JPH04250802A - Vertical type deep layer precipitation tank - Google Patents
Vertical type deep layer precipitation tankInfo
- Publication number
- JPH04250802A JPH04250802A JP1035391A JP1035391A JPH04250802A JP H04250802 A JPH04250802 A JP H04250802A JP 1035391 A JP1035391 A JP 1035391A JP 1035391 A JP1035391 A JP 1035391A JP H04250802 A JPH04250802 A JP H04250802A
- Authority
- JP
- Japan
- Prior art keywords
- materials
- section
- inflow
- string
- strip
- 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
Links
- 238000001556 precipitation Methods 0.000 title abstract description 6
- 239000000463 material Substances 0.000 claims abstract description 37
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 16
- 239000000835 fiber Substances 0.000 claims abstract description 8
- 238000004062 sedimentation Methods 0.000 claims description 27
- 230000033001 locomotion Effects 0.000 abstract description 4
- 238000006243 chemical reaction Methods 0.000 abstract description 3
- 230000010355 oscillation Effects 0.000 abstract description 2
- 235000014676 Phragmites communis Nutrition 0.000 abstract 3
- 210000004081 cilia Anatomy 0.000 abstract 2
- 230000001133 acceleration Effects 0.000 abstract 1
- 239000011148 porous material Substances 0.000 abstract 1
- 230000000694 effects Effects 0.000 description 11
- 238000010586 diagram Methods 0.000 description 7
- 239000010802 sludge Substances 0.000 description 6
- 238000002474 experimental method Methods 0.000 description 4
- 239000007788 liquid Substances 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 239000000243 solution Substances 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 230000001886 ciliary effect Effects 0.000 description 2
- 238000002347 injection Methods 0.000 description 2
- 239000007924 injection Substances 0.000 description 2
- 239000010865 sewage Substances 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 238000012935 Averaging Methods 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
- 239000008399 tap water Substances 0.000 description 1
- 235000020679 tap water Nutrition 0.000 description 1
Abstract
Description
【0001】0001
【産業上の利用分野】本発明は、汚水(工業排水等を含
む)を沈澱処理する縦型深層沈澱槽、すなわち原水を流
入する流入部と処理水を流出させる流出部との間の距離
に比べて深さがはるかに深い(例えば30m以上)沈澱
槽に関する。なお、本発明で言う沈澱槽はいわゆる沈澱
池も含む概念とする。[Industrial Application Field] The present invention relates to a vertical deep sedimentation tank for sedimentation treatment of sewage (including industrial wastewater, etc.), that is, the distance between the inlet where raw water flows in and the outlet where treated water flows out. It relates to a sedimentation tank that is much deeper (for example, 30 m or more) compared to the above. Note that the sedimentation tank referred to in the present invention is a concept that also includes a so-called sedimentation tank.
【0002】0002
【従来の技術】特開昭61−157310号公報に記載
されている超深層沈澱槽は、縦長円筒状の槽本体内に、
原液導入側が下り傾斜に形成された複数の傾斜板からな
る固液分離部材を設け、またこの固液分離部材より原液
導入側に多孔整流板を配置し、該多孔整流板で整流され
た原液中の汚泥を傾斜板に衝突させて沈降させるもので
ある。[Prior Art] The ultra-deep sedimentation tank described in Japanese Patent Application Laid-Open No. 157310/1980 has a vertically long cylindrical tank body with
A solid-liquid separation member consisting of a plurality of inclined plates with the undiluted solution introduction side sloped downward is provided, and a porous rectifier plate is arranged on the undiluted solution introduction side of the solid-liquid separation member, and the undiluted solution is rectified by the porous rectifier plate. The sludge collides with the inclined plate and settles.
【0003】0003
【発明が解決しようとする課題】しかし、これによると
、傾斜板に汚泥が付着してその上に堆積してしまうとか
、傾斜板により上昇流が生じて汚泥の沈降が抑制され、
沈澱効果が悪いとか、固液分離部材の清掃・交換が面倒
である等の問題がある。[Problems to be Solved by the Invention] However, according to this, sludge adheres to the inclined plate and accumulates thereon, or the inclined plate creates an upward flow that suppresses the settling of sludge.
