JP2002058910A - Flocculating/separation equipment - Google Patents

Flocculating/separation equipment

Info

Publication number
JP2002058910A
JP2002058910A JP2000247821A JP2000247821A JP2002058910A JP 2002058910 A JP2002058910 A JP 2002058910A JP 2000247821 A JP2000247821 A JP 2000247821A JP 2000247821 A JP2000247821 A JP 2000247821A JP 2002058910 A JP2002058910 A JP 2002058910A
Authority
JP
Japan
Prior art keywords
tank
wastewater
center well
sedimentation
coagulation
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP2000247821A
Other languages
Japanese (ja)
Inventor
Shigeo Hishikawa
茂生 菱川
Naoshi Matsuo
尚資 松尾
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.)
TOKAI PLANT ENG KK
Original Assignee
TOKAI PLANT ENG KK
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by TOKAI PLANT ENG KK filed Critical TOKAI PLANT ENG KK
Priority to JP2000247821A priority Critical patent/JP2002058910A/en
Publication of JP2002058910A publication Critical patent/JP2002058910A/en
Pending legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To provide flocculating/separation equipment which is excellent in separation efficiency of flocculated precipitates and treated water and can attain small-sizing of the equipment. SOLUTION: The flocculating/separation device is provided with a center well 10 having a bottom part communicated with the tank in the tank 2 having an opened upper part and has a tank structure with which waste water added with a flocculating agent is separated to flocculated precipitates and treated water. Further a waste water introducing means 12A, a waste water stirring means 23 and a waste water straightening means 36 are installed in the center well from an upper part to a lower part.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】この発明は、廃水に凝集剤を
添加して廃水に含まれる固形物や浮遊物等を凝集物(凝
集沈殿ともいう。)として分離し処理水を得る、凝集沈
殿分離装置(以下、単に分離装置ともいう。)に関する
ものである。
[0001] The present invention relates to a coagulation-sedimentation separation method in which a flocculant is added to wastewater to separate solids and suspended matter contained in the wastewater as coagulation (also referred to as coagulation-sedimentation) to obtain treated water. The present invention relates to an apparatus (hereinafter, also simply referred to as a separation apparatus).

【0002】[0002]

【従来の技術】従来の凝集沈殿分離装置は、図8に示す
ように、廃水に凝集剤を加えて凝集反応させるための撹
拌槽101と、凝集反応による凝集物を沈殿させる沈殿
槽(沈降槽)102とよりなる。なお、図8の撹拌槽1
01は無機凝集剤を加えて急速(高速)撹拌する第1撹
拌槽101Aと、高分子凝集剤を加えて緩速撹拌する第
2撹拌槽101Bよりなる。撹拌槽101で処理された
凝集物を含む廃水は沈殿槽102のセンタウエル103
内に送られるようになっている。
2. Description of the Related Art As shown in FIG. 8, a conventional coagulation / sedimentation / separation apparatus comprises a stirring tank 101 for adding a coagulant to wastewater to cause a coagulation reaction, and a sedimentation tank (sedimentation tank) for precipitating agglomerates by the coagulation reaction. ) 102. The stirring tank 1 shown in FIG.
Numeral 01 is composed of a first stirring tank 101A for adding an inorganic coagulant and stirring rapidly (high speed), and a second stirring tank 101B for adding a polymer coagulant and stirring slowly. Wastewater containing aggregates treated in the stirring tank 101 is supplied to the center well 103 of the settling tank 102.
To be sent inside.

【0003】前記沈殿槽102は槽内中央上部にセンタ
ウエル103の筒体を有し、槽内底面に凝集沈殿の排出
口104、槽上端部に処理水の排水部105が設けられ
ている。また、排出口104の上部には凝集沈殿を集め
て排出口104へ送るための、撹拌羽根106が槽上部
のモータ107により回転可能に形成されている。セン
タウエル103に入った凝集物を含む廃水は下降して槽
内底部において凝集物が沈殿し、処理水は槽上端部の排
水部105より排出される。凝集物の沈殿は撹拌羽根1
06の低速回転により排出口104へ送られ、排出口1
04より排出されるようになっている。
The sedimentation tank 102 has a cylindrical body of a center well 103 at the upper center of the tank, and an outlet 104 for coagulation and sedimentation is provided at the bottom of the tank, and a drainage part 105 for treated water is provided at the upper end of the tank. Further, a stirring blade 106 for collecting the coagulated sediment and sending the collected sediment to the discharge port 104 is formed at the upper part of the discharge port 104 so as to be rotatable by a motor 107 at the upper part of the tank. The wastewater containing the condensate that has entered the center well 103 descends and the condensate precipitates at the bottom of the tank, and the treated water is discharged from the drain 105 at the upper end of the tank. Aggregate sedimentation is caused by stirring blade 1
06 is sent to the discharge port 104 by the low speed rotation, and the discharge port 1
04.

【0004】このように、従来の分離装置は、廃水に凝
集反応を行なうための撹拌槽101と、凝集反応により
生じた凝集物を分離するための沈殿槽102とよりなる
二槽構造のものが一般的である。
As described above, the conventional separation apparatus has a two-tank structure including the stirring tank 101 for performing the coagulation reaction on the wastewater and the sedimentation tank 102 for separating the coagulated matter generated by the coagulation reaction. General.

