JPS6384693A - Fluidized bed type sewage treatment device - Google Patents
Fluidized bed type sewage treatment deviceInfo
- Publication number
- JPS6384693A JPS6384693A JP61227782A JP22778286A JPS6384693A JP S6384693 A JPS6384693 A JP S6384693A JP 61227782 A JP61227782 A JP 61227782A JP 22778286 A JP22778286 A JP 22778286A JP S6384693 A JPS6384693 A JP S6384693A
- Authority
- JP
- Japan
- Prior art keywords
- water
- tank
- nozzles
- nozzle
- carrier
- 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.)
- Pending
Links
- 239000010865 sewage Substances 0.000 title claims description 12
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 53
- 238000002347 injection Methods 0.000 claims abstract description 21
- 239000007924 injection Substances 0.000 claims abstract description 21
- 239000002351 wastewater Substances 0.000 claims abstract description 19
- 244000005700 microbiome Species 0.000 claims abstract description 7
- 239000000969 carrier Substances 0.000 claims abstract description 5
- 238000013019 agitation Methods 0.000 claims description 2
- 239000005416 organic matter Substances 0.000 claims description 2
- 238000003756 stirring Methods 0.000 abstract description 23
- 238000005507 spraying Methods 0.000 abstract 2
- 238000000034 method Methods 0.000 description 5
- 230000000694 effects Effects 0.000 description 4
- 238000007596 consolidation process Methods 0.000 description 3
- 238000005243 fluidization Methods 0.000 description 3
- 238000005192 partition Methods 0.000 description 3
- 238000001179 sorption measurement Methods 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- 230000002776 aggregation Effects 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 238000005056 compaction Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000010419 fine particle Substances 0.000 description 2
- 239000012530 fluid Substances 0.000 description 2
- 238000007689 inspection Methods 0.000 description 2
- 230000000813 microbial effect Effects 0.000 description 2
- 230000000737 periodic effect Effects 0.000 description 2
- 238000000926 separation method 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
- 230000009471 action Effects 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 238000005054 agglomeration Methods 0.000 description 1
- 238000004220 aggregation Methods 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
- 230000007246 mechanism Effects 0.000 description 1
- 230000000149 penetrating effect Effects 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 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
Abstract
Description
【発明の詳細な説明】
「産業上の利用分野」
本発明は廃水の流動床式汚水処理装置に係わり、!ヱ)
、りは−記動[l豫lこ松いて項内2−辻り与Jや能ピ
太ス微生物付着担体を早期に安定化した流動状態にし得
るとともに、通常運転時において優れた処理能力を発揮
できる汚水処理装置に関するものである。[Detailed Description of the Invention] "Industrial Application Field" The present invention relates to a fluidized bed sewage treatment system for wastewater.ヱ)
It is possible to bring the microorganism-attached carrier into a stable fluid state at an early stage, and to maintain excellent processing capacity during normal operation. This is related to a sewage treatment device that can achieve the desired results.
「従来の技術」
最近、第6図に示すように、砂、活性炭、ゼオライト等
の微粒子(0,1〜0.5mm)を組木1として充填し
た処理槽2内に処理しようとする廃水を注入し、槽内の
流速を循環ポンプ3等の補助手段によって高めて担体l
を流動状態に維持し、同担体lの表面に微生物膜を形成
して槽内に微生物を保持することによって、有機廃水処
理を行う流動床式汚水処理法が開発されている。``Prior art'' Recently, as shown in Fig. 6, wastewater to be treated is placed in a treatment tank 2 filled with fine particles (0.1 to 0.5 mm) of sand, activated carbon, zeolite, etc. as a block 1. The flow rate in the tank is increased by auxiliary means such as a circulation pump 3, and the carrier l is injected into the tank.
A fluidized bed sewage treatment method has been developed in which organic wastewater is treated by maintaining the carrier in a fluidized state and forming a microbial film on the surface of the carrier l to retain the microorganisms in the tank.
