JP3284225B2 - Coagulation sedimentation equipment - Google Patents

Coagulation sedimentation equipment

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Publication number
JP3284225B2
JP3284225B2 JP36300897A JP36300897A JP3284225B2 JP 3284225 B2 JP3284225 B2 JP 3284225B2 JP 36300897 A JP36300897 A JP 36300897A JP 36300897 A JP36300897 A JP 36300897A JP 3284225 B2 JP3284225 B2 JP 3284225B2
Authority
JP
Japan
Prior art keywords
sedimentation tank
tank
coagulation
raw water
pellets
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
JP36300897A
Other languages
Japanese (ja)
Other versions
JPH11169609A (en
Inventor
茂 吉田
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.)
Ebara Corp
Original Assignee
Ebara Corp
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 Ebara Corp filed Critical Ebara Corp
Priority to JP36300897A priority Critical patent/JP3284225B2/en
Priority to CN98100334A priority patent/CN1128649C/en
Publication of JPH11169609A publication Critical patent/JPH11169609A/en
Application granted granted Critical
Publication of JP3284225B2 publication Critical patent/JP3284225B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)

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】本発明は、上下水、産業廃水
その他の水処理に使用される凝集沈殿装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a coagulating sedimentation apparatus used for treating water and sewage, industrial wastewater and other water.

【0002】[0002]

【従来の技術】前記水処理にあっては、原水を沈殿池に
静置することで該原水の固液分離を図り、上方に溜まっ
た上澄み液を処理水として、底部に溜まった固体状の汚
泥を濃縮汚泥としてそれぞれ処理することが広く行われ
ている。近年、廃水の処理能力の増大等の必要性に答え
るため、無機凝集剤及び有機高分子凝集剤等を使用して
フロックを形成する凝集沈殿法を利用した高速凝集沈殿
装置が種々開発されている。更に、引抜き汚泥の処理を
行う上で、高濃度汚泥の排泥を必要とする場合には、濃
縮機構を付設することも広く行われている。
2. Description of the Related Art In the above-mentioned water treatment, the raw water is allowed to stand in a sedimentation basin to separate solid and liquid from the raw water. It is widely practiced to treat sludge as concentrated sludge. In recent years, various high-speed coagulation sedimentation apparatuses utilizing the coagulation sedimentation method of forming flocs using an inorganic coagulant and an organic polymer coagulant have been developed in order to respond to the necessity of increasing the treatment capacity of wastewater. . Further, when the treatment of the extracted sludge requires the discharge of high-concentration sludge, it is widely practiced to provide a thickening mechanism.

【0003】従来、この種の濃縮機構を備えた凝集沈殿
装置として、例えば、図2に示すようなものが知られて
いる。これは、いわゆる沈殿凝集槽と濃縮機構とを一体
としたもので、略円筒状の凝集沈殿槽1の内部に逆円錐
状の造粒沈殿槽2が配置されている。そして、前記造粒
沈殿槽2の内部に撹拌羽根3が回転自在に配置されて造
粒沈殿部4が形成されている。一方、凝集沈殿槽1の底
部に掻寄せ羽根5が回転自在に配置されて、造粒沈殿槽
で形成されたフロック又はペレットを圧密に濃縮し、圧
密なペレットを形成する濃縮部6が配置されている。更
に、前記造粒沈殿槽2の下部には流入管7が、凝集沈殿
槽1の底面には排泥管8が、凝集沈殿槽1の上端部に
は、処理水流出管9がそれぞれ接続されている。
Conventionally, for example, a coagulation-sedimentation apparatus having such a concentrating mechanism as shown in FIG. 2 is known. This has a so-called sedimentation flocculation tank and a concentration mechanism integrated, and an inverted conical granulation sedimentation tank 2 is disposed inside a substantially cylindrical coagulation sedimentation tank 1. A stirring blade 3 is rotatably arranged inside the granulation settling tank 2 to form a granulation settling section 4. On the other hand, a scraper blade 5 is rotatably arranged at the bottom of the coagulation sedimentation tank 1, and a concentrating unit 6 for condensing the flocs or pellets formed in the granulation sedimentation tank to form a compact pellet is arranged. ing. Further, an inflow pipe 7 is connected to the lower part of the granulation and sedimentation tank 2, a sludge discharge pipe 8 is connected to the bottom of the coagulation and sedimentation tank 1, and a treated water outflow pipe 9 is connected to an upper end of the coagulation and sedimentation tank 1. ing.

