JPH05138192A - Anaerobic treatment of high-concentration organic waste water containing organic suspended solid and equipment thereof - Google Patents

Anaerobic treatment of high-concentration organic waste water containing organic suspended solid and equipment thereof

Info

Publication number
JPH05138192A
JPH05138192A JP30628291A JP30628291A JPH05138192A JP H05138192 A JPH05138192 A JP H05138192A JP 30628291 A JP30628291 A JP 30628291A JP 30628291 A JP30628291 A JP 30628291A JP H05138192 A JPH05138192 A JP H05138192A
Authority
JP
Japan
Prior art keywords
organic
concentration
organic suspended
liquid
solid
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.)
Granted
Application number
JP30628291A
Other languages
Japanese (ja)
Other versions
JP3152357B2 (en
Inventor
Hiroshi Kobayashi
浩志 小林
Akihiro Nagano
晃弘 長野
Etsuro Arikawa
悦朗 有川
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 JP30628291A priority Critical patent/JP3152357B2/en
Publication of JPH05138192A publication Critical patent/JPH05138192A/en
Application granted granted Critical
Publication of JP3152357B2 publication Critical patent/JP3152357B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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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

Landscapes

  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Treatment Of Sludge (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

PURPOSE:To enhance the degree of decomposition of organic suspended solid by washing the organic suspended solid with treated water and performing liquid-solid separation to separate the same into supernatant and concentrate and treating supernatant by a high efficient anaerobic bioreactor and treating condensate by a device combined with a floating type bioreactor and a membrane separator, CONSTITUTION:Drainage containing organic suspended solid at high concentration in a raw liquid tank 1 is sent to a washing tank 3, washed and separated into organic suspended solid and liquid. Organic suspended solid difficult to be decomposed is removed by a filter member 4. Then filtrate is sent to a liquid-solid separator 6 and separated into supernatant 6b and concentrate 6a. Supernatant 6b is treated at high load by using a high efficient anaerobic bioreactor 12 such as a fluidized bed reactor. Concentrate 6a is treated by a floating type bioration membrane and a precision filtration membrane. Thereby the degree of decomposition of organic substance is enhanced because the concentration of suspended solid is low in the high efficient anaerobic bioreactor 12.

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、有機性の懸濁物質(S
S)を高濃度に含む廃水を嫌気性処理する方法およびそ
の装置に関するものである。
The present invention relates to an organic suspended substance (S
The present invention relates to a method and an apparatus for anaerobically treating wastewater containing S) in a high concentration.

【0002】[0002]

【従来の技術】従来、有機性の懸濁物質(SS)を高濃
度に含む廃水を嫌気性処理するために、UASB(Upfl
ow Anaeiohic SladgeBlanket)(汚泥床),流動床,固
定床など高効率の嫌気性バイオリアクターが開発されて
いる。
2. Description of the Related Art Conventionally, in order to anaerobically treat wastewater containing a high concentration of organic suspended solids (SS), UASB (Upfl
ow Anaeiohic Sladge Blanket (sludge bed), fluidized bed, fixed bed and other highly efficient anaerobic bioreactors have been developed.

【0003】[0003]

【発明が解決しようとする課題】しかし、何れの処理方
法を用いても、例えば、焼酎廃水,ビール酵母洗浄廃
水,清酒の洗米廃水,澱粉廃液などに代表される高濃度
の有機性の懸濁物質(SS)を含む場合は、グラニュー
ルができない(UASB)、生物膜が剥離する(流動
床)、ろ床が閉塞する(固定床)、有機性の懸濁物質
(SS)のショートパスによって除去率が悪化するなど
の理由によって処理できない。
However, whichever treatment method is used, high-concentration organic suspensions represented by, for example, shochu wastewater, brewer's yeast washing wastewater, sake rinsing wastewater, starch wastewater, etc. are used. When the substance (SS) is included, it cannot be granulated (UASB), the biofilm is separated (fluidized bed), the filter bed is blocked (fixed bed), and the organic suspended substance (SS) is short-passed. It cannot be processed because the removal rate deteriorates.

【0004】また、完全混合浮遊型のバイオリアクター
を用いると、処理速度が遅いため、巨大なバイオリアク
ターを必要とする、有機性の懸濁物質(SS)が分解せ
ず流出する、脱水する汚泥の量が非常に多いという問題
点があった。
Further, when a completely mixed floating type bioreactor is used, the processing speed is slow, and therefore a huge bioreactor is required. Organic suspended solids (SS) flow out without being decomposed and dehydrated sludge. There was a problem that the amount was very large.

【0005】しかも、これらの廃水に含まれる有機性の
懸濁物質(SS)は、廃水中の有機物の10〜50%を
占めており、粘性が非常に高く、低コストで濃縮・脱水
することが困難である。
Moreover, the organic suspended solids (SS) contained in these wastewaters account for 10 to 50% of the organic matter in the wastewater, have a very high viscosity, and can be concentrated and dehydrated at low cost. Is difficult.

【0006】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、有機性の懸濁物質
(SS)を高濃度に含む廃水を、固液分離することによ
って、有機性の懸濁物質(SS)の濃度の比較的小さい
上澄液と高濃度に有機性の懸濁物質(SS)を含む濃縮
液とに分離し、これらを個別に嫌気性処理することを可
能とした有機性の懸濁物質(SS)を含む高濃度有機性
廃水の嫌気性処理方法およびその装置を提供することに
ある。
The present invention has been made to solve such conventional problems, and an object thereof is to perform solid-liquid separation of waste water containing an organic suspended solid (SS) in a high concentration. , Separate into a supernatant liquid containing a relatively small concentration of organic suspended solids (SS) and a concentrated liquid containing a high concentration of organic suspended solids (SS), and subject them individually to anaerobic treatment An object of the present invention is to provide a method and an apparatus for anaerobic treatment of highly concentrated organic wastewater containing an organic suspended substance (SS) that enables the above.

