JPH0555162B2 - - Google Patents

Info

Publication number
JPH0555162B2
JPH0555162B2 JP59170903A JP17090384A JPH0555162B2 JP H0555162 B2 JPH0555162 B2 JP H0555162B2 JP 59170903 A JP59170903 A JP 59170903A JP 17090384 A JP17090384 A JP 17090384A JP H0555162 B2 JPH0555162 B2 JP H0555162B2
Authority
JP
Japan
Prior art keywords
wastewater
tank
water
pipe
treated
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
JP59170903A
Other languages
Japanese (ja)
Other versions
JPS6150610A (en
Inventor
Tooru Matsuoka
Minoru Takayasu
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP17090384A priority Critical patent/JPS6150610A/en
Publication of JPS6150610A publication Critical patent/JPS6150610A/en
Publication of JPH0555162B2 publication Critical patent/JPH0555162B2/ja
Granted legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5281Installations for water purification using chemical agents

Landscapes

  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は廃水処理装置に係り、特に種々の性状
の懸濁浮遊物を含む廃水を静置状態で固液分離方
式により処理する廃水処理装置に関する。
Detailed Description of the Invention (Industrial Application Field) The present invention relates to a wastewater treatment device, and particularly to a wastewater treatment device that treats wastewater containing suspended solids of various properties by a solid-liquid separation method in a stationary state. Regarding.

(従来技術の問題点) 従来廃水を簡便に処理する装置としては、比重
差を利用して沈澱池等で固体物を沈降分離するも
のまたはこれにバツフルやフイルタ等を組合わせ
たもの等種々の形式の装置が広く知られている。
しかし、被処理水が比較的粒径の小さな種々の懸
濁浮遊物を含む場合にはこのような従来の装置で
はその分離が必ずしも容易ではなかつた。さらに
懸濁浮遊物の種類に応じて種々の構成の装置を使
い分けなければならず、かつ実用上充分な処理効
果を挙げるためには装置が大規模化し設備や維持
コストが増大する場合が多い。
(Problems with the prior art) Conventionally, there are various types of devices that can easily treat wastewater, such as those that use the difference in specific gravity to settle and separate solids in a sedimentation tank or the like, or those that combine this with a bathtub, a filter, etc. This type of device is widely known.
However, when the water to be treated contains various suspended solids having relatively small particle sizes, it is not always easy to separate them using such conventional devices. Furthermore, it is necessary to use devices with various configurations depending on the type of suspended matter, and in order to obtain a practically sufficient treatment effect, the scale of the device is often increased, and the cost of equipment and maintenance increases.

(発明の目的) 本発明の目的はこのような従来技術の欠点を解
消し、種々の懸濁浮遊物を含む廃水を簡便な構造
により許容できるレベルまで効率的に処理するこ
とのできる廃水処理装置を提供することにある。
(Object of the Invention) The object of the present invention is to provide a wastewater treatment device that eliminates the drawbacks of the prior art and can efficiently treat wastewater containing various suspended solids to an acceptable level with a simple structure. Our goal is to provide the following.

(発明の構成) 前記目的を達成するための本発明の廃水処理装
置は微細な懸濁浮遊物を含む被処理水の導入口お
よび処理後の排水の溢流口を夫々上端部に有しか
つ被処理水から沈降、分離された懸濁浮遊物の排
出口を下端部に有する処理槽と、前記処理槽の内
部の上端部から下端部にわたつて垂設され槽の内
部を被処理水の沈降領域と該沈降領域に下端部付
近で連通する水流の反転上昇域とに仕切区分する
仕切筒と、前記仕切筒の内部に径方向の間〓をも
つてほぼ同心的に垂設され上端部が前記導入口に
接続され下端部が前記仕切筒の下端部より上方の
位置で前記懸濁浮遊物の排出口側に開口されかつ
週壁に多数の透孔を形成された沈降パイプとを備
え、前記沈降領域と前記反転上昇域とを仕切る前
記仕切筒の下端部に対して狭い連通間〓を介して
対向する前記処理槽の下端部の槽壁が上方に向け
て所定の角度で傾斜されており、前記処理槽の懸
濁浮遊物の排出口に排出端の高さを調節可能とし
た排出管を接続したことを特徴とする。
(Structure of the Invention) To achieve the above object, the wastewater treatment apparatus of the present invention has an inlet for treated water containing fine suspended solids and an overflow port for treated wastewater at the upper end thereof. A treatment tank has a discharge port for suspended matter that has been settled and separated from the water to be treated at the lower end, and a treatment tank that is vertically disposed from the upper end to the lower end of the inside of the treatment tank and is connected to the water to be treated. a partition tube that partitions into a settling region and a water flow reversal rising region that communicates with the settling region near the lower end; a settling pipe connected to the inlet, the lower end of which is opened toward the outlet of the suspended solids at a position above the lower end of the partition tube, and has a large number of through holes formed in the wall. , a tank wall at a lower end of the processing tank, which faces the lower end of the partition tube that partitions the settling region and the inversion rising region through a narrow communication gap, is inclined upward at a predetermined angle. The treatment tank is characterized in that a discharge pipe whose height can be adjusted is connected to the discharge port of the suspended solids in the treatment tank.

