JPH06165901A - Sewage treatment device - Google Patents

Sewage treatment device

Info

Publication number
JPH06165901A
JPH06165901A JP4341023A JP34102392A JPH06165901A JP H06165901 A JPH06165901 A JP H06165901A JP 4341023 A JP4341023 A JP 4341023A JP 34102392 A JP34102392 A JP 34102392A JP H06165901 A JPH06165901 A JP H06165901A
Authority
JP
Japan
Prior art keywords
water
endless
water channel
inner cylinder
tank
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.)
Granted
Application number
JP4341023A
Other languages
Japanese (ja)
Other versions
JP3278216B2 (en
Inventor
Masakazu Kuroda
正和 黒田
Megumi Yuzawa
恩 湯沢
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.)
Yamato Setubi Construction Co Ltd
Original Assignee
Yamato Setubi Construction Co Ltd
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 Yamato Setubi Construction Co Ltd filed Critical Yamato Setubi Construction Co Ltd
Priority to JP34102392A priority Critical patent/JP3278216B2/en
Publication of JPH06165901A publication Critical patent/JPH06165901A/en
Application granted granted Critical
Publication of JP3278216B2 publication Critical patent/JP3278216B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related 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 provide a sewage treatment device which can efficiently settle and separate the solids in sewage. CONSTITUTION:An inside cylinder 11 is vertically provided in a treatment tank 10 by parting the bottom end of the cylinder from the bottom of the tank to form an endless water path. The front end of a water feed pipe 13 plunged into the water of the endless water path is provided with two branch ejection ports 14a, 14b which supply raw water to the endless water path in diametrically opposite direction to whirl the water. A baffle plate 16 which crosses the endless water path is oscillatably hung down in the position diametrically opposite from the position within the endless water path where the water feed pipe is provided.

Description

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

【0001】[0001]

【産業上の利用分野】この発明は、間欠的に排出される
汚水の量や水質が短時間で変化するような有機性の生活
排水、産業排水などの前段処理に適した汚水処理装置に
関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a wastewater treatment apparatus suitable for pretreatment of organic domestic wastewater, industrial wastewater, etc., in which the amount and quality of intermittently discharged wastewater change in a short time.

【0002】[0002]

【従来の技術】本特許出願人の一人、大和設備工事株式
会社は、特開昭63−158191号公報により処理槽
の内部に、下端を槽底から上に離し、上端が水面上に突
出した内筒を縦設して処理槽の内周と、内筒の外周との
間に無端水路を形成し、該無端水路中に原水を給水管で
供給し、処理水を内筒の内部から処理槽の外に排水管で
抜き出すようにした汚水処理装置を提案した。この汚水
処理装置は、固液の沈降分離装置であって、無端水路の
水中に突入した給水管の先端に、原水を該無端水路に沿
った一方向の旋回流とする横向きの噴出口を設け、原水
中の粗大固形物は無端水路の下方の槽底に、微細なSS
は内筒の内部下方の槽底に沈降させる。
2. Description of the Related Art One of the applicants of this patent, Yamato Equipment Co., Ltd., discloses that a lower end of a processing tank is separated from a bottom of the processing tank and an upper end thereof is projected above the water surface according to Japanese Patent Laid-Open No. 63-158191. An inner cylinder is installed vertically to form an endless water channel between the inner circumference of the treatment tank and the outer circumference of the inner cylinder, and raw water is supplied to the endless water channel by a water supply pipe to treat the treated water from the inside of the inner cylinder. We proposed a sewage treatment device that drains out of the tank with a drainage pipe. This sewage treatment apparatus is a solid-liquid settling / separating apparatus, and is provided with a lateral jet outlet at the tip of a water supply pipe that rushes into the water of an endless water channel to turn raw water into a unidirectional swirling flow along the endless water channel. , Coarse solids in raw water are fine SS on the bottom of the endless water channel.
Is allowed to settle on the bottom of the tank below the inner cylinder.

【0003】[0003]

【発明が解決しようとする課題】上記先行提案では、給
水管の先端の横向きの噴出口から無端水路に噴出した原
水の旋回流は重力と、水路壁面との摩擦によってしか運
動エネルギを低減しない。このため槽内は旋回流により
攪乱され、槽内の液が静止するには時間を要し、その間
に槽底に沈積した固形物を舞い上げたり、槽底に固形物
を一様に沈降させることが十分できない。更に、高い処
理水質を得るため生物学的処理を行うには、内筒から処
理槽の外に抜き出した処理水を、別個に設置した生物処
理槽に導いて処理しなければならず、設置スペース、コ
ストアップ等の問題が生じる。
According to the above-mentioned prior proposal, the swirling flow of the raw water ejected from the lateral ejection port at the tip of the water supply pipe into the endless channel reduces kinetic energy only by gravity and friction between the channel wall surface. Therefore, the inside of the tank is disturbed by the swirling flow, and it takes time for the liquid in the tank to stand still, during which the solid matter deposited on the bottom of the tank is lifted up or the solid matter is settled uniformly on the bottom of the tank. Can't do enough. Furthermore, in order to perform biological treatment in order to obtain high treated water quality, the treated water extracted from the inner cylinder to the outside of the treatment tank must be introduced to a separately installed biological treatment tank for treatment, and the installation space However, problems such as cost increase occur.

