JPH0210719B2 - - Google Patents
Info
- Publication number
- JPH0210719B2 JPH0210719B2 JP58229958A JP22995883A JPH0210719B2 JP H0210719 B2 JPH0210719 B2 JP H0210719B2 JP 58229958 A JP58229958 A JP 58229958A JP 22995883 A JP22995883 A JP 22995883A JP H0210719 B2 JPH0210719 B2 JP H0210719B2
- Authority
- JP
- Japan
- Prior art keywords
- tank
- fluidized bed
- carrier
- carriers
- precipitate
- 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
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 39
- 239000000969 carrier Substances 0.000 claims description 22
- 238000005273 aeration Methods 0.000 claims description 21
- 230000000813 microbial effect Effects 0.000 claims description 17
- 239000002244 precipitate Substances 0.000 claims description 15
- 238000000926 separation method Methods 0.000 claims description 15
- 244000005700 microbiome Species 0.000 claims description 14
- 239000007788 liquid Substances 0.000 claims description 12
- 238000011282 treatment Methods 0.000 claims description 12
- 238000004062 sedimentation Methods 0.000 claims description 9
- 230000005484 gravity Effects 0.000 claims description 6
- 239000000463 material Substances 0.000 claims 1
- 238000000034 method Methods 0.000 description 7
- 241000894006 Bacteria Species 0.000 description 4
- 239000002245 particle Substances 0.000 description 4
- 238000010586 diagram Methods 0.000 description 3
- 239000012528 membrane Substances 0.000 description 3
- 238000005192 partition Methods 0.000 description 3
- 239000004576 sand Substances 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- 239000002351 wastewater Substances 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- 238000009825 accumulation Methods 0.000 description 2
- 238000013019 agitation Methods 0.000 description 2
- 238000013461 design Methods 0.000 description 2
- 230000006866 deterioration Effects 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 238000009287 sand filtration Methods 0.000 description 2
- 239000010802 sludge Substances 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- 238000005299 abrasion Methods 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
- 230000001580 bacterial effect Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000007664 blowing Methods 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 230000005764 inhibitory process Effects 0.000 description 1
- 238000011835 investigation Methods 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 238000012805 post-processing Methods 0.000 description 1
- 230000001376 precipitating effect Effects 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 230000035755 proliferation Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 239000010457 zeolite Substances 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
Description
【発明の詳細な説明】
本発明は、槽内に微生物付着用の担体を懸濁さ
せ、槽内に配備したエアリフト管を使用して気体
撹拌を行いながら前記担体を槽内で循環流動させ
ながら処理する流動床式の汚水の生物処理装置に
関するものである。Detailed Description of the Invention The present invention involves suspending a carrier for attaching microorganisms in a tank, and circulating and flowing the carrier in the tank while performing gas agitation using an air lift tube installed in the tank. This invention relates to a fluidized bed biological treatment device for wastewater.
最近、活性汚泥法によるバルキング現象や維持
管理の複雑さを解消したものとして、チユーブ接
触酸化法、回転円板法、粒状固体流動床法などを
採用した各種の生物膜式汚水処理装置が実用化さ
れている。これらのうち、槽内に懸濁させた粒状
担体の表面に微生物を付着させ、槽内に配備した
エアリフト管を介して気体撹拌を行いながら前記
担体を槽内で循環流動させて汚水と接触させるこ
とによつて汚水中の汚泥物質を除去する流動床法
は、他の生物膜法に比べて微生物の付着に供する
担体の表面積が飛曜的に大きくとれるために槽内
に多量の微生物を保持できる点、担体が槽内を循
環流動しているから目詰りや部分的な嫌気化など
のトラブルが起こらない点など、多くの利点を有
しているために注目を集めている。 Recently, various biofilm-based sewage treatment systems have been put into practical use, employing tube catalytic oxidation, rotating disk method, granular solid fluidized bed method, etc., to eliminate the bulking phenomenon caused by the activated sludge method and the complexity of maintenance. has been done. Among these, microorganisms are attached to the surface of granular carriers suspended in a tank, and the carriers are circulated and flowed in the tank while performing gas agitation via an air lift pipe installed in the tank, and brought into contact with wastewater. The fluidized bed method, which removes sludge substances from wastewater, has a much larger surface area of the carrier for microorganisms to attach to than other biofilm methods, so it is possible to retain a large amount of microorganisms in the tank. It is attracting attention because it has many advantages, such as the fact that the carrier circulates in the tank and does not cause problems such as clogging or partial anaerobic formation.