(発明の実施例) 前記本発明のさらに具体的な構成ならびにそれ
に基いて得られる作用効果を以下図面に示す実施
例に基いてさらに詳細に説明する。
(Embodiments of the Invention) More specific configurations of the present invention and the effects obtained based thereon will be explained in more detail below based on embodiments shown in the drawings.

第1図および第2図は夫々本発明に係る廃水処
理装置の一実施例の概要を示す上面図および縦断
面図である。
FIG. 1 and FIG. 2 are a top view and a vertical sectional view, respectively, showing an outline of an embodiment of a wastewater treatment apparatus according to the present invention.

図中、断面円形の竪形の円筒型の処理槽4は後
述するように上端部の導入口1から処理される廃
水を導入し、槽中で沈降、分離された廃水中の懸
濁浮遊物を下端部の排出口3から濃縮スラリの形
態として排出すると共に、処理された排水を上端
部の溢流口2から外部に放出するようになされて
いる。
In the figure, a vertical cylindrical treatment tank 4 with a circular cross section introduces wastewater to be treated from an inlet 1 at the upper end, as will be described later, and suspended suspended matter in the wastewater is sedimented and separated in the tank. is discharged in the form of concentrated slurry from a discharge port 3 at the lower end, and treated wastewater is discharged to the outside from an overflow port 2 at the upper end.

前記処理槽4の内部にはその上端部から下端部
にかけて断面円形の円筒型の仕切筒6をほぼ垂直
に垂設し処理槽4の内部を廃水の沈降領域5と処
理後の排水の反転上昇域7とに区分するようにな
されている。
Inside the treatment tank 4, a cylindrical partition tube 6 with a circular cross section is vertically installed from the upper end to the lower end, and the inside of the treatment tank 4 is divided into a sedimentation area 5 for wastewater and an inversion and rise area for wastewater after treatment. It is divided into Area 7.

前記仕切筒6の垂設下端部は前記処理槽4の下
端部の懸濁浮遊物の排出口3側に開口している。
この垂設下端部の開口縁部は処理槽4の下端部の
周壁に対して所定の間隙Dを介して対向させてあ
り、仕切筒6の内部に形成された沈降領域5を通
して下降する水流を間隙Dを通して反転上昇させ
仕切板6の外側の排水の反転上昇域7中を処理槽
4の上端部に向けて上昇させるようになされてい
る。
The lower end of the partition tube 6 is opened toward the discharge port 3 of the suspended solids at the lower end of the processing tank 4 .
The opening edge of this hanging lower end is opposed to the peripheral wall of the lower end of the processing tank 4 with a predetermined gap D therebetween, and allows the water flow to descend through the settling area 5 formed inside the partition tube 6. The wastewater is inverted and raised through the gap D, and is raised in the inverted and raised area 7 of the wastewater outside the partition plate 6 toward the upper end of the treatment tank 4.

ここで前記仕切筒6の垂設下端部に対して間隙
Dをもつて対向している処理槽4の周壁は上方に
向つて所定の角度で傾斜されている。
Here, the peripheral wall of the processing tank 4, which faces the vertical lower end of the partition tube 6 with a gap D therebetween, is inclined upward at a predetermined angle.

