなされている。(例えば
特公昭55−17633、特公昭55−15279.) しかしながら加圧浮上分離槽を嫌気性反応槽と別に設け
るようにしたのでは、広い設置スペースを必要とすると
共に、放熱量が多くなり、嫌気性反応槽を適正な反応温
度に維持するための加熱費用も増加するようになる。
Therefore, a proposal has been made to install a pressurized flotation tank outside the reaction tank, perform pressure flotation separation on the mixed liquid flowing out from the anaerobic reaction tank, and return the separated sludge to the reaction tank. (For example, Japanese Patent Publication No. 55-17633, Japanese Patent Publication No. 55-15279.) However, if the pressurized flotation tank is installed separately from the anaerobic reaction tank, a large installation space is required, and the amount of heat dissipated increases. Heating costs for maintaining the anaerobic reaction tank at an appropriate reaction temperature also increase.

またスラ・ンジブランケット型反応槽においては、反応
槽内の汚泥が沈降性の良好なベレット又はフロ7クにな
ることが良好な運転を行なう上で重要であるが、このよ
うなペレフト化又はフロ。
In addition, in a sludge blanket type reactor, it is important for good operation that the sludge in the reactor be turned into pellets or flocs with good settling properties. .

り化させるに好適な条件は必ずしも明確ではなく、スラ
ッジブランケット型反応槽においては反応槽内の75泥
が分散状態となって汚泥の沈降が41分となり、汚泥が
系外に流出してしまうことがある。
The conditions suitable for sludge conversion are not necessarily clear, but in a sludge blanket type reaction tank, the 75 sludge in the reaction tank becomes dispersed, the sludge settles for 41 minutes, and the sludge flows out of the system. There is.

そこでスラッジブランケット型反応槽の処理水流出部に
ハニカムや波板などの充填材、又は傾斜板型の沈降分離
装置を設置し、汚泥の系外への流出を防止することが考
えられているが、このような充填材や沈降分離装置は汚
泥を単に捕捉するのみであり、長期間運転を行なうと充
填材や沈降分離装置が汚泥により閉塞する可能性がある
。さらに捕捉した汚泥を反応槽内に返送することが基本
的にできないため、反応槽内の7り泥量が減少すること
は避けられなかった。
Therefore, it has been considered to install a filler such as a honeycomb or corrugated plate, or an inclined plate type sedimentation separator at the treated water outflow part of the sludge blanket type reaction tank to prevent the sludge from flowing out of the system. However, such fillers and sedimentation separators only capture sludge, and if operated for a long period of time, there is a possibility that the fillers and sedimentation separators will become clogged with sludge. Furthermore, since it is basically impossible to return the captured sludge to the reaction tank, it was inevitable that the amount of sludge in the reaction tank would decrease.

[発明の目的] 本発明の目的は上記従来技術の問題点を解消し、装置が
コンパクトになり、かつ放熱量が少なく加熱コストも低
廉であると共に、長期間安定した運転を行なえる妖気性
処理装置を提供することにある。
[Objective of the Invention] The object of the present invention is to solve the problems of the above-mentioned conventional technology, and to provide a gas treatment which has a compact device, has a small amount of heat dissipated, has a low heating cost, and can operate stably for a long period of time. The goal is to provide equipment.

[発明の構成] この目的を達成するために、本発明は、反1心部よりも
上方の嫌気性反応槽内に反応槽の消化カスを用いて浮上
分離する手段を設け、反応槽の処理水のf”j泥をこの
浮上分離手段で分離して反応部に返送するようMIII
&シたものである。
[Structure of the Invention] In order to achieve this object, the present invention provides a means for flotation separation using digested waste of the reaction tank in the anaerobic reaction tank above the core part of the reaction tank, and performs treatment of the reaction tank. The f''j mud of the water is separated by this flotation separation means and sent back to the reaction section.
&shita thing.

[発明の実施例] 以下図面を参照して実施例について説明する。[Embodiments of the invention] Examples will be described below with reference to the drawings.

p、t、 1図は本発明の実施個装δの断面図である。Figures p, t, and 1 are cross-sectional views of the individual packaging δ according to the present invention.

1は嫌気性反応槽であり、底部には原水導入箔2が接続
され、上部には処理水排出管3が設置されている。この
反応槽lはスラッジブランケット型嫌気性反応槽であり
、反応槽l内部の液4の下部にはスラッジブランケット
5が形成されている。
1 is an anaerobic reaction tank, a raw water introduction foil 2 is connected to the bottom, and a treated water discharge pipe 3 is installed at the top. This reaction tank 1 is a sludge blanket type anaerobic reaction tank, and a sludge blanket 5 is formed below the liquid 4 inside the reaction tank 1.