There are problems such as poor precipitation effect and troublesome cleaning and replacement of the solid-liquid separation member.
【0004】本発明の目的は、単純な構造であるにも拘
らず沈澱効果が非常に良好でかつ保守も容易な縦型深層
沈澱槽を提供することにある。[0004] An object of the present invention is to provide a vertical deep sedimentation tank which has a very good sedimentation effect and is easy to maintain despite its simple structure.
【0005】[0005]
【課題を解決するための手段】本発明による縦型深層沈
澱槽は、多数の孔を設けた縦長の多孔整流板を流入部側
と流出部側にそれぞれ配置し、また複数本の長い紐状材
又は棒状材を、水平流と交差する方向に所定の間隔をお
いて平行に垂下して簾状とし、これを、流入側多孔整流
板と流出側多孔整流板との間において水平流の方向に前
後所定の間隔をおいて複数段配置したものである。無数
の繊維ループを有する紐状材を使用し、その複数本を揺
動可能に垂下して簾状にすると良い。[Means for Solving the Problems] The vertical deep sedimentation tank according to the present invention has vertically elongated porous rectifying plates each having a large number of holes arranged on the inlet side and the outlet side, and also has a plurality of long string-like straightening plates. Materials or rod-shaped materials are suspended in parallel at a predetermined interval in the direction intersecting the horizontal flow to form a blind, and this is placed between the inlet side porous rectifier plate and the outlet side porous rectifier plate in the direction of the horizontal flow. A plurality of stages are arranged at predetermined intervals in the front and back. It is preferable to use a string-like material having countless fiber loops, and to hang a plurality of strings so as to be able to swing to form a curtain-like shape.
【0006】[0006]
【作用】沈澱槽の深さが深くしかもその流入側と流出側
に多孔整流板が設けられているため、原水は沈澱槽内を
微流速で流入部から流出部へと流れる。流入側の多孔整
流板の孔を通った水平流は、簾状をなす第1番目の複数
本の紐状材又は棒状材により抵抗を受けながら、平行に
垂下するその紐状材又は棒状材の間を通り抜けた後、同
様に第2番目の紐状材又は棒状材の間、次に第3番目、
第4番目と順次通り抜け、最後に流出側の多孔整流板の
孔を通って流出する。この場合、水平流は微流速である
ため、複数本の紐状材又は棒状材がそれらの間に垂直な
間隙を平行に形成しているので、沈澱作用を水平流の方
向に多段に受けることになり、浮遊物質の沈降は益々助
長される。[Operation] Because the sedimentation tank is deep and has porous rectifying plates on the inflow and outflow sides, raw water flows through the sedimentation tank from the inflow part to the outflow part at a small flow rate. The horizontal flow passing through the holes of the porous rectifying plate on the inflow side is resisted by the first plurality of strings or rods forming a curtain shape, and the horizontal flow flows through the strings or rods hanging in parallel. After passing through the space, similarly between the second string or bar, then the third,
It passes through the fourth and fourth holes in order, and finally flows out through the holes in the porous rectifier plate on the outflow side. In this case, since the horizontal flow has a small flow velocity, multiple string-like materials or rod-like materials form vertical gaps between them in parallel, so that the sedimentation action is applied in multiple stages in the direction of the horizontal flow. This will further promote the settling of suspended solids.
【0007】従って、上記のような相乗作用により沈澱
効果が非常に良く、本発明によると、互いに独立した複
数の沈澱部を水平方向に多段に並設し、それに処理水を
順次微流速で移し変えて繰り返し沈澱させるのと同様の
効果が得られ、水面積を極大に増大させ、その結果、小
敷地面積内で水面積負荷の軽減と、沈澱池数を増したと
同様の効果が得られる。すなわち、浮遊物の沈澱効果を
損なわずに沈澱池の敷地面積の縮小が可能となる。また
、複数本の紐状材又は棒状材は各段ごとに簾状になって
いるため、単に吊り下げ、また引き上げるだけで簡単に
交換でき、しかもその簾状のまま強制的に揺動又は振動
させるだけで、付着した浮遊物質を容易に落とすことが
できる。[0007] Therefore, due to the synergistic action as described above, the settling effect is very good, and according to the present invention, a plurality of mutually independent settling sections are arranged in parallel in multiple stages in the horizontal direction, and the treated water is sequentially transferred thereto at a small flow rate. The same effect as repeated sedimentation can be obtained, and the water area can be maximized, resulting in a reduction in the water area load within a small site area and the same effect as increasing the number of sedimentation tanks. In other words, it is possible to reduce the site area of the sedimentation pond without impairing the sedimentation effect of suspended matter. In addition, since the multiple string-like materials or rod-like materials are shaped like blinds at each stage, they can be easily replaced by simply hanging or pulling them up, and they can be forcibly swung or vibrated while maintaining the blind shape. You can easily remove adhering suspended substances by simply letting it dry.