さらに、前記仕切筒6の内部にはこれも断面円
形の円筒化の沈降パイプ8を仕切筒に対して径方
向の間隙をもつて同心状に垂設し、その上端部に
前記廃水の導入口1を接続し、その下端部は前記
仕切筒6の下端部と同様にして懸濁浮遊物の排出
口3側に開口させてある。この沈降パイプ8の周
面には多数の透孔9,9,…を適宜な上下方向お
よび周方向のピツチで穿設して、そのパイプ内部
の流域を前記仕切筒6の内部に形成された沈降領
域5と流通させるようになされている。
Further, inside the partition tube 6, a cylindrical settling pipe 8 also having a circular cross section is vertically disposed concentrically with a radial gap with respect to the partition tube, and an inlet for the waste water is provided at the upper end of the tube. 1 is connected, and its lower end is opened to the suspended matter discharge port 3 side in the same way as the lower end of the partition tube 6. A large number of through holes 9, 9, . It is configured to communicate with the sedimentation area 5.

さらに、本発明の図示の実施例においては前記
処理槽4の下端部の濃縮スラリーの排出口3に対
して排出管10を接続し、処理槽4の側壁に沿つ
てほぼその上端部まで立上げてある。排出管10
の上方の排出端部10Aは可撓性の大きなプラス
チツク管等で形成され、これを屈曲することによ
つて処理槽4の水面に対する排出管上端部の相対
的な高さを調節できるようになされている。10
Bは排出管の支持部材である。
Furthermore, in the illustrated embodiment of the present invention, a discharge pipe 10 is connected to the concentrated slurry discharge port 3 at the lower end of the processing tank 4, and is raised along the side wall of the processing tank 4 almost to its upper end. There is. Discharge pipe 10
The upper discharge end 10A is formed of a large flexible plastic pipe or the like, and by bending this, the relative height of the upper end of the discharge pipe with respect to the water surface of the treatment tank 4 can be adjusted. ing. 10
B is a support member for the discharge pipe.

(作用および効果) 前記第1図および第2図に示す廃水処理装置で
懸濁浮遊物を含む廃水を処理する際には、廃水を
導入口1から処理槽4内の沈降パイプ8の上部に
徐々に注入する。処理の進行中には廃水から沈
降、分離された懸濁浮遊物が処理槽4の下端部の
排出口3付近に蓄積され必要に応じて排出管10
を通して排出される。一方処理後の排出は処理槽
4の水流の反転上昇域7の最上部に設けられた溢
流口2から連続的に引抜かれる。
(Functions and Effects) When treating wastewater containing suspended solids with the wastewater treatment apparatus shown in FIGS. Inject gradually. During the progress of the treatment, suspended solids that have settled and been separated from the wastewater are accumulated near the discharge port 3 at the lower end of the treatment tank 4, and are removed from the discharge pipe 10 as necessary.
is discharged through. On the other hand, the discharge after treatment is continuously drawn out from the overflow port 2 provided at the top of the water flow reversal and rise area 7 of the treatment tank 4.

ここで前記仕切筒6の沈降領域5中の廃水は沈
降パイプ8の上部から絶えず注入される廃水によ
つて徐々に下方に移動し、仕切筒6の垂設下端部
の周縁と処理槽4の下端部との間の間隙Dを通し
て流れの方向を反転し、仕切筒6の外部と処理槽
4との間の水流の上昇域7に入る。上昇域7に入
つた沈降パイプ8に連続的に注入される廃水の水
圧によつて上昇し、最上端部の溢流口2から処理
済の廃水として引抜かれる。
Here, the wastewater in the sedimentation area 5 of the partition tube 6 gradually moves downward due to the wastewater continuously injected from the upper part of the sedimentation pipe 8, and the periphery of the hanging lower end of the partition tube 6 and the treatment tank 4. The direction of the flow is reversed through the gap D with the lower end and enters the rising region 7 of the water flow between the outside of the partition tube 6 and the processing tank 4 . The wastewater that has entered the rising region 7 is raised by the water pressure of the wastewater continuously injected into the settling pipe 8, and is drawn out from the overflow port 2 at the top end as treated wastewater.