この処理方法は、他の処理方法に比べて微生物の付着に
供する担体1の表面積を飛躍的に大きく採れるため、処
理槽2内に多量の微生物を保持できる利点があり、かつ
、処理槽内が流動している関係上目詰まりなどのトラブ
ルが起こりにくい利点もあってその高性能が注目されて
いる。This treatment method has the advantage that a large amount of microorganisms can be retained in the treatment tank 2 because the surface area of the carrier 1 for attachment of microorganisms can be dramatically increased compared to other treatment methods. Its high performance is attracting attention, as it has the advantage of being less prone to problems such as clogging due to its fluid nature.
「発明が解決しようとする問題点」
上記流動床式汚水処理法にあっては、通常運転時におい
て一担体lを流動させるエネルギーを減少させる目的か
ら同担体lを細粒化することが好ましく、しかも、最小
流動状態を保持することが好ましいが、その際、運転条
件によっては、微生物を付着させた担体lが吸着凝集し
て圧密を起こし、偏流が生ずる恐れがある。その対応策
として処理槽2内で攪拌翼を回転させ、これにより圧密
防止を図ったものもあるが、このような対応策では装置
の構造が複雑で大がかりとなり、かつ攪拌翼を回転させ
るための所要動力が必要となるという不具合を伴う。"Problems to be Solved by the Invention" In the fluidized bed sewage treatment method described above, it is preferable to make the carrier 1 into fine particles for the purpose of reducing the energy required to fluidize the carrier 1 during normal operation. Furthermore, although it is preferable to maintain a minimum fluidity state, depending on the operating conditions, the carrier l to which the microorganisms are attached may adsorb and coagulate, causing compaction and causing uneven flow. As a countermeasure, a stirring blade is rotated within the processing tank 2 to prevent consolidation, but such a countermeasure requires a complicated and large-scale device structure, and requires a lot of effort to rotate the stirring blade. This has the disadvantage of requiring a large amount of power.
また、上記流動床式汚水処理法にあっては、起動時ある
いは事故により流入水が停止した場合担体lが処理槽下
部に沈積し、しかもそれが長時間に渡るときには圧密を
起こして運転開始が不能になる場合すらあるという問題
があった。In addition, in the fluidized bed sewage treatment method mentioned above, when the inflow water stops due to startup or an accident, the carrier l settles at the bottom of the treatment tank, and if this continues for a long time, it causes consolidation and prevents the start of operation. The problem was that there were even cases where it became impossible.
本発明は上記事情に鑑みてなされたもので、装置構造が
簡単でかつ特別な所要動力を要することなく担体の圧密
防止が図れ、また圧密を起こした担体の躍動化を容易に
する流動床式汚水処理装置を提供することを目的とする
。The present invention has been made in view of the above circumstances, and is a fluidized bed type device that has a simple device structure, can prevent the consolidation of carriers without requiring special power, and can easily make the consolidated carriers more dynamic. The purpose is to provide sewage treatment equipment.
[問題点を解決するための手段」
本発明では係る目的を達成するために、下部に原水流入
部、上部に処理水流出部、並びに上下部をつなぐ循環水
系を有する処理槽内に、微生物を付着させた担体を流動
させることによって廃水中の有機物を嫌気性状態にて処
理し除去する廃水の流動床式汚水処理装置において、前
記処理槽下部に注入水ノズルを設けるとともに、処理槽
中間部に攪拌ノズルを設け、かつ、それらノズルを注入
水メイン管から枝管を介し分岐させて配置し、それらメ
イン管から分岐した各枝管にそれぞれ切換弁を介装させ
たことを特徴とする。[Means for Solving the Problems] In order to achieve the above object, the present invention introduces microorganisms into a treatment tank having a raw water inlet at the bottom, a treated water outlet at the top, and a circulating water system connecting the upper and lower parts. In a fluidized bed wastewater treatment device for treating and removing organic matter in wastewater in an anaerobic state by fluidizing the adhered carrier, an injection water nozzle is provided at the bottom of the treatment tank, and an injection water nozzle is provided at the middle of the treatment tank. The present invention is characterized in that stirring nozzles are provided, and these nozzles are arranged so as to be branched from the main injection water pipe via branch pipes, and each branch pipe branched from the main pipe is provided with a switching valve, respectively.
