JPH025154B2 - - Google Patents
Info
- Publication number
- JPH025154B2 JPH025154B2 JP60108281A JP10828185A JPH025154B2 JP H025154 B2 JPH025154 B2 JP H025154B2 JP 60108281 A JP60108281 A JP 60108281A JP 10828185 A JP10828185 A JP 10828185A JP H025154 B2 JPH025154 B2 JP H025154B2
- Authority
- JP
- Japan
- Prior art keywords
- tank
- liquid
- solid
- fluidized bed
- section
- 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
- 239000007788 liquid Substances 0.000 claims description 34
- 239000002245 particle Substances 0.000 claims description 23
- 244000005700 microbiome Species 0.000 claims description 20
- 238000005192 partition Methods 0.000 claims description 15
- 238000012545 processing Methods 0.000 claims description 8
- 239000007787 solid Substances 0.000 claims description 8
- 102000004190 Enzymes Human genes 0.000 claims description 7
- 108090000790 Enzymes Proteins 0.000 claims description 7
- 230000003100 immobilizing effect Effects 0.000 claims description 6
- 239000011550 stock solution Substances 0.000 claims description 6
- 238000005273 aeration Methods 0.000 claims description 5
- 239000008187 granular material Substances 0.000 claims description 5
- 239000000126 substance Substances 0.000 claims description 5
- 238000006243 chemical reaction Methods 0.000 description 15
- 239000007789 gas Substances 0.000 description 12
- 238000000034 method Methods 0.000 description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 5
- 238000000855 fermentation Methods 0.000 description 5
- 230000004151 fermentation Effects 0.000 description 5
- 239000001301 oxygen Substances 0.000 description 5
- 229910052760 oxygen Inorganic materials 0.000 description 5
- 241000894006 Bacteria Species 0.000 description 4
- 239000013618 particulate matter Substances 0.000 description 4
- 238000004062 sedimentation Methods 0.000 description 4
- 239000003814 drug Substances 0.000 description 3
- 239000000463 material Substances 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- 239000003570 air Substances 0.000 description 2
- 239000011324 bead Substances 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 229940079593 drug Drugs 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000002474 experimental method Methods 0.000 description 2
- 239000012530 fluid Substances 0.000 description 2
- 235000013305 food Nutrition 0.000 description 2
- 239000011521 glass Substances 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 230000000813 microbial effect Effects 0.000 description 2
- 230000001546 nitrifying effect Effects 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 238000010992 reflux Methods 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- 238000004065 wastewater treatment Methods 0.000 description 2
- 241000588724 Escherichia coli Species 0.000 description 1
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 1
- 240000004808 Saccharomyces cerevisiae Species 0.000 description 1
- 238000013019 agitation Methods 0.000 description 1
