JP2000325705A - Flocculating settling apparatus - Google Patents

Flocculating settling apparatus

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Publication number
JP2000325705A
JP2000325705A JP11138546A JP13854699A JP2000325705A JP 2000325705 A JP2000325705 A JP 2000325705A JP 11138546 A JP11138546 A JP 11138546A JP 13854699 A JP13854699 A JP 13854699A JP 2000325705 A JP2000325705 A JP 2000325705A
Authority
JP
Japan
Prior art keywords
tank
flow velocity
coagulation
sedimentation
cyclone
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
Application number
JP11138546A
Other languages
Japanese (ja)
Other versions
JP3901392B2 (en
Inventor
Tomoaki Miyanoshita
友明 宮ノ下
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.)
Organo Corp
Original Assignee
Organo Corp
Japan Organo Co Ltd
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 Organo Corp, Japan Organo Co Ltd filed Critical Organo Corp
Priority to JP13854699A priority Critical patent/JP3901392B2/en
Publication of JP2000325705A publication Critical patent/JP2000325705A/en
Application granted granted Critical
Publication of JP3901392B2 publication Critical patent/JP3901392B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

PROBLEM TO BE SOLVED: To facilitate the maintenance of and reduce the running cost of a flocculating settling apparatus by minimizing the wear of a discharge line in such a manner that an intermediate receiver is equipped in the discharge line, and that a low flow rate passage is set from a settling vessel to the intermediate receiver and a high flow rate passage from the intermediate receiver to a cyclone. SOLUTION: Suspended substances in raw water are flocculated as flocculated substances containing an inorganic fluocculant 6, a high molecular flocculant 8 and sand 9 in a flocculating vessel 2 equipped with an agitator 11 driven by a motor 10. The water to treat is introduced into a settling vessel 3 through a weir 12, and precipitates 13 are separated from the upper water to treat. A discharge line 18 which discharge the precipitates 13 and which separates into sludge 17 and the sand 9 by a cyclone 16, and which feeds back the sand 9, is connected with the bottom of the settling vessel 3. Then discharge line 18 is provided with an intermediate receiver 19 storing the precipitates 13. A low flow rate passage 20 is provided from the settling vessel 3 to the intermediate receiver 19, and a high flow rate passage 21 from the receiver 19 to the cyclone 16.

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、原水中の懸濁物質
を凝集沈澱により汚泥と処理水とに分離する凝集沈澱装
置に関し、とくに、沈澱工程後の沈澱物の搬送ラインの
構造の改良に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a coagulation sedimentation apparatus for separating suspended substances in raw water into sludge and treated water by coagulation sedimentation, and more particularly, to an improvement in the structure of a sediment transport line after a sedimentation step. .

【0002】[0002]

【従来の技術】原水中に懸濁している物質(以下、SS
[Suspended Solid] と称することもある。)を沈澱によ
り分離除去する装置が知られている。従来の原水中のS
Sを除去するための凝集沈澱装置として、原水に単に凝
集剤を添加して凝集物を沈澱させ、凝集物を汚泥として
引き抜くとともに上部から処理水を導出するようにした
装置はよく知られている。
2. Description of the Related Art Substances suspended in raw water (hereinafter referred to as SS
Sometimes called [Suspended Solid]. Is known. S in conventional raw water
As a coagulation sedimentation apparatus for removing S, an apparatus is known which simply adds a coagulant to raw water to precipitate coagulation, pulls out the coagulation as sludge, and discharges treated water from the upper part. .

【0003】このような一般的な凝集沈澱装置では、凝
集物の沈澱に長時間を要し、沈澱槽としても極めて大型
のものが要求されることから、より効率よく凝集沈澱を
行わせるようにした凝集沈澱装置が提案されている。
In such a general coagulation / sedimentation apparatus, it takes a long time to settle the coagulates, and an extremely large sedimentation tank is required. A coagulating sedimentation apparatus has been proposed.

【0004】たとえばフランス特許第1411792号
には、凝集槽において、原水に凝集剤とともに粒状物
(代表的には、砂)を添加し、凝集槽内を攪拌して、原
水中のSSを比重の大きい粒状物を含んだ比較的大きな
フロックとして凝集させ、沈澱槽において凝集槽から導
入された被処理水中のフロックを沈澱させて処理水と分
離する凝集沈澱装置が開示されている。沈澱槽から引き
抜かれた沈澱フロックは、分離器としてのサイクロンに
より汚泥と粒状物とに分離され、分離された粒状物は凝
集槽に戻されて循環使用される。
[0004] For example, French Patent No. 1411172 discloses that in a coagulation tank, a granular material (typically, sand) is added to raw water together with a coagulant, and the inside of the coagulation tank is stirred to reduce SS in the raw water to a specific gravity. There is disclosed a coagulation / sedimentation apparatus which coagulates as relatively large flocs containing large particulate matter, sediments the flocs in the water to be treated introduced from the coagulation tank in the sedimentation tank, and separates them from the treated water. The sediment floc pulled out of the sedimentation tank is separated into sludge and particulate matter by a cyclone as a separator, and the separated particulate matter is returned to the flocculation tank and used for circulation.

