JPH0579399B2 - - Google Patents
Info
- Publication number
- JPH0579399B2 JPH0579399B2 JP59192372A JP19237284A JPH0579399B2 JP H0579399 B2 JPH0579399 B2 JP H0579399B2 JP 59192372 A JP59192372 A JP 59192372A JP 19237284 A JP19237284 A JP 19237284A JP H0579399 B2 JPH0579399 B2 JP H0579399B2
- Authority
- JP
- Japan
- Prior art keywords
- reaction vessel
- partition wall
- inner cylinder
- gas
- wastewater
- 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
Links
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Apparatus Associated With Microorganisms And Enzymes (AREA)
- Biological Treatment Of Waste Water (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〕
この発明は、微生物を利用して有価物を製造
し、汚濁物を浄化するバイオリアクタに係り、特
に微生物担体を流動状態で反応に供する流動床型
バイオリアクタに関する。[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to a bioreactor that uses microorganisms to produce valuables and purify pollutants, and particularly relates to a bioreactor that uses microorganisms to produce valuables and purify pollutants, and particularly relates to a bioreactor that uses microorganisms to produce valuables and purify pollutants, and particularly relates to a bioreactor that uses microorganisms to produce valuable substances and purify pollutants, and particularly relates to a bioreactor that uses microorganisms to produce valuable substances and purify pollutants. Regarding floor bioreactors.
従来の流動床型バイオリアクタとしては、例え
ば第3図に示すようなものが知られている。この
バイオリアクタ1は、円筒状の反応容器2の逆円
錐状の底部3から液体または気体を噴出し、容器
2の底部3近傍から中部にかけてただよつている
微生物担体4…を流動状態とし、微生物担体4…
に固着、付着もしくは包含されている微生物で、
反応容器2内の廃水5を生物処理し、処理された
廃水5を反応容器2の上部の越流堰6から越流管
6′を通し流出するように構成されている。
As a conventional fluidized bed type bioreactor, for example, the one shown in FIG. 3 is known. This bioreactor 1 ejects liquid or gas from the inverted conical bottom 3 of a cylindrical reaction container 2 to bring microbial carriers 4 floating from the vicinity of the bottom 3 to the middle of the container 2 into a fluid state. Carrier 4...
Microorganisms that adhere to, adhere to, or are contained in
The wastewater 5 in the reaction vessel 2 is subjected to biological treatment, and the treated wastewater 5 is configured to flow out from an overflow weir 6 at the upper part of the reaction vessel 2 through an overflow pipe 6'.
しかしながら、このようなバイオリアクタ1に
あつては、処理水は反応容器2の上端部の越流堰
6より上澄みを流出するようにしているので、微
生物担体4…を処理水から分離せねばならない。
この担体4…の分離は、通常コストの点から重力
沈降分離で行われている。このため、担体4…は
必然的に水よりも十分重い砂、ケイソウ土などを
用いざるを得ない。ところが、重い担体4…を使
用すると、比重が大きいのでこれを流動化させる
ためのエネルギーが多く必要となり、よつて担体
量が制限されることになる。このため、担体4…
の充填量は反応容器2の実質反応容積のわずか3
〜20%程度であり、流動展開状態で反応容積の50
〜60%が上限となる。したがつて、担体4…に保
持される微生物量も制限され、例えば糖廃液を対
象廃水とするメタン醗酵では40000ppmが限度で
あつた。
However, in such a bioreactor 1, the supernatant of the treated water flows out from the overflow weir 6 at the upper end of the reaction vessel 2, so it is necessary to separate the microbial carriers 4 from the treated water. .
This separation of the carriers 4 is usually carried out by gravity sedimentation separation from the viewpoint of cost. For this reason, the carrier 4 must necessarily be made of sand, diatomaceous earth, or the like, which is much heavier than water. However, if a heavy carrier 4 is used, since the specific gravity is large, a large amount of energy is required to fluidize the carrier, thereby limiting the amount of carrier. For this reason, carrier 4...
The filling amount is only 3 of the actual reaction volume of reaction vessel 2.
~20% of the reaction volume in the fluidized state
The upper limit is ~60%. Therefore, the amount of microorganisms retained on the carrier 4 is also limited, and for example, in methane fermentation using sugar wastewater as the target wastewater, the limit is 40,000 ppm.