「作用」
起動時あるいは定期点検後の再起動時において、循環ポ
ンプ、原水ポンプを一時的に多数並列運転し、かつ切換
弁を操作することによりまず処理槽中間部に配置した攪
拌ノズルのみから廃水を噴射させ、その後、槽下部の注
入水ノズルのみから噴射させる。このように、廃水を各
ノズルからそれぞれ別個に強く噴射させ、もって、処理
槽内の圧密した担体の躍動化を容易にし、処理槽内の担
体流量状態を早期に実現できる。``Operation'' When starting up or restarting after a periodic inspection, by temporarily operating multiple circulation pumps and raw water pumps in parallel, and operating the switching valve, wastewater is first diverted from only the stirring nozzle located in the middle of the treatment tank. is injected, and then only from the injection water nozzle at the bottom of the tank. In this way, the waste water is strongly injected from each nozzle separately, thereby making it easier to make the compacted carrier in the treatment tank more active, and quickly achieving a carrier flow rate state in the treatment tank.
また、通常運転時には、注入水ノズルから廃水を噴射さ
せることによる担体の流量化作用と攪拌ノズルから廃水
を噴射させることによる担体の攪拌作用とが相まって、
処理槽全域にわたり微生物付着担体が吸着凝集して起こ
る偏流を容易に防止することができる。In addition, during normal operation, the flow rate effect of the carrier by injecting waste water from the injection water nozzle is combined with the agitating effect of the carrier by injecting waste water from the stirring nozzle.
It is possible to easily prevent uneven flow caused by adsorption and aggregation of microorganism-adhered carriers over the entire area of the processing tank.
「実施例」 以下、本発明の一実施例を図面を参照して説明する。"Example" Hereinafter, one embodiment of the present invention will be described with reference to the drawings.
第1図は装置全体の概略構成を示し、図中符号11は処
理槽である。処理槽11の下部には上部あるいは中間部
に比べて狭小とされた原水注入部12が設けられ、そこ
には、第2図に示すように多系統(図では3系統)に分
かれた供給管13a〜13cが配備されている。それら
供給管には後述する注入水ノズル14が所定間隔置きに
設けられ、清)−) l庄 り一 リ; n)↑
仁 1ml +々 同 7し 4! −ノ −−1【
スン 八 壮 士 柄たメイン管16に接続されてい
る。各供給管13a=13cおよびそれら供給管をメイ
ン管I6につなぐ接続管(枝管)!7にはそれぞれ切換
弁I8.19が介装されている。なお、上記の如く原水
注入部12を狭小としたのは、特に、起動時において廃
水の流動速度を増大させるためである。FIG. 1 shows a schematic configuration of the entire apparatus, and reference numeral 11 in the figure is a processing tank. A raw water injection part 12 is provided at the bottom of the treatment tank 11, which is narrower than the upper or middle part, and there are supply pipes divided into multiple systems (three systems in the figure) as shown in Figure 2. 13a to 13c are provided. Injection water nozzles 14, which will be described later, are provided at predetermined intervals in these supply pipes.
Jin 1ml + etc. Same 7shi 4! −ノ −−1 [
It is connected to the main pipe 16. Each supply pipe 13a=13c and a connecting pipe (branch pipe) that connects these supply pipes to the main pipe I6! A switching valve I8.19 is interposed in each case. Note that the reason why the raw water injection part 12 is made narrow as described above is to increase the flow rate of wastewater especially at the time of startup.