【0005】この凝集沈澱装置は、たとえば図2のよう
に構成されている。図2においては、原水101にたと
えば無機凝集剤102が添加されてラインミキサー10
3により混合され、凝集槽104で高分子凝集剤105
とともに粒状物としての砂106が添加され、凝集槽1
04内で攪拌機107で攪拌されつつ原水中のSSが凝
集され、砂106を含む比重の大きな沈澱しやすいフロ
ックに成長される。成長した砂含有のフロックを含む被
処理水が沈澱槽108に導入されるので、フロックはよ
り効率よく迅速に沈澱し、沈澱物109はより短時間で
処理水110と分離できるようになる。沈澱槽108の
底部に沈澱した沈澱物109は汚泥引抜ポンプ111に
より引き抜かれ、引き抜きライン112(輸送管)を通
してサイクロン113に送られ、サイクロン113での
遠心分離によって汚泥114と砂106とに分離され、
分離された砂106が凝集槽104に戻されて循環使用
されるようになっている。
[0005] This coagulation-sedimentation apparatus is constructed, for example, as shown in FIG. In FIG. 2, for example, an inorganic coagulant 102 is added to raw water 101 and a line mixer 10 is added.
3 and the polymer flocculant 105 in the flocculation tank 104.
And sand 106 as granular material is added to the coagulation tank 1
The SS in the raw water is agglomerated while being stirred by the stirrer 107 in the inside 04, and grows into flocs containing the sand 106 and having a large specific gravity and easy to precipitate. Since the water to be treated containing the grown sand-containing flocs is introduced into the sedimentation tank 108, the flocs precipitate more efficiently and quickly, and the precipitates 109 can be separated from the treated water 110 in a shorter time. The sediment 109 that has settled at the bottom of the sedimentation tank 108 is drawn by a sludge drawing pump 111, sent to a cyclone 113 through a drawing line 112 (transportation pipe), and separated into sludge 114 and sand 106 by centrifugation in the cyclone 113. ,
The separated sand 106 is returned to the coagulation tank 104 and used for circulation.

【0006】[0006]

【発明が解決しようとする課題】ところが、上記のよう
な凝集沈澱装置においては、沈澱槽108から引き抜か
れた、砂106を含む沈澱物は、サイクロン113を用
いて汚泥114と砂106とに遠心分離されるため、高
流速でサイクロン113に送られる必要がある。また、
輸送のための汚泥引き抜きポンプ111には、高い吐出
圧でかつ、高流速で吐出できるポンプを使用する必要が
ある。
However, in the coagulating sedimentation apparatus as described above, the sediment containing the sand 106 extracted from the sedimentation tank 108 is centrifuged into the sludge 114 and the sand 106 using the cyclone 113. Since they are separated, they need to be sent to the cyclone 113 at a high flow rate. Also,
It is necessary to use a pump capable of discharging at a high discharge pressure and a high flow rate as the sludge extraction pump 111 for transportation.

【0007】そのため、砂106を含む沈澱物は、引き
抜きライン112中を、高圧、高流速でサイクロン11
3に輸送されることになる。砂106を含む沈澱物がポ
ンプ111や引き抜きライン112の管内を高圧、高流
速で輸送されると、砂106による研磨作用が起こり、
ポンプ111のシール部分やインペラ、引き抜きライン
112の曲がり管部分等では、摩耗が進行し、望ましく
ない損傷が比較的短期間のうちに発生するおそれがあ
る。その結果、特にこれらの部位における部品の交換頻
度が高くなり、メンテナンス作業上、ランニングコスト
上問題となっている。
[0007] Therefore, the sediment containing the sand 106 flows through the drawing line 112 at high pressure and high flow rate in the cyclone 11.
3 will be transported. When the sediment containing the sand 106 is transported at high pressure and high flow rate in the pipes of the pump 111 and the drawing line 112, a polishing action by the sand 106 occurs,
At the seal portion of the pump 111, the impeller, the bent tube portion of the drawing line 112, etc., the abrasion proceeds, and undesirable damage may occur in a relatively short period of time. As a result, the frequency of replacement of parts especially at these parts increases, which causes problems in maintenance work and running costs.

【0008】管の摩耗に対しては、硬度の高い材質を用
いるなどの対策も考えられるが、設備費の高騰を招くと
ともに、損傷に至るまでの時間が多少延長されるだけ
で、根本的な解決策にはならない。
[0010] Countermeasures such as using a material having high hardness can be considered for the wear of the pipe. However, the cost of equipment is soared, and the time required until the damage is slightly prolonged. It is not a solution.

【0009】そこで本発明の課題は、上記のような問題
点に着目し、沈澱槽からの沈澱物の引き抜き分離ライン
の構成を根本的に改良し、摩耗、損傷の発生を抑制して
その寿命を大幅に延長し、部品の交換頻度および交換量
を大幅に低減してメンテナンスの容易化、ランニングコ
ストの低減を達成できる凝集沈澱装置を提供することに
ある。
Accordingly, an object of the present invention is to focus on the problems described above, and to fundamentally improve the structure of a separation line for extracting a precipitate from a sedimentation tank to suppress the occurrence of abrasion and damage to reduce the life of the line. The present invention is to provide a coagulation sedimentation apparatus that can greatly reduce the frequency and amount of replacement of parts, thereby facilitating maintenance and reducing running costs.