【0008】無数の繊維ループを有する紐状材の複数本
を揺動可能に垂下して簾状にした場合には、各紐状材自
体が自由に揺動し易いと共に、摩擦作用などにより浮遊
物質の水平流速を減衰させ、その沈澱を促進する。[0008] When a plurality of string-like materials having innumerable fiber loops are hung swingably to form a blind, each string-like material itself is easy to swing freely and also floats due to frictional action. Attenuates the horizontal flow velocity of the material and promotes its precipitation.
【0009】[0009]
【実施例】以下、本発明の実施例について説明する。図
1から図3は角型にした場合の例で、槽本体1は縦長角
筒状になっている。この槽本体1内の前側に、多数の孔
2を設けた縦長の流入側多孔整流板3、後側に同じく多
数の孔4を設けた縦長の流出側多孔整流板5が垂直に配
置され、槽本体1の前壁6と流入側多孔整流板2との間
に流入部7、後壁8と流出側多孔整流板5との間に流出
部9がそれぞれ形成されている。槽本体1の底部10は
、図の例では前側部分が流入側より流出側へ向かって下
向きに傾斜しているが、水平でも良い。[Examples] Examples of the present invention will be described below. FIGS. 1 to 3 show examples in which the tank is square, and the tank body 1 is in the shape of a vertically long square tube. On the front side of this tank body 1, a vertically elongated inflow side porous current plate 3 provided with a large number of holes 2, and a vertically elongated outflow side multihole current plate 5 provided with the same large number of holes 4 on the rear side are arranged vertically. An inflow portion 7 is formed between the front wall 6 of the tank body 1 and the inflow side porous current plate 2, and an outflow portion 9 is formed between the rear wall 8 and the outflow side porous current plate 5. In the illustrated example, the front portion of the bottom portion 10 of the tank body 1 is inclined downward from the inflow side to the outflow side, but it may be horizontal.
【0010】流入側多孔整流板2と流出側多孔整流板5
との間には、複数の簾状体11が前後に所定の間隔をお
いて槽本体1の左右壁12,13間に前後多段に吊持さ
れている。各簾状体11は、多数本の長い紐状材14を
水平な支持棒15に左右に所定の間隔をおいて揺動自在
に懸吊したもので、槽本体1に対し個々に着脱可能にな
っている。簾状体11相互の間隔は例えば約10cm、
各簾状体11における紐状材13の間隔は例えば約3c
mである。紐状材14としては、無数の繊維ループを形
成ししかも螺旋状に捻じって伸縮性をもたせた公知の紐
状濾材を用いると良い。Inflow side porous current plate 2 and outflow side porous current plate 5
Between the left and right walls 12 and 13 of the tank body 1, a plurality of screen-like bodies 11 are suspended in multiple stages in the front and rear at predetermined intervals in the front and rear. Each screen-like body 11 has a large number of long string-like members 14 suspended from horizontal support rods 15 at a predetermined interval so as to be swingable, and can be attached to and detached from the tank body 1 individually. It has become. The distance between the blinds 11 is, for example, about 10 cm,
The distance between the strings 13 in each screen 11 is, for example, about 3c.
It is m. As the string-like material 14, it is preferable to use a known string-like filter material that has countless fiber loops and is twisted spirally to provide elasticity.