【0007】[0007]

【課題を解決するための手段】請求項1の有機性の懸濁
物質を含む高濃度有機性廃水の嫌気性処理方法は、有機
性の懸濁物質を高濃度に含む廃水を洗浄し、固液分離を
行ない、固液分離された上澄液を、嫌気性バイオリアク
ターに供給して、メタン醗酵により処理し、固液分離さ
れた有機性の懸濁物質を、膜分離装置を有する浮遊型の
嫌気性バイオリアクターに供給して、メタン醗酵により
処理するものである。
A method for anaerobic treatment of high-concentration organic wastewater containing organic suspended solids according to claim 1, wherein the wastewater containing high-concentration organic suspended solids is washed and solidified. Liquid-separated, the solid-liquid separated supernatant is supplied to the anaerobic bioreactor and processed by methane fermentation, and the solid-liquid separated organic suspended substance is a floating type with a membrane separator. It is supplied to the anaerobic bioreactor of the above and treated by methane fermentation.

【0008】請求項2の有機性の懸濁物質を含む高濃度
有機性廃水の嫌気性処理方法は、有機性の懸濁物質を高
濃度に含む廃水を処理水又は希釈水で洗浄するものであ
る。請求項3の有機性の懸濁物質を含む高濃度有機性廃
水の嫌気性処理方法は、請求項1において、有機性の懸
濁物質を含む高濃度有機性廃水が、焼酎廃水,ビール酵
母洗浄廃水,清酒の洗米廃水,澱粉廃液であるものであ
る。
The anaerobic treatment method for high-concentration organic wastewater containing organic suspended solids according to claim 2 is to wash wastewater containing organic suspended solids in high concentration with treated water or diluted water. is there. The method for anaerobic treatment of high-concentration organic wastewater containing organic suspended matter according to claim 3, wherein the high-concentration organic wastewater containing organic suspended matter is shochu distilled water, brewer's yeast washing according to claim 1. It is waste water, rice rinsing waste water of sake, and starch waste liquor.

【0009】請求項4の有機性の懸濁物質を含む高濃度
有機性廃水の嫌気性処理方法は、請求項1において、有
機性の懸濁物質を高濃度に含む廃水を洗浄し、300μ
m以上の有機性の懸濁物質を除去するものである。
According to a fourth aspect of the present invention, there is provided an anaerobic treatment method for high-concentration organic wastewater containing an organic suspended substance, wherein the wastewater containing an organic suspended substance in a high concentration is washed to obtain 300 μm.
It removes organic suspended matter of m or more.

【0010】請求項5の有機性の懸濁物質を含む高濃度
有機性廃水の嫌気性処理装置は、有機性の懸濁物質を高
濃度に含む廃水を貯留する原液槽と、有機性の懸濁物質
を高濃度に含む廃水を洗浄する洗浄装置と、固液分離装
置と、固液分離装置の上澄液を取り込み、メタン醗酵に
より処理する嫌気性バイオリアクリーと、固液分離装置
の濃縮された有機性の懸濁物質を高濃度に含む廃水を取
り込み、メタン醗酵により処理する浮遊型の嫌気性バイ
オリアクリーと、浮遊型の嫌気性バイオリアクリーと連
結する膜分離装置と、を備えたものである。
According to a fifth aspect of the present invention, there is provided an anaerobic treatment apparatus for high-concentration organic wastewater containing organic suspended solids, which comprises a stock solution tank for storing wastewater containing high-concentration organic suspended solids and an organic suspension tank. A washing device for washing wastewater containing a high concentration of turbid substances, a solid-liquid separation device, an anaerobic bioreactor that takes in the supernatant of the solid-liquid separation device and processes it by methane fermentation, and concentration of the solid-liquid separation device Equipped with a floating type anaerobic bioreakly that takes in wastewater containing a high concentration of the suspended organic suspended matter and treats it by methane fermentation, and a membrane separation device that connects with the floating type anaerobic bioreakly It is a thing.

【0011】請求項6の有機性の懸濁物質を含む高濃度
有機性廃水の嫌気性処理装置は、請求項5において、有
機性の懸濁物質を高濃度に含む廃水を洗浄する洗浄装置
には、300μm以上の有機性の懸濁物質を除去するろ
過部材が設けられているものである。
According to a sixth aspect of the present invention, there is provided an anaerobic treatment apparatus for high-concentration organic wastewater containing organic suspended matter, which is the cleaning apparatus for washing wastewater containing high-concentration organic suspended matter. Is provided with a filtering member for removing organic suspended matter of 300 μm or more.

【0012】請求項7の有機性の懸濁物質を含む高濃度
有機性廃水の嫌気性処理装置は、請求項5において、浮
遊型の嫌気性バイオリアクリーと、膜分離装置との間に
は、循環装置が介装されているものである。
According to a seventh aspect of the present invention, in the anaerobic treatment apparatus for high-concentration organic wastewater containing organic suspended matter, the floating type anaerobic bioreactor and the membrane separation apparatus in the fifth aspect are provided. The circulation device is interposed.

【0013】[0013]

【作用】請求項1ないし3の有機性の懸濁物質を(S
S)含む高濃度有機性廃水の嫌気性処理方法において
は、有機性の懸濁物質(SS)を高濃度に含む廃水を洗
浄し、有機性の懸濁物質(SS)の濃度の比較的小さい
上澄液と高濃度に有機性の懸濁物質(SS)を含む濃縮
液とに分離し、有機性の懸濁物質(SS)の濃度の比較
的小さい上澄液を、嫌気性バイオリアクターに供給し
て、メタン醗酵により処理し、高濃度に有機性の懸濁物
質(SS)を含む濃縮液を、膜分離装置を有する浮遊型
の嫌気性バイオリアクターに供給して、メタン醗酵によ
り処理する。
The organic suspending substance according to claim 1 (S
S) In the anaerobic treatment method of high-concentration organic wastewater containing, the wastewater containing high concentration of organic suspended solids (SS) is washed, and the concentration of organic suspended solids (SS) is relatively low. The supernatant and the concentrated liquid containing a high concentration of organic suspended solids (SS) are separated, and the supernatant containing a relatively small concentration of organic suspended solids (SS) is transferred to the anaerobic bioreactor. It is supplied and processed by methane fermentation, and a concentrated liquid containing a high concentration of organic suspended solids (SS) is supplied to a floating type anaerobic bioreactor having a membrane separation device and processed by methane fermentation. ..