このような流動床法では、微生物付着用の担体
として砂、アンスラサイト、活性炭、ゼオライ
ト、プラスチツク球などの微生物の付着に適して
おり、かつ槽内を円滑に循環流動するに適した比
重、粒径を持つた粒状固体が用いられるが、通常
は、価格、入手の難易なども考慮して砂が多く用
いられている。 In this type of fluidized bed method, sand, anthracite, activated carbon, zeolite, plastic balls, etc. are used as carriers for microbial attachment, and particles with specific gravity and particles suitable for smooth circulation and flow in the tank are used. A granular solid with a certain diameter is used, but sand is usually used due to its price and availability.
このような流動床法を用いた流動床装置は、第
1図示例の如く、槽1内に微生物付着用の担体2
を懸濁させてあり、槽1内に配備したエアリフト
管3は、その下部に空気導入管4が連結されてお
り、エアリフト管3内に吹き込まれた空気のエア
リフト作用により、原水導入管5から導入された
原水とともに担体2がエアリフト管3の内外を循
環流動している。 In a fluidized bed apparatus using such a fluidized bed method, as shown in the first illustrated example, a carrier 2 for attaching microorganisms is placed in a tank 1.
The air lift pipe 3 installed in the tank 1 has an air introduction pipe 4 connected to its lower part, and due to the air lift action of the air blown into the air lift pipe 3, water is removed from the raw water introduction pipe 5. The carrier 2 is circulating in and out of the air lift pipe 3 together with the introduced raw water.
また、槽1内は、上端が水面上にあり下端が水
面下で槽底と離隔した隔壁6によつて、一部又は
全周が区画され、エアリフト管3の外側に担体2
の分離部7が形成されており、槽1内の懸濁液の
一部はこの分離部7を上昇する間に、担体2を分
離し、上方の流出部8から流出水9として取り出
されるようになつている。 The inside of the tank 1 is partially or entirely partitioned by a partition wall 6 whose upper end is above the water surface and whose lower end is below the water surface and is separated from the tank bottom.
A separation section 7 is formed, and while a part of the suspension in the tank 1 rises through this separation section 7, it separates the carrier 2 and is taken out as effluent water 9 from an upper outflow section 8. It's getting old.
この従来の流動床装置においては、前記流出水
9は後処理のための凝集沈殿装置、砂ろ過装置な
どに送られ、該流出水9中のSS、BOD、COD除
去等の処理を受け、最終処理水となる。しかしな
がら、流動床装置内の担体2は、処理の継続に伴
つて、微生物が付着して肥大化していくため、該
担体2の沈降速度は次第に低下し、遂には分離部
7においては分離しきれなくなり、流出水9中に
同伴されるようになる。その結果、後段の凝集沈
殿装置や砂ろ過装置に閉塞、摩耗等のトラブルを
引き起こすことになる。 In this conventional fluidized bed apparatus, the effluent water 9 is sent to a coagulation-sedimentation device, a sand filtration device, etc. for post-treatment, and is subjected to treatments such as removing SS, BOD, and COD from the effluent water 9, and finally It becomes treated water. However, as the treatment continues, microorganisms adhere to the carrier 2 in the fluidized bed apparatus and the carrier 2 becomes enlarged, so the sedimentation rate of the carrier 2 gradually decreases, and eventually the separation section 7 cannot completely separate the carrier 2. It disappears and becomes entrained in the runoff water 9. As a result, troubles such as clogging and abrasion occur in the coagulation-sedimentation device and sand filter device in the subsequent stage.