処理槽IIの中央部外周にはリング管2oが配備され、
該リング管20には周方向所定間隔置きに径方向内方へ
延びて処理槽11の側壁を貫通する枝管21・・・が設
けられ、該枝管21の先端には後述する攪拌ノズル22
が取り付けられている(第3図参照)。これら攪拌ノズ
ル22の内、−個置きに配されたノズルは処理槽IIの
中心に向かうように設けられ、残りのノズル22は処理
槽1」の側壁内面に沿って周方向に傾斜して噴射できる
ように設けられている。また、前記リング管20は切換
弁23が介装された攪拌接続管(枝管)24を介して、
前記メイン管I6の原水ポンプI5の下流側に接続され
ている。A ring pipe 2o is arranged on the outer periphery of the central part of the processing tank II,
The ring pipe 20 is provided with branch pipes 21 extending radially inward and penetrating the side wall of the processing tank 11 at predetermined intervals in the circumferential direction, and at the tips of the branch pipes 21 are provided stirring nozzles 22 to be described later.
is attached (see Figure 3). Among these stirring nozzles 22, every other nozzle is provided so as to face the center of the processing tank II, and the remaining nozzles 22 are inclined in the circumferential direction along the inner surface of the side wall of the processing tank 1. It is set up so that you can. Further, the ring pipe 20 is connected to a stirring connecting pipe (branch pipe) 24 in which a switching valve 23 is interposed.
The main pipe I6 is connected to the downstream side of the raw water pump I5.
処理槽11の上側大径部′)5肉lこは− リ゛ノゲi
Pの隔壁26が設けられ、該隔壁26の外側は分離室2
7が形成されている。分離室27の上部には越流せき2
8によって仕切られた処理水流出部29が設けられ、こ
こにたまる処理後の水は流出管30を通じて外部に排出
される。また、隔壁26の内部からは循環水管31が処
理槽11の側壁を貫通して外部まで延びて設けられ、該
循環水管31は前記メイン管16に接続されるとともに
、そこにはポンプ32が介装されている。なお、前記原
水ポンプ15および循環ポンプ32にはともに予備のポ
ンプが併設されている。The upper large diameter part of the processing tank 11 is
A partition wall 26 of P is provided, and the outside of the partition wall 26 is connected to the separation chamber 2.
7 is formed. There is an overflow weir 2 in the upper part of the separation chamber 27.
A treated water outflow section 29 partitioned by 8 is provided, and the treated water that accumulates there is discharged to the outside through an outflow pipe 30. Further, a circulating water pipe 31 is provided from inside the partition wall 26 to extend to the outside through the side wall of the processing tank 11, and the circulating water pipe 31 is connected to the main pipe 16, and a pump 32 is interposed therebetween. equipped. Note that a spare pump is provided for both the raw water pump 15 and the circulation pump 32.
第1図中符号33は処理槽11の大径部25下側の傾斜
部に設けられた余剰汚水引抜管を示す。Reference numeral 33 in FIG. 1 indicates an excess sewage withdrawal pipe provided at the lower inclined portion of the large diameter portion 25 of the treatment tank 11.
一方、第4図に示すノズル34は、前記注入水ノズル1
4および攪拌ノズル22として利用されるものであって
、ノズル孔34aの上端近傍にはボール35が介装させ
てなる逆止弁36を有し、外周にはステー37を介して
支持されるノズルリング38を有している。このノズル
孔34aを通った廃水は、ノズルリング38の内側に存
する廃水も誘引し、ノズルリング38の上端径の大きな
流れとなって槽内に噴射される。On the other hand, the nozzle 34 shown in FIG.
4 and the stirring nozzle 22, which has a check valve 36 in which a ball 35 is interposed near the upper end of the nozzle hole 34a, and a nozzle supported on the outer periphery via a stay 37. It has a ring 38. The wastewater passing through the nozzle hole 34a also attracts the wastewater existing inside the nozzle ring 38, and is injected into the tank as a flow with a large diameter at the upper end of the nozzle ring 38.
また、第5図に示すノズル40は、前記注入水ノズル1
4として利用されるしのであって、前記ノズル34と共
に適宜の割合で面記供給管13a〜13cに取り付けら
れるものである。このノズル40は、第4図に示すもの
と同様な構成の逆止弁36を有し、かつ、上部外周には
ステー41を介して開口を下方に向けて支持された椀状
の水流変向ガイド42を有している。ノズル孔40aを
通った廃水は水流変向ガイド42に案内されて下方に向
けて噴射される。Further, the nozzle 40 shown in FIG. 5 is the injection water nozzle 1.