一方、この廃水中に含まれている懸濁浮遊物は
導入口1から沈降パイプ8の上部に注入される廃
水の下方への移動にともなつて沈降領域5中を下
方に運ばれるが、この場合、処理槽4の容量(本
実施例では約12cm3)を注入される廃水の量(たと
えば、200/分)に比較して十分に大きくして
おけば沈降領域5中の廃水の下降速度は極めて緩
やかになる。そして、特に沈降パイプ8に注入さ
れた廃水の中の大部分の流れがパイプ周壁に穿設
された透孔9を通して一旦仕切筒6との間の間隙
に水平方向に排出されてから筒内を降下する経路
をとるので、沈降領域5を降下する懸濁浮遊物は
全体として比較的長い流路を長時間にわたつて
徐々に下方に移動する。そして仕切筒6の下端部
に至ると、ほとんどの懸濁浮遊物が水から分離さ
れて排出口3の付近に沈積する。
On the other hand, the suspended solids contained in this wastewater are carried downward in the settling area 5 as the wastewater is injected from the inlet 1 into the upper part of the settling pipe 8 and moves downward. In this case, if the capacity of the treatment tank 4 (approximately 12 cm 3 in this example) is made sufficiently large compared to the amount of wastewater injected (e.g. 200/min), the rate of descent of the wastewater in the sedimentation area 5 can be reduced. becomes extremely gradual. In particular, most of the wastewater injected into the settling pipe 8 passes through a through hole 9 drilled in the peripheral wall of the pipe and is once discharged horizontally into the gap between it and the partition cylinder 6, and then flows into the cylinder. Since it takes a descending path, the suspended solids descending through the sedimentation area 5 gradually move downward over a long period of time through a relatively long flow path as a whole. When reaching the lower end of the partition tube 6, most of the suspended matter is separated from the water and deposited near the discharge port 3.

ここで粒径の小さな一部の懸濁浮遊物は仕切筒
6の垂設下端部で間隙Dを通して反転上昇する排
水にともなわれて浮上しようとするが、開口面積
の狭い間隙Dからより広い反転上昇域7に出る際
に浮遊懸濁物はほとんど運動エネルギを失ない、
大部分のものが処理槽4の下端部の傾斜面に沿つ
て再び排出口3に沈積する。その後、反転上昇域
7を排水と共に上昇する間にその中に含まれてい
る残余の懸濁浮遊物の相当量の部分がさらに沈降
し、上昇域7の最上端の溢流口2から引抜かれる
処理後の排水に残存する懸濁浮遊物はその粒径に
して約300メツシユより小さなもののみとなる。
本実施例においては前記装置仕様および処理条件
で、ss濃度約200ppmの廃水を連続的に処理した
結果、得られる処理後の排水のss濃度は約20ppm
に低下する。
Here, some of the suspended solids with small particle sizes try to float up along with the drainage that reverses upward through the gap D at the vertical lower end of the partition tube 6, but from the gap D with a narrow opening area, a larger part The floating suspended matter loses almost no kinetic energy when exiting the inversion rising region 7,
Most of the waste is deposited in the discharge port 3 along the slope of the lower end of the processing tank 4. Thereafter, while rising in the inversion rising area 7 along with the drainage water, a considerable portion of the remaining suspended solids contained therein further settles and is drawn out from the overflow port 2 at the top end of the rising area 7. The suspended solids remaining in the wastewater after treatment are only particles smaller than about 300 mesh in particle size.
In this example, as a result of continuously treating wastewater with an ss concentration of approximately 200 ppm using the equipment specifications and treatment conditions described above, the ss concentration of the resulting treated wastewater was approximately 20 ppm.
decreases to

一方、廃水から沈降、分離されて処理槽4の下
端部の排出口3に沈積した懸濁浮遊物は槽内の水
圧に押されて排出管10中を通つて上昇し、処理
槽4の水面の高さ付近に位置された排出端部10
Aから濃縮スラリーの形態として槽外に排出され
る。ここで、たとえば廃水処理作業中において排
出端部10Aの高さを処理槽4の水面より高くし
ておけばスラリは排出されず、また所望の時期に
この可撓性の排出端部10Aを下方に屈曲させて
その高さを水面以下に下げることにより管内の濃
厚なスラリが槽外に排出される。この場合、下方
の排出管10を支持部材10Bから取外して排出
端部10Aの高さを大幅に下げれば槽内の沈積物
が廃水と共に一挙に排出されて処理槽4内が簡単
に清掃される。
On the other hand, the suspended solids that have been sedimented and separated from the wastewater and deposited at the discharge port 3 at the lower end of the treatment tank 4 are pushed by the water pressure in the tank and rise through the discharge pipe 10, and rise to the water surface of the treatment tank 4. The discharge end 10 is located near the height of
It is discharged from A to the outside of the tank in the form of a concentrated slurry. For example, if the height of the discharge end 10A is set higher than the water surface of the treatment tank 4 during wastewater treatment work, the slurry will not be discharged, and at the desired time, the flexible discharge end 10A can be lowered. By bending the pipe to lower its height below the water surface, the thick slurry inside the pipe is discharged to the outside of the tank. In this case, if the lower discharge pipe 10 is removed from the support member 10B and the height of the discharge end 10A is significantly lowered, the deposits in the tank will be discharged at once together with the waste water, and the inside of the treatment tank 4 will be easily cleaned. .