【0004】[0004]

【課題を解決するための手段】請求項1は、旋回流の運
動エネルギを急速に低減して前述の問題点を解消した沈
降分離装置としての汚水処理装置に関するもので、処理
槽の内部に、下端を槽底から上に離し、上端が水面上に
突出した内筒を縦設して処理槽の内周と、内筒の外周と
の間に無端水路を形成し、該無端水路中に原水を給水管
で供給し、処理水を内筒の内部から処理槽の外に排水管
で抜き出すようにした汚水処理装置において、前記無端
水路の水中に突入した給水管の先端に、原水を該無端水
路に正反対の方向に供給して旋回させる2つの分岐噴出
口を設けると共に、前記無端水路内の、給水管が設けら
れた位置とは正反対の位置に該無端水路を横切る邪魔板
を設けたことを特徴とする。又、請求項2は、沈降分離
と、嫌気的生物処理を1つの槽で行うようにした汚水処
理装置に関するもので、処理槽の内部に、下端を槽底か
ら上に離し、上端が水面上に突出した内筒を縦設して処
理槽の内周と、内筒の外周との間に無端水路を形成し、
該無端水路中に原水を給水管で供給し、処理水を内筒の
内部から処理槽の外に排水管で抜き出すようにした汚水
処理装置において、前記無端水路の水中に突入した給水
管の先端に、原水を該無端水路に正反対の方向に供給し
て旋回させる2つの分岐噴出口を設け、前記無端水路内
の、給水管が設けられた位置とは正反対の位置に該無端
水路を横切る邪魔板を設けると共に、微生物を付着した
坦体群を内筒の内部に密集して支持し、且つ該坦体群を
内筒の下端から垂れ下げたことを特徴とする。請求項
1、請求項2のいずれかの汚水処理装置においても、前
記無端水路内の、給水管とは正反対の位置に設けられた
邪魔板は、該無端水路を横切って揺動可能に吊下げるこ
とが好ましい。
According to a first aspect of the present invention, there is provided a sewage treatment apparatus as a sedimentation separation apparatus in which the kinetic energy of a swirling flow is rapidly reduced to solve the above-mentioned problems. An inner cylinder with the lower end separated from the tank bottom and the upper end protruding above the water surface is vertically installed to form an endless water channel between the inner circumference of the treatment tank and the outer circumference of the inner cylinder. In the wastewater treatment device in which the treated water is supplied from the inside of the inner cylinder to the outside of the treatment tank by the drainage pipe, the raw water is supplied to the end of the water supply pipe protruding into the water of the endless water channel. Two branch jets are provided in the water channel to supply and rotate in opposite directions, and a baffle plate that traverses the endless water channel is provided at a position in the endless water channel which is exactly opposite to the position where the water supply pipe is provided. Is characterized by. Further, claim 2 relates to a sewage treatment apparatus in which settling separation and anaerobic biological treatment are performed in one tank, wherein the lower end is separated from the tank bottom and the upper end is above the water surface inside the treatment tank. An inner cylinder protruding vertically is formed to form an endless water channel between the inner circumference of the treatment tank and the outer circumference of the inner cylinder.
In a sewage treatment apparatus in which raw water is supplied to the endless water channel by a water supply pipe, and treated water is drawn out of a treatment tank from the inside of an inner cylinder by a drain pipe, the tip of the water supply pipe protruding into the water of the endless water channel. Is provided with two branch spouts for supplying raw water to the endless water channel in opposite directions to swirl the same, and an obstacle that crosses the endless water channel at a position in the endless water channel opposite to the position where the water supply pipe is provided. It is characterized in that a plate is provided, the carrier group to which microorganisms are adhered is densely supported inside the inner cylinder, and the carrier group is hung from the lower end of the inner cylinder. In the sewage treatment apparatus according to any one of claims 1 and 2, the baffle plate provided in the position opposite to the water supply pipe in the endless water channel is swingably suspended across the endless water channel. It is preferable.

【0005】[0005]

【実施例】図1,2は請求項1の汚水処理装置の一実施
例、図3,4は請求項2の汚水処理装置の一実施例を示
す。この各実施例において、10は底を有する処理槽、
11は処理槽の内部に縦設されて下端を槽底10´から
上に離し、上端が水面上に突出した内筒であり、処理槽
10の内周と、内筒11の外周との間には無端水路12
が形成されている。13は上記無端水路12中に原水
(汚水)を供給する給水管、15は内筒11の内部から
処理水を処理槽10の外に抜き出す排水管であり、内筒
内の処理水は排水管にオーバフローして流入し、内筒1
1の内部、及び無端水路12内の水位Lは一定に保たれ
る。内筒11の下端は、槽底10´から水位のほゞ40
〜50%に位置する。
1 and 2 show an embodiment of a sewage treatment apparatus according to claim 1, and FIGS. 3 and 4 show an embodiment of a sewage treatment apparatus according to claim 2. In each of these examples, 10 is a processing tank having a bottom,
Reference numeral 11 denotes an inner cylinder that is vertically installed inside the processing tank, has its lower end separated from the tank bottom 10 ′ and has its upper end protruding above the water surface, and is located between the inner circumference of the processing tank 10 and the outer circumference of the inner cylinder 11. There are 12 endless waterways
Are formed. Reference numeral 13 is a water supply pipe for supplying raw water (dirty water) into the endless water channel 12, 15 is a drain pipe for extracting treated water from the inside of the inner cylinder 11 to the outside of the treatment tank 10, and the treated water in the inner cylinder is a drain pipe. Overflows and flows into the inner cylinder 1
The water level L inside 1 and in the endless water channel 12 is kept constant. The lower end of the inner cylinder 11 has a water level of about 40 degrees from the tank bottom 10 '.
Located at ~ 50%.