4, and is attached to the surface supply pipes 13a to 13c together with the nozzle 34 at an appropriate ratio. This nozzle 40 has a check valve 36 having a configuration similar to that shown in FIG. It has a guide 42. The waste water that has passed through the nozzle hole 40a is guided by the water flow direction guide 42 and is jetted downward.
次に、上記構成の流動床式汚水処理装置の作用について
説明する。Next, the operation of the fluidized bed type sewage treatment apparatus having the above configuration will be explained.
起動時あるいは定期点検後の再起動時においては、原水
ポンプ15および循環ポンプ32を予備を含め一時的に
多数並列運転し、所要の噴射水量を確保する。At startup or at restart after periodic inspection, a large number of raw water pumps 15 and circulation pumps 32, including backup ones, are temporarily operated in parallel to ensure the required amount of water to be injected.
そして、まず、注入水ノズル14側の切換弁!9を閉じ
るとともに攪拌ノズル22側の切換弁23を開き、攪拌
ノズル22のみから廃水を噴射させる。これにより、槽
内に沈積した圧密担体層の上部を膨張させて躍動化させ
る。First, the switching valve on the injection water nozzle 14 side! 9 is closed, and the switching valve 23 on the stirring nozzle 22 side is opened to inject waste water only from the stirring nozzle 22. This causes the upper part of the consolidated carrier layer deposited in the tank to expand and become dynamic.
次に、切換弁23を閉じるとともに切換弁19を開き、
廃水を注入水ノズル14のみから噴射させて圧密担体層
の下部を躍動化させる。しかも、このとき、切換弁18
・・・を操作し、注入水ノズル14が設けられた3系統
の内−つの系統づつ順に廃水を供給し、注入水ノズル1
4からの噴射水量がより多く得られるようにする。なお
、このとき既に圧密層の上側を躍動化させているから、
下側の圧密層の躍動化は比較的容易に行なえる。Next, close the switching valve 23 and open the switching valve 19,
Waste water is injected only from the injection water nozzle 14 to make the lower part of the consolidated carrier layer dynamic. Moreover, at this time, the switching valve 18
... to supply wastewater to each of the three systems in which the injection water nozzle 14 is installed in sequence, and
To obtain a larger amount of water jetted from 4. Furthermore, since the upper side of the consolidated layer has already been activated at this time,
Activation of the lower consolidated layer is relatively easy.
このように、上下の圧密層に対しておのおの別個に躍動
化させて、担体の圧密状態を解く。In this way, the upper and lower compacted layers are individually activated to release the compacted state of the carrier.
一方、通常運転時には、原水ポンプ15と循環ポンプ3
2を作動させ、処理槽11下部に配置した各注入水ノズ
ル14双方から廃水を分配流入させて上向流を起こし、
担体を均一に流動化させるとともに、処理槽中間部に配
置したa拌ノズル2を攪拌流動さ仕て、担体の吸着圧密
による偏流を防止する。On the other hand, during normal operation, the raw water pump 15 and the circulation pump 3
2 is activated, wastewater is distributed and inflowed from both injection water nozzles 14 arranged at the bottom of the treatment tank 11 to create an upward flow,
In addition to uniformly fluidizing the carrier, a stirring nozzle 2 disposed in the middle of the processing tank is used to stir and flow, thereby preventing uneven flow due to adsorption and compaction of the carrier.
なお、上記実施例では処理槽11の中間部に攪拌ノズル
を22を上下方向に一層しか設けていないが、処理槽1
1の形状によっては攪拌ノズル22を多層設けてもよい
。In the above embodiment, the stirring nozzle 22 is provided in the middle part of the processing tank 11 in only one layer in the vertical direction, but the processing tank 1
Depending on the shape of the stirring nozzle 1, the stirring nozzles 22 may be provided in multiple layers.