【0010】[0010]

【課題を解決するための手段】上記課題を解決するため
に、本発明の凝集沈澱装置は、原水中の懸濁物質を凝集
剤と粒状物の添加により凝集させる凝集槽と、凝集槽か
ら導入される被処理水中の凝集物を沈澱させ処理水と沈
澱物とに分離する沈澱槽と、沈澱槽から沈澱物を引き抜
き、引き抜かれた沈澱物を汚泥と粒状物とに分離するサ
イクロンを備え、分離された粒状物を凝集槽に戻す引き
抜き分離ラインとを備えた凝集沈澱装置において、引き
抜き分離ライン中に、中間受け槽を設けるとともに、引
き抜き分離ラインの沈澱槽から中間受け槽までを低流速
流路に、中間受け槽からサイクロンまでを高流速流路に
構成したことを特徴とするものからなる。
SUMMARY OF THE INVENTION In order to solve the above-mentioned problems, a coagulation / sedimentation apparatus according to the present invention comprises a coagulation tank for coagulating a suspended substance in raw water by adding a coagulant and particulate matter, and a coagulation tank. A sedimentation tank for sedimenting aggregates in the treated water to be separated into treated water and sediment, a cyclone for extracting the sediment from the sedimentation tank, and separating the extracted sediment into sludge and particulate matter, A coagulating sedimentation device having a drawing separation line for returning the separated particulate matter to the coagulation tank, an intermediate receiving tank is provided in the drawing separation line, and a low flow rate is set between the sedimentation tank and the intermediate receiving tank of the drawing separation line. The path is configured such that a path from the intermediate receiving tank to the cyclone is formed as a high flow velocity flow path.

【0011】上記低流速流路における流速と高流速流路
における流速との比としては、1:2以上であることが
好ましく、より好ましくは1:3以上、さらに好ましく
は1:5以上である。また、低流速流路における管内流
速としては、1.5m/s以下であることが好ましく、
より好ましくは1m/s以下、さらに好ましくは0.5
m/s以下、とくに好ましくは0.1m/s以下であ
る。
The ratio of the flow velocity in the low flow velocity flow path to the flow velocity in the high flow velocity flow path is preferably 1: 2 or more, more preferably 1: 3 or more, and further preferably 1: 5 or more. . Further, the flow velocity in the pipe in the low flow velocity channel is preferably 1.5 m / s or less,
More preferably 1 m / s or less, further preferably 0.5 m / s
m / s or less, particularly preferably 0.1 m / s or less.

【0012】中間受け槽の形態は特に限定しないが、大
気開放型の槽からなることが好ましい。大気開放型の中
間受け槽とすることで、その上下流側に位置する低流速
流路と高流速流路との縁を一旦完全に切ることができる
ので、各流路が互いに影響し合うことなく、各流路をそ
れぞれ独立に望ましい流速の流路に構成できる。
Although the form of the intermediate receiving tank is not particularly limited, it is preferable that the intermediate receiving tank be an open-to-air tank. By using an open-to-atmosphere intermediate receiving tank, the edges of the low-flow channel and the high-flow channel located on the upstream and downstream sides can be cut completely once, so that each channel affects each other. Instead, each channel can be independently configured as a channel having a desired flow rate.

【0013】各流路においてそれぞれ好ましい流速とす
るために、低流速流路には低速輸送用ポンプが、高流速
流路には高速輸送用ポンプが、各々設けられる。低速輸
送用ポンプには、上記のような低流速流路における望ま
しい管内流速を達成できるポンプが選択され、高速輸送
用ポンプには、基本的には、サイクロンでの遠心分離が
可能な流速を達成できるポンプが選択される。
In order to obtain a preferable flow rate in each flow path, a low-speed flow path is provided with a low-speed transport pump, and a high-speed flow rate pump is provided in the high-flow rate flow path. As the low-speed transport pump, a pump capable of achieving the desired flow rate in the pipe in the low-velocity flow path as described above is selected, and the high-speed transport pump basically achieves a flow rate capable of performing centrifugal separation in a cyclone. Pumps that can be selected are selected.

【0014】凝集フロック生成用に用いる粒状物として
は、代表的には砂を使用することができ、とくに粒径を
揃えたものが好ましい。また、凝集剤としては、通常、
無機凝集剤と高分子凝集剤を使用することができる。無
機凝集剤は、原水中の懸濁物質を効率よく凝集させるこ
とができ、高分子凝集剤は、無機凝集剤によって生成し
た微細な凝集フロックをさらにポリマーを絡めてより大
きなフロックへと成長させる。この成長したフロック内
に、比重の大きい砂等からなる粒状物が混在し、全体と
して比重(密度)の大きい沈澱しやすいフロックが形成
されることになる。
As the granular material used for the generation of the flocculated floc, sand can be typically used, and those having a uniform particle size are particularly preferable. Also, as a coagulant, usually,
Inorganic and polymeric flocculants can be used. The inorganic flocculant can efficiently flocculate the suspended substance in the raw water, and the polymer flocculant grows fine flocculated flocs generated by the inorganic flocculant into larger flocs by further entanglement of the polymer. Granules made of sand or the like having a large specific gravity are mixed in the grown flocks, and flocs having a large specific gravity (density) and easy to precipitate are formed as a whole.