また、別途に担体分離のための沈殿槽を設ける
場合もあるが、その場合は新たに沈殿槽が必要の
上、沈殿槽で分離するためには微生物付着状態で
水より重い担体が必要であり、装置全体に流動展
開するためには大きなエネルギーが必要となる。 In some cases, a separate sedimentation tank is installed to separate carriers, but in that case, a new sedimentation tank is required, and in order to separate in the sedimentation tank, carriers with microorganisms attached and heavier than water are required. , a large amount of energy is required to spread the fluid throughout the device.
一方、バイオリアクタにあつては、反応速度は
微生物量に比例し、微生物量が多ければ反応速度
が高くなり、滞留時間が減少し、装置のコンパク
ト化が図れることが知られている。 On the other hand, in the case of a bioreactor, it is known that the reaction rate is proportional to the amount of microorganisms, and the larger the amount of microorganisms, the higher the reaction rate, the shorter the residence time, and the more compact the device can be.
よつて、従来の流動床型のバイオリアクタ1で
は、反応容器2の単位容積当りの処理効率が悪
く、高効率の処理が行えず、装置の小型化を図る
ことも困難であるなどの問題点があつた。 Therefore, the conventional fluidized bed type bioreactor 1 has problems such as poor processing efficiency per unit volume of the reaction vessel 2, inability to perform highly efficient processing, and difficulty in downsizing the device. It was hot.
そこで、この発明では、反応容器本体内部に、
該反応容器本体より小径に形成され上端が貯留液
面より上方に突出し下端が反応容器本体底部に近
接した中筒体を設け、被処理廃水を受け入れるた
めの廃水受入口を該中筒体内部に設ける一方、処
理廃水を取り出すための廃水排出口を該中筒体外
部に設け、かつ前記反応容器本体底部に気体を散
気する噴出し手段を配するとともに、前記中筒体
内の中央部の下半部にこの中筒体とは一定間隔を
隔て、前記噴出し手段から散気された気体を上方
に導く内筒部が前記反応容器本体底部との間に一
定間隔を隔てて設けられ、該内筒部の略鉛直上方
に、前記中筒体の内側の、中筒体内部を上下方向
に略2分する位置に、前記中筒体と一定の間隙を
開けて、前記内筒部により上方に導かれてきた気
体の上昇を遮るとともに該気体を内筒部の外方に
導く笠状の隔壁を、その頂部を上方に向けて配置
させて設け、前記内筒部上端周縁と前記隔壁下端
周縁との間を前記液体より比重の大きな重量微生
物担体を下方に沈降させて流動させる導出領域と
し、前記隔壁下端周縁と前記中筒体との間を前記
内筒部の外方へ導かれた気体を上方へ導いて、前
記液体より比重の小さな軽量微生物担体を前記隔
壁の上側で流動させる噴き上げ領域とすることに
より、上記問題点を解決するようにした。
Therefore, in this invention, inside the reaction vessel main body,
An intermediate cylindrical body is formed to have a smaller diameter than the reaction vessel main body, an upper end protrudes above the level of the stored liquid, and a lower end is close to the bottom of the reaction vessel main body, and a wastewater receiving port for receiving the wastewater to be treated is provided inside the intermediate cylindrical body. At the same time, a waste water outlet for taking out treated wastewater is provided outside the middle cylinder, and a jetting means for dispersing gas is disposed at the bottom of the reaction vessel main body, and a waste water outlet is provided at the bottom of the main body of the reaction vessel. An inner cylindrical part is provided in the half part at a constant interval from the middle cylinder body and guides the gas diffused from the jetting means upward, and is spaced at a constant interval from the bottom of the reaction vessel main body. Approximately vertically above the inner cylindrical portion, a certain gap is opened between the inner cylindrical body and the inner cylindrical body at a position that approximately bisects the interior of the middle cylindrical body in the vertical direction. A cap-shaped partition wall is provided with its top facing upward to block the rise of the gas guided by the inner cylinder part and to guide the gas to the outside of the inner cylinder part. The space between the periphery and the periphery is a derivation area in which the heavy microbial carriers having a specific gravity higher than the liquid are allowed to settle downward and flow, and the space between the lower end periphery of the partition wall and the middle cylinder is guided to the outside of the inner cylindrical part. The above-mentioned problem is solved by guiding the gas upward to create a blow-up region in which lightweight microbial carriers having a specific gravity smaller than the liquid flow above the partition wall.