- 150000001413 amino acids Chemical class 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 description 1
- RHZUVFJBSILHOK-UHFFFAOYSA-N anthracen-1-ylmethanolate Chemical compound C1=CC=C2C=C3C(C[O-])=CC=CC3=CC2=C1 RHZUVFJBSILHOK-UHFFFAOYSA-N 0.000 description 1
- 239000003830 anthracite Substances 0.000 description 1
- 239000011805 ball Substances 0.000 description 1
- 239000011942 biocatalyst Substances 0.000 description 1
- 238000005842 biochemical reaction Methods 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 238000004113 cell culture Methods 0.000 description 1
- 238000005119 centrifugation Methods 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 238000006911 enzymatic reaction Methods 0.000 description 1
- 238000005243 fluidization Methods 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 238000000465 moulding Methods 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000011236 particulate material Substances 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 229920003023 plastic Polymers 0.000 description 1
- 229920002401 polyacrylamide Polymers 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- 230000002250 progressing effect Effects 0.000 description 1
- 238000012827 research and development Methods 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 230000003746 surface roughness Effects 0.000 description 1
- 239000008399 tap water Substances 0.000 description 1
- 235000020679 tap water Nutrition 0.000 description 1
- 230000005514 two-phase flow Effects 0.000 description 1
- 238000000108 ultra-filtration Methods 0.000 description 1
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
- 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
- Biological Treatment Of Waste Water (AREA)
Description
〔産業上の利用分野〕
本発明は、発酵、医薬品、食品製造、動植物細
胞培養、下廃水処理など、微生物反応、酵素反応
を利用して目的生産物を得る産業分野における新
しい反応装置に関するものである。
〔従来の技術〕
槽内に有機物分解資化性細菌、硝化菌を収納し
て、排水中の有機物の分解除去反応、アンモニア
性窒素の硝酸化反応を行わせる方法並びに装置と
しては、従来より活性汚泥法を始め、散水ろ床
法、ハニコムチユーブ接触酸化装置、回転円板装
置、粒状媒体流動床装置など種々のものが実用に
供されてきているが、中でも高負荷処理が可能
で、維持管理が容易な上、粒状媒体が槽内を流動
しているために目詰まりによる嫌気化などのトラ
ブルが起こらないなどの利点を有するため、粒状
媒体流動床法が注目を集め、研究開発が進められ
ている。この粒状媒体流動床法には、槽内に配設
したエアリフト管を介して微生物の付着に供する
粒状媒体を循環流動させるもの、あらかじめ、空
気、酸素富化気体で、原水に溶存酸素を供給し、
粒状媒体を収納した槽の底部より該原水を導入し
て粒状媒体を流動化させるもの、粒状媒体を収納
した槽下部より、空気、原水を個別に導入し該媒
体を流動化させるものなど様々なタイプの装置が
提案されてきているが、従来のこれらの装置で
は、空気呼込みによる撹拌によつて、処理液中に
微生物付着粒子が溢出したり、微生物の付着が進
むに従つて次第に粒子の密度が低下し、沈降速度
が低下した粒子が槽外へ溢出するなどの欠点をも
ち、このため、槽上部に撹拌器を設けて粒子から
微生物膜の強制的剥離を行つたり、槽外に流出し
た粒状媒体を沈殿池に設けて沈降させ回収するな
どの対策が講じられてきたが、いずれも効果が不
十分であつたり、新たな装置の付加によりコンパ
クト性が失われたり不経済性が増すなど十分なも
のではなかつた。
微生物を利用して醗酵を行わせ、食品、医薬品
等の有用物質を合成する分野についてみると、従
来は浮遊微生物を槽内に収納した反応操作が主流
であつたが、反応を高効率化、連続化するため、
生体触媒となる微生物を高濃度に培養器中に保持
するため該微生物を高分子物質によつて固定化成
形した粒状物を用いたり、ガラスビーズ、高分子
物質等の担体上に付着させて、反応器内に収納し
て発酵操作を行う方法が近年検討されている。こ
れらの反応操作においても当然、微生物付着粒
子、又は固定化微生物と処理液との分離が必要と
なるが、現在までに有効な分離方法はみられず、
超ろ過膜や遠心分離などの高価な分離方法に依つ
ているのが実情である。
〔発明が解決しようとする問題点〕
本発明は、従来の装置の持つこれら問題点、と
りわけ槽内粒状物の槽外流出を防止し、安価にし
て確実に槽内に保持せしめることを可能にし、も
