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JPH0635000B2 - Sewage treatment equipment - Google Patents
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JPH0635000B2 - Sewage treatment equipment - Google Patents

Sewage treatment equipment

Info

Publication number
JPH0635000B2
JPH0635000B2 JP4861685A JP4861685A JPH0635000B2 JP H0635000 B2 JPH0635000 B2 JP H0635000B2 JP 4861685 A JP4861685 A JP 4861685A JP 4861685 A JP4861685 A JP 4861685A JP H0635000 B2 JPH0635000 B2 JP H0635000B2
Authority
JP
Japan
Prior art keywords
reaction tank
fluidized bed
membrane separation
liquid
separation device
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 - Lifetime
Application number
JP4861685A
Other languages
Japanese (ja)
Other versions
JPS61209097A (en
Inventor
幹夫 北川
元之 依田
敦 渡辺
美和子 服部
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 JP4861685A priority Critical patent/JPH0635000B2/en
Publication of JPS61209097A publication Critical patent/JPS61209097A/en
Publication of JPH0635000B2 publication Critical patent/JPH0635000B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Biological Treatment Of Waste Water (AREA)
  • Separation Using Semi-Permeable Membranes (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、汚水の処理装置に係り、特に流動床反応槽と
膜分離装置とを組み合せた汚水の処理装置に関するもの
である。
TECHNICAL FIELD The present invention relates to an apparatus for treating wastewater, and more particularly to an apparatus for treating wastewater in which a fluidized bed reactor and a membrane separator are combined.

[従来の技術] 各種産業廃水、生活廃水等の有機性廃水の処理方法とし
て、生物的処理方法がある。
[Prior Art] There is a biological treatment method as a treatment method of organic wastewater such as various industrial wastewater and domestic wastewater.

生物的処理方法は、微生物を利用して主に水中の有機物
を除去するために用いられる方法である。この生物的処
理を行う装置として流動床式のものがある。
The biological treatment method is a method mainly used for removing organic matter in water by utilizing microorganisms. As a device for performing this biological treatment, there is a fluidized bed type.

流動床式の汚水の処理装置は、容器状の反応槽内に菌体
を担持させた担体を投入して流動床を形成し、この反応
槽内に原水を供給し、槽内を流動状態に保ちつつ、処理
を行うものである。流動床方式の汚水の処理装置は、微
生物を担体粒子表面に高濃度で保持せしめることができ
るので、処理効率が高く、好適な処理方式である。
A fluidized bed type wastewater treatment device forms a fluidized bed by adding a carrier supporting cells to a container-shaped reaction tank, and supplies raw water into the reaction tank to bring the tank into a fluidized state. The processing is carried out while keeping it. The fluidized bed type sewage treatment apparatus has a high treatment efficiency because it can retain the microorganisms on the surface of the carrier particles at a high concentration, which is a preferable treatment method.

また、近年、処理水の水質をより優れたものとする高度
な処理を要する場合も多くなっている。そのため、例え
ば、2次処理(生物処理)液に更に高次の処理を施す高
次処理が採用されることがある。この高次処理を行う装
置の1つとして膜分離装置がある。
Further, in recent years, there are many cases in which advanced treatment for improving the quality of treated water is required. Therefore, for example, a higher-order treatment for applying a higher-order treatment to the secondary treatment (biological treatment) liquid may be adopted. There is a membrane separation device as one of the devices for performing this higher-order treatment.

ところで、流動床反応槽においては、一般に流動床の担
体(ゼオライトや砂等)を所定の展開率で展開させるた
めに、流動床反応槽から取り出された処理液の一部を流
動床反応槽の入口側に循環させるようにしており、この
処理液の循環を行うための循環ポンプが設置されてい
る。
By the way, in a fluidized bed reaction tank, a part of the treatment liquid taken out from the fluidized bed reaction tank is generally stored in the fluidized bed reaction tank in order to develop a carrier (zeolite, sand, etc.) in the fluidized bed at a predetermined expansion rate. It is arranged to circulate on the inlet side, and a circulation pump for circulating this treatment liquid is installed.

