Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPH0634985B2 - Bioreactor - Google Patents
[go: Go Back, main page]

JPH0634985B2 - Bioreactor - Google Patents

Bioreactor

Info

Publication number
JPH0634985B2
JPH0634985B2 JP9295085A JP9295085A JPH0634985B2 JP H0634985 B2 JPH0634985 B2 JP H0634985B2 JP 9295085 A JP9295085 A JP 9295085A JP 9295085 A JP9295085 A JP 9295085A JP H0634985 B2 JPH0634985 B2 JP H0634985B2
Authority
JP
Japan
Prior art keywords
membrane
separation membrane
liquid
biological treatment
bioreactor
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
JP9295085A
Other languages
Japanese (ja)
Other versions
JPS61249592A (en
Inventor
幹夫 北川
良雄 谷口
光春 古市
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 JP9295085A priority Critical patent/JPH0634985B2/en
Publication of JPS61249592A publication Critical patent/JPS61249592A/en
Publication of JPH0634985B2 publication Critical patent/JPH0634985B2/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
    • 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

  • External Artificial Organs (AREA)
  • Biological Treatment Of Waste Water (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)
  • Treatment Of Biological Wastes In General (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Treatment Of Sludge (AREA)

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は生物反応装置に係り、特に限外瀘過膜や精密瀘
過膜などの分離膜に微生物を固定化させたものを用いて
生物反応を行わせるようにした生物反応装置に関するも
のである。
Description: TECHNICAL FIELD The present invention relates to a bioreactor, and in particular, it uses a separation membrane such as an ultrafiltration membrane or a precision filtration membrane in which microorganisms are immobilized to form a living organism. The present invention relates to a bioreactor designed to carry out a reaction.

[従来の技術] 生物処理装置を膜分離装置とを組み合わせた生物反応装
置が、廃水処理装置などの分野において知られている。
例えば、特開昭57−7293には生物処理装置からの
生物処理液を膜分離処理し、この濃縮液を生物処理装置
に返送するようにしたものが、また、特公昭46−41
584には生物処理後の処理水を膜分離し処理水の水質
向上を図るようにしたものが開示されている。
[Prior Art] A bioreactor in which a biotreatment device is combined with a membrane separator is known in the field of wastewater treatment devices and the like.
For example, Japanese Patent Laid-Open No. 57-7293 discloses a method in which a biological treatment liquid from a biological treatment device is subjected to membrane separation treatment and the concentrated liquid is returned to the biological treatment device.
584 discloses that the treated water after biological treatment is separated into membranes to improve the quality of the treated water.

このように、従来の膜分離装置を備えた生物反応装置に
おける膜分離膜の役割りは、生物処理装置内の汚泥濃度
を所定値以上に保持したり、生物処理水中のSS除去、
生物処理で分解されない残留成分の除去等であり、終
沈、凝集沈殿、瀘過などの役割りを果している。
Thus, the role of the membrane separation membrane in the bioreactor equipped with a conventional membrane separator, the sludge concentration in the biological treatment device is maintained at a predetermined value or more, SS removal of biological treatment water,
It removes residual components that are not decomposed by biological treatment, and plays a role in final precipitation, coagulation precipitation, and filtration.

このような従来の生物反応装置においても、例えば生物
処理装置内の微生物濃度(例えば汚泥濃度)を高めるこ
とは可能であり、これにより負荷量の高い処理装置を提
供し得る。
Even in such a conventional bioreactor, for example, it is possible to increase the concentration of microorganisms (eg, sludge concentration) in the biotreatment device, and thus a treatment device with a high load can be provided.