このように本発明の実施例においては、処理槽
4に注入される廃水を仕切筒6によつて槽内に区
分して形成された沈降領域5を通して降下させた
後、仕切筒6の垂設下端部と処理槽4の下端部と
の間の狭い間隙Dを通して反転上昇域7の溢流口
2側に反転上昇させるようにしてあるので、廃水
中に含まれる懸濁浮遊物はこの廃水の沈降、上昇
の間に固液分離されて槽底に沈積する。
As described above, in the embodiment of the present invention, after the wastewater injected into the treatment tank 4 is lowered through the sedimentation area 5 which is divided and formed in the tank by the partition pipe 6, the vertical installation of the partition pipe 6 is performed. Since the wastewater is inverted and raised to the overflow port 2 side of the inversion and rise area 7 through the narrow gap D between the lower end and the lower end of the treatment tank 4, the suspended solids contained in the wastewater are removed from the wastewater. During settling and rising, solid and liquid are separated and deposited on the bottom of the tank.

そして特に本発明の実施例では前記仕切筒6の
沈降領域5中にさらに沈降パイプ8に設けてその
周壁に穿設された多数の透孔9を介して廃水の流
れを水平方向に変えて沈降領域5中に流出させる
ようにしてあるので、槽内での廃水の流路長が増
大すると共に流れが極めて緩かでかつ乱れのない
ものとする。したがつて、廃水中に含まれている
大部分の懸濁浮遊物を徐々に沈降、分離しながら
排出口3側に効率的に沈積させて廃水から分離す
ることができる。
Particularly, in the embodiment of the present invention, a settling pipe 8 is further provided in the settling area 5 of the partition tube 6, and the flow of the waste water is changed horizontally through a number of through holes 9 bored in the peripheral wall of the settling pipe 8. Since the waste water is allowed to flow out into the region 5, the flow path length of the waste water in the tank is increased, and the flow is extremely slow and undisturbed. Therefore, most of the suspended solids contained in the wastewater can be gradually settled and separated, efficiently deposited on the discharge port 3 side, and separated from the wastewater.

さらに本実施例では前記処理槽4の下端部の懸
濁浮遊物の排出口にサイフオン式の排出管10を
接続してあるので、沈積した固体物を極めて簡単
に槽外に排出回収することができる。すなわちこ
の排出管10の上端部の高さを処理槽内の水面よ
り幾分低くしておけば水圧によつて沈澱した固体
物を常時連続的に排出することができ、また固体
含有分が比較的少ない廃水の場合では必要な時だ
け排出管の高さを低くしてスラリを一時に排出さ
せることもできる。このような調節は排出管端部
10Aを可撓性の大きな材質のもので形成するこ
により容易に行なわれる。さらに、排出管10全
体を支持部10Bからはずして端部を大幅に引下
げれば槽内の沈積物を廃水と共に一挙に排出させ
ることができ槽の清掃および保守が極めて容易に
なる。
Furthermore, in this embodiment, a siphon type discharge pipe 10 is connected to the discharge port of the suspended solids at the lower end of the treatment tank 4, so that the settled solids can be extremely easily discharged and recovered from the tank. can. In other words, by setting the height of the upper end of the discharge pipe 10 to be somewhat lower than the water level in the treatment tank, the precipitated solids can be continuously discharged by water pressure, and the solid content can be compared. In the case of wastewater with a small amount of wastewater, the height of the discharge pipe can be lowered to discharge the slurry at once only when necessary. Such adjustment can be easily performed by forming the discharge pipe end 10A from a highly flexible material. Furthermore, if the entire discharge pipe 10 is removed from the support part 10B and the end is pulled down significantly, the deposits in the tank can be discharged all at once together with the waste water, making cleaning and maintenance of the tank extremely easy.