【0014】請求項4の有機性の懸濁物質(SS)を含
む高濃度有機性廃水の嫌気性処理方法においては、有機
性の懸濁物質(SS)を高濃度に含む廃水を洗浄し、例
えば、芋の皮,根,幹などのように分解されずらい30
0μm以上の有機性の懸濁物質(SS)を除去する。
In the method for anaerobic treatment of high-concentration organic wastewater containing organic suspended solids (SS) according to claim 4, the wastewater containing high-concentration organic suspended solids (SS) is washed, For example, potato peels, roots, trunks, etc.
Remove organic suspended solids (SS) above 0 μm.

【0015】請求項5の有機性の懸濁物質(SS)を含
む高濃度有機性廃水の嫌気性処理装置においては、原液
槽に貯留した有機性の懸濁物質(SS)を高濃度に含む
廃水を、洗浄装置で洗浄し、固液分離装置で、有機性の
懸濁物質(SS)の濃度の比較的小さい上澄液と高濃度
に有機性の懸濁物質(SS)を含む濃縮液とに分離し、
有機性の懸濁物質(SS)の濃度の比較的小さい上澄液
を、嫌気性バイオリアクリーにてメタン醗酵により処理
し、高濃度に有機性の懸濁物質(SS)を含む濃縮液
を、浮遊型の嫌気性バイオリアクリーでメタン醗酵によ
り処理するとともに、膜分離装置によって膜分離処理す
る。
In the anaerobic treatment apparatus for high-concentration organic wastewater containing organic suspended solids (SS) according to claim 5, the organic suspended solids (SS) stored in the stock solution tank are contained in high concentration. The wastewater is washed with a washing device, and in the solid-liquid separation device, a supernatant containing a relatively small concentration of organic suspended solids (SS) and a concentrated liquid containing a high concentration of organic suspended solids (SS) Separated into and
A supernatant containing a relatively low concentration of organic suspended solids (SS) is processed by methane fermentation in an anaerobic bioreactor to obtain a concentrated liquid containing a high concentration of organic suspended solids (SS). , A floating type anaerobic bioreactor and methane fermentation, and a membrane separation device.

【0016】請求項6の有機性の懸濁物質(SS)を含
む高濃度有機性廃水の嫌気性処理装置においては、30
0μm以上の有機性の懸濁物質(SS)をろ過部材によ
って除去する。
In the anaerobic treatment apparatus for high-concentration organic wastewater containing organic suspended solids (SS) according to claim 6, 30
An organic suspended substance (SS) of 0 μm or more is removed by a filter member.

【0017】請求項7の有機性の懸濁物質(SS)を含
む高濃度有機性廃水の嫌気性処理装置においては、高濃
度に有機性の懸濁物質(SS)を含む濃縮液を、浮遊型
の嫌気性バイオリアクリーでメタン醗酵により処理する
とともに、膜分離装置によって膜分離処理する循環処理
を行なう。
In the anaerobic treatment apparatus for high-concentration organic wastewater containing organic suspended solids (SS) according to claim 7, a concentrated liquid containing high-concentration organic suspended solids (SS) is suspended. Type anaerobic bioreactor is used for methane fermentation, and the membrane is separated by a membrane separator.

【0018】[0018]

【実施例】以下、本発明を添付図面を参照しながら詳細
に説明する。図1は本発明に係る有機性の懸濁物質を含
む高濃度有機性廃水の嫌気性処理装置の一実施例を示す
もので、1は原液槽である。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described in detail below with reference to the accompanying drawings. FIG. 1 shows an embodiment of an anaerobic treatment apparatus for high-concentration organic wastewater containing an organic suspended substance according to the present invention, and 1 is a stock solution tank.

【0019】この原液槽1には、例えば、焼酎廃水,ビ
ール酵母洗浄廃水,清酒の洗米廃水,澱粉廃液などに代
表される高濃度の有機性の懸濁物質(SS)を含む廃水
が貯留される。この原液槽1は、配管2を介して洗浄装
置3と連絡している。
The stock solution tank 1 stores waste water containing high-concentration organic suspended substances (SS) represented by, for example, shochu waste water, brewer's yeast washing waste water, sake rinsing waste water, starch waste liquid, and the like. It The stock solution tank 1 is connected to the cleaning device 3 via a pipe 2.

【0020】この洗浄装置3は、例えば、直径が0.5mm
の多数の小孔を設けたパンチング板, フィルター,スク
リーンなどのように、300μm以上の大きな有機性の
懸濁物質(SS)を除去するろ過部材4が設けられてい
る。また、この洗浄装置3には、有機性の懸濁物質(S
S)を廃水と充分に分離するために、井水又は循環水が
供給されるようになっている。そのために必要な井水又
は循環水は、廃水の性状によって異なるが、無希釈から
100倍程度である。希釈倍率の設定は、廃水の粘性に
よって決定し、10cP以下になるようにする。この洗
浄装置3は、配管5を介してSS濃縮槽からなる固液分
離装置6と連絡している。
The cleaning device 3 has, for example, a diameter of 0.5 mm.
A filtering member 4 for removing large organic suspended solids (SS) of 300 μm or more is provided, such as a punching plate having a large number of small holes, a filter, and a screen. In addition, the cleaning device 3 has an organic suspended substance (S
Well water or circulating water is supplied in order to sufficiently separate S) from waste water. The well water or circulating water required for that purpose is from undiluted to about 100 times, depending on the properties of the waste water. The setting of the dilution ratio is determined by the viscosity of the waste water and should be 10 cP or less. The cleaning device 3 is connected via a pipe 5 to a solid-liquid separation device 6 composed of an SS concentration tank.