第1図はこの発明の流動床型バイオリアクタの
一例を示すもので、図中符号11は反応容器本体
である。この反応容器本体11は、円筒状の外筒
部11aとこれに連接された逆円錐状の底部11
bとから構成されている。この反応容器本体11
内には上記外筒部11aに対して同軸状に円筒状
の中間筒部(中筒体)12が設けられ、この中間
筒部(中筒体)12は外筒部11aとの間に所定
の間隔が保たれている。また、この中間筒部12
の内側の略中央部には、笠状の隔壁13が設けら
れている。この隔壁13は、中間筒部12内部の
空間を上下方向にそのほぼ中央で二分するように
配され、かつその笠の上部に相当する部分が上方
に来るように配置されている。そして、この隔壁
13は、この隔壁13と中間筒部12との間で流
体が流通可能な所定の間隔を保つて配設されてい
る。また、隔壁13の上方には、橿鉢状の循環板
14が設けられている。この循環板14はその底
部に当る部分が取り除かれて欠落しており、液体
の流通が可能となつている。また、循環板14は
中間筒部12とやはり所定の間隔をあけて配置さ
れている。さらに、隔壁13の鉛直下方、すなわ
ち中間筒部12の下半部には、やや小径の円筒体
からなる内筒部15が、中間筒部12とは一定間
隔を隔てて設けられている。この内筒部15の下
端部は、中間筒部12の下端部よりもさらに下方
の、反応容器本体11の底部11bと一定の間隔
を隔てた位置にまで延びており、かつ末広状に拡
径されている。この内筒部15の下方には散気部
材16が設けられている。この散気部材16に
は、反応容器本体11の底部11bの中央部を貫
通してブロア17から弁18を経て延びる散気管
(噴出し手段)19が接続されている。
FIG. 1 shows an example of a fluidized bed bioreactor of the present invention, and reference numeral 11 in the figure is a reaction vessel main body. This reaction vessel main body 11 includes a cylindrical outer cylinder part 11a and an inverted conical bottom part 11 connected to the outer cylinder part 11a.
It is composed of b. This reaction container body 11
Inside, a cylindrical intermediate cylinder part (middle cylinder body) 12 is provided coaxially with the outer cylinder part 11a, and this intermediate cylinder part (middle cylinder body) 12 has a predetermined space between it and the outer cylinder part 11a. spacing is maintained. Moreover, this intermediate cylinder portion 12
A cap-shaped partition wall 13 is provided approximately at the center of the inner side of the housing. This partition wall 13 is arranged so as to vertically divide the space inside the intermediate cylinder part 12 into two at approximately the center thereof, and is arranged so that the part corresponding to the upper part of the shade is located upward. The partition wall 13 is disposed at a predetermined distance between the partition wall 13 and the intermediate cylindrical portion 12 so that fluid can flow therebetween. Further, above the partition wall 13, a circular plate 14 in the shape of a cone is provided. The bottom portion of the circulation plate 14 has been removed and is missing, allowing liquid to flow therethrough. Further, the circulation plate 14 is also arranged at a predetermined distance from the intermediate cylinder portion 12. Further, vertically below the partition wall 13, that is, in the lower half of the intermediate cylindrical portion 12, an inner cylindrical portion 15 made of a cylindrical body with a slightly smaller diameter is provided at a constant distance from the intermediate cylindrical portion 12. The lower end of this inner cylindrical part 15 extends to a position further below the lower end of the intermediate cylindrical part 12 and at a constant distance from the bottom 11b of the reaction vessel main body 11, and has a wide diameter. has been done. A diffuser member 16 is provided below this inner cylindrical portion 15 . A diffuser pipe (spouting means) 19 is connected to the diffuser member 16, which extends from the blower 17 through the valve 18, passing through the center of the bottom 11b of the reaction vessel main body 11.