以上のように本発明の実施例は極めて簡単な構
造によつて廃水中の懸濁浮遊物を長時間の静置を
要することなく連続的に沈降、分離させることが
できる。さらにこの実施例においては、基本的に
はその処理のために何等の化学的ないしは生物化
学的手段や運転のための動力を必要とせず、した
がつて一旦設置したあとでは通常ほとんど保守、
調整を要することがない。
As described above, the embodiments of the present invention are capable of continuously settling and separating suspended substances in wastewater without requiring them to stand still for a long time using an extremely simple structure. Furthermore, this embodiment basically does not require any chemical or biochemical means for its treatment or power for operation, and therefore, once installed, it usually requires little maintenance.
No adjustment is required.

本実施例では約200ppmの廃水のss濃度をその
性状、種類にはかかわりなく約20ppmに低下させ
ることができかつ約300メツシユまでの浮遊懸濁
物をほとんど除くことができた。
In this example, the ss concentration of wastewater of about 200 ppm could be reduced to about 20 ppm regardless of its properties and types, and most of the suspended solids up to about 300 mesh could be removed.

しかし、本発明によればss濃度がさらに高い濃
厚廃水(たとえば、ss10000以上の畜産汚水等)
についても予じめこれを適宜に水で希釈した後に
前記処理槽に導入することによつて同様な固液分
離処理を行なうことができる。また廃水中に金属
スラツジ等が含まれていて凝集剤処理が必要な場
合にはかかる処理を施こされた後のフロツク水を
同様にして前記実施例の処理槽で処理することが
できる。
However, according to the present invention, concentrated wastewater with even higher ss concentration (for example, livestock sewage with ss10,000 or more)
A similar solid-liquid separation treatment can also be carried out by diluting this appropriately with water in advance and introducing it into the treatment tank. Furthermore, if the wastewater contains metal sludge or the like and requires flocculant treatment, the floc water after such treatment can be treated in the same manner as in the treatment tank of the above embodiment.

尚、前記実施例で処理された廃水は直接河川等
への放流を許容される程度のものであるが、本実
施例はこれを土砂等の除去を前提とする上水道処
理や微生物活性を利用した廃水処理の前処理装置
として用いると本来の処理装置の負荷を著しく軽
減させることができる。したがつて本発明は単な
る廃水の処理に限らず広く一般の水処理に用いら
れるいわゆる固液分離装置ないしはシツクナとし
て広範囲な用途を有する。
Although the wastewater treated in the above example is of a level that is acceptable for direct discharge into rivers, etc., this example uses water supply treatment that assumes the removal of sediment, etc. and microbial activity. When used as a pre-treatment device for wastewater treatment, the load on the original treatment device can be significantly reduced. Therefore, the present invention has a wide range of uses, not only in wastewater treatment but also as a so-called solid-liquid separator or syringe, which is widely used in general water treatment.

以上本発明を比較的小型でかつコンパクトな円
筒状の形状を有する一実施例について説明した
が、もとより本発明は用途に応じてその他の種々
の形態として実施することができる。たとえば、
前記処理槽は第1図および第2図に示すような円
筒状に限らず、断面方形の角柱状としてもよい。
この場合第1図における処理槽4あるいは必要に
よつては仕切筒6、沈降パイプ8等の断面を夫々
互いに同心的な方形の形状に変更するだけでよ
い。さらにまた、沈降パイプに穿設する透孔の形
状、大きさおよび配設ピツチならびに処理槽下端
部の間隙Dや傾斜角度等も必要に応じて種々の寸
法、形状に設計することができる。
Although the present invention has been described above with respect to an embodiment having a relatively small and compact cylindrical shape, the present invention can of course be implemented in various other forms depending on the application. for example,
The processing tank is not limited to the cylindrical shape as shown in FIGS. 1 and 2, but may be prismatic with a square cross section.
In this case, it is only necessary to change the cross sections of the processing tank 4 in FIG. 1 or, if necessary, the partition tube 6, settling pipe 8, etc., to concentric rectangular shapes. Furthermore, the shape, size, and pitch of the through-holes drilled in the settling pipe, as well as the gap D and inclination angle of the lower end of the processing tank, can be designed to have various dimensions and shapes as required.

