JPH07171588A - Continuous fluidizing contact waste water treatment apparatus - Google Patents

Continuous fluidizing contact waste water treatment apparatus

Info

Publication number
JPH07171588A
JPH07171588A JP5320331A JP32033193A JPH07171588A JP H07171588 A JPH07171588 A JP H07171588A JP 5320331 A JP5320331 A JP 5320331A JP 32033193 A JP32033193 A JP 32033193A JP H07171588 A JPH07171588 A JP H07171588A
Authority
JP
Japan
Prior art keywords
wastewater treatment
treatment chamber
wastewater
treated
waste water
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
Application number
JP5320331A
Other languages
Japanese (ja)
Inventor
Iwao Mizusawa
巖 水澤
Kazuo Yamazaki
和夫 山崎
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Maezawa Kasei Kogyo KK
Original Assignee
Maezawa Kasei Kogyo KK
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 by Maezawa Kasei Kogyo KK filed Critical Maezawa Kasei Kogyo KK
Priority to JP5320331A priority Critical patent/JPH07171588A/en
Publication of JPH07171588A publication Critical patent/JPH07171588A/en
Pending legal-status Critical Current

Links

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

Abstract

PURPOSE:To treat waste water with high efficiency by aeration using a small amt. of air by circulating bacteria supported carriers in a waste treatment chamber under stirring to react a BOD substance in waste water to be treated with oxygen in air. CONSTITUTION:The interior of a waste water treatment tank having an almost circular vertical cross section is vertically partitioned and divided at the intermediate part of the vertical cross section by a partition wall 4 and respective circulating stream generating parts 7 are formed to the upper end of the partition wall 4 and air or oxygen blown out of the aerators 8 arranged to the bottom parts of first and second waste water treatment chambers 5, 6 respectively impinges against the circulating stream generating parts 7 as air bubbles. Therefore, circulating streams are generated in the first and second waste water treatment chambers 5, 6 and the bacteria supported carriers 12 are circulated within the first and second waste water treatment chambers 5, 6 under stirring and a BOD substance in waste water to be treated is reacted with oxygen in air. By this constitution, waste water can be treated with high efficiency by aeration using a small amt. of air.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、処理槽内に被処理水を
連続的に流動させて接触処理する小型の連続流動接触排
水処理装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a small continuous fluidized contact wastewater treatment apparatus for continuously treating water to be treated by continuously flowing it into a treatment tank.

【0002】[0002]

【従来の技術】従来、この種の連続流動接触排水処理装
置は、単一の排水処理槽に被処理水の排水原水を導入
し、空気などの酸素を含む気体を送気することにより、
排水処理装置の原水中に予め存在する微生物の保持担体
を流動させながら、この流動状の微生物保持担体と送気
された気体中の酸素を接触させながら反応させ、被処理
水中のBOD物質を分解、浄化させてから処理後の排水
を排出する方法が採られている。そして、このような排
水処理装置としては、土地の有効利用を図ることから地
下に設置されることが好ましく、FRPなどの合成樹脂
材料で工場生産することにより、効率的かつ経済的に製
造できる浄化槽が用いられている。
2. Description of the Related Art Conventionally, this type of continuous fluidized contact wastewater treatment equipment introduces raw water from the wastewater to be treated into a single wastewater treatment tank and sends a gas containing oxygen such as air,
The carrier for microorganisms existing in the raw water of the wastewater treatment device is made to flow, and the carrier for supporting microorganisms in a fluid state is reacted with oxygen in the gas sent to react to decompose the BOD substance in the water to be treated. , The method of purifying and then discharging the waste water after treatment is adopted. As such a wastewater treatment device, it is preferable to install it underground in order to effectively use the land, and a septic tank that can be manufactured efficiently and economically by factory production with a synthetic resin material such as FRP. Is used.

【0003】このような浄化槽の排水処理装置では、微
生物の保持担体を連続的に均一に循環流動させることに
より、排水中のBOD物質を処理する能力が大きくな
り、処理槽の容量を小さくすることができる。
In the wastewater treatment equipment for such a septic tank, the ability to treat the BOD substance in the wastewater is increased and the capacity of the treatment tank is reduced by continuously and uniformly circulating the carrier for holding the microorganisms. You can

【0004】[0004]

【発明が解決しようとする課題】しかしながら、上記の
方法では高効率で処理するには、処理槽内の微生物保持
担体を常時連続的に均一に流動させる必要がある。すな
わち、被処理水量を減少する休日などでも微生物保持担
体を連続的に循環流動させるために、常時排水処理槽に
送気して最小の曝気量を保持しなくてはならず、被処理
水の処理量が減少しても曝気量を減らして動力費を節減
することが困難である。このため、動力費が管理コスト
中の大きな比重を占めるという問題があった。
However, in the above method, in order to perform treatment with high efficiency, it is necessary to constantly and evenly flow the microorganism holding carrier in the treatment tank. That is, in order to continuously circulate the microorganism retention carrier even on holidays when the amount of water to be treated is reduced, it is necessary to constantly send air to the wastewater treatment tank to maintain the minimum aeration amount, and It is difficult to reduce power consumption by reducing the aeration amount even if the treatment amount decreases. For this reason, there is a problem that power costs occupy a large proportion of management costs.

【0005】また、この従来の方法では単一の連続排水
処理する排水処理槽を使用するので、被処理水の中に含
まれる成分が異なる場合と被処理水の流入量が異なる場
合に対して対応ができない問題がある。
Also, since this conventional method uses a single wastewater treatment tank for continuous wastewater treatment, it is possible to compare the case where the components contained in the water to be treated are different and the case where the inflow amount of the water to be treated is different. There is a problem that cannot be dealt with.