【0006】処理槽10、及び内筒11は図示の実施例
では円筒形で、同心円状の配置になっているため、無端
水路12は環状であるが、処理槽及び/或いは内筒は多
角筒形、楕円筒形であってもよいと共に、処理槽に対す
る内筒の配置はクローズドな無端水路12が形成される
のであれば同心でなくてもよい。又、処理槽10の直径
と深さ、内筒11の直径と長さは処理すべき汚水の排出
量、滞流時間等に応じ適切に定める。
In the illustrated embodiment, the treatment tank 10 and the inner cylinder 11 are cylindrical, and are arranged concentrically, so that the endless water channel 12 is annular, but the treatment tank and / or the inner cylinder is a polygonal cylinder. The shape of the inner cylinder with respect to the treatment tank may not be concentric as long as the closed endless water channel 12 is formed. Further, the diameter and depth of the treatment tank 10 and the diameter and length of the inner cylinder 11 are appropriately determined according to the discharge amount of sewage to be treated, stagnant time and the like.

【0007】無端水路12の水中に突入した給水管13
の先端部はT形になっていて2つの分岐噴出口14a,
14bを備えている。両噴出口14a,14bは内筒1
1に対して接線方向の反対向きになっているため、給水
管13で間欠的に供給される原水は分岐噴出口14a,
14bでほゞ二分され、各分岐噴出口14a,14bか
ら矢印で示すよう無端水路12中に反対向きに噴出して
正反対の方向の二つの旋回流A,Bを生じる(図2,
4,5)。
A water supply pipe 13 protruding into the water of the endless water channel 12
Has a T-shaped tip and has two branch jets 14a,
14b. Both spouts 14a and 14b are the inner cylinder 1
1, the raw water intermittently supplied by the water supply pipe 13 is tangentially opposite to
It is roughly divided into two by 14b, and jets in opposite directions from the respective branch jets 14a, 14b into the endless water channel 12 to generate two swirling flows A, B in opposite directions (Fig. 2,
4, 5).

【0008】無端水路12内の、給水管13が設けられ
た位置とは正反対の位置、この実施例では処理槽10、
内筒11が円筒形なので、給水管13の位置と直径方向
に対向した位置に無端水路12を横切る邪魔板16が設
けてある。この邪魔板16の上端は無端水路12中の水
位Lから上に突出する。
A position in the endless water channel 12 which is opposite to the position where the water supply pipe 13 is provided, in this embodiment, the treatment tank 10,
Since the inner cylinder 11 is cylindrical, a baffle plate 16 that crosses the endless water channel 12 is provided at a position diametrically opposed to the position of the water supply pipe 13. The upper end of the baffle plate 16 projects upward from the water level L in the endless water channel 12.

【0009】前述したように給水管13で間欠的に供給
される原水は該管13の下端に設けた反対向きの2つの
分岐噴出口14a,14bでほゞ二分され、各分岐噴出
口14a,14bから反対の向きに噴出して無端水路中
に正反対の方向の2つの旋回流A,Bを生じる。この旋
回流A,Bは図5に示すように、給水管13とは正反対
の位置で無端水路12中を横切る前記邪魔板16の各面
に衝突し、衝突によって折返す反転流A´,B´にな
る。邪魔板16は、このように旋回流A,Bを反対の向
きの反転流A´,B´に変化させるためのものであるか
ら、その下端16´の位置ないしは邪魔板の下向き長さ
は無端水路中で下向きに拡がりながらやって来る旋回流
A,Bが確実に衝突できるように定める。
As described above, the raw water intermittently supplied through the water supply pipe 13 is roughly bisected by the two opposite branch jets 14a and 14b provided at the lower end of the pipe 13, and each branch jet 14a, Two swirling flows A and B in opposite directions are generated in the endless water channel by ejecting from 14b in opposite directions. As shown in FIG. 5, the swirling flows A and B collide with the respective surfaces of the baffle plate 16 that traverses the endless water channel 12 at a position opposite to the water supply pipe 13, and the reversing flows A ′ and B return by the collision. become. Since the baffle plate 16 is for changing the swirling flows A and B into the reverse flows A ′ and B ′ in the opposite directions, the position of the lower end 16 ′ or the downward length of the baffle plate is endless. The swirling flows A and B, which spread downward in the waterway, are determined so that they can collide reliably.

