JPH0135272Y2 - - Google Patents

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Publication number
JPH0135272Y2
JPH0135272Y2 JP1986156716U JP15671686U JPH0135272Y2 JP H0135272 Y2 JPH0135272 Y2 JP H0135272Y2 JP 1986156716 U JP1986156716 U JP 1986156716U JP 15671686 U JP15671686 U JP 15671686U JP H0135272 Y2 JPH0135272 Y2 JP H0135272Y2
Authority
JP
Japan
Prior art keywords
chamber
carrier
reaction tank
circulation chamber
center
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
Application number
JP1986156716U
Other languages
Japanese (ja)
Other versions
JPS6363195U (en
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed filed Critical
Priority to JP1986156716U priority Critical patent/JPH0135272Y2/ja
Publication of JPS6363195U publication Critical patent/JPS6363195U/ja
Application granted granted Critical
Publication of JPH0135272Y2 publication Critical patent/JPH0135272Y2/ja
Expired legal-status Critical Current

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Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

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  • Biological Treatment Of Waste Water (AREA)

Description

【考案の詳細な説明】 〔産業上の利用分野〕 本考案は、下水、し尿、産業廃水などの有機性
汚水、もしくは上水源をはじめとするアンモニア
含有水を生物学的に酸化処理する装置に関するも
のである。
[Detailed description of the invention] [Field of industrial application] The present invention relates to an apparatus for biologically oxidizing organic wastewater such as sewage, human waste, and industrial wastewater, or ammonia-containing water such as water sources. It is something.

〔従来の技術〕[Conventional technology]

有機性汚水やアンモニア含有水を生物学的に酸
化する方法は大きく二つに大別される。その第1
は活性汚泥法に代表される浮遊汚泥法であり、第
2は散水床法に代表される生物膜処理法であ
る。これらの違いは、前者が浮遊状態の微生物群
によつて浄化作用を発揮させるのに対し、後者は
生物付着担体を用いて該担体の表面に付着する生
物膜を利用することにある。
Methods for biologically oxidizing organic wastewater and ammonia-containing water can be broadly classified into two types. The first
The second method is a suspended sludge method typified by the activated sludge method, and the second is a biofilm treatment method typified by the sprinkled bed method. The difference between these is that the former uses a group of microorganisms in suspension to exert its purification effect, whereas the latter uses a bioadhesive carrier and utilizes the biofilm that adheres to the surface of the carrier.

近年、生物膜処理法は、生物付着担体の開発に
伴い様々な方法が開発され、脚光をあびている技
術である。なかでも、担体を流動状態で用いるも
のは生物膜処理法の最大の欠点である担体の目詰
まりを抜本的に解決する方法として注目をあびて
いる。
In recent years, biofilm treatment is a technology that has been in the spotlight as various methods have been developed along with the development of bioadhesive carriers. Among these, methods that use a carrier in a fluid state are attracting attention as a method that fundamentally solves the clogging of the carrier, which is the biggest drawback of biofilm treatment methods.

〔考案が解決しようとする問題点〕[Problem that the invention attempts to solve]

しかしながら、生物付着担体を流動状態に適切
に維持するためには、様々な工夫が必要となる。
特に、反応槽の一部に担体がたい積したり、もし
くは浮上したままであつたりして、十分な流動状
態が得られないと、すべての担体が活用されない
ために処理能力が低下すると共に、流動しない部
分が嫌気的になつて悪臭を発生させるなど二次公
害の問題も発生しかねない。
However, various measures are required to properly maintain the bioadhesive carrier in a fluid state.
In particular, if sufficient fluidity cannot be achieved due to carriers accumulating in a part of the reaction tank or remaining floating, all the carriers will not be utilized, resulting in a decrease in processing capacity and There is also the risk of secondary pollution problems, such as areas that are not used becoming anaerobic and emitting bad odors.

本考案は、このような問題点を解決し、反応槽
内で理想的な担体の流動状態が得られる様に工夫
した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 purpose of the present invention is to solve these problems and provide a biological treatment device that is devised so that an ideal carrier fluidity state can be obtained in the reaction tank.