而して反応槽l内の反応部(この実施例ではスラッジブ
ランケット5)よりも上方の部位には、加圧分離室6か
分離板7によって画成されている。
A pressurized separation chamber 6 or a separation plate 7 defines a region above the reaction section (in this embodiment, the sludge blanket 5) in the reaction tank 1.

この分IIn室6の天井部は閉しられ、消化カス抜出管
8が接続されている。また分離室6の底部は開放されて
おり、この底部には浮上分離用の微細な気泡を吹き出す
ための吹出管9が配設されている。
At this time, the ceiling of the IIn chamber 6 is closed, and the digested waste extraction pipe 8 is connected. The bottom of the separation chamber 6 is open, and a blowout pipe 9 for blowing out fine bubbles for flotation and separation is provided at the bottom.

この吹出管9へは、抜出管8で抜き出された消化ガスが
コンプレッサ10で加圧された後供給される。なお分離
室6は、その下部が液4に浸漬するよう設置されており
、これにより反応槽l内の液4は自然に分離室6の底部
開口を通って分離室6内に流入する。
Digestion gas extracted from the extraction pipe 8 is supplied to the blow-off pipe 9 after being pressurized by a compressor 10 . Note that the separation chamber 6 is installed so that its lower part is immersed in the liquid 4, so that the liquid 4 in the reaction tank 1 naturally flows into the separation chamber 6 through the bottom opening of the separation chamber 6.

図中11は、分離室6内で浮−上方階された115泥を
スラッジブランケット5に返送するためのポンプ13を
有する管路であり、その」一部には浮1−7り泥を集め
て吸い込むためのベルマウス12が取りけけられ、また
その−F部は反応槽lの1部に接続されている。
In the figure, reference numeral 11 denotes a pipe line having a pump 13 for returning the 115 sludge floating upward in the separation chamber 6 to the sludge blanket 5, and a part of the line 11 collects the floating sludge. A bell mouth 12 for suction is removed, and its -F portion is connected to a portion of the reaction tank 1.

図中14は、反応槽1内の液がスラッジ7テンケツト5
から直に排出管3へ流れ込むのを防」1するための流出
防止板であり、分離板7と反応槽l内壁面との間の流路
がスラッジブランケット5と短絡しない様反応槽l内壁
面がら中・D側に突設されている。
14 in the figure indicates that the liquid in the reaction tank 1 is sludge 7
This is an outflow prevention plate to prevent the sludge from flowing directly into the discharge pipe 3, and to prevent the flow path between the separation plate 7 and the inner wall surface of the reaction tank 1 from shorting with the sludge blanket 5. It protrudes from the center/D side.

このように構成された嫌気性処理装置において、原水は
導入管2がら反応槽1内に入り、スランシプランヶ・シ
ト5内に滞留して嫌気性処理され、原水中の有機物は次
第にメタンと炭酸カスとを主とする消化カスに分解され
てゆく。
In the anaerobic treatment device configured as described above, raw water enters the reaction tank 1 through the introduction pipe 2, stays in the slanship plan tank 5, and undergoes anaerobic treatment, and the organic matter in the raw water is gradually converted into methane and carbon dioxide. It is broken down into digestive scum, mainly consisting of

このスラッジブランケット5内で嫌気性処理された液は
スラ・ンジブランケット5がら出て反メε伯1内を徐々
に上昇し分離室6内に入る。そして蔽気管9から吹き込
まれたカスにより、分離室6内の液に含まれる汚泥は浮
上分離されスカム15となる。このスカム15は、ベル
マウス12、管路11、ポンプ13を経てスラッジブラ
ンケット5に返送される。
The liquid that has been anaerobically treated in the sludge blanket 5 comes out of the sludge blanket 5, gradually rises inside the tank 1, and enters the separation chamber 6. Then, the sludge contained in the liquid in the separation chamber 6 is floated and separated by the sludge blown from the air shield pipe 9 into scum 15. This scum 15 is returned to the sludge blanket 5 via a bell mouth 12, a pipe line 11, and a pump 13.

一方分離室6内で汚泥を分離された液は処理水となり、
分離室6の底部開口から抜は出し、分離板7と反応槽l
内壁面との間を通り、排出管3より排出される。
On the other hand, the liquid from which sludge is separated in the separation chamber 6 becomes treated water.
The extraction is taken out from the bottom opening of the separation chamber 6, and the separation plate 7 and the reaction tank l are removed.
It passes between the inner wall surface and is discharged from the discharge pipe 3.