【0006】本発明は、このような点に鑑みなされたも
ので、少量の曝気量を保持する送気量で微生物保持担体
を十分に循環に流動させでき、動力費を節減できると共
に被処理水の水質及び水量が異なっても、高効率的に均
一の処理ができ、排水処理槽の製造が容易で、小型高性
能の処理能力を有し、地上設置ばかりでなく、地下埋設
も可能な連続流動接触排水処理装置を提供することを目
的とする。
[0006] The present invention has been made in view of the above-mentioned problems, and it is possible to sufficiently circulate the microorganism-retaining carrier in a circulation with an air supply amount that holds a small aeration amount, reduce power costs, and treat water to be treated. Even if the water quality and amount of water are different, it can perform uniform treatment with high efficiency, easy manufacturing of wastewater treatment tank, has small and high-performance treatment capacity, and can be installed underground as well as underground. An object is to provide a fluidized contact wastewater treatment device.

【0007】[0007]

【課題を解決するための手段】請求項1記載の発明の連
続流動接触排水処理装置は、縦断面が略円形の排水処理
槽を備え、この処理槽の内部を縦断面に対し隔壁によっ
て左右対称に第1の排水処理室と第2の排水処理室とを
それぞれ仕切り分割し、第1の排水処理室と第2の排水
処理室とのそれぞれ一端側に流入口を形成すると共に、
他端側に流出室を形成し、前記隔壁の上部に位置して前
記第1の排水処理室と第2の排水処理室との上部にそれ
ぞれ突出する循環流起生部を形成し、この各循環流起生
部に対向して第1の排水処理室と第2の排水処理室との
底部から吹き出す気体によりこの第1の排水処理室と第
2の排水処理室とを上昇する気泡が前記循環流起生部に
衝突することにより、両処理室内の液体を循環させ、第
1の排水処理室と第2の排水処理室内に収納した微生物
保持担体を両処理室内にそれぞれ撹拌循環させて被処理
排水中のBOD物質と気体中の酸素を反応させる曝気装
置を配設したものである。
According to a first aspect of the present invention, there is provided a continuous fluidized contact wastewater treatment apparatus which comprises a wastewater treatment tank having a substantially circular vertical section, and the inside of the treatment tank is symmetrical with respect to the vertical section by partition walls. The first wastewater treatment chamber and the second wastewater treatment chamber are each divided into partitions to form inflow ports at one end side of each of the first wastewater treatment chamber and the second wastewater treatment chamber,
An outflow chamber is formed on the other end side, and a circulation flow generating part is formed above the partition wall and protrudes above the first wastewater treatment chamber and the second wastewater treatment chamber, respectively. The gas rising from the bottoms of the first wastewater treatment chamber and the second wastewater treatment chamber facing the circulation flow generating portion causes the bubbles that rise in the first wastewater treatment chamber and the second wastewater treatment chamber to rise. By colliding with the circulation flow generation part, the liquid in both treatment chambers is circulated, and the microorganism-holding carrier stored in the first wastewater treatment chamber and the second wastewater treatment chamber is agitated and circulated in both treatment chambers, respectively. An aeration device for reacting the BOD substance in the treated wastewater with oxygen in the gas is provided.

【0008】請求項2記載の発明の連続流動接触排水処
理装置は、請求項1記載の連続流動接触排水処理装置に
おいて、第1の排水処理室と第2の排水処理室との排水
の流入量をそれぞれに調節可能としたものである。
The continuous fluidized contact wastewater treatment equipment of the second aspect of the present invention is the continuous fluidized contact wastewater treatment equipment of the first aspect, wherein the inflow amount of the wastewater into the first wastewater treatment chamber and the second wastewater treatment chamber is the same. Each is adjustable.

【0009】請求項3記載の発明の連続流動接触排水処
理装置は、請求項1または2記載の連続流動接触排水処
理装置において、第1の排水処理室と第2の排水処理室
とにそれぞれ異なる被処理排水原水を流入可能としたも
のである。
The continuous fluidized contact wastewater treatment equipment of the third aspect of the invention is the continuous fluidized contact wastewater treatment equipment of the first or second aspect, wherein the first wastewater treatment chamber and the second wastewater treatment chamber are different from each other. Raw water from treated wastewater can be introduced.

【0010】請求項4記載の発明の連続流動接触排水処
理装置は、請求項1ないし請求項3のいずれかに記載の
連続流動接触排水処理装置において、微生物保持担体は
プラスチックあるいはその発泡体、または多孔質セラミ
ック、またはペレット状活性炭、または微生物を固定化
したプラスチック、または表面を活性炭で被覆したプラ
スチックからなるものである。
A continuous fluidized contact wastewater treatment system according to a fourth aspect of the present invention is the continuous fluidized contact wastewater treatment system according to any one of the first to third aspects, wherein the microorganism retention carrier is plastic or a foam thereof, or It is made of porous ceramics, pellet-like activated carbon, plastic on which microorganisms are immobilized, or plastic whose surface is coated with activated carbon.

【0011】[0011]