【0005】また、従来の凝集沈殿分離装置としては、
(イ)分離槽(沈殿槽に相当する。)のセンタウエル外
周に傾斜板を配置して、センタウエルを通過し、センタ
ウエル外周部を上昇する処理水の凝集物の分離処理を向
上させ、装置の小型化を図った構造のもの、(ロ)セン
タウエル内に撹拌機を設け、凝集物の凝集反応の促進を
させる構造のもの、また(ハ)センタウエル外周部の処
理水の上昇領域に整流板を配置し、整流板下部に汚泥に
よる濾過層を形成し、処理水中の凝集物の分離能力を高
めた構造のもの、などが知られている。
[0005] Conventional coagulation-sedimentation separation devices include:
(A) An inclined plate is arranged on the outer periphery of the center well of the separation tank (corresponding to the sedimentation tank) to improve the separation of the aggregate of the treated water passing through the center well and rising on the outer periphery of the center well. (2) A structure in which a stirrer is provided in the center well to promote the agglutination reaction of aggregates. (C) A rising area of the treated water on the outer periphery of the center well. There is known a structure in which a rectifying plate is disposed in a rectifying plate, a filtration layer formed of sludge is formed below the rectifying plate, and the ability to separate aggregates in the treated water is enhanced.

【0006】[0006]

【発明が解決しようとする課題】しかしながら、凝集反
応には滞留時間を要するために凝集反応を行なう槽はあ
る程度の大きさを必要とし、装置全体の小型化は困難で
あった。このため、配管内で撹拌させ、凝集反応を促進
させる構造も考案されたが、この構造は固形物の付着成
長により配管の閉塞する障害が起き易い問題があった。
また、前記(イ)(ハ)の傾斜板、整流板を設けた構造
は、傾斜板、整流板部分の処理水の流速が遅いがため、
分離した凝集物が傾斜板、整流板に堆積もしくは付着成
長する障害を生じた。
However, since the coagulation reaction requires a residence time, a tank for performing the coagulation reaction needs to have a certain size, and it has been difficult to reduce the size of the entire apparatus. For this reason, a structure has been devised in which the agitation reaction is promoted by stirring in the pipe. However, this structure has a problem that a blockage of the pipe is liable to occur due to adhesion and growth of solids.
In addition, in the structure provided with the inclined plate and the rectifying plate of (a) and (c), the flow rate of the treated water in the inclined plate and the rectifying plate portion is low,
There was an obstacle that the separated aggregates were deposited or adhered and grown on the inclined plate and the current plate.

【0007】また、前記(ロ)のセンタウエル内で凝集
反応を促進させるための撹拌機を設けたものでは、十分
な凝集反応の促進効果が得られる様に撹拌した場合、そ
れにより生じた旋回水流が槽内全体の水流に影響を及ぼ
し、沈降しようとして浮遊状態にある凝集物を槽内上部
に巻き上げ凝集物の分離効率の低下となった。従来、分
離装置の小型化が望まれているが、上記のように、凝集
反応の促進効果が得られ、かつ旋回水流が分離槽内全体
の水流に影響を及ぼさない様にし、かつ小型の分離装置
とすることは容易ではなかった。
In the above-mentioned (b) in which a stirrer for promoting the agglutination reaction is provided in the center well, when the stirring is carried out so as to obtain a sufficient effect of promoting the agglutination reaction, the swirling caused by the agitation is performed. The water flow affected the water flow in the entire tank, and the suspended aggregates were lifted up in the tank in an attempt to settle, and the separation efficiency of the aggregates was reduced. Conventionally, a reduction in the size of the separation device has been desired. However, as described above, the effect of accelerating the agglutination reaction is obtained, and the swirling water flow is prevented from affecting the entire water flow in the separation tank. It was not easy to make a device.

【0008】そこで、本発明の課題は、前記した従来の
要望に応えようとしたものであり、凝集沈殿と処理水の
分離が良好でかつ小型化し得る凝集沈殿分離装置を提供
することにある。
It is an object of the present invention to provide a coagulation / sedimentation / separation apparatus which can cope with coagulation / sedimentation and treated water and can be reduced in size.

【0009】[0009]

【課題を解決するための手段】前記した課題を達成する
ために、請求項1の発明は、上方が開放された槽内に、
底部が槽内に連通するセンタウエルを備え、凝集剤を加
えた廃水を凝集沈殿と処理水に分離する槽構造の装置で
あって、前記センタウエル内には上部より下部へ廃水導
入手段、廃水撹拌手段、廃水整流手段が設けられてなる
ことを特徴とする。
Means for Solving the Problems In order to achieve the above-mentioned object, the invention according to claim 1 is provided in a tank having an open upper part.
An apparatus having a tank structure in which a bottom is provided with a center well communicating with the inside of a tank, and a wastewater added with a flocculant is separated into a flocculated sediment and treated water. It is characterized in that stirring means and wastewater rectification means are provided.

