JPH043680Y2 - - Google Patents
Info
- Publication number
- JPH043680Y2 JPH043680Y2 JP1984188235U JP18823584U JPH043680Y2 JP H043680 Y2 JPH043680 Y2 JP H043680Y2 JP 1984188235 U JP1984188235 U JP 1984188235U JP 18823584 U JP18823584 U JP 18823584U JP H043680 Y2 JPH043680 Y2 JP H043680Y2
- Authority
- JP
- Japan
- Prior art keywords
- tank
- tube
- advection
- liquid
- aeration 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.)
- Expired
Links
- 238000005273 aeration Methods 0.000 claims description 58
- 239000007788 liquid Substances 0.000 claims description 45
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 43
- 239000000203 mixture Substances 0.000 claims description 10
- 238000004062 sedimentation Methods 0.000 description 9
- 239000010802 sludge Substances 0.000 description 7
- 230000001105 regulatory effect Effects 0.000 description 5
- 238000005192 partition Methods 0.000 description 4
- 238000005276 aerator Methods 0.000 description 3
- 239000010840 domestic wastewater Substances 0.000 description 2
- 238000009434 installation Methods 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- 238000004659 sterilization and disinfection Methods 0.000 description 2
- 230000003254 anti-foaming effect Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000006260 foam Substances 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 229920003002 synthetic resin Polymers 0.000 description 1
- 239000000057 synthetic resin Substances 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Treatment Of Biological Wastes In General (AREA)
- Aeration Devices For Treatment Of Activated Polluted Sludge (AREA)
- Feeding, Discharge, Calcimining, Fusing, And Gas-Generation Devices (AREA)
Description
〔産業上の利用分野〕
本考案はオキシデーシヨンデイツチといわれる
大型曝気槽から沈殿槽へ常に一定流量で曝気槽混
合液を移流する水処理装置における定量移流装置
に関する。
〔従来の技術〕
都市排水等の生活排水を処理する水処理装置に
流入する被処理水の流入量は、1日の時間帯によ
つて高低があり、朝夕にピークがあり昼は少く更
に夜間は少量となる。このような時間帯による流
入量の差は大規模な処理装置では問題にならない
が、1日の処理量が100m3/日〜1000m3/日程度
の中小規模の処理装置においては曝気槽から沈殿
槽へ曝気槽混合液を移流させる場合朝夕のピーク
時には沈殿槽に一時に大量の曝気槽混合液が流入
して沈殿槽内が攪拌されてしまうため沈殿機能が
低下するという問題があり、この問題を解決する
ために、従来は、曝気槽の手前に調節槽を設けて
被処理水の供給を調節していた。このため調整槽
の設備並に設置面積を必要とするという問題があ
つた。
〔考案が解決しようとする問題点〕
本考案は水量調整のための調整槽を設置せず、
小型で簡単な構造で沈殿槽へ常に一定流量で曝気
槽から曝気槽混合液を移流させようとするもので
ある。
〔問題点を解決するための手段〕
本考案は、曝気槽と沈殿槽間に設けられ曝気槽
から曝気槽混合液が導入される定量槽と、この定
量槽中に立設され前記沈殿槽に連通された移流筒
と、一端吸入側を前記定量槽の液中に挿入され他
端吐出側を前記移流筒中に挿入したサイホン管
と、前記移流筒の液面に浮上させ前記サイホン管
の吐出口を液中に開口させるとともに前記定量槽
の液面に浮上させたフロートに連結され前記サイ
ホン管で導入された曝気槽混合液を溢流させて移
流筒に供給する浮動筒とよりなりサイホン管の流
出側を曝気槽の水位差に応じて浮動する浮動筒に
挿入したことにより曝気槽の液面と浮動槽の液面
