JP2002263683A - Upward stream anaerobic processor - Google Patents
Upward stream anaerobic processorInfo
- Publication number
- JP2002263683A JP2002263683A JP2001069602A JP2001069602A JP2002263683A JP 2002263683 A JP2002263683 A JP 2002263683A JP 2001069602 A JP2001069602 A JP 2001069602A JP 2001069602 A JP2001069602 A JP 2001069602A JP 2002263683 A JP2002263683 A JP 2002263683A
- Authority
- JP
- Japan
- Prior art keywords
- gas
- treated water
- sludge
- treated
- granules
- 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
Links
Classifications
-
- Y02W10/12—
Landscapes
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、有機性排水を嫌気
性処理槽内に形成された微生物の自己造粒汚泥床(以下
単に汚泥床という。)を上向流通させて、微生物の生物
学的作用で排水中の有機物を分解処理する上向流嫌気性
処理装置(以下単に処理装置という。)に関する。[0001] The present invention relates to the biological biology of microorganisms by flowing organic wastewater upward through a self-granulated sludge bed (hereinafter simply referred to as sludge bed) of microorganisms formed in an anaerobic treatment tank. The present invention relates to an upflow anaerobic treatment device (hereinafter, simply referred to as a treatment device) that decomposes organic matter in wastewater by a specific action.
【0002】[0002]
【従来の技術】従来、食品加工排水、醗酵工場排水、化
学工場排水及び紙パルプ工場排水などの有機性産業排水
や下水を処理する装置として、底部に被処理水供給手
段、上部に処理水排出手段及び生成ガス排出手段を配設
し、内部の下方にメタン菌を主体とした嫌気性微生物が
粒子化(以下グラニュールという。)し、そのグラニュ
ールを一定高さで展開滞留させて汚泥床を形成した嫌気
性処理槽にあって、汚泥床の下部に被処理水供給手段か
ら有機性排水を供給して汚泥床を上向流通させることに
より、排水中の有機物が、グラニュールを構成する嫌気
性微生物で生物学的に分解され、発生したメタンガスや
炭酸ガスなどの生成ガス、処理水およびグラニュールを
上部で分離し、処理水は処理水排出手段、生成ガスはガ
ス排出手段から排出し、グラニュールは汚泥床に沈降さ
せる処理装置が用いられている。2. Description of the Related Art Conventionally, as a device for treating organic industrial wastewater or sewage such as food processing wastewater, fermentation plant wastewater, chemical plant wastewater, and pulp and paper plant wastewater, means for supplying treated water at the bottom and treatment water at the top. And anaerobic microorganisms mainly composed of methane bacteria are formed into particles (hereinafter, referred to as granules) below the inside thereof, and the granules are developed and retained at a certain height, and the sludge bed is formed. In the anaerobic treatment tank formed, the organic matter in the wastewater constitutes a granule by supplying organic wastewater from the treated water supply means to the lower part of the sludge bed and flowing the sludge bed upward. Biologically decomposed by anaerobic microorganisms, generated gas such as methane gas and carbon dioxide gas, treated water and granules are separated at the top, treated water is discharged from treated water discharge means, and generated gas is discharged from gas discharge means , Granule processing apparatus to precipitate the sludge bed is used.
【0003】前記処理装置は、排水中の有機物を生物学
的に分解する嫌気性微生物が、微生物自体又は微細粒子
を核として粒子化するため、微生物が高密度で保持で
き、高濃度の有機性排水を効率的に処理することができ
ることにより、装置の設置面積の縮小化が図れ、また、
生成するメタンガスを燃料や化学製品製造用原料などと
して利用できる利点があり、多数設置されている。[0003] In the above-mentioned treatment apparatus, anaerobic microorganisms that biologically decompose organic matter in wastewater are converted into particles using the microorganisms themselves or fine particles as nuclei. By being able to treat wastewater efficiently, the installation area of the device can be reduced,
There is an advantage that the generated methane gas can be used as a fuel or a raw material for producing chemical products, and a large number of them are installed.