【0021】この固液分離装置6としては、沈澱池や遠
心分離機が用いられる。この固液分離装置6において
は、沈降速度が1m/時以上の比較的粒径の大きな有機
性の懸濁物質(SS)が、濃縮液6a側に移行し、上澄
液6bの方には沈降速度1m/時以下の軽い有機性の懸
濁物質(SS)のみとなる。この際、濃縮液の有機性の
懸濁物質(SS)の濃度は、50,000mg/l以下に
制御する。この固液分離装置6は、配管7を介して上澄
液貯槽8と連絡するとともに、配管9を介して浮遊型バ
イオリアクター10に連絡している。
As the solid-liquid separator 6, a sedimentation tank or a centrifuge is used. In this solid-liquid separator 6, an organic suspended substance (SS) having a relatively large particle size and having a sedimentation velocity of 1 m / hour or more is transferred to the concentrated liquid 6a side, and the suspended liquid 6b is discharged toward the supernatant liquid 6b. Only a light organic suspended solid (SS) with a sedimentation speed of 1 m / hour or less is used. At this time, the concentration of the organic suspended substance (SS) in the concentrated liquid is controlled to 50,000 mg / l or less. The solid-liquid separation device 6 communicates with the supernatant liquid storage tank 8 via a pipe 7 and also communicates with the floating bioreactor 10 via a pipe 9.

【0022】上澄液貯槽8は、配管11を介して嫌気性
バイオリアクター12と連絡している。この嫌気性バイ
オリアクター12としては、高負荷を許容するUASB
(Upflow Anaeiohic Sladge Blanket)(汚泥床)型リア
クター,流動床型リアクター,固定床流動床型リアクタ
ーの何れかが用いられている。本例では、流動床型リア
クターが示されている。また、嫌気性バイオリアクター
12は、配管13を介して上澄液が循環するようにして
ある。この循環ラインには、沈澱槽を設置し、循環液の
有機性の懸濁物質(SS)の濃度が、3,000mg/l以下に
なるようにコントロールされる必要がある。
The supernatant storage tank 8 is in communication with the anaerobic bioreactor 12 via a pipe 11. As the anaerobic bioreactor 12, a UASB that allows a high load
(Upflow Anaeiohic Sladge Blanket) (sludge bed) type reactor, fluidized bed type reactor, or fixed bed fluidized bed type reactor is used. In this example, a fluidized bed reactor is shown. Further, in the anaerobic bioreactor 12, the supernatant liquid is circulated through the pipe 13. It is necessary to install a precipitation tank in this circulation line and control the concentration of the organic suspended solids (SS) in the circulation liquid to be 3,000 mg / l or less.

【0023】嫌気性バイオリアクター12は、無希釈時
の上澄液CODcr濃度によってUASB(Upflow Anaei
ohic Sladge Blanket)(汚泥床)型リアクター,流動床
型リアクター,固定床流動床型リアクターの何れかが用
いられている。
The anaerobic bioreactor 12 uses the UASB (Upflow Anaei) depending on the CODcr concentration of the supernatant liquid when undiluted.
Either an ohic sludge blanket (sludge bed) type reactor, a fluidized bed type reactor, or a fixed bed fluidized bed type reactor is used.

【0024】ちなみに、上澄液CODcr濃度が、6,000m
g/l以下の場合には、UASBが用いられ、リアクター
の循環比は0〜10である。上澄液CODcr濃度が、6,
000〜15,000mg/lの場合には、固定床が用いられ、リ
アクターの循環比は10〜20である。上澄液CODcr
濃度が15,000mg/lの場合には、固定床が用いられ、リ
アクターの循環比は20〜100である。
By the way, the supernatant CODcr concentration is 6,000 m
In the case of g / l or less, UASB is used and the circulation ratio of the reactor is 0-10. The supernatant CODcr concentration is 6,
In the case of 000-15,000 mg / l, a fixed bed is used and the circulation ratio of the reactor is 10-20. Supernatant CODcr
When the concentration is 15,000 mg / l, a fixed bed is used and the circulation ratio of the reactor is 20-100.

【0025】ここで、発生する循環液の一部又は全部
を、洗浄装置3の洗浄用の循環水として用いられる。希
釈時の有機性の懸濁物質(SS)の濃度は、1,000mg/l
以下にコントロールすることが望ましい。
Here, a part or all of the generated circulating liquid is used as circulating water for cleaning the cleaning device 3. The concentration of organic suspended solids (SS) when diluted is 1,000 mg / l.
It is desirable to control the following.

【0026】なお、UASBでは、上向流速は、1m/
時以上に設定して、有機性の懸濁物質(SS)が分解で
きない場合でも、処理水側に有機性の懸濁物質(SS)
が流出して、反応には影響を与えないように、系外に押
し出すように制御する。他のリアクターの場合は、上向
流速が1m/時よりも大きいので、有機性の懸濁物質
(SS)の影響は殆どない。
In UASB, the upward flow velocity is 1 m /
Even if the organic suspended solids (SS) cannot be decomposed by setting the time more than the time, the organic suspended solids (SS) will remain on the treated water side.
Is controlled to flow out of the system so as not to affect the reaction. In the case of the other reactors, the upward flow velocity is higher than 1 m / hour, so that there is almost no influence of organic suspended solids (SS).

【0027】また、BOD負荷は、5Kg−BOD/m3/日
以上、BOD効率は85%が期待できる。さらに、嫌気
性バイオリアクター12には、配管14を介して生物膜
分離槽15が連絡するとともに、配管16を介してガス
ホルダー17が連絡している。また、生物膜分離槽15
には、処理水と余剰汚泥を取り出す配管18,19が取
り付けられている。さらに、ガスホルダー17には、メ
タンガスを取り出す配管20が取り付けられている。
Further, the BOD load can be expected to be 5 kg-BOD / m 3 / day or more, and the BOD efficiency can be expected to be 85%. Further, the anaerobic bioreactor 12 is connected to the biofilm separation tank 15 via the pipe 14 and to the gas holder 17 via the pipe 16. Also, the biofilm separation tank 15
Pipes 18 and 19 for removing treated water and excess sludge are attached to the pipes. Further, a pipe 20 for taking out methane gas is attached to the gas holder 17.