従来、このようなトラブルを引き起こさないよ
うに、分離部7をできるだけ余裕をもつて大きく
設計することによつて対応してきたが、どの程度
に微生物が付着し、沈降速度がどの程度までに低
下した担体2を分離するべきなのか判然とし難い
場合が多く、したがつて、勢い分離部7を過大に
設計することになり、構造上も不安定で、かつ不
経済なものとなる場合が多くみられた。 Conventionally, in order to avoid such troubles, the separation section 7 has been designed to have as much room as possible and be made as large as possible. In many cases, it is difficult to determine whether or not the carrier 2 should be separated, and as a result, the force separation section 7 is often designed to be excessively large, resulting in an unstable and uneconomical structure. It was done.
また、流出水9を一旦沈殿池に導き、ここで十
分に沈殿させることで、流出水9に同伴して流出
した微生物の付着した担体2を回収することも考
えられてきたが、この際、流出水9中に含まれる
浮遊状の菌体も担体2と共に沈殿する。この沈殿
物を流動床装置に返送すると、沈殿物中の浮遊状
菌体も同時に返送されるため、流動床内の浮遊菌
体濃度が高くなる。このため、微生物の担体2へ
の付着増殖が妨げられ、本来の機能を低下させた
り、また担体2の流出を助長するなどの新たなト
ラブルを生むこととなつた。 It has also been considered to collect the microorganism-attached carriers 2 that flowed out with the runoff water 9 by once leading the runoff water 9 to a sedimentation tank and sufficiently precipitating it there, but in this case, Floating bacterial cells contained in the effluent water 9 also precipitate together with the carrier 2. When this precipitate is returned to the fluidized bed apparatus, the suspended microbial cells in the precipitate are also returned at the same time, so that the concentration of suspended microbial cells in the fluidized bed increases. For this reason, the adhesion and proliferation of microorganisms to the carrier 2 is hindered, resulting in new troubles such as deterioration of the original function and promotion of outflow of the carrier 2.
本発明は、流動床装置の実際の設計運用にあた
つて発生するこれら従来のトラブルを十分調査研
究して発明されたもので、これら従来のトラブル
を解消し、コンパクトで高負荷処理機能を安定し
て発揮することができる合理的でしかも経済的な
流動床式生物処理装置を提供することを目的とす
るものである。 The present invention was developed after thorough investigation and research into these conventional troubles that occur during the actual design and operation of fluidized bed equipment. The purpose of the present invention is to provide a rational and economical fluidized bed biological treatment device that can perform the following tasks.
本発明は、槽内に微生物付着用の担体を懸濁さ
せ、槽内に配備したエアリフト管によつて前記担
体を循環流動させ、該担体を分離部において比重
差によつて分離して分離水を流出させる流動床式
曝気槽と、該流動床式曝気槽から流出する分離水
を導いて沈殿分離する沈殿槽と、該沈殿槽にて沈
殿した沈殿物を導いて該沈殿物中の前記担体を分
離する液体サイクロンと、該液体サイクロンで分
離された前記担体を前記流動床式曝気槽へ返送す
る返送機構とからなることを特徴とするものであ
り、また本発明は、前記沈殿槽と液体サイクロン
との間に、沈殿槽の沈殿物を導いて該沈殿物中の
担体に付着した微生物膜を剥離する微生物膜剥離
装置を付設したことをも特徴とするものである。 The present invention involves suspending carriers for attaching microorganisms in a tank, circulating the carriers through airlift pipes installed in the tank, and separating the carriers in a separation section based on the difference in specific gravity to produce separated water. a fluidized bed type aeration tank for discharging water, a settling tank for guiding the separated water flowing out from the fluidized bed type aeration tank to precipitate and separate the water, and a settling tank for guiding the precipitate precipitated in the settling tank to remove the carriers in the precipitate. and a return mechanism that returns the carrier separated by the liquid cyclone to the fluidized bed type aeration tank. It is also characterized in that a microbial film stripping device is attached between the cyclone and the microbial film that guides the precipitate in the sedimentation tank and strips the microbial film attached to the carrier in the precipitate.