【作用】請求項1記載の発明の連続流動接触排水処理装
置は、縦断面が略円形の排水処理槽の内部を縦断面に対
して、中間部に垂直状に仕切り分割した隔壁の上端にそ
れぞれ循環流起生部が形成され、第1の排水処理室と第
2の排水処理室との底部にそれぞれ設けた曝気装置から
吹き出す空気または酸素が気泡となって循環流起生部に
当たり、第1及び第2の排水処理室内に循環流が生じ、
微生物保持担体は第1及び第2の排水処理室をそれぞれ
撹拌されながら循環し、被処理排水中のBOD物質と気
体中の酸素を反応させて高効率的に処理できる。そし
て、処理槽内は第1の排水処理室と第2の排水処理室と
に仕切られているので、被処理水の流入量が例えば2分
の1以下に少なくなった場合は、一方の排水処理室にの
み被処理水の原水を流入し、この一方の排水処理室の曝
気装置のみを作動させることにより、被処理排水を効率
良く処理でき、動力費を削減できる。また、異なる性質
の二種類の被処理排水の処理に際しては第1及び第2の
排水処理室にそれぞれ異なる性質の被処理排水を流入さ
せてそれぞれ独立して処理することにより高効率に排水
処理ができる。また、処理槽は縦断面略円形の形状とし
たため、仕切り形成された第1の排水処理室と第2の排
水処理室との対称形状となり、非対称の形状に比して強
度を保持する処理槽外殻の強度を容易に保持でき、ま
た、角型の処理槽に比して外側の内壁は円弧状に形成さ
れ、曝気装置を隔壁の下方に設けるのみで充分な循環流
が起生され、外殻強度も高められる。
In the continuous fluidized contact wastewater treatment equipment according to the first aspect of the present invention, the inside of the wastewater treatment tank having a substantially circular vertical section is divided into vertical partitions in the middle portion with respect to the vertical section. The circulation flow generation part is formed, and the air or oxygen blown out from the aeration devices provided at the bottoms of the first waste water treatment chamber and the second waste water treatment chamber becomes bubbles to hit the circulation flow generation part. And a circulating flow occurs in the second wastewater treatment chamber,
The microorganism holding carrier circulates in the first and second waste water treatment chambers while being stirred, and reacts the BOD substance in the waste water to be treated with oxygen in the gas for highly efficient treatment. Since the inside of the treatment tank is divided into the first wastewater treatment chamber and the second wastewater treatment chamber, when the inflow amount of the water to be treated is reduced to, for example, one half or less, one of the wastewater is discharged. The raw water to be treated flows into only the treatment chamber, and only the aeration device of the wastewater treatment chamber on one side is operated, whereby the treated wastewater can be efficiently treated and the power cost can be reduced. In addition, when treating two types of wastewater having different properties, the wastewater having different properties is made to flow into the first and second wastewater treatment chambers and treated independently to achieve highly efficient wastewater treatment. it can. In addition, since the treatment tank has a substantially circular vertical cross section, the first wastewater treatment chamber and the second wastewater treatment chamber, which are formed as partitions, have a symmetrical shape, and a treatment tank that retains strength as compared with an asymmetrical shape. The strength of the outer shell can be easily maintained, and the inner wall on the outer side is formed in an arc shape as compared with the rectangular processing tank, and a sufficient circulation flow is generated only by providing the aeration device below the partition wall. The outer shell strength is also increased.

【0012】請求項2記載の発明の連続流動接触排水処
理装置は、被処理水の処理量または被処理排水の性質に
応じて流入量を調節することにより、被処理排水の原水
に応じた条件で処理することができると共に、被処理排
水量が少ないときには一方の排水処理室にのみ流入させ
て処理することもできる。
In the continuous fluidized contact wastewater treatment apparatus of the second aspect of the present invention, the inflow amount is adjusted according to the treatment amount of the treated water or the property of the treated wastewater, so that the condition according to the raw water of the treated wastewater is satisfied. It is also possible to treat the wastewater by treating it in one of the wastewater treatment chambers when the amount of wastewater to be treated is small.

【0013】請求項3記載の発明の連続流動接触排水処
理装置は、それぞれ異なる被処理排水を同一の処理槽内
で同時に処理することができる。
In the continuous fluidized contact wastewater treatment equipment of the third aspect of the present invention, different wastewaters to be treated can be simultaneously treated in the same treatment tank.

【0014】請求項4記載の発明の連続流動接触排水処
理装置は、微生物保持担体は高価な材質で作る必要がな
く、その比重は被処理水よりやや大きくて表面に微生物
を付着し易く、処理室底部の曝気装置で少量の気体を送
気して気泡の上昇による連続的な循環流動が確実にで
き、経済性が向上する。
In the continuous fluidized contact wastewater treatment equipment of the fourth aspect of the present invention, the microorganism holding carrier does not need to be made of an expensive material, and its specific gravity is slightly larger than that of the water to be treated so that microorganisms are easily attached to the surface of the treated water. A small amount of gas is sent by the aerator at the bottom of the chamber to ensure continuous circulating flow due to rising bubbles, which improves economic efficiency.

【0015】[0015]

【実施例】以下、本発明の連続流動接触排水処理装置の
一実施例の構成を図面に参照して説明する。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS The construction of one embodiment of the continuous fluidized contact wastewater treatment equipment of the present invention will be described below with reference to the drawings.

【0016】図1は排水処理槽の縦断正面図、図2はそ
の平面図、図3はその縦断側面図で、図1乃至図3にお
いて、1は縦断面が略円形状の排水処理槽で、FRPな
どの合成樹脂にて成型されている。この排水処理槽1の
上部に点検修理用のマンホール口2が上方に向って開口
され、このマンホール口2には開閉自在の上蓋3が設け
られている。
FIG. 1 is a vertical sectional front view of the wastewater treatment tank, FIG. 2 is a plan view thereof, and FIG. 3 is a vertical sectional side view thereof. In FIGS. 1 to 3, reference numeral 1 is a wastewater treatment tank having a substantially circular longitudinal section. It is made of synthetic resin such as FRP. A manhole port 2 for inspection and repair is opened upward at an upper part of the wastewater treatment tank 1, and the manhole port 2 is provided with an upper lid 3 which can be opened and closed.

【0017】また、前記排水処理槽1の内部は、中間部
から左右に対称に仕切って分割する垂直平板状の隔壁4
が設けられ、この隔壁4にて第1の排水処理室5と第2
の排水処理室6が左右に区画形成されている。この隔壁
4の上部はそれぞれ第1の排水処理室5及び第2の排水
処理室6の上部に突出する円弧状の循環流起生部7,7
が設けられている。
Further, the interior of the wastewater treatment tank 1 is divided into left and right symmetrical partitions from an intermediate portion and is a vertical flat plate-shaped partition wall 4.
The partition wall 4 is provided with a first wastewater treatment chamber 5 and a second wastewater treatment chamber 5.
The wastewater treatment chamber 6 is divided into left and right sections. The upper part of the partition wall 4 has arcuate circulation flow generating parts 7, 7 protruding above the first waste water treatment chamber 5 and the second waste water treatment chamber 6, respectively.
Is provided.