【0004】また、従来の一般的な処理装置における処
理槽の高さを2〜3倍に高くし、高さ方向に複数のガス
回収フ−ドを設けたガス分離部を上下2段に設け、回収
ガスを液の内部循環流発生用に使用し、有機物負荷を従
来の2〜3倍も高くできる高効率処理装置が、特開昭6
1−71896号公報に記載されており、また、特開昭
61−204093号公報には、高さ方向の千鳥状位置
に3段のガス回収フ−ドによるガス分離部を設けた高効
率処理装置が記載されている。Further, the height of the processing tank in a conventional general processing apparatus is increased by two to three times, and gas separation sections provided with a plurality of gas recovery hoods in the height direction are provided in two upper and lower stages. A high-efficiency processing apparatus that uses a recovered gas to generate an internal circulation flow of a liquid and can increase the organic substance load by a factor of two to three times as compared with the prior art is disclosed in
Japanese Patent Application Laid-Open No. 1-71896, and Japanese Patent Application Laid-Open No. 61-204093 discloses a high-efficiency processing in which a gas separation unit is provided with a three-stage gas recovery hood at a staggered position in the height direction. An apparatus is described.
【0005】[0005]
【発明が解決しようとする課題】従来の一般的な処理装
置では、生成したメタンガスによって処理槽内の液に乱
流が生じるため、被処理水の上向流速を速めるとグラニ
ュールが処理水に伴われて処理水排出手段から流出する
恐れがある。また、被処理水の上向流速を速めると、局
部的に汚泥負荷が過負荷状態になり、グラニュール表面
に酸生成菌が密集増殖し、グラニュールの構造がガスの
透過しにくい構造となり、グラニュールの比重が軽くな
って流出しやすくなるため、高速、高負荷条件で処理効
率を上げることが困難であった。また、高効率処理装置
の構成では、処理槽内に多数のパイプやガス回収用フ−
ドが配置されるため、装置が必要以上に複雑となり、ま
た設備費も嵩む問題がある。従って、本発明は、前記従
来技術の問題点に鑑みて成されたものであり、浮上グラ
ニュールを確実に分離でき、処理水に伴われて処理水排
出手段から流出する恐れがないため、有機性排水の高効
率処理が可能な上向流嫌気性処理装置を提供する目的で
成されたものである。In a conventional general treatment apparatus, turbulent flow occurs in the liquid in the treatment tank due to the generated methane gas. Therefore, when the upward flow velocity of the water to be treated is increased, the granules are generated in the treated water. There is a risk that the water will flow out of the treated water discharge means. Also, when the upward flow velocity of the water to be treated is increased, the sludge load is locally overloaded, acid-producing bacteria grow densely on the granule surface, and the structure of the granule becomes a structure that is difficult for gas to permeate, Since the specific gravity of the granules is reduced and the granules easily flow out, it has been difficult to increase the processing efficiency under high-speed and high-load conditions. Also, in the configuration of the high-efficiency processing apparatus, a large number of pipes and gas collection
The arrangement of the nodes causes the apparatus to be more complicated than necessary, and also raises the cost of equipment. Therefore, the present invention has been made in view of the above-mentioned problems of the prior art, and it is possible to reliably separate the floating granules, and there is no possibility of flowing out of the treated water discharging means with the treated water. The purpose of the present invention is to provide an upward anaerobic treatment device capable of efficiently treating effluent wastewater.