【0004】これにより、有機高分子凝集剤等を注入し
た原水を流入管7から造粒沈殿槽2内に導き、この内部
の撹拌羽根3を回転させて原水と有機高分子凝集剤等と
を撹拌させることで、フロック群、更にはこれらのフロ
ックの内部の水を絞り出して圧密化した緻密なペレット
が生成される。そして、生成されたフロック又はペレッ
トを造粒凝集槽2の上端2aからオーバーフローさせ、
このオーバーフローしたフロック又はペレットを凝集沈
殿槽1の底部に堆積させて更に沈降濃縮させ、同時に、
掻寄せ羽根5を回転させることで、圧密なペレットを形
成し、このペレットを中央部に掻き寄せて、中央部に配
設された排泥管8から外部に排出するようになってい
る。
The raw water into which the organic polymer flocculant and the like have been injected is guided from the inflow pipe 7 into the granulation sedimentation tank 2, and the stirring blade 3 inside the raw water is rotated to separate the raw water from the organic polymer flocculant and the like. By agitating, flocks, and furthermore, water inside these flocks is squeezed out to produce compacted and dense pellets. Then, the generated flocs or pellets overflow from the upper end 2a of the granulation and aggregation tank 2,
The overflowed flocs or pellets are deposited on the bottom of the coagulation sedimentation tank 1 and further settled and concentrated.
By rotating the raking blades 5, compact pellets are formed, the pellets are raked toward the center, and are discharged to the outside from a mud pipe 8 provided at the center.

【0005】ここに、前記造粒凝集槽2の内部には、前
記緻密なペレットにより高濃度で安定したブランケット
層が形成され、原水は、このブランケット層を通過する
間に濾過され、この濾過後の凝集沈殿槽1の上部に溜ま
った上澄み液は、処理水流出管9から外部に排出され処
理水として処理される。
[0005] Here, a high concentration and stable blanket layer is formed by the dense pellets in the inside of the granulation and aggregation tank 2, and the raw water is filtered while passing through the blanket layer. The supernatant liquid collected in the upper part of the coagulation sedimentation tank 1 is discharged outside from the treated water outflow pipe 9 and treated as treated water.

【0006】[0006]

【発明が解決しようとする課題】しかしながら、上記従
来例にあっては、例えば浮遊物濃度(SS)が50pp
m以下の原水に対しては、所望の処理を行うことができ
るものの、例えば浮遊物濃度が100ppmを超える原
水を処理しようとすると、造粒凝集槽の上端からオーバ
ーフローするペレットが濃縮され過ぎて、該造粒凝集槽
と凝集沈殿槽部との間に詰まって、この処理に支障を来
してしまうことがある。
However, in the above conventional example, for example, the suspended solids concentration (SS) is 50 pp.
m or less, for raw water, although the desired treatment can be performed, for example, when trying to treat raw water having a suspended matter concentration of more than 100 ppm, pellets overflowing from the upper end of the granulation and coagulation tank are too concentrated, Clogging may occur between the granulation and coagulation tank and the coagulation and sedimentation tank, which may hinder this treatment.

【0007】なお、造粒沈殿槽と濃縮槽とを互いに並設
し、造粒沈殿槽からオーバーフローしたペレットを該造
粒沈殿槽に隣接した濃縮槽内に導くようにした、いわゆ
る横置き型のものも知られているが、このような横置き
型のものにあっては、広い設置スペースが必要となると
いう問題がある。
A so-called horizontal type in which a granulation settling tank and a concentration tank are arranged in parallel with each other, and pellets overflowing from the granulation settling tank are guided into a concentration tank adjacent to the granulation settling tank. Although there is also known a horizontal type, there is a problem that a large installation space is required.