【0010】請求項1の発明によれば、センタウエル内
に導入された凝集剤を含む廃水は廃水撹拌手段の撹拌に
より、凝集反応が促進され、凝集物を含む廃水となる。
この廃水は下部の廃水整流手段にて整流されて槽底部に
流下される。凝集物を含む廃水(この廃水は処理水とな
っている。)は廃水整流手段を経て流下されるので、槽
底部における凝集物の巻き上げがないことより、処理水
と凝集物の分離性がよい。請求項1の発明では廃水撹拌
手段、廃水整流手段を有するセンタウエルを槽内に設け
たことより、従来のように別の二槽に分けることなく、
一槽にて凝集沈殿を処理水と良好に分離し沈殿させるこ
とができ、装置の小型をなし得る。
According to the first aspect of the present invention, the wastewater containing the flocculant introduced into the center well is promoted by the agitation of the wastewater stirring means to become the wastewater containing the aggregate.
This wastewater is rectified by the wastewater rectification means at the bottom and flows down to the bottom of the tank. Since wastewater containing aggregates (this wastewater is treated water) flows down through the wastewater rectification means, there is no agglomeration of aggregates at the bottom of the tank, so that separability between treated water and aggregates is good. . In the invention of claim 1, since the center well having the waste water stirring means and the waste water rectification means is provided in the tank, it is not divided into two separate tanks as in the related art.
The coagulated sediment can be satisfactorily separated and separated from the treated water in one tank, and the apparatus can be made compact.

【0011】前記課題を達成するための、請求項2の発
明は、請求項1の発明において、槽内底部には、センタ
ウエルの廃水整流手段を介して流下される廃水中の凝集
沈殿を沈殿排出口へ導く沈殿誘導手段が設けられている
ことを特徴とする。
According to a second aspect of the present invention, in order to achieve the above object, the coagulated sediment in the wastewater flowing down through the wastewater rectification means of the center well is formed at the bottom of the tank. It is characterized in that a sedimentation guiding means for leading to the discharge port is provided.

【0012】請求項2の発明によっれば、センタウエル
より流下した廃水中の凝集沈殿は沈殿誘導手段にて沈殿
排出口に送られ、槽内より除去される。
According to the second aspect of the present invention, the coagulated sediment in the wastewater flowing down from the center well is sent to the sediment discharge port by the sedimentation induction means and removed from the tank.

【0013】前記課題を達成するための、請求項3の発
明は、請求項2の発明において、槽内底部の沈殿誘導手
段は凝集沈殿を槽内に巻き上げない程度の低速で移動さ
れることを特徴とする。
According to a third aspect of the present invention, in order to achieve the above object, in the second aspect of the present invention, the sedimentation inducing means at the bottom of the tank is moved at such a low speed that the coagulated sediment is not wound into the tank. Features.

【0014】請求項3の発明によれば、槽内の沈殿誘導
手段は低速移動させるので、センタウエルを出た凝集沈
殿を含む廃水は槽内底部において凝集沈殿を巻き上げる
ことなく、凝集沈殿をスムーズに排出口へ送ることがで
きる。
According to the third aspect of the present invention, since the sediment inducing means in the tank is moved at a low speed, the wastewater containing the coagulated sediment which has exited the center well can smoothly coagulate and sediment without rolling up the coagulated sediment at the bottom of the tank. Can be sent to the outlet.

【0015】[0015]

【発明の実施の形態】次に、本発明の実施の形態を図1
〜図7に基づいて説明する。まず、図1により凝集沈殿
分離装置1の構造を説明する。この分離装置1の槽本体
2は底面2Aが外方に突出した円錐形で上端が開口2B
とされた形状をなす。円錐形の底面2Aの中心部は沈殿
物の排出口3を兼ねた凹部4とされ、凹部4には沈殿物
抜取り管5が接続されている。槽本体2の開口2B付近
の内周面には処理水のオーバーフロー分を流入するため
の受け樋6が周設され、その一部には排水口7が設けら
れ、排出口7には排水管8が接続されている。
FIG. 1 shows an embodiment of the present invention.
This will be described with reference to FIG. First, the structure of the coagulation / sedimentation / separation apparatus 1 will be described with reference to FIG. The tank body 2 of the separation device 1 has a conical bottom surface 2A projecting outward and an upper end opening 2B.
And the shape. A central portion of the conical bottom surface 2A is a concave portion 4 also serving as a sediment discharge port 3, and a sediment extracting pipe 5 is connected to the concave portion 4. A drain gutter 6 is provided around the inner peripheral surface of the tank body 2 near the opening 2B for flowing the overflow of the treated water, and a drain port 7 is provided in a part of the drain gutter 6, and a drain pipe is provided in the discharge port 7. 8 are connected.

【0016】槽本体2内の中央には、筒体よりなるセン
タウエル10がその下部を槽本体2内の底部と連通させ
て縦向きに配置されている。センタウエル10の上端は
槽本体2の開口2Bに横設した桟部材11に固定されて
いる。なお、図2に示すように、センタウエル10上方
は桟部材11、中段桟部材11A、上段桟部材11Bの
三段構造にされている。
In the center of the tank body 2, a center well 10 formed of a cylindrical body is disposed vertically with its lower part communicating with the bottom of the tank body 2. The upper end of the center well 10 is fixed to a crosspiece 11 provided laterally in the opening 2B of the tank body 2. As shown in FIG. 2, the upper part of the center well 10 has a three-stage structure of a bar member 11, a middle bar member 11A, and an upper bar member 11B.