【0018】そして、前記排水処理槽1の第1の排水処
理室5と第2の排水処理室6の底部には前記循環流起生
部7,7の下方に位置して空気あるいは酸素の含量が高
い空気を送気する曝気装置8,8がそれぞれに設けられ
ている。この曝気装置8,8の一端と接続した送気用配
管9,9は曝気調節弁10,10を介して送風ブロワー11,
11に接続されている。この曝気装置8,8から吹き出す
気体は気泡となって前記円弧状の循環流起生部7,7に
向って垂直状に上昇し、上昇水流が生じることにより気
泡と微生物保持担体12とはこの円弧状の循環流起生部
7,7と衝突し、両排水処理室5,6の外側の円弧状の
内面壁13,13に沿って両排水処理室5,6の底部に戻る
循環流によって被処理排水中のBOD物質と垂直状に上
昇する気泡中の酸素とが撹拌され流動接触により酸化さ
れ浄化処理される。
At the bottoms of the first waste water treatment chamber 5 and the second waste water treatment chamber 6 of the waste water treatment tank 1, there are located below the circulating flow generating portions 7, 7 and the air or oxygen content is reduced. Aeration devices 8 and 8 for supplying high air are respectively provided. Air supply pipes 9 and 9 connected to one end of the aeration devices 8 and 8 are provided with a blower blower 11 through an aeration control valve 10 and 10.
Connected to 11. The gas blown out from the aeration devices 8 and 8 becomes bubbles and rises vertically toward the arc-shaped circulation flow generating portions 7 and 7, and the bubbles and the microorganism-holding carrier 12 are separated by the rising water flow. By the circulation flow that collides with the arc-shaped circulation flow generation parts 7, 7 and returns to the bottoms of the waste water treatment chambers 5 and 6 along the arc-shaped inner surface walls 13 and 13 outside the waste water treatment chambers 5 and 6. The BOD substance in the wastewater to be treated and the oxygen in the bubbles rising vertically are stirred and oxidized by fluid contact to be purified.

【0019】また、前記第1の排水処理室5と第2の排
水処理室6とには、循環流が良好に行われるように各排
水処理室5,6のそれぞれ略中央部に垂直状にバッフル
14,14を必要に応じて設けることができる。
Further, in the first wastewater treatment chamber 5 and the second wastewater treatment chamber 6, each of the wastewater treatment chambers 5 and 6 is vertically arranged at a substantially central portion thereof so that a circulating flow is favorably performed. Baffle
14, 14 can be provided as needed.

【0020】また、前記排水処理槽1の一端側上部には
被処理排水の原水の流入口15,15が前記第1の排水処理
室5と第2の排水処理室6の上部に下方に向ってそれぞ
れ開口して設けられ、他端側上部には図2、図3に示す
ように前記第1の排水処理室5と第2の排水処理室6と
の間の上方中央部に位置して処理水の排出口16が開口さ
れている。
In addition, in the upper part of one end of the waste water treatment tank 1, raw water inlets 15, 15 of the waste water to be treated are directed downward to the upper parts of the first waste water treatment chamber 5 and the second waste water treatment chamber 6. 2 and 3, located at the upper center between the first waste water treatment chamber 5 and the second waste water treatment chamber 6 as shown in FIGS. 2 and 3. The treated water discharge port 16 is opened.

【0021】そして、図3に示すように排水処理槽1の
他端側部に前記排出口16と連通する流出室17が仕切板18
にて形成され、この仕切板18の下部に流出孔19が形成さ
れ、この流出孔19には微生物保持担体12の粒子が流出し
ないように粒子よりメッシュの小さい金網20,20が配設
されている。この金網20,20の材質は微生物の付着を防
止するためには銅にて形成することが好ましい。
As shown in FIG. 3, an outflow chamber 17 communicating with the discharge port 16 is provided at the other end of the waste water treatment tank 1 with a partition plate 18.
The outlet plate 19 is formed in the lower part of the partition plate 18, and wire meshes 20, 20 having a smaller mesh than the particles are arranged in the outlet hole 19 so that the particles of the microorganism-holding carrier 12 do not flow out. There is. The material of the wire nets 20, 20 is preferably made of copper in order to prevent the adhesion of microorganisms.

【0022】また、前記第1の排水処理室5と第2の排
水処理室6内に予めに存在する微生物保持担体12は、そ
の比重が被処理排水の原水よりやや大きく、各排水処理
室5,6の底部に位置される曝気装置8,8から吹き出
した上昇気泡によって垂直状に上昇することにより、隔
壁4の上端に略円弧状の循環流起生部7,7と衝突して
から、各排水処理室5,6の円弧状の内面壁13,13に沿
ってこの排水処理室5,6の底部に戻って充分に循環流
動させることができるので、高価な材質で作る必要がな
く、その比重は被処理排水の原水よりやや大きくて表面
または裏面に微生物を付着し易いプラスチックあるいは
その発泡体、または多孔質セラミック、またはペレット
状活性炭、または微生物を固定化したプラスチック、ま
たは表面を活性炭で被覆したプラスチックのようなもの
が好ましい。
The microorganism holding carrier 12 existing in advance in the first wastewater treatment chamber 5 and the second wastewater treatment chamber 6 has a specific gravity slightly larger than the raw water of the wastewater to be treated, and each wastewater treatment chamber 5 has a specific gravity. , 6 vertically rises by the rising bubbles blown from the aerators 8 and 8 located at the bottom of the separators 6, and collides with the upper end of the partition wall 4 with the circular flow generation portions 7 and 7, It is possible to return to the bottoms of the wastewater treatment chambers 5, 6 along the arc-shaped inner walls 13, 13 of the respective wastewater treatment chambers 5, 6 and to circulate them sufficiently, so there is no need to make them with expensive materials, Its specific gravity is slightly larger than the raw water of the wastewater to be treated, and plastic or its foam that easily attaches microorganisms to the front or back surface, or porous ceramics, or pelletized activated carbon, or plastic on which microorganisms are immobilized, or activated carbon on the surface. Such is preferred as the overturned plastic.

【0023】なお、前記曝気による第1の排水処理室5
と第2の排水処理室6との排気口は例えば、前記上蓋3
に形成する。
The first wastewater treatment chamber 5 by the aeration described above.
The exhaust port between the second wastewater treatment chamber 6 and the second wastewater treatment chamber 6 is, for example, the upper lid 3
To form.