【0010】この発明による汚水処理装置では、給水管
13の先端に設けた2つの分岐噴出口14a,14bが
無端水路12中に供給する汚水をほゞ二分し、水路中に
正反対の向きの2つの旋回流A,Bを生じさせる。この
二分された各旋回流A,Bの運動エネルギは、二分され
ない1つの旋回流の運動エネルギよりも小である。従っ
て、2つの旋回流A,Bの運動エネルギは無端水路の壁
面との摩擦によって低減する割合が大きい。
In the sewage treatment apparatus according to the present invention, the two branch jets 14a, 14b provided at the tip of the water supply pipe 13 roughly divide the sewage supplied into the endless water channel 12 into the water channel in opposite directions. Two swirl flows A and B are generated. The kinetic energy of each of the divided swirling flows A and B is smaller than the kinetic energy of one undivided swirling flow. Therefore, the kinetic energy of the two swirling flows A and B is largely reduced by the friction with the wall surface of the endless water channel.

【0011】そして、この2つの旋回流A,Bは運動エ
ネルギを低減しながら邪魔板16に衝突し、反転流A
´,B´になって折返すが、邪魔板との衝突によって運
動エネルギは大きく低減し、反転流A´,B´の運動エ
ネルギは大幅に減衰する。以上の結果、無端水路12に
間欠的に汚水が供給され、2つの旋回流、反転流が無端
水路中に生じるが、水路中の液は速やかに静置し、槽底
に沈積する固形物(堆積汚泥)の再浮上、舞い上げが起
きない。そして、2つの旋回流と反転流とによって汚水
中の質量の大きな固形物は無端水路12の下方の槽底1
0´に一様に沈積し、偏積することがない。
The two swirling flows A and B collide with the baffle plate 16 while reducing the kinetic energy, and the reverse flow A
The kinetic energy is greatly reduced by the collision with the baffle plate, and the kinetic energy of the reversal flows A'and B'is greatly attenuated. As a result, sewage is intermittently supplied to the endless water channel 12, and two swirling flows and reverse flows are generated in the endless water channel, but the liquid in the water channel is quickly left to stand and solid matter deposited on the tank bottom ( Re-floating of sedimented sludge) does not occur. Then, due to the two swirling flows and the reversing flow, the solid matter having a large mass in the wastewater is discharged from the bottom 1 of the tank 1 below the endless water channel 12.
It uniformly deposits at 0'and does not accumulate.

【0012】無端水路12中で旋回流A,Bを反対の向
きの反転流A´,B´に変化させる前記邪魔板16は、
給水管13とは正反対の位置に固定して設けてもよい
が、無端水路の水中に振子式に揺動可能に吊下げて設け
ることが後述の理由で好ましい。図示の各実施例では排
水管15に邪魔板を吊下げる役目を兼ねさせるため、無
端水路上の邪魔板16の吊下げ位置に排水管15を横断
させ、邪魔板の上端に取付けた支持具17を排水管に嵌
めて邪魔板を揺動可能に吊下げてあるが、これに限定さ
れず排水管以外の横軸を無端水路上に横断して固定し、
これに邪魔板を揺動可能に吊下げてもよいし、又、無端
水路上に横断して固定した支持体に邪魔板をヒンジで揺
動可能に吊り下げてもよい。
The baffle plate 16 for changing the swirling flows A and B into the reverse flows A'and B'in the opposite directions in the endless water channel 12,
It may be fixedly provided at a position opposite to the water supply pipe 13, but it is preferable to be provided so as to be swingable like a pendulum in the water of the endless water channel for the reason described later. In the illustrated embodiments, since the drain pipe 15 also serves to suspend the baffle plate, the drain pipe 15 is traversed to the position where the baffle plate 16 is suspended on the endless water channel, and the support 17 attached to the upper end of the baffle plate 17 is provided. Is fitted to the drain pipe to suspend the baffle so that it can swing, but not limited to this, the horizontal axis other than the drain pipe is fixed across the endless water channel,
The baffle plate may be oscillatedly hung on this, or the baffle plate may be oscillatedly hung by a hinge on a support fixed transversely on the endless water channel.

【0013】前述したように給水管13の先端の2つの
分岐噴出口14a,14bは、無端水路12中に汚水を
ほゞ二分して供給し、水路中に正反対の向きの2つの旋
回流A,Bを生じさせるが、分岐噴出口14aと、14
bから流出する汚水の流量には差があるため、2つの旋
回流AとBは非対称な不等流となる。この傾向は浴槽排
水など一時的に大量の汚水が給水管13から無端水路1
2に流入する場合に顕著に表れる。そして、このように
非対称な不等流の旋回流AとBが邪魔板16に衝突した
後の反転流A´,B´は、邪魔板が固定であると対称な
反転流にならず、運動量のバランスを保つため槽底への
下向流を生じ、槽内の流れが攪乱される。しかし、上述
したように邪魔板16を揺動可能に吊下げると、非対称
な不等流の旋回流A,Bの運動量に釣合う角度まで邪魔
板16は振られるので、邪魔板に衝突した後の反転流A
´とB´とはほゞ完全な対称の流れになって運動量のバ
ランスが保たれ、槽底への下向流は抑止されて槽内の流
れの制動効果は高まり、攪乱は生じない。
As described above, the two branch jets 14a and 14b at the tip of the water supply pipe 13 roughly divide the sewage into the endless water channel 12 and supply it to the water channel. , B, but with the branch jets 14a, 14
Since there is a difference in the flow rate of the sewage flowing out of b, the two swirling flows A and B are asymmetrical non-uniform flows. This tendency is that a large amount of sewage, such as drainage from a bathtub, is temporarily discharged from the water supply pipe 13 to the endless water channel 1.
It appears remarkably when flowing into 2. Then, the reversal flows A ′ and B ′ after the asymmetrical non-uniform swirling flows A and B collide with the baffle plate 16 do not become symmetrical reversal flows when the baffle plate is fixed, and the momentum In order to maintain the balance of the above, a downward flow to the bottom of the tank is generated and the flow in the tank is disturbed. However, if the baffle plate 16 is swingably suspended as described above, the baffle plate 16 is swung up to an angle that balances the momentum of the asymmetrical non-uniform swirling flows A and B. Reverse flow A
′ And B ′ are almost completely symmetrical flows to maintain the balance of momentum, the downward flow to the bottom of the tank is suppressed, the damping effect of the flow in the tank is enhanced, and no disturbance occurs.