「発明の効果」
以上説明したように本発明によれば、以下の優れた効果
を奏する。"Effects of the Invention" As explained above, the present invention provides the following excellent effects.
■ 起動時または再起動時、槽中間部の攪拌ノズルと槽
下部の注入水ノズルとをグループ毎に使用すること、ま
た原水ポンプおよび循環ポンプを一時的に多数並列運転
することにより、各ノズルから充分な噴射水量が得られ
るとともに圧密担体層を上下別個に躍動化させることが
でき、もって、槽内の担体流動状態の安定化を早期に図
ることができる。■ At startup or restart, the stirring nozzle in the middle of the tank and the injection water nozzle in the bottom of the tank are used in groups, and by temporarily operating many raw water pumps and circulation pumps in parallel, it is possible to A sufficient amount of water can be obtained, and the upper and lower consolidated carrier layers can be activated separately, thereby making it possible to quickly stabilize the flow state of the carrier in the tank.
■ 通常運転時、槽下部に配した注入水ノズルからの注
入水による担体の流動化の作用と、槽中間 六I?
l−Ll 5 1 +−IA?II I
イ +1. A、 、j rTy nn t
l↓ 1し l−1−’F担体の攪拌作用とが相互に作
用し、微生物付着組体が吸着、凝集して起こる槽内の偏
流を容易に防止することができる。■ During normal operation, the fluidization of the carrier by the injection water from the injection water nozzle placed at the bottom of the tank and the fluidization of the carrier in the middle of the tank.
l-Ll 5 1 +-IA? II I
A +1. A, ,j rTy nn t
1↓ 1 and 1-1-'F The stirring action of the carrier interacts with the carrier, and it is possible to easily prevent uneven flow in the tank caused by adsorption and agglomeration of the microbial adhering assembly.
■ また、流動および攪拌にはすべて噴射水を利用する
ので、機構が単純で装置を簡素化できる。■ In addition, since jet water is used for all fluidization and stirring, the mechanism is simple and the equipment can be simplified.
第1図〜第5図は本発明の一実施例を示し、第1図は装
置全体の概略構成図、第2図は第1図の■−■線矢視図
、第3図は第1図の■−■線矢視図、第4図および第5
図は注入水ノズル、攪拌ノズルの例を示す側断面図、第
6図は流動床式汚水処理装置の一従来例を示す概略構成
図である。
11・・・・・・処理槽、12・・・・・・原水流入部
、14・・・・・・注入水ノズル、15・・・・・・原
水ポンプ、16・・・・・・メイン管、17・・・・・
・接続管(枝管)、18.19.23・・・・・・切換
弁、20・・・・・・リング管、22・・・・・・攪拌
ノズル、24・・・・・・攪拌接続管(枝管)、29・
・・・・・処理水流出部、32・・・・・・循環ポンプ
。
第1図
0a1 to 5 show one embodiment of the present invention, FIG. 1 is a schematic configuration diagram of the entire device, FIG. 2 is a view taken along the line ■-■ in FIG. 1, and FIG. ■-■ line arrow view, Figures 4 and 5 in the figure
The figure is a side sectional view showing an example of an injection water nozzle and an agitation nozzle, and FIG. 6 is a schematic configuration diagram showing a conventional example of a fluidized bed type sewage treatment apparatus. 11... Treatment tank, 12... Raw water inlet, 14... Injection water nozzle, 15... Raw water pump, 16... Main Tube, 17...
・Connecting pipe (branch pipe), 18.19.23...Switching valve, 20...Ring pipe, 22...Stirring nozzle, 24...Stirring Connecting pipe (branch pipe), 29.