第3図および第4図に比較的大容量の工場廃水
の処理に適した本発明の別の実施例を示す。
FIGS. 3 and 4 show another embodiment of the invention suitable for treating relatively large volumes of industrial wastewater.

第3図および第4図の実施例中に示す各部分の
中、前記第1図および第2図に対応する符号で示
したものは夫々前記実施例において説明したのと
同一の機能を有している。本実施例では、仕切筒
6と処理槽4との間に形成される水流の反転上昇
域が隔離板11によつて比較的面積の大きな捕集
域12および廃水取出域13に区分され捕集域1
2にはシユータ14が設けられている。
Among the parts shown in the embodiments of FIGS. 3 and 4, those indicated by the reference numerals corresponding to those in FIGS. 1 and 2 have the same functions as explained in the embodiments, respectively. ing. In this embodiment, the water flow reversal rising region formed between the partition tube 6 and the treatment tank 4 is divided by the separator 11 into a relatively large collection region 12 and a wastewater extraction region 13 for collection. Area 1
2 is provided with a shutter 14.

ここで導入された廃水を仕切筒6および沈降パ
イプ8等により処理し、かつ沈降、分離したスラ
リを取出す態様は前記第1図および第2図に示し
た実施例の場合と基本的には同一である。
The manner in which the introduced wastewater is treated by the partition tube 6 and the settling pipe 8, etc., and the sedimented and separated slurry is taken out is basically the same as in the embodiment shown in FIGS. 1 and 2. It is.

第3図および第4図の実施例ではほとんどの懸
濁浮遊物の分離後に間隙Dから反転上昇する廃水
はまず捕集域12の下方に導かれる。ここで廃水
中に含有されていた比重の小さな木屑および場合
によつては油類等が急速に浮上して捕集域12の
水面に集められシユータ14を通して槽外に排出
処理される。廃水はさらに徐々に上昇して廃水取
出域13に至り溢流口15から排出される。
In the embodiment of FIGS. 3 and 4, after most of the suspended solids have been separated, the waste water that reverses upward from the gap D is first directed below the collection zone 12. Here, wood chips with a low specific gravity and, in some cases, oil, etc. contained in the wastewater rapidly float to the surface, are collected on the water surface of the collection area 12, and are discharged to the outside of the tank through the shooter 14. The wastewater further gradually rises to reach the wastewater extraction area 13 and is discharged from the overflow port 15.

本実施例は廃水の処理量が大きく、殊に木屑や
油類等の比較的比重の小さな浮遊物を多量に含む
工場廃水の処理用途に適している。
This embodiment can treat a large amount of wastewater, and is particularly suitable for treating factory wastewater containing a large amount of floating matter with relatively low specific gravity such as wood chips and oils.

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

第1図は本発明の一実施例の上面図、第2図は
前記実施例の縦断面図、第3図は本発明の別の実
施例の上面図、第4図は前記実施例の縦断面図で
ある。 1……廃水の導入口、2……廃水の溢流口、3
……沈積物の排出口、4……処理槽、5……沈降
領域、6……仕切筒、7……水流の反転上昇域、
8……沈降パイプ、9……透孔、10……排出
管。
FIG. 1 is a top view of one embodiment of the present invention, FIG. 2 is a longitudinal sectional view of the embodiment, FIG. 3 is a top view of another embodiment of the invention, and FIG. 4 is a longitudinal sectional view of the embodiment. It is a front view. 1...Wastewater inlet, 2...Wastewater overflow port, 3
... Sediment discharge port, 4 ... Treatment tank, 5 ... Sedimentation region, 6 ... Partition tube, 7 ... Water flow reversal and rise region,
8...Settlement pipe, 9...Through hole, 10...Discharge pipe.