【0011】上記のような構成において、流入部7に原
水(汚水)を流入しながら処理水を流出部9から流出(
例えば越流)させると、流入部7に流入した原水は、流
入側多孔整流板3の多数の孔2を通ることにより整流さ
れ、流入部7から流出部9側へ流れる。この場合、槽本
体1が深いこと、流入側と流出側にそれぞれ多孔整流板
3,5が配置されていることにより、微流速で流れる。In the above configuration, while raw water (sewage) flows into the inflow section 7, treated water flows out from the outflow section 9 (
For example, when the flow is overflowed), the raw water that has flowed into the inflow section 7 is rectified by passing through the many holes 2 of the inflow side porous current plate 3, and flows from the inflow section 7 to the outflow section 9 side. In this case, because the tank body 1 is deep and the porous rectifying plates 3 and 5 are arranged on the inflow side and the outflow side, the water flows at a small flow rate.
【0012】流入側多孔整流板3の多数の孔2を通った
微流速の水平流は、第1番目、第2番目、第3番目と順
次に各セクションの簾状体11の紐状材14の間を通る
。そして、各セクションにおいて、紐状材14が等間隔
で左右に並んで平行に垂下し、しかも紐状材14が水平
流の流れの強弱に従い揺動し、かつ各紐状材14におい
て無数の繊維ループが繊毛運動をするため、各セクショ
ンごとに流速の平均化が効率良く行われ、さらに前セク
ションより後セクションへ進むに従い平均化が一層進む
。紐状材14は、伸縮性があるためその上下端を固定し
ておいても揺動可能である。[0012] The horizontal flow at a slight velocity passing through the large number of holes 2 of the inflow side porous rectifying plate 3 passes through the string-like material 14 of the screen-like body 11 of each section in the first, second, third and so on. pass between. In each section, the string-like materials 14 are lined up left and right at equal intervals and hang down in parallel, and the string-like materials 14 oscillate according to the strength of the horizontal flow, and each string-like material 14 has countless fibers. Because the loops make ciliary motion, the flow velocity is efficiently averaged in each section, and the averaging progresses further from the front section to the rear section. Since the string-like material 14 has elasticity, it can swing even if its upper and lower ends are fixed.
【0013】水平流がこのように流速を平均化されるの
と併行して、浮遊物質は、各紐状材14による抵抗とそ
の揺動及び繊維ループの繊毛運動により順次下降エネル
ギーを与えられ、しかも簾状体11が前後に多段になっ
ているため、それを繰り返し受け、つまり多槽式反応槽
における反応の促進と同様の作用を受け、浮遊物質の沈
降が促進される。At the same time that the flow velocity of the horizontal flow is averaged in this way, the suspended solids are sequentially given downward energy by the resistance and oscillation of each string material 14 and the ciliary movement of the fiber loops. In addition, since the screen-like bodies 11 are arranged in multiple stages in the front and back, they are repeatedly exposed to this effect, which is similar to the reaction promotion in a multi-vessel reaction tank, and the sedimentation of suspended substances is promoted.
【0014】図4及び図5は円型にした例で、槽本体1
を底部が円錐形の縦長円筒状とし、その中央部にパイプ
状の流入部7を設け、これを中心として流入側多孔整流
板3、複数の簾状体11、流出側多孔整流板5及び流出
部9を同心円状に配置したもので、作用は上記と同様で
ある。FIGS. 4 and 5 show an example of a circular tank body 1.
has a vertically elongated cylindrical shape with a conical bottom, and a pipe-shaped inflow section 7 is provided in the center thereof, and around this, the inflow side porous current plate 3, the plurality of blinds 11, the outflow side porous current plate 5, and the outflow side are connected. The parts 9 are arranged concentrically, and the operation is the same as that described above.