また、反応容器本体11の上端部には、本体1
1を気密的に覆う蓋部20が設けられている。こ
の蓋部20には、発生ガス排出管21と循環ガス
管22とが接続さているとともに、上記中間筒部
12の上端部が気密的に連接されている。また、
蓋部20の一部は越流堰(廃水排出口)23を構
成しており、越流堰23には弁24を介して排水
管25が接続されている。さらに、蓋部20に
は、この蓋部20を貫通して中間筒部12内に被
処理水を導入する流入管(廃水受入口)26が取
り付けられている。また、上記発生ガス排出管2
1は弁27を介してガス貯槽28に接続され、循
環ガス管22は弁29を経てブロア17に接続さ
れるとともに弁30を経て散気管19に接続され
ている。 Further, the upper end of the reaction vessel main body 11 has a main body 1
1 is provided with a lid portion 20 that airtightly covers the device. A generated gas discharge pipe 21 and a circulating gas pipe 22 are connected to the lid part 20, and the upper end of the intermediate cylinder part 12 is connected in an airtight manner. Also,
A part of the lid part 20 constitutes an overflow weir (wastewater discharge port) 23 , and a drain pipe 25 is connected to the overflow weir 23 via a valve 24 . Furthermore, an inflow pipe (wastewater receiving port) 26 is attached to the lid 20 to introduce the water to be treated into the intermediate cylinder 12 through the lid 20 . In addition, the generated gas exhaust pipe 2
1 is connected to a gas storage tank 28 via a valve 27, and the circulating gas pipe 22 is connected to the blower 17 via a valve 29 and to the aeration pipe 19 via a valve 30.
次に、このようなバイオリアクタの運転方法に
ついて、糖廃液を例にとつて説明する。 Next, a method of operating such a bioreactor will be explained using sugar waste liquid as an example.
反応容器本体11内に、まず糖廃液が流入管2
6から供給される。このとき、流入管26は中間
筒部12内部に開口しているので、糖廃液はこの
中間筒部12内に供給される。反応容器本体11
内には重量微生物担体と軽量微生物担体とが充填
されている。重量微生物担体は、中間筒部12内
の隔壁13の下方に置かれ、軽量微生物担体は同
じく上方に置かれる。重量微生物担体と軽量微生
物担体とは容量比で3:2の比率とされ、反応容
器本体11の実質反応容積の40%相当量が充填さ
れる。軽量微生物担体としては、水より比重の小
さいプラスチツク粒子、内部に気泡あるいは細孔
を有する軽石などの天然鉱物粒子、発泡プラスチ
ツク粒子、その他天然または人口の使用状態で水
より軽い粒子に、目的とする生物処理に応じた種
類の微生物を固着、付着もしくは包含したものが
使用され、その粒径0.1〜10mm程度とされ、使用
状態での比重が0.90〜0.97程度のものが好適であ
る。また、重量微生物担体としては、比重が水よ
り大きい、例えば砂、活性炭、ケイソウ土、リン
鉱石、コークス、ゼオライト、プラスチツクなど
の粒子、発泡プラスチツク粒子、内部に気泡、細
孔を有する天然鉱物粒子などが使用され、その粒
径が0.1〜1mm程度の粒子に同様に微生物を固着、
付着若しくは包含したものが使用され、使用状態
での比重が1.05〜1.20程度のものが好適に使用さ
れる。そして、比重の大きい重量微生物担体のも
のほど小径の粒子が、また比重の小さな軽量微生
物担体のものほど小径の粒子を使用することが望
ましい。 In the reaction vessel main body 11, the sugar waste liquid is first introduced into the inflow pipe 2.
Supplied from 6. At this time, since the inflow pipe 26 opens into the interior of the intermediate cylindrical portion 12, the sugar waste liquid is supplied into the intermediate cylindrical portion 12. Reaction container body 11
The interior is filled with heavy microbial carriers and lightweight microbial carriers. The heavy microbial carriers are placed below the partition wall 13 in the intermediate cylinder 12, and the lightweight microbial carriers are also placed above. The weight microbial carrier and the lightweight microbial carrier are set at a volume ratio of 3:2, and an amount equivalent to 40% of the actual reaction volume of the reaction vessel body 11 is filled. As lightweight microbial carriers, plastic particles with a specific gravity lower than that of water, natural mineral particles such as pumice with air bubbles or pores inside, foamed plastic particles, and other particles lighter than water in natural or artificial usage conditions can be used. A material containing fixed, attached, or encapsulated microorganisms depending on the type of biological treatment is used, and a particle size of about 0.1 to 10 mm and a specific gravity of about 0.90 to 0.97 in the used state are suitable. Examples of gravimetric microbial carriers include particles with a specific gravity greater than water, such as sand, activated carbon, diatomaceous earth, phosphate rock, coke, zeolite, plastic particles, foamed plastic particles, and natural mineral particles having air bubbles and pores inside. is used to similarly fix microorganisms to particles with a particle size of about 0.1 to 1 mm.