Claims (1)

【特許請求の範囲】[Claims] 1 微細な懸濁浮遊物を含む被処理水の導入口1
および処理後の排水の溢流口2を夫々上端部に有
しかつ被処理水から沈降、分離された懸濁浮遊物
の排出口3を下端部に有する処理槽4と、前記処
理槽4の内部の上端部から下端部にわたつて垂設
され槽4の内部を被処理水の沈降領域5と該沈降
領域5に下端部付近で連通する水流の反転上昇域
7とに仕切区分する仕切筒6と、前記仕切筒6の
内部に径方向の間〓をもつてほぼ同心的に垂設さ
れ上端部が前記導入口1に接続され下端部が前記
仕切筒6の下端部より上方の位置で前記懸濁浮遊
物の排出口3側に開口されかつ周壁に多数の透孔
9を形成された沈降パイプ8とを備え、前記沈降
領域5と前記反転上昇域7とを仕切る前記仕切筒
6の下端部に対して狭い連通間〓Dを介して対向
する前記処理槽4の下端部の槽壁が上方に向けて
所定の角度で傾斜されており、前記処理槽4の懸
濁浮遊物の排出口3に排出端10Aの高さを調節
可能とした排出管10を接続したことを特徴とす
る廃水処理装置。
1 Inlet port 1 for treated water containing fine suspended solids
and a treatment tank 4 having an overflow port 2 for treated wastewater at its upper end and a discharge port 3 for suspended matter settled and separated from the water to be treated at its lower end; A partition tube that is installed vertically from the upper end to the lower end of the tank 4 and partitions the inside of the tank 4 into a settling region 5 of the water to be treated and a water flow reversal rising region 7 that communicates with the settling region 5 near the lower end. 6, which are vertically disposed substantially concentrically with a radial gap inside the partition tube 6, have an upper end connected to the introduction port 1, and have a lower end located above the lower end of the partition tube 6. The partitioning pipe 6 is provided with a settling pipe 8 which is opened on the side of the suspended matter discharge port 3 and has a large number of through holes 9 formed in the peripheral wall, and partitions the settling region 5 and the inversion rising region 7. The tank wall at the lower end of the processing tank 4, which faces the lower end via a narrow communication gap D, is inclined upward at a predetermined angle, and the suspended matter in the processing tank 4 is discharged. A wastewater treatment device characterized in that an outlet 3 is connected to a discharge pipe 10 whose height can be adjusted at a discharge end 10A.
JP17090384A 1984-08-16 1984-08-16 Apparatus for treating waste water Granted JPS6150610A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP17090384A JPS6150610A (en) 1984-08-16 1984-08-16 Apparatus for treating waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP17090384A JPS6150610A (en) 1984-08-16 1984-08-16 Apparatus for treating waste water

Publications (2)

Publication Number Publication Date
JPS6150610A JPS6150610A (en) 1986-03-12
JPH0555162B2 true JPH0555162B2 (en) 1993-08-16

Family

ID=15913468

Family Applications (1)

Application Number Title Priority Date Filing Date
JP17090384A Granted JPS6150610A (en) 1984-08-16 1984-08-16 Apparatus for treating waste water

Country Status (1)

Country Link
JP (1) JPS6150610A (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0744984B1 (en) * 1994-02-16 1999-04-07 Baker Hughes Incorporated Separation of a suspension into its component parts
JP4765022B2 (en) * 2005-03-25 2011-09-07 株式会社西原環境 Solid-liquid separator
JP5812237B2 (en) * 2010-09-21 2015-11-11 井上 虎男 Precipitation device for sediment in water tank
US20140110333A1 (en) * 2011-04-12 2014-04-24 Richard Kibbee Solid from liquid separation apparatus

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4526055Y1 (en) * 1965-07-26 1970-10-12
JPS499765A (en) * 1972-05-27 1974-01-28
JPS575896B2 (en) * 1975-10-07 1982-02-02
JPS58183912A (en) * 1982-04-22 1983-10-27 Kawasaki Steel Corp Precipitation basin
JPS5926108A (en) * 1982-08-02 1984-02-10 Oji Paper Co Ltd Apparatus for concentrating slurry

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4726569U (en) * 1971-04-20 1972-11-25
JPS6326169Y2 (en) * 1980-06-12 1988-07-15

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4526055Y1 (en) * 1965-07-26 1970-10-12
JPS499765A (en) * 1972-05-27 1974-01-28
JPS575896B2 (en) * 1975-10-07 1982-02-02
JPS58183912A (en) * 1982-04-22 1983-10-27 Kawasaki Steel Corp Precipitation basin
JPS5926108A (en) * 1982-08-02 1984-02-10 Oji Paper Co Ltd Apparatus for concentrating slurry

Also Published As

Publication number Publication date
JPS6150610A (en) 1986-03-12

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