【0008】本発明は上記事情に鑑みて為されたもの
で、濃縮機構を備えた一体型で、浮遊物濃度が、例えば
100ppm以上の原水であっても、この処理を確実に
行うことができる、コンパクトな構造で且つ効率的な水
処理が可能な凝集沈殿装置を提供することを目的とす
る。
The present invention has been made in view of the above circumstances, and is an integral type having a concentration mechanism, and can reliably perform this treatment even if the concentration of suspended solids is, for example, 100 ppm or more of raw water. It is an object of the present invention to provide a coagulating sedimentation apparatus having a compact structure and capable of efficient water treatment.

【0009】[0009]

【課題を解決するための手段】本発明の凝集沈殿装置
は、沈殿槽内の上部に配置され凝集剤を添加した原水を
沈降することでフロックを形成する仕切壁内に配置され
た造粒凝集部と、該造粒凝集部の下方開口部の下側に配
置された傘状の分散板と、該傘状の分散板の側方の沈殿
槽内壁に配設されたバッフル板と、沈殿槽内の底部に配
置され沈降した濃縮凝集物を撹拌して更に濃縮する濃縮
機構と、沈殿槽上部に配置された溢流部とを備えたこと
を特徴とする。
The coagulation and sedimentation apparatus of the present invention comprises a granulation and coagulation apparatus disposed in an upper part of a sedimentation tank and disposed in a partition wall for forming flocs by sedimenting raw water to which a coagulant is added. Part, an umbrella-shaped dispersion plate disposed below the lower opening of the granulation aggregation part, a baffle plate disposed on the inner wall of the sedimentation tank beside the umbrella-shaped dispersion plate, and a sedimentation tank It is characterized by comprising a concentrating mechanism arranged at the bottom of the inside to stir and further concentrate the settled concentrated aggregates, and an overflow portion arranged at the top of the sedimentation tank.

【0010】上述した本発明によれば、槽上部に配置さ
れた造粒凝集部で形成されたフロックを、凝集沈殿槽中
間部に配置された傘状分散板と整流板とにより形成され
たブランケット層を通過させることで固液分離を促進
し、固化した凝集物を凝集沈殿槽底部に沈降させて掻寄
せ機にて掻き寄せ、濃密なペレットとして取出すことが
できる。従って、凝集沈殿槽上部から圧入された凝集剤
を含む原水が下方に進むにつれて造粒沈殿され、造粒凝
集部を通過後に凝集沈殿槽中間部のブランケット層を通
過することで濃密化されたペレットと上澄み液とに分離
され、ペレットは凝集沈殿槽底部に配置された濃縮機構
に落下して濃縮され、更に濃密なペレットとして取出さ
れる。又、緻密なブランケット層を通過して原水が濾過
されるので、きれいな上澄み液が得られ、槽上部より排
出される。それ故、従来の凝集沈殿装置のような凝集物
の通過の隘路となる部分がないので、縦型のコンパクト
な構造で且つ原水の汚物濃度が高くても、安定に濃密な
ペレットを生成することができる。
According to the present invention described above, the floc formed by the granulation / aggregation section arranged at the upper part of the tank is replaced with the blanket formed by the umbrella-shaped dispersion plate and the rectifying plate arranged at the middle part of the aggregation / sedimentation tank. By passing through the layer, solid-liquid separation is promoted, and the solidified aggregates are settled at the bottom of the coagulation sedimentation tank, scraped by a scraper, and taken out as dense pellets. Therefore, the raw water containing the coagulant injected from the upper part of the coagulation sedimentation tank is granulated and precipitated as it proceeds downward, and after passing through the granulation coagulation part, the pellets are densified by passing through the blanket layer in the middle part of the coagulation sedimentation tank. The pellets are separated into a supernatant and a supernatant, and the pellets fall into a concentrating mechanism arranged at the bottom of the coagulation sedimentation tank, are concentrated, and are taken out as dense pellets. Further, since the raw water is filtered through the dense blanket layer, a clear supernatant liquid is obtained and discharged from the upper part of the tank. Therefore, since there is no portion that becomes a bottleneck for the passage of the coagulated material as in the conventional coagulating sedimentation apparatus, it is possible to stably produce dense pellets even with a vertical compact structure and a high concentration of contaminated raw water. Can be.

【0011】[0011]

【発明の実施の形態】以下、本発明の実施の形態を図1
を参照して説明する。
FIG. 1 is a block diagram showing an embodiment of the present invention.
This will be described with reference to FIG.

