JPH0149559B2 - - Google Patents

Info

Publication number
JPH0149559B2
JPH0149559B2 JP61127714A JP12771486A JPH0149559B2 JP H0149559 B2 JPH0149559 B2 JP H0149559B2 JP 61127714 A JP61127714 A JP 61127714A JP 12771486 A JP12771486 A JP 12771486A JP H0149559 B2 JPH0149559 B2 JP H0149559B2
Authority
JP
Japan
Prior art keywords
partition plate
reactor
gas lift
anaerobic biological
separation mechanism
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.)
Expired
Application number
JP61127714A
Other languages
Japanese (ja)
Other versions
JPS62282691A (en
Inventor
Nobuo Araki
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.)
Sanki Engineering Co Ltd
Original Assignee
Sanki Engineering Co 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 Sanki Engineering Co Ltd filed Critical Sanki Engineering Co Ltd
Priority to JP61127714A priority Critical patent/JPS62282691A/en
Publication of JPS62282691A publication Critical patent/JPS62282691A/en
Publication of JPH0149559B2 publication Critical patent/JPH0149559B2/ja
Granted 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
    • 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
    • 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

Landscapes

  • Treatment Of Sludge (AREA)
  • Biological Treatment Of Waste Water (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、嫌気性微生物の高濃度培養を目的と
した上向流型付着生物膜反応装置の改良に関する
ものである。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to an improvement in an upflow type adherent biofilm reaction device for the purpose of culturing anaerobic microorganisms at high concentrations.

〔従来の技術〕[Conventional technology]

従来、嫌気性生物膜反応器は、例えば『用水と
廃水』(Vol.24 No.2(1982)の『嫌気性処理の最
近の動向()』(P.43〜P.55、稲森悠平氏、須藤
隆一氏)及び『用水と廃水』(Vol.25 No.10
(1983)の『有機性排水の嫌気性処理の現状と今
後の動向』(P.3〜P.21、稲森悠平氏、須藤隆一
氏)に於て開示される如く、生物膜を形成させる
ことによつて廃水の水理学的滞留時間(HRT)
と汚泥滞留時間(SRT)を独立させたものであ
り、その結果、短HRTに於ても反応器内の生物
濃度を高く維持することができ、高容積負荷の許
容を可能にするものである。
Conventionally, anaerobic biofilm reactors have been used, for example, in "Recent Trends in Anaerobic Treatment ()" (P.43-P.55, Yuhei Inamori, "Water and Wastewater" (Vol. 24 No. 2 (1982)). , Ryuichi Sudo) and “Water and Wastewater” (Vol.25 No.10)
(1983), “Current status and future trends of anaerobic treatment of organic wastewater” (P.3-P.21, Yuhei Inamori, Ryuichi Sudo), forming a biofilm. Hydraulic Residence Time (HRT) of Wastewater by
and sludge retention time (SRT), and as a result, it is possible to maintain a high biological concentration in the reactor even at short HRT, making it possible to tolerate high volume loads. .

この反応器は、内部上方に代謝ガス、汚泥と処
理水を分離する固気液分離器が設置されている。
This reactor has a solid-gas-liquid separator installed above the interior to separate metabolic gas, sludge, and treated water.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

然し、このような反応装置は、嫌気性生物の増
殖速度が小さい上に生物膜の形成が必要なことか
ら、3〜9ケ月の長期間を必要とする欠点を持つ
ている。嫌気性生物、特にメタン菌に関しては、
生物膜を形成する際に重要な役割を果たすと考え
られる細胞外粘着物質の分泌が極めて少なく、生
物膜の形成を遅らせる原因になつている。
However, such a reactor has the disadvantage that it requires a long period of 3 to 9 months because the growth rate of anaerobic organisms is slow and biofilm formation is required. Regarding anaerobic organisms, especially methane bacteria,
The secretion of extracellular adhesive substances, which are thought to play an important role in biofilm formation, is extremely low, which is the cause of the delay in biofilm formation.

