JPH0374156B2 - - Google Patents
Info
- Publication number
- JPH0374156B2 JPH0374156B2 JP61028940A JP2894086A JPH0374156B2 JP H0374156 B2 JPH0374156 B2 JP H0374156B2 JP 61028940 A JP61028940 A JP 61028940A JP 2894086 A JP2894086 A JP 2894086A JP H0374156 B2 JPH0374156 B2 JP H0374156B2
- Authority
- JP
- Japan
- Prior art keywords
- carrier
- immobilized
- microbial cells
- gel
- gel beads
- 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
- 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)
- Treatment Of Biological Wastes In General (AREA)
Description
【発明の詳細な説明】
[産業上の利用分野]
本発明は微生物菌体を担体に膜状に固定化し、
有機物を含有する廃水をこの固定化生物膜に接触
させて処理する廃水の生物化学的処理に用いる菌
体固定化担体並びに該担体の製造法に関するもの
である。[Detailed Description of the Invention] [Industrial Application Field] The present invention immobilizes microbial cells on a carrier in a membrane shape,
The present invention relates to a microbial cell-immobilized carrier used in the biochemical treatment of wastewater in which wastewater containing organic matter is treated by bringing it into contact with the immobilized biofilm, and a method for producing the carrier.
[従来の技術]
廃水中に溶解している有機物を除去するため、
微生物を利用した生物化学的処理が用いられてい
る。従来この方法は廃水中の有機物を基質として
増殖する好気性微生物を処理装置内に浮遊せしめ
て曝気する活性汚泥法が一般的であつたが、この
方法は処理装置内の微生物密度が低いため単位容
積当りの廃水処理量が小さい、維持管理が難しい
ためにフロツクの形成状態によつては固液分離が
難しくなる、等々の問題があつた。この欠点を解
消するためアンスラサイト、砂、活性炭等を微生
物担体に用い、これを処理装置内に充填する固定
層型又は粒状体として流動化させる流動層型によ
り生物膜を付着させて有機物を処理する生物膜法
が用いられている。[Prior art] In order to remove organic matter dissolved in wastewater,
Biochemical treatment using microorganisms is used. Conventionally, this method was generally an activated sludge method in which aerobic microorganisms, which grow using organic matter in wastewater as a substrate, are suspended in a treatment equipment and aerated, but this method has a low density of microorganisms in the treatment equipment, so There were problems such as the small amount of wastewater treated per volume, the difficulty in maintenance, and the difficulty in solid-liquid separation depending on the state of floc formation. To overcome this drawback, anthracite, sand, activated carbon, etc. are used as microbial carriers, and organic matter is treated by attaching biofilm using either a fixed bed type in which the microbial carrier is filled into the processing equipment, or a fluidized bed type in which it is fluidized as a granular material. The biofilm method is used.
[発明が解決しようとする問題点]
上記微生物固定担体を用いる処理法では処理装
置内の微生物密度が高くなるので単位容積当りの
廃水処理量が多くなる。又担体を用いるため固液
分離が容易で余剰汚泥発生量も少ない、といつた
利点がある。しかしこれらの担体は運転開始より
長時間にわたつて生物膜が付着しにくく、又付着
しても担体同志の衝突などにより生物膜が一度剥
離すると、もう一度付着するまでに長時間を要
し、微生物が再び担体表面を覆うまでの間、処理
水の水質が極めて悪化するという欠点があつた。[Problems to be Solved by the Invention] In the treatment method using the above microorganism-immobilized carrier, the density of microorganisms in the treatment device becomes high, so the amount of wastewater treated per unit volume increases. Furthermore, since a carrier is used, solid-liquid separation is easy and the amount of surplus sludge generated is small. However, it is difficult for biofilms to adhere to these carriers for a long time after the start of operation, and even if they do, once the biofilm detaches due to collisions between carriers, it takes a long time for it to attach again, and microorganisms The problem was that the quality of the treated water deteriorated significantly until it covered the surface of the carrier again.