〔問題点を解決するための手段〕[Means for solving problems]

本考案は、生物付着担体を流動可能に収容した
反応槽内を、垂直隔壁によつて区画して中央部に
循環室を形成すると共にその外側に散気室を形成
し、該散気室底部に散気装置を配備し、これら循
環室と散気室とを前記垂直隔壁の上下部において
連通し、更に前記循環室の底部を中央部で高く前
記散気室側に低い斜面に形成したことを特徴とす
る生物処理装置を提供するものである。
In the present invention, the inside of the reaction tank containing the biofouling carrier in a fluidized manner is partitioned by vertical partition walls to form a circulation chamber in the center, and an aeration chamber is formed on the outside of the circulation chamber. The circulation chamber and the air diffusion chamber are connected to each other at the upper and lower portions of the vertical partition wall, and the bottom of the circulation chamber is formed to have a high slope in the center and a low slope toward the air diffusion chamber. The present invention provides a biological treatment device characterized by:

〔実施例〕〔Example〕

本考案の実施例を図面を参照しながら説明すれ
ば、第1図及び第2図例において、1は反応槽で
あつて、原水流入部2と処理水流出部3が設けら
れ、反応槽1内には生物付着用の担体4が流動可
能に収容されている。
Embodiments of the present invention will be described with reference to the drawings. In the examples shown in FIGS. A carrier 4 for biofouling is fluidly accommodated therein.

生物付着用の担体4は、容易に流動化できるも
ので、かつ微生物を多量に保持できるもの、更に
は適切な大きさを有し反応槽1から系外に流出し
にくいものが良い。具体的には、 網目状三次元構造体であり、 比重が水よりわずかに大きいもの (比重1.0〜1.2) 大きさとして10〜50mm角のものが好ましい。
The carrier 4 for biological attachment is preferably one that can be easily fluidized and can hold a large amount of microorganisms, and furthermore, one that has an appropriate size and is difficult to flow out of the reaction tank 1. Specifically, it is preferably a three-dimensional network structure with a specific gravity slightly higher than water (specific gravity 1.0 to 1.2) and a size of 10 to 50 mm square.

また、網目の目開きが小さ過ぎると、担体内部
への基質移動や酸素移動が制限され、担体内部が
有効に利用されなくなる。従つて、網目の目開き
と担体の大きさとの関係は重要であり、例えば10
〜50mm角の大きさを満足させるための網目の目開
きは、種々実験を繰り返した結果、1mm以上が好
ましく、しかし3mm以上では担体内部に微生物が
繁殖しにくいことがわかつた。
Furthermore, if the mesh opening is too small, substrate movement and oxygen movement into the inside of the carrier will be restricted, and the inside of the carrier will not be used effectively. Therefore, the relationship between the mesh opening and the size of the carrier is important; for example, 10
As a result of repeated experiments, it was found that the opening of the mesh to satisfy the size of ~50 mm square is preferably 1 mm or more, but that microorganisms are difficult to breed inside the carrier if it is 3 mm or more.

次に、反応槽1内は、垂直隔壁5,5′によつ
て区画され、中央部に循環室A、その両外側に散
気室B,B′が形成され、散気室B,B′の底部に
は散気装置6が配備され、これらの循環室Aと散
気室B,B′は垂直隔壁5,5′の上下部で連通さ
れている。
Next, the inside of the reaction tank 1 is divided by vertical partition walls 5, 5', and a circulation chamber A is formed in the center, and aeration chambers B and B' are formed on both sides of the circulation chamber A. An air diffuser 6 is provided at the bottom of the chamber, and the circulation chamber A and the air diffuser chambers B and B' are communicated with each other at the upper and lower portions of the vertical partition walls 5 and 5'.