【0012】この実施の形態は、原水に無機凝集剤を添
加して混合した後、この無機凝集剤の付着活性力により
繊維状の凝集物を生成し、その後有機高分子凝集剤を注
入することで造粒するようにした例を示している。図示
するように、底部に原水流入管10を接続した混合槽1
1が備えられ、原水流入管10から混合槽11内に流入
した原水に無機凝集剤が注入され、原水がこの混合槽1
1内を上方に向けて螺旋状に流れる間に該原水と無機凝
集剤とが混合し、繊維状の凝集物が生成される。
In this embodiment, after adding and mixing an inorganic coagulant to raw water, a fibrous aggregate is generated by the adhesive activity of the inorganic coagulant, and then an organic polymer coagulant is injected. This shows an example in which granulation is carried out. As shown, a mixing tank 1 having a raw water inflow pipe 10 connected to the bottom thereof.
An inorganic coagulant is injected into the raw water flowing into the mixing tank 11 from the raw water inflow pipe 10, and the raw water is supplied to the mixing tank 1.
The raw water and the inorganic coagulant are mixed while spirally flowing upward in 1, and fibrous aggregates are generated.

【0013】この混合槽11の側方には、略円筒状の凝
集沈殿槽12が設置され、この凝集沈殿槽12の内部に
造粒凝集部である略円筒状の仕切壁13が同心状に配置
されている。そして、前記仕切壁13の内部と前記混合
槽11の内部とは、それらの上部において流入管14で
互いに連通され、混合槽11で繊維状の凝集物が生成さ
れた原水は仕切壁13の内部に圧入されるようになって
いる。この流入管14の途中に有機高分子凝集剤注入用
の注入口15が設けられている。これにより、無機凝集
剤が添加されて繊維状の凝集物が沈殿された原水は、流
入管14内を流れ、この途中で有機高分子凝集剤が注入
されて、仕切壁13内に導入される。そして仕切壁13
内を沈降する過程で粒状の沈殿物が生成されるように構
成されている。
A substantially cylindrical coagulation sedimentation tank 12 is provided on the side of the mixing tank 11, and a substantially cylindrical partition wall 13, which is a granulation aggregation part, is concentrically formed inside the coagulation sedimentation tank 12. Are located. The inside of the partition wall 13 and the inside of the mixing tank 11 are communicated with each other at an upper portion thereof by an inflow pipe 14, and the raw water in which fibrous aggregates are generated in the mixing tank 11 is inside the partition wall 13. To be press-fitted. An injection port 15 for injecting the organic polymer flocculant is provided in the middle of the inflow pipe 14. As a result, the raw water in which the inorganic coagulant is added and the fibrous coagulate is precipitated flows in the inflow pipe 14, and the organic polymer coagulant is injected in the middle thereof and introduced into the partition wall 13. . And the partition 13
It is configured such that a granular sediment is generated in the process of sedimentation in the inside.

【0014】即ち、前記仕切壁13の内部には、第1の
回転軸21と第2の回転軸22とが同心状に配置され、
これらの各回転軸21,22は、モータ23を介して個
々に駆動されるようなっている。ここに、前記仕切壁1
3の内部に位置して、前記第1の回転軸21には、放射
状に突出する予撹拌羽根31が取付けられている。これ
により、前記有機高分子凝集剤が注入された原水を、こ
れが仕切壁13の内部から回転体25の円筒体28の内
部を沈降する間に、特に有機凝集剤の作用により、原水
に含まれる繊維状凝集物が粒状の凝集沈殿物(フロッ
ク)に成長する造粒沈殿が行われる。この間、撹拌羽根
31で撹拌して、フロックの生成を促進することができ
る。
That is, a first rotating shaft 21 and a second rotating shaft 22 are arranged concentrically inside the partition wall 13.
These rotary shafts 21 and 22 are individually driven via a motor 23. Here, the partition wall 1
3, a pre-mixing blade 31 is attached to the first rotating shaft 21 so as to protrude radially. As a result, the raw water into which the organic polymer flocculant has been injected is contained in the raw water by the action of the organic flocculant, in particular, while the raw water is settling from the inside of the partition wall 13 to the inside of the cylindrical body 28 of the rotating body 25. Granulation sedimentation in which the fibrous aggregate grows into a granular aggregate sediment (floc) is performed. During this time, the generation of flocs can be promoted by stirring with the stirring blades 31.