【0017】センタウエル10の上側部にはセンタウエ
ル10に廃水を導入するための廃水導管12(図4参
照。)の導入管部12Aが横設されている。なお廃水導
管12には廃水送りポンプ13(図4参照。)が介装さ
れ、廃水がセンタウエル10内に導入可能である。
On the upper side of the center well 10, an introduction pipe 12A of a waste water conduit 12 (see FIG. 4) for introducing waste water into the center well 10 is provided horizontally. The wastewater conduit 12 is provided with a wastewater feed pump 13 (see FIG. 4) so that wastewater can be introduced into the center well 10.

【0018】図1、図2に示すように、センタウエル1
0内には、槽本体2の開口2B上方より槽本体(2)の
底面2Aの凹部4に到る回転軸15が挿通され、凹部4
内の軸受け17と中段桟部材11Aに取付けた軸受け1
8により回転可能に軸支されている。
As shown in FIGS. 1 and 2, the center well 1
0, a rotary shaft 15 is inserted from above the opening 2B of the tank body 2 to the recess 4 of the bottom surface 2A of the tank body (2).
Bearing 17 and bearing 1 attached to middle stage member 11A
8 rotatably supported.

【0019】回転軸15の槽内底面付近には沈殿誘導手
段となる羽根体16が取付けられている。羽根体16は
底面2Aに近接して回転するように斜状に形成されてい
る。図2に示すように、回転軸15の上端部は上段桟部
材11Bに固定した両軸モータ20の下側の駆動軸20
Aにカップリング21を介して接続され、回転軸15は
両軸モータ20の駆動により低速で回転可能にされてい
る。
Near the bottom surface of the rotary shaft 15 in the tank, a blade 16 serving as a precipitation inducing means is attached. The blade 16 is formed obliquely so as to rotate close to the bottom surface 2A. As shown in FIG. 2, the upper end of the rotating shaft 15 is connected to the lower drive shaft 20 of the dual shaft motor 20 fixed to the upper rail member 11B.
A is connected to the motor A via a coupling 21, and the rotating shaft 15 is rotatable at a low speed by the drive of the double shaft motor 20.

【0020】また、図2に示すように、センタウエル1
0内の導入管部12Aの入口より下方位置には廃水撹拌
手段としての撹拌羽根23が配置されている。撹拌羽根
23は、回転軸15に外挿し上部を回転可能に支持した
回転筒22の下部に取付けられている。回転筒22の上
部は、図2に示すように、桟部材11上で軸受け24に
より支持され、上端には従動鎖車25が取付けられてい
る。
Further, as shown in FIG.
A stirring blade 23 as a waste water stirring means is disposed at a position below the inlet of the introduction pipe portion 12 </ b> A in the inside 0. The stirring blade 23 is attached to a lower part of a rotary cylinder 22 which is externally mounted on the rotary shaft 15 and has an upper part rotatably supported. As shown in FIG. 2, the upper part of the rotary cylinder 22 is supported by the bearing 24 on the crosspiece member 11, and the driven wheel 25 is attached to the upper end.

【0021】一方、図2に示すように、前記両軸モータ
20の一側には、たて向きの伝達軸26が上部固定部材
27及び桟部材11に取付けた軸受け28,29にて支
持されている。伝達軸26の上側鎖車30は両軸モータ
20の上側駆動軸20Bに取付けた駆動鎖車31とチェ
ン32にて回転可能に接続されている。また、伝達軸2
6の下側鎖車33は回転筒22の従動鎖車25にチェン
34により接続されている。なお、両軸モータ20の駆
動により回転筒22の撹拌羽根23の回転が、回転軸1
5の羽根体16より所定の高速回転されるように、駆動
鎖車31、上側鎖車30、下側鎖車33、従動鎖車25
のギヤ比が設定されている。両軸モータ20の回転によ
り回転軸15を介して羽根体16が低速回転され、回転
筒22を介して撹拌羽根23が高速回転される。
On the other hand, as shown in FIG. 2, on one side of the double-shaft motor 20, a vertically oriented transmission shaft 26 is supported by upper fixing members 27 and bearings 28 and 29 attached to the beam member 11. ing. An upper sprocket 30 of the transmission shaft 26 is rotatably connected to a drive sprocket 31 attached to an upper drive shaft 20B of the double shaft motor 20 by a chain 32. Also, transmission shaft 2
6 is connected to the driven wheel 25 of the rotating cylinder 22 by a chain 34. The rotation of the stirring blade 23 of the rotary cylinder 22 by the driving of the double shaft motor 20 causes the rotation of the rotary shaft 1.
The drive wheel 31, the upper wheel 30, the lower wheel 33, and the driven wheel 25 are rotated so as to rotate at a predetermined high speed from the blade body 16 of FIG.
Gear ratio is set. The rotation of the double-shaft motor 20 causes the blade 16 to rotate at a low speed via the rotary shaft 15, and the stirring blade 23 to rotate at a high speed via the rotary cylinder 22.