[発明が解決しようとする問題点] しかしながら、上記従来の生物反応装置は、それぞれ作
用の異なる生物処理装置と膜分離装置とを単に組み合わ
せたものであり、高効率化には限界があった。また、従
来の生物反応装置における分離膜には、生物処理装置か
らの膜汚染物質(例えば汚泥、残留成分、原液中の無機
物質、生物の代謝物質等)が付着し、分離膜の透過水量
を低下させ、薬品洗浄、ボール洗浄などの膜面付着物質
の除去操作を必要とした。また、従って、上記生物反応
装置においては、生物処理装置(反応槽)、分離膜の他
に、膜洗浄装置をも必要とし、三つの異なる機能を有す
るユニットが必要とされていた。
[Problems to be Solved by the Invention] However, the above-mentioned conventional bioreactor is merely a combination of a biotreatment device and a membrane separation device, each of which has a different action, and there is a limit to increase the efficiency. In addition, membrane contaminants from biological treatment equipment (such as sludge, residual components, inorganic substances in undiluted solution, and metabolites of organisms) from biological treatment equipment adhere to the separation membrane in the conventional bioreactor, and the amount of permeated water through the separation membrane increases. It was necessary to remove the substances adhering to the film surface, such as chemical cleaning and ball cleaning. Therefore, in the above-mentioned biological reaction device, in addition to the biological treatment device (reaction tank) and the separation membrane, a membrane cleaning device is required, and a unit having three different functions is required.

[問題点を解決するための手段] 本発明は、液透過可能な支持材上に分離膜を配材し、こ
の分離膜の原液側表面に生物処理用微生物を担持させ、
これを反応容器内に設置する。そして、原液を反応容器
内に導入し、分離膜に担持された生物処理用微生物によ
り生物処理を施した後、該分離膜及び支持材を透過させ
て反応容器から取り出すようにしたものである。
[Means for Solving Problems] The present invention provides a separation membrane on a liquid-permeable support material, and allows the raw solution-side surface of the separation membrane to carry a microorganism for biological treatment.
This is installed in the reaction vessel. Then, the stock solution is introduced into the reaction vessel, subjected to biological treatment by the microorganism for biological treatment carried on the separation membrane, and then the separation membrane and the supporting material are permeated and taken out from the reaction vessel.

[作用] 本発明においては、分離膜面上に生物処理用微生物が担
持されているので、従来のごとき生物処理装置と膜分離
装置とを単に組み合わせた生物反応装置とは異なり、生
物処理手段と膜分離手段とを一つのユニット内に組み入
れることができ、高効率でコンパクトな処理装置とし得
る。また、分離膜への付着物質が固定化微生物により分
解されるので、膜の洗浄が不必要かあるいはその頻度が
極めて少なくて足りる。
[Operation] In the present invention, since the microorganism for biological treatment is carried on the surface of the separation membrane, unlike the conventional bioreactor in which the biological treatment apparatus and the membrane separation apparatus are simply combined, a biological treatment means The membrane separation means and the membrane separation means can be incorporated into one unit, and a highly efficient and compact processing apparatus can be obtained. Further, since the substances adhering to the separation membrane are decomposed by the immobilized microorganisms, it is not necessary to wash the membrane or the frequency thereof is extremely low.

[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生物反応装置の縦断面
図、第2図及び第3図はそれぞれ第1図II−II線、III
−III線に沿う断面図、第4図は異なる実施例に係る生
物反応装置の縦断面図である。
FIG. 1 is a longitudinal sectional view of a bioreactor according to an embodiment of the present invention, and FIGS. 2 and 3 are FIG. 1 II-II line and III, respectively.
Fig. 4 is a sectional view taken along line -III, and Fig. 4 is a longitudinal sectional view of a bioreactor according to another embodiment.

第4図は本発明の最も基本的な構成を示すものであるの
で、まず第4図を参照して本発明の構成について説明す
る。
Since FIG. 4 shows the most basic configuration of the present invention, the configuration of the present invention will be described first with reference to FIG.

第4図において1は反応装置の容器であって、上部に原
液の導入口2が、そして下部に生産液の取出口3が設け
られている。そして、容器1を水平方向に横断するよう
に液透過可能な材質からなる支持材4が設置され、これ
により容器1内が原液室1aと生産液室1bとに2分さ
れている。支持材4の液導入側には分離膜5が設けられ
ており、この分離膜5の表面には生物処理用微生物が担
持された層(生物固定化層)6が設けられている。
In FIG. 4, reference numeral 1 denotes a container of the reactor, which is provided with an inlet port 2 for the undiluted solution in the upper part and an outlet port 3 for the product solution in the lower part. A support material 4 made of a liquid-permeable material is installed so as to traverse the container 1 in the horizontal direction, whereby the inside of the container 1 is divided into a stock solution chamber 1a and a production solution chamber 1b. A separation membrane 5 is provided on the liquid introduction side of the support material 4, and a layer (biological immobilization layer) 6 carrying a biological treatment microorganism is provided on the surface of the separation membrane 5.