ここで重要なことは、循環室Aが中央部に位置
し、その両外側に散気室B,B′を対称的に形成
する点である。即ち、反応槽1の中央部から散気
すると、槽の端に担体4が浮上したままの状態に
なることがあり、特に、比重が小さくて内部に微
生物を保持する担体を用いた時に顕著にあらわ
れ、スカム状に浮上するばかりでなく、ひどい場
合には大きな塊りになり、少々つついたくらいで
は沈降しないことがある。このように、担体が有
効に利用されないと共に、激しい悪臭を放ち、問
題を生ずるが、本考案のように中央部を循環室A
にし両外側を散気室B,B′とすれば、前記問題
がなくなる。また、循環室Aの底部は、中央部で
高く散気室B,B′側に低い斜面に形成してある
から、循環室Aから散気室B,B′への担体4の
流動を一層円滑にし、担体4が底部へたい積する
ことを有効に防止することができる。なお、反応
槽1の底部自体をこのような形状につくることも
できるが、図示例の様な斜面形成板7を設けても
良い。
What is important here is that the circulation chamber A is located in the center, and the diffuser chambers B and B' are formed symmetrically on both sides of the circulation chamber A. That is, when air is diffused from the center of the reaction tank 1, the carrier 4 may remain floating at the edge of the tank, which is particularly noticeable when using a carrier that has a low specific gravity and retains microorganisms inside. Not only do they appear and float to the surface in the form of a scum, but in severe cases, they form in large clumps that may not settle even if you poke them a little. In this way, the carrier is not used effectively and gives off a strong odor, causing problems.
If both outer sides are made into air diffusion chambers B and B', the above problem will be eliminated. In addition, since the bottom of the circulation chamber A is formed with a slope that is high at the center and low toward the diffusion chambers B and B', the flow of the carrier 4 from the circulation chamber A to the diffusion chambers B and B' is further improved. This can effectively prevent the carrier 4 from accumulating on the bottom. Although the bottom of the reaction tank 1 itself can be formed into such a shape, a slope forming plate 7 as shown in the illustrated example may also be provided.

また、反応槽1の規模が大きくなつた場合に
は、第3図に示す様に垂直板8を循環室A底部の
斜面の頂上に配備すれば、更に担体4の流動が促
進されて効果的である。
In addition, when the scale of the reaction tank 1 increases, if a vertical plate 8 is placed on the top of the slope at the bottom of the circulation chamber A as shown in FIG. 3, the flow of the carrier 4 will be further promoted and effective. It is.

なお、9は散気装置6に空気を送るためのブロ
ワーその他の空気源を示し、10は処理水流出部
3に設けられたスクリーンを示す。
Note that 9 indicates a blower or other air source for sending air to the air diffuser 6, and 10 indicates a screen provided at the treated water outlet portion 3.

しかして、原水は原水流入部2から反応槽1内
に流入し、散気室B,B′底部の散気装置6から
供給される空気によつて原水は微生物を保持した
担体4と共に流動化し、循環室Aを経由しながら
循環流動しつつ好気条件下で生物学的に浄化さ
れ、スクリーン10にて担体4を分離して処理水
流出部3から系外に流出する。そして、循環室A
は反応槽1内中央部に位置し、その両外側に散気
室B,B′があるから、循環流動は槽内全体にわ
たつて円滑、確実に行われ、反応槽全体が均一に
好気状態に維持される。
Thus, the raw water flows into the reaction tank 1 from the raw water inlet 2, and the raw water is fluidized together with the carrier 4 holding microorganisms by the air supplied from the aeration device 6 at the bottom of the aeration chambers B and B'. The water is biologically purified under aerobic conditions while circulating through the circulation chamber A, and the carrier 4 is separated by the screen 10 and flows out of the system from the treated water outlet 3. And circulation room A
is located in the center of the reaction tank 1, and there are aeration chambers B and B' on both sides of it, so circulation flow is carried out smoothly and reliably throughout the tank, and the entire reaction tank is uniformly aerobic. maintained in condition.

上記実施例では反応槽1が角形である場合につ
いて述べたが、反応槽1が円形である場合には、
第4図に示す様に、垂直隔壁5によつて循環室A
を反応槽1と同心的に中央部に形成し、その外周
を散気室Bとする。この場合、循環室Aの底部の
斜面は、円錐又は角錐状の形状とするのが好まし
い。また、その作用は上記角形槽におけると同様
である。
In the above embodiment, the case where the reaction tank 1 is square is described, but when the reaction tank 1 is circular,
As shown in FIG. 4, the circulation chamber A is
is formed in the center concentrically with the reaction tank 1, and its outer periphery is defined as an aeration chamber B. In this case, it is preferable that the slope at the bottom of the circulation chamber A has a conical or pyramidal shape. Moreover, the effect is the same as in the above-mentioned square tank.