【0028】一方、浮遊型バイオリアクター10には、
配管21を介して循環水槽22が連結されている。この
循環水槽22には、配管23,25を介して限外ろ過膜
又は精密ろ過膜を用いたクロスフロータイプの膜分離装
置24が連結されている。この膜分離装置24には、分
離された処理水を取り出すための配管28が取り付けら
れている。また、循環水槽22には、配管26,29を
介して浮遊型バイオリアクター10に戻り経路が連結さ
れている。さらに、浮遊型バイオリアクター10では、
配管27,29を介して汚泥が引き抜かれるようにして
ある。さらに、浮遊型バイオリアクター10は、配管3
0を介してガスホルダー17に発生ガスを送るようにな
っている。 この浮遊型バイオリアクター10では、有
機性の懸濁物質(SS)の分解が遅いため、BOD負荷
は1〜5Kg/m3/日程度に設定する。また、浮遊型バイオ
リアクター10では、汚泥を引き抜くことにより、浮遊
型バイオリアクター10内の汚泥濃度は、30,000mg/l
以下に制御する。さらに、膜面流速0.2 m/秒以上で膜
面洗浄に用いる汚泥循環液の一部又は全部を浮遊型バイ
オリアクター10の撹拌混合用として用いる。循環液に
よる撹拌だけでは、混合が不十分な場合には、浮遊型バ
イオリアクター10の発生ガスによるエアリフト撹拌を
併用する。通常、この操作によってBOD除去率95%
以上が期待できる。
On the other hand, in the floating bioreactor 10,
A circulating water tank 22 is connected via a pipe 21. A cross-flow type membrane separator 24 using an ultrafiltration membrane or a microfiltration membrane is connected to the circulating water tank 22 via pipes 23 and 25. A pipe 28 for taking out the separated treated water is attached to the membrane separation device 24. Further, in the circulating water tank 22, a return path is connected to the floating bioreactor 10 via pipes 26 and 29. Furthermore, in the floating bioreactor 10,
The sludge is drawn out through the pipes 27 and 29. Furthermore, the floating bioreactor 10 has a pipe 3
The generated gas is sent to the gas holder 17 via 0. In this floating type bioreactor 10, the decomposition of organic suspended solids (SS) is slow, so the BOD load is set to about 1 to 5 kg / m 3 / day. In the floating bioreactor 10, the sludge concentration in the floating bioreactor 10 is 30,000 mg / l by pulling out the sludge.
Control to the following. Further, a part or all of the sludge circulating liquid used for cleaning the membrane surface is used for stirring and mixing the floating bioreactor 10 at a membrane surface flow velocity of 0.2 m / sec or more. When the mixing is insufficient only by stirring with the circulating liquid, air lift stirring with the generated gas of the floating bioreactor 10 is also used. Normally, this operation results in a BOD removal rate of 95%
The above can be expected.

【0029】次に、本発明の有機性の懸濁物質(SS)
を含む高濃度有機性廃水の嫌気性処理方法を図1を用い
て説明する。まず、原液槽1内の有機性の懸濁物質を高
濃度に含む廃水を、配管2を介して洗浄槽3に送る。こ
こでは、井水又は循環水によって、有機性の懸濁物質
(SS)が充分に洗浄されることによって、有機性の懸
濁物質(SS)と液とに充分に分離することができる。
そして、例えば、芋の皮,根,幹などのように分解され
ずらい300μm以上の有機性の懸濁物質(SS)が、
ろ過部材3によって除去される。ろ過液の粘性は、10
cP以下になるように処理される。
Next, the organic suspended substance (SS) of the present invention
An anaerobic treatment method for high-concentration organic wastewater containing the above will be described with reference to FIG. First, waste water containing a high concentration of organic suspended substances in the stock solution tank 1 is sent to the cleaning tank 3 via the pipe 2. Here, the organic suspended substance (SS) can be sufficiently separated into the liquid by thoroughly washing the organic suspended substance (SS) with well water or circulating water.
And, for example, organic suspension substances (SS) of 300 μm or more which are hard to be decomposed, such as potato skin, root, and trunk,
It is removed by the filtering member 3. The viscosity of the filtrate is 10
It is processed so as to be less than or equal to cP.

【0030】次に、ろ過液を配管5を介して固液分離装
置6に送る。ここでは、沈降速度が1m/時以上の比較
的粒径の大きな有機性の懸濁物質(SS)は、濃縮液6
a側に移行し、上澄液6b側には沈降速度1m/時以下
の比較的粒径の軽い有機性の懸濁物質(SS)のみとな
る。この際、濃縮液6aの有機性の懸濁物質(SS)の
濃度は、50,000mg/l以下に制御する。
Next, the filtrate is sent to the solid-liquid separator 6 through the pipe 5. Here, the organic suspension material (SS) having a relatively large particle size with a sedimentation speed of 1 m / hour or more is
Transferred to the side a, and on the side of the supernatant 6b, only the organic suspended substance (SS) having a sedimentation speed of 1 m / hour or less and a relatively small particle size is formed. At this time, the concentration of the organic suspended substance (SS) in the concentrated liquid 6a is controlled to 50,000 mg / l or less.

【0031】このように、有機性の懸濁物質(SS)を
含む高濃度有機性廃水は、有機性の懸濁物質(SS)を
あまり含まない上澄液6bと、高濃度の有機性の懸濁物
質(SS)を含む濃縮液6aとに分離される。
As described above, the high-concentration organic wastewater containing the organic suspended solids (SS) contains the supernatant liquid 6b containing little organic suspended solids (SS) and the high-concentrated organic wastewater. It is separated into a concentrated liquid 6a containing a suspended substance (SS).

【0032】次いで、上澄液6bと濃縮液6aとは、夫
々別々に処理される。まず、上澄液6bの処理について
説明する。有機性の懸濁物質(SS)の濃度の低い上澄
液6bは、流動床リアクターなどの高効率嫌気性バイオ
リアクター12を用いて、BOD負荷5Kg- BOD/m
3 /日以上の高負荷で処理される。
Then, the supernatant 6b and the concentrate 6a are separately processed. First, the treatment of the supernatant 6b will be described. The supernatant liquid 6b having a low concentration of organic suspended solids (SS) was used in a high efficiency anaerobic bioreactor 12 such as a fluidized bed reactor to obtain a BOD load of 5 kg-BOD / m.
It is processed with a high load of 3 / day or more.