つて高効率でコンパクトな流動層反応装置を提供
するものである。
〔問題点を解決するための手段〕
本発明は、前に述べた問題点を解決するために
種々の実験を積み重ねた結果、処理液中への粒子
の同伴流出を防止し、槽内に安定して粒状物を保
持して反応を安定して進行させるためには、先
ず、固気液三相流動部から気体の分離された固液
二相部を形成し、該固液二相部から担体粒子を分
離するのが有効であるとの知見に基いてなされた
もので、下部に原液供給部および散気部を有する
槽内に微生物の付着に供する固体粒子、または高
分子物質等により微生物または酵素を固定化成形
して成る粒状物を収納して成る流動層反応槽であ
つて、該槽内にその下端部が該槽壁との間に開口
部を形成する如く傾斜した隔壁を設け、かつ該開
口部下方に該隔壁とほぼ平行に邪魔板を配設する
ことにより固液二相部と固気液三相流動部を区画
形成せしめるとともに、該固液二相部と固気液三
相流動部を区画形成せしめるとともに、該固液二
相部の上部に処理液取出し口を、固気液三相流動
部の上部に分離された気体の出口を設けて成るこ
とを特徴とする流動層反応装置である。
本発明の一実施例を第1図を参照しながら説明
すれば、流動反応槽3の下部は、好適には下方に
行くに従つて断面積が縮少する様に傾斜してお
り、該下部には原液流入部1および散気部2が配
設されており、該槽3内には微生物の付着に供す
る固体粒子または高分子物質等により微生物また
は酵素を固定化成形して成る固定化粒状物11が
収納されている。そして該槽3下部より流入した
原液および空気または酸素富化気体により固体粒
子または固定化粒状物は流動状態に保たれてい
る。原水および空気または酸素富化気体の流入部
は第1図に示す如く、個別に導入される様配設さ
れていても良く、またあらかじめ気液が混合され
た混相流として導入される様配設されていても方
法は問わない。槽内に収納される粒状物は、微生
物を表面上に付着させて反応を行わしめる場合に
は、付着に適し、かつ流動化に適した物性(粒
径、密度、気孔率、表面粗度、沈降速度等)を持
つものが選定され得るが、微生物が付着した場合
の沈降速度の低下、原液の通液速度、空気または
酸素富化気体の通気速度、原液の水理的滞留時間
および層膨脹等を考慮して、一般には、砂、焼結
材、プラスチツク球、アンスラサイト、活性炭、
軽量骨材、ガラスビーズ等が処理目的に応じて選
択使用される。また槽内への充てん量は、通液時
の層膨脹が、沈積時の2培程度となるよう、通液
通気速度を考慮した上、充てん量が決定される。
微生物または酵素を高分子物質等により固定化
成形して成る粒状物を収納する場合には、反応目
的に沿つて製造されたものを利用することができ
る。例えば、用排水処理の場合には、硝化菌をポ
リアクリルアミド、または光架橋性樹脂などで固
定化し、アンモニアの硝化反応を行わせるケー
ス、リグニン分解菌を固定化して紙パルプ系排水
中などからの脱色反応を行わせるケース、また発
酵分野においては、酵母菌を固定化してアルコー
ル生産を行うケースや、アミノ酸発酵のケース、
または遺伝子操作されたE.coli.を固定化して有用
医薬品を生産するケースなど、目的により、その
目的を達成しうる微生物または酵素を選択して固
定化成形した粒状物を用いる等様々な応用ケース
が考えられる。
導入された原液は、槽内で流動化する微生物ま
たは酵素と接触して、好気条件化で生物化学的ま
たは化学的な反応を受けながら、上向流にて槽内
を通過する。
槽の下部では、固体粒子は比較的乱れの少い安
定した流動層9を形成するが、気液の層通過に伴
つて、層界面付近より、特に気泡12に同伴され
て固体粒子が層中より上方に溢出する。槽の上部
には、その下端部が該槽壁との間に開口部14を
形成する如く傾斜した隔壁4が設けられており、
かつ該隔壁とほぼ併行に開口部を覆うように邪魔
板4′が配設されていて、気泡に同伴して溢出し
た粒子は、該邪魔板に沿つて、斜め上方に導かれ
気泡と分離され、隔壁4、邪魔板4′の間隙を通
過して、固液二相流動部10へ流入する。ここ
で、該粒子は液中より分離され、邪魔板、槽壁間
の間隙13を通つて、三相流動部9へ還流する。
この還流路13には、気泡の流入を防ぎ還流を円
滑にするため、整流突起8を設けることが効果的
である。粒子を固液分離した処理液は、固液二相
部上方に配設された処理液取出し口5より流出
し、また邪魔板4′により分離された気泡は、固
気液三相流動部上方に設けられた気体排出口6よ
り槽外に排出される。邪魔板4′の長さは、気泡
が固液2相部へ流入しない長さのものであれば十
分である。
第2図は、本発明の他の実施例を示したもの
で、該隔壁7の長さを短かくし、かつ邪魔板が図
示の様に複数の併行せる板4′,4′……であつて
も同様の効果をもたらす。
槽3は、円筒状または角槽状のいずれであつて
も同様の効果をもたらす様、任意に設計製作する
ことができる。
また、隔壁及び邪魔板の角度は、気泡が固液2
相部へ流入しない角度であれば任意の角度でよい
が、40゜〜60゜位の角度が好ましい。
〔実施例〕
巾50mm×長450mm×高4000mmの第1図及び第2
図に示したような構造の実験装置を用いて、隔壁
4,7、邪魔板4′を設けた場合と設けない場合
の比較実験を行つた。
実験条件
原水:水道水
気体:空気
充てん粒子:粒径0.5〜0.7mm焼結ろ材初期充
填高さ500mm
通液速度:0.4cm/sec
通気速度:0.25cm/sec
24時間連続運転後、処理水中に溢出した粒子
量を測定した。
隔壁及び邪魔板4,4′:槽中間上方部に45゜
傾斜させ、50mm間隔で配設し
た。
隔壁及び邪魔板7,4′:槽中間上方に45゜傾
斜させ、30mm間隔で、4枚の
邪魔板を配設した。
実験結果を表−1に示す。