Those that are attached or included are used, and those that have a specific gravity of about 1.05 to 1.20 in the used state are preferably used. It is desirable to use particles with a smaller diameter for a heavy microorganism carrier with a higher specific gravity, and to use particles with a smaller diameter for a lightweight microorganism carrier with a lower specific gravity.
ついで、ブロア17を作動させて散気部材16
より気体を散気して、容器本体11内の各担体を
流動化させ、循環させる。かくして、各担体に保
持された微生物の働きにより糖廃液中の糖が酸醗
酵およびメタン醗酵されメタンガス(CH4)と二
酸化炭素(CO2)が生成すると同時に糖廃液が浄
化される。 Then, the blower 17 is operated to remove the air diffuser 16.
The gas is further diffused to fluidize and circulate each carrier within the container body 11. In this way, the sugar in the sugar waste liquid is subjected to acid fermentation and methane fermentation by the action of the microorganisms held on each carrier, producing methane gas (CH 4 ) and carbon dioxide (CO 2 ), and at the same time, the sugar waste liquid is purified.
ここで、散気により内筒部15下方にある重量
微生物担体は内筒部15内を上昇してゆき、隔壁
13によつて上昇が遮られて、隔壁13に沿つて
外方に流れ、上昇のエネルギーを失つて内筒部1
5の上端周縁と隔壁13下端周縁との間の導出領
域から下方に沈降し底部11bに戻り、ここで再
び散気され、同様に循環する。(第1図中実線矢
印参照)。一方、散気気体は隔壁13の底面から
外側に流れ、隔壁13下端周縁と中間筒部12と
の間の噴き上げ領域から隔壁13の上側に上昇し
て、中間筒部12の内側に沿つて循環板14の外
側を上昇し、水面より逃げる(第1図中破線矢印
参照)。この気体の流れに伴われて、軽量微生物
担体は、循環板14の外側を上昇し、ついで循環
板14の内側を流下し、循環板14の周囲を循環
する。 Here, the heavy microorganism carriers located below the inner cylinder part 15 rise within the inner cylinder part 15 due to the aeration, and the rising is blocked by the partition wall 13, flows outward along the partition wall 13, and rises. The inner cylinder part 1 loses its energy.
5 and the lower end periphery of the partition wall 13, the air sinks downward and returns to the bottom 11b, where it is diffused again and circulated in the same way. (See the solid line arrow in Figure 1). On the other hand, the diffused gas flows outward from the bottom surface of the partition wall 13 , rises to the upper side of the partition wall 13 from the blow-up area between the lower edge of the partition wall 13 and the intermediate cylinder part 12 , and circulates along the inside of the intermediate cylinder part 12 . It rises on the outside of the plate 14 and escapes from the water surface (see the broken line arrow in Figure 1). Accompanied by this gas flow, the lightweight microbial carrier rises on the outside of the circulation plate 14, then flows down on the inside of the circulation plate 14, and circulates around the circulation plate 14.
生物反応によつて発生したメタンガスおよび二
酸化炭素は、その一部が発生ガス排出管21から
引き抜かれ、ガス貯槽28に貯えられ、残部は循
環ガス管22を経てブロア順に送られ、散気用気
体として循環使用される。 A part of the methane gas and carbon dioxide generated by the biological reaction is extracted from the generated gas discharge pipe 21 and stored in the gas storage tank 28, and the remaining part is sent to the blower via the circulating gas pipe 22 to be used as a diffuser gas. used in circulation as
また、浄化された処理糖廃液は、中間筒部12
と外筒部11aとの間をゆつくりと上昇し、越流
堰23から流出し、排水管25を経て、次の高次
処理工程に送られる。 Further, the purified treated sugar waste liquid is transferred to the intermediate cylindrical portion 12.
and the outer cylinder part 11a, flows out from the overflow weir 23, passes through the drain pipe 25, and is sent to the next higher treatment step.