【0022】また、センタウエル10内の撹拌羽根23
の下方部には撹拌羽根23にて旋回される廃水を整流し
てセンタウエル10下端より流下させるための整流手段
36が取付けられている。整流手段36は、多数の流水
孔37〜37がたて向きに形成された厚板構造38より
なる。厚板構造38における流水孔37〜37の平面形
状は、たとえば、図3(A)の厚板構造38では格子形
の流水孔37A、図3(B)の厚板構造38ではハニカ
ム形の流水孔37B、図3(C)の厚板構造38では放
射状の流水孔37Cとなし得る。なお、図3(A)
(B)(C)におけるGは回転軸15の軸孔である。本
例では格子形の流水孔37A〜37Aのものが用いられ
ている。
The stirring blades 23 in the center well 10
A rectifying means 36 for rectifying waste water swirled by the stirring blades 23 and flowing down from the lower end of the center well 10 is attached to a lower portion of the center well. The flow straightening means 36 has a thick plate structure 38 in which a number of flowing water holes 37 to 37 are vertically formed. The planar shape of the flowing water holes 37 to 37 in the thick plate structure 38 is, for example, a lattice-shaped flowing water hole 37A in the thick plate structure 38 in FIG. 3A and a honeycomb-shaped flowing water in the thick plate structure 38 in FIG. The hole 37B and the thick plate structure 38 in FIG. 3C can be formed as radial water holes 37C. Note that FIG.
G in (B) and (C) is a shaft hole of the rotating shaft 15. In this example, grid-shaped water holes 37A to 37A are used.

【0023】前記した分離装置1の廃水導管12には凝
集剤の供給手段、pH調整のための薬剤供給手段が組付
けられている。図4に示すように、廃水導管12には流
量測定装置40が介装され、分離装置1に供給される廃
水量が測定可能である。
The wastewater conduit 12 of the separation apparatus 1 is provided with a coagulant supply means and a chemical supply means for pH adjustment. As shown in FIG. 4, a flow measuring device 40 is interposed in the wastewater conduit 12, and the amount of wastewater supplied to the separation device 1 can be measured.

【0024】一方、図4に示すように、廃水導管12の
近傍には無機凝集剤を入れた第1凝集剤槽42,pH調
整用アルカリ剤を入れたアルカリ槽44,pH調整用酸
剤を入れた酸槽46が配置され、各送りポンプ42A,
44A,46Aを介して各々供給導管42B,44B,
46Bが廃水送りポンプ13の吸込み側に導びかれ、各
薬剤が廃水導管12の廃水に供給可能にされている。
On the other hand, as shown in FIG. 4, a first coagulant tank 42 containing an inorganic coagulant, an alkali tank 44 containing an alkali agent for pH adjustment, and an acid agent for pH adjustment are provided near the waste water conduit 12. The inserted acid tank 46 is arranged, and each feed pump 42A,
Supply conduits 42B, 44B, 44A, 46A, respectively.
46B is led to the suction side of the wastewater feed pump 13 so that each chemical can be supplied to the wastewater in the wastewater conduit 12.

【0025】なお、廃水送りポンプ13の吐出側にはp
H測定装置48が配置され、廃水のpHを測定可能とさ
れ、この測定値により酸槽46の送りポンプ46Aが制
御され、廃水のpHが調整されるようになっている。ま
た、廃水送りポンプ13の吐出側近傍には高分子凝集剤
を入れた第2凝集剤槽50が配置され、送りポンプ50
Aを介して供給導管50Bにより高分子凝集剤が廃水道
管12の廃水に供給可能にされている。
The discharge side of the wastewater feed pump 13 has p
An H measuring device 48 is arranged to measure the pH of the wastewater, and the measured value controls the feed pump 46A of the acid tank 46 to adjust the pH of the wastewater. A second coagulant tank 50 containing a polymer coagulant is disposed near the discharge side of the wastewater feed pump 13.
The polymer flocculant can be supplied to the wastewater of the waste water pipe 12 through the supply conduit 50B via A.

【0026】次に、分離装置1の使用例を、図4、図5
を参照して説明する。いま、廃水導管12に介装した廃
水送りポンプ13及び分離装置1の両軸モータ20は作
動状態にされている。また、第1凝集剤槽42、アルカ
リ槽44、酸槽46、第2凝集剤槽50の各送りポンプ
42A,44A,46A,50Aも作動し得る状態にさ
れている。しかして、廃水導管12の廃水は流量測定装
置40にて流量が測定され、供給導管42B,44B,
46Bにより廃水に無機凝集剤、アルカリ剤、又は酸剤
が加えられる。次いで、pH測定装置48により、廃水
のpH測定がされた後、供給導管50Bにより高分子凝
集剤が加えられる。
Next, examples of use of the separation apparatus 1 will be described with reference to FIGS.
This will be described with reference to FIG. Now, the wastewater feed pump 13 interposed in the wastewater conduit 12 and the two-axis motor 20 of the separation device 1 are in an operating state. Further, the feed pumps 42A, 44A, 46A, 50A of the first coagulant tank 42, the alkali tank 44, the acid tank 46, and the second coagulant tank 50 are also in a state where they can be operated. Thus, the flow rate of the waste water in the waste water conduit 12 is measured by the flow measuring device 40, and the supply conduits 42B, 44B,
46B adds an inorganic coagulant, an alkaline agent, or an acid agent to the wastewater. Next, after the pH of the wastewater is measured by the pH measuring device 48, the polymer flocculant is added through the supply conduit 50B.