また、精密濾過膜や限外濾過膜等の透過膜を内蔵した膜
分離装置においては、この膜分離装置の液受け入れ側に
所定圧力で被処理液を供給する必要があり、このため
に、膜分離装置の上流側に液供給用のポンプを設置して
いる。
Further, in a membrane separation device having a permeable membrane such as a microfiltration membrane or an ultrafiltration membrane, it is necessary to supply the liquid to be treated at a predetermined pressure to the liquid receiving side of the membrane separation device. A pump for liquid supply is installed on the upstream side of the separator.

而して、流動床式反応槽と膜分離装置とを組み合せた従
来の汚水の処理装置においては、少なくとも2台のポン
プ、即ち、流動床反応槽の展開率を保つために該反応槽
の処理液を循環させるための循環ポンプと、膜分離装置
に液を供給するための供給ポンプとを設置しなければな
らなかった。
Thus, in the conventional sewage treatment apparatus in which the fluidized bed type reaction tank and the membrane separator are combined, at least two pumps, that is, the treatment of the reaction tank in order to maintain the expansion rate of the fluidized bed reaction tank. A circulation pump for circulating the liquid and a supply pump for supplying the liquid to the membrane separation device had to be installed.

[発明が解決しようとする問題点] 流動床反応槽と膜分離装置とを組み合せた従来の汚水の
処理装置においては、ポンプの設置台数が多く、コスト
(イニシャルコスト及びランニングコストの双方)が増
大していた。
[Problems to be Solved by the Invention] In a conventional sewage treatment apparatus that combines a fluidized bed reactor and a membrane separator, the number of pumps installed is large, and the cost (both initial cost and running cost) increases. Was.

また、膜分離装置の濃縮液は、供給ポンプ、ボール洗浄
装置、膜モジュール等から発生する熱によって加温され
ているのであるが、この濃縮液に加えられる熱の有効な
利用が図られていなかった。(流動床反応槽が嫌気性流
動床反応槽である場合、処理槽内の液温を高めると嫌気
性分解反応が活発となる。従って、膜分離装置の濃縮液
に加えられる熱を、流動床反応槽内の液温を高めるため
の加熱用熱源として利用すれば、それだけ外部から熱エ
ネルギーを加えることなく、処理効率を高めることがで
きるはずである。しかるに、従来の汚水の処理装置にお
いては、かかる膜分離装置において生ずる熱の有効な利
用が図られていなかった。) そのため、汚水処理装置の系統全体におけるエネルギー
消費に無駄があった。
Further, the concentrated liquid of the membrane separation device is heated by the heat generated from the supply pump, the ball cleaning device, the membrane module, etc., but the heat applied to this concentrated liquid has not been effectively utilized. It was (When the fluidized bed reaction tank is an anaerobic fluidized bed reaction tank, increasing the liquid temperature in the treatment tank activates the anaerobic decomposition reaction. Therefore, the heat applied to the concentrated liquid of the membrane separation device is applied to the fluidized bed reaction tank. If it is used as a heat source for heating to raise the temperature of the liquid in the reaction tank, it should be possible to increase the treatment efficiency without adding heat energy from the outside. The heat generated in such a membrane separation device has not been effectively used.) Therefore, there is a waste of energy consumption in the entire system of the wastewater treatment device.

[問題点を解決するための手段] 本発明は、微生物を担持した流動可能な担持粒子を内蔵
する流動床反応槽を備えてなり、該反応槽上部の取出口
から取り出された処理液を、循環ポンプを介して反応槽
底部の導入口へ循環させ、前記担持粒子に保持した微生
物で汚水を処理する汚水の処理装置において、循環ポン
プの吐出側に連絡されており前記循環される反応槽処理
液を受け入れて膜分離処理する透過膜を内蔵した膜分離
装置を設置すると共に、この膜分離装置の濃縮液を前記
反応槽底部の導入口へ循環させるように膜分離装置と流
動床反応槽とを連絡してなり、前記循環ポンプの吐出圧
力及び吐出流によって該膜分離装置での膜透過処理と前
記流動床反応槽での担体粒子の流動とを行なわせるよう
にしたことを特徴とするものである。
[Means for Solving the Problems] The present invention comprises a fluidized bed reaction tank containing flowable carrier particles carrying microorganisms, and a treatment liquid taken out from an outlet at the upper part of the reaction tank, In a sewage treatment device that circulates to an inlet at the bottom of a reaction tank through a circulation pump and treats sewage with microorganisms held on the carrier particles, the circulated reaction tank treatment that is connected to the discharge side of the circulation pump A membrane separation device having a built-in permeable membrane for receiving the liquid and performing a membrane separation process is installed, and a membrane separation device and a fluidized bed reaction tank are provided so that the concentrated liquid of the membrane separation device is circulated to the inlet at the bottom of the reaction tank. Characterized in that the membrane permeation treatment in the membrane separation device and the carrier particle flow in the fluidized bed reaction tank are performed by the discharge pressure and discharge flow of the circulation pump. Is.