なお反応槽1内の妹気性分解反応により発生したメタン
等のカスは抜出管8により抜き出され、その一部はコン
プレッサにて加圧され、上記の浮上分離用気体に用いら
れ、余剰のガスはカス排出管16から系外へ抜き出され
る。
Note that methane and other scum generated by the gaseous decomposition reaction in the reaction tank 1 is extracted by the extraction pipe 8, and a part of it is pressurized by a compressor and used as the above-mentioned flotation separation gas, and the surplus is The gas is extracted from the system through the waste discharge pipe 16.

このような嫌気性処理装置においては、浮上分離室6が
反応4al内に設けられているので、従来の如く浮上分
離層を反応槽の外部に別個に設けるようにした装置に比
へ、小型でコンパクトになると共に、浮上分離層からの
放熱もそれだけ少なくなるので、反応槽の加熱コストが
低廉になる。
In such an anaerobic treatment device, the flotation separation chamber 6 is provided inside the reaction chamber 4al, so it is smaller and smaller than the conventional device in which the flotation separation layer is provided separately outside the reaction tank. In addition to being more compact, the heat dissipated from the flotation separation layer is also reduced accordingly, so the heating cost of the reaction tank is reduced.

また浮上分離室6は、ハニカムや波板等の汚泥捕捉材と
異なり、汚泥による閉塞のおそれがなく、長時間安定し
て装置の運転が行なえる。
Furthermore, unlike sludge trapping materials such as honeycombs and corrugated plates, the flotation separation chamber 6 is free from the risk of clogging with sludge, allowing stable operation of the apparatus for a long period of time.

また沈降性の良好でない汚泥であっても、加圧浮上によ
り十分に分離されるので、系外に流出する汚泥量が低減
し、常時設定負荷で運転できる。
Furthermore, even if the sludge does not settle well, it is sufficiently separated by pressurized flotation, so the amount of sludge flowing out of the system is reduced, and the system can be operated at a constant load.

なお上記実施例では、消化カスを加圧して吹出管9から
吹き出すようにしているか、この消化カスを処理水に加
圧して解は込ませて加圧水とし、この加圧水を吹出管か
ら浮上分離室内に吹き出すようにしても良い。
In the above embodiment, either the digested scum is pressurized and blown out from the blow-off pipe 9, or the digested scum is pressurized and dissolved in the treated water to form pressurized water, and this pressurized water is sent from the blow-off pipe into the flotation separation chamber. You can also make it blow out.

なお吹出管の設置レベルは、装置容M等によっても変わ
るが、通常は水面下1〜2m程度とされる。また吹出管
から吹き出される消化ガスは、通常、2〜5 K g 
/ c m’程度に加圧されて吹き出される。(加圧水
を用いる場合も、通−9□、2〜5K g / c m
’程度に加圧する。)[発明の効果] 以上詳述した通り、本発明の妹気性処理装’Itは、反
応槽内部の上部に汚泥の浮上分離手段を設けるようにし
たものであり、コンノぐクトで設置スペースが少なくて
足りる。また放熱量も少なくカロ熱コストが低廉になる
。そして、長時間安定して設定負荷で運転することが可
能となる。
The installation level of the blow-off pipe varies depending on the equipment capacity M, etc., but is usually about 1 to 2 meters below the water surface. In addition, the digestive gas blown out from the blow-off pipe is usually 2 to 5 kg.
/ cm' and is blown out. (Even when using pressurized water, 2-9□, 2-5K g/cm
' Pressurize to a certain degree. ) [Effects of the Invention] As detailed above, the aqueous treatment system of the present invention is provided with a sludge flotation separation means in the upper part of the inside of the reaction tank, and the installation space is saved in the connoux. Less is more. In addition, the amount of heat dissipated is small, and the heating cost is low. Then, it becomes possible to operate stably at the set load for a long period of time.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は本発明の嫌気性処理装置の実施例装置の断面図
である。 l・・・嫌気性反応槽、 5・・争スラッジブランケット、 6・・・加圧分離室、 8・・φガス抜出管、 9・・・吹出管、 11・・・汚泥返送用管路。 代理人 弁理士 重 野 剛 第1図
FIG. 1 is a sectional view of an embodiment of the anaerobic treatment apparatus of the present invention. l...Anaerobic reaction tank, 5...Sludge blanket, 6...Pressure separation chamber, 8...φ gas extraction pipe, 9...Blowout pipe, 11...Sludge return pipe . Agent Patent Attorney Tsuyoshi Shigeno Figure 1