このため、菌体をゲルの微細な格子の中に包み
込むか、半透膜性のポリマー皮膜によつて被覆す
る包括固定化法が開発され、包括固定化の担体と
してポリビニールアルコールをはじめ、ポリアク
リルアミド、寒天等、多くの材料が用いられてい
る。しかし好気性微生物を固定化して廃水の生物
学的処理に用いる場合、包括法ではゲル内への酸
素の拡散が律速となり、微生物の増殖が制限さ
れ、担体の種類や大きさによるが事実上担体のご
く表層の微生物しか反応に関与しない。また包括
固定化法においては、原理的には菌体自身は結合
等反応に直接関与しないが、実際の固定化の操作
では、菌体を包み込む高分子のゲルや皮膜の原料
となるモノマーやポリマーと菌体とを混合して重
合させる、あるいは不溶化させる等の反応を進め
て菌体を固定化するため、この過程で菌体が失活
する可能性がある。これに対してポリビニルアル
コール担体の表面に、穏やかな条件で菌体を結合
固定化させることができれば、固定化の際の失活
を防ぎ、かつ菌体は基質や酸素の失透しやすい担
体表面に多く存在することになり、これを担体と
して有利に利用することができる。 For this reason, entrapping immobilization methods have been developed in which the bacterial cells are encapsulated in a fine lattice of gel or coated with a semipermeable polymer film. Many materials are used, such as acrylamide and agar. However, when immobilizing aerobic microorganisms and using them for biological treatment of wastewater, in the inclusion method, the diffusion of oxygen into the gel becomes rate-limiting, limiting the growth of microorganisms, and depending on the type and size of the carrier, it is effectively Only microorganisms on the surface layer participate in the reaction. In addition, in the entrapment immobilization method, in principle, the bacterial cells themselves are not directly involved in reactions such as binding, but in actual immobilization operations, monomers and polymers that are the raw materials for the polymer gel and film that envelop the bacterial cells are used. Since the bacteria are immobilized by mixing the bacteria and the bacteria and proceeding with a reaction such as polymerization or insolubilization, the bacteria may become inactivated during this process. On the other hand, if bacterial cells can be bonded and immobilized on the surface of a polyvinyl alcohol carrier under mild conditions, deactivation during immobilization can be prevented, and the bacterial cells can easily devitrify the substrate and oxygen on the surface of the carrier. Therefore, it can be advantageously used as a carrier.
ポリビニールアルコールを包括法の菌体固定化
担体として利用する方法は、冷凍法(特願昭59−
261547号)、ホウ酸法(特願昭59−222832号)な
どが報告されている。しかし冷凍法では型に入れ
冷凍によりゲル化された後、円柱状、直方体等に
成形する必要があり、かつこのような形状では機
械攪拌や通気により角が摩耗してまるくなり、担
体が損失するという欠点があつた。又冷凍法、ホ
ウ酸法いずれも水中で使用しているとゲルが溶解
し、固定化した菌体が漏出するため廃水処理装置
内で長時間利用することができないという欠点が
あつた。 The method of using polyvinyl alcohol as a bacterial cell immobilization carrier in the entrapment method is the freezing method (patent application 1983-
261547) and the boric acid method (Japanese Patent Application No. 1983-222832). However, in the freezing method, it is necessary to put it into a mold and gel it by freezing, and then mold it into a cylinder, rectangular parallelepiped, etc., and in such shapes, the corners are worn and rounded due to mechanical stirring and ventilation, resulting in loss of carrier. There was a drawback. Furthermore, both the freezing method and the boric acid method have the disadvantage that when used in water, the gel dissolves and the immobilized bacterial cells leak out, making it impossible to use them for a long time in a wastewater treatment device.
また従来のアンスラサイトや砂等を用いた微生
物の固定化法は、担体をカラム等に充填し、所望
の微生物懸濁液を連続的に通水する形で行われ、
菌体が自然に付着するのを持つものであつたが、
この方法では菌体量をコントロールできない、又
付着する生物膜は極めて薄く、担体表面積当りの
菌体密度を高く保持することができないという問
題点を有していた。 In addition, the conventional immobilization method of microorganisms using anthracite, sand, etc. is carried out by filling a column with a carrier and continuously passing water through the desired microorganism suspension.