【0024】さらに、図4に示すように被処理排水の原
水調節槽21に接続した流入管22はそれぞれ流入量調節弁
23,23を介して排水処理槽1の第1の排水処理室5と第
2の排水処理室6との流入口15,15に分岐接続されてい
る。
Further, as shown in FIG. 4, the inflow pipes 22 connected to the raw water control tank 21 for the wastewater to be treated are respectively inflow control valves.
It is branched and connected to the inlets 15 and 15 of the first wastewater treatment chamber 5 and the second wastewater treatment chamber 6 of the wastewater treatment tank 1 via 23 and 23.

【0025】つぎに、この実施例の作用について説明す
る。
Next, the operation of this embodiment will be described.

【0026】縦断面が略円形の排水処理槽1の内部にお
いては、中心部に垂直状の隔壁4で第1の排水処理室5
と第2の排水処理室6を完全に分けられ、この隔壁4の
上端には左右対称に略円弧状の循環流起生部7,7がそ
れぞれ形成されているので、第1の排水処理室5と第2
の排水処理室6の底部に設けた曝気装置8,8から吹き
出した気体は気泡となって前記の略円弧状の循環流起生
部7,7に向って垂直状に上昇する。前記第1の排水処
理室5と第2の排水処理室6内に予めに存在する微生物
保持担体12もこの上昇の気泡によって上昇し、前記隔壁
4の上端に略円弧状の循環流起生部7,7と衝突するこ
とにより、排水処理槽1内の第1の排水処理室5と第2
の排水処理室6の円弧状の内面壁13に沿って両排水処理
室5,6の底部に戻る循環流により排水処理槽1内の第
1の排水処理室5と第2の排水処理室6の被処理水中の
BOD物質は微生物保持担体12と曝気装置8,8から吹
き出した気泡中の酸素との連続的に流動接触により酸化
して高効率的に分解処理される。
Inside the wastewater treatment tank 1 having a substantially circular vertical section, the first wastewater treatment chamber 5 is formed by the partition wall 4 which is vertical to the center.
And the second waste water treatment chamber 6 are completely divided, and the circular flow generation portions 7, 7 having a substantially circular arc shape are formed symmetrically at the upper end of the partition wall 4, respectively. 5 and 2
The gas blown out from the aeration devices 8 provided at the bottom of the waste water treatment chamber 6 becomes bubbles and rises vertically toward the above-mentioned substantially arc-shaped circulation flow generating portions 7, 7. The microorganism holding carrier 12 existing in advance in the first wastewater treatment chamber 5 and the second wastewater treatment chamber 6 also rises due to the rising bubbles, and a substantially circular arc-shaped circulation flow generating portion is formed at the upper end of the partition wall 4. By colliding with the first and second wastewater treatment chambers 5 and 2 in the wastewater treatment tank 1,
The first wastewater treatment chamber 5 and the second wastewater treatment chamber 6 in the wastewater treatment tank 1 by the circulation flow returning to the bottoms of the wastewater treatment chambers 5 and 6 along the arc-shaped inner wall 13 of the wastewater treatment chamber 6 of FIG. The BOD substance in the water to be treated is oxidized by the continuous fluid contact between the microorganism holding carrier 12 and the oxygen in the bubbles blown out from the aeration devices 8 and is decomposed with high efficiency.

【0027】第1の排水処理室5と第2の排水処理室6
にて処理された処理水は流出孔19から流出室17に流入
し、このとき、微生物保持担体12は金網20,20により処
理排水と共に流出されることがなく、流出孔19から第1
の排水処理室5と第2の排水処理室6にて処理された処
理水が合流して排出される。
First wastewater treatment chamber 5 and second wastewater treatment chamber 6
The treated water treated in 1 flows into the outflow chamber 17 through the outflow hole 19, and at this time, the microorganism holding carrier 12 does not flow out together with the treated wastewater by the wire nets 20, 20,
The treated water treated in the wastewater treatment chamber 5 and the second wastewater treatment chamber 6 are combined and discharged.

【0028】また、休日または、操業時間帯により被処
理水の流入量が減少した場合には、曝気調節弁10,10を
調節して、適当な曝気量とし、また、被処理排水原水
が、例えば、所定流量より2分の1以下になった場合に
は、原水調節弁23,23の一方の原水調節弁を閉じると共
に、曝気調節弁10,10の一方を閉じて排水処理室5,6
の一方の排水処理室を休止することにより、曝気用動力
費用を低減できる。
Further, when the inflow amount of the treated water decreases due to holidays or the operating hours, the aeration control valves 10 and 10 are adjusted to an appropriate aeration amount, and the raw water to be treated is For example, when the flow rate becomes half or less than the predetermined flow rate, one of the raw water control valves 23, 23 is closed and one of the aeration control valves 10, 10 is closed to close the wastewater treatment chambers 5, 6.
By shutting down one of the wastewater treatment chambers, the power cost for aeration can be reduced.

【0029】なお、曝気装置8,8は、第1の排水処理
室5と第2の排水処理室6の底部に循環流起生部7,7
と対向した位置に設けるので、曝気装置から吹き出す気
体量を少なくでき、効率よく被処理排水と微生物保持担
体12を連続した流動を循環させることができる。
The aeration devices 8 and 8 have circulation flow generating portions 7 and 7 at the bottoms of the first waste water treatment chamber 5 and the second waste water treatment chamber 6, respectively.
Since it is provided at a position opposed to, the amount of gas blown out from the aeration device can be reduced, and a continuous flow of the wastewater to be treated and the microorganism holding carrier 12 can be efficiently circulated.

【0030】次に、他の実施例を図5について説明す
る。
Next, another embodiment will be described with reference to FIG.

【0031】この実施例では、排水処理槽1は前記図1
の実施例と同じであるが、それぞれ異なる被処理水の原
水調節槽21,21にそれぞれ流入量調節弁23,23を有する
流入管22,22を介して排水処理槽1の第1の排水処理室
5及び第2の排水処理室6の流入口15,15にそれぞれ接
続する。
In this embodiment, the waste water treatment tank 1 is the same as that shown in FIG.
The first wastewater treatment of the wastewater treatment tank 1 through the inflow pipes 22, 22 having the inflow control valves 23, 23 in the raw water control tanks 21, 21 respectively different from each other. Connected to the inlets 15 and 15 of the chamber 5 and the second wastewater treatment chamber 6, respectively.