[作用] 本発明においては、流動床反応槽における担体粒子の展
開率を所定のものとするために、流動床反応槽上部の取
出口から取り出して流動床反応槽底部の導入口に循環さ
せる液として、膜分離装置の濃縮液(濃縮側出口液)が
用いられる。
[Operation] In the present invention, a liquid which is taken out from the outlet of the upper portion of the fluidized bed reaction tank and circulated to the inlet of the lower portion of the fluidized bed reaction tank in order to make the expansion rate of the carrier particles in the fluidized bed reaction tank a predetermined value. As the liquid, a concentrated liquid of the membrane separation device (concentration side outlet liquid) is used.

そのため、ポンプの設置台数が減少できるようになり、
コスト(イニシャルコスト及びランニングコストの双
方)を低減することが可能とされる。
Therefore, the number of installed pumps can be reduced,
The cost (both initial cost and running cost) can be reduced.

また、膜分離装置の濃縮液が保有する熱を、流動床反応
槽内の液温を高めるための熱エネルギーとして利用でき
るようになる。
Further, the heat retained by the concentrated liquid of the membrane separation device can be used as heat energy for increasing the liquid temperature in the fluidized bed reaction tank.

なお、膜分離装置に供給される液量は(処理水として該
膜分離装置から取り出される水の量よりも例えば数十倍
程度も多く)流動床反応槽の展開率を所定展開率以上に
保つために必要とする最低水準よりも大量であること、
膜分離装置から取り出される濃縮液は、通常1kg/m
2若しくはそれ以上の圧力を保持していることから、膜
分離装置の濃縮液は、流動床反応槽における担体の展開
を行わせるための循環液として十分に使用できる。
The amount of liquid supplied to the membrane separator (for example, about several tens of times larger than the amount of water taken out from the membrane separator as treated water) keeps the expansion rate of the fluidized bed reaction tank at a predetermined expansion rate or more. Greater than the minimum level required for
Concentrated liquid taken out from the membrane separator is usually 1 kg / m
Since the pressure of 2 or more is maintained, the concentrated liquid of the membrane separation device can be sufficiently used as a circulating liquid for developing the carrier in the fluidized bed reaction tank.

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

第1図は本発明の実施例に係る汚水の処理装置の構成を
示す系統図である。第1図において2はゼオライトや砂
等の適宜の流動担体を有する流動床反応槽であって、そ
の底部に接続された原水供給管1から原水が導入され
る。流動床反応槽2の上部には該流動床反応槽2内にお
いて処理を受けた液を取り出すための取り出し管3が接
続されており、この取り出し管3の途中にはポンプ4が
設置されている。
FIG. 1 is a system diagram showing a configuration of a wastewater treatment apparatus according to an embodiment of the present invention. In FIG. 1, reference numeral 2 denotes a fluidized bed reaction tank having an appropriate fluid carrier such as zeolite or sand, and raw water is introduced from a raw water supply pipe 1 connected to the bottom of the fluidized bed reaction tank. A take-out pipe 3 for taking out the liquid treated in the fluidized-bed reaction tank 2 is connected to the upper part of the fluidized-bed reaction tank 2, and a pump 4 is installed in the middle of the taken-out pipe 3. .