It was something that had bacterial bodies that naturally attached to it, but
This method has the problem that the amount of bacterial cells cannot be controlled, and the attached biofilm is extremely thin, making it impossible to maintain a high density of bacterial cells per surface area of the carrier.
そこで本発明は、前記従来技術の欠点を解消す
べく担体表面に微生物を固定化することによつて
これが殖種菌として働き、運転開始時の生物膜が
付着しやすく、生物膜が剥離しても速やかに再生
することができる微生物菌体固定化担体を提供す
ることを目的とするものである。 Therefore, in order to eliminate the drawbacks of the prior art, the present invention immobilizes microorganisms on the surface of a carrier, so that they act as propagating bacteria, which makes it easy for biofilm to adhere at the start of operation, and even when the biofilm peels off. The object of the present invention is to provide a microbial cell immobilization carrier that can be rapidly regenerated.
[問題点を解決するための手段]
上記目的を達成するため、本発明の第1番目は
ポリビニールアルコールごとき親水性プラスチツ
クのゲルビーズの溶化、膨潤した表面に粘着させ
た微生物菌体を前記プラスチツクの再ゲル化物に
より半ば包括した状態で結合固定化させて廃水処
理用微生物固定化担体としたものであり、第2番
目の発明は担体に親水性プラスチツクのゲルビー
ズを用い、その表面に菌体を特殊な方法で固定化
することを特徴とする。すなわち、ポリビニール
のごとき親水性プラスチツクの水溶液をゲル化剤
液中に滴下してゲル化させた後、生成したゲルビ
ーズを水、または固定化する微生物菌体の基質水
溶液、もしくは菌体を遠心分離した上澄中におい
て溶化、膨潤させ、次いで膨潤させたゲルビーズ
に凍結乾燥した菌体を粘着させたのち凍結、解凍
を繰り返して再ゲル化させ、ゲルビーズ表面に粘
着させた微生物菌体を前記再ゲル化物により半ば
包括した形で結合固形化することを特徴とする廃
水処理用菌体固定化担体の製造法にかかるもので
ある。[Means for Solving the Problems] In order to achieve the above object, the first aspect of the present invention is to dissolve gel beads made of hydrophilic plastic such as polyvinyl alcohol, and to attach microbial cells attached to the swollen surface of the plastic. This is a carrier for immobilizing microorganisms for wastewater treatment by bonding and immobilizing them in a state where they are partially encapsulated by the regelled product.The second invention uses gel beads made of hydrophilic plastic as the carrier, and the microorganisms are specially coated on the surface of the gel beads. It is characterized by being immobilized in a fixed manner. That is, after dropping an aqueous solution of a hydrophilic plastic such as polyvinyl into a gelling agent solution and gelling it, the resulting gel beads are poured into water, or an aqueous solution of a substrate of microorganisms to be immobilized, or the cells are centrifuged. The microbial cells were dissolved and swollen in the supernatant, and then the lyophilized microbial cells were adhered to the swollen gel beads, and the microbial cells were repeatedly frozen and thawed to re-gel. The present invention relates to a method for producing a bacterial cell-immobilized carrier for wastewater treatment, which is characterized by binding and solidifying the carrier in a semi-enclosed form with a compound.
本発明における親水性プラスチツクとは、水中
において膨潤して糊状となること、その膨潤させ
る操作が、固定化する菌体に悪影響のないこと
(例えば有機溶媒中での膨潤化は不適)、凍結、解
凍のように菌体を粘着させたのち、溶液中で反応
させるもものでないこと(溶液中では粘着した菌
体が脱落してしまう)、更に凍結・解凍の際に再
ゲル化することが望ましく、一般的にはポリビニ
ールアルコールが用いられる。 In the present invention, hydrophilic plastics are defined as those that swell in water to become pasty, that the swelling operation has no adverse effect on the immobilized microorganisms (for example, swelling in organic solvents is inappropriate), and that it is not suitable for freezing. , The bacteria should not be allowed to react in a solution after being made sticky (as in thawing) (adhesive bacteria will fall off in a solution), and furthermore, it should not re-gel during freezing and thawing. Desirably, polyvinyl alcohol is commonly used.