【0027】図5に示すように、各処理剤の加えられた
廃水Hは分離装置1の導入管部12Aよりセンタウエル
10内に導入される。センタウエル10に導入された廃
水Hは撹拌羽根23の高速回転により旋回されるため、
廃水H中の浮遊物等は凝集剤の凝集反応により凝集物T
となり廃水Hと共に旋回する。センタウエル10内には
順次廃水Hが導入されることにより、凝集物Tを含む廃
水Hは下方に流下され、整流手段36を通過して整流さ
れ、センタウエル10下部より槽内底部に排出される。
As shown in FIG. 5, the wastewater H to which each treatment agent has been added is introduced into the center well 10 through the introduction pipe 12A of the separation device 1. Since the wastewater H introduced into the center well 10 is swirled by the high-speed rotation of the stirring blade 23,
The suspended matter and the like in the wastewater H are aggregated T
And turns with wastewater H. By sequentially introducing the wastewater H into the center well 10, the wastewater H containing the aggregate T flows downward, is rectified through the rectifying means 36, and is discharged from the lower part of the center well 10 to the bottom of the tank. You.

【0028】次いで図5に示すように、凝集物Tを含む
廃水Hは槽内底部より、槽内周面とセンタウエル10外
周面との間を上昇する。この上昇する間において凝集物
Tは沈殿層となり分離され、凝集物Tの分離された廃水
Hは処理水Sとして上面をオーバーフローし、受け樋6
に入り、排水口7を介して排水管8により所定個所に送
られる。
Next, as shown in FIG. 5, the wastewater H containing the aggregate T rises between the inner peripheral surface of the tank and the outer peripheral surface of the center well 10 from the bottom of the tank. During the ascent, the aggregate T becomes a sedimentary layer and is separated, and the separated wastewater H of the aggregate T overflows the upper surface as the treated water S, and the receiving trough 6
And is sent to a predetermined location by a drain pipe 8 through a drain port 7.

【0029】一方、凝集物Tの沈殿は槽内底面の羽根体
16の低速回転により底面2Aの凹部4に導かれ、沈殿
物抜取り管5にて所定部所に排出される。
On the other hand, the sediment of the aggregate T is guided to the recess 4 of the bottom surface 2A by the low-speed rotation of the blade body 16 on the inner bottom surface of the tank, and is discharged to a predetermined portion by the sediment removal pipe 5.

【0030】この分離装置1はセンタウエル10内の上
部に撹拌羽根23を設け、その下方に整流手段36を設
けたので、図8に示す従来の撹拌槽101と同等の機能
をなし得る。この分離装置1はセンタウエル10内の上
部で撹拌することより、凝集剤の加えられた廃水は凝集
反応が促進され、生長した凝集物を含む廃水(処理水)
とすることができる。槽底面の羽根体16は低速回転で
あるから生成した凝集物を破壊することはない。また、
センタウエル10内の導入管部12Aから廃水の供給さ
れる部分は、部分的に水流の偏りが生ずるが、撹拌羽根
23により偏流を解消させることができる。
Since the separation device 1 has the stirring blades 23 provided in the upper part in the center well 10 and the rectification means 36 provided below the stirring blades 23, the same function as the conventional stirring tank 101 shown in FIG. By agitating the separation device 1 at the upper part in the center well 10, the agglutination reaction is promoted in the wastewater to which the flocculant is added, and the wastewater containing the agglomerated matter (treated water)
It can be. Since the blade body 16 on the bottom of the tank rotates at a low speed, the generated aggregates are not broken. Also,
In the portion of the center well 10 where the wastewater is supplied from the introduction pipe portion 12A, the water flow is partially biased, but the drift can be eliminated by the stirring blades 23.

【0031】撹拌羽根23による旋回水流は整流手段3
6により整流水として槽底部に流下させることができ、
凝集物を上方へ巻き上げることがない。また、羽根体1
6は低速回転であることより凝集物を巻き上げない。こ
のため、凝集物を良好に沈降させることができ、固液分
離を効果的になし得る。したがって、本実施形態の分離
装置1によれば装置全体を小型化することができる。
The swirling water flow generated by the stirring blades 23
6 allows the water to flow down to the bottom of the tank as rectified water,
Agglomerates do not roll up. In addition, the wing body 1
No. 6 does not wind up agglomerates due to low speed rotation. Therefore, aggregates can be favorably settled, and solid-liquid separation can be effectively performed. Therefore, according to the separation device 1 of the present embodiment, the entire device can be reduced in size.