の水位差を常に一定に保ち、サイホン管から浮動
層を介して移流筒へ移流する単位時間当りの水量
を定量に保ち移流槽から常に一定量で沈殿槽へ移
流させるようにし調整槽を不要にしようとするも
のである。
〔作用〕
曝気槽から曝気槽混合液が導入される定量槽は
曝気槽と等しい水位になつている。そして移流筒
にはサイホン管により定量槽からの曝気槽混合液
が導入され、この液に浮上させた浮動筒が定量槽
に浮上させたフロートにより支持されたサイホン
管の吸入側は定量槽に、吐出側は浮動筒に開口さ
せ浮動筒から液が溢流して移流筒に流入している
から、定量槽の水位の変動に伴つて等しい高さで
浮動筒の液面が変動し定量槽と浮動筒の水位差は
常に一定である。したがつてサイホン管に作用す
る水位差も常に一定で、定量槽の水位の変化にか
かわらず常に一定の流速で定量槽から移流筒へさ
らに移流筒から沈殿槽へと液を移流することがで
きる。
〔実施例〕
本考案の一実施例を添附図面について説明す
る。
全体のフローシートを第1図によつて説明す
る。1は散気手段を備えた曝気沈殿槽で一端に原
子流入管2が導入され、他端流出口3には荒目ス
クリーン4が張設されている。さらに流出口3よ
り上澄液が流出する流出槽5には破砕機6が設け
られ、流出槽5のバイパス7には細目スクリーン
8が設けられている。
9はオキシデーシヨンデイツチ型曝気槽で、前
記流出槽5から流入管10で被処理水が導入され
る楕円形水路よりなり、上面が密閉されていると
もとに途中が流路を遮断する仕切壁11で仕切ら
れている。さらに仕切壁11の上流側と下流側と
は曝気槽9の底面より掘り下げた一対の流通路1
2で連通され、この流通路12の流入側開口部1
3にはドラフトチユーブエアレータ14が夫々連
結されている。
ドラフトチユーブエアレータ14は、曝気槽9
の上壁より整流板23を有する支持杆15が吊下
げられ下端を前記流通路12に連通させたドラフ
トチユーブ16と、このドラフトチユーブ16の
上端開口部近くに挿入され前記曝気槽9上に支持
された電動機17にその回転軸18が連結された
回転羽根20と、この回転羽根20の下方に臨ま
せて開口した多数の散気孔を開口させた散気体2
1と、この散気体21に連通させコンプレツサよ
り圧縮空気を送られる圧縮空気管22とより構成
されている。
24は上面を開口し、曝気槽9と流入路25で
連通した定量槽で、この定量槽24中に上面を開
口した移流筒26が植立され、この移流筒26中
に、定量槽24に支持杆27で固定され一端吸入
側28を定量槽24中に挿入されたサイホン管2
9の他端吐出側30が挿入されている。さらに移
流筒26中に挿入されたサイホン管29の吐出口
31は移流筒26の水面に浮上させ上面を開口さ
せた浮動筒32の水中に開口され、この浮動筒3
2から溢流した曝気槽混合液が移流筒26に流入
するようになつている。またサイホン管29の上
端には開閉弁33付の空気抜管34が設けられ、
さらに流入側には空気管35が接続されている。
浮動筒32は、外周面3ケ所に固定した短管3
6に夫々長尺のロツド37が挿通されこのロツド
37に短管36の上下でワツシヤを介してナツト
が螺着されロツド37を浮動筒32に固定されて
いる。また、移流筒26の外周には合成樹脂発泡
体を充填した環状のフロート38が上下動自在に
嵌挿され、このフロート38の平面3等分位置に
夫々上下方向に短管39が挿通固定されている。
そして、夫々の短管39にロツド40が挿通され
て短管39の上下ワツシヤとナツトで短管39に
固定されている。そして浮動筒32とフロート3
8のロツド37,40は定量槽24よりも上方に
突出し連結金具41で一体に連結される。
連結金具41は連結板42で連結された上下一
対の連結片43,43間にロツド37,40の間
隔と等しい間隔で一対の短管44,45が固定さ
れたものであり、夫々の短管44,45にロツド
37,40の上端を挿通し夫々の短管44,45
の上下においてロツド37,40にワツシヤを介
してナツトで締着することにより浮動筒32はフ
ロート38に一体に連結される。移流筒26の上
端外周の3ケ所からガイド片47が突設されこの
ガイド片47の案内孔48にフロート38のロツ
ド40の途中が挿通されている。ガイド片47は
半円弧形の支持枠46から突設され、支持枠46
は両端の締付部49で移流筒26の外周に締付固
定されている。
50は沈殿槽で、汚泥掻寄機61を備え、前記
移流筒26の下部から導出された移流管52が中
心部に導入されている。
53は汚泥貯留槽で、汚泥を返送するポンプ5
4を備えている。
55は沈殿槽50と流入管56で連通した消泡
槽、57は消毒槽で、薬液注入管58と散気管5
9を備え、消泡槽55と流入管60で連通され、
処理水流出管61が導出されている。
尚曝気槽9は第4図に示すように長楕円形に形
成され長さ方向の両端部に流通路を残すようにし
て中央部長さ方向仕切壁62で仕切り環状の水路
を形成し、この曝気槽9の流出端部に外接させて
定量槽24、沈殿槽50を形成するか、或いは第
5図に示すように曝気槽9を中心に空間部63を
有する楕円形の環状の水路に形成し、空間部63
に定量槽24、沈殿槽50その他の水処理設備を
設ける場合もある。また、定量槽24を設けず移
流筒26を調節曝気槽9中に植立することも考え
られるが、水流によつてフロート38の動作が不
安定になるという問題がある。
次に上述の実施例の作用を説明する。
曝気槽9には、流入路10より曝気沈殿槽1、
荒目スクリーン4、細目スクリーン8、破砕機6
を通過した被処理水が導入される。導入された被
処理水は還流被処理水とともにドラフトチユーブ
エアレータ14に導かれ、ドラフトチユーブ16
の上部に挿入した回転羽根20によつて散気体2
1から噴出される圧縮空気を捲き込みながら、ド