ポリビニールアルコールはけん化度によつて完
全けん化物と部分けん化物に大別され、さらに重
合度によつて低重合度(300〜500)、中重合度
(1000〜1500)、高重合度(1700〜2400)に分類さ
れる。このうち水に対する溶解性、水溶液粘度及
びその安定性から完全けん化物で中重合度のもの
を用いるのが望ましいと考えられるが、本発明は
これに限定されるものではなく、固定化する微生
物菌体により種々のポリビニールアルコールが使
用し得る。ポリビニールアルコールの濃度は高い
程生成担体ゲルのゲル強度が高くなるが、水に対
する溶解性、水溶液粘度から10〜14%の濃度にな
るように水に溶解した。又溶解に加熱が必要であ
るが、この加熱方法は水蒸気を吹き込む方法(85
〜95℃)等あるが、ママコの生成を防ぐためオー
トクレープ(加圧釜)(100〜120℃)を用いた。
こうして溶解したポリビニールアルコール水溶液
を、液滴を作るべく細口を有するシリンジより直
ちにゲル化剤中に滴下し、球形ゲルを得る。ゲル
化剤としては、たとえば塩化ナトリウム、硫酸ナ
トリウム、ホウ砂、ホウ酸、メチルアルコール、
アセトン等を用いることができるが、ゲル化性か
ら飽和ホウ酸水溶液を用いた。ゲル化を完全に進
行させるためゲル化剤中で1晩程度攪拌、浮遊さ
せた後取り出し、流水にて十分洗浄し、表面のゲ
ル化剤を洗い落とす。 Polyvinyl alcohol is broadly classified into completely saponified products and partially saponified products depending on the degree of saponification, and further classified into low degree of polymerization (300-500), medium degree of polymerization (1000-1500), and high degree of polymerization (1700). ~2400). Among these, it is considered desirable to use a completely saponified product with a medium degree of polymerization in view of its solubility in water, aqueous solution viscosity, and its stability, but the present invention is not limited to this, and the microorganisms to be immobilized are Various polyvinyl alcohols can be used depending on the body. The higher the concentration of polyvinyl alcohol, the higher the gel strength of the resulting carrier gel, but it was dissolved in water to a concentration of 10 to 14% based on its solubility in water and the viscosity of the aqueous solution. Also, heating is required for melting, but this heating method is similar to the method of blowing steam (85
~95℃), but an autoclave (pressure cooker) (100~120℃) was used to prevent the formation of mako.
The polyvinyl alcohol aqueous solution dissolved in this manner is immediately dropped into the gelling agent from a syringe having a narrow opening to form droplets to obtain a spherical gel. Examples of gelling agents include sodium chloride, sodium sulfate, borax, boric acid, methyl alcohol,
Although acetone or the like can be used, a saturated boric acid aqueous solution was used because of its gelling property. In order to allow gelation to proceed completely, the material is stirred and suspended in the gelling agent for about one night, then taken out and thoroughly washed with running water to remove the gelling agent from the surface.
前記のように、従来の微生物の固定化法は、菌
体量をコントロールできないし、又付着する生物
膜は極めて薄く、担体表面積当りの菌体密度を高
く保持することができない。これに対し本発明に
おいては、固定化する菌体を凍結乾燥することに
よつて菌体細胞の有する自由水、間隙水等を昇華
除去し、単位体積当りの乾燥菌体重量を増してこ
れを固定化するため菌体密度を高く維持できる。 As mentioned above, conventional methods for immobilizing microorganisms cannot control the amount of microbial cells, and the attached biofilm is extremely thin, making it impossible to maintain a high density of microbial cells per surface area of the carrier. In contrast, in the present invention, free water, interstitial water, etc. contained in the bacterial cells are sublimated and removed by freeze-drying the bacterial cells to be immobilized, and the dry bacterial weight per unit volume is increased. Because it is immobilized, bacterial cell density can be maintained at a high level.