[Industrial Field of Application] The present invention relates to a new reaction device for use in industrial fields such as fermentation, pharmaceuticals, food manufacturing, animal and plant cell culture, and wastewater treatment, which produce desired products using microbial reactions and enzymatic reactions. be. [Prior art] There are conventional methods and devices for carrying out decomposition and removal reactions of organic matter in wastewater and nitrification reactions of ammonia nitrogen by storing bacteria that decompose and assimilate organic matter and nitrifying bacteria in a tank. Various methods have been put into practical use, including the sludge method, trickling filter method, honeycomb tube catalytic oxidation device, rotating disk device, and granular media fluidized bed device. The granular media fluidized bed method is attracting attention and research and development is progressing because it has the advantage of being easy to use, and because the granular media is flowing in the tank, problems such as anaerobic formation due to clogging do not occur. ing. This granular media fluidized bed method involves circulating and fluidizing the granular media used for the attachment of microorganisms through an airlift pipe installed in a tank, and supplies dissolved oxygen to the raw water in advance with air or oxygen-enriched gas. ,
There are various methods, such as those that introduce raw water from the bottom of a tank containing granular media to fluidize the granular media, and those that fluidize the media by individually introducing air and raw water from the bottom of the tank that contains granular media. However, with these conventional devices, particles attached to microorganisms overflow into the processing liquid due to agitation by air intake, and as the adhesion of microorganisms progresses, the density of particles gradually decreases. This has disadvantages such as particles with reduced sedimentation speed overflowing out of the tank.For this reason, it is necessary to install an agitator at the top of the tank to forcibly separate the microbial film from the particles, or to prevent particles from flowing out of the tank. Countermeasures have been taken, such as setting up a sedimentation tank to settle and recover the granular media, but these methods are not sufficiently effective, and the addition of new equipment causes a loss of compactness and increases uneconomical performance. It was not enough. In the field of fermentation using microorganisms to synthesize useful substances for foods, medicines, etc., conventionally the mainstream reaction operation was to store floating microorganisms in a tank, but now there is a need to make the reaction more efficient. In order to make it continuous,
In order to maintain a high concentration of microorganisms that can serve as biocatalysts in an incubator, the microorganisms are immobilized and molded using a polymeric material, or granules are used, or the microorganisms are attached to a carrier such as glass beads or a polymeric material. In recent years, methods of carrying out fermentation operations by storing them in a reactor have been studied. Naturally, in these reaction operations, it is necessary to separate microorganism-adhered particles or immobilized microorganisms from the treatment liquid, but to date no effective separation method has been found.