さらに本発明の実施例を図面を参照しながら説
明すれば、第2図示例において、1は流動床式曝
気槽を示し、第1図に示した従来装置とほとんど
同様であつて、同一符号は同一部分を示すもので
ある。この槽1からの流出水9は、沈殿槽10に
導かれるように連結され、沈殿槽10内に沈殿し
た沈殿物11はポンプPなどによつて液体サイク
ロン12に導かれ、この液体サイクロン12にて
分離された担体2は返送管13により再び流動床
式曝気槽1に返送されるように配列されている。 Further, an embodiment of the present invention will be described with reference to the drawings. In the second illustrated example, 1 indicates a fluidized bed aeration tank, which is almost the same as the conventional device shown in FIG. 1, and the same reference numerals are used. They show the same parts. Outflow water 9 from this tank 1 is connected to be guided to a settling tank 10, and the precipitate 11 settled in the settling tank 10 is led to a hydrocyclone 12 by a pump P etc. The separated carriers 2 are arranged so as to be returned to the fluidized bed type aeration tank 1 via a return pipe 13.
図中、14は沈殿槽10からの溢流水を示す。 In the figure, 14 indicates overflow water from the settling tank 10.
しかして、必要に応じて前処理を受けた原水
は、原水導入管5から流動床式曝気槽1に導入さ
れる。流動床式曝気槽1内には、微生物が付着し
た担体2が懸濁しており、槽内に配備されたエア
リフト管3内に空気導入管4から吹き込まれた空
気によるエアリフト作用により、エアリフト管3
内外を循環流動しており、導入された原水も共に
循環流動する。そして、原水中の汚濁物質は、槽
1内を循環流動している間に、微生物の付着した
担体2と接触し、生物学的に分解除去される。か
くて槽内液の一部は隔壁6にて区画された分離部
7に導かれ、ここで担体2の大部分を比重差によ
り沈降分離して流出部8から流出水9として流出
する。この分離部7の分離面積は、担体2の大部
分が沈降分離され、かつ原水中のSSや、槽1内
で増殖した浮遊状の菌体は流出水9に同伴され流
出するような分離面積となるように決定される。 Thus, the raw water that has been pretreated as necessary is introduced into the fluidized bed type aeration tank 1 from the raw water introduction pipe 5. In the fluidized bed type aeration tank 1, carriers 2 to which microorganisms are attached are suspended, and due to the air lift action of the air blown from the air introduction pipe 4 into the air lift pipe 3 arranged in the tank, the air lift pipe 3
It circulates inside and outside, and the raw water that is introduced also circulates and flows. Then, while circulating and flowing in the tank 1, the pollutants in the raw water come into contact with the carrier 2 to which microorganisms are attached, and are biologically decomposed and removed. A part of the liquid in the tank is thus led to a separation section 7 partitioned by a partition wall 6, where most of the carrier 2 is sedimented and separated due to the difference in specific gravity, and flows out from an outflow section 8 as effluent water 9. The separation area of this separation section 7 is such that most of the carriers 2 are sedimented and separated, and SS in the raw water and floating bacteria grown in the tank 1 are carried away with the outflow water 9 and flowed out. It is determined that
槽1からの流出水9は、続いて沈殿槽10に送
られ、ここで流出水9中に残留している担体2及
び一部の浮遊状SSが沈殿分離される。この沈殿
槽10の分離面積は、大部分の浮遊状SSが沈殿
せず、かつ流入する水中に残留している担体2が
完全に分離するように決められるが、前述した流
動床曝気槽1内の分離部7と異なり、ここでは担
体2が、その単粒子の終末沈降速度にて沈降する
ため、比較的小規模なもので目的を達成すること
が可能である。沈殿槽10で分離されて流出する
溢流水14は、必要に応じて図示しない後段の凝
集沈殿、砂ろ過等の後処理装置に送られる。 The effluent water 9 from the tank 1 is then sent to a settling tank 10, where the carriers 2 and some suspended SS remaining in the effluent water 9 are separated by precipitation. The separation area of this settling tank 10 is determined so that most of the suspended SS does not settle and the carriers 2 remaining in the inflowing water are completely separated. Unlike the separation section 7, here the carrier 2 settles at the terminal sedimentation velocity of its single particles, so it is possible to achieve the purpose with a relatively small scale. The overflow water 14 that is separated in the settling tank 10 and flows out is sent to a subsequent post-processing device (not shown) such as coagulation sedimentation, sand filtration, etc., as necessary.