すなわち、前述のように水洗したゲルビーズを
水又は菌体懸濁液を遠心分離した上澄中に混合
し、数時間攪拌することによりビーズは表面が膨
潤、溶解し、糊状となる。これを水より分離し、
別途凍結乾燥した菌体と混合、表面に乾燥菌体を
粘着させ、次いで冷凍庫内(−20〜−80℃)で凍
結後、室温で解凍、この凍結の操作を2〜3回繰
り返すことによつて溶解したゲル表面は再ゲル化
する。この再表面に粘着していた乾燥菌体は、ゲ
ルに半ば包括される形で結合固定化される。この
ため副次効果として、好気性菌に比較して一般に
担体等への付着力が小さいといわれている嫌気性
菌の固定化にも本発明は利用でき、廃水処理への
用途は拡大すると考えられる。 That is, by mixing the gel beads washed with water as described above in water or the supernatant obtained by centrifuging the bacterial cell suspension and stirring for several hours, the surface of the beads swells, dissolves, and becomes pasty. Separate this from water,
Mix with separately freeze-dried cells, stick the dried cells to the surface, freeze in the freezer (-20 to -80℃), thaw at room temperature, and repeat this freezing process 2 to 3 times. The surface of the gel that has been dissolved by heating is re-gelled. The dried bacterial cells that had been adhering to the resurfaced gel were bound and immobilized in a manner that they were partially encapsulated in the gel. Therefore, as a side effect, the present invention can also be used to immobilize anaerobic bacteria, which are said to have a lower adhesion to carriers than aerobic bacteria, and we believe that its use in wastewater treatment will expand. It will be done.
また、上記特願昭59−261547号および同59−
222832号のごとく冷凍法、ホウ酸法によつて菌体
を固定化したものは、処理期間中にゲルが溶解
し、固定化した菌体が漏出するおそれがある。こ
れに対し本発明のごとく、ポリビニールアルコー
ルで球状様のゲルを作つたのち菌体を表面に固定
化する場合、成形の問題は容易に回避され、又当
該固定化担体を使用する場合においては、表面に
結合した菌体の増殖により菌体同志が粘着結合
し、ゲル形状が保たれるため、長時間の使用に耐
え得る固定化担体を提供することができる。 In addition, the above-mentioned Japanese Patent Application Nos. 59-261547 and 59-261547
When the bacteria are immobilized by the freezing method or the boric acid method as in No. 222832, there is a risk that the gel will dissolve during the treatment period and the immobilized bacteria may leak out. On the other hand, when the bacteria are immobilized on the surface after making a spherical gel with polyvinyl alcohol as in the present invention, the problem of molding can be easily avoided, and when using the immobilization carrier, The growth of the cells bound to the surface causes the cells to adhere to each other and maintain the gel shape, making it possible to provide an immobilization carrier that can withstand long-term use.
なお第1図は、本発明固定化担体作成のフロー
シートを示すものであつて、符号1はPVAの溶
解、2はPVAの水溶液、3はPVA水溶液をゲル
化剤液中に滴下してゲル化、4はゲルビーズの分
離・水洗、5はゲルビーズの表面再溶解、6は被
固定化微生物の懸濁液、7遠心分離、8は凍結乾
燥、9は粉砕、10は前記表面再溶解ゲルビーズ
と粉砕された乾燥菌体との混合、11は冷凍、1
2は解凍、13は冷凍・解凍を繰り返すための回
路、14は固定化担体を示している。 FIG. 1 shows a flow sheet for preparing the immobilization carrier of the present invention, in which reference numeral 1 indicates dissolution of PVA, reference numeral 2 indicates an aqueous solution of PVA, and reference numeral 3 indicates dissolution of PVA by dropping an aqueous PVA solution into a gelling agent solution to form a gel. 4 is separation and washing of gel beads, 5 is surface redissolution of gel beads, 6 is suspension of immobilized microorganisms, 7 is centrifugation, 8 is freeze drying, 9 is pulverization, 10 is surface redissolution of gel beads and Mixing with crushed dry bacterial cells, 11 frozen, 1
2 indicates thawing, 13 a circuit for repeating freezing and thawing, and 14 an immobilization carrier.