【0015】上記のような本発明に係る凝集沈澱装置に
おいては、沈澱槽からの引き抜き分離ライン中に中間受
け槽が設けられ、引き抜き分離ラインが中間受け槽の部
分で一旦分割されて、沈澱槽から中間受け槽までが低流
速流路に、中間受け槽からサイクロンまでが高流速流路
に構成される。低流速流路においては、粒状物含有の沈
澱物が低速で輸送されるから、従来問題であった、ポン
プの摩耗や輸送管の管内摩耗が大幅に軽減される。ま
た、高流速流路においては、基本的にはサイクロンでの
遠心分離に必要な流速が要求されるが、引き抜き分離ラ
イン全長が中間受け槽の部分で一旦分割されていること
から、この高流速流路は容易に短い管に構成され、しか
も、実質的に直管のみで構成することも可能である。し
たがって、高い管内流速は要求されるものの、高圧は必
要でなく、従来の圧力に比べ、大幅に低下させた圧力で
よくなる。その結果、高流速流路においても、ポンプの
摩耗や輸送管の管内摩耗の大幅な低減が可能になる。す
なわち、引き抜き分離ラインの全体にわたって、粒状物
輸送に起因する摩耗の低減が可能になる。
In the coagulating sedimentation apparatus according to the present invention as described above, an intermediate receiving tank is provided in a separation line for drawing out from the sedimentation tank. From the intermediate receiving tank to the cyclone is configured as a high flow rate channel. In the low flow velocity flow path, the precipitate containing the particulate matter is transported at a low speed, so that the conventional problems of wear of the pump and abrasion of the transport pipe are greatly reduced. In addition, the high flow velocity flow path basically requires a flow velocity necessary for centrifugal separation in a cyclone. However, since the entire length of the drawing separation line is once divided at the intermediate receiving tank, this high flow velocity flow path is required. The flow path is easily formed into a short pipe, and may be formed substantially only with a straight pipe. Therefore, although a high flow velocity in the pipe is required, a high pressure is not required, and the pressure can be reduced to a value significantly lower than the conventional pressure. As a result, even in the high flow velocity flow path, the wear of the pump and the wear in the transport pipe can be significantly reduced. That is, it is possible to reduce abrasion caused by transport of particulate matter over the entire drawing separation line.

【0016】したがって、引き抜き分離ラインの各部の
寿命は大幅に延長され、部品の交換頻度や配管等の交換
量は格段に低減され、メンテナンスが大幅に容易化され
るとともに、装置のランニングコストも大幅に低減され
る。
Therefore, the life of each part of the pull-out separation line is greatly extended, the frequency of replacement of parts and the amount of replacement of piping and the like are greatly reduced, maintenance is greatly facilitated, and the running cost of the apparatus is also greatly increased. To be reduced.

【0017】[0017]

【発明の実施の形態】以下に、本発明の望ましい実施の
形態について、図面を参照して説明する。図1は、本発
明の一実施態様に係る凝集沈澱装置1を示している。凝
集沈澱装置1は、凝集槽2と、それに隣接配置された沈
澱槽3を備えている。凝集槽2には、原水供給ライン4
を介して原水5が供給され、本実施態様では、無機凝集
剤6がライン注入される。無機凝集剤6の注入位置の下
流側には、スタティックミキサー等からなるラインミキ
サー7が介装されており、注入された凝集剤が原水に良
好に混合されるようになっている。ただし、この無機凝
集剤6は、凝集槽2に直接投入することも可能である。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Preferred embodiments of the present invention will be described below with reference to the drawings. FIG. 1 shows a coagulation / sedimentation apparatus 1 according to one embodiment of the present invention. The coagulation / sedimentation apparatus 1 includes a coagulation tank 2 and a sedimentation tank 3 disposed adjacent thereto. The coagulation tank 2 has a raw water supply line 4
The raw water 5 is supplied via a line, and in the present embodiment, the inorganic coagulant 6 is injected into the line. A line mixer 7 composed of a static mixer or the like is interposed downstream of the injection position of the inorganic coagulant 6, so that the injected coagulant is mixed well with the raw water. However, the inorganic coagulant 6 can be directly charged into the coagulation tank 2.

【0018】凝集槽2には、高分子凝集剤8と粒状物と
しての砂9が添加される。この高分子凝集剤8は、ライ
ン注入することも可能であり、たとえば、上記ミキサー
7の下流側でライン注入することができる。凝集槽2に
は、モータ10によって駆動される攪拌機11が設けら
れており、攪拌機11による攪拌によって原水中の懸濁
物質が、無機凝集剤6、高分子凝集剤8、砂9を含むフ
ロックとして凝集される。
The coagulation tank 2 is added with a polymer coagulant 8 and sand 9 as a granular material. The polymer flocculant 8 can be injected in a line, for example, in a line downstream of the mixer 7. The flocculation tank 2 is provided with a stirrer 11 driven by a motor 10, and the suspended substance in the raw water is stirred by the stirrer 11 to form a floc containing the inorganic coagulant 6, the polymer coagulant 8, and the sand 9. Agglomerated.