このような流動床型バイオリアクタによれば、
隔壁13で反応領域を上下方向に2分し、その上
方に軽量微生物担体を、その下方に重量微生物担
体をそれぞれ配して気体の散気により流動させる
ようにしたので、全体として微生物担体量が実質
反応容積の40〜50%程度まで多くなり、微生物量
も大きくすることができ、例えばこの例の糖廃液
のメタン醗酵のように60000〜80000ppmまで増加
させうる。したがつて、処理効率が大幅に高めら
れ、装置の小型化を図ることができる。また、微
生物担体の流動化のためのエネルギーは、従来の
重量微生物担体を流動化させるエネルギーと同じ
でよく、エネルギー効率もよくなる。さらに、軽
量微生物担体を用い、これを反応容器本体11の
上部領域で流動化しているにもかかわらず、中間
筒部12及び隔壁13の存在によつて軽量微生物
担体の流出が全くない。また、重量微生物担体も
中間筒部12内部に設けられ、かつ散気部材16
により上昇流が中間筒部12の中央部に生ずるた
め、この重量微生物担体も中間筒部12の外部に
漏れ出ることがなく、しかも処理廃水の取り出し
が中間筒部12の外部にてなされるので、ここで
の微生物担体の完全分離が可能である。また、隔
壁13により、軽量微生物担体と重量微生物担体
との双方についてもこれらが常時ほぼ完全に分離
した状態に保たれ、常に所期の機能が発揮され
る。 According to such a fluidized bed bioreactor,
The reaction area is vertically divided into two parts by the partition wall 13, and the lightweight microbial carriers are placed above and the heavy microbial carriers are placed below, respectively, and are made to flow by gas aeration, so that the overall amount of microbial carriers can be reduced. The amount of microorganisms can be increased to about 40 to 50% of the actual reaction volume, and the amount of microorganisms can be increased to 60,000 to 80,000 ppm, for example, as in the case of methane fermentation of sugar waste liquid in this example. Therefore, processing efficiency is greatly increased and the device can be made smaller. Furthermore, the energy for fluidizing the microbial carrier may be the same as the energy for fluidizing the conventional heavy microbial carrier, resulting in improved energy efficiency. Furthermore, even though lightweight microbial carriers are used and fluidized in the upper region of the reaction vessel main body 11, the presence of the intermediate cylinder portion 12 and the partition wall 13 prevents any outflow of the lightweight microbial carriers. Further, a heavy microorganism carrier is also provided inside the intermediate cylinder part 12, and the air diffuser 16
Since an upward flow is generated in the center of the intermediate cylinder part 12, the heavy microbial carriers will not leak out of the intermediate cylinder part 12, and furthermore, the treated wastewater can be taken out outside the intermediate cylinder part 12. , here complete separation of microbial carriers is possible. Moreover, the partition wall 13 keeps both the lightweight microbial carrier and the heavy microbial carrier almost completely separated at all times, so that the intended function is always exhibited.
第2図はこの発明のバイオリアクタの他の例を
示すもので、第1図に示した例と同一構成部分に
は同一符号を付してその説明を省略する。この例
の流動床型バイオリアクタは、微生物担体の流動
化に処理液を用いるようにしたものである。隔壁
13の上方には、処理液を吸引する吸液管31が
開口しており、この吸液管31は蓋部20を貫通
し、弁32を経て送液ポンプ33に接続されてい
る。送液ポンプ33で圧送された処理液の一部は
吹出管34、弁35、を経て、本体11の底部1
1bに開口している吹出口(噴出し手段)36か
ら吹き出され、残部は弁37、散水管38を経
て、水面上に設けられた散水部材39に送られ、
散水される。軽量微生物担体は主としてこの散水
部材39からの散水によつて流動化され、隔壁1
3の上方の領域で循環する。軽量微生物担体に
は、より軽量のものが好ましい。 FIG. 2 shows another example of the bioreactor of the present invention, and the same components as in the example shown in FIG. 1 are given the same reference numerals and their explanations will be omitted. The fluidized bed bioreactor of this example uses a treatment liquid to fluidize microbial carriers. A liquid suction pipe 31 for sucking the processing liquid is opened above the partition wall 13 , and this liquid suction pipe 31 penetrates through the lid 20 and is connected to a liquid pump 33 via a valve 32 . A part of the processing liquid pumped by the liquid pump 33 passes through the blow-off pipe 34 and the valve 35 and reaches the bottom 1 of the main body 11.