このように構成された生物反応装置において、導入口2
から反応容器1内に導入された原液は生物固定化層6と
接触して生物処理を受け、生物学的に分解される。そし
て、分解生成物は分離膜5を透過し支持材4を通過して
生産液取出室1bに入り、次いで取出口3から取り出さ
れる。
In the bioreactor configured in this way, the inlet 2
The stock solution introduced into the reaction vessel 1 from the above is brought into contact with the biological immobilization layer 6 to undergo biological treatment and is biologically decomposed. Then, the decomposition products pass through the separation membrane 5, pass through the support material 4, enter the product liquid take-out chamber 1 b, and are taken out from the take-out port 3.

このように、分離膜5面上に担持されている生物処理用
微生物により分解又は改質された物質は直ちに分離膜に
より分離される。また、膜面に付着し透過水量を減少さ
せる膜面閉塞汚染物質は固定化微生物により生物学的に
分解される。そのため、処理効率が高いと共に、膜の目
詰りが抑制され、膜洗浄処理の頻度が極めて少なくな
る。
Thus, the substance decomposed or modified by the biological treatment microorganisms carried on the surface of the separation membrane 5 is immediately separated by the separation membrane. Further, the membrane surface blocking contaminants that adhere to the membrane surface and reduce the amount of permeated water are biologically decomposed by the immobilized microorganisms. Therefore, the treatment efficiency is high, the clogging of the membrane is suppressed, and the frequency of the membrane cleaning treatment is extremely reduced.

なお、11〜13の部材については実験例の項において
説明する。
The members 11 to 13 will be described in the section of Experimental Example.

次に第1図を参照して本発明の好ましい実施例について
説明する。
Next, a preferred embodiment of the present invention will be described with reference to FIG.

第1図において、反応容器1は原液導入口2を上部に、
また生産液取出口3を下部に有し、その内部には仕切板
7が設けられている。その仕切板7は複数個の円形の孔
を有しており、この孔から原液室1a側に立ち上がるよ
うに筒状の支持材4が設けられている。そして、この筒
状支持材4の周面に分離膜5が設けられ、この分離膜5
の表面に生物固定化層6が設けられている。なお支持材
4、分離膜5及び生物固定化層6の上端面は蓋状部材8
によって封じられている。
In FIG. 1, the reaction container 1 has a stock solution inlet 2 at the top,
Further, it has a production liquid outlet 3 at the bottom, and a partition plate 7 is provided inside the outlet. The partition plate 7 has a plurality of circular holes, and a cylindrical support member 4 is provided so as to rise from the holes toward the stock solution chamber 1a. Then, a separation membrane 5 is provided on the peripheral surface of the cylindrical support member 4, and the separation membrane 5 is provided.
The biological immobilization layer 6 is provided on the surface of the. The support member 4, the separation membrane 5, and the biological immobilization layer 6 have lid-shaped members 8 on their upper end surfaces.
Is sealed by.

この第1図の実施例においても、導入口2から原液室1
aに導入された原液は、生物固定化層6に固定化されて
いる生物処理用微生物によって生物学的な処理(例え
ば、分解、改質反応等)を受ける。生じた物質は分離膜
5及び支持材4を透過して生産液室1bに入り、取出口
3から取り出される、図中10はガス抜出口である。
Also in the embodiment shown in FIG.
The stock solution introduced into a is subjected to biological treatment (for example, decomposition, reforming reaction, etc.) by the biological treatment microorganisms immobilized on the biological immobilization layer 6. The produced substance permeates the separation membrane 5 and the support material 4, enters the production liquid chamber 1b, and is taken out from the take-out port 3. In the figure, 10 is a gas vent port.

この第1図の実施例は、第4図の実施例に比べ反応容器
1内に設けられている支持材4の表面積が大きいので、
微生物固定化層6の面積も大きく、従って同一容量で処
理し得る原液の量が極めて多い。
In the embodiment shown in FIG. 1, the surface area of the support material 4 provided in the reaction vessel 1 is larger than that in the embodiment shown in FIG.
The area of the microorganism immobilization layer 6 is also large, and therefore the amount of stock solution that can be treated with the same volume is extremely large.

