JP2002355506A - Flocculating and settling equipment - Google Patents

Flocculating and settling equipment

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Publication number
JP2002355506A
JP2002355506A JP2001164968A JP2001164968A JP2002355506A JP 2002355506 A JP2002355506 A JP 2002355506A JP 2001164968 A JP2001164968 A JP 2001164968A JP 2001164968 A JP2001164968 A JP 2001164968A JP 2002355506 A JP2002355506 A JP 2002355506A
Authority
JP
Japan
Prior art keywords
sludge
tank
water
coagulation
separator
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
JP2001164968A
Other languages
Japanese (ja)
Other versions
JP2002355506A5 (en
JP4535419B2 (en
Inventor
Kazuhiko Shimizu
和彦 清水
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 JP2001164968A priority Critical patent/JP4535419B2/en
Publication of JP2002355506A publication Critical patent/JP2002355506A/en
Publication of JP2002355506A5 publication Critical patent/JP2002355506A5/ja
Application granted granted Critical
Publication of JP4535419B2 publication Critical patent/JP4535419B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Treatment Of Sludge (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a flocculating and settling equipment in which a sludge separated by a separator is concentrated more efficiently when concentrated by using a concentrating means such as a floatation separation column so that the concentrated sludge sent from the concentrating means can be treated efficiently in a concentrated sludge storage tank and a dehydrator, and the capacity of sludge storage tank and the pomp for the dehydrator can be restrained from being large-sized. SOLUTION: This flocculating and settling equipment provided with a flocculating tank for flocculating the suspended matter in raw water as flocks by adding a granular material and a flocculant, a settling tank for settling the flocks in the water introduced from the flocculating tank and separating the flock-containing water into the treated water and slurry, the separator for separating the slurry withdrawn from the settling tank into sludge and the granular material and returning the separated granular material to the flocculating tank, is characterize in that a concentrating means for furthermore separating the sludge separated by the separator into the concentrated sludge and the treated water for circulation and returning the treated water for circulation to the raw water side in provided and a macromolecular flocculant adding means is additionally arranged between the separator and the concentrating means.

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
を粒状物と凝集剤を添加して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、とくに凝集沈澱に
より分離した汚泥を効率よくさらに濃縮できるできるよ
うにした凝集沈澱装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a coagulation sedimentation apparatus for separating a suspended substance in raw water into sludge and treated water by coagulation sedimentation by adding a particulate matter and a coagulant, and in particular, sludge separated by coagulation sedimentation. The present invention relates to a coagulation-sedimentation apparatus capable of efficiently and further concentrating the water.

【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。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。
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. . In such a general coagulation and sedimentation apparatus, it takes a long time to settle the coagulates, and an extremely large sedimentation tank is required. Therefore, the coagulation and sedimentation is more efficiently performed. A device has been proposed.

【0003】たとえば、原水中のSSを除去するための
凝集沈澱装置として、原水に粒径10〜200μm程度
の粒状物(砂)と高分子凝集剤を添加して原水中のSS
とともにフロックを形成させる凝集槽と、フロック形成
槽(凝集槽)から流出するフロックを処理水と分離する
沈澱槽と、沈澱槽から引き抜いた沈降フロック(スラリ
ー)を砂と汚泥に分離する分離器(サイクロン)とから
構成される装置が知られている。
For example, as a coagulating sedimentation apparatus for removing SS in raw water, a particulate matter (sand) having a particle size of about 10 to 200 μm and a polymer flocculant are added to raw water to remove SS in raw water.
A flocculation tank for forming flocs together with the floc, a sedimentation tank for separating the flocs flowing out of the floc formation tank (coagulation tank) from the treated water, and a separator for separating the sedimented flocs (slurry) drawn from the sedimentation tank into sand and sludge ( (Cyclone) is known.

【0004】このような凝集沈澱装置においては、サイ
クロンの上部出口から排出される汚泥は比較的濃度が低
く、その後の工程で汚泥濃縮処理を円滑に行うことが困
難であるため、また、凝集沈澱処理に用いる無機凝集剤
による反応を促進させるために、先に本出願人により、
上記サイクロンの上部出口からの汚泥ラインに分級塔を
設置する構造が提案されている(特開2000−317
220号公報)。
[0004] In such a coagulating sedimentation apparatus, the sludge discharged from the upper outlet of the cyclone has a relatively low concentration, and it is difficult to smoothly perform the sludge concentration treatment in the subsequent process. In order to promote the reaction by the inorganic coagulant used for the treatment,
A structure in which a classification tower is installed in a sludge line from the upper exit of the cyclone has been proposed (Japanese Patent Laid-Open No. 2000-317).
No. 220).