【0014】以上の結果、無端水路12に間欠的に汚水
が供給され、2つの旋回流、反転流が生じるが、水路中
の液は速やかに静置し、槽底に沈積する固形物(堆積汚
泥)の再浮上、舞い上げが起きない。そして、2つの旋
回流と反転流とによって汚水中の質量の大きな固形物は
無端水路12の下方の槽底10´に一様に沈積し、偏積
することがない。そして、図1,2の汚水処理装置の場
合、内筒11の内部の水面近くの上澄み処理水が排水管
15にオーバフローして入り、外に抜き出されるにつ
れ、内筒の外の液が内筒の内部に下から入り、こゝで液
中に懸濁するSSはスラッジブランケット状に内筒の下
方の槽底10´上に沈降堆積する。
As a result of the above, sewage is intermittently supplied to the endless water channel 12 to generate two swirling flows and a reverse flow, but the liquid in the water channel is quickly allowed to stand still, and solid matter deposited on the bottom of the tank (accumulation) Re-emergence of sludge) does not occur. Then, due to the two swirling flows and the reversing flow, the solid matter having a large mass in the wastewater is uniformly deposited on the tank bottom 10 ′ below the endless water channel 12 and is not accumulated. Then, in the case of the wastewater treatment device of FIGS. 1 and 2, as the supernatant treated water near the water surface inside the inner cylinder 11 overflows into the drain pipe 15 and is drawn out, the liquid outside the inner cylinder is The SS that enters the inside of the cylinder from below and is suspended in the liquid is settled and deposited on the tank bottom 10 'below the inner cylinder in the form of a sludge blanket.

【0015】図3,4の実施例の汚水処理装置の場合
は、嫌気性菌や、好気性菌などの微生物を付着した坦体
18の多数を筒体11の内部に密集して支持し、内筒の
下端から処理槽の槽底までか、槽底と内筒の下端との中
間位置まで垂れ下げる。坦体18は軽量で柔軟性があ
り、且つ菌体固着性の良い不織布のようなものでも、プ
ラスチック等でできた菌体固着性の良い固形のものでも
よい。密集した坦体18の上端と下端に金網状の支持板
19を取付け、上端を取付けた支持板を内筒11の内部
に固定し、下端に取付けた支持板で坦体を上下方向にピ
ンと張り、且つ坦体が個々に水流で動くのを防止するこ
とが好ましい。
In the case of the sewage treatment apparatus of the embodiments shown in FIGS. 3 and 4, a large number of carriers 18 to which microorganisms such as anaerobic bacteria and aerobic bacteria are adhered are densely supported inside the cylindrical body 11, It hangs from the lower end of the inner cylinder to the bottom of the processing tank, or to an intermediate position between the bottom and the lower end of the inner cylinder. The carrier 18 may be a non-woven fabric that is lightweight and flexible and has good bacterial cell adhesion, or may be a solid material made of plastic or the like having good bacterial cell adhesion. Wire mesh-like support plates 19 are attached to the upper and lower ends of the densely packed carriers 18, the support plates with the upper ends are fixed inside the inner cylinder 11, and the carriers are vertically tensioned with the support plates attached to the lower ends. And, it is preferred to prevent the carriers from moving individually in a water stream.

【0016】この汚水処理装置でも、前述したように無
端水路12に間欠的に供給される汚水によって水路内に
は2つの旋回流、反転流が生じるが、水路中の液は速や
かに静置し、槽底に沈積する固形物(堆積汚泥)の再浮
上、舞い上げが起きない。そして、2つの旋回流と反転
流とによって汚水中の質量の大きな固形物は無端水路1
2の下方の槽底10´に一様に沈積し、偏積することが
ない。そして、内筒11の内部の水面近くの上澄み処理
水が排水管15にオーバフローして入り、外に抜き出さ
れるにつれ、内筒の外の液は内筒の下端から下がる密集
した坦体18の間を通って内筒の内部に下から入って水
面へ上昇し、その上昇速度は坦体18の流動抵抗により
低減されるため、質量の小さい微細な固形物の掃流を抑
止すると共に、液の滞留時間を増加させ、その際に坦体
に付着した微生物と接触し液中のBOD成分などは生物
学的に処理され、排水管15で抜き出される処理水のB
OD濃度は低下する。
In this sewage treatment apparatus also, as described above, two swirling flows and a reverse flow are generated in the water channel due to the sewage intermittently supplied to the endless water channel 12, but the liquid in the water channel is promptly left to stand still. , Re-floatation of solid matter (sludge sludge) deposited on the bottom of the tank and soaring does not occur. Then, due to the two swirling flows and the reversing flow, the solid matter having a large mass in the wastewater is converted into the endless water channel 1.
2 is uniformly deposited on the bottom 10 ′ of the tank 2 and does not accumulate. Then, as the supernatant-treated water near the water surface inside the inner cylinder 11 overflows into the drain pipe 15 and is drawn out, the liquid outside the inner cylinder falls from the lower end of the inner cylinder to the dense carrier 18 As it enters the inside of the inner cylinder from below through the space and rises to the water surface, and its rising speed is reduced by the flow resistance of the carrier 18, it suppresses the sweeping of fine solids with a small mass and the liquid. B of the treated water which is brought into contact with the microorganisms adhering to the carrier at that time and biologically treats the BOD component in the liquid, and is discharged from the drain pipe 15
The OD concentration decreases.