【0006】[0006]
【課題を解決するための手段】前記目的を達成するため
の本発明の要旨は、請求項1に記載の発明においては、
底部に被処理水供給手段、上部に処理水排出手段及び生
成ガス排出手段を配設した嫌気性処理槽にあって、該嫌
気性処理槽内の下方に自己造粒汚泥により形成された汚
泥床、該汚泥床の上方部にガス、液及び汚泥の三層に分
離する三層分離部及び頂上部にガス滞留部が形成され、
有機性排水を上向流通させて処理する上向流嫌気性処理
装置において、前記ガス滞留部に処理液面に向けて液を
噴射するスプレ−手段を配設し、前記処理水排出手段を
処理水流入口に固形分分離部材が具備されたオ−バ−フ
ロ−手段としたことを特徴とする上向流嫌気性処理装置
である。なお、前記オ−バ−フロ−手段の処理水流入口
に具備される固形分分離部材としては、ノッチ、スリッ
ト状、格子状、又は金網などで形成された部材を用いる
ことができるが、処理水に同伴されて浮上してきた微生
物粒子が流出しない構造であればよい。The gist of the present invention for achieving the above object is as follows.
A sludge bed formed by self-agglomerated sludge in the anaerobic treatment tank provided with a treated water supply means at the bottom and a treated water discharge means and a generated gas discharge means at the top. A three-layer separation part for separating into three layers of gas, liquid and sludge at the upper part of the sludge bed and a gas retention part at the top,
In an upward anaerobic treatment apparatus for treating an organic wastewater by flowing it upward, a spray means for spraying a liquid toward a treatment liquid surface is disposed in the gas retaining section, and the treated water discharge means is treated. An upflow anaerobic treatment device characterized by an overflow means provided with a solid content separation member at a water inlet. As the solid content separation member provided at the treated water inlet of the overflow means, a member formed of a notch, a slit, a lattice, a wire mesh, or the like can be used. Any structure can be used as long as the microbial particles that have floated up with the air do not flow out.
【0007】前記の構成により、スプレ−手段で浮上グ
ラニュールに付着した気泡を剥離除去するとともに、グ
ラニュールを破壊して内封された気泡を分離することが
でき、また、固形分分離部材でグラニュールが確実に分
離されるため、処理水の清澄度が高くなるとともに、グ
ラニュール流出による微生物濃度の減少が防止されるた
め、高効率処理が可能となる。[0007] With the above structure, the air bubbles adhering to the floating granules can be separated and removed by the spraying means, and the granules can be broken to separate the enclosed air bubbles. Since the granules are surely separated, the clarity of the treated water is increased, and the decrease in the concentration of microorganisms due to the outflow of the granules is prevented, so that highly efficient treatment is possible.
【0008】[0008]
【発明の実施の形態】本発明の実施の形態を図面に基づ
いて説明する。図1は本発明の一実施の形態の上向流嫌
気性処理装置の系統図である。Embodiments of the present invention will be described with reference to the drawings. FIG. 1 is a system diagram of an upflow anaerobic treatment device according to an embodiment of the present invention.
【0009】図1において、1は密閉構造で円筒形状の
嫌気性処理槽(以下単に処理槽という。)であるが、矩
形体形状の処理槽であってもよい。処理槽1の下部に
は、被処理水供給流路10が接続した被処理水供給手段
2が設けられ、上部には、処理水流入口に固形分分離部
材5が具備されたオ−バ−フロ−手段4が設けられ、処
理水排出流路12が接続している。また、頂部には、図
示しないガス吸引装置が具備された生成ガス排出手段1
1が設けられている。In FIG. 1, reference numeral 1 denotes a cylindrical anaerobic treatment tank having a closed structure (hereinafter simply referred to as a treatment tank), but may be a rectangular treatment tank. At the lower part of the treatment tank 1, there is provided treated water supply means 2 to which a treated water supply passage 10 is connected, and at the upper part, an overflow having a solids separation member 5 at the treated water inlet. Means 4 is provided, and the treated water discharge channel 12 is connected. On the top, a generated gas discharging means 1 provided with a gas suction device (not shown)
1 is provided.