なお本発明においては、第1図及び第4図に示すよう
に、生産液の一部を原液室1a側に戻すように配管1c
を設けてもよい。もちろん、一過式に流下させてもよ
い。
In the present invention, as shown in FIGS. 1 and 4, a pipe 1c is provided so as to return a part of the production liquid to the stock solution chamber 1a side.
May be provided. Of course, it may be allowed to flow down temporarily.

本発明において支持材4としては、焼結合金、多孔質セ
ラミックス、素焼き陶器などを用いることができる。
In the present invention, as the support material 4, a sintered alloy, porous ceramics, unglazed pottery, or the like can be used.

分離膜としては、特に限定されることなく各種のものを
用いることができるが、反応の種類に応じて選定するの
が好ましい。例えば通常の廃水処理を行う場合には孔径
1〜0.1μmの精密瀘過膜を用いることができ、高度
な廃水処理を行う場合は分画分子量が20000〜10
00の限外瀘過膜を用いることができる。
The separation membrane is not particularly limited and various kinds can be used, but it is preferable to select it according to the type of reaction. For example, a precision filtration membrane having a pore size of 1 to 0.1 μm can be used when performing ordinary wastewater treatment, and a cut-off molecular weight of 20,000 to 10 when performing advanced wastewater treatment.
An ultrafiltration membrane of 00 can be used.

分離膜面上に担持される生物処理用微生物としては、目
的とする反応に応じて選定されるのであるが、例えば嫌
気性の廃水処理を行う場合は、酸生成菌、メタン生成菌
を用いる。また好気性の廃水処理を行う場合にはズーグ
レア等を用いる。
The biological treatment microorganisms carried on the surface of the separation membrane are selected according to the intended reaction. For example, when anaerobic wastewater treatment is performed, acid-producing bacteria and methanogenic bacteria are used. When aerobic wastewater treatment is performed, zoo glare or the like is used.

なお、酸生成菌、メタン生成菌等の嫌気性菌を固定化さ
せた。嫌気性生物処理を行う場合には、原液室1aを嫌
気状態とする。また、好気性微生物を固定化して好気性
生物処理を行う場合には、原液室1aに散気装置を設け
たり、或いは予め原液に酸素を十分に溶存させて原液室
1aに導入する。
In addition, anaerobic bacteria such as acid-producing bacteria and methanogenic bacteria were immobilized. When anaerobic organism treatment is performed, the stock solution chamber 1a is placed in an anaerobic state. When immobilizing aerobic microorganisms and performing aerobic biological treatment, an oxygen diffuser is provided in the stock solution chamber 1a, or oxygen is sufficiently dissolved in the stock solution in advance and introduced into the stock solution chamber 1a.

分離膜面上に生物処理用微生物を担持させる手段として
は次のような方法を用いることができる。
The following method can be used as a means for supporting the microorganism for biological treatment on the surface of the separation membrane.

分離膜の表面に、アクリルアミド、カラギーナンな
どの通水可能な性質を有する糊材を用いて微生物を付着
させる。
Microorganisms are attached to the surface of the separation membrane by using a paste material having a water-permeable property such as acrylamide or carrageenan.

活性炭やスポンジ等のポーラスな性状の充填剤を上
記アクリルアミドやカラギーナンなどの糊材を用いて分
離膜表面に付着させ、この充填剤の表面や細孔内に微生
物を付着、増殖させる。
A porous filler such as activated carbon or sponge is attached to the surface of the separation membrane using the above-mentioned acrylamide or a carrageenan paste, and microorganisms are attached and proliferated on the surface or in the pores of the filler.