【0032】この実施例では、例えば、食品加工業など
被処理水の性質が異なる場合には、一方のBODの濃度
が高い被処理水と他方のBOD濃度が低い被処理水を第
1及び第2の排水処理室5,6にそれぞれ分離して流入
させるようにし、濃度が高い被処理水を処理する処理室
に対しては曝気調節弁10を調節して曝気量を増加させ、
または濃度が低い被処理水を処理する処理室に対して曝
気調節弁10,10を調節して曝気量を減らして処理しある
いは、被処理水の条件によって微生物保持担体12の量を
調節して被処理水の性質に合わせた処理条件で処理し、
流出室17に処理後の二種類の排水を合流することによ
り、この流出室17の上方中央部に設けられた一つの排出
口16から排出する。
In this embodiment, for example, when the properties of the water to be treated are different, such as in the food processing industry, one of the water to be treated having a high BOD concentration and the other one of the water to be treated having a low BOD concentration are first and second. Separately inflow into the two waste water treatment chambers 5 and 6, and increase the aeration amount by adjusting the aeration control valve 10 for the treatment chamber that processes the high-concentration water to be treated,
Alternatively, by adjusting the aeration control valves 10 and 10 for a treatment chamber for treating low-concentration treated water, the amount of aeration is reduced for treatment, or the amount of the microorganism-holding carrier 12 is adjusted according to the condition of the treated water. Treat with treatment conditions that match the properties of the water to be treated,
By combining the two kinds of treated wastewater with the outflow chamber 17, the wastewater is discharged from one discharge port 16 provided in the upper center of the outflow chamber 17.

【0033】さらに、他の実施例を図6について説明す
る。
Further, another embodiment will be described with reference to FIG.

【0034】この実施例では、排水処理槽1には第1の
排水処理室5と第2の排水処理室6と連通する流出室1
7,17とをそれぞれ仕切り、各流出室17,17の上部にそ
れぞれ排出口16,16が開口されている。また、被処理水
の原水調節槽21,21にそれぞれ流入量調節弁23,23を有
する流入管22,22を介して、排水処理槽1の第1の排水
処理室5と第2の排水処理室6の流入口15,15にそれぞ
れ接続する。
In this embodiment, the drainage treatment tank 1 has an outflow chamber 1 communicating with the first wastewater treatment chamber 5 and the second wastewater treatment chamber 6.
7 and 17 are partitioned from each other, and discharge ports 16 and 16 are opened at the upper portions of the outflow chambers 17 and 17, respectively. In addition, the first wastewater treatment chamber 5 and the second wastewater treatment chamber 5 of the wastewater treatment tank 1 are connected to the raw water control tanks 21 and 21 through the inflow pipes 22 and 22 having the inflow control valves 23 and 23, respectively. Connected to the inlets 15 and 15 of the chamber 6, respectively.

【0035】この実施例の構成でも、被処理水の性質が
異なる場合の処理に適し、また、処理された被処理水を
別々排出して次の処理を別々に行うこともできる。
The configuration of this embodiment is also suitable for treatment when the properties of the water to be treated are different, and the treated water to be treated can be discharged separately and the next treatment can be performed separately.

【0036】さらに、他の実施例の構成を図7に基づい
て説明する。
The structure of another embodiment will be described with reference to FIG.

【0037】図7は連続流動接触排水処理装置の処理槽
の縦断正面図で、前記図1の実施例と同一の構造部分は
同一の符号で示して具体的な説明を省略して異なる構成
部分について説明する。
FIG. 7 is a vertical sectional front view of the treatment tank of the continuous fluidized contact waste water treatment apparatus. The same structural parts as those of the embodiment of FIG. 1 are designated by the same reference numerals, and detailed description thereof will be omitted. Will be described.

【0038】この実施例では、排水処理槽1を縦断面略
卵形形状に形成したもので、縦断面に対して隔壁25によ
って左右対称に第1の排水処理室5aと第2の排水処理室
6aとに仕切る。この隔壁25は底部から上方に向って略V
字状に拡閉した形状とし、この隔壁25の上部を第1の排
水処理室5aと第2の排水処理室6a側にそれぞれ突出する
循環流起生部26,26として隔壁25と循環流起生部26,26
とを一体に形成する。
In this embodiment, the wastewater treatment tank 1 is formed in a substantially oval shape in the vertical cross section, and the first wastewater treatment chamber 5a and the second wastewater treatment chamber are symmetrical with respect to the vertical cross section by the partition wall 25.
Divide into 6a. The partition wall 25 is approximately V upward from the bottom.
The shape of the partition wall 25 is expanded and closed, and the upper part of the partition wall 25 is formed as the circulation flow generating portions 26, 26 projecting toward the first waste water treatment chamber 5a and the second waste water treatment chamber 6a, respectively. Ikube 26, 26
And are integrally formed.

【0039】そして、この循環流起生部26,26の下方に
位置して第1の排水処理室5aと第2の排水処理室6aとの
底部にそれぞれ曝気装置8,8をそれぞれ配設する。
Then, aeration devices 8 are respectively arranged at the bottoms of the first wastewater treatment chamber 5a and the second wastewater treatment chamber 6a located below the circulation flow generating portions 26, 26. .

【0040】この曝気装置8,8から吹き出した気体は
気泡となってV字状の隔壁25,25に沿って上昇して、上
部の循環流起生部26,26に当たり、第1の排水処理室5a
と第2の排水処理室6aの略円形状の内面壁27,27に沿っ
て排水処理室5a,6aの底部に循環することにより循環流
を生じる。
The gas blown out from the aeration devices 8 and 8 becomes bubbles and rises up along the V-shaped partition walls 25 and 25, hits the circulation flow generation parts 26 and 26 at the upper part, and undergoes the first wastewater treatment. Chamber 5a
And a circulation flow is generated by circulating the second wastewater treatment chamber 6a along the substantially circular inner walls 27, 27 to the bottoms of the wastewater treatment chambers 5a, 6a.