ラフトチユーブ16に導入され、ドラフトチユー
ブ16から流路12を通つて曝気されながら仕切
壁11の反対側へ流出し、返送汚泥を混合されて
さらに曝気槽9を回流した曝気槽混合液はこの流
出口25から定量槽24に導出される。曝気槽9
においては底部近くで曝気されるから液面の上下
が曝気に影響することがない。
定量槽24で曝気槽混合液は、曝気槽9と同じ
水位L1になり定量槽24の液中に一端を挿入さ
れたサイホン管29によつて定量槽24の液を移
流筒26中に移流させる。この際、サイホン管2
9の吐出口31は移流筒26中の液面に浮上させ
た浮動筒32中に開口しているから、定量槽24
中の液は、一旦浮動筒32中に流入し、この浮動
筒32から溢流して移流筒26へ流出する。移流
筒26中の浮動筒32は、移流筒26の液面に浮
上するとともにロツド37,40と連結金具41
によつて定量槽34中のフロート38に支持さ
れ、定量槽24の液面の上下に伴つて同じ高さだ
け上下動する。したがつて第2図において定量槽
24の水位がL1からL1′に変化すると浮動筒32
の水位はL2からL2′に変化するが、L1−L2=l、
L2−L2′=l′とすればl=l′であり、定量槽24の
水位が変化しても定量槽24と浮動筒の水位差は
常に等しい。したがつてサイホン管29の水位差
は水面の上下動によつて変化せず、サイホン管2
9による曝気槽混合液の移流速度は水位L1の変
動とは無関係に常に一定である。よつて1日の時
間帯によつて原水流入量が変化し曝気槽9の水位
が変化しても、サイホン管29による液の移流速
度は常に一定であり、一時に大量の曝気槽混合液
が移流筒52から沈殿槽50へ移流することがな
く、沈殿槽52が移流する液によつて攪拌される
ようなことがない。またサイホン管29の始動時
に内部の空気を排除する場合は、空気抜管34を
眞空ポンプ等に接続し開閉弁33を開いて空気を
排除する。
以上のようにして沈殿槽50に移流した曝気槽
混合液は、沈殿槽50で汚泥を分離され、さらに
消泡槽55、消毒槽57を経て河川へ放流され
る。汚泥は掻寄機51で掻寄せられ汚泥タンク5
3から一部は曝気槽9へ返送され他は濃縮されて
搬出される。
放流される処理水の水質は次のとおりである。
[Industrial Field of Application] The present invention relates to a quantitative advection device in a water treatment system that always advects an aeration tank mixture at a constant flow rate from a large aeration tank called an oxidation date to a settling tank. [Prior art] The amount of water to be treated that flows into water treatment equipment that processes domestic wastewater such as urban wastewater varies depending on the time of the day, with a peak in the morning and evening, a low amount in the afternoon, and a low amount at night. will be a small amount. Such differences in the amount of inflow depending on the time of day are not a problem in large-scale treatment equipment, but in small- to medium-sized treatment equipment with a daily treatment volume of 100 m 3 /day to 1000 m 3 /day, sedimentation from the aeration tank is not a problem. When advecting the aeration tank mixture to the tank, there is a problem that during peak hours in the morning and evening, a large amount of the aeration tank mixture flows into the sedimentation tank at once, stirring the inside of the sedimentation tank, which reduces the sedimentation function. In order to solve this problem, conventionally, a regulating tank was provided in front of the aeration tank to adjust the supply of water to be treated. For this reason, there was a problem in that the equipment and installation area for the regulating tank were required. [Problems to be solved by the invention] The invention does not install an adjustment tank to adjust the water volume.