【0033】固液分離装置6から流出する上澄液6b
は、配管7を介して上澄液貯槽8に貯留され、配管11
を介して高効率嫌気性バイオリアクター12に送られ
る。この際、高効率嫌気性バイオリアクター12は、無
希釈時の上澄液6bのCODcr濃度によって、3種類の
バイオリアクターが用意されている。即ち、無希釈時の
上澄液6bのCODcr濃度が、6,000mg/l以下の場合に
は、UASB、6,000 〜15,000mg/l以下の場合には、
固定床、15,000mg/l以上の場合には、流動床、とされ
る。
Supernatant liquid 6b flowing out of the solid-liquid separation device 6
Is stored in the supernatant liquid storage tank 8 through the pipe 7, and the pipe 11
To the highly efficient anaerobic bioreactor 12 via. At this time, as the high-efficiency anaerobic bioreactor 12, three types of bioreactors are prepared depending on the CODcr concentration of the supernatant 6b when undiluted. That is, when the CODcr concentration of the undiluted supernatant 6b is 6,000 mg / l or less, UASB, and when 6,000 to 15,000 mg / l or less,
A fixed bed, and a fluidized bed when it is 15,000 mg / l or more.

【0034】高効率嫌気性バイオリアクター12では、
有機性の懸濁物質(SS)の濃度の低い上澄液6bのた
め、有機物の分解率が飛躍的に向上し、嫌気性のみで9
0%以上のBOD除去率が達成され、その結果として大
量のメタンガスが得られる。発生したメタンガスは、配
管16を介してガスホルダー17に貯留される。
In the high efficiency anaerobic bioreactor 12,
Since the supernatant 6b has a low concentration of organic suspended solids (SS), the decomposition rate of organic substances is dramatically improved, and only 9 is anaerobic.
A BOD removal rate of 0% or more is achieved, resulting in a large amount of methane gas. The generated methane gas is stored in the gas holder 17 via the pipe 16.

【0035】次に、濃縮液6aの処理について説明す
る。高濃度の有機性の懸濁物質(SS)を含む濃縮液6
aは、限外ろ過膜や精密ろ過膜を有する膜分離装置24
と組み合わせた浮遊型バイオリアクター10で処理され
る。
Next, the treatment of the concentrated liquid 6a will be described. Concentrated liquid containing high concentration of organic suspended solids (SS) 6
a is a membrane separation device 24 having an ultrafiltration membrane or a microfiltration membrane
It is processed in the floating bioreactor 10 in combination with.

【0036】高濃度の有機性の懸濁物質(SS)を含む
濃縮液6aは、固液分離装置6の濃縮液6a側と連絡す
る配管9を介して浮遊型バイオリアクター10に送られ
る。浮遊型バイオリアクター10では、汚泥循環液によ
る撹拌作用や発生ガスによるエアリフトによる撹拌作用
によって撹拌されながら、BOD負荷1〜5kg−BOD
/m3/日程度の比較的高負荷で処理される。そして、浮
遊型バイオリアクター10内の汚泥を引き抜いて、汚泥
濃度が30,000mg/l以下になるように制御する。同時
に、循環水槽22によって、浮遊型バイオリアクター1
0内の汚泥は、膜分離装置24によって、膜分離処理さ
れる。
The concentrated liquid 6a containing a high-concentration organic suspended substance (SS) is sent to the floating bioreactor 10 through a pipe 9 which communicates with the concentrated liquid 6a side of the solid-liquid separator 6. In the floating bioreactor 10, the BOD load is 1 to 5 kg-BOD while being agitated by the agitating action of the sludge circulating liquid and the agitating action of the air lift by the generated gas.
It is processed at a relatively high load of about / m 3 / day. Then, the sludge in the floating bioreactor 10 is extracted and controlled so that the sludge concentration becomes 30,000 mg / l or less. At the same time, by the circulating water tank 22, the floating bioreactor 1
The sludge in 0 is subjected to a membrane separation process by the membrane separation device 24.

【0037】以上のように、上澄液6bと濃縮液6aと
は、夫々別々に処理するため、有機性の懸濁物質(S
S)の滞留時間を飛躍的に長く保持することができるこ
と、酸素や菌体を高濃度に保持できること、処理水質が
良好でかつ安定していること、などの利点がある。これ
によって、BOD負荷2Kg−BOD/m3/日程度の比較
的高負荷で処理が可能で、余剰汚泥の発生を非常に小さ
くできる。また、発生した汚泥は、比較的簡単に濃縮・
脱水できるので、汚泥処理に掛かるエネルギーや薬品費
を節減できる。
As described above, since the supernatant liquid 6b and the concentrated liquid 6a are separately processed, the organic suspended substance (S
There are advantages such that the retention time of S) can be remarkably extended, oxygen and bacteria can be maintained at a high concentration, and the treated water quality is good and stable. As a result, the treatment can be performed with a relatively high load of BOD load of about 2 kg-BOD / m 3 / day, and the generation of excess sludge can be made extremely small. In addition, the generated sludge can be concentrated and
Since it can be dehydrated, energy and chemical costs for sludge treatment can be saved.

【0038】次に、本発明をとうもろこし焼酎廃液に適
用した場合について説明する。まず、上澄液ついて、C
ODcr濃度18,000mg/lのとうもろこし焼酎廃液を、
流動型バイオリアクターを用いて処理したところ、BO
D負荷13.5Kg−BOD/m3/日、BOD除去率85%以
上が得られた。また、CODcrの90%以上がメタン
として回収できた。
Next, the case where the present invention is applied to corn shochu waste liquid will be described. First, for the supernatant, C
Waste liquor from corn with an ODcr concentration of 18,000 mg / l,
When treated with a fluidized bioreactor, BO
A D load of 13.5 Kg-BOD / m 3 / day and a BOD removal rate of 85% or more were obtained. Further, 90% or more of CODcr could be recovered as methane.

【0039】次に、濃縮液ついて、とうもろこし焼酎廃
液では、20,000mg/lの有機性の懸濁物質(SS)の9
0%以上が分解可能で、CODcrの除去率は90%以
上であった。また、除去CODcrの90%以上がメタ
ンとして回収できた。
Next, concerning the concentrated liquid, in the corn shochu waste liquid, 9% of 20,000 mg / l of the organic suspended substance (SS) was added.
0% or more was decomposable, and the CODcr removal rate was 90% or more. Further, 90% or more of the removed CODcr could be recovered as methane.