以上のように本発明によれば、担体の表面に固
定化された菌体が増殖菌として作用し、生物膜が
速く付着すると共に、たとえ運転中に生物膜が剥
離しても再生が速やかに行われ、一貫して良好な
水質の処理水が得られる。 As described above, according to the present invention, the bacterial cells immobilized on the surface of the carrier act as proliferating bacteria, and the biofilm quickly attaches to it, and even if the biofilm peels off during operation, it is quickly regenerated. This process consistently results in treated water of good quality.
次に実施例に基づいて本発明を詳述するが、本
発明はこれに限定されるものではない。 Next, the present invention will be described in detail based on Examples, but the present invention is not limited thereto.
[実施例]
けん化度98%以上、重合約2000のポリビニール
アルコール250gを水2に懸濁し、オートクレ
ープを用いて120℃(2Kg/cm2)20分で加熱溶解
した。この水溶液を1mm径のノズルより飽和ホウ
酸水溶液中に滴下し、球形のビニールアルコー
ル・ゲルビーズを生成、1晩ホウ酸溶液中で攪拌
した。浄化微生物(活性汚泥)(MLSS4100mg/
)5を遠心分離により集菌し、菌体は3%シ
ヨ糖溶液200mlに分散浮遊させて−55℃で2時間
かけて凍結乾燥させた後、乾式粉砕機により粉砕
し、乾燥粉末菌体21gを得た。活性汚泥を遠心分
離した上澄中で5時間攪拌し、表面を溶解させた
ポリビニールアルコール・ゲルビーズを乾燥菌体
と混合、表面に菌体を粘着させた。これを−40℃
の冷凍庫内で1日凍結させた後、室温で解凍、こ
の凍結、解凍の操作を2回繰り返し、溶解したゲ
ルを再ゲル化して固定化担体2180gを得た。[Example] 250 g of polyvinyl alcohol with a saponification degree of 98% or more and a polymerization of about 2000 was suspended in 2 parts of water, and dissolved by heating at 120°C (2 kg/cm 2 ) for 20 minutes using an autoclave. This aqueous solution was dropped into a saturated boric acid aqueous solution through a 1 mm diameter nozzle to produce spherical vinyl alcohol gel beads, which were stirred overnight in the boric acid solution. Purification microorganisms (activated sludge) (MLSS4100mg/
) 5 was collected by centrifugation, the bacterial cells were dispersed and suspended in 200 ml of 3% sucrose solution, freeze-dried at -55°C for 2 hours, and then ground with a dry grinder to obtain 21 g of dry powdered bacterial cells. I got it. The activated sludge was centrifuged and stirred for 5 hours in the supernatant, and polyvinyl alcohol gel beads whose surfaces had been dissolved were mixed with dried bacterial cells to adhere the bacterial cells to the surface. This is −40℃
After freezing in a freezer for one day, thawing was performed at room temperature, and this freezing and thawing operation was repeated twice to regelify the dissolved gel to obtain 2180 g of immobilized carrier.
得られた固定化担体は、径3.5〜4mmの球状で
前記ゲルビースの表面に粘着乾燥した菌体の一部
が再ゲル化したポリビニールアルコールの薄い被
膜で覆われている。 The obtained immobilization carrier has a spherical shape with a diameter of 3.5 to 4 mm and is covered with a thin film of polyvinyl alcohol in which a portion of the dried bacterial cells that have adhered to the surface of the gel beads has been regelled.
試験例
実施例1で得られた固定化担体を3容の曝気
槽内に投入し、BOD290〜370mg/の都市下水
(CODMo:120〜170mg/、SS:150〜200mg/
)を連続して通水し、滞留時間4時間、容積負
荷2.0Kg−BOD/m3・dayで処理した。90日間運
転した結果を第2図に示す。3日目で処理水は安
定し、その後も良好な処理水が安定して得られ
た。Test Example The immobilized carrier obtained in Example 1 was put into a 3-volume aeration tank, and urban sewage (COD Mo : 120-170 mg/, SS: 150-200 mg/
) was treated by continuously passing water through it for a residence time of 4 hours and a volumetric load of 2.0 Kg-BOD/m 3 ·day. Figure 2 shows the results after 90 days of operation. The treated water became stable on the third day, and good treated water was stably obtained thereafter.