しかして、本発明においては、上述のように膜面に付着
し、透過水量を減少させる膜面閉塞汚染物質は、分離膜
面上に担持されている生物処理用微生物により生物学的
に分解されるので、分離膜の目詰りが殆ど進行しない。
しかしながら、長期間装置の運転を継続すると、原液中
の無機物質、難分解性物質、生物代謝物質等が分離膜の
表面や空隙に溜まり閉塞を生じることもあり得る。その
場合には、清浄な液や生産液を生産液室1b側から支持
材4を通して供給し分離膜を逆洗し閉塞物質を剥離させ
しめる。
Therefore, in the present invention, the membrane surface clogging contaminant that adheres to the membrane surface and reduces the permeated water as described above is biologically decomposed by the biological treatment microorganisms carried on the separation membrane surface. Therefore, the separation membrane is hardly clogged.
However, if the operation of the apparatus is continued for a long period of time, inorganic substances, hardly decomposable substances, bio-metabolites, etc. in the stock solution may accumulate on the surface or voids of the separation membrane and cause blockage. In that case, a clean liquid or a production liquid is supplied from the production liquid chamber 1b side through the support material 4, and the separation membrane is backwashed to remove the blocking substances.

次に好適な実験例について説明する。Next, a suitable experimental example will be described.

実験例1(本発明例) 第4図に示す装置において、反応容器1として直径10
cm、高さ20cmの撹拌装置11付のカラムを用い、
支持材4として素焼陶器を用いた。この上に分画分離量
8000の限外瀘過膜5を設け、更にその上に生物固定
材としてスポンジを厚さ10mmのものを1%寒天液を
用いて付着させた。
Experimental Example 1 (Example of the present invention) In the apparatus shown in FIG.
cm, using a column with a stirrer 11 of 20 cm in height,
As the support material 4, unglazed pottery was used. An ultrafiltration membrane 5 having a fractional separation amount of 8000 was provided thereon, and a sponge having a thickness of 10 mm as a biological immobilizing material was further adhered thereon using 1% agar solution.

このスポンジ上に次のようにして嫌気性菌体を付着させ
た。即ちグルコースと酢酸を混合した合成基質を用いて
増殖させておいた嫌気性菌体をVSS量として1gを濃
縮して反応容器1内に投入し、寒天を用いスポンジに菌
体を付着させた。
Anaerobic bacteria were adhered to this sponge as follows. That is, 1 g of anaerobic bacterial cells, which had been grown using a synthetic substrate in which glucose and acetic acid were mixed, was concentrated into the reaction vessel 1 as a VSS amount, and the bacterial cells were attached to the sponge using agar.

この寒天濃度は0.1%以下とした。This agar concentration was 0.1% or less.

実験用の基質としてはグルコースと酢酸との混合したC
ODcr10000mg/の合成基質を用いた。
As a substrate for the experiment, C mixed with glucose and acetic acid was used.
ODcr10000 mg / synthetic substrate was used.

この基質を、ポンプにより反応容器1内に連続的に10
0ml/日で注入すると共に、反応容器1内の液面レベ
ルを一定とするためレベル計を設置して該レベルを検出
し、液面レベルが下ったときには生産液の一部を原液室
1aに返送した。また原液質1a及び生産液室1bに背
圧弁12を有する配管13を接続し、運転圧力をこの背
圧弁12を調整することにより2kg/cm2とした。
なお、反応容器1内の液量は1とし、原液室1aの液
のpHは、リン酸バッファを用い、6.8〜7.2とし
た。
This substrate is continuously pumped into the reaction vessel 1 by 10 times.
While injecting at 0 ml / day, a level meter is installed to keep the liquid level in the reaction container 1 constant, and the level is detected. When the liquid level falls, a part of the production liquid is placed in the stock solution chamber 1a. I sent it back. Further, a pipe 13 having a back pressure valve 12 was connected to the raw liquid quality 1a and the production liquid chamber 1b, and the operating pressure was adjusted to 2 kg / cm 2 by adjusting the back pressure valve 12.
The amount of liquid in the reaction vessel 1 was 1, and the pH of the liquid in the stock solution chamber 1a was 6.8 to 7.2 using a phosphate buffer.

運転開始後10日、20日及び30日経過後の生産液の
水質、限外瀘過膜の液透過量を第1表に示す。
Table 1 shows the water quality of the produced liquid and the amount of liquid permeated through the ultrafiltration membrane 10 days, 20 days, and 30 days after the start of operation.