従つて、嫌気性菌が担体に付着していなかつた
り、自己集塊化していない場合には、これら細菌
から汚泥フロツクは、上向流速や代謝ガスの上昇
によつて汚泥が容易に浮揚し、流出することにな
る。それを防止するために、汚泥分離器が取り付
けられるか、清澄ゾーンを設けただけでは沈降し
た汚泥を反応器内に戻す部分が上向流となる構造
であるために汚泥が分離器内に対流し、反応器内
に効率良く循環されないものである。
Therefore, if anaerobic bacteria are not attached to the carrier or self-agglomerated, sludge flocs from these bacteria will be easily floated by the upward flow rate and increase in metabolic gas. It will leak out. In order to prevent this, a sludge separator is installed, or if only a clarification zone is installed, the part where the settled sludge is returned to the reactor has an upward flow, so the sludge flows into the separator by convection. However, it is not efficiently circulated within the reactor.

〔発明の目的〕[Purpose of the invention]

本発明は斯かる従来の問題点を解決するために
為されたもので、その目的は、代謝ガスの上昇及
び上向流速に伴つて浮揚する汚泥の反応器外への
流出を防止して反応部分に効率良く循環させるこ
とにある。
The present invention was made in order to solve such conventional problems, and its purpose is to prevent the sludge that floats due to the rise in metabolic gas and the upward flow rate from flowing out of the reactor, thereby preventing the reaction from occurring. The purpose is to efficiently circulate the parts.

〔問題点を解決するための手段〕[Means for solving problems]

本発明に係る嫌気性生物反応装置に於ける沈降
分離機構は、上向流型付着生物膜反応装置の上部
に、傾斜する仕切板を配し、仕切板の上部にガス
リフトチユーブを形成すると共に、仕切板の側部
に重力沈降槽を形成し、且つ仕切板の下部に沈降
する汚泥を流下させる開口部を設けたものであ
る。
The sedimentation separation mechanism in the anaerobic bioreactor according to the present invention includes an inclined partition plate arranged at the top of the upflow type attached biofilm reaction device, a gas lift tube formed at the top of the partition plate, and A gravity settling tank is formed on the side of the partition plate, and an opening is provided at the bottom of the partition plate to allow the settled sludge to flow down.

〔発明の作用〕[Action of the invention]

本発明に於ては、反応部分から代謝ガス及び上
向流速によつて上昇して来た汚泥フロツクは、仕
切板に沿つて浮揚してガスリフトチユーブを通つ
て清澄ゾーンに流入し、ガスリフトチユーブ内で
発生した乱流が汚泥フロツクに付着したガス泡を
分離すると共に、ガスから分離された汚泥フロツ
クは清澄ゾーンで重力沈降する。そして、仕切板
に沿つて沈降して来た汚泥は、ガスリフトチユー
ブにガス泡を含む汚泥混合液が上昇通過すること
によつて発生する清澄ゾーン内の緩やかな循環流
によつて、仕切板の下部を通つて再度反応部分に
戻される。
In the present invention, the sludge flocs that have risen from the reaction section due to metabolic gas and upward flow velocity are floated along the partition plate, flow into the clarification zone through the gas lift tube, and flow into the gas lift tube. The generated turbulence separates the gas bubbles attached to the sludge flocs, and the sludge flocs separated from the gas settle by gravity in the clarification zone. The sludge that has settled along the partition plate is removed by the gentle circulation flow in the clarification zone that is generated when the sludge mixture containing gas bubbles rises and passes through the gas lift tube. It passes through the lower part and returns to the reaction section again.

〔発明の実施例〕[Embodiments of the invention]

以下、本発明の実施例を図面に基づいて説明す
る。
Embodiments of the present invention will be described below based on the drawings.

第1図は本発明の第一実施例を示す。 FIG. 1 shows a first embodiment of the invention.

図に於て、1は上向流型付着生物膜反応器で、
下部には公知の反応器2が形成され、上部に汚泥
沈降機構3が設けられている。
In the figure, 1 is an upflow type attached biofilm reactor,
A known reactor 2 is formed in the lower part, and a sludge settling mechanism 3 is provided in the upper part.