このポンプ4によって加圧された液は膜分離装置(例え
ば、精密濾過装置、限外濾過装置、逆浸透装置など)5
に導入される。膜分離装置5の透過膜6を透過した液
は、処理液として配管7から取り出され、放流工程や再
利用工程に送られる。膜分離装置5の濃縮液は配管8か
ら流動床反応槽2の液導入側に循環される。
The liquid pressurized by the pump 4 is a membrane separation device (for example, microfiltration device, ultrafiltration device, reverse osmosis device, etc.) 5
Will be introduced to. The liquid that has permeated the permeable membrane 6 of the membrane separation device 5 is taken out from the pipe 7 as a treatment liquid and sent to the discharge process or the reuse process. The concentrated liquid of the membrane separation device 5 is circulated from the pipe 8 to the liquid introduction side of the fluidized bed reaction tank 2.

本実施例においては、膜分離装置5を迂回するバイパス
管路9が設置されており、ポンプ4によって加圧された
液はこのバイパス管路9を通って直に流動床反応槽2の
液導入側に循環可能とされている。
In the present embodiment, a bypass pipe 9 that bypasses the membrane separation device 5 is installed, and the liquid pressurized by the pump 4 is directly introduced into the fluidized bed reaction tank 2 through the bypass pipe 9. It is possible to circulate to the side.

図中10、11及び12はそれぞれ配管3、8及び9に
設けられた弁である。
In the figure, 10, 11 and 12 are valves provided in the pipes 3, 8 and 9, respectively.

このように構成された実施例に係る汚水の処理装置にお
いて、導入管1から流動床反応槽2の底部に供給された
液は、この反応槽内部において形成されている流動床に
よって嫌気的若しくは好気的な処理を受ける。この流動
床反応槽2においては、配管3及び8を通って循環され
る液によって流動担体が所定の展開率となるように展開
されている。
In the sewage treatment apparatus according to the example configured as described above, the liquid supplied from the introduction pipe 1 to the bottom of the fluidized bed reaction tank 2 is anaerobic or favorable due to the fluidized bed formed inside the reaction tank. Receive a tempered treatment. In the fluidized bed reaction tank 2, the fluidized carrier is developed by the liquid circulated through the pipes 3 and 8 so that the fluidized carrier has a predetermined development rate.

この循環された液は、膜分離装置5及びポンプ4におい
て発生するジュール熱等の熱によって加温されており
(運転条件によっては例えば10〜20℃程度昇温す
る。)、流動床反応槽2内の液温も高められている。そ
のため、この流動床反応槽2内においては、極めて効率
の良い生物処理が行われる。
The circulated liquid is heated by heat such as Joule heat generated in the membrane separation device 5 and the pump 4 (for example, the temperature is raised to about 10 to 20 ° C. depending on operating conditions), and the fluidized bed reaction tank 2 is used. The liquid temperature inside is also raised. Therefore, extremely efficient biological treatment is performed in the fluidized bed reaction tank 2.

生物処理を受けた液は、配管3、ポンプ4を経て膜分離
装置5に導入され膜分離処理を受け、これにより極めて
水質の優れた処理水が得られる。
The liquid subjected to the biological treatment is introduced into the membrane separation device 5 through the pipe 3 and the pump 4 and undergoes the membrane separation treatment, whereby treated water having extremely excellent water quality is obtained.

バイパス管路9は、膜分離装置5を修理したり膜の洗浄
を行ったりするために膜分離装置5を停止する際に使用
される系統であって、弁10及び11を閉とすると共に
弁12を開とすることにより、流動床反応槽2の上部の
取り出し管3から取り出された液はポンプ4から配管9
を経て流動床反応槽2の底部の液導入側に循環される。
そのため、本実施例においては、膜分離装置5を停止し
ている時でも、連続的に流動床反応槽2の運転を継続す
ることができる。
The bypass line 9 is a system used when the membrane separation device 5 is stopped in order to repair the membrane separation device 5 or clean the membrane, and the valves 10 and 11 are closed and the valve 10 is closed. By opening 12, the liquid taken out from the take-out pipe 3 in the upper part of the fluidized bed reaction tank 2 is fed from the pump 4 to the pipe 9
And is circulated to the liquid introduction side at the bottom of the fluidized bed reaction tank 2.
Therefore, in this embodiment, the operation of the fluidized bed reaction tank 2 can be continuously continued even when the membrane separation device 5 is stopped.