... Treated water outflow section, 32 ... Circulation pump. Figure 1 0a
Claims (1)
をつなぐ循環水系を有する処理槽内に、微生物を付着さ
せた担体を流動させることによつて廃水中の有機物を嫌
気性状態にて処理し除去する廃水の流動床式汚水処理装
置において、前記処理槽下部に注入水ノズルを設けると
ともに、処理槽中間部に攪拌ノズルを設け、かつ、それ
らノズルを注入水メイン管から枝管を介し分岐させて配
置し、それらメイン管から分岐した各枝管にそれぞれ切
換弁を介装させたことを特徴とする流動床式汚水処理装
置。Organic matter in wastewater is kept in an anaerobic state by flowing carriers with microorganisms attached to the treatment tank, which has a raw water inlet at the bottom, a treated water outlet at the top, and a circulating water system that connects the upper and lower parts. In a fluidized bed type sewage treatment equipment for wastewater to be treated and removed, an injection water nozzle is provided at the bottom of the treatment tank, an agitation nozzle is provided at the middle of the treatment tank, and these nozzles are connected to the injection water main pipe through a branch pipe. A fluidized bed sewage treatment device characterized in that the pipes are arranged in a branched manner, and each branch pipe branched from the main pipe is provided with a switching valve.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP61227782A JPS6384693A (en) | 1986-09-26 | 1986-09-26 | Fluidized bed type sewage treatment device |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP61227782A JPS6384693A (en) | 1986-09-26 | 1986-09-26 | Fluidized bed type sewage treatment device |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS6384693A true JPS6384693A (en) | 1988-04-15 |
Family
ID=16866294
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP61227782A Pending JPS6384693A (en) | 1986-09-26 | 1986-09-26 | Fluidized bed type sewage treatment device |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS6384693A (en) |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH0240293A (en) * | 1988-07-27 | 1990-02-09 | Japan Organo Co Ltd | Apparatus for anaerobically treating upward flow |
JPH0482084U (en) * | 1990-11-27 | 1992-07-16 | ||
EP0630966A1 (en) * | 1993-06-23 | 1994-12-28 | Gaz De France | Improved apparatus for the anaerobic fermentation of organic materials |
JP2002192179A (en) * | 2000-12-22 | 2002-07-10 | Asahi Eng Co Ltd | Liquid dispersing nozzle |
JP2008086862A (en) * | 2006-09-29 | 2008-04-17 | Nippon Paper Industries Co Ltd | Anaerobic treatment method and arrangement |
CN102976487A (en) * | 2012-12-17 | 2013-03-20 | 吉林市信富机电设备有限责任公司 | Anaerobic water jet stirring device for sewage treatment |
JP2019141781A (en) * | 2018-02-20 | 2019-08-29 | 栗田工業株式会社 | Aerobic biological treatment apparatus and operation method of the same |
-
1986
- 1986-09-26 JP JP61227782A patent/JPS6384693A/en active Pending
Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH0240293A (en) * | 1988-07-27 | 1990-02-09 | Japan Organo Co Ltd | Apparatus for anaerobically treating upward flow |
JPH0482084U (en) * | 1990-11-27 | 1992-07-16 | ||
EP0630966A1 (en) * | 1993-06-23 | 1994-12-28 | Gaz De France | Improved apparatus for the anaerobic fermentation of organic materials |
FR2706905A1 (en) * | 1993-06-23 | 1994-12-30 | Gaz De France | |
US5523234A (en) * | 1993-06-23 | 1996-06-04 | Gaz De France | Equipment for the anaerobic fermentation of organic materials |
JP2002192179A (en) * | 2000-12-22 | 2002-07-10 | Asahi Eng Co Ltd | Liquid dispersing nozzle |
JP2008086862A (en) * | 2006-09-29 | 2008-04-17 | Nippon Paper Industries Co Ltd | Anaerobic treatment method and arrangement |
CN102976487A (en) * | 2012-12-17 | 2013-03-20 | 吉林市信富机电设备有限责任公司 | Anaerobic water jet stirring device for sewage treatment |
JP2019141781A (en) * | 2018-02-20 | 2019-08-29 | 栗田工業株式会社 | Aerobic biological treatment apparatus and operation method of the same |
WO2019163424A1 (en) * | 2018-02-20 | 2019-08-29 | 栗田工業株式会社 | Aerobic biological treatment device and method for operating same |
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