This system uses a small and simple structure to advect the aeration tank mixture from the aeration tank to the settling tank at a constant flow rate. [Means for solving the problem] The present invention consists of a metering tank that is installed between an aeration tank and a settling tank and into which the aeration tank mixed liquid is introduced from the aeration tank, and a metering tank that is installed upright in the metering tank and is connected to the settling tank. a siphon tube having one end suction side inserted into the liquid of the metering tank and the other end discharge side inserted into the advection tube, and a discharge port of the siphon tube that is floated on the liquid surface of the advection tube. The floating tube opens into the liquid and is connected to a float floated on the liquid surface of the quantitative tank, causing the aeration tank mixture introduced by the siphon tube to overflow and supply to the advection tube. By inserting the outflow side into a floating tube that floats according to the water level difference in the aeration tank, the water level difference between the liquid level in the aeration tank and the liquid level in the floating tank is always kept constant, and the flow from the siphon tube through the floating layer is transferred to the advection tube. This aims to eliminate the need for a regulating tank by keeping the amount of water advected per unit time constant and allowing a constant amount of water to be advected from the advection tank to the settling tank at all times. [Function] The metering tank into which the aeration tank mixed liquid is introduced from the aeration tank has the same water level as the aeration tank. Then, the aeration tank mixed liquid from the metering tank is introduced into the advection tube by a siphon tube, and the floating tube floated on this liquid is supported by the float floated on the metering tank.The suction side of the siphon tube is connected to the metering tank. The discharge side is opened to the floating tube, and the liquid overflows from the floating tube and flows into the advection tube, so as the water level in the metering tank fluctuates, the liquid level in the floating tube fluctuates at the same height, causing it to float with the metering tank. The water level difference between the tubes is always constant. Therefore, the water level difference acting on the siphon pipe is always constant, and liquid can always be advected from the metering tank to the advection tube and from the advection tube to the settling tank at a constant flow rate regardless of changes in the water level in the metering tank. . [Embodiment] An embodiment of the present invention will be described with reference to the accompanying drawings. The entire flow sheet will be explained with reference to FIG. Reference numeral 1 denotes an aeration sedimentation tank equipped with an aeration means, into which an atomic inflow pipe 2 is introduced at one end, and a coarse screen 4 is provided over an outlet 3 at the other end. Further, an outflow tank 5 from which the supernatant liquid flows out from the outflow port 3 is provided with a crusher 6, and a bypass 7 of the outflow tank 5 is provided with a fine screen 8. Reference numeral 9 denotes an oxidation date type aeration tank, which consists of an elliptical waterway into which water to be treated is introduced from the outflow tank 5 through an inflow pipe 10, the upper surface of which is sealed, and the flow path is blocked in the middle. It is separated by a partition wall 11. Furthermore, the upstream side and downstream side of the partition wall 11 are a pair of flow passages 1 dug from the bottom of the aeration tank 9.
2, and the inflow side opening 1 of this flow path 12
3 are connected to draft tube aerators 14, respectively. The draft tube aerator 14 is an aeration tank 9
A draft tube 16 having a support rod 15 having a rectifying plate 23 suspended from the upper wall and having a lower end communicating with the flow passage 12, and a draft tube 16 inserted near the upper end opening of the draft tube 16 and supported on the aeration tank 9. A rotating blade 20 whose rotating shaft 18 is connected to an electric motor 17, and a gas diffuser 2 having a large number of air diffuser holes facing downward from the rotating blade 20.