The reality is that we rely on expensive separation methods such as ultrafiltration membranes and centrifugation. [Problems to be Solved by the Invention] The present invention solves these problems of conventional devices, in particular, prevents particulate matter from flowing out of the tank, and makes it possible to maintain the particulate matter in the tank reliably at a low cost. This provides a highly efficient and compact fluidized bed reactor. [Means for Solving the Problems] As a result of various experiments conducted in order to solve the above-mentioned problems, the present invention prevents particles from flowing out into the processing liquid and stabilizes them in the tank. In order to hold the particulate matter and allow the reaction to proceed stably, first, a solid-liquid two-phase part from which gas is separated is formed from the solid-gas-liquid three-phase flow part, and then the solid-liquid two-phase part is separated from the solid-liquid two-phase part. This was done based on the knowledge that it is effective to separate carrier particles, and solid particles to which microorganisms can adhere or polymer substances are used to remove microorganisms in a tank that has a stock solution supply section and an aeration section at the bottom. Alternatively, a fluidized bed reaction tank containing a granular material formed by immobilizing and molding an enzyme, in which a partition wall is provided whose lower end is inclined so that an opening is formed between the tank wall and the tank wall. , and by disposing a baffle plate below the opening substantially parallel to the partition wall, a solid-liquid two-phase part and a solid-gas-liquid three-phase flow part are partitioned, and the solid-liquid two-phase part and the solid-gas-liquid A three-phase flow section is formed into sections, and a processing liquid outlet is provided at the top of the solid-liquid two-phase section, and a separated gas outlet is provided at the top of the solid-gas-liquid three-phase flow section. This is a fluidized bed reactor. An embodiment of the present invention will be described with reference to FIG. 1. The lower part of the fluidized reaction tank 3 is preferably sloped so that the cross-sectional area decreases as it goes downward. A stock solution inflow section 1 and an aeration section 2 are arranged in the tank 3, and in the tank 3 there is provided an immobilized particulate material formed by immobilizing microorganisms or enzymes using solid particles or polymeric substances to which microorganisms can adhere. Item 11 is stored. The solid particles or immobilized particles are kept in a fluid state by the raw solution and air or oxygen-enriched gas flowing from the lower part of the tank 3. The inlets for raw water and air or oxygen-enriched gas may be arranged so that they are introduced individually, as shown in Fig. 1, or they may be arranged so that they are introduced as a multiphase flow in which gas and liquid are mixed in advance. Even if it is done, the method does not matter. When a reaction is to be carried out by attaching microorganisms to the surface, the particulate matter stored in the tank must have physical properties suitable for attachment and fluidization (particle size, density, porosity, surface roughness, etc.). However, the reduction in sedimentation rate when microorganisms are attached, the flow rate of the stock solution, the aeration speed of air or oxygen-enriched gas, the hydraulic retention time of the stock solution, and bed expansion can be selected. In general, sand, sintered material, plastic balls, anthracite, activated carbon,
Lightweight aggregates, glass beads, etc. are selected and used depending on the processing purpose. Further, the amount of filling into the tank is determined in consideration of the aeration rate of liquid passage so that the layer expansion during liquid passage is approximately 2 times the size during sedimentation. When storing granular materials formed by immobilizing microorganisms or enzymes with polymeric substances, etc., it is possible to use those manufactured according to the purpose of the reaction. For example, in the case of industrial wastewater treatment, nitrifying bacteria are immobilized with polyacrylamide or photocrosslinkable resin to carry out the nitrification reaction of ammonia, and lignin-degrading bacteria are immobilized to treat pulp and paper wastewater. In the fermentation field, there are cases where yeast is immobilized to produce alcohol, amino acid fermentation cases, etc.
Alternatively, there are various application cases such as the production of useful medicines by immobilizing genetically engineered E. coli, and the use of granules made by selecting and immobilizing microorganisms or enzymes that can achieve the purpose depending on the purpose. is possible. The introduced stock solution comes into contact with microorganisms or enzymes fluidized in the tank, and passes through the tank in an upward flow while undergoing a biochemical or chemical reaction under aerobic conditions. At the bottom of the tank, solid particles form a stable fluidized bed 9 with relatively little turbulence, but as gas and liquid pass through the layer, solid particles are entrained in the layer from near the layer interface, especially by air bubbles 12. It overflows further upwards. A partition wall 4 is provided at the upper part of the tank, and the partition wall 4 is inclined so that its lower end forms an opening 14 between it and the tank wall.