第1図は本発明の微生物固定化担体を作成する
ための工程図、第2図は同上担体を使用して廃水
を曝気処理した場合のBODの経日変化である。
FIG. 1 is a process diagram for producing the microorganism-immobilized carrier of the present invention, and FIG. 2 is a diagram showing the daily change in BOD when wastewater is aerated using the same carrier.
Claims (1)
潤した表面に粘着させた微生物菌体を前記プラス
チツクの再ゲル化物により半ば包括した状態で結
合固定化させたことを特徴とする廃水処理用微生
物固定化担体。 2 親水性プラスチツクの水溶液をゲル化剤液中
に滴化してゲル化させた後、生成したゲルビーズ
を水、または固定化する微生物菌体の基質水溶
液、もしくは菌体を遠心分離した上澄中において
溶化、膨潤させ、次いで上記膨潤したゲルビーズ
に凍結、乾燥した菌体を粘着させたのち凍結、解
凍を繰り返して再ゲル化させ、ゲルビーズ表面に
粘着させた微生物菌体を前記再ゲル化物により半
ば包括した形で結合固定化することを特徴とする
廃水処理用微生物固定化担体の製造法。[Scope of Claims] 1. A wastewater treatment characterized in that microbial cells adhered to the solubilized and swollen surface of hydrophilic plastic gel beads are bound and immobilized in a state in which they are partially encapsulated by the regelled product of the plastic. Microorganism immobilization carrier. 2. After gelling an aqueous solution of hydrophilic plastic in a gelling agent solution, the resulting gel beads are placed in water, an aqueous substrate solution of microbial cells to be immobilized, or a supernatant obtained by centrifuging the microbial cells. After being solubilized and swollen, the frozen and dried microbial cells are adhered to the swollen gel beads, and then frozen and thawed are repeated to regelify the microbial cells, and the microbial cells adhered to the surface of the gel beads are partially encapsulated by the regelled product. A method for producing a microorganism-immobilized carrier for wastewater treatment, characterized by binding and immobilizing microorganisms in such a form.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP61028940A JPS62186995A (en) | 1986-02-14 | 1986-02-14 | Microorganism immobilized carrier for waste water treatment and its production |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP61028940A JPS62186995A (en) | 1986-02-14 | 1986-02-14 | Microorganism immobilized carrier for waste water treatment and its production |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS62186995A JPS62186995A (en) | 1987-08-15 |
| JPH0374156B2 true JPH0374156B2 (en) | 1991-11-26 |
Family
ID=12262403
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP61028940A Granted JPS62186995A (en) | 1986-02-14 | 1986-02-14 | Microorganism immobilized carrier for waste water treatment and its production |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS62186995A (en) |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0372996A (en) * | 1989-08-11 | 1991-03-28 | Kuraray Co Ltd | Water purifying of closed water system and water purifying process |
| US6007712A (en) * | 1997-02-28 | 1999-12-28 | Kuraray Co., Ltd. | Waste water treatment apparatus |
| GB2399084B (en) * | 2002-07-30 | 2007-01-31 | Univ Liverpool | Porous beads and method of production thereof |
| AU2004265544A1 (en) * | 2003-07-31 | 2005-02-24 | Cambridge Polymer Group | Systems and methods for controlling and forming polymer gels |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS55111895A (en) * | 1979-02-20 | 1980-08-28 | Achilles Corp | Filter material for waste liquid treating apparatus |
| JPS59127693A (en) * | 1983-01-08 | 1984-07-23 | Hitachi Plant Eng & Constr Co Ltd | Wastewater treatment method and activated sludge enclosing fixation body used in the method |
-
1986
- 1986-02-14 JP JP61028940A patent/JPS62186995A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS62186995A (en) | 1987-08-15 |
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