【0019】無機凝集剤6としては、たとえばポリ塩化
アルミニウム(PAC)、塩化第二鉄、硫酸第二鉄を使
用でき、高分子凝集剤8としては、たとえばノニオン
性、アニオン性あるいは両性の高分子凝集剤を用いるこ
とができる。アニオン性の高分子凝集剤としては、たと
えば、アクリル酸またはその塩の重合物、アクリル酸ま
たはその塩とアクリルアミドとの共重合物、アクリルア
ミドと2−アクリルアミド−2メチルプロパンスルホン
酸塩の共重合物、アクリル酸またはその塩とアクリルア
ミドと2−アクリルアミド−2−メチルプロパンスルホ
ン酸塩の3元共重合物、ポリアクリルアミドの部分加水
分解物などが挙げられるが、特にこれらに限定されるも
のではない。ノニオン性の高分子凝集剤としては、代表
的なものとしてポリアクリルアミドが挙げられるが、特
にこれに限定されるものではない。両性の高分子凝集剤
としては、たとえば、ジメチルアミノエチル(メタ)ア
クリレートの3級塩および4級塩(塩化メチル塩等)等
の少なくとも1種のカチオン性単量体と、アクリル酸お
よびその塩(ナトリウム、カルシウム等の塩類)、2−
アクリルアミド−2−メチルプロパンスルホン酸塩(ナ
トリウム、カルシウム等の塩類)等の少なくとも1種の
アニオン性単量体の共重合物、あるいは、上記の少なく
とも1種のカチオン性単量体および上記の少なくとも1
種のアニオン性単量体とアクリルアミド等の少なくとも
1種のノニオン性単量体との三元もしくは四元以上の共
重合物等が挙げられるが、特にこれらに限定されるもの
ではない。高分子凝集剤の分子量の範囲は特に限定され
ないが、500万〜2000万の範囲が好ましい。これ
らの高分子凝集剤は、単独で又は混合物として用いるこ
とができる。高分子凝集剤の添加量は、一般的に経済的
な観点から0.3〜2mg/l程度である。
As the inorganic coagulant 6, for example, polyaluminum chloride (PAC), ferric chloride, and ferric sulfate can be used. As the polymer coagulant 8, for example, a nonionic, anionic or amphoteric polymer can be used. Flocculants can be used. Examples of the anionic polymer coagulant include a polymer of acrylic acid or a salt thereof, a copolymer of acrylic acid or a salt thereof and acrylamide, and a copolymer of acrylamide and 2-acrylamido-2-methylpropanesulfonic acid salt And a tertiary copolymer of acrylic acid or a salt thereof, acrylamide and 2-acrylamido-2-methylpropanesulfonate, and a partial hydrolyzate of polyacrylamide, but are not particularly limited thereto. A typical nonionic polymer flocculant includes polyacrylamide, but is not particularly limited thereto. Examples of the amphoteric polymer flocculant include at least one cationic monomer such as a tertiary salt and a quaternary salt of dimethylaminoethyl (meth) acrylate (eg, a methyl chloride salt), acrylic acid and a salt thereof. (Salts such as sodium and calcium), 2-
A copolymer of at least one anionic monomer such as acrylamide-2-methylpropanesulfonate (salts such as sodium and calcium), or at least one of the above cationic monomers and at least one of the above 1
Ternary or quaternary or higher copolymers of at least one kind of anionic monomer and at least one kind of nonionic monomer such as acrylamide are exemplified, but not particularly limited thereto. The range of the molecular weight of the polymer flocculant is not particularly limited, but is preferably in the range of 5,000,000 to 20,000,000. These polymer flocculants can be used alone or as a mixture. The addition amount of the polymer flocculant is generally about 0.3 to 2 mg / l from an economic viewpoint.

【0020】この凝集槽2内での凝集においては、無機
凝集剤6が懸濁物質を凝集させて微細なフロックを生成
させ、それに高分子凝集剤8が絡まってより大きなフロ
ックに成長させ、成長したフロックには比重の大きい粒
状物としての砂9が含有され、全体として比較的大き
な、比重の大きい沈澱しやすいフロックに成長する。
In the coagulation in the coagulation tank 2, the inorganic coagulant 6 coagulates the suspended substance to form fine flocs, and the polymer coagulant 8 becomes entangled to grow into larger flocs. The resulting floc contains sand 9 as a particulate matter having a large specific gravity, and as a whole, grows into a relatively large floc having a large specific gravity and easy to precipitate.

【0021】成長した凝集フロックを含む被処理水は、
本実施態様では、水中ぜき12(もぐりぜき)を介して
沈澱槽3へと導入される。この水中ぜき12の代わりに
越流ぜきを用いてもよい。沈澱槽3では、導入水中の凝
集フロックが下方に沈澱され、沈澱物13は上方の処理
水14に対して分離される。沈澱槽3内の上部には、複
数の傾斜板15が並設されており、処理水14とともに
フロック(沈澱物)が流出するのを抑制している。
The water to be treated containing the grown flocculants is
In the present embodiment, the water is introduced into the precipitation tank 3 through a submerged weir 12. An overflow weir may be used in place of the underwater weir 12. In the settling tank 3, flocculated flocs in the introduced water are settled downward, and the precipitate 13 is separated from the treated water 14 above. A plurality of inclined plates 15 are juxtaposed at the upper part in the sedimentation tank 3 to prevent the floc (sediment) from flowing out together with the treated water 14.

【0022】沈澱槽3の底部には、沈澱槽3からスラリ
ー状の沈澱物13を引き抜き、引き抜かれた沈澱物13
を、サイクロン16による遠心分離によって、汚泥17
と砂9とに分離し、分離された砂9を凝集槽2に戻す引
き抜き分離ライン18が接続されている。分離された砂
9は、再び凝集槽2内に戻されて循環使用される。
At the bottom of the sedimentation tank 3, a slurry-like precipitate 13 is withdrawn from the sedimentation tank 3, and the withdrawn sediment 13
Is separated from the sludge 17 by centrifugation using a cyclone 16.
And a drawing / separation line 18 for returning the separated sand 9 to the coagulation tank 2. The separated sand 9 is returned to the flocculation tank 2 again and used for circulation.