汚泥沈降機構3は、略ハ字状に対向して配され
ている一対の仕切板4,4と、仕切板4の上部に
対向して連接して形成される一対のガスリフトチ
ユーブ5,5と、ガスリフトチユーブ5,5の上
部に位置し、ガスリフトチユーブ5,5よりも広
幅になるように対向して配される一対の板体7,
7によつて構成される清澄ゾーン6と、仕切板4
の側部に形成される重力沈降槽8と、この重力沈
降槽8の上方の流出口9に配設される多数の傾斜
板10と、重力沈降槽8の下部に位置し、仕切板
4の下部と反応器1との間に形成される汚泥戻り
用開口部11とによつて構成されている。
The sludge settling mechanism 3 includes a pair of partition plates 4, 4 which are disposed opposite each other in a substantially V-shape, and a pair of gas lift tubes 5, 5 which are formed in opposition to and connected to the upper part of the partition plate 4. , a pair of plates 7 located above the gas lift tubes 5, 5 and arranged facing each other so as to be wider than the gas lift tubes 5, 5;
A clearing zone 6 constituted by 7 and a partition plate 4
a gravity settling tank 8 formed on the side of the gravity settling tank 8; a large number of inclined plates 10 disposed at the outlet 9 above the gravity settling tank 8; It is constituted by a sludge return opening 11 formed between the lower part and the reactor 1.

又、汚泥沈降機構3の上方には、公知の上向流
型付着生物膜反応装置と同様にガス溜り12と処
理水受け13とが設けてある。そして、ガス溜り
12では生成されたメタンガスが収容され、処理
水受け13では清澄ゾーン6及び多数の傾斜板1
0を通つて来た処理水が流出口9から流出するよ
うになつている。
Further, above the sludge settling mechanism 3, a gas reservoir 12 and a treated water receiver 13 are provided, similar to the known upward flow type attached biofilm reaction device. The generated methane gas is stored in the gas reservoir 12, and the treated water receiver 13 has a clarification zone 6 and a large number of inclined plates 1.
The treated water that has passed through the outlet 9 flows out from the outlet 9.

次に、上述のように構成された本実施例の作用
を説明する。
Next, the operation of this embodiment configured as described above will be explained.

反応器2から矢印Aで示すように代謝ガスの上
昇やガス泡が付着してから浮揚する汚泥フロツク
は、仕切板4,4に沿つて上昇し、ガスリフトチ
ユーブ5,5を介して清澄ゾーン6に流入する。
そして、ガスリフトチユーブ5,5内で発生する
乱流が、汚泥フロツクに付着したガス泡を分離す
る。ガスから分離された混合液中の汚泥フロツク
は、清澄ゾーン6で重力沈降する。
As shown by the arrow A from the reactor 2, the sludge flocs that float after the rise of metabolic gas and the adhesion of gas bubbles rise along the partition plates 4, 4, and pass through the gas lift tubes 5, 5 to the clarification zone 6. flows into.
The turbulent flow generated within the gas lift tubes 5, 5 separates the gas bubbles adhering to the sludge floes. The sludge flocs in the mixed liquor separated from the gas settle by gravity in the clarification zone 6.

清澄ゾーン6から沈降する汚泥フロツクは、ガ
スリフトチユーブ5,5にガス泡を含む混合液が
上昇通過することによつて発生する循環流れによ
る下向流に伴われて重力沈降槽8を仕切板4,4
に沿つて沈降する。又、清澄ゾーン6から沈降す
る汚泥フロツクの内の重力沈降の遅い微細なフロ
ツクは、流出口9部分に設けられた多数の傾斜板
10によつて流出を阻止されて重力沈降槽8に案
内される。
The sludge flocs settling from the clarification zone 6 are moved through the gravity settling tank 8 by the downward flow caused by the circulating flow generated by the upward passage of the mixed liquid containing gas bubbles through the gas lift tubes 5, 5. ,4
It settles along. Further, among the sludge flocs settling from the clarification zone 6, fine flocs that settle slowly due to gravity are prevented from flowing out by a large number of inclined plates 10 provided at the outlet 9, and are guided to the gravity settling tank 8. Ru.

斯くして、仕切板4,4の下部に沈降して来た
汚泥フロツクは、清澄ゾーン6内に生じた緩い循
環流れによつて矢印Bで示すように仕切板4と反
応器1の壁面との間11から反応器2に押し戻さ
れる。
In this way, the sludge flocs that have settled at the bottom of the partition plates 4, 4 are moved between the partition plate 4 and the wall surface of the reactor 1 as shown by arrow B due to the slow circulation flow generated in the clarification zone 6. It is pushed back into the reactor 2 from the interval 11.