実験例2(比較例) 支持材4の上に分画分子量8000の限外瀘過膜5を設
けただけで、その上の生物固定化層6は設けなかった。
そして、この生物固定化層の代りに原液室1内に菌体を
浮遊せしめ、上記実験例1と同様にして実験を行った。
運転10日、20日、30日後の生産液の水質、限外瀘
過膜の透過量の測定結果を第1表に示す。
Experimental Example 2 (Comparative Example) Only the ultrafiltration membrane 5 having a molecular weight cut off of 8000 was provided on the support material 4, and the biological immobilization layer 6 thereon was not provided.
Then, instead of the organism-immobilized layer, the cells were suspended in the stock solution chamber 1 and the experiment was conducted in the same manner as in Experimental Example 1 above.
Table 1 shows the measurement results of the water quality of the produced liquid and the permeation amount of the ultrafiltration membrane after 10 days, 20 days, and 30 days of operation.

なお、第1表中、生産液の水質は原液からのCODcrの
除去率として示す。
In Table 1, the water quality of the production liquid is shown as the removal rate of CODcr from the stock solution.

第1表より、生産液の水質は実験例1、2共に差はない
が、液透過量は本発明例の場合比較例に比べ2倍以上の
数値を示し、運転期間を長くしても液透過量の低下がな
いことが認められる。
From Table 1, there is no difference in the water quality of the produced liquid in both Experimental Examples 1 and 2, but the liquid permeation amount in the case of the present invention example is more than twice that in the comparative example, and even if the operation period is extended, the liquid It is recognized that there is no reduction in the amount of permeation.

[効果] 以上詳述した通り、本発明の生物反応装置においては、
分離膜面上に生物処理用微生物が担持されているので、
装置全体の構成が極めてコンパクトとなる。更に、この
生物処理用微生物の作用により分離膜の目詰りが防止さ
れ、膜透過液量の減少が極めて少ない。そして、分離膜
の洗浄が不要であるか極めて少なくて足りる。更に、従
来の分離膜のように薬品洗浄を行うことは不要であり、
洗浄を行う場合でも簡単な逆洗で足りる。
[Effect] As described in detail above, in the biological reaction device of the present invention,
Since the biological treatment microorganisms are carried on the separation membrane surface,
The configuration of the entire device becomes extremely compact. Furthermore, the action of the microorganism for biological treatment prevents clogging of the separation membrane, and the decrease in the amount of the membrane permeate is extremely small. Further, the cleaning of the separation membrane is unnecessary or extremely small. Furthermore, it is not necessary to perform chemical cleaning like the conventional separation membrane,
Even when cleaning, a simple backwash is sufficient.

また、本発明の装置においては、生産液は分離膜を透過
した液であるので、SS成分のない極めて高度な浄化液
である。更に、分離膜透過用動力も不要とし得る。
Further, in the apparatus of the present invention, the production liquid is a liquid that has permeated the separation membrane, and therefore is a highly advanced purification liquid without SS components. Furthermore, power for separating membrane permeation may be unnecessary.

【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生物反応装置の縦断面
図、第2図及び第3図はそれぞれ第1図II−II線、及び
III−III線に沿う断面図、第4図は異なる実施例に係る
生物反応装置の断面図である。 1……反応容器、2……導入口、 3……取出口、4……支持材、 5……分離膜、6……生物固定化層、 7……仕切板。
FIG. 1 is a longitudinal sectional view of a bioreactor according to an embodiment of the present invention, FIGS. 2 and 3 are FIG. 1 line II-II, and FIG.
FIG. 4 is a sectional view taken along line III-III, and FIG. 4 is a sectional view of a bioreactor according to a different embodiment. 1 ... Reaction container, 2 ... Inlet port, 3 ... Outlet port, 4 ... Support material, 5 ... Separation membrane, 6 ... Bioimmobilization layer, 7 ... Partition plate.