【0041】なお、前記実施例では、排水処理槽1は縦
断面略円形または卵形としたが、左右対称形状として縦
断面における外殻形状を円弧状に形成した楕円形状など
適宜形状とすることができる。
In the above embodiment, the wastewater treatment tank 1 has a substantially vertical cross section or an oval shape, but it may have an appropriate shape such as a bilaterally symmetrical shape such as an elliptical outer shell shape in the vertical cross section. You can

【0042】また、微生物保持担体12は処理する排水よ
りやや比重が大きい多孔質の材質を用いることにより、
曝気量を少くして流動化できる利点を有している。
The microorganism holding carrier 12 is made of a porous material having a specific gravity slightly higher than that of the wastewater to be treated,
It has the advantage that it can be fluidized by reducing the amount of aeration.

【0043】また、前記曝気装置8,8の送風ブロワー
は各曝気装置8,8ごとに設けることなく、インバータ
ーを利用して一個の送風ブロワー11とすることもでき
る。
Further, the blower blowers of the aeration devices 8 and 8 may not be provided for each of the aeration devices 8 and 8 but may be a single blower blower 11 using an inverter.

【0044】また、仕切板18の下部の流出孔19は微生物
保持担体12が流出しない小孔とすることもできる。
Further, the outflow hole 19 in the lower part of the partition plate 18 may be a small hole through which the microorganism holding carrier 12 does not flow out.

【0045】[0045]

【発明の効果】請求項1記載の発明によれば、縦断面略
円形の排水処理槽内において中心部に設けた隔壁により
仕切られた排水処理室を形成し、この隔壁の上端に循還
流起生部を形成し、微生物保持担体は各処理室の底部に
循環流起生部と対応して設けられた曝気装置から吹き出
した上昇の気泡によって、この循環流起生部と衝突して
連続的に循環状の水流を生じることにより、微生物と被
処理水中のBOD物質と垂直状に上昇した気泡中の酸素
とが接触して酸化、分解されるので連続的に高効率で浄
化することができる。
According to the first aspect of the present invention, a wastewater treatment chamber partitioned by a partition wall provided at the center is formed in a wastewater treatment tank having a substantially circular vertical section, and the circulation and recirculation occurs at the upper end of this partition wall. The microorganism holding carrier collides with the circulation flow generation portion by the rising bubbles blown from the aeration device provided at the bottom of each processing chamber corresponding to the circulation flow generation portion and continuously By generating a circulating water flow in the air, the microorganisms, the BOD substance in the water to be treated, and the oxygen in the bubbles that have risen vertically come into contact with each other to be oxidized and decomposed, so that continuous purification can be performed with high efficiency. .

【0046】また、排水処理槽は縦断面が略円形または
略楕円形に形成されているので、地下に埋設した状態で
土圧に耐えられ、地上設置ばかりでなく、地下設置型と
することもできる。
Also, since the wastewater treatment tank is formed in a substantially circular or elliptical vertical section, it can withstand earth pressure when buried underground and can be installed not only on the ground but also underground. it can.

【0047】請求項2記載の発明によれば、この排水処
理槽の内部に形成された二つの排水処理室の流入量を調
節可能としたので、被処理排水原水の条件に応じて各排
水処理室に流入される流入量を調節することにより、被
処理排水原水に応じた処理ができ、また、休日などの被
処理排水原水が減少したような場合、一方の排水処理室
のみで処理し、他方の排水処理室への流入を停止して曝
気装置の動力費などを節減できる。
According to the second aspect of the present invention, the inflow rates of the two wastewater treatment chambers formed inside the wastewater treatment tank can be adjusted. Therefore, each wastewater treatment can be performed according to the conditions of the raw water to be treated. By adjusting the inflow volume that flows into the room, it is possible to treat according to the raw wastewater to be treated, and when the raw wastewater to be treated has decreased, such as on holidays, treat it only in one of the wastewater treatment chambers. By stopping the inflow to the other wastewater treatment room, the power cost of the aeration device can be saved.

【0048】請求項3記載の発明によれば、例えば、食
品加工業用のような被処理排水原水の性質が異なる場合
に、BODの含有量が異なる二種類の被処理排水は別々
にそれぞれの排水処理室に流入させることができ、被処
理排水の性質に合わせた処理条件で処理できる。
According to the third aspect of the present invention, for example, when the raw water to be treated has different properties, such as those used in the food processing industry, the two types of treated wastewater having different BOD contents are treated separately. It can be made to flow into the wastewater treatment room and can be treated under treatment conditions that match the properties of the wastewater to be treated.

【0049】さらに、請求項4記載の発明によれば、微
生物保持担体がプラスチックあるいはその発泡体、また
は多孔質セラミック、またはペレット状活性炭、または
微生物を固定化したプラスチック、または表面を活性炭
で被覆したプラスチックからなるので、微生物保持担体
は高価の材質で作る必要がなく、処理室底部の曝気装置
で少量の気体を送気しても、この微生物保持担体は気泡
の上昇による高効率的に連続の循環状流動ができ、かつ
経済性が向上することができる。
Further, according to the invention of claim 4, the microorganism-holding carrier is plastic or its foam, or porous ceramic, or pelletized activated carbon, or plastic on which microorganisms are immobilized, or the surface is coated with activated carbon. Since it is made of plastic, the microbial carrier does not have to be made of an expensive material, and even if a small amount of gas is sent by the aeration device at the bottom of the processing chamber, the microbial carrier is highly efficient and continuous due to the rise of bubbles. Circular flow can be achieved, and economic efficiency can be improved.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明の一実施例を示す連続流動接触排水処理
装置の縦断正面図である。
FIG. 1 is a vertical sectional front view of a continuous fluidized contact wastewater treatment equipment showing one embodiment of the present invention.

【図2】同上連続流動接触排水処理装置の平面図であ
る。
FIG. 2 is a plan view of the continuous fluidized contact wastewater treatment device of the above.