多数の傾斜板10を設けた流出口9からは、処
理水が流出して処理水受け13から反応器1外に
排出される。又、清澄ゾーン6で分離されたメタ
ンガスは、ガス溜り12内に貯えられ、ラインを
介して燃料等として利用される。
The treated water flows out from the outlet 9 provided with a large number of inclined plates 10 and is discharged to the outside of the reactor 1 from the treated water receiver 13. The methane gas separated in the clarification zone 6 is stored in a gas reservoir 12 and is used as fuel or the like via a line.

尚、上記実施例では、1組の仕切板4,4とガ
スリフトチユーブ5,5を用いた場合について説
明したが、例えば第2図に示すように2組の仕切
板4,4とガスリフトチユーブ5,5を設けたも
のであつても良い。又、仕切板4及びガスリフト
チユーブ5は、例えば第3図に示すように一個で
あつても良い。更に、本発明に於ては、上向流型
付着生物膜反応装置の形式は、膨脹床法又は濾床
法の何れでも良い。
In the above embodiment, a case was explained in which one set of partition plates 4, 4 and gas lift tubes 5, 5 were used, but for example, as shown in FIG. 2, two sets of partition plates 4, 4 and gas lift tube 5 were used. , 5 may be provided. Further, the partition plate 4 and the gas lift tube 5 may be one piece as shown in FIG. 3, for example. Furthermore, in the present invention, the upflow type attached biofilm reaction apparatus may be of either an expanded bed method or a filter bed method.

〔発明の効果〕〔Effect of the invention〕

以上のように本発明は、傾斜する仕切板を上向
流型付着生物膜反応装置の上方に配し、仕切板の
上部にガスリフトチユーブを形成すると共にその
上部に清澄ゾーンを形成し、仕切板の側部に重力
沈降槽を形成し、且つ仕切板の下部に沈降する汚
泥を流下させる開口部を設けたものであるから、
代謝ガス又は上向流れによつて上昇して来た汚泥
フロツクを、清澄ゾーンに於てガスと汚泥とに効
率良く分離し、汚泥フロツクを循環流れによつて
重力沈降させて再び反応器に戻すことが可能とな
る。
As described above, the present invention arranges an inclined partition plate above an upflow type attached biofilm reaction device, forms a gas lift tube in the upper part of the partition plate, and forms a clarification zone in the upper part of the partition plate. A gravity settling tank is formed on the side of the partition plate, and an opening is provided at the bottom of the partition plate to allow the settling sludge to flow down.
The sludge flocs that have risen due to metabolic gases or upward flow are efficiently separated into gas and sludge in the clarification zone, and the sludge flocs are gravity-sedimented by the circulating flow and returned to the reactor. becomes possible.

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

第1図は本発明の第一実施例を示す要部断面
図、第2図は本発明の第二実施例を示す一部切欠
き斜視図、第3図は本発明の第三実施例を示す要
部断面図である。 1……上向流型付着生物膜反応器、2……反応
器、3……汚泥沈降機構、4……仕切板、5……
ガスリフトチユーブ、6……清澄ゾーン、7……
板体、8……重力沈降槽、9……流出口、10…
…傾斜板、11……開口部、12……ガス溜り、
13……処理水受け。
Fig. 1 is a cross-sectional view of a main part showing a first embodiment of the invention, Fig. 2 is a partially cutaway perspective view showing a second embodiment of the invention, and Fig. 3 is a sectional view of a third embodiment of the invention. FIG. DESCRIPTION OF SYMBOLS 1... Upflow type attached biofilm reactor, 2... Reactor, 3... Sludge settling mechanism, 4... Partition plate, 5...
Gas lift tube, 6... Clarification zone, 7...
Plate body, 8... Gravity settling tank, 9... Outlet, 10...
... inclined plate, 11 ... opening, 12 ... gas reservoir,
13... Treated water receiver.