【0005】たとえば図3に示すように、予備凝集槽1
01に導入された原水102に無機凝集剤103を添加
して攪拌機104で攪拌し、その原水に高分子凝集剤1
05を添加して凝集槽106に導入し、攪拌機107で
攪拌して粒状物(砂)115とともにフロック108を
形成させ、その被処理水を沈澱槽109に導入して汚泥
を沈降分離するとともに、傾斜板110を介して上部か
ら処理水111を得る。沈澱槽109の下部から汚泥引
抜ポンプ112によりスラリーを引き抜き、ライン11
3を介して分離器としてのサイクロン114に送って汚
泥と粒状物とに分離し、分離した粒状物115を凝集槽
106に戻す。また、サイクロン114上部出口から
は、分離された汚泥が分級塔116に送られ、そこで重
力により濃縮汚泥117と、上部からの循環処理水11
8とに分離され、循環処理水118が原水側に戻される
ようになっている。この提案装置では、サイクロンで分
離された汚泥を、さらに濃縮汚泥と、原水側へと戻され
る循環処理水とに分級させ、この濃縮汚泥を後段の汚泥
濃縮工程に送るようにしている。
[0005] For example, as shown in FIG.
The inorganic coagulant 103 is added to the raw water 102 introduced into the raw water 01 and stirred by the stirrer 104.
05 is added to the flocculation tank 106 and stirred by the stirrer 107 to form flocs 108 together with the particulate matter (sand) 115. The water to be treated is introduced into the settling tank 109 to settle and separate sludge. The treated water 111 is obtained from above through the inclined plate 110. The slurry is drawn from the lower part of the settling tank 109 by a sludge drawing pump 112,
3, is sent to a cyclone 114 as a separator to separate sludge and particulate matter, and the separated particulate matter 115 is returned to the flocculation tank 106. Separated sludge is sent from the upper outlet of the cyclone 114 to the classification tower 116, where the concentrated sludge 117 and the circulated water 11
8 and the circulated treated water 118 is returned to the raw water side. In the proposed apparatus, the sludge separated by the cyclone is further classified into concentrated sludge and circulating treated water returned to the raw water side, and the concentrated sludge is sent to a subsequent sludge concentration step.

【0006】また、未だ出願未公開の段階にあるが、先
に本出願人により、上記分級塔に代えて、気泡の浮上に
より濃縮汚泥と循環処理水とに分離する浮上分離槽を設
けた構造も提案されている(特願2000−27902
0号)。この提案装置では、原水中のSSが生物汚泥の
ような沈降しにくい成分の場合、サイクロンから排出さ
れてくる汚泥をさらに効率よく濃縮することが可能とな
る。
Although the application has not yet been published, the present applicant has previously provided a flotation / separation tank which separates the concentrated sludge and circulating treated water by the flotation of air bubbles instead of the classification tower. Has also been proposed (Japanese Patent Application No. 2000-27902).
No. 0). In the proposed apparatus, when SS in raw water is a component that is unlikely to settle, such as biological sludge, it is possible to more efficiently concentrate sludge discharged from the cyclone.

【0007】[0007]