【0010】前記処理槽1内には、下方に自己造粒汚泥
により形成された汚泥床A、汚泥床Aの上方部にガス、
液及び汚泥の三層に分離する三層分離部B及び頂上部に
ガス滞留部Cが形成されており、三層分離部Bには、下
段に山形衝突板3aと、上段にガスフード3bが上下千
鳥状に配置され、液を蛇行させて上昇させる流路を形成
し、生成ガスを捕集及び浮上グラニュール9を滞留させ
て沈降させるガスコレクタ3が設けられている。また、
ガス滞留部Cには、処理液面に向けて液を噴射し、浮上
グラニュール9に付着した気泡を剥離除去するととも
に、グラニュール9を破壊して内封された気泡を分離す
ることができるスプレ−手段6が配置されている。な
お、ガスフード3bで捕集した生成ガスをガス滞留部C
に導入する構成となっているが、捕集した生成ガスを図
示しないガスタンクなどへそのまま抜出して貯留する構
成としてもよい。更に、三層分離部Bは、上下に複数の
ガスフードを設けたガスコレクタや、そのガスコレクタ
を上下に複数設けた構成としてもよい。また、排出され
た処理水の一部を貯留する処理水貯留タンク7が設けら
れ、処理水供給ポンプ8が付設されて、処理槽1内にお
ける所定の上向流速維持のための循環水及びスプレ−手
段6のスプレー水として供給される構成となっている。In the treatment tank 1, a sludge bed A formed by self-agglomerated sludge is provided below, and gas is provided above the sludge bed A.
A three-layer separation part B for separating into three layers of liquid and sludge and a gas retention part C are formed at the top. The three-layer separation part B includes a mountain-shaped collision plate 3a in a lower stage and a gas hood 3b in an upper stage. There is provided a gas collector 3 which is arranged in a zigzag manner, forms a flow path for meandering and raising the liquid, and collects the generated gas and causes the floating granules 9 to stay and settle. Also,
The liquid is sprayed toward the processing liquid surface in the gas retaining section C to remove and remove the bubbles attached to the floating granules 9 and to break the granules 9 to separate the enclosed bubbles. A spray means 6 is arranged. In addition, the generated gas collected by the gas hood 3b is transferred to the gas retaining section C.
However, the collected product gas may be directly extracted and stored in a gas tank (not shown) or the like. Further, the three-layer separating section B may have a gas collector provided with a plurality of gas hoods above and below, or a configuration provided with a plurality of gas collectors above and below. Further, a treated water storage tank 7 for storing a part of the discharged treated water is provided, and a treated water supply pump 8 is provided, and circulating water and spray for maintaining a predetermined upward flow velocity in the treatment tank 1 are provided. -It is configured to be supplied as spray water of the means 6.
【0011】前記オ−バ−フロ−手段4の処理水流入口
に具備される固形分分離部材5としては、ノッチ、スリ
ット状、格子状、又は金網などで形成された板状部材を
用いることができるが、処理水に同伴されて浮上してき
た微生物粒子が流出しない構造であればよい。As the solids separating member 5 provided at the treated water inlet of the overflow means 4, a notch, a slit, a grid, or a plate member formed of a wire mesh or the like is used. Although it is possible, any structure may be used as long as it does not allow the microbial particles floating with the treated water to flow out.
【0012】被処理水供給手段2は、被処理水を処理槽
1の水平断面全体を均一に上向流通させるのが好ましい
ため、処理槽1の底面に多数の供給口を設けた格子状部
材を底面の略全面にわたって配置するのが好ましいが、
被処理水を処理槽1内の接線方向に供給する部材であっ
てもよく、これらには限定されない。The treated water supply means 2 preferably distributes the treated water uniformly upward in the entire horizontal section of the treatment tank 1. It is preferable to dispose over almost the entire bottom surface,
The member for supplying the water to be treated in the tangential direction in the treatment tank 1 may be used, but is not limited thereto.