【0032】センタウエル10内の整流手段36は撹拌
手段(撹拌羽根23)により生じる旋回流を消滅させ、
安定した均一な下降流とすることにより、固液分離処理
(凝集沈殿と処理水の分離)を効率化させる。なお、分
離槽のセンタウエル外に整流板を設けた、前述した
(イ)(ロ)の従来のものは、処理水の流速の遅い部位
に整流板を配置しているので、整流板に凝集物の付着や
その生長があり整流板を閉塞する不都合があった。本実
施の形態では流速の速いセンタウエル内下部に整流板を
設けるので従来の不都合が解消される。
The rectifying means 36 in the center well 10 eliminates the swirling flow generated by the stirring means (the stirring blade 23),
By making a stable and uniform downward flow, the solid-liquid separation treatment (separation of coagulated sediment and treated water) is made more efficient. In the above-mentioned conventional devices (a) and (b) in which a flow straightening plate is provided outside the center well of the separation tank, since the flow straightening plate is arranged at a portion where the flow rate of the treated water is low, the flow straightening plate is aggregated. There was an inconvenience that the current plate was closed due to the adhesion of the object and its growth. In the present embodiment, since the current plate is provided in the lower portion of the center well where the flow velocity is high, the conventional disadvantage is solved.

【0033】なお、流水孔37の孔径は100mm程
度、板厚は100mm以上が望ましい。安定した整流
(整水流)を得るには整流手段36の下方には整流手段
板厚の2倍以上の長さのセンタウエル部分を設けること
が望ましい。
It is preferable that the hole 37 has a diameter of about 100 mm and a thickness of 100 mm or more. In order to obtain a stable rectification (water flow), it is desirable to provide a center well portion having a length twice or more the thickness of the rectification means below the rectification means 36.

【0034】前記整流手段36は板状のものであったが
整流手段36は上部の旋回流を整流し得る適宜な構造を
採用することができる。たとえば図6(A)に示す、上
部に斜状の切欠部55Aを設けたたて向きの板片55を
センタウエル10の内周面に、図6(B)に示すよう
に、対称に配置したものとしてもよい。板片55は切欠
部55Aにより旋回流が徐々に減速し、凝集物の破壊を
せず、下方への整流を良好になし得る。なお、各板片5
5の大きさ、形状は、たとえば、幅がセンタウエル10
の内径の75〜100%程度、長さがセンタウエル10
の内径の100%以上、斜角は20〜30度程度、板片
55は4枚以上とすることが望ましい。この整流手段3
6を採用した図7の分離装置1のセンタウエル10も良
好な整流効果が得られる。
Although the rectifying means 36 has a plate shape, the rectifying means 36 may employ an appropriate structure capable of rectifying the upper swirling flow. For example, as shown in FIG. 6 (A), a vertically oriented plate piece 55 having an inclined cutout 55A provided on the upper side is symmetrically arranged on the inner peripheral surface of the center well 10 as shown in FIG. 6 (B). It may be done. The swirling flow of the plate piece 55 is gradually decelerated by the notch portion 55A, so that the aggregate is not broken and the downward flow can be satisfactorily performed. In addition, each plate piece 5
The size and shape of the center well 10 are, for example, the width of the center well 10.
About 75 to 100% of the inner diameter of the center well 10
, The oblique angle is about 20 to 30 degrees, and the number of the plate pieces 55 is desirably four or more. This rectification means 3
The center well 10 of the separation device 1 of FIG.

【0035】前記した実施の形態では凝集沈殿を排出口
3へ導く沈殿誘導手段としては槽底面付近を低速回転す
る羽根体16を用いたが、沈殿誘導手段は槽内底部の凝
集沈殿を巻き上げることなく、排出口3へ送り得る手段
を広く採用することができる。沈殿誘導手段は、たとえ
ば槽内底面付近を往復動する可動板であってもよい(図
示せず)。
In the above-described embodiment, the blade 16 that rotates at a low speed near the bottom of the tank is used as the precipitation inducing means for guiding the coagulated sediment to the discharge port 3, but the sedimentation inducing means is to wind up the coagulated sediment at the bottom in the tank. In addition, means that can be sent to the outlet 3 can be widely used. The precipitation inducing means may be, for example, a movable plate that reciprocates near the bottom surface in the tank (not shown).

【0036】[0036]

【発明の効果】本発明によれば、凝集沈殿と処理水の分
離が良好で小型化し得る分離装置が得られる。
According to the present invention, it is possible to obtain a separation apparatus which can separate coagulated sediment and treated water well and can be miniaturized.

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

【図1】本発明実施形態の分離装置の構造図である。FIG. 1 is a structural view of a separation device according to an embodiment of the present invention.

【図2】図1の主要部の拡大構造図である。FIG. 2 is an enlarged structural view of a main part of FIG.

【図3】整流構造の拡大斜視図であり、(A)は格子形
流水孔、(B)はハニカム形流水孔(C)は放射形流水
孔のものを示す。
FIGS. 3A and 3B are enlarged perspective views of a rectifying structure, in which FIG. 3A shows a grid type flowing water hole, FIG. 3B shows a honeycomb type flowing water hole, and FIG. 3C shows a radial type flowing water hole.