【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、沈澱槽から引き抜いた粒状物
(砂)を含んだ汚泥(スラリー)を汚泥引抜ポンプで移
送してサイクロンで汚泥と砂に分離すると、汚泥が強く
攪拌される、破壊、微細化されたフロックとなるため、
分級塔や浮上分離槽での汚泥濃縮性が悪くなり、後段の
汚泥貯槽に送られる濃縮汚泥の濃度が薄くなる。その結
果、汚泥貯槽の容量や濃縮汚泥をさらに脱水機に移送す
るポンプを大型化する必要が生じ、さらには汚泥貯槽等
において濃縮汚泥に添加する高分子凝集剤の添加量が増
加するという問題が残されている。
However, in the above-mentioned coagulating sedimentation apparatus, the sludge (slurry) containing the particulate matter (sand) drawn from the sedimentation tank is transferred by a sludge drawing pump, and the sludge and sand are separated by a cyclone. When separated into sludge, the sludge is vigorously stirred, resulting in destruction and miniaturized flocs.
The sludge concentration property in the classification tower and the flotation tank becomes poor, and the concentration of the concentrated sludge sent to the subsequent sludge storage tank becomes thin. As a result, it becomes necessary to increase the capacity of the sludge storage tank and the size of the pump for transferring the concentrated sludge to the dehydrator, and further increase the amount of the polymer flocculant added to the concentrated sludge in the sludge storage tank. Is left.

【0008】そこで本発明の課題は、上記のような問題
点に着目し、分離器で分離された汚泥を分級塔や浮上分
離槽などの濃縮手段で濃縮するに際し、より効率よく濃
縮できるようにし、それによって濃縮手段から送られて
くる濃縮汚泥の汚泥貯槽や脱水機における処理を容易な
かつ効率のよいものにするとともにそれらの大型化を抑
制することが可能な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 pay attention to the above problems, and to concentrate the sludge separated by the separator with a concentration means such as a classification tower or a flotation tank more efficiently. Accordingly, it is an object of the present invention to provide an agglomerated sedimentation apparatus capable of easily and efficiently treating a concentrated sludge sent from a concentration means in a sludge storage tank and a dehydrator and suppressing an increase in the size thereof. .

【0009】[0009]

【課題を解決するための手段】上記課題を解決するため
に、本発明に係る凝集沈澱装置は、原水中の懸濁物質を
粒状物と凝集剤の添加によりフロックとして凝集させる
凝集槽と、凝集槽からの導入水中のフロックを沈降させ
処理水とスラリーとに分離する沈澱槽と、沈澱槽から抜
き出したスラリーを汚泥と粒状物とに分離し、分離した
粒状物を凝集槽に戻す分離器とを備えた凝集沈澱装置に
おいて、分離器で分離した汚泥をさらに濃縮汚泥と循環
処理水とに分離し、循環処理水を原水側に戻す濃縮手段
を設けるとともに、該濃縮手段と前記分離器の間に、高
分子凝集剤添加手段を設け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 as flocs by adding particulate matter and a coagulant; A sedimentation tank for sedimenting flocs in the introduced water from the tank and separating the treated water and slurry, a separator for separating the slurry extracted from the sedimentation tank into sludge and particulate matter, and returning the separated particulate matter to the flocculation tank; In the coagulating sedimentation apparatus provided with, a sludge separated by the separator is further separated into concentrated sludge and circulating treated water, and a concentrating means for returning the circulating treated water to the raw water side is provided. And a means for adding a polymer flocculant.

【0010】上記濃縮手段は、たとえば、重力により濃
縮汚泥と循環処理水とに分級する図3に示したような分
級手段、あるいは、気泡の浮上により濃縮汚泥と循環処
理水とに分離する浮上分離手段からなる。
The concentrating means is, for example, a classifying means as shown in FIG. 3 for classifying into concentrated sludge and circulating treated water by gravity, or a floating separation for separating into concentrated sludge and circulating treated water by floating air bubbles. Consisting of means.

【0011】また、高分子凝集剤添加手段により添加す
る凝集剤としては、アニオン、ノニオン、カチオン性の
凝集剤等のいずれのものでも使用できるが、凝集槽に添
加する高分子凝集剤がアニオンもしくはノニオン性の場
合は、カチオン性の高分子凝集剤を用いると、そのイオ
ン性が故により密に反応するため、濃縮性が一層向上す
る。
As the flocculant to be added by the polymer flocculant adding means, any of anionic, nonionic, cationic flocculants and the like can be used. In the case of nonionic properties, when a cationic polymer flocculant is used, it reacts more densely because of its ionicity, so that the concentration property is further improved.

【0012】このような本発明に係る凝集沈澱装置は、
原水のSS分に比較して無機凝集剤が多い場合や重金属
のアルカリ凝集沈澱を行う場合等の濃縮しずらいフロッ
クが生成される場合に特に有効である。
[0012] Such a coagulating sedimentation apparatus according to the present invention comprises:
This is particularly effective when floc that is difficult to concentrate is generated, such as when the amount of the inorganic coagulant is larger than the SS content of the raw water or when alkali coagulation and precipitation of heavy metals is performed.