【0023】この引き抜き分離ライン18中には、一旦
輸送されてきた沈澱物13を収容する中間受け槽19が
設けられている。そして、沈澱槽3から中間受け槽19
までは、管内流速のより遅い低流速流路20に、中間受
け槽19からサイクロン16までは、管内流速のより速
い高流速流路21に、それぞれ構成されている。この流
速差は、低流速流路20に設けた低速輸送用ポンプ22
と、高流速流路21に設けた高速輸送用ポンプ23によ
ってもたらされる。
In the drawing separation line 18, there is provided an intermediate receiving tank 19 for storing the precipitate 13 once transported. And, from the settling tank 3 to the intermediate receiving tank 19
Up to, a low flow velocity channel 20 having a lower flow velocity in the pipe is formed, and from the intermediate receiving tank 19 to the cyclone 16, a high flow velocity flow path 21 having a higher flow velocity in the pipe is formed. This flow velocity difference is caused by the low speed transport pump 22 provided in the low flow velocity flow path 20.
Is provided by the high-speed transport pump 23 provided in the high flow velocity channel 21.

【0024】低流速流路20における流速と高流速流路
21における流速との比としては、前述の如く、1:2
以上であることが好ましく、より好ましくは1:3以
上、さらに好ましくは1:5以上である。また、低流速
流路20における管内流速としては、1.5m/s以下
であることが好ましく、より好ましくは1m/s以下、
さらに好ましくは0.5m/s以下、とくに好ましくは
0.1m/s以下である。たとえば、後述の実施例に示
すように、低流速流路20における管内流速が0.05
m/s程度に、高流速流路21における管内流速が、従
来流速と同じ3m/s程度に設定されることが好まし
い。
As described above, the ratio of the flow velocity in the low flow velocity flow path 20 to the flow velocity in the high flow velocity flow path 21 is 1: 2.
It is preferably at least 1: 3, more preferably at least 1: 3, even more preferably at least 1: 5. Further, the flow velocity in the pipe in the low flow velocity channel 20 is preferably 1.5 m / s or less, more preferably 1 m / s or less,
It is more preferably at most 0.5 m / s, particularly preferably at most 0.1 m / s. For example, as shown in an example described later, the flow velocity in the pipe in the low flow velocity flow path 20 is 0.05
Preferably, the flow velocity in the pipe in the high flow velocity channel 21 is set to about 3 m / s, which is the same as the conventional flow velocity.

【0025】中間受け槽19は、本実施態様では大気開
放型の槽に構成されているが、密閉型の槽に構成するこ
とも可能である。この中間受け槽19の配設位置は、極
力サイクロン16に近い位置が好ましい。サイクロン1
6に近接した位置に中間受け槽19を配置することで、
高流速流路21の流路長を短く抑えることができ、場合
によっては、高流速流路21を実質的に短い直管のみで
構成することも可能になる。
In the present embodiment, the intermediate receiving tank 19 is configured as a tank that is open to the atmosphere, but it may be configured as a closed tank. The position of the intermediate receiving tank 19 is preferably a position as close to the cyclone 16 as possible. Cyclone 1
By arranging the intermediate receiving tank 19 at a position close to 6,
The flow path length of the high flow velocity flow path 21 can be kept short, and in some cases, the high flow velocity flow path 21 can be composed of only a substantially short straight pipe.

【0026】上記のように構成された凝集沈澱装置1に
おいては、沈澱槽3から引き抜かれた沈澱物13は、ま
ず、低速輸送用ポンプ22により、低流速流路20中を
低管内流速をもって中間受け槽19へと輸送される。低
流速でよいので、低流速流路20中における管内摩耗は
大幅に軽減され、低速輸送用ポンプ22におけるシール
部や本体部の摩耗も小さく抑えられる。
In the coagulating sedimentation apparatus 1 constructed as described above, the sediment 13 withdrawn from the sedimentation tank 3 is first passed through the low-speed transport pump 22 through the low-velocity flow path 20 at a low pipe flow rate. It is transported to the receiving tank 19. Since a low flow rate is sufficient, wear in the pipe in the low flow rate flow path 20 is significantly reduced, and wear of the seal portion and the main body of the low-speed transport pump 22 is also reduced.

【0027】また、高流速流路21における管内流速
は、基本的には、サイクロン16での遠心分離に必要な
流速が要求される。しかし、引き抜き分離ライン18が
中間受け槽19で一旦縁が切られ、中間受け槽19から
サイクロン16に至る高流速流路21は短い流路でよい
ので、高流速で輸送しても、輸送に要する負荷は比較的
低く抑えられ、したがって、発生する圧力も比較的低く
抑えられる。すなわち、この高流速流路21において
は、サイクロン16での遠心分離に必要な高流速を達成
しつつ、比較的低圧に保つことが可能になる。その結
果、高流速流路21における管内摩耗もまた大幅に軽減
され、高速輸送用ポンプ23におけるシール部や本体部
の摩耗も小さく抑えられることになる。
In addition, the flow velocity in the pipe in the high flow velocity flow path 21 is basically required to be a flow velocity required for centrifugal separation in the cyclone 16. However, the drawing separation line 18 is once cut off in the intermediate receiving tank 19, and the high flow velocity channel 21 from the intermediate receiving tank 19 to the cyclone 16 may be a short flow path. The required load is kept relatively low, and thus the pressure generated is kept relatively low. That is, in the high flow velocity channel 21, it is possible to maintain a relatively low pressure while achieving a high flow velocity required for centrifugation in the cyclone 16. As a result, abrasion in the pipe in the high flow velocity channel 21 is also greatly reduced, and wear of the seal portion and the main body portion in the high-speed transport pump 23 is also reduced.

【0028】本発明による効果を確認するために、図1
に示した本発明に係る装置および図2に示した従来装置
を用いて、以下のような条件で実験を行った。
In order to confirm the effect of the present invention, FIG.
An experiment was performed under the following conditions using the apparatus according to the present invention shown in FIG. 1 and the conventional apparatus shown in FIG.