【0013】以下に本発明の作用を図に基づいて説明す
る。食品加工排水などの有機性排水の被処理水を、被処
理水供給流路10から被処理水供給手段2を介して処理
槽1内の下部に供給し、処理槽1内を均一な上向流とし
て流通させることにより、初期に充填された下水汚泥な
どを種菌として自己造粒したメタン菌などの微生物によ
るグラニュール9の汚泥床Aが形成されるが、初期に他
の装置からのグラニュール9を充填してもよい。The operation of the present invention will be described below with reference to the drawings. Water to be treated as organic wastewater such as food processing wastewater is supplied to the lower part of the treatment tank 1 from the treatment water supply passage 10 via the treatment water supply means 2, and the inside of the treatment tank 1 is uniformly turned upward. The sludge bed A of the granules 9 is formed by the microorganisms such as methane bacteria which are self-granulated by using the initially filled sewage sludge as a seed microorganism by distributing the sludge as a stream. 9 may be filled.
【0014】処理槽1内に供給された被処理水は、汚泥
床Aを上向流通する間に被処理水中の有機物が微生物の
生物学的作用で分解処理され、メタンガスや炭酸ガスな
どが生成される。なお、被処理水の上向流速は、従来の
処理装置にあっては、汚泥床Aの膨張展開に伴うグラニ
ュール9の流出を防止するため、遅い上向流速(例え
ば、1〜2m/hr)で運転されており、被処理水に含
まれる無機性固形物がグラニュール9に捕捉されやす
く、汚泥の生物活性を高く維持することができないとと
もに、被処理水供給量も少ないため、高速、高負荷条件
で処理効率を上げることが困難であったが、本発明の処
理装置では、グラニュール9流出を完全に防止すること
ができるため、速い上向流速(例えば、3〜10m/h
r)とすることができ、汚泥床Aの膨張展開を積極的に
図り、被処理水とグラニュール9との接触効率を高める
ことができる。また、被処理水供給量も多くでき、高
速、高負荷条件で処理効率を上げることができる。In the water to be treated supplied into the treatment tank 1, organic substances in the water to be treated are decomposed by the biological action of microorganisms while flowing upward through the sludge bed A to produce methane gas, carbon dioxide gas and the like. Is done. In addition, in the conventional treatment apparatus, the upward flow velocity of the water to be treated is low to prevent the granules 9 from flowing out due to the expansion and deployment of the sludge bed A (for example, 1 to 2 m / hr). ), The inorganic solids contained in the water to be treated are easily trapped by the granules 9, and the biological activity of the sludge cannot be maintained at a high level. Although it was difficult to increase the processing efficiency under high load conditions, the processing apparatus of the present invention can completely prevent the granules 9 from flowing out, and therefore has a high upward flow velocity (for example, 3 to 10 m / h).
r), the sludge bed A can be positively expanded and deployed, and the contact efficiency between the water to be treated and the granules 9 can be increased. Further, the supply amount of the water to be treated can be increased, and the treatment efficiency can be increased under high-speed and high-load conditions.
【0015】汚泥床Aの微生物で有機物が分解された被
処理水は、更に上昇して三層分離部Bのガスコレクタ3
に至り、下段の山形衝突板3aで浮上グラニュール9が
分離され、汚泥床Aに沈降循環され、また、浮上グラニ
ュール9の一部や生成ガスは処理液に伴なわれて蛇行上
昇し、上段のガスフード3bにより浮上グラニュール9
及び生成ガスが分離される。生成ガスはガスフード3b
で集められてガス滞留部Cに導入され、浮上グラニュー
ル9は滞留する間に汚泥床Aへ沈降される。The water to be treated, in which the organic matter is decomposed by the microorganisms in the sludge bed A, further rises and rises in the gas collector 3 in the three-layer separation section B.
, The floating granules 9 are separated by the lower chevron impact plate 3a and settled and circulated to the sludge bed A, and a part of the floating granules 9 and generated gas meander upward with the processing liquid, Floating granules 9 by upper gas hood 3b
And the product gas. Generated gas is gas hood 3b
The floating granules 9 are collected in the gas storage section C, and settle on the sludge bed A while staying.