【0017】又、無端水路12での固形物の沈降分離が
効率よく行われるため、坦体18に付着した微生物に対
する固形物の過負荷状態が防止されるので微生物による
生物学的処理も効率的に行われる。
Further, since the sedimentation and separation of the solid matter in the endless water channel 12 is efficiently performed, the overloaded state of the solid matter with respect to the microorganisms adhering to the carrier 18 is prevented, and the biological treatment by the microorganisms is also efficient. To be done.

【0018】更に、坦体18に付着した微生物は増殖す
ると坦体から一部剥離して槽底10´に沈降し、槽底に
堆積している固形物の汚泥を生物学的に処理する。
Further, when the microorganisms attached to the carrier 18 grow, they partly separate from the carrier and settle on the bottom 10 'of the tank, and biologically treat the solid sludge accumulated on the bottom of the tank.

【0019】従来型の沈殿槽(従来装置と記す。)と、
図3,4に示した汚水処理装置(実施装置と記す。)を
用い3月から8月の同一期間で、A家庭の合併汚水(雑
排水と水洗トイレ排水)を処理した比較実験結果を図6
に示す。同一の槽容量に対して、実施装置の処理水のB
OD濃度は、従来装置の処理水のBOD濃度の半分近く
まで低下して居り、実施装置の処理能力が極めて高いこ
とが実証された。又、処理水のBOD濃度の変動幅も実
施装置では従来装置に比して、極めて小さい。図7に、
上記比較実験例について、処理水のSS濃度を示す。S
S濃度も、BOD濃度と同様に実施装置の処理能力の方
が、従来装置よりも極めて高い。
A conventional settling tank (hereinafter referred to as a conventional apparatus),
Figure 3 shows the results of a comparative experiment in which the combined sewage (miscellaneous drainage and flush toilet drainage) of household A was treated in the same period from March to August using the sewage treatment equipment (referred to as implementation equipment) shown in Figs. 6
Shown in. For the same tank capacity, B
The OD concentration decreased to almost half of the BOD concentration of the treated water of the conventional apparatus, demonstrating that the treatment capacity of the embodying apparatus was extremely high. Further, the fluctuation range of the BOD concentration of the treated water is extremely small in the embodying apparatus as compared with the conventional apparatus. In Figure 7,
The SS concentration of treated water is shown for the above comparative experiment example. S
Similarly to the BOD concentration, the S concentration has a significantly higher processing capacity of the embodying apparatus than that of the conventional apparatus.

【0020】図8に、従来型の嫌気濾床槽(従来装置と
記す。)と、図3,4に示した汚水処理装置(実施装
置)を用い、ほゞ同一期間、同一家族構成のB家庭の合
併汚水を処理した比較実験結果を示す。実施装置で処理
した処理水のBODは、従来装置に比して極めて安定し
ている。又、従来装置は嫌気濾床が2室構成になってい
るのに対し、実施装置は単一槽であるため槽容量は小さ
く、設置にスペースをとらない。この比較実験の際の処
理水のSS濃度を図9に示す。実施装置のSS濃度は、
従来装置に較べて低いことに加えて、SS濃度の変動幅
が著しく小さい。特に経過日数100日以降では、従来
装置のSS濃度は上昇傾向にあること、又、第1室に比
して第2室が高くなっていることから第1室では目詰り
が生じていることが伺えるのに反し、実施装置でのSS
濃度は極めて安定している。
FIG. 8 shows a conventional type anaerobic filter bed tank (referred to as a conventional device) and a sewage treatment device (implementing device) shown in FIGS. The result of the comparative experiment which treated combined domestic wastewater is shown. The BOD of the treated water treated by the embodying device is extremely stable as compared with the conventional device. Further, in the conventional apparatus, the anaerobic filter bed has a two-chamber structure, whereas the apparatus for carrying out the present invention has a single tank, so the tank capacity is small, and therefore no space is required for installation. The SS concentration of treated water in this comparative experiment is shown in FIG. The SS concentration of the implementing device is
In addition to being lower than conventional devices, the fluctuation range of SS concentration is extremely small. In particular, after 100 days have passed, the SS concentration of the conventional apparatus tends to increase, and since the second chamber is higher than the first chamber, clogging occurs in the first chamber. Contrary to what you can see, SS at the implementing device
The concentration is extremely stable.