1, and a compressed air pipe 22 that communicates with the gas diffuser 21 and receives compressed air from a compressor. Reference numeral 24 denotes a metering tank with an open top and communicating with the aeration tank 9 through an inflow path 25. An advection tube 26 with an open top is installed in this metering tank 24. A siphon pipe 2 fixed with a support rod 27 and having one end suction side 28 inserted into a quantitative tank 24
9, the other end discharge side 30 is inserted. Further, the discharge port 31 of the siphon pipe 29 inserted into the advection tube 26 is opened into the water of a floating tube 32 which floats on the water surface of the advection tube 26 and has an open upper surface.
The aeration tank mixed liquid overflowing from 2 flows into the advection cylinder 26. Further, an air vent pipe 34 with an on-off valve 33 is provided at the upper end of the siphon pipe 29.
Further, an air pipe 35 is connected to the inflow side. The floating tube 32 has short tubes 3 fixed at three locations on the outer circumferential surface.
A long rod 37 is inserted through each of the short tubes 6 and 6, and nuts are screwed onto the rods 37 through washers at the top and bottom of the short tube 36, thereby fixing the rods 37 to the floating tube 32. Furthermore, an annular float 38 filled with synthetic resin foam is fitted onto the outer periphery of the advection tube 26 so as to be movable up and down, and short tubes 39 are inserted and fixed in the vertical direction into three equal parts of the plane of the float 38, respectively. ing.
A rod 40 is inserted into each of the short tubes 39 and fixed to the short tubes 39 by upper and lower washers of the short tubes 39 and nuts. And floating cylinder 32 and float 3
The eight rods 37 and 40 protrude above the quantitative tank 24 and are connected together by a connecting fitting 41. The connecting fitting 41 has a pair of short pipes 44, 45 fixed between a pair of upper and lower connecting pieces 43, 43 connected by a connecting plate 42 at an interval equal to the interval between the rods 37, 40. Insert the upper ends of the rods 37 and 40 into the short tubes 44 and 45, respectively.
The floating tube 32 is integrally connected to the float 38 by tightening the rods 37 and 40 at the top and bottom of the tube with nuts through washers. Guide pieces 47 are provided protruding from three locations on the outer periphery of the upper end of the advection cylinder 26, and a rod 40 of the float 38 is inserted halfway through a guide hole 48 of the guide piece 47. The guide piece 47 protrudes from the semicircular arc-shaped support frame 46 .
is fastened to the outer periphery of the advection tube 26 by fastening portions 49 at both ends. Reference numeral 50 denotes a settling tank, which is equipped with a sludge scraper 61, and has an advection pipe 52 led out from the lower part of the advection tube 26 introduced into its center. 53 is a sludge storage tank, and a pump 5 returns the sludge.
It is equipped with 4. 55 is an antifoaming tank that communicates with the settling tank 50 through an inflow pipe 56; 57 is a disinfection tank;
9, communicated with the defoaming tank 55 through an inflow pipe 60,
A treated water outflow pipe 61 is led out. As shown in FIG. 4, the aeration tank 9 is formed into an elongated oval shape, with flow passages left at both ends in the longitudinal direction, forming an annular waterway partitioned by a partition wall 62 in the longitudinal direction of the central length. A quantitative tank 24 and a settling tank 50 are formed by circumscribing the outflow end of the tank 9, or an elliptical annular waterway having a space 63 around the aeration tank 9 is formed as shown in FIG. , space part 63
In some cases, a quantitative tank 24, a settling tank 50, and other water treatment equipment are provided. It is also conceivable to install the advection cylinder 26 in the regulating aeration tank 9 without providing the quantitative tank 24, but there is a problem that the operation of the float 38 becomes unstable due to the water flow. Next, the operation of the above embodiment will be explained. The aeration tank 9 is connected to an aeration sedimentation tank 1 from an inflow path 10.
Coarse screen 4, fine screen 8, crusher 6
The water to be treated that has passed through is introduced. The introduced treated water is guided to the draft tube aerator 14 together with the recirculated treated water, and then to the draft tube 16.