【0016】三層分離部Bのガスコレクタ3で生成ガス
とグラニュール9が分離された被処理水は、更に上昇
し、ガス滞留部Cに至り、残存する生成ガスが静置分離
され、オ−バ−フロ−手段4の処理水流入口に具備され
た固形分分離部材5により残存グラニュール9が分離さ
れ、清澄な処理水として処理水排出流路12から処理槽
外に排出される。また、ガス滞留部Cに分離された、生
成ガスは、図示しないガス吸引装置を介して生成ガス排
出手段から図示しないガスタンクなどに回収される。The water to be treated, from which the product gas and the granules 9 have been separated by the gas collector 3 of the three-layer separation section B, rises further, reaches the gas retaining section C, and the remaining product gas is separated by standing. The remaining granules 9 are separated by the solid content separation member 5 provided at the treated water inlet of the bar flow means 4 and discharged out of the treated tank from the treated water discharge channel 12 as clear treated water. Further, the generated gas separated into the gas retaining section C is collected from a generated gas discharging unit to a gas tank (not shown) through a gas suction device (not shown).
【0017】なお、ガス滞留部に滞留する被処理水は、
スプレ−手段6から噴射される処理水により、残存する
浮上グラニュール9に付着した気泡が剥離除去されると
ともに、グラニュール9を破壊して内封された気泡が分
離されるため、効率的にグラニュール9を沈降分離する
ことができる。The water to be treated staying in the gas staying section is:
The treated water sprayed from the spray means 6 removes and removes the air bubbles adhered to the remaining floating granules 9 and breaks the granules 9 to separate the enclosed air bubbles, so that the air bubbles are efficiently separated. The granules 9 can be settled off.
【0018】処理水排出流路12から処理槽1外に排出
された清澄な処理水は系外に排出されるが、その一部
は、処理水貯留タンク7に貯留されたのち、処理水供給
ポンプ8を介して、その一部を処理水循環流路14を介
して処理槽1内における所定の上向流速維持のために、
被処理水供給流路10に合流して被処理水に混合し、処
理槽1内に循環され、残部の処理水はスプレー水供給流
路13を介してスプレ−手段6のスプレー水として供給
される。The clear treated water discharged from the treated water discharge channel 12 to the outside of the treated tank 1 is discharged to the outside of the system. A part of the treated water is stored in the treated water storage tank 7 and then supplied to the treated water supply tank 7. In order to maintain a predetermined upward flow velocity in the treatment tank 1 through the treatment water circulation flow path 14,
It merges with the water to be treated and mixes with the water to be treated, is circulated in the treatment tank 1, and the remaining treated water is supplied as spray water of the spray means 6 through the spray water supply flow path 13. You.
【0019】[0019]
【発明の効果】本発明は、浮上グラニュールを確実に分
離でき、処理水に伴われて処理水排出手段から流出する
恐れがないため、有機性排水の高効率処理が可能な上向
流嫌気性処理装置である。According to the present invention, the floating granules can be reliably separated, and there is no possibility that the floating granules will flow out of the treated water discharge means with the treated water. Sexual processing device.
【図1】本発明の一実施の形態の上向流嫌気性処理装置
の系統図FIG. 1 is a system diagram of an upward anaerobic treatment device according to an embodiment of the present invention.