Claims (2)

【特許請求の範囲】[Claims] (1) 導入された原水を嫌気性処理する反応部を有す
る嫌気性反応槽と、該嫌気性反応槽の消化カスを用いて
反応槽処理液中の汚泥を浮上分離する加圧浮上分離手段
と、該加圧浮上分離手段で分離された汚泥を前記反応部
へ返送する手段と、を備えた嫌気性処理装置において、
前記加圧浮上分離手段を前記嫌気性反応槽内であってか
つl1ij記反応部よりも上方の部位に設けたことを特
徴とする嫌気性処理装置。
(1) An anaerobic reaction tank having a reaction section for anaerobically treating introduced raw water; and a pressurized flotation means for flotation-separating sludge in the reaction tank treatment liquid using digested waste from the anaerobic reaction tank. , means for returning the sludge separated by the pressure flotation means to the reaction section,
An anaerobic treatment apparatus characterized in that the pressure flotation separation means is provided in the anaerobic reaction tank and above the reaction section.
(2) 嫌気性反応槽はスラッジブランケット型鎌気性
反応槽であることを特徴とする特許請求の範囲第1項に
記載の嫌気性処理装置。
(2) The anaerobic treatment apparatus according to claim 1, wherein the anaerobic reaction tank is a sludge blanket type sickle reaction tank.
JP59078020A 1984-04-18 1984-04-18 Anaerobic treatment apparatus Pending JPS60220194A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59078020A JPS60220194A (en) 1984-04-18 1984-04-18 Anaerobic treatment apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59078020A JPS60220194A (en) 1984-04-18 1984-04-18 Anaerobic treatment apparatus

Publications (1)

Publication Number Publication Date
JPS60220194A true JPS60220194A (en) 1985-11-02

Family

ID=13650115

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59078020A Pending JPS60220194A (en) 1984-04-18 1984-04-18 Anaerobic treatment apparatus

Country Status (1)

Country Link
JP (1) JPS60220194A (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS639300U (en) * 1986-07-07 1988-01-21
WO1999051532A1 (en) * 1998-04-07 1999-10-14 Usf Deutschland Gmbh Method and device for anaerobic purification of waste water using the uasb method
WO2001002309A1 (en) * 1999-07-06 2001-01-11 Usf Deutschland Gmbh Method and device for the purification of wastewaters
WO2007068446A1 (en) * 2005-12-14 2007-06-21 Röhren- und Pumpenwerk Bauer Gesellschaft m.b.H. Plant and process for generating biogas from biodegradable material containing liquid and solid components, in particular waste products, and also biogas generation container for use in the plant
US7993521B2 (en) 2005-12-14 2011-08-09 Dietrich Eichler Plant and method for generating biogas from biologically degradable material containing liquid and solid components, in particular waste products, and a biogas generation container for use in the plant
CN102616930A (en) * 2012-04-19 2012-08-01 徐富 Methane air floating anaerobic reactor
CN103043778A (en) * 2013-01-10 2013-04-17 浙江大学 Bioreactor based on automatic float sludge breaking and circulation

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS639300U (en) * 1986-07-07 1988-01-21
JPH0434960Y2 (en) * 1986-07-07 1992-08-19
WO1999051532A1 (en) * 1998-04-07 1999-10-14 Usf Deutschland Gmbh Method and device for anaerobic purification of waste water using the uasb method
US6478963B1 (en) 1998-04-07 2002-11-12 Usf Deuthschland Gmbh Gutling Method and device for anaerobic purification of waste water using the UASB method
WO2001002309A1 (en) * 1999-07-06 2001-01-11 Usf Deutschland Gmbh Method and device for the purification of wastewaters
US6602416B1 (en) 1999-07-06 2003-08-05 Usf Deutschland Gmbh Method and a device for the purification of waste waters
WO2007068446A1 (en) * 2005-12-14 2007-06-21 Röhren- und Pumpenwerk Bauer Gesellschaft m.b.H. Plant and process for generating biogas from biodegradable material containing liquid and solid components, in particular waste products, and also biogas generation container for use in the plant
US7993521B2 (en) 2005-12-14 2011-08-09 Dietrich Eichler Plant and method for generating biogas from biologically degradable material containing liquid and solid components, in particular waste products, and a biogas generation container for use in the plant
CN102616930A (en) * 2012-04-19 2012-08-01 徐富 Methane air floating anaerobic reactor
CN103043778A (en) * 2013-01-10 2013-04-17 浙江大学 Bioreactor based on automatic float sludge breaking and circulation

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