【0015】前記第1の回転軸21には、第1の撹拌羽
根24aと第2の撹拌羽根24bを有する回転体25
が、前記第2の回転軸22には、前記回転体25の下方
に位置して傘状の分散板26がそれぞれ連結され、更に
この傘状の分散板26に対向して、端部を凝集沈殿槽1
2の内周面に固着した放射状のバッフル板27が配置さ
れている。
The first rotating shaft 21 has a rotating body 25 having a first stirring blade 24a and a second stirring blade 24b.
However, an umbrella-shaped dispersing plate 26 is connected to the second rotating shaft 22 below the rotating body 25, and further, the ends are aggregated in opposition to the umbrella-shaped dispersing plate 26. Settling tank 1
A radial baffle plate 27 fixed to the inner peripheral surface of the second baffle 2 is disposed.

【0016】前記回転体25には、前記仕切壁13から
下方に延出する円筒体28が備えられて、この円筒体2
8の外周面に前記第1の撹拌羽根24aと第2の撹拌羽
根24bが設けられている。そして、前記傘状の分散板
26は、下方に開いた傘状に形成されている。
The rotating body 25 is provided with a cylindrical body 28 extending downward from the partition wall 13.
8 is provided with the first stirring blade 24a and the second stirring blade 24b. The umbrella-shaped dispersion plate 26 is formed in an umbrella shape opened downward.

【0017】これにより、前記有機高分子凝集剤により
形成されたフロックを含む原水は、仕切壁13の内部か
ら回転体25の円筒部28の内部を流れ、その下方に位
置する傘状分散板26に衝突してバッフル板27の上方
に向けて流される。その後、凝集沈殿槽12の内壁及び
その周辺に配設されたバッフル板27に衝突してはね返
る。そして、撹拌羽根24a,24bの回転に伴って撹
拌されて、この傘状の分散板26とバッフル板27の上
方に、フロック群、更にはフロックに含まれる内部の水
を絞り出して圧密化した緻密なペレット群が生成され、
ここにこの緻密なペレット群による高密度で安定したブ
ランケット層30が形成される。
As a result, the raw water containing flocs formed by the organic polymer flocculant flows from the inside of the partition wall 13 to the inside of the cylindrical portion 28 of the rotating body 25, and the umbrella-shaped dispersion plate 26 And flows toward the upper side of the baffle plate 27. After that, it collides with the baffle plate 27 arranged on the inner wall of the coagulation sedimentation tank 12 and its periphery, and rebounds. Then, the water is stirred with the rotation of the stirring blades 24a and 24b, and the flock group and the water contained in the flock are squeezed out above the umbrella-shaped dispersing plate 26 and the baffle plate 27, and are compacted. Pellet group is generated,
Here, a dense and stable blanket layer 30 is formed by the dense pellet group.

【0018】仕切壁13内を沈降してくる多量のフロッ
クを含む原水は、傘状分散板26に衝突し、側方に流さ
れ、更に凝集沈殿槽12の内壁及びバッフル板27に衝
突する。また、回転する撹拌板24a,24bにより撹
拌される。これにより固液分離が進行し、濃密化したペ
レットは、下方に落下し、水は緻密なペレット群からな
るブランケット層30を通過して凝集沈殿槽上部に上昇
する。
The raw water containing a large amount of floc settled in the partition wall 13 collides with the umbrella-shaped dispersion plate 26, flows to the side, and further collides with the inner wall of the coagulation sedimentation tank 12 and the baffle plate 27. Further, the mixture is stirred by the rotating stirring plates 24a and 24b. As a result, solid-liquid separation proceeds, and the dense pellets fall downward, and water passes through the blanket layer 30 composed of a group of dense pellets and rises to the upper part of the coagulation sedimentation tank.

【0019】ここに、前述のように、前記傘状の分散板
26とバッフル板27の上部には、緻密なペレットによ
る高密度で安定したブランケット層30が形成されてい
るため、原水は、このブランケット層30を通過する間
に濾過されて、この濾過後の上澄み液が処理水排水管5
2から外部に排出されることになる。
As described above, a high-density and stable blanket layer 30 made of dense pellets is formed on the umbrella-shaped dispersion plate 26 and the baffle plate 27. It is filtered while passing through the blanket layer 30 and the supernatant liquid after the filtration is treated water drainage pipe 5
2 to the outside.