1b is blown out from the outlet (spouting means) 36, and the remainder is sent to a water sprinkling member 39 provided above the water surface via a valve 37 and a water sprinkling pipe 38.
Water is sprinkled. The lightweight microbial carrier is mainly fluidized by water sprinkling from this water sprinkling member 39, and is
It circulates in the area above 3. For lightweight microbial carriers, lighter ones are preferred.
以上説明したように、この発明の流動床型バイ
オリアクタは、反応容器本体内部に中筒体を設
け、この中筒体内部を隔壁で上下方向に二分し、
この隔壁の上方の領域に軽量微生物担体を、下方
の領域に重量微生物担体を配して流動させるよう
にしたものであるので、従来と同一の流動化エネ
ルギーで、微生物担体量を実質反応容器容積の40
〜50%にまで増加させることができ、微生物保持
量を従来の1.5〜2倍程度にまで多くでき、よつ
て反応の容積効率を30〜50%程度改善することが
できる。また、中筒体および噴出し手段の作用に
より軽量微生物担体および重量微生物担体の双方
が常に中筒体内で流動するものとなり、微生物担
体の流出がなく、微生物担体と処理水との完全分
離が可能である。しかも、隔壁により軽量微生物
担体と重量微生物担体との分離もほぼ完全になさ
れるため、全流動型であるにも拘わらず常に所期
の高い機能を発揮することができる。
As explained above, the fluidized bed bioreactor of the present invention includes a middle cylinder provided inside the reaction vessel main body, the inside of this middle cylinder divided vertically into two by a partition wall,
Light microbial carriers are arranged in the upper region of this partition wall, and heavy microbial carriers are arranged in the lower region for fluidization, so the amount of microbial carriers can be reduced to the actual reaction vessel volume with the same fluidization energy as before. of 40
50%, the amount of microorganisms retained can be increased to about 1.5 to 2 times the conventional amount, and the volumetric efficiency of the reaction can be improved by about 30 to 50%. In addition, due to the action of the inner cylinder and the ejection means, both the lightweight microbial carrier and the heavy microbial carrier are constantly flowing within the inner cylinder, so there is no leakage of the microbial carrier, and complete separation of the microbial carrier and the treated water is possible. It is. Furthermore, since the partition wall almost completely separates the lightweight microbial carriers from the heavy microbial carriers, it is possible to always exhibit the desired high functionality even though it is a completely fluid type.
第1図および第2図は、いずれもこの発明の流
動床型バイオリアクタの例を示す概略構成図、第
3図は従来の流動床型バイオリアクタを示す概略
構成図である。
11……反応容器本体、11a……外筒部、1
1b……底部、12……中間筒部(中筒体)、1
3……隔壁、16……散気部材(噴出し手段)、
17……ブロア、19……散気管、20……蓋
部、22……循環ガス管、31……吸液管、33
……送液ポンプ、34……吹出管、36……吹出
口(噴出し手段)、39……散水部材。
FIG. 1 and FIG. 2 are both schematic configuration diagrams showing an example of a fluidized bed type bioreactor of the present invention, and FIG. 3 is a schematic configuration diagram showing an example of a conventional fluidized bed type bioreactor. 11...Reaction container main body, 11a...Outer cylinder part, 1
1b...bottom, 12...middle cylinder part (middle cylinder), 1
3... Partition wall, 16... Air diffusion member (spouting means),
17...Blower, 19...Diffuser pipe, 20...Lid, 22...Circulating gas pipe, 31...Liquid suction pipe, 33
. . . Liquid feed pump, 34 . . . Blowout pipe, 36 .