〔考案の効果〕[Effect of idea]

以上述べたように本考案によれば、次の様なき
わめて有用なる効果がある。
As described above, the present invention has the following extremely useful effects.

反応槽内の一部に生物付着用の担体がたい積
することがない。
Biofouling carriers do not accumulate in a part of the reaction tank.

反応槽内の一部で生物付着用の担体が浮上
し、スカム状になることがない。
The carrier for bioadhesion does not float up in a part of the reaction tank and form a scum.

反応槽内全体を好気状態に維持することがで
き、悪臭が発生しない。
The entire interior of the reaction tank can be maintained in an aerobic state and no bad odor is generated.

すべての生物付着用の担体が適切に流動化す
るため、常に最高の処理能力を維持することが
できる。
Proper fluidization of all biofouling carriers ensures maximum throughput at all times.

【図面の簡単な説明】[Brief explanation of the drawing]

図面は本考案の実施例を示し、第1図は縦断面
図、第2図はその平面図、第3図は第1図の中央
部底部付近の一例を示す断面図、第4図は他の実
施例を示す平面図である。 A……循環室、B,B′……散気室、1……反
応槽、2……原水流入部、3……処理水流出部、
4……担体、5,5′……垂直隔壁、6……散気
装置、7……斜面形成板、8……垂直板、9……
空気源、10……スクリーン。
The drawings show an embodiment of the present invention, in which Fig. 1 is a longitudinal sectional view, Fig. 2 is a plan view thereof, Fig. 3 is a sectional view showing an example near the center bottom of Fig. 1, and Fig. 4 is a cross-sectional view showing another example. It is a top view showing an example of. A... Circulation room, B, B'... Diffusion room, 1... Reaction tank, 2... Raw water inlet, 3... Treated water outlet,
4...Carrier, 5,5'...Vertical partition wall, 6...Diffuser, 7...Slope forming plate, 8...Vertical plate, 9...
Air source, 10...screen.

Claims (1)

【実用新案登録請求の範囲】 (1) 生物付着担体を流動可能に収容した反応槽内
を、垂直隔壁によつて区画して中央部に循環室
を形成すると共にその外側に散気室を形成し、
該散気室底部に散気装置を配備し、これら循環
室と散気室とを前記垂直隔壁の上下部において
連通し、更に前記循環室の底部を中央部で高く
前記散気室側に低い斜面に形成したことを特徴
とする生物処理装置。 (2) 前記生物付着担体が網目状三次元構造体であ
つて、比重1.0〜1.2、大きさ10〜50mm角である
実用新案登録請求の範囲第1項又は第2項記載
の生物処理装置。
[Claims for Utility Model Registration] (1) The interior of a reaction tank in which a bioadhesive carrier is fluidly accommodated is partitioned by vertical partitions to form a circulation chamber in the center and an aeration chamber outside the chamber. death,
An air diffuser is provided at the bottom of the air diffusion chamber, the circulation chamber and the air diffusion chamber are connected to each other at the upper and lower portions of the vertical partition, and the bottom of the circulation chamber is higher at the center and lower toward the air diffusion chamber. A biological treatment device characterized by being formed on a slope. (2) The biological treatment device according to claim 1 or 2, wherein the bioadhesive carrier is a three-dimensional network structure with a specific gravity of 1.0 to 1.2 and a size of 10 to 50 mm square.
JP1986156716U 1986-10-15 1986-10-15 Expired JPH0135272Y2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1986156716U JPH0135272Y2 (en) 1986-10-15 1986-10-15

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1986156716U JPH0135272Y2 (en) 1986-10-15 1986-10-15

Publications (2)

Publication Number Publication Date
JPS6363195U JPS6363195U (en) 1988-04-26
JPH0135272Y2 true JPH0135272Y2 (en) 1989-10-26

Family

ID=31078597

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1986156716U Expired JPH0135272Y2 (en) 1986-10-15 1986-10-15

Country Status (1)

Country Link
JP (1) JPH0135272Y2 (en)

Also Published As

Publication number Publication date
JPS6363195U (en) 1988-04-26

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