【0020】即ち、前記凝縮沈殿槽12の上端部には、
凝縮沈殿槽12の上部に溜まった上澄み液を処理水とし
て外部に排出するため、水排出用の樋50と溢流堰51
が設けられているとともに、処理水排水管52が備えら
れている。上澄み液は、溢流堰51を越えて樋50に流
入し、更に処理水排水管52から外部に排出される。
尚、前記溢流堰51の下方には、仕切壁13の保持を兼
ねた整流板53が配置され、上昇してくる上澄み液を整
流すると共に、仕切壁13を凝集沈殿槽内に保持、固定
している。
That is, at the upper end of the condensation and settling tank 12,
In order to discharge the supernatant liquid accumulated in the upper part of the condensation and sedimentation tank 12 to the outside as treated water, a water discharge gutter 50 and an overflow weir 51 are provided.
Are provided, and a treated water drainage pipe 52 is provided. The supernatant liquid flows into the gutter 50 over the overflow weir 51, and is further discharged from the treated water drain pipe 52 to the outside.
In addition, below the overflow weir 51, a rectifying plate 53 which also serves to hold the partition wall 13 is arranged, rectifies the rising supernatant liquid, and holds and fixes the partition wall 13 in the coagulation sedimentation tank. are doing.

【0021】一方、前記凝集沈殿槽12の底部には、濃
縮部40が設けられている。即ち、前記第2の回転軸2
2を更に下方に延出させ、この下端に掻寄せ羽根41を
連結するとともに、掻寄せ羽根41の下方にこの下面に
沿った形状の底板42を配置している。
On the other hand, a concentrating unit 40 is provided at the bottom of the coagulation / sedimentation tank 12. That is, the second rotating shaft 2
2 is further extended downward, a raking blade 41 is connected to the lower end, and a bottom plate 42 along the lower surface is arranged below the raking blade 41.

【0022】これにより、濃縮されたペレットは、自由
落下により凝集沈殿槽12の底部の底板42上に堆積し
て沈降濃縮され、この濃縮されたペレット(濃縮汚泥)
が掻寄せ羽根41の回転に伴って、撹拌されると共に、
中央に掻き寄せられる。この時、濃縮されたペレット
は、凝集沈殿槽内の略全面から供給されるため、従来技
術のようにこのペレットによって該ペレットの流路が詰
まってしまうことはない。前記底板42には、前述のよ
うにして掻き寄せられた濃縮汚泥を外部に排出する排泥
管43が接続されており、底板42の中央部に掻き寄せ
られた濃縮汚泥は、排泥管43から外部に排出される。
As a result, the concentrated pellets are deposited on the bottom plate 42 at the bottom of the coagulation sedimentation tank 12 by free fall, settled and concentrated, and the concentrated pellets (condensed sludge).
Are stirred along with the rotation of the raking blades 41,
It is rushed to the center. At this time, since the concentrated pellets are supplied from almost the entire surface in the coagulation sedimentation tank, the flow path of the pellets is not blocked by the pellets as in the related art. The bottom plate 42 is connected to a sludge pipe 43 for discharging the concentrated sludge scraped as described above to the outside. The concentrated sludge scraped to the center of the bottom plate 42 is connected to the sludge pipe 43. Is discharged to the outside.

【0023】尚、以上の実施形態においては、凝集沈殿
槽の略中間部に配置した傘状分散板と槽内壁に配置した
バッフル板とにより、仕切壁内を沈降してくるフロック
を含む原水を分散させることで、緻密なブランケット層
を形成している。しかしながら、凝集沈殿槽中間部のブ
ランケット層の形成は、傘状分散板とバッフル板と同一
の作用を奏するもので代用可能である。
In the above embodiment, the umbrella-shaped dispersion plate disposed substantially in the middle of the coagulation and sedimentation tank and the baffle plate disposed on the inner wall of the tank separates the raw water containing floc that has settled in the partition wall. By dispersing, a dense blanket layer is formed. However, the formation of the blanket layer in the middle part of the coagulation sedimentation tank can be replaced with the one having the same action as the umbrella-shaped dispersion plate and the baffle plate.