【0013】上記のような本発明に係る凝集沈澱装置に
おいては、分離器で分離された汚泥は、濃縮手段へと送
られ、さらに濃縮されて濃縮汚泥とされるが、分離器と
濃縮手段の間で高分子凝集剤が添加されるので、汚泥引
抜ポンプや分離器で破壊、微細化されたフロックが高分
子凝集剤によって再凝集し、フロックが大きく密に成長
して濃縮性が向上する。したがって、この高分子凝集剤
が添加された後に濃縮手段で分離される汚泥は、十分に
濃い濃縮汚泥となる。その結果、この濃縮手段の後段に
設けられる汚泥貯槽の容量や、濃縮汚泥を脱水機に移送
するポンプの大型化は回避され、コスト増大等を招くこ
となく、容易に処理や移送を効率よく行うことが可能に
なる。また、この濃縮汚泥は十分に濃いものとされてい
るので、脱水機前で高分子凝集剤を添加する場合にも、
その添加量を減少することが可能になる。
[0013] In the coagulating sedimentation apparatus according to the present invention as described above, the sludge separated by the separator is sent to the concentration means and further concentrated to be concentrated sludge. Since the polymer flocculant is added in between, the floc broken and miniaturized by the sludge drawing pump or the separator is reagglomerated by the polymer flocculant, and the floc grows large and densely, thereby improving the concentrating property. Therefore, the sludge separated by the concentration means after the addition of the polymer flocculant becomes a sufficiently thick concentrated sludge. As a result, the capacity of the sludge storage tank provided at the subsequent stage of the concentrating means and the increase in the size of the pump for transferring the concentrated sludge to the dehydrator are avoided, and the processing and transfer are easily performed efficiently without increasing the cost. It becomes possible. Also, since this concentrated sludge is sufficiently thick, even when a polymer flocculant is added before the dehydrator,
It is possible to reduce the amount added.

【0014】[0014]

【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
明の第1実施態様に係る凝集沈澱装置を示している。図
1において、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。原水5は、原水供
給ライン4を介して予備凝集槽7に供給され、そこで無
機凝集剤6が添加される。予備凝集槽7には、モータ8
によって駆動される攪拌機9が設けられており、攪拌機
9で攪拌された後、凝集槽2に送られるときにさらに高
分子凝集剤10が注入されるようになっている。
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 according to a first embodiment of the present invention. In FIG. 1, the coagulation / sedimentation apparatus 1 includes a coagulation tank 2 and a sedimentation tank 3 disposed adjacent thereto. The raw water 5 is supplied to the pre-coagulation tank 7 via the raw water supply line 4, where the inorganic coagulant 6 is added. The pre-coagulation tank 7 has a motor 8
Is provided, and after being stirred by the stirrer 9, the polymer flocculant 10 is further injected when it is sent to the flocculation tank 2.

【0015】凝集槽2内には、粒状物としての砂11が
添加される。凝集槽2には、モータ12によって駆動さ
れる攪拌機13が設けられており、攪拌機13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10、砂11を含むフロックとして凝集、成長さ
れる。
In the coagulation tank 2, sand 11 as a granular material is added. The flocculation tank 2 is provided with a stirrer 13 driven by a motor 12, and the suspended substance in the raw water is stirred by the stirrer 13 to form a floc containing the inorganic coagulant 6, the polymer coagulant 10, and the sand 11. Aggregated and grown.

【0016】この凝集においては、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10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11が含有され、全体として比較的大きな、比重の大
きい沈降しやすいフロックに成長する。
In this flocculation, the inorganic flocculant 6 flocculates the suspended substance to form fine flocs, and the polymer flocculant 10 becomes entangled to grow into larger flocs, and the grown flocs have specific gravity. It contains sand 11 as a large granular material, and grows into a relatively large floc having a high specific gravity and easy to settle as a whole.