The gas diffuser 2 is
The compressed air ejected from 1 is introduced into the draft tube 16 while being drawn in, and flows from the draft tube 16 through the flow path 12 to the opposite side of the partition wall 11 while being aerated, where it is mixed with return sludge and further aerated. The aeration tank mixed liquid that has circulated through the tank 9 is led out to the quantitative tank 24 from this outlet 25. Aeration tank 9
Since aeration is carried out near the bottom, the rise and fall of the liquid level does not affect the aeration. In the quantitative tank 24, the aeration tank mixed liquid reaches the same water level L1 as in the aeration tank 9, and the liquid in the quantitative tank 24 is advected into the advection tube 26 by the siphon pipe 29, one end of which is inserted into the liquid in the quantitative tank 24. let At this time, siphon tube 2
Since the discharge port 31 of No. 9 opens into the floating tube 32 which is floated on the liquid level in the advection tube 26, the metering tank 24
The liquid inside once flows into the floating tube 32, overflows from the floating tube 32, and flows out to the advection tube 26. The floating tube 32 in the advection tube 26 floats on the liquid surface of the advection tube 26 and connects the rods 37, 40 and the connecting fitting 41.
It is supported by a float 38 in the quantitative tank 34 and moves up and down by the same height as the liquid level in the quantitative tank 24 rises and falls. Therefore, in FIG. 2, when the water level of the quantitative tank 24 changes from L 1 to L 1 ', the floating tube 32
The water level changes from L 2 to L 2 ′, but L 1 −L 2 = l,
If L 2 −L 2 ′=l′, then l=l′, and even if the water level in the quantitative tank 24 changes, the difference in water level between the quantitative tank 24 and the floating tube is always the same. Therefore, the water level difference in the siphon pipe 29 does not change due to the vertical movement of the water surface, and the water level difference in the siphon pipe 29 does not change due to the vertical movement of the water surface.
The advection speed of the aeration tank mixture according to 9 is always constant regardless of fluctuations in the water level L1 . Therefore, even if the amount of raw water flowing in changes depending on the time of day and the water level in the aeration tank 9 changes, the advection speed of the liquid through the siphon pipe 29 is always constant, and a large amount of the mixed liquid in the aeration tank can flow at once. There is no advection of liquid from the advection tube 52 to the settling tank 50, and the settling tank 52 is not agitated by the advected liquid. Further, when the air inside the siphon pipe 29 is to be removed when starting the siphon pipe 29, the air vent pipe 34 is connected to a vacuum pump or the like, and the on-off valve 33 is opened to remove the air. The aeration tank mixed liquid advected to the settling tank 50 as described above is separated from the sludge in the settling tank 50, and is further discharged into the river via the defoaming tank 55 and the disinfection tank 57. The sludge is collected by a scraper 51 and sent to the sludge tank 5.
A portion from 3 is returned to the aeration tank 9, and the rest is concentrated and transported. The quality of the treated water discharged is as follows.
本考案によれば、曝気槽と沈殿槽間に設けられ
曝気槽から曝気槽混合液が導入される定量槽と、
この定量槽中に立設され前記沈殿槽に連通された
移流筒と、一端吸入側を前記定量槽の液中に挿入
され他端吐出側を前記移流筒中に挿入したサイホ
ン管と、前記移流筒の液面に浮上させ前記サイホ
ン管の吐出口を液中に開口させるとともに前記定
量槽の液面に浮上させたフロートに連結され前記
サイホン管で導入された曝気槽混合液を溢流させ
て移流筒に供給する浮動筒とよりなるため、定量
槽の液中から移流筒に挿入されたサイホン管は、
その吐出口が移流筒の吸面に浮上されるとともに
定量槽に浮上させたフロートで支持された浮動筒
の液中に開口され、定量槽に流入する液量によつ
て定量槽の液面に上下の変動を生じた場合も定量
槽の液面と浮動筒の液面との水位差を常に一定に
保つことができる。したがつてサイホン管の水位
差を曝気槽の液面の変動に関係なく常に一定に保
ち移流筒から沈殿槽へ移流する曝気槽混合液の流
速を常に一定に保つことができる。このため時間
帯によつて排出量が大巾に変化する生活排水の水
処理装置において、曝気槽から沈殿槽へ移流する
曝気槽混合液が一時に大量排出されて沈殿槽を攪
拌してしまうようなことがなく沈殿効率を向上さ
せることができる。また定量槽は従来の調整槽に
比べ大量の被処理水を貯留する必要がなくサイホ
ン管を設けるだけの小容量のものでよいから水処
理装置全体の設置面積を縮小することができる。
According to the present invention, a quantitative tank is provided between the aeration tank and the settling tank and into which the aeration tank mixture is introduced from the aeration tank;