【図3】同上連続流動接触排水処理装置の縦断側面図で
ある。
FIG. 3 is a vertical sectional side view of the continuous fluidized contact wastewater treatment device of the above.

【図4】同上連続流動接触排水処理装置の説明図であ
る。
FIG. 4 is an explanatory diagram of the continuous fluidized contact wastewater treatment device of the above.

【図5】本発明の他の実施例を示す連続流動接触排水処
理装置の説明図である。
FIG. 5 is an explanatory view of a continuous fluidized contact wastewater treatment equipment showing another embodiment of the present invention.

【図6】他の実施例を示す連続流動接触排水処理装置の
説明図である。
FIG. 6 is an explanatory view of a continuous fluidized contact wastewater treatment equipment showing another embodiment.

【図7】本発明の他の実施例を示す連続流動接触排水処
理装置の縦断正面図である。
FIG. 7 is a vertical cross-sectional front view of a continuous fluidized contact wastewater treatment equipment showing another embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1 排水処理槽 4,25 隔壁 5,5a 第1の排水処理室 6,6a 第2の排水処理室 7,26 循環流起生部 8 曝気装置 12 微生物保持担体 15 流入口 16 排出口 17 流出室 1 Wastewater treatment tank 4,25 Partition wall 5,5a First wastewater treatment chamber 6,6a Second wastewater treatment chamber 7,26 Circulation flow generation part 8 Aeration device 12 Microorganism retention carrier 15 Inlet 16 Outlet 17 Outlet chamber

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】 縦断面が略円形の排水処理槽を備え、こ
の処理槽の内部を縦断面に対し隔壁によって左右対称に
第1の排水処理室と第2の排水処理室とをそれぞれ仕切
り分割し、この第1の排水処理室と第2の排水処理室と
のそれぞれ一端側に流入口を形成すると共に、他端側に
流出室を形成し、 前記隔壁の上部に位置して前記第1の排水処理室と第2
の排水処理室との上部にそれぞれ突出する循環流起生部
を形成し、この各循環流起生部に対向して第1の排水処
理室と第2の排水処理室との底部から吹き出す気体によ
りこの第1の排水処理室と第2の排水処理室とを上昇す
る気泡が前記循環流起生部に衝突することにより両処理
室内の液体を循環させ、第1の排水処理室と第2の排水
処理室内に収納した微生物保持担体を両処理室内にそれ
ぞれ撹拌循環させて被処理排水中のBOD物質と気体中
の酸素を反応させる曝気装置を配設したことを特徴とす
る連続流動接触排水処理装置。
1. A wastewater treatment tank having a substantially circular vertical cross section, and the inside of this treatment tank is divided into a first wastewater treatment chamber and a second wastewater treatment chamber by a partition wall symmetrically with respect to the vertical cross section. The first wastewater treatment chamber and the second wastewater treatment chamber each have an inflow port formed at one end side thereof and an outflow chamber formed at the other end side thereof, and the first wastewater treatment chamber is located above the partition wall. Wastewater treatment room and second
Gas that blows out from the bottoms of the first wastewater treatment chamber and the second wastewater treatment chamber facing the respective circulation flow generation portions. As a result, bubbles rising in the first wastewater treatment chamber and the second wastewater treatment chamber collide with the circulation flow generating portion to circulate the liquid in both treatment chambers, thereby causing the first wastewater treatment chamber and the second wastewater treatment chamber to circulate. Continuous flow contact wastewater, characterized in that an aeration device for reacting the BOD substance in the wastewater to be treated with oxygen in the gas is disposed by agitating and circulating the microorganism-holding carrier stored in the wastewater treatment room Processing equipment.
【請求項2】 第1の排水処理室と第2の排水処理室と
の排水の流入量をそれぞれに調節可能としたことを特徴
とする請求項1記載の連続流動接触排水処理装置。
2. The continuous fluidized contact wastewater treatment equipment according to claim 1, wherein the inflow amounts of the wastewater into the first wastewater treatment chamber and the second wastewater treatment chamber can be adjusted respectively.
【請求項3】 第1の排水処理室と第2の排水処理室と
にそれぞれ異なる被処理排水原水を流入可能としたこと
を特徴とする請求項1または2記載の連続流動接触排水
処理装置。
3. The continuous fluidized contact wastewater treatment equipment according to claim 1 or 2, wherein different raw wastewater to be treated can flow into the first wastewater treatment chamber and the second wastewater treatment chamber, respectively.
【請求項4】 微生物保持担体はプラスチックあるいは
その発泡体、または多孔質セラミック、またはペレット
状活性炭、または微生物を固定化したプラスチック、ま
たは表面を活性炭で被覆したプラスチックからなること
を特徴とする請求項1ないし請求項3のいずれかに記載
の連続流動接触排水処理装置。
4. The microorganism-supporting carrier is made of plastic, foam thereof, porous ceramics, pellet-like activated carbon, plastic on which microorganisms are immobilized, or plastic whose surface is coated with activated carbon. The continuous fluidized contact wastewater treatment equipment according to any one of claims 1 to 3.
JP5320331A 1993-12-20 1993-12-20 Continuous fluidizing contact waste water treatment apparatus Pending JPH07171588A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5320331A JPH07171588A (en) 1993-12-20 1993-12-20 Continuous fluidizing contact waste water treatment apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5320331A JPH07171588A (en) 1993-12-20 1993-12-20 Continuous fluidizing contact waste water treatment apparatus

Publications (1)

Publication Number Publication Date
JPH07171588A true JPH07171588A (en) 1995-07-11

Family

ID=18120293

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5320331A Pending JPH07171588A (en) 1993-12-20 1993-12-20 Continuous fluidizing contact waste water treatment apparatus

Country Status (1)

Country Link
JP (1) JPH07171588A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20180060677A (en) * 2016-11-29 2018-06-07 성균관대학교산학협력단 Highly efficient water treatment system that recycles the escaping gas using its own pressure

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20180060677A (en) * 2016-11-29 2018-06-07 성균관대학교산학협력단 Highly efficient water treatment system that recycles the escaping gas using its own pressure

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