なお、本発明において、流動床反応槽2としては嫌気性
流動床反応槽及び好気性流動床反応槽のいずれであって
も良い。
In the present invention, the fluidized bed reaction tank 2 may be either an anaerobic fluidized bed reaction tank or an aerobic fluidized bed reaction tank.

[効果] 以上詳述した通り、本発明の汚水の処理装置は、流動床
反応槽における担体粒子の展開率を所定の展開率とする
ために、反応槽上部の取出口から取り出して反応槽底部
の導入口に循環させる循環液として、反応槽上部の取出
口から取り出された処理液を膜分離装置で膜分離処理し
て得られる濃縮液を用いるようにしたものであり、 ポンプ設置台数が少なくて足り、イニシャルコスト
及びランニングコストの双方が低減される。
[Effect] As described in detail above, in the wastewater treatment apparatus of the present invention, in order to make the expansion rate of the carrier particles in the fluidized bed reaction tank a predetermined expansion rate, it is taken out from the outlet of the upper part of the reaction tank and the bottom of the reaction tank. As the circulating liquid to be circulated to the inlet of the reactor, the concentrated liquid obtained by subjecting the treated liquid taken out from the outlet on the upper part of the reaction tank to the membrane separation treatment with a membrane separator is used. Sufficient, both initial cost and running cost are reduced.

膜分離装置やポンプにおいて発生する熱を流動床反
応槽内の液温を高めるための熱源として利用することが
でき、効率の良い生物処理を行うことが可能とされる。
The heat generated in the membrane separation device or the pump can be used as a heat source for increasing the liquid temperature in the fluidized bed reaction tank, which enables efficient biological treatment.

流動床式反応槽内の液温が高められるので、膜分離
装置の透過水量を多くすることができる。(一般に、膜
分離装置においては、処理される液の温度が高い程その
透過水量が多くなる。なお、本発明において流動床反応
槽が嫌気性流動床反応槽である場合は、その処理液温が
好気性流動反応槽のものに比べ生物反応による熱の発生
が更に多いので、膜の透過水量が一層多くなる。) 処理水は、生物処理及び膜分離装置の二段の処理を
受けているので、極めて優れた水質のものとなる。
Since the liquid temperature in the fluidized bed reactor is increased, the amount of permeated water of the membrane separation device can be increased. (In general, in a membrane separator, the higher the temperature of the liquid to be treated, the larger the amount of permeated water. In the present invention, when the fluidized bed reaction tank is an anaerobic fluidized bed reaction tank, the temperature of the treated liquid is increased. However, the amount of permeated water through the membrane is much higher than that of the aerobic fluidized reactor, because the amount of heat generated by the biological reaction is even greater.) Therefore, the water quality is extremely excellent.

等の優れた効果が奏される。And so on.

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

第1図は本発明の実施例に係る汚水の処理装置の構成を
示す系統図である。 2……流動床反応層、 4……ポンプ、 5……膜分離装置。
FIG. 1 is a system diagram showing a configuration of a wastewater treatment apparatus according to an embodiment of the present invention. 2 ... Fluidized bed reaction layer, 4 ... Pump, 5 ... Membrane separation device.

フロントページの続き (72)発明者 服部 美和子 神奈川県横浜市保土ヶ谷区仏向町1723番地 栗田工業株式会社総合研究所内 (56)参考文献 特公 昭48−40971(JP,B2) 「日本の最新技術シリーズ(2)やさし いライフサイエンス百科バイオテクノロジ ーが拓く新しい未来と工業」第146頁、昭 和56年5月31日、日本工業新聞社発行Front page continuation (72) Miwako Hattori Inventor Miwako 1723, Bulguko-cho, Hodogaya-ku, Yokohama, Kanagawa Prefecture Kurita Water Industries Co., Ltd. Research Institute (56) (2) Gentle Life Science Encyclopedia, The New Future and Industry Opened by Biotechnology ”, p. 146, May 31, 1981, published by The Nihon Kogyo Shimbun.