an advection cylinder installed upright in the quantitative tank and communicated with the settling tank; a siphon pipe with one end of the suction side inserted into the liquid of the quantitative tank and the other end of the discharge side inserted into the advection cylinder; and the advection cylinder. The aeration tank mixture is connected to the float floated to the liquid surface of the quantitative tank, and the aeration tank mixture introduced by the siphon pipe is caused to overflow and advection. The siphon tube inserted into the advection tube from the liquid in the metering tank is
The discharge port is floated on the suction surface of the advection cylinder and opened into the liquid in the floating cylinder supported by a float floated on the quantitative tank, and the liquid level in the quantitative tank is raised by the amount of liquid flowing into the quantitative tank. Even when vertical fluctuations occur, the water level difference between the liquid level in the metering tank and the liquid level in the floating cylinder can always be kept constant. Therefore, the water level difference in the siphon pipe can be kept constant regardless of fluctuations in the liquid level in the aeration tank, and the flow rate of the aeration tank mixed liquid advected from the advection tube to the settling tank can be kept constant at all times. For this reason, in water treatment equipment for domestic wastewater, where the amount of discharge varies widely depending on the time of day, a large amount of the aeration tank mixed liquid that advects from the aeration tank to the sedimentation tank may be discharged at once and agitate the sedimentation tank. The precipitation efficiency can be improved without any problems. Furthermore, the metering tank does not need to store a large amount of water to be treated compared to a conventional regulating tank, and only needs to be equipped with a siphon pipe, so the installation area of the entire water treatment device can be reduced.
第1図は本考案の一実施例を示す水処理装置の
フローシート、第2図は同上定量槽の縦断側面
図、第3図は同上平面図、第4図は同上曝気槽の
平面図、第5図は同上曝気槽の他の実施例を示す
平面図である。
9……曝気槽、24……定量槽、26……移流
筒、29……サイホン管、32……浮動筒、38
……フロート、50……沈殿槽。
Fig. 1 is a flow sheet of a water treatment device showing an embodiment of the present invention, Fig. 2 is a vertical cross-sectional side view of the quantitative tank as above, Fig. 3 is a plan view of the same as above, Fig. 4 is a plan view of the aeration tank as above; FIG. 5 is a plan view showing another embodiment of the aeration tank. 9... Aeration tank, 24... Quantitative tank, 26... Advection tube, 29... Siphon pipe, 32... Floating tube, 38
... Float, 50 ... Sedimentation tank.
Claims (1)
混合液が導入される定量槽と、この定量槽中に立
設され前記沈殿槽に連通された移流筒と、一端吸
入側を前記定量槽の液中に挿入され他端吐出側を
前記移流筒中に挿入したサイホン管と、前記移流
筒の液面に浮上させ前記サイホン管の吐出口を液
中に開口させるとともに前記定量槽の液面に浮上
させたフロートに連結され前記サイホン管で導入
された曝気槽混合液を溢流させて移流筒に供給す
る浮動筒とよりなることを特徴とする水処理装置
における定量移流装置。 A metering tank provided between the aeration tank and the settling tank and into which the aeration tank mixed liquid is introduced from the aeration tank, an advection tube installed upright in the metering tank and communicating with the settling tank, and one end of the suction side connected to the metering tank. A siphon tube is inserted into the liquid and the other end discharge side is inserted into the advection tube, and the siphon tube is floated on the liquid surface of the advection tube to open the discharge port of the siphon tube into the liquid and the other end is inserted into the liquid surface of the quantitative tank. 1. A quantitative advection device for a water treatment equipment, comprising a floating tube connected to a float that floats and causes the aeration tank mixture introduced by the siphon tube to overflow and supply to the advection tube.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP1984188235U JPH043680Y2 (en) | 1984-12-12 | 1984-12-12 |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP1984188235U JPH043680Y2 (en) | 1984-12-12 | 1984-12-12 |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS61102296U JPS61102296U (en) | 1986-06-30 |
| JPH043680Y2 true JPH043680Y2 (en) | 1992-02-04 |
Family
ID=30745707
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP1984188235U Expired JPH043680Y2 (en) | 1984-12-12 | 1984-12-12 |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH043680Y2 (en) |
-
1984
- 1984-12-12 JP JP1984188235U patent/JPH043680Y2/ja not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS61102296U (en) | 1986-06-30 |
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