【0029】実験条件 〔従来装置と本発明に係る装置での共通条件〕 ・原水流量:300m3 /day(12.5m3 /h) ・沈澱槽負荷:処理水上昇速度50m/h ・凝集用砂:ケイ砂、比重2.5、有効径0.1mm、
凝集槽内添加量20g/l ・原水濁度:12度 ・原水pH:7.1 ・無機凝集剤:PAC 10mg/l ・高分子凝集剤:アニオン系有機高分子 1mg/l
(ポリアクリルアミド系アニオン性ポリマー) ・汚泥引き抜き量:原水流量に対して5%(10.4リ
ットル/min)
[0029] [common condition in apparatus according to the conventional apparatus and the present invention] Experimental Conditions raw water flow rate: 300m 3 /day(12.5m 3 / h) · settling tank Load: treated water rising rate 50 m / h, for agglomeration Sand: silica sand, specific gravity 2.5, effective diameter 0.1mm,
Addition amount in coagulation tank 20g / l Raw water turbidity: 12 degrees Raw water pH: 7.1 Inorganic coagulant: PAC 10mg / l Polymer coagulant: anionic organic polymer 1mg / l
(Polyacrylamide-based anionic polymer) Sludge withdrawal amount: 5% (10.4 liter / min) with respect to raw water flow rate

【0030】〔従来装置における汚泥輸送条件〕 ・砂分離装置:サイクロン ・汚泥輸送装置:高速砂輸送ポンプ、砂輸送量5.2リ
ットル/min、管内流速3m/s ・高速砂輸送管長:6m
[Sludge transport conditions in conventional apparatus]-Sand separator: cyclone-Sludge transporter: High-speed sand transport pump, sand transport rate 5.2 l / min, flow velocity in pipe 3 m / s-High-speed sand transport pipe length: 6 m

【0031】〔本発明に係る装置における汚泥輸送条
件〕 ・砂分離装置:サイクロン ・中間受け槽:汚泥滞留時間1min ・低流速流路:低速砂輸送ポンプ、輸送量5.2リット
ル/min、管内流速0.05m/s ・高流速流路:高速砂輸送ポンプ、輸送量5.2リット
ル/min、管内流速3/s、輸送管長1m
[Sludge transport conditions in the apparatus according to the present invention] Sand separator: cyclone Intermediate receiving tank: Sludge residence time 1 min Low flow velocity flow path: Low-speed sand transport pump, transport volume 5.2 l / min, inside pipe Flow velocity: 0.05 m / s-High flow velocity flow path: High-speed sand transport pump, transport volume: 5.2 l / min, flow velocity in pipe: 3 / s, transport pipe length: 1 m

【0032】上記条件で実験を実施し、主として管の交
換量(長さの累計)について、本発明装置と従来装置と
を比較した。結果を表1に示す。表1から分かるよう
に、本発明装置においては、管の交換量が大幅に低減し
た。また、ポンプシール部の交換頻度、ポンプ本体(イ
ンペラ等)の交換頻度についても、本発明装置では大幅
に低減できた。
Experiments were carried out under the above conditions, and the apparatus of the present invention and the conventional apparatus were compared mainly with respect to the exchange amount of tubes (cumulative length). Table 1 shows the results. As can be seen from Table 1, in the device of the present invention, the exchange amount of the tube was greatly reduced. Further, the replacement frequency of the pump seal portion and the replacement frequency of the pump main body (impeller and the like) were significantly reduced by the apparatus of the present invention.

【0033】[0033]

【表1】 [Table 1]

【0034】[0034]

【発明の効果】以上説明したように、本発明の凝集沈澱
装置によれば、引き抜き分離ラインに中間受け槽を設け
てラインを分割し、沈澱槽から中間受け槽までを低流速
流路に、中間受け槽からサイクロンまでを高流速流路に
構成したので、低流速流路においては管、ポンプの摩耗
を著しく低減でき、高流速流路においても圧力を低下さ
せて管、ポンプの摩耗を大幅に低減でき、引き抜き分離
ライン全体として、摩耗の発生を低減して、各部の交換
頻度、交換量を大幅に低減することができる。その結
果、メンテナンスの容易化はもちろんのこと、ランニン
グコストの大幅な低減を達成できる。
As described above, according to the coagulation / sedimentation apparatus of the present invention, the drawing / separation line is provided with an intermediate receiving tank, and the line is divided. Since the high-speed flow path from the intermediate receiving tank to the cyclone is configured, the wear of pipes and pumps can be significantly reduced in low-flow rate flow paths, and the pressure is also reduced in high-flow rate flow paths to greatly reduce pipe and pump wear. The occurrence of abrasion is reduced as a whole of the pull-out separation line, and the replacement frequency and replacement amount of each part can be greatly reduced. As a result, not only can maintenance be facilitated, but also running costs can be significantly reduced.

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

【図1】本発明の一実施態様に係る凝集沈澱装置の全体
構成図である。
FIG. 1 is an overall configuration diagram of a coagulation / sedimentation apparatus according to an embodiment of the present invention.

【図2】従来の凝集沈澱装置の概略構成図である。FIG. 2 is a schematic configuration diagram of a conventional coagulation / sedimentation apparatus.