───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 昭58−187190(JP,A) 大矢晴彦編「逆浸透法・限外▲ろ▼過法 ▲II▼応用 膜利用技術ハンドブック」 幸書房初版(昭53−6−30)、P90−92, P233−236,及びP363〜364 ─────────────────────────────────────────────────── ─── Continuation of the front page (56) Reference JP-A-58-187190 (JP, A) Haruhiko Oya ed. “Reverse osmosis method, ultra ▲ ro ▼ past ▲ II ▼ application membrane application technology handbook” Koshobo first edition (Sho 53-6-30), P90-92, P233-236, and P363-364.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】有機性廃液を生物処理用微生物を用いて生
物学的に処理する生物反応装置であって、原液の導入口
及び生産液の取出口を備えた反応容器と、該導入口と取
出口とを隔てるように該反応容器内に配置された液透過
可能な支持材と、該支持材の原液側表面に配材された分
離膜と、該分離膜の原液側表面に設けられた生物処理用
微生物を担持する層とを有することを特徴とする生物反
応装置。
1. A bioreactor for biologically treating an organic waste liquid by using a microorganism for biological treatment, comprising a reaction container having an inlet for a raw liquid and an outlet for a product liquid, and the inlet. A liquid-permeable support material disposed in the reaction vessel so as to separate the outlet, a separation membrane provided on the surface of the support material on the side of the undiluted solution, and a surface of the separation membrane on the side of the undiluted solution. A bioreactor comprising: a layer supporting a microorganism for biological treatment.
JP9295085A 1985-04-30 1985-04-30 Bioreactor Expired - Lifetime JPH0634985B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9295085A JPH0634985B2 (en) 1985-04-30 1985-04-30 Bioreactor

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9295085A JPH0634985B2 (en) 1985-04-30 1985-04-30 Bioreactor

Publications (2)

Publication Number Publication Date
JPS61249592A JPS61249592A (en) 1986-11-06
JPH0634985B2 true JPH0634985B2 (en) 1994-05-11

Family

ID=14068740

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9295085A Expired - Lifetime JPH0634985B2 (en) 1985-04-30 1985-04-30 Bioreactor

Country Status (1)

Country Link
JP (1) JPH0634985B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2737202B1 (en) * 1995-07-25 1997-10-17 Omnium Traitement Valorisa PLANT FOR BIOLOGICAL TREATMENT OF WATER FOR POTABILIZATION
US5932099A (en) * 1995-07-25 1999-08-03 Omnium De Traitements Et De Valorisation (Otv) Installation for biological water treatment for the production of drinkable water
WO2015083717A1 (en) * 2013-12-02 2015-06-11 東レ株式会社 Water treatment method

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
大矢晴彦編「逆浸透法・限外▲ろ▼過法▲II▼応用膜利用技術ハンドブック」幸書房初版(昭53−6−30)、P90−92,P233−236,及びP363〜364

Also Published As

Publication number Publication date
JPS61249592A (en) 1986-11-06

Similar Documents

Publication Publication Date Title
US6808628B2 (en) Membrane bioreactor using non-woven fabric filtration
JPH0470958B2 (en)
JPH07256281A (en) Waste water purifying method and tank
KR102100991B1 (en) Liquefied fertilizer purification apparatus using porous ceramic membrane
WO2008066497A1 (en) Water reclamation without biosludge production
EP1899273B1 (en) Water treatment process
JPH10263594A (en) Removing method and device of nitrate ion in waste water
Nishijima et al. Particle separation as a pretreatment of an advanced drinking water treatment process by ozonation and biological activated carbon
JP2014000495A (en) Sewage treatment apparatus, and sewage treatment method using the same
JP2016117064A (en) Sewage treatment device and sewage treatment method using it
JPH0634985B2 (en) Bioreactor
JPS61120694A (en) Treatment of organic waste water
JP4859170B2 (en) Nitrogen-containing organic wastewater treatment system
JPH0957289A (en) Biological treating device of fluidized bed type
JPH11104698A (en) Wastewater treatment method
JPH0683835B2 (en) Membrane bioreactor treatment method
JPS61249598A (en) Two-phase anaerobic treatment equipment
KR20030097075A (en) Hybrid Submerged Plate Type Membrane Bioreactor Using microfilter Combined With Biofilm-Activated Carbon for Advanced Treatment of Sewage and Wastewater
JPH0647399A (en) Water purifying treatment method
Lobos et al. Membrane bioreactor performances: effluent quality ofcontinuous and sequencing systems for water reuse
JPH09108672A (en) Parallel two-stage membrane separation type septic tank
JPS62168598A (en) Methane fermenting device
JP3819457B2 (en) Biological denitrification of wastewater
JP4104806B2 (en) Solid-liquid separation method and apparatus for organic wastewater treatment
Arnot et al. Membrane bioreactors as an alternative to conventional waste water treatment processes

Legal Events

Date Code Title Description
EXPY Cancellation because of completion of term