【0015】本発明の作用・効果を確認するため、本発
明者らは透明な模型沈澱槽を使用して次のような実験を
行った。図6及び図7はその実験例を示し、模型沈澱槽
16の深さ120cm、前後の長さ60cm、左右の幅
15cm、流入側及び流出側の多孔整流板17,18の
高さ120cm、左右の幅15cm、厚さ3mmとし、
これら多孔整流板17,18にそれぞれ直径8mmの孔
19を上下に46段、左右に7列設けた。流入部20及
び流出部21の前後の広さはいずれも5cmである。多
孔整流板17,18の間に簾状体22を前後に10cm
の間隔で4個所に配置した。各簾状体22としては、上
記のような構造の紐状濾材23を3cmの間隔でそれぞ
れ5本ずつ支持棒に吊持し、各紐状濾過材23の下端を
模型沈澱槽16の底部に固定した。流出部21の流出パ
イプ24より流出する高さ(115cm) まで模型沈
澱槽16内に予め水道水を入れておき、直径4mmの孔
25を上下5cmの間隔で19段設けた直径2cmの注
入管26を流入部20に入れ、活性汚泥を含む原水(S
S濃度611mg/リットル) を毎分2.1リットル
の流量で注入した。In order to confirm the action and effect of the present invention, the present inventors conducted the following experiment using a transparent model sedimentation tank. Figures 6 and 7 show an example of the experiment, in which the depth of the model settling tank 16 is 120 cm, the front and back length is 60 cm, the left and right width is 15 cm, the height of the porous rectifier plates 17 and 18 on the inflow side and outflow side is 120 cm, and the left and right sides are 120 cm. The width is 15 cm, the thickness is 3 mm,
Each of these porous current plates 17 and 18 was provided with holes 19 having a diameter of 8 mm in 46 stages vertically and in 7 rows horizontally. The front and rear widths of the inflow section 20 and the outflow section 21 are both 5 cm. Between the porous rectifying plates 17 and 18, a screen-like body 22 is placed 10 cm back and forth.
They were placed in four locations at intervals of . As each screen-like body 22, five string-like filter media 23 having the above-mentioned structure are suspended from support rods at intervals of 3 cm, and the lower ends of each string-like filter media 23 are attached to the bottom of the model sedimentation tank 16. Fixed. Tap water was previously filled in the model sedimentation tank 16 up to the height (115 cm) at which it flows out from the outflow pipe 24 of the outflow section 21, and an injection pipe with a diameter of 2 cm was provided with 19 steps of holes 25 each having a diameter of 4 mm at intervals of 5 cm above and below. 26 into the inflow part 20, and the raw water (S
S concentration 611 mg/liter) was injected at a flow rate of 2.1 liters per minute.
【0016】図8から図15は、この実験において観測
した模型沈澱槽16内の活性汚泥の濃淡の分布を図式化
したもので、図8は注入して2分後、図9は8分後、図
10は10分後、図11は20分後、図12は30分後
、図13は40分後、図14は50分後、図15は60
分後の状況をそれぞれ示す。この実験により、活性汚泥
の沈澱が簾状体22で区切られるように段階的に行われ
、各セクションごとに恰も一つの沈澱池内で起こるよう
な旋回流が観測され、上述したような作用が起こること
が確かめられた。[0016] Figures 8 to 15 are diagrammatic representations of the density distribution of activated sludge in the model settling tank 16 observed in this experiment. , Figure 10 is after 10 minutes, Figure 11 is after 20 minutes, Figure 12 is after 30 minutes, Figure 13 is after 40 minutes, Figure 14 is after 50 minutes, Figure 15 is after 60 minutes.
Each shows the situation after a minute. In this experiment, the sedimentation of activated sludge was carried out in stages separated by screen-shaped bodies 22, and a swirling flow was observed in each section as if it were occurring in one sedimentation tank, and the above-mentioned effects occurred. This was confirmed.
【0017】なお、上記の実施例では、紐状材として無
数の繊維ループを形成ししかも螺旋状に捻じって伸縮性
をもたせた紐状濾材を使用したが、これ以外の形態の紐
状材でも良く、また紐状材に限らず棒状材でも構わない
。[0017] In the above embodiment, a string-like filter material having countless fiber loops formed therein and twisted spirally to provide elasticity was used as the string-like material, but other forms of string-like material may be used. However, it is also possible to use not only a string-like material but also a bar-like material.