【符号の説明】[Explanation of symbols]

1 凝集沈澱装置 2 凝集槽 3 沈澱槽 4 原水供給ライン 5 原水 6 無機凝集剤 7 ラインミキサー 8 高分子凝集剤 9 粒状物としての砂 10 モータ 11 攪拌機 12 せき 13 沈澱物 14 処理水 15 傾斜板 16 サイクロン 17 汚泥 18 引き抜き分離ライン 19 中間受け槽 20 低流速流路 21 高流速流路 22 低速輸送用ポンプ 23 高速輸送用ポンプ DESCRIPTION OF SYMBOLS 1 Coagulation sedimentation apparatus 2 Coagulation tank 3 Sedimentation tank 4 Raw water supply line 5 Raw water 6 Inorganic coagulant 7 Line mixer 8 Polymer coagulant 9 Granular sand 10 Motor 11 Stirrer 12 Cough 13 Precipitate 14 Treated water 15 Inclined plate 16 Cyclone 17 Sludge 18 Extraction separation line 19 Intermediate receiving tank 20 Low flow velocity channel 21 High flow velocity flow path 22 Low speed pump 23 High speed pump

Claims (7)

【特許請求の範囲】[Claims] 【請求項1】 原水中の懸濁物質を凝集剤と粒状物の添
加により凝集させる凝集槽と、凝集槽から導入される被
処理水中の凝集物を沈澱させ処理水と沈澱物とに分離す
る沈澱槽と、沈澱槽から沈澱物を引き抜き、引き抜かれ
た沈澱物を汚泥と粒状物とに分離するサイクロンを備
え、分離された粒状物を凝集槽に戻す引き抜き分離ライ
ンとを備えた凝集沈澱装置において、引き抜き分離ライ
ン中に、中間受け槽を設けるとともに、引き抜き分離ラ
インの沈澱槽から中間受け槽までを低流速流路に、中間
受け槽からサイクロンまでを高流速流路に構成したこと
を特徴とする凝集沈澱装置。
1. A flocculation tank for flocculating a suspended substance in raw water by adding a flocculant and a particulate matter, and an aggregate in water to be treated introduced from the flocculation tank is precipitated to be separated into treated water and a precipitate. A coagulating sedimentation apparatus comprising a sedimentation tank, a cyclone for extracting the sediment from the sedimentation tank, separating the extracted sediment into sludge and particulate matter, and a drawing separation line for returning the separated particulate matter to the coagulation tank In the drawing, an intermediate receiving tank is provided in the drawing separation line, and a low flow path is formed from the settling tank to the intermediate receiving tank of the drawing separation line, and a high flow path is formed from the intermediate receiving tank to the cyclone. Coagulation sedimentation equipment.
【請求項2】 低流速流路における流速と高流速流路に
おける流速との比が1:2以上である、請求項1の凝集
沈澱装置。
2. The coagulation sedimentation apparatus according to claim 1, wherein the ratio of the flow velocity in the low flow velocity flow path to the flow velocity in the high flow velocity flow path is 1: 2 or more.
【請求項3】 低流速流路における管内流速が1.5m
/s以下である、請求項1または2の凝集沈澱装置。
3. The flow velocity in the pipe in the low flow velocity flow path is 1.5 m.
3. The coagulation sedimentation device according to claim 1, wherein the concentration is not more than / s.
【請求項4】 中間受け槽が大気開放型の槽からなる、
請求項1ないし3のいずれかに記載の凝集沈澱装置。
4. The intermediate receiving tank comprises an open-to-atmosphere tank.
The coagulation sedimentation apparatus according to claim 1.
【請求項5】 低流速流路に低速輸送用ポンプが、高流
速流路に高速輸送用ポンプが、それぞれ設けられてい
る、請求項1ないし4のいずれかに記載の凝集沈澱装
置。
5. The coagulating sedimentation apparatus according to claim 1, wherein a low-speed transport pump is provided in the low-flow-rate channel, and a high-speed transport pump is provided in the high-flow-rate channel.
【請求項6】 粒状物が砂である、請求項1ないし5の
いずれかに記載の凝集沈澱装置。
6. The coagulating sedimentation apparatus according to claim 1, wherein the granular material is sand.
【請求項7】 凝集剤が無機凝集剤と高分子凝集剤を含
む、請求項1ないし6のいずれかに記載の凝集沈澱装
置。
7. The coagulation / sedimentation apparatus according to claim 1, wherein the coagulant includes an inorganic coagulant and a polymer coagulant.
JP13854699A 1999-05-19 1999-05-19 Coagulation sedimentation equipment Expired - Fee Related JP3901392B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP13854699A JP3901392B2 (en) 1999-05-19 1999-05-19 Coagulation sedimentation equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP13854699A JP3901392B2 (en) 1999-05-19 1999-05-19 Coagulation sedimentation equipment

Publications (2)

Publication Number Publication Date
JP2000325705A true JP2000325705A (en) 2000-11-28
JP3901392B2 JP3901392B2 (en) 2007-04-04

Family

ID=15224691

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002355506A (en) * 2001-05-31 2002-12-10 Japan Organo Co Ltd Flocculating and settling equipment
WO2006036014A1 (en) * 2004-09-30 2006-04-06 Nishihara Environment Technology, Inc. Coagulation-separation apparatus

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002355506A (en) * 2001-05-31 2002-12-10 Japan Organo Co Ltd Flocculating and settling equipment
JP4535419B2 (en) * 2001-05-31 2010-09-01 オルガノ株式会社 Coagulation sedimentation equipment
WO2006036014A1 (en) * 2004-09-30 2006-04-06 Nishihara Environment Technology, Inc. Coagulation-separation apparatus

Also Published As

Publication number Publication date
JP3901392B2 (en) 2007-04-04

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