【0040】図2および図3は、この実験に基づいて作
成したもので、図2はとうもろこし焼酎廃液のメタン醗
酵処理における汚泥転換率を示し、図3はとうもろこし
焼酎廃液のメタン醗酵処理におけるCOD除去率を示
す。
FIGS. 2 and 3 were prepared based on this experiment. FIG. 2 shows the sludge conversion rate in the methane fermentation treatment of the corn shochu waste liquor, and FIG. 3 shows the COD removal in the methane fermentation treatment of the corn shochu waste liquor. Indicates the rate.

【0041】[0041]

【発明の効果】以上説明したように本発明に係る有機性
の懸濁物質を含む高濃度有機性廃水の嫌気性処理方法お
よびその装置によれば、高濃度の有機性の懸濁物質(S
S)を含む高濃度有機性廃水の嫌気性処理するに際し、
希釈水又は処理水によって、有機性の懸濁物質(SS)
を充分に洗浄し、固液分離して、有機性の懸濁物質(S
S)濃度の比較的小さい上澄液と高濃度に有機性の懸濁
物質(SS)を含む濃縮液とに分離し、上澄液はUAS
B,固体床,流動床といった高効率嫌気性バイオリアク
ターで高速に処理し、濃縮液は浮遊型バイオリアクター
と膜分離装置とを組み合わせた装置で処理するものであ
るから、有機性の懸濁物質(SS)の分解率が飛躍的に
向上し、嫌気性処理のみで90%以上のBOD除去率が
達成され、その結果として大量のメタンガスが得られ
る。発生したメタンガスは、エネルギー源として利用が
可能である。上澄液を処理する嫌気性バイオリアクター
と濃縮液を処理する高効率の浮遊型ドイオリアクターと
に掛かる負荷を平均すると、BOD負荷3.3Kg −BOD
/m3/日以上の高負荷を達成することができるので、装
置の設置面積を小さくでき、建設コストを節減できる。
As described above, according to the method and apparatus for anaerobic treatment of high-concentration organic wastewater containing organic suspended matter according to the present invention, the high-concentration organic suspended matter (S
During the anaerobic treatment of high-concentration organic wastewater containing S),
Organic suspension substance (SS) by dilution water or treated water
Are thoroughly washed, and solid-liquid separation is performed, and an organic suspended substance (S
S) Separation into a supernatant liquid having a relatively low concentration and a concentrated liquid containing a high concentration of an organic suspended substance (SS), and the supernatant liquid is UAS.
B, a high-efficiency anaerobic bioreactor such as a solid bed or a fluidized bed is processed at a high speed, and a concentrated liquid is processed by a device combining a floating bioreactor and a membrane separation device. The decomposition rate of (SS) is dramatically improved, and a BOD removal rate of 90% or more is achieved only by anaerobic treatment, and as a result, a large amount of methane gas is obtained. The generated methane gas can be used as an energy source. The average load applied to the anaerobic bioreactor that processes the supernatant and the highly efficient floating doio reactor that processes the concentrate is a BOD load of 3.3 kg-BOD.
Since it is possible to achieve a high load of / m 3 / day or more, the installation area of the device can be reduced and construction costs can be reduced.

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

【図1】本発明に係る有機性の懸濁物質を含む高濃度有
機性廃水の嫌気性処理装置の一実施例を示す説明図であ
る。
FIG. 1 is an explanatory view showing an embodiment of an anaerobic treatment apparatus for high-concentration organic wastewater containing an organic suspended substance according to the present invention.

【図2】とうもろこし焼酎廃液のメタン醗酵処理におけ
る汚泥転換率を示しグラフである。
FIG. 2 is a graph showing a sludge conversion rate in a methane fermentation process of corn shochu waste liquid.

【図3】とうもろこし焼酎廃液のメタン醗酵処理におけ
るCOD除去率を示すグラフである。
FIG. 3 is a graph showing the COD removal rate in the methane fermentation treatment of corn shochu waste liquid.

【符号の説明】[Explanation of symbols]

1 原液槽 3 洗浄装置 6 固液分離装置 10 浮遊型バイオリアクター 12 嫌気性バイオリアクター 23 循環水槽 24 膜分離装置 1 stock solution tank 3 washing device 6 solid-liquid separation device 10 floating bioreactor 12 anaerobic bioreactor 23 circulating water tank 24 membrane separation device

Claims (7)