【0018】[0018]
【発明の効果】本発明によれば、複数本の長い紐状材又
は棒状材を所定の間隔をおいて平行に垂下して簾状とし
、これを流入側多孔整流板と流出側多孔整流板との間に
おいて水流の方向に前後所定の間隔をおいて複数段配置
するだけで、互いに独立した複数の沈澱部を水平方向に
多段に並設し、それに処理水を順次微流速で移し変えて
繰り返し沈澱させるのと同様の効果が得られるので、そ
れを小さい平面積内で深さを深くすることにより有効に
かつ経済的に行える。すなわち、従来の沈澱池に比べ敷
地面積を大幅に縮小でき、処理施設全体を狭い敷地内に
納めることができる。Effects of the Invention According to the present invention, a plurality of long string-like materials or rod-like materials are hung in parallel at predetermined intervals to form a blind, and these are connected to the inflow side porous current plate and the outflow side porous current plate. By simply arranging multiple stages at a predetermined distance from front to back in the direction of water flow, a plurality of mutually independent settling sections are arranged in parallel in multiple stages in the horizontal direction, and treated water is sequentially transferred thereto at a small flow rate. Since the same effect as repeated precipitation can be obtained, it can be done effectively and economically by increasing the depth within a small plane area. In other words, the site area can be significantly reduced compared to conventional sedimentation ponds, and the entire treatment facility can be housed within a narrow site.
【0019】また、複数本の紐状材又は棒状材は各段ご
とに簾状になっているため、単に吊り下げ、また引き上
げるだけで簡単に交換でき、しかもその簾状のまま強制
的に揺動又は振動させるだけで、付着した浮遊物質を容
易に落とすことができ、保守が容易である。[0019] Furthermore, since the plurality of string-like materials or rod-like materials are shaped like blinds at each stage, they can be easily replaced by simply hanging and pulling them up. Adhering floating substances can be easily removed by simply moving or vibrating, making maintenance easy.
【図1】 本発明による縦型深層沈澱槽を角型にした
場合の例の概要斜視図である。FIG. 1 is a schematic perspective view of an example of a rectangular vertical deep sedimentation tank according to the present invention.
【図2】 同上の概要平面図である。FIG. 2 is a schematic plan view of the same as above.
【図3】 同上の概要断面図である。FIG. 3 is a schematic cross-sectional view of the same as above.
【図4】 円型にした場合の例の一部切欠斜視図
である。FIG. 4 is a partially cutaway perspective view of an example of a circular shape.
【図5】 同上の平面図である。FIG. 5 is a plan view of the same as above.
【図6】 模型沈澱槽による実験例の斜視図であ
る。FIG. 6 is a perspective view of an experimental example using a model settling tank.
【図7】 同上の平面図である。FIG. 7 is a plan view of the same as above.
【図8】 実験例における活性汚泥の注入2分後
の濃淡分布図である。FIG. 8 is a density distribution diagram 2 minutes after the injection of activated sludge in an experimental example.
【図9】 8分後の濃淡分布図である。FIG. 9 is a shading distribution map after 8 minutes.
【図10】 10分後の濃淡分布図である。FIG. 10 is a density distribution diagram after 10 minutes.
【図11】 20分後の濃淡分布図である。FIG. 11 is a density distribution diagram after 20 minutes.
【図12】 30分後の濃淡分布図である。FIG. 12 is a density distribution diagram after 30 minutes.
【図13】 40分後の濃淡分布図である。FIG. 13 is a density distribution diagram after 40 minutes.
【図14】 50分後の濃淡分布図である。FIG. 14 is a density distribution diagram after 50 minutes.
【図15】 60分後の濃淡分布図である。FIG. 15 is a density distribution diagram after 60 minutes.