【0017】成長した凝集フロック14を含む被処理水
は、越流ぜき15を介して沈澱槽3へと導入される。沈
澱槽3では、導入水中のフロックが下方に沈降され、沈
降されたフロックは上方の処理水16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17が並設さ
れており、処理水16とともにフロックが流出するのを
抑制している。
The water to be treated including the grown floc 14 is introduced into the sedimentation tank 3 through the overflow weir 15. In the settling tank 3, the flocs in the introduced water are settled downward, and the settled flocs are separated from the treated water 16 above. A plurality of inclined plates 17 are arranged in the upper part in the settling tank 3 so as to prevent the floc from flowing out together with the treated water 16.

【0018】沈澱槽3の底部には、沈降されたフロック
を引き抜くための引抜ライン18が接続されており、汚
泥引抜ポンプ19によって、沈降した凝集フロックを含
む汚泥スラリーが引き抜かれる。引き抜かれたスラリー
は、分離器としてのサイクロン20に送られ、サイクロ
ン20内における遠心分離により、汚泥21と砂11と
に分離される。分離された砂11は、サイクロン20の
下部出口22から再び凝集槽2内に戻されて循環再使用
される。
The bottom of the settling tank 3 is connected to a drawing line 18 for drawing out settled flocs, and a sludge drawing pump 19 draws out sludge slurry containing settled flocs. The extracted slurry is sent to a cyclone 20 as a separator, and is separated into sludge 21 and sand 11 by centrifugation in the cyclone 20. The separated sand 11 is returned from the lower outlet 22 of the cyclone 20 to the flocculation tank 2 again, and is circulated and reused.

【0019】サイクロン20で分離され、サイクロン2
0の上部出口23から排出された濃縮前の汚泥21は、
導出ライン24を介して、濃縮手段25に送られる。本
実施態様では、濃縮手段25は、導入されてくる汚泥
を、重力により濃縮汚泥26と循環処理水27とに分級
する分級塔(分級手段)に構成されている。濃縮汚泥2
6は、汚泥送給ライン28を介して後段の汚泥貯槽、さ
らには脱水機へと送られるようになっている(図示
略)。循環処理水27は、返送ライン29を介して原水
側に、本実施態様では予備凝集槽7へと戻されるように
なっている。
Separated by cyclone 20, cyclone 2
The sludge 21 before concentration discharged from the upper outlet 23 of
It is sent to the concentration means 25 via the lead-out line 24. In this embodiment, the concentration means 25 is configured as a classification tower (classification means) for classifying the introduced sludge into the concentrated sludge 26 and the circulating water 27 by gravity. Thickened sludge 2
Numeral 6 is sent to a sludge storage tank at a later stage and further to a dehydrator via a sludge feed line 28 (not shown). The circulated treated water 27 is returned to the raw water side via the return line 29, and in this embodiment, to the pre-coagulation tank 7.

【0020】上記サイクロン20の上部出口23と分級
塔25との間に、高分子凝集剤添加手段30が設けら
れ、分級塔25に導入される前の汚泥に、導出ライン2
4にて高分子凝集剤31がライン注入されるようになっ
ている。
A polymer coagulant adding means 30 is provided between the upper outlet 23 of the cyclone 20 and the classification tower 25, and the sludge before being introduced into the classification tower 25 is supplied to the outlet line 2.
At 4, the polymer coagulant 31 is injected into the line.