【0024】[0024]

【発明の効果】以上に説明したように、本発明によれ
ば、浮遊物濃度が、例えば100ppm以上の原水であ
っても、緻密なペレットで該ペレットの流路が詰まって
しまうことを防止して、汚泥の濃縮処理を確実に行うこ
とができる。しかも、濃縮機構を備えた一体型とするこ
とで、小型コンパクト化を図ることができる。
As described above, according to the present invention, even if the concentration of suspended solids is, for example, raw water having a concentration of 100 ppm or more, it is possible to prevent the flow path of the pellets from being clogged with dense pellets. Thus, the sludge concentration treatment can be reliably performed. In addition, the size and the size can be reduced by using the integral type including the concentration mechanism.

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

【図1】本発明の実施の形態を示す凝集沈殿装置の断面
図。
FIG. 1 is a cross-sectional view of a coagulation and sedimentation apparatus showing an embodiment of the present invention.

【図2】従来の凝集沈殿装置の概略断面図。FIG. 2 is a schematic sectional view of a conventional coagulation and sedimentation apparatus.

【符号の説明】[Explanation of symbols]

11 混合槽 12 凝集沈殿槽 13 仕切壁 20 造粒凝集部 21,22 回転軸 24a,24b 撹拌羽根 25 回転体 26 傘状の分散板 27 バッフル板 30 ブランケット層 31,32 撹拌羽根 40 濃縮部 41 掻寄せ羽根 42 底板 DESCRIPTION OF SYMBOLS 11 Mixing tank 12 Aggregation sedimentation tank 13 Partition wall 20 Granulation aggregation part 21,22 Rotating shaft 24a, 24b Stirring blade 25 Rotating body 26 Umbrella-shaped dispersion plate 27 Baffle plate 30 Blanket layer 31, 32 Stirring blade 40 Thickening part 41 Scratching Wings 42 bottom plate

───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) B01D 21/00 - 21/34 ──────────────────────────────────────────────────続 き Continued on front page (58) Field surveyed (Int. Cl. 7 , DB name) B01D 21/00-21/34

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 沈殿槽内の上部に配置され凝集剤を添加
した原水を沈降することでフロックを形成する仕切壁内
に配置された造粒凝集部と、該造粒凝集部の下方開口部
の下側に配置された傘状の分散板と、該傘状の分散板の
側方の沈殿槽内壁に配設されたバッフル板と、沈殿槽内
の底部に配置され沈降した濃縮凝集物を撹拌して更に濃
縮する濃縮機構と、沈殿槽上部に配置された溢流部とを
備えたことを特徴とする凝集沈殿装置。
1. A granulating and aggregating part disposed in an upper part of a sedimentation tank and forming a floc by forming a floc by settling raw water to which a flocculant is added, and a lower opening of the granulating and aggregating part. An umbrella-shaped dispersion plate disposed on the lower side, a baffle plate disposed on the inner wall of the sedimentation tank on the side of the umbrella-shaped dispersion plate, and a concentrated agglomerate disposed and settled at the bottom of the sedimentation tank A coagulation sedimentation apparatus comprising: a concentration mechanism for stirring and further concentrating; and an overflow portion disposed above the sedimentation tank.
JP36300897A 1997-12-12 1997-12-12 Coagulation sedimentation equipment Expired - Lifetime JP3284225B2 (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP36300897A JP3284225B2 (en) 1997-12-12 1997-12-12 Coagulation sedimentation equipment
CN98100334A CN1128649C (en) 1997-12-12 1998-01-15 Condensing precipitator

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP36300897A JP3284225B2 (en) 1997-12-12 1997-12-12 Coagulation sedimentation equipment

Publications (2)

Publication Number Publication Date
JPH11169609A JPH11169609A (en) 1999-06-29
JP3284225B2 true JP3284225B2 (en) 2002-05-20

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JP (1) JP3284225B2 (en)
CN (1) CN1128649C (en)

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Also Published As

Publication number Publication date
CN1128649C (en) 2003-11-26
CN1219439A (en) 1999-06-16
JPH11169609A (en) 1999-06-29

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