【0021】浴槽排水が一時に大量に流入した場合に付
いて、図3,4の汚水処理装置(実施装置と記す。)、
従来型沈殿装置、及び従来型嫌気濾床槽からの処理水の
BOD濃度と、SS濃度を表1に示す。実施装置の値
は、従来型の2つの装置のいずれかの値よりも極めて低
く、実施装置の処理能力が高いことが実証された。
When a large amount of drainage from the bath tub flows in at one time, the sewage treatment apparatus shown in FIGS.
Table 1 shows the BOD concentration and the SS concentration of the treated water from the conventional settling device and the conventional anaerobic filter bed tank. The value of the practitioner was significantly lower than that of either of the two conventional devices, demonstrating the high throughput of the practitioner.

【表1】 [Table 1]

【0022】[0022]

【発明の効果】請求項1の汚水処理装置によって汚水中
の固形物の沈降分離を極めて効率的に行うことができ
る。このため、この汚水処理装置を家庭、事務所、ホテ
ル、公民館等の比較的に小規模で、非定常的に排水され
る有機性汚水の浄化施設の前段に使用することで、後段
の処理装置の固形物、SSによる負荷を大幅に軽減で
き、最終処理水の水質の向上に寄与する。
According to the sewage treatment apparatus of the first aspect, sedimentation and separation of solid matter in sewage can be performed very efficiently. Therefore, by using this sewage treatment device in a relatively small scale such as homes, offices, hotels, public halls, etc. in the front stage of a purification facility for organic sewage that is discharged unsteady, The solid load and the load of SS can be greatly reduced, contributing to the improvement of the quality of the final treated water.

【0023】又、請求項2の汚水処理装置によって単一
の処理槽で効率的な沈降分離と、微生物による生物学的
処理とを行うことができる。従って、この汚水処理装置
を家庭、事務所、ホテル、公民館等の比較的に小規模
で、非定常的に排水される有機性汚水の浄化施設の前段
に使用することで、後段の処理装置の固形物、SSによ
る負荷を大幅に軽減できると共に、脱窒、脱燐等の処理
性能を向上し、最終処理水の水質の向上に著しく寄与す
る。
The sewage treatment apparatus according to the second aspect enables efficient sedimentation and separation and biological treatment with microorganisms in a single treatment tank. Therefore, by using this sewage treatment equipment in a relatively small scale such as homes, offices, hotels, public halls, etc. in front of a purification facility for organic sewage discharged unsteadily, It can significantly reduce the load of solid matter and SS, improve the treatment performance such as denitrification and dephosphorization, and significantly contribute to the improvement of the water quality of the final treated water.

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

【図1】請求項1の汚水処理装置の一実施例の縦断面図
である。
FIG. 1 is a vertical cross-sectional view of an embodiment of the sewage treatment apparatus according to claim 1.

【図2】図1の平面図である。FIG. 2 is a plan view of FIG.

【図3】請求項2の汚水処理装置の一実施例の縦断面図
である。
FIG. 3 is a vertical cross-sectional view of an embodiment of the sewage treatment apparatus according to claim 2.

【図4】図3の平面図である。FIG. 4 is a plan view of FIG.

【図5】図1,図3の汚水処理装置の沈降分離作用を示
す模式図である。
FIG. 5 is a schematic diagram showing a sedimentation separation action of the wastewater treatment device of FIGS. 1 and 3.

【図6】従来型の沈殿分離槽と、本発明の汚水処理装置
とで処理した処理水のBOD濃度を示す比較図表であ
る。
FIG. 6 is a comparative chart showing the BOD concentration of treated water treated by the conventional sedimentation separation tank and the sewage treatment apparatus of the present invention.

【図7】従来型の沈殿分離槽と、本発明の汚水処理装置
とで処理した処理水のSS濃度を示す比較図表である。
FIG. 7 is a comparative chart showing the SS concentration of treated water treated by the conventional sedimentation separation tank and the sewage treatment apparatus of the present invention.

【図8】従来型の2床式嫌気濾床槽と、本発明の汚水処
理装置とで処理した処理水のBOD濃度を示す比較図表
である。
FIG. 8 is a comparative chart showing the BOD concentration of treated water treated by the conventional two-bed type anaerobic filter bed tank and the sewage treatment apparatus of the present invention.

【図9】従来型の2床式嫌気濾床槽と、本発明の汚水処
理装置とで処理した処理水のSS濃度を示す比較図表で
ある。
FIG. 9 is a comparative chart showing SS concentrations of treated water treated by the conventional two-bed type anaerobic filter bed tank and the sewage treatment apparatus of the present invention.