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】微生物を担持した流動可能な担体粒子を内
蔵する流動床反応槽を備えてなり、 該反応槽上部の取出口から取り出された処理液を、循環
ポンプを介して反応槽底部の導入口へ循環させ、前記担
体粒子に保持した微生物で汚水を処理する汚水の処理装
置において、 循環ポンプの吐出側に連絡されており前記循環される反
応槽処理液を受け入れて膜分離処理する透過膜を内蔵し
た膜分離装置を設置すると共に、 この膜分離装置の濃縮液を前記反応槽底部の導入口へ循
環させるように膜分離装置と流動床反応槽とを連絡して
なり、 前記循環ポンプの吐出圧力及び吐出流によって該膜分離
装置での膜透過処理と前記流動床反応槽での担体粒子の
流動とを行なわせるようにしたことを特徴とする汚水の
処理装置。
1. A fluidized bed reaction tank containing flowable carrier particles carrying microorganisms is provided, and a treatment liquid taken out from an outlet at the upper part of the reaction tank is supplied to a bottom of the reaction tank via a circulation pump. In a sewage treatment device that circulates to the inlet and treats sewage with microorganisms retained on the carrier particles, it is connected to the discharge side of a circulation pump and receives the circulated reaction tank treatment liquid to perform membrane separation treatment. A membrane separation device having a built-in membrane is installed, and the membrane separation device and the fluidized bed reaction tank are connected to each other so that the concentrated liquid of the membrane separation device is circulated to the inlet at the bottom of the reaction tank. The sewage treatment apparatus characterized in that the membrane permeation treatment in the membrane separation apparatus and the carrier particle flow in the fluidized bed reaction tank are performed by the discharge pressure and the discharge flow.
【請求項2】膜分離装置を迂回して循環ポンプの吐出側
と流動床反応槽とを連絡しており、膜分離装置の運転停
止時に通液されるバイパス系統が設けられていることを
特徴とする特許請求の範囲第1項に記載の汚水の処理装
置。
2. A bypass system is provided, which bypasses the membrane separation device and connects the discharge side of the circulation pump to the fluidized bed reaction tank, and is provided with a bypass system through which liquid is passed when the operation of the membrane separation device is stopped. The sewage treatment apparatus according to claim 1.
JP4861685A 1985-03-12 1985-03-12 Sewage treatment equipment Expired - Lifetime JPH0635000B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4861685A JPH0635000B2 (en) 1985-03-12 1985-03-12 Sewage treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4861685A JPH0635000B2 (en) 1985-03-12 1985-03-12 Sewage treatment equipment

Publications (2)

Publication Number Publication Date
JPS61209097A JPS61209097A (en) 1986-09-17
JPH0635000B2 true JPH0635000B2 (en) 1994-05-11

Family

ID=12808340

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4861685A Expired - Lifetime JPH0635000B2 (en) 1985-03-12 1985-03-12 Sewage treatment equipment

Country Status (1)

Country Link
JP (1) JPH0635000B2 (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2821347A1 (en) * 2001-02-23 2002-08-30 Vanlaer Fluides Et Automation AQUEOUS MEMBRANE TREATMENT SYSTEM AND FERMENTATION
JP4858467B2 (en) * 2008-03-10 2012-01-18 富士電機株式会社 Methane fermentation treatment method and methane fermentation treatment apparatus
JP5912353B2 (en) * 2011-09-09 2016-04-27 オルガノ株式会社 Anaerobic biological treatment method and anaerobic biological treatment apparatus
JP5801769B2 (en) * 2012-06-28 2015-10-28 水ing株式会社 Method and apparatus for anaerobic digestion treatment of organic wastewater

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5337428B2 (en) * 1971-10-01 1978-10-09

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
「日本の最新技術シリーズ(2)やさしいライフサイエンス百科バイオテクノロジーが拓く新しい未来と工業」第146頁、昭和56年5月31日、日本工業新聞社発行

Also Published As

Publication number Publication date
JPS61209097A (en) 1986-09-17

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