In addition, a baffle plate 4' is arranged almost parallel to the partition wall to cover the opening, and the particles that overflow along with the air bubbles are led obliquely upward along the baffle plate and are separated from the air bubbles. , the partition wall 4, and the baffle plate 4', and flows into the solid-liquid two-phase flow section 10. Here, the particles are separated from the liquid and flow back to the three-phase flow section 9 through the gap 13 between the baffle plate and the tank wall.
It is effective to provide a rectifying protrusion 8 in this reflux path 13 in order to prevent bubbles from flowing in and smooth the reflux. The processing liquid that has separated the particles into solid and liquid flows out from the processing liquid outlet 5 disposed above the solid-liquid two-phase section, and the bubbles separated by the baffle plate 4' flow out above the solid-gas-liquid three-phase flow section. The gas is discharged to the outside of the tank from a gas discharge port 6 provided in the tank. It is sufficient that the length of the baffle plate 4' is long enough to prevent air bubbles from flowing into the solid-liquid two-phase portion. FIG. 2 shows another embodiment of the present invention, in which the length of the partition wall 7 is shortened and the baffle plate is a plurality of parallel plates 4', 4', etc. as shown in the figure. has the same effect. The tank 3 can be arbitrarily designed and manufactured to provide the same effect, whether it is cylindrical or square. Also, the angles of the partition walls and baffle plates are such that the air bubbles are solid-liquid 2
Any angle may be used as long as it does not flow into the phase, but an angle of about 40° to 60° is preferable. [Example] Figures 1 and 2 of width 50mm x length 450mm x height 4000mm
Using an experimental apparatus having the structure shown in the figure, a comparative experiment was conducted with and without the partition walls 4, 7 and the baffle plate 4'. Experimental conditions Raw water: tap water Gas: air Filled particles: particle size 0.5-0.7mm Sintered filter medium initial filling height 500mm Liquid passing rate: 0.4cm/sec Air flow rate: 0.25cm/sec After 24 hours of continuous operation, the treated water was The amount of spilled particles was measured. Partition walls and baffle plates 4, 4': They were arranged at an angle of 45° at an interval of 50 mm in the upper middle part of the tank. Partition walls and baffle plates 7, 4': Four baffle plates were arranged at an angle of 45° above the middle of the tank and spaced at 30 mm intervals. The experimental results are shown in Table-1.
【表】
以上の様に本発明によれば、従来装置のもつ欠
点を簡易な構造にて効果的に解消できる効果的な
流動層反応装置を供給することができる。[Table] As described above, according to the present invention, it is possible to provide an effective fluidized bed reactor that can effectively eliminate the drawbacks of conventional devices with a simple structure.
第1図及び第2図は夫々本発明の流動層反応装
置の断面概略図である。
1……原液流入部、2……散気部、3……流動
反応槽、4,7……隔壁、4′……邪魔板、5…
…処理液取出し口、6……気体排出口、8……整
流突起、11……固体粒子、12……気泡。
1 and 2 are schematic cross-sectional views of the fluidized bed reactor of the present invention, respectively. DESCRIPTION OF SYMBOLS 1... Raw solution inlet, 2... Air diffuser, 3... Fluid reaction tank, 4, 7... Partition wall, 4'... Baffle plate, 5...
...Processing liquid outlet, 6... Gas discharge port, 8... Rectifying projection, 11... Solid particle, 12... Air bubble.