沈殿槽10にて沈殿した沈殿物11は、ポンプ
Pにて液体サイクロン12に送られ、ここで担体
2と浮遊状のSSが分離され、担体2は回収され
て返送管13から流動床曝気槽1に返送され、浮
遊状のSSは別に取り出されて、場合によつては
前記沈殿槽10の溢流水14と共に後処理装置に
送られる。 The precipitate 11 precipitated in the settling tank 10 is sent to the liquid cyclone 12 by a pump P, where the carrier 2 and floating SS are separated, and the carrier 2 is recovered and sent from the return pipe 13 to the fluidized bed aeration tank. 1, the suspended SS is separately taken out and sent to a post-treatment device together with the overflow water 14 of the settling tank 10, as the case may be.
この液体サイクロン12を設けたことによつ
て、流動床曝気槽1への浮遊菌体の返送がなくな
り、従来起こりがちであつた、流動床曝気槽1内
に浮遊菌体が蓄積することによつて微生物の担体
2への付着が阻害されて処理機能が悪化したり、
担体2の槽外への過度の流出を引き起こすなどの
トラブルを解消することができる。 By providing this liquid cyclone 12, the return of floating bacteria to the fluidized bed aeration tank 1 is eliminated, and the accumulation of floating bacteria in the fluidized bed aeration tank 1, which has tended to occur in the past, is prevented. As a result, the adhesion of microorganisms to the carrier 2 is inhibited, and the processing function deteriorates.
Troubles such as excessive outflow of the carrier 2 out of the tank can be eliminated.
また、本発明は、第3図示例のように、前記液
体サイクロン12の前に微生物膜剥離装置15を
付設することによつても、前述した目的をさらに
効果的に達成することができる。 Further, the present invention can achieve the above-mentioned object more effectively also by attaching a microbial film peeling device 15 in front of the liquid cyclone 12 as shown in the third illustrated example.
すなわち、前記液体サイクロン12の前に微生
物膜剥離装置15を付設し、該剥離装置15に沈
殿槽10からの沈殿物11を導き、沈殿物11中
の過剰に微生物が付着して流出しやすくなつた担
体2から微生物膜を剥離したのち、液体サイクロ
ン12により担体2を分離、回収して流動床曝気
槽1へ返送することによつて、槽1から流出する
担体2の増加を防止し、かつ槽1内の微生物量を
一定に保つことができ、安定した生物処理を継続
することが可能となる。 That is, a microbial membrane stripping device 15 is attached in front of the liquid cyclone 12, and the precipitate 11 from the settling tank 10 is guided to the stripping device 15, so that excess microorganisms in the precipitate 11 adhere to it and easily flow out. After removing the microbial membrane from the carriers 2, the carriers 2 are separated and recovered by the liquid cyclone 12 and returned to the fluidized bed aeration tank 1, thereby preventing an increase in the number of carriers 2 flowing out from the tank 1. The amount of microorganisms in the tank 1 can be kept constant, making it possible to continue stable biological treatment.