【符号の説明】[Explanation of symbols]

10 処理槽 10´ 槽底 11 内筒 12 無端水路 13 給水管 14a 分岐噴出口 14b 分岐噴出口 15 排水管 16 邪魔板 17 支持具 18 微生物の坦体 19 支持板 A 旋回流 B 旋回流 A´ 反転流 B´ 反転流 10 treatment tank 10 'tank bottom 11 inner cylinder 12 endless water channel 13 water supply pipe 14a branch jet 14b branch jet 15 drain pipe 16 baffle plate 17 support 18 microorganism carrier 19 support plate A swirling flow B swirling flow A' inversion Flow B'reverse flow

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 処理槽の内部に、下端を槽底から上に離
し、上端が水面上に突出した内筒を縦設して処理槽の内
周と、内筒の外周との間に無端水路を形成し、該無端水
路中に原水を給水管で供給し、処理水を内筒の内部から
処理槽の外に排水管で抜き出すようにした汚水処理装置
において、 前記無端水路の水中に突入した給水管の先端に、原水を
該無端水路に正反対の方向に供給して旋回させる2つの
分岐噴出口を設けると共に、前記無端水路内の、給水管
が設けられた位置とは正反対の位置に該無端水路を横切
る邪魔板を設けたことを特徴とする汚水処理装置。
1. An inner cylinder having a lower end separated from the tank bottom and an upper end projecting above the water surface is vertically installed inside the treatment tank to provide an endless structure between the inner circumference of the treatment tank and the outer circumference of the inner cylinder. In a sewage treatment apparatus that forms a water channel, supplies raw water into the endless water channel with a water supply pipe, and drains the treated water from the inside of the inner cylinder to the outside of the treatment tank with a drain pipe. At the tip of the water supply pipe, two branch jets for supplying raw water to the endless water channel in the opposite directions to swirl are provided, and at the position in the endless water channel opposite to the position where the water supply pipe is provided. A sewage treatment apparatus comprising a baffle plate that traverses the endless water channel.
【請求項2】 処理槽の内部に、下端を槽底から上に離
し、上端が水面上に突出した内筒を縦設して処理槽の内
周と、内筒の外周との間に無端水路を形成し、該無端水
路中に原水を給水管で供給し、処理水を内筒の内部から
処理槽の外に排水管で抜き出すようにした汚水処理装置
において、 前記無端水路の水中に突入した給水管の先端に、原水を
該無端水路に正反対の方向に供給して旋回させる2つの
分岐噴出口を設け、前記無端水路内の、給水管が設けら
れた位置とは正反対の位置に該無端水路を横切る邪魔板
を設けると共に、微生物を付着した坦体群を内筒の内部
に密集して支持し、且つ該坦体群を内筒の下端から垂れ
下げたことを特徴とする汚水処理装置。
2. An inner cylinder having a lower end separated from the tank bottom and an upper end projecting above the water surface is vertically installed inside the treatment tank to provide an endless structure between the inner circumference of the treatment tank and the outer circumference of the inner cylinder. In a sewage treatment apparatus that forms a water channel, supplies raw water into the endless water channel with a water supply pipe, and drains the treated water from the inside of the inner cylinder to the outside of the treatment tank with a drain pipe. At the tip of the water supply pipe, two branch jets for supplying raw water to the endless water channel in the opposite directions to swirl are provided, and in the endless water channel, a position opposite to the position where the water supply pipe is provided is provided. A sewage treatment characterized by providing a baffle that traverses an endless water channel, densely supporting a carrier group to which microorganisms are attached inside an inner cylinder, and suspending the carrier group from the lower end of the inner cylinder. apparatus.
【請求項3】 請求項1、請求項2のどれか1項に記載
の汚水処理装置において、前記無端水路内の、給水管と
は正反対の位置に設けられた邪魔板は、該無端水路を横
切って揺動可能に吊下げられていることを特徴とする汚
水処理装置。
3. The sewage treatment apparatus according to claim 1, wherein the baffle plate provided in the endless water channel at a position directly opposite to the water supply pipe serves to connect the endless water channel. A sewage treatment device characterized in that it is swingably suspended across.
JP34102392A 1992-11-30 1992-11-30 Sewage treatment equipment Expired - Fee Related JP3278216B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP34102392A JP3278216B2 (en) 1992-11-30 1992-11-30 Sewage treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP34102392A JP3278216B2 (en) 1992-11-30 1992-11-30 Sewage treatment equipment

Publications (2)

Publication Number Publication Date
JPH06165901A true JPH06165901A (en) 1994-06-14
JP3278216B2 JP3278216B2 (en) 2002-04-30

Family

ID=18342510

Family Applications (1)

Application Number Title Priority Date Filing Date
JP34102392A Expired - Fee Related JP3278216B2 (en) 1992-11-30 1992-11-30 Sewage treatment equipment

Country Status (1)

Country Link
JP (1) JP3278216B2 (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20020041691A (en) * 2000-11-28 2002-06-03 홍성욱 Cyclone sludge separator and electrolytic water treatment system having the same
KR100382810B1 (en) * 2002-03-22 2003-05-09 Global Technology Dt Inc Settling tank with improved structure
CN105401646A (en) * 2015-12-09 2016-03-16 武汉圣禹排水系统有限公司 Initial rain cyclone separation well
CN113461280A (en) * 2021-08-19 2021-10-01 河南佳诺威木业有限公司 Industrial sewage treatment device

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20020041691A (en) * 2000-11-28 2002-06-03 홍성욱 Cyclone sludge separator and electrolytic water treatment system having the same
KR100382810B1 (en) * 2002-03-22 2003-05-09 Global Technology Dt Inc Settling tank with improved structure
CN105401646A (en) * 2015-12-09 2016-03-16 武汉圣禹排水系统有限公司 Initial rain cyclone separation well
CN113461280A (en) * 2021-08-19 2021-10-01 河南佳诺威木业有限公司 Industrial sewage treatment device

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Publication number Publication date
JP3278216B2 (en) 2002-04-30

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