Claims (1)
径に形成され上端が貯留液面より上方に突出し下
端が反応容器本体底部に近接した中筒体を設け、
被処理廃水を受け入れるための廃水受入口を該中
筒体内部に設ける一方、処理廃水を取り出すため
の廃水排出口を該中筒体外部に設け、かつ前記反
応容器本体底部に気体を散気する噴出し手段を配
するとともに、前記中筒体内の中央部の下半部に
この中筒体とは一定間隔を隔て、前記噴出し手段
から散気された気体を上方に導く内筒部が前記反
応容器本体底部との間に一定間隔を隔てて設けら
れ、該内筒部の略鉛直上方に、前記中筒体の内側
の中筒体内部を上下方向に略2分する位置に、前
記中筒体と一定の間隙を開けて、前記内筒部によ
り上方に導かれてきた気体の上昇を遮るとともに
該気体を内筒部の外方に導く笠状の隔壁を、その
頂部を上方に向けて配置させて設け、前記内筒部
上端周縁と前記隔壁下端周縁との間を前記液体よ
り比重の大きな重量微生物担体を下方に沈降させ
て流動させる導出領域とし、前記隔壁下端周縁と
前記中筒体との間を前記内筒部の外方へ導かれた
気体を上方へ導いて、前記液体より比重の小さな
軽量微生物担体を前記隔壁の上側で流動させる噴
き上げ領域としたとを特徴とする流動床型バイオ
リアクタ。1. A middle cylindrical body is provided inside the reaction vessel body, the diameter of which is smaller than that of the reaction vessel body, the upper end of which protrudes above the level of the stored liquid, and the lower end of which is close to the bottom of the reaction vessel body;
A wastewater inlet for receiving the wastewater to be treated is provided inside the middle cylinder, while a wastewater outlet for taking out the treated wastewater is provided outside the middle cylinder, and gas is diffused at the bottom of the reaction vessel main body. A blowout means is disposed in the lower half of the central part of the middle cylinder, and an inner cylinder part is spaced apart from the middle cylinder by a certain distance and guides the gas diffused from the blowout means upward. The inner cylinder is provided at a constant interval from the bottom of the reaction vessel main body, and is located approximately vertically above the inner cylinder at a position that vertically divides the inside of the inner cylinder into approximately two parts. A cap-shaped partition wall is opened with a certain gap from the cylinder body to block the rise of the gas guided upward by the inner cylinder part and to guide the gas to the outside of the inner cylinder part, with its top facing upward. The area between the upper end periphery of the inner cylinder part and the lower end periphery of the partition wall is used as a derivation area in which heavy microorganism carriers having a specific gravity greater than the liquid are allowed to settle and flow downward, and the lower end periphery of the partition wall and the middle cylinder A flow characterized in that the gas guided to the outside of the inner cylindrical part between the body and the body is guided upward to create a blow-up area in which lightweight microbial carriers having a specific gravity smaller than the liquid flow above the partition wall. Floor bioreactor.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP59192372A JPS6171891A (en) | 1984-09-13 | 1984-09-13 | Fluidized bed bioreactor |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP59192372A JPS6171891A (en) | 1984-09-13 | 1984-09-13 | Fluidized bed bioreactor |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6171891A JPS6171891A (en) | 1986-04-12 |
| JPH0579399B2 true JPH0579399B2 (en) | 1993-11-02 |
Family
ID=16290187
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP59192372A Granted JPS6171891A (en) | 1984-09-13 | 1984-09-13 | Fluidized bed bioreactor |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6171891A (en) |
Families Citing this family (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS63133978A (en) * | 1986-11-26 | 1988-06-06 | Rikagaku Kenkyusho | Cell cultivation device |
| JP4631204B2 (en) * | 2001-04-27 | 2011-02-16 | 栗田工業株式会社 | Dry methane fermentation of organic waste |
| JP5880217B2 (en) * | 2012-03-30 | 2016-03-08 | 栗田工業株式会社 | Treatment method for oil-containing wastewater |
| US12545885B2 (en) | 2020-03-30 | 2026-02-10 | Honda Motor Co., Ltd. | Culture device and culture method |
| JP7691563B1 (en) * | 2024-09-24 | 2025-06-11 | 株式会社クボタ | Methane fermentation tank and methane fermentation treatment method |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS553038A (en) * | 1978-06-20 | 1980-01-10 | Nec Corp | Microprogram control unit |
| JPS5861887A (en) * | 1981-10-09 | 1983-04-13 | Kubota Ltd | Treatment of waste water |
-
1984
- 1984-09-13 JP JP59192372A patent/JPS6171891A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6171891A (en) | 1986-04-12 |
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