なお、この微生物膜剥離装置15としては、撹
拌機あるいは空気吹込みその他による撹拌効果を
利用するなど、担体2表面の微生物膜を十分に剥
離せしめるものであればよいが、例えば第4図示
の実開昭58−40295号公報にみられるような、内
部に担体2よりも粒径又は比重の大なる粒状固体
16を充填した撹拌槽が効果的であつた。 The microbial film peeling device 15 may be any device that can sufficiently peel off the microbial film on the surface of the carrier 2, such as by using a stirrer or the stirring effect of air blowing. For example, the device shown in FIG. A stirring tank filled with granular solids 16 having a larger particle size or specific gravity than the carrier 2, as disclosed in Japanese Patent Publication No. 58-40295, was effective.
以上述べたように、本発明によれば、従来の流
動床装置の欠点であつた、分離部の過大な設計に
よる不経済さ、微生物付着担体の流出による後段
装置のトラブル、流動床曝気槽内への浮遊菌体の
蓄積による担体への付着阻害と処理機能の劣化の
いずれをも解消することができ、流動床生物処理
装置本来の特徴であるコンパクトな装置で、合理
的かつ経済的に高負荷処理性能を安定して発揮せ
しめることができるものである。 As described above, according to the present invention, the drawbacks of the conventional fluidized bed apparatus, such as uneconomical design due to an excessively large separation section, troubles in the downstream equipment due to the outflow of microbial-attached carriers, and problems in the fluidized bed aeration tank. It is possible to eliminate both the inhibition of adhesion to the carrier and the deterioration of the treatment function due to the accumulation of suspended bacteria on the carrier, and it is a compact device that is an original feature of fluidized bed biological treatment equipment, and is rationally and economically efficient. It is possible to stably exhibit load processing performance.
第1図は従来の流動床曝気槽のモデル図、第2
〜3図はそれぞれ本発明の実施例を示すモデル
図、第4図は本発明中の微生物膜剥離装置の一例
を示すモデル図である。
1……流動床曝気槽、2……担体、3……エア
リフト管、4……空気導入管、5……原水導入
管、6……隔壁、7……分離部、8……流出部、
9……流出水、10……沈殿槽、11……沈殿
物、12……液体サイクロン、13……返送管、
15……微生物膜剥離装置。
Figure 1 is a model diagram of a conventional fluidized bed aeration tank, Figure 2
3 to 3 are model diagrams showing embodiments of the present invention, and FIG. 4 is a model diagram showing an example of a microbial membrane peeling device in the present invention. DESCRIPTION OF SYMBOLS 1... Fluidized bed aeration tank, 2... Carrier, 3... Air lift pipe, 4... Air introduction pipe, 5... Raw water introduction pipe, 6... Partition wall, 7... Separation part, 8... Outflow part,
9... Outflow water, 10... Sedimentation tank, 11... Sediment, 12... Liquid cyclone, 13... Return pipe,
15...Microbial film peeling device.