1:嫌気性処理槽 2:被処理水供給手段 3:ガスコレクタ 4:オ−バ−フロ−手段 5:固形分分離部材 6:スプレ−手段 7:処理水貯留タンク 8:処理水供給ポンプ 9:グラニュール A:汚泥床 B:三層分離部 C:ガス滞留部 1: Anaerobic treatment tank 2: Treatment water supply means 3: Gas collector 4: Overflow means 5: Solids separation member 6: Spray means 7: Treated water storage tank 8: Treated water supply pump 9 : Granule A: Sludge bed B: Three-layer separation section C: Gas retention section
Claims (1)
出手段及び生成ガス排出手段を配設した嫌気性処理槽に
あって、該嫌気性処理槽内の下方に自己造粒汚泥により
形成された汚泥床、該汚泥床の上方部にガス、液及び汚
泥の三層に分離する三層分離部及び頂上部にガス滞留部
が形成され、有機性排水を上向流通させて処理する上向
流嫌気性処理装置において、前記ガス滞留部に処理液面
に向けて液を噴射するスプレ−手段を配設し、前記処理
水排出手段を処理水流入口に固形分分離部材が具備され
たオ−バ−フロ−手段としたことを特徴とする上向流嫌
気性処理装置。1. An anaerobic treatment tank provided with a treated water supply means at a bottom part, a treated water discharge means and a generated gas discharge means at an upper part, and self-granulated sludge below the anaerobic treatment tank. The formed sludge bed, a three-layer separation part for separating into three layers of gas, liquid and sludge at the upper part of the sludge bed and a gas retention part at the top are formed to process organic wastewater by flowing upward. In the upward flow anaerobic treatment apparatus, a spray means for injecting a liquid toward a treatment liquid surface is disposed in the gas retaining section, and a solids separation member is provided at the treatment water inflow port for the treatment water discharge means. An upflow anaerobic treatment device characterized by an overflow means.
Priority Applications (1)
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Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2001069602A JP2002263683A (en) | 2001-03-13 | 2001-03-13 | Upward stream anaerobic processor |
Publications (1)
Publication Number | Publication Date |
---|---|
JP2002263683A true JP2002263683A (en) | 2002-09-17 |
Family
ID=18927620
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2007190461A (en) * | 2006-01-17 | 2007-08-02 | Sumitomo Heavy Ind Ltd | Anaerobic treatment apparatus |
JP2007229657A (en) * | 2006-03-02 | 2007-09-13 | Kajima Corp | Method for feeding organic matter-containing liquid into fermentation tank, and treatment apparatus for the organic matter-containing liquid |
KR101114972B1 (en) | 2011-09-07 | 2012-03-06 | 김수명 | Divice and method of anaerobic digestion using liquid impulse mixing |
WO2012049909A1 (en) * | 2010-10-15 | 2012-04-19 | 株式会社明電舎 | Waste water treatment equipment |
JP2015051405A (en) * | 2013-09-09 | 2015-03-19 | ヴェオリア・ウォーター・ジャパン株式会社 | Treatment apparatus and treatment method of organic matter-containing effluent |
-
2001
- 2001-03-13 JP JP2001069602A patent/JP2002263683A/en active Pending
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2007190461A (en) * | 2006-01-17 | 2007-08-02 | Sumitomo Heavy Ind Ltd | Anaerobic treatment apparatus |
JP2007229657A (en) * | 2006-03-02 | 2007-09-13 | Kajima Corp | Method for feeding organic matter-containing liquid into fermentation tank, and treatment apparatus for the organic matter-containing liquid |
JP4641271B2 (en) * | 2006-03-02 | 2011-03-02 | 鹿島建設株式会社 | Fermenter charging method and processing apparatus for organic substance-containing liquid |
WO2012049909A1 (en) * | 2010-10-15 | 2012-04-19 | 株式会社明電舎 | Waste water treatment equipment |
JP2012086109A (en) * | 2010-10-15 | 2012-05-10 | Meidensha Corp | Wastewater treatment apparatus |
KR101114972B1 (en) | 2011-09-07 | 2012-03-06 | 김수명 | Divice and method of anaerobic digestion using liquid impulse mixing |
JP2015051405A (en) * | 2013-09-09 | 2015-03-19 | ヴェオリア・ウォーター・ジャパン株式会社 | Treatment apparatus and treatment method of organic matter-containing effluent |
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