1 槽本体 2 孔 3 流入側多孔整流板 4 孔 5 流出側多孔整流板 7 流入部 9 流出部 11 簾状体 14 紐状材 1 Tank body 2 Hole 3 Inflow side porous rectifier plate 4 Hole 5 Outflow side porous rectifier plate 7 Inflow section 9 Outflow part 11. Curtain-like body 14 String material
Claims (2)
る流出部との間の距離に比べて深さがはるかに深い縦型
深層沈澱槽において、多数の孔を設けた縦長の多孔整流
板を上記流入部側と流出部側にそれぞれ配置し、また複
数本の長い紐状材又は棒状材を、水平流と交差する方向
に所定の間隔をおいて平行に垂下して簾状とし、これを
、流入側多孔整流板と流出側多孔整流板との間において
水平流の方向に前後所定の間隔をおいて複数段配置した
ことを特徴とする縦型深層沈澱槽。Claim 1: A vertically elongated porous rectifier with a large number of holes in a vertical deep sedimentation tank that is much deeper in depth than the distance between the inlet where raw water flows in and the outlet where treated water flows out. Plates are respectively arranged on the inlet side and the outlet side, and a plurality of long string-like materials or rod-like materials are hung in parallel at a predetermined interval in a direction intersecting the horizontal flow to form a blind shape, A vertical deep sedimentation tank characterized in that a plurality of layers are arranged at a predetermined interval back and forth in the direction of horizontal flow between an inflow side porous current plate and an outflow side porous current plate.
、その複数本を揺動可能に垂下して簾状にしたことを特
徴とする請求項1記載の縦型深層沈澱槽。2. The vertical deep sedimentation tank according to claim 1, characterized in that a cord-like material having countless fiber loops is used, and a plurality of cord-like materials are swingably suspended to form a screen-like screen.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3010353A JPH07114885B2 (en) | 1991-01-07 | 1991-01-07 | Vertical deep sedimentation tank |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3010353A JPH07114885B2 (en) | 1991-01-07 | 1991-01-07 | Vertical deep sedimentation tank |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH04250802A true JPH04250802A (en) | 1992-09-07 |
| JPH07114885B2 JPH07114885B2 (en) | 1995-12-13 |
Family
ID=11747821
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP3010353A Expired - Lifetime JPH07114885B2 (en) | 1991-01-07 | 1991-01-07 | Vertical deep sedimentation tank |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH07114885B2 (en) |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0889709A (en) * | 1994-09-27 | 1996-04-09 | Hideyuki Kobayashi | Separating and removing method of mixture in liquid |
| JP2006272257A (en) * | 2005-03-30 | 2006-10-12 | Maezawa Ind Inc | Flocculator |
| KR100799763B1 (en) * | 2006-09-25 | 2008-02-01 | 주식회사 젠트로 | Sedimentation bulkhead |
| JP2017074539A (en) * | 2015-10-13 | 2017-04-20 | 日本ソリッド株式会社 | Sedimentation device |
| CN109289258A (en) * | 2018-10-30 | 2019-02-01 | 青岛思普润水处理股份有限公司 | A kind of sedimentation pond for water treatment |
| JP2021137782A (en) * | 2020-03-09 | 2021-09-16 | 住友重機械エンバイロメント株式会社 | Settling accelerator and sedimentation basin facility |
Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5580011U (en) * | 1978-11-27 | 1980-06-02 |
-
1991
- 1991-01-07 JP JP3010353A patent/JPH07114885B2/en not_active Expired - Lifetime
Patent Citations (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5580011U (en) * | 1978-11-27 | 1980-06-02 |
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0889709A (en) * | 1994-09-27 | 1996-04-09 | Hideyuki Kobayashi | Separating and removing method of mixture in liquid |
| JP2006272257A (en) * | 2005-03-30 | 2006-10-12 | Maezawa Ind Inc | Flocculator |
| KR100799763B1 (en) * | 2006-09-25 | 2008-02-01 | 주식회사 젠트로 | Sedimentation bulkhead |
| JP2017074539A (en) * | 2015-10-13 | 2017-04-20 | 日本ソリッド株式会社 | Sedimentation device |
| CN109289258A (en) * | 2018-10-30 | 2019-02-01 | 青岛思普润水处理股份有限公司 | A kind of sedimentation pond for water treatment |
| CN109289258B (en) * | 2018-10-30 | 2024-03-01 | 青岛思普润水处理股份有限公司 | Water treatment sedimentation tank |
| JP2021137782A (en) * | 2020-03-09 | 2021-09-16 | 住友重機械エンバイロメント株式会社 | Settling accelerator and sedimentation basin facility |
Also Published As
| Publication number | Publication date |
|---|---|
| JPH07114885B2 (en) | 1995-12-13 |
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