Claims (1)
に配備したエアリフト管によつて前記担体を循環
流動させ、該担体を分離部において比重差によつ
て分離して分離水を流出させる流動床式曝気槽
と、該流動床式曝気槽から流出する分離水を導い
て沈殿分離する沈殿槽と、該沈殿槽にて沈殿した
沈殿物を導いて該沈殿物中の前記担体を分離する
液体サイクロンと、該液体サイクロンで分離され
た前記担体を前記流動床式曝気槽へ返送する返送
機構とからなることを特徴とする生物処理装置。 2 槽内に微生物付着用の担体を懸濁させ、槽内
に配備したエアリフト管によつて前記担体を循環
流動させ、該担体を分離部において比重差によつ
て分離して分離水を流出させる流動床式曝気槽
と、該流動床式曝気槽から流出する分離水を導い
て沈殿分離する沈殿槽と、該沈殿槽にて沈殿した
沈殿物を導いて該沈殿物中の前記担体に付着した
微生物膜を剥離する微生物膜剥離装置と、該微生
物膜剥離装置の流出物を導いて流出物中の前記担
体を分離する液体サイクロンと、該液体サイクロ
ンで分離された前記担体を前記流動床式曝気槽へ
返送する返送機構とからなることを特徴とする生
物処理装置。[Scope of Claims] 1. A carrier for attaching microorganisms is suspended in a tank, the carrier is circulated and flowed through an air lift tube provided in the tank, and the carrier is separated in a separation section based on the difference in specific gravity. A fluidized bed type aeration tank that allows separated water to flow out of the fluidized bed type aeration tank, a settling tank that guides the separated water flowing out from the fluidized bed type aeration tank to precipitate and separate the water, and a sedimentation tank that guides the precipitate precipitated in the settling tank and separates it into the precipitate. A biological treatment device comprising: a liquid cyclone that separates the carrier; and a return mechanism that returns the carrier separated by the liquid cyclone to the fluidized bed aeration tank. 2. Suspend carriers for microbial attachment in a tank, circulate and flow the carriers using an air lift pipe installed in the tank, separate the carriers in a separation section based on the difference in specific gravity, and let the separated water flow out. A fluidized bed type aeration tank, a settling tank for guiding the separated water flowing out from the fluidized bed type aeration tank to precipitate and separate the water, and guiding the precipitate precipitated in the settling tank to adhere to the carrier in the precipitate. A microbial film stripping device that strips a microbial film, a liquid cyclone that guides the effluent of the microbial film stripping device and separates the carriers in the effluent, and a fluidized bed aeration system that removes the carriers separated by the liquid cyclone. A biological treatment device characterized by comprising a return mechanism for returning the material to a tank.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP58229958A JPS60122095A (en) | 1983-12-07 | 1983-12-07 | Biological treatment device |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP58229958A JPS60122095A (en) | 1983-12-07 | 1983-12-07 | Biological treatment device |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS60122095A JPS60122095A (en) | 1985-06-29 |
JPH0210719B2 true JPH0210719B2 (en) | 1990-03-09 |
Family
ID=16900368
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP58229958A Granted JPS60122095A (en) | 1983-12-07 | 1983-12-07 | Biological treatment device |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS60122095A (en) |
Families Citing this family (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2745001B1 (en) * | 1996-02-16 | 1998-04-17 | Degremont | REACTOR FOR BIOLOGICAL ELIMINATION OF ORGANIC WATER POLLUTION |
BR112016009051B1 (en) | 2013-10-22 | 2022-11-01 | Renewable Fibers LLC dba RF WasteWater, LLC | SYSTEM FOR TREATMENT OF A FLUID AND METHOD FOR REDUCING THE CONCENTRATION OF ONE OR MORE SUBSTANCES PRESENT IN A FLUID |
AU2015264014B2 (en) * | 2014-05-21 | 2018-09-06 | Nuvoda Llc | Biofilm media, treatment system and method of treatment |
US10494279B2 (en) | 2015-06-09 | 2019-12-03 | EssDe GmbH | Method for biological cleaning of wastewater |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS56147688A (en) * | 1980-04-15 | 1981-11-16 | Hitachi Plant Eng & Constr Co Ltd | Method and device for fluidized-bed type biological treatment of waste water |
JPS57119892A (en) * | 1981-01-16 | 1982-07-26 | Ebara Infilco Co Ltd | Biological treatment of waste water |
-
1983
- 1983-12-07 JP JP58229958A patent/JPS60122095A/en active Granted
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS56147688A (en) * | 1980-04-15 | 1981-11-16 | Hitachi Plant Eng & Constr Co Ltd | Method and device for fluidized-bed type biological treatment of waste water |
JPS57119892A (en) * | 1981-01-16 | 1982-07-26 | Ebara Infilco Co Ltd | Biological treatment of waste water |
Also Published As
Publication number | Publication date |
---|---|
JPS60122095A (en) | 1985-06-29 |
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