Claims (1)

【特許請求の範囲】 1 上向流型付着生物膜反応装置の上部に、清澄
ゾーン、ガス溜り及び処理水受けを設けた嫌気性
生物反応装置に於て、傾斜する仕切板を上向流型
付着生物膜反応装置の上方に配し、仕切板の上部
にガスリフトチユーブを形成すると共にその上部
に清澄ゾーンを形成し、仕切板の側部に重力沈降
槽を形成し、且つ仕切板の下部に沈降する汚泥を
流下させる開口部を設けたことを特徴とする嫌気
性生物反応装置に於ける沈降分離機構。 2 仕切板は、一対の板体を略ハ字状に対向して
配されていることを特徴とする特許請求の範囲第
1項記載の嫌気性生物反応装置に於ける沈降分離
機構。 3 ガスリフトチユーブは、一対の板体を仕切板
の上部に対向して連接されていることを特徴とす
る特許請求の範囲第1項記載の嫌気性生物反応装
置に於ける沈降分離機構。 4 ガスリフトチユーブの上部に形成した清澄ゾ
ーンは、ガスリフトチユーブよりも広幅に成るよ
うに一対の板体を対向して配して構成されている
ことを特徴とする特許請求の範囲第1項記載の嫌
気性生物反応装置に於ける沈降分離機構。 5 重力沈降槽の上方には、多数の傾斜板が配設
されて、重力沈降分離されない微細なフロツク等
が反応器外に流出しないように構成されているこ
とを特徴とする特許請求の範囲第1項記載の嫌気
性生物反応装置に於ける沈降分離機構。 6 上向流型付着生物膜反応装置は、膨脹床法又
は濾床法による嫌気性処理装置である特許請求の
範囲第1項記載の嫌気性生物反応装置に於ける沈
降分離機構。
[Claims] 1. In an anaerobic biological reactor in which a clarification zone, a gas reservoir, and a treated water receiver are provided in the upper part of an upflow type attached biofilm reaction device, an inclined partition plate is used as an upflow type attached biofilm reaction device. Arranged above the attached biofilm reactor, a gas lift tube is formed at the top of the partition plate, a clarification zone is formed above it, a gravity settling tank is formed at the side of the partition plate, and a gas lift tube is formed at the bottom of the partition plate. 1. A sedimentation separation mechanism in an anaerobic biological reaction device, characterized by having an opening through which settling sludge flows down. 2. The sedimentation separation mechanism in an anaerobic biological reaction apparatus according to claim 1, wherein the partition plate has a pair of plates facing each other in a substantially V-shape. 3. The sedimentation separation mechanism in an anaerobic biological reaction apparatus according to claim 1, wherein the gas lift tube has a pair of plates connected to each other so as to face each other at the upper part of a partition plate. 4. The clarification zone formed in the upper part of the gas lift tube is constructed by disposing a pair of plates facing each other so as to be wider than the gas lift tube. Sedimentation separation mechanism in an anaerobic biological reactor. 5. A large number of inclined plates are arranged above the gravity settling tank to prevent fine flocs, etc. that are not separated by gravity settling from flowing out of the reactor. A sedimentation separation mechanism in the anaerobic biological reaction device according to item 1. 6. The sedimentation separation mechanism in an anaerobic biological reaction device according to claim 1, wherein the upflow type attached biofilm reaction device is an anaerobic treatment device using an expanded bed method or a filter bed method.
JP61127714A 1986-06-02 1986-06-02 Settling and separating mechanism for anaerobic biological reaction device Granted JPS62282691A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP61127714A JPS62282691A (en) 1986-06-02 1986-06-02 Settling and separating mechanism for anaerobic biological reaction device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP61127714A JPS62282691A (en) 1986-06-02 1986-06-02 Settling and separating mechanism for anaerobic biological reaction device

Publications (2)

Publication Number Publication Date
JPS62282691A JPS62282691A (en) 1987-12-08
JPH0149559B2 true JPH0149559B2 (en) 1989-10-25

Family

ID=14966888

Family Applications (1)

Application Number Title Priority Date Filing Date
JP61127714A Granted JPS62282691A (en) 1986-06-02 1986-06-02 Settling and separating mechanism for anaerobic biological reaction device

Country Status (1)

Country Link
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JP2003320390A (en) * 2001-06-29 2003-11-11 Asahi Beer Eng:Kk Wastewater treatment apparatus
JP4350495B2 (en) * 2003-12-15 2009-10-21 住友重機械エンバイロメント株式会社 Organic sludge volume reduction device and wastewater treatment device
EP1806323A1 (en) * 2006-01-05 2007-07-11 Biothane Systems International B.V. Process and reactor for anaerobic waste water purification
JP6048557B1 (en) * 2015-09-25 2016-12-21 栗田工業株式会社 Anaerobic treatment apparatus and anaerobic treatment method

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