【特許請求の範囲】[Claims] 【請求項1】 有機性の懸濁物質を高濃度に含む廃水を
洗浄し、固液分離を行ない、固液分離された上澄液を、
嫌気性バイオリアクターに供給して、メタン醗酵により
処理し、固液分離された有機性の懸濁物質を、膜分離装
置を有する浮遊型の嫌気性バイオリアクターに供給し
て、メタン醗酵により処理することを特徴とする有機性
の懸濁物質を含む高濃度有機性廃水の嫌気性処理方法。
1. Washing wastewater containing an organic suspended substance in a high concentration, performing solid-liquid separation, and separating the solid-liquid separated supernatant liquid,
It is supplied to an anaerobic bioreactor and treated by methane fermentation, and the solid-liquid separated organic suspended substance is supplied to a floating type anaerobic bioreactor having a membrane separation device and treated by methane fermentation. An anaerobic treatment method for high-concentration organic wastewater containing organic suspended matter, which is characterized by the above.
【請求項2】 請求項1において、有機性の懸濁物質を
高濃度に含む廃水を処理水又は希釈水で洗浄することを
特徴とする有機性の懸濁物質を含む高濃度有機性廃水の
嫌気性処理方法。
2. The high-concentration organic wastewater containing organic suspended substances according to claim 1, wherein the wastewater containing high-concentration organic suspended substances is washed with treated water or diluted water. Anaerobic treatment method.
【請求項3】 請求項1において、有機性の懸濁物質を
含む高濃度有機性廃水が、焼酎廃水,ビール酵母洗浄廃
水,清酒の洗米廃水,澱粉廃液であることを特徴とする
有機性の懸濁物質を含む高濃度有機性廃水の嫌気性処理
方法。
3. The organic wastewater according to claim 1, wherein the high-concentration organic wastewater containing organic suspended matter is shochu wastewater, brewer's yeast wash wastewater, sake rinsing wastewater, and starch wastewater. Anaerobic treatment method for highly concentrated organic wastewater containing suspended solids.
【請求項4】 請求項1において、有機性の懸濁物質を
高濃度に含む廃水を洗浄し、300μm以上の有機性の
懸濁物質を除去することを特徴とする有機性の懸濁物質
を含む高濃度有機性廃水の嫌気性処理方法。
4. The organic suspended substance according to claim 1, which is characterized in that waste water containing a high concentration of the organic suspended substance is washed to remove the organic suspended substance of 300 μm or more. Anaerobic treatment method for high concentration organic wastewater containing.
【請求項5】 有機性の懸濁物質を高濃度に含む廃水を
貯留する原液槽と、有機性の懸濁物質を高濃度に含む廃
水を洗浄する洗浄装置と、固液分離装置と、固液分離装
置の上澄液を取り込み、メタン醗酵により処理する嫌気
性バイオリアクリーと、固液分離装置の濃縮された有機
性の懸濁物質を高濃度に含む廃水を取り込み、メタン醗
酵により処理する浮遊型の嫌気性バイオリアクリーと、
浮遊型の嫌気性バイオリアクリーと連結する膜分離装置
と、を備えたことを特徴とする有機性の懸濁物質を含む
高濃度有機性廃水の嫌気性処理装置。
5. A stock solution tank for storing waste water containing a high concentration of organic suspended solids, a washing device for washing waste water containing a high concentration of organic suspended solids, a solid-liquid separation device, and a solid-liquid separator. Anaerobic bioreakly, which takes in the supernatant of the liquid separator and treats it by methane fermentation, and wastewater containing a high concentration of concentrated organic suspended matter in the solid-liquid separator, which is treated by methane fermentation. Floating type anaerobic bio rear cree,
An anaerobic treatment device for high-concentration organic wastewater containing organic suspended matter, comprising: a membrane separation device connected to a floating type anaerobic bioreactor.
【請求項6】 請求項5において、有機性の懸濁物質を
高濃度に含む廃水を洗浄する洗浄装置には、300μm
以上の有機性の懸濁物質を除去するろ過部材が設けられ
ていることを特徴とする有機性の懸濁物質を含む高濃度
有機性廃水の嫌気性処理装置。
6. The cleaning device according to claim 5, wherein the cleaning device for cleaning the wastewater containing a high concentration of organic suspended solids is 300 μm.
An anaerobic treatment apparatus for high-concentration organic wastewater containing organic suspended matter, comprising a filter member for removing the organic suspended matter described above.
【請求項7】 請求項5において、浮遊型の嫌気性バイ
オリアクリーと、膜分離装置との間には、循環装置が介
装されていることを特徴とする有機性の懸濁物質を含む
高濃度有機性廃水の嫌気性処理装置。
7. The organic suspension substance according to claim 5, wherein a circulation device is interposed between the floating type anaerobic bioreactor and the membrane separation device. Anaerobic treatment equipment for highly concentrated organic wastewater.
JP30628291A 1991-11-21 1991-11-21 Anaerobic treatment method and apparatus for high-concentration organic wastewater containing organic suspended matter Expired - Fee Related JP3152357B2 (en)

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Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000263018A (en) * 1999-03-15 2000-09-26 Toshiba Corp Treatment apparatus for organic waste
KR100363562B1 (en) * 1999-10-28 2003-03-29 선일엔지니어링 주식회사 The treatment method and apparatus of the organic wastewater having the high concentration
JP2005218897A (en) * 2004-02-03 2005-08-18 Babcock Hitachi Kk Methane fermentation apparatus
CN1331774C (en) * 2004-12-14 2007-08-15 中国科学院生态环境研究中心 Tubular dynamic membrane reactor for biological catalytic oxidation
CN100465108C (en) * 2007-01-18 2009-03-04 同济大学 Multifunction nitration back nitration integrated auto dynamic film bioreactor
JP2009255074A (en) * 2008-04-11 2009-11-05 Hanbat National Univ Industry-Academic Cooperation Foundation Anaerobic integration process apparatus for organic waste treatment
JP2011528986A (en) * 2008-07-23 2011-12-01 パーパスエナジー・インコーポレイテッド Method and apparatus for treating organic waste
JP2012187534A (en) * 2011-03-11 2012-10-04 National Institute Of Advanced Industrial Science & Technology Method for treating organic matter waste liquid
JP2013056321A (en) * 2011-09-09 2013-03-28 Japan Organo Co Ltd Anaerobic biological treatment method and anaerobic biological treatment apparatus
JP2014008431A (en) * 2012-06-28 2014-01-20 Swing Corp Method and apparatus for anaerobic digestion treatment of organic wastewater
WO2014156216A1 (en) * 2013-03-27 2014-10-02 栗田工業株式会社 Anaerobic treatment method

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000263018A (en) * 1999-03-15 2000-09-26 Toshiba Corp Treatment apparatus for organic waste
KR100363562B1 (en) * 1999-10-28 2003-03-29 선일엔지니어링 주식회사 The treatment method and apparatus of the organic wastewater having the high concentration
JP2005218897A (en) * 2004-02-03 2005-08-18 Babcock Hitachi Kk Methane fermentation apparatus
CN1331774C (en) * 2004-12-14 2007-08-15 中国科学院生态环境研究中心 Tubular dynamic membrane reactor for biological catalytic oxidation
CN100465108C (en) * 2007-01-18 2009-03-04 同济大学 Multifunction nitration back nitration integrated auto dynamic film bioreactor
JP2009255074A (en) * 2008-04-11 2009-11-05 Hanbat National Univ Industry-Academic Cooperation Foundation Anaerobic integration process apparatus for organic waste treatment
JP2011528986A (en) * 2008-07-23 2011-12-01 パーパスエナジー・インコーポレイテッド Method and apparatus for treating organic waste
JP2012187534A (en) * 2011-03-11 2012-10-04 National Institute Of Advanced Industrial Science & Technology Method for treating organic matter waste liquid
JP2013056321A (en) * 2011-09-09 2013-03-28 Japan Organo Co Ltd Anaerobic biological treatment method and anaerobic biological treatment apparatus
JP2014008431A (en) * 2012-06-28 2014-01-20 Swing Corp Method and apparatus for anaerobic digestion treatment of organic wastewater
WO2014156216A1 (en) * 2013-03-27 2014-10-02 栗田工業株式会社 Anaerobic treatment method

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