【図4】分離装置の使用状態図である。FIG. 4 is a diagram illustrating a use state of the separation device.

【図5】分離装置の作用図である。FIG. 5 is an operation diagram of the separation device.

【図6】整流構造の別例を示し、(A)は整流構造を構
成する整流板の斜視図、(B)は整流板配置状態を示す
センタウエル平断面図である。
6A and 6B show another example of the rectifying structure, in which FIG. 6A is a perspective view of a rectifying plate constituting the rectifying structure, and FIG. 6B is a plan view of a center well showing a rectifying plate arrangement state.

【図7】図5の整流板による整流構造を設けた分離装置
を示す断面図である。
FIG. 7 is a cross-sectional view illustrating a separation device provided with a rectifying structure using the rectifying plate of FIG.

【図8】従来の分離装置の使用状態図である。FIG. 8 is a diagram illustrating a use state of a conventional separation device.

【符号の説明】[Explanation of symbols]

1 (凝集沈殿)分離装置 2 槽本体 3 排出口 6 受け樋 7 排水口 10 センタウエル 12A 導入管部 15 回転軸 16 羽根体 20 両軸モータ 22 回転筒 23 撹拌羽根 36 整流手段 37 流水孔 38 厚板構造 55 板片 55A 切欠部 DESCRIPTION OF SYMBOLS 1 (Coagulation sedimentation) separation apparatus 2 Tank main body 3 Outlet 6 Receiving trough 7 Drainage outlet 10 Center well 12A Introducing pipe part 15 Rotating shaft 16 Blade body 20 Double shaft motor 22 Rotating cylinder 23 Stirring blade 36 Rectifying means 37 Flowing water hole 38 Thickness Plate structure 55 Plate piece 55A Notch

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 上方が開放された槽内に、底部が槽内に
連通するセンタウエルを備え、凝集剤を加えた廃水を凝
集沈殿と処理水に分離する槽構造の装置であって、前記
センタウエル内には上部より下部へ廃水導入手段、廃水
撹拌手段、廃水整流手段が設けられてなることを特徴と
した凝集沈殿分離装置。
1. An apparatus having a tank structure provided with a center well having a bottom portion communicating with the inside of a tank having an open top and separating wastewater containing a coagulant into coagulated sedimentation and treated water. A coagulation / sedimentation / separation apparatus characterized in that a wastewater introduction means, a wastewater stirring means, and a wastewater rectification means are provided in a center well from an upper part to a lower part.
【請求項2】 槽内底部には、センタウエルの廃水整流
手段を介して流下される廃水中の凝集沈殿を沈殿排出口
へ導く沈殿誘導手段が設けられていることを特徴とした
請求項1に記載の凝集沈殿分離装置。
2. A sedimentation guiding means for guiding coagulated sediment in wastewater flowing down through a wastewater rectification means of a center well to a sedimentation discharge port is provided at a bottom portion in the tank. 3. The coagulation sedimentation separation device according to item 1.
【請求項3】 槽内底部の沈殿誘導手段は凝集沈殿を槽
内に巻き上げない程度の低速で移動されることを特徴と
した請求項2に記載の凝集沈殿分離装置。
3. The coagulation / sedimentation separation apparatus according to claim 2, wherein the sedimentation guiding means at the bottom of the tank is moved at such a low speed that the coagulation sediment is not wound up in the tank.
JP2000247821A 2000-08-17 2000-08-17 Flocculating/separation equipment Pending JP2002058910A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000247821A JP2002058910A (en) 2000-08-17 2000-08-17 Flocculating/separation equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000247821A JP2002058910A (en) 2000-08-17 2000-08-17 Flocculating/separation equipment

Publications (1)

Publication Number Publication Date
JP2002058910A true JP2002058910A (en) 2002-02-26

Family

ID=18737835

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000247821A Pending JP2002058910A (en) 2000-08-17 2000-08-17 Flocculating/separation equipment

Country Status (1)

Country Link
JP (1) JP2002058910A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008246282A (en) * 2007-03-29 2008-10-16 Shinroku Seiki Kk Muddy water purifying separator
KR101307288B1 (en) * 2013-02-21 2013-09-11 대호산업 주식회사 Initial storm runoff particulate pollutant reduction device
JP2019198803A (en) * 2018-05-14 2019-11-21 オルガノ株式会社 Water treatment method and water treatment device
CN115253401A (en) * 2022-08-17 2022-11-01 同济大学 HRT and SRT separated organic solid waste anaerobic digestion reaction device

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2008246282A (en) * 2007-03-29 2008-10-16 Shinroku Seiki Kk Muddy water purifying separator
KR101307288B1 (en) * 2013-02-21 2013-09-11 대호산업 주식회사 Initial storm runoff particulate pollutant reduction device
JP2019198803A (en) * 2018-05-14 2019-11-21 オルガノ株式会社 Water treatment method and water treatment device
JP7026570B2 (en) 2018-05-14 2022-02-28 オルガノ株式会社 Water treatment method and water treatment equipment
CN115253401A (en) * 2022-08-17 2022-11-01 同济大学 HRT and SRT separated organic solid waste anaerobic digestion reaction device

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