【0021】図3は、本発明の第2実施態様に係る凝集
沈澱装置41を示している。本実施態様では、上記第1
実施態様に比べ、濃縮手段に、気泡の浮上により濃縮汚
泥と循環処理水とに分離する浮上分離槽42(浮上分離
手段)が設けられている。サイクロン20の上部出口2
3から浮上分離槽42への汚泥の導出ライン43に、浮
上分離用水供給ライン44が合流されている。浮上分離
槽42は、本実施態様では、内筒45と外筒41を有
し、外筒45の外側に浮上分離槽42の槽壁47が位置
する構造となっている。汚泥導出ライン43と合流され
た浮上分離用水供給ライン44は、内筒45内に臨むよ
うに接続されており、この内筒45内で浮上分離のため
の気泡が浮上される。内筒45の上方および外筒46内
上部には、浮上分離処理によって分離されたスカム48
が集められ、濃縮汚泥49として後段の汚泥貯槽、さら
には脱水機へと送られるようになっている(図示略)。
FIG. 3 shows a coagulation / sedimentation apparatus 41 according to a second embodiment of the present invention. In the present embodiment, the first
Compared to the embodiment, the concentration means is provided with a flotation separation tank 42 (flotation separation means) which separates the concentrated sludge and the circulating treated water by the floating of bubbles. Upper exit 2 of cyclone 20
A floatation / separation water supply line 44 is joined to a sludge discharge line 43 from the tank 3 to the flotation / separation tank 42. In the present embodiment, the flotation tank 42 has an inner cylinder 45 and an outer cylinder 41, and the tank wall 47 of the flotation tank 42 is located outside the outer cylinder 45. The flotation / separation water supply line 44 joined to the sludge discharge line 43 is connected so as to face the inner cylinder 45, and bubbles for flotation / separation float in the inner cylinder 45. A scum 48 separated by a floating separation process is provided above the inner cylinder 45 and inside the outer cylinder 46.
Is collected and sent as a concentrated sludge 49 to a later-stage sludge storage tank and further to a dehydrator (not shown).

【0022】浮上分離槽42の底部からは、該底部に沈
降してきた汚泥50が引き抜かれる。この汚泥50は、
上記浮上分離槽42の上部からの濃縮汚泥49と合流さ
せて後段の処理に供してもよいし、別個に処理してもよ
い。また、外筒46と槽壁47との間の上部から、汚泥
と分離された循環処理水としての浮上分離処理水51が
浮上分離処理水返送ライン52を介して予備凝集槽7に
戻され、凝集沈澱系へと循環されるようになっている。
From the bottom of the flotation tank 42, the sludge 50 settled at the bottom is pulled out. This sludge 50
The condensed sludge 49 from the upper part of the flotation tank 42 may be combined with the concentrated sludge 49 and subjected to the subsequent treatment, or may be treated separately. Further, from the upper part between the outer cylinder 46 and the tank wall 47, the floatation / separation treatment water 51 as circulation treatment water separated from the sludge is returned to the preliminary flocculation tank 7 via the floatation / separation treatment water return line 52, It is intended to be recycled to the coagulation sedimentation system.

【0023】浮上分離用水供給ライン44には、浮上分
離のための気泡生成用の空気53が注入されるようにな
っており、本実施態様では加圧空気として注入される。
また、浮上分離用水供給ライン44には、加圧ポンプ5
4と加圧タンク55が設けられており、注入された空気
を所定の加圧状態にした後、内筒45内に供給される際
に急激に減圧状態(大気圧状態)に解放して、気泡を生
成できるようになっている。
Air 53 for generating air bubbles for flotation is injected into the water supply line 44 for flotation, and is injected as pressurized air in this embodiment.
In addition, a pressurized pump 5
4 and a pressurized tank 55 are provided. After the injected air is pressurized to a predetermined pressurized state, when it is supplied into the inner cylinder 45, it is rapidly released to a reduced pressure state (atmospheric pressure state). Bubbles can be generated.

【0024】浮上分離用水供給ライン44に供給する水
は、別の系から採水することも可能であるが、沈澱槽3
からの処理水16のラインから分岐して処理水16の一
部を利用するのが効率がよい。
The water supplied to the flotation water supply line 44 can be collected from another system.
It is efficient to use a part of the treated water 16 by branching off from the line of treated water 16 from.

【0025】上記サイクロン20の上部出口23と浮上
分離槽42との間に、高分子凝集剤添加手段56が設け
られ、汚泥導出ライン43中の汚泥に、浮上分離用水供
給ライン44の合流前の位置にて、高分子凝集剤57が
ライン注入されるようになっている。
A polymer flocculant adding means 56 is provided between the upper outlet 23 of the cyclone 20 and the flotation tank 42, and the sludge in the sludge discharge line 43 is added before the flotation water supply line 44 joins the sludge. At the position, the polymer flocculant 57 is injected in a line.

【0026】その他の構成は、実質的に図1に示した第
1実施態様と同じであるので、図1と同一の符号を付す
ことにより説明を省略する。
The other structure is substantially the same as that of the first embodiment shown in FIG. 1, and the description thereof will be omitted by retaining the same reference numerals as in FIG.

【0027】