Claims (1)
に、微生物の付着に供する固体粒子、または高分
子物質等により微生物または酵素を固定化、成形
して成る粒状物を収納してなる流動層反応装置で
あつて、該槽内にその下端部が該槽壁との間に開
口部を形成する如く傾斜した隔壁を設け、かつ該
開口部下方に該隔壁とほぼ並行に邪魔板を配設す
ることにより固液二相部と固気液三層流動部を区
画形成せしめるとともに、該固液二相部の上部に
処理液取出し口を、固気液三相流動部の上部に分
離された気体の排出口を設けて成る流動層反応装
置。 2 邪魔板が複数の平行せる板である特許請求の
範囲第1項記載の流動層反応装置。[Scope of Claims] 1. Solid particles to which microorganisms attach, or granular materials formed by immobilizing microorganisms or enzymes with a polymeric substance, etc., are placed in a tank having a stock solution supply section and an aeration section at the bottom. A fluidized bed reactor is a fluidized bed reactor in which a partition wall is provided in the tank, the lower end of which is inclined such that an opening is formed between the tank wall and the partition wall, which is substantially parallel to the partition wall below the opening. By disposing a baffle plate in the solid-liquid two-phase section and the solid-gas-liquid three-phase flow section, a processing liquid outlet is provided at the top of the solid-liquid two-phase section, and a solid-gas-liquid three-phase flow section is formed. A fluidized bed reactor comprising a separated gas outlet at the top of the reactor. 2. The fluidized bed reactor according to claim 1, wherein the baffle plates are a plurality of parallel plates.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60108281A JPS61268396A (en) | 1985-05-22 | 1985-05-22 | Fluidized bed reaction apparatus |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60108281A JPS61268396A (en) | 1985-05-22 | 1985-05-22 | Fluidized bed reaction apparatus |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS61268396A JPS61268396A (en) | 1986-11-27 |
| JPH025154B2 true JPH025154B2 (en) | 1990-01-31 |
Family
ID=14480668
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP60108281A Granted JPS61268396A (en) | 1985-05-22 | 1985-05-22 | Fluidized bed reaction apparatus |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS61268396A (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| TWI235284B (en) * | 1999-03-17 | 2005-07-01 | Winbond Electronics Corp | Photoresist supply device |
| CA2693117A1 (en) * | 2007-06-14 | 2008-12-24 | Kansas State University Research Foundation | Fluidized bed precipitator |
| JP4925208B2 (en) * | 2007-09-12 | 2012-04-25 | 学校法人早稲田大学 | Aerobic granule formation method, water treatment method and water treatment apparatus |
-
1985
- 1985-05-22 JP JP60108281A patent/JPS61268396A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS61268396A (en) | 1986-11-27 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN101842323B (en) | Liquid-solid fluidized bed waste water treatment system for simultaneous carbon, nitrogen and phosphorus removal | |
| CN101977853B (en) | Method and device for the treatment of waste water | |
| EP0213691B1 (en) | A bioconversion reactor | |
| JP5945342B2 (en) | Method and reactor for biological purification of wastewater | |
| CA1143684A (en) | Downflow bioreactor | |
| US6048459A (en) | Method and apparatus for fluidization of particulate bed materials | |
| US5545327A (en) | Wastewater treatment method and apparatus | |
| JPH0729109B2 (en) | Bioreactor | |
| JPS6111136A (en) | Fluidized bed reactor equipped with means for securing uniform distribution of fluid to be treated | |
| US7018534B2 (en) | Apparatus and method for controlling biomass growth in suspended carrier bioreactor | |
| JPS5949075B2 (en) | Wastewater treatment method and device using microorganisms | |
| JPH025154B2 (en) | ||
| JPH06254588A (en) | Ascending flow anaerobic sludge blanket type reaction chamber and method for preventing outflow of granule sludge in this reaction chamber | |
| JPS63214177A (en) | Membrane bioreactor | |
| CN114772870B (en) | Sewage treatment device and method for continuous flow particle size controllable sludge particles | |
| JPS5857238B2 (en) | Wastewater treatment method | |
| GB2425305A (en) | Controlling biomass growth in suspended carrier bioreactor | |
| JPS586555Y2 (en) | Biological treatment equipment for wastewater | |
| JPH0228393B2 (en) | KENKISEIBISEIBUTSUNORYOHOHO | |
| JPS6321554B2 (en) | ||
| KR20010046314A (en) | A Fluidized Biofilm Bed Reactor | |
| JPH0434960Y2 (en) | ||
| JPS6094194A (en) | Treating apparatus for organic waste water | |
| JPS5933438B2 (en) | Anaerobic biological treatment method and device for wastewater | |
| JPS5855090A (en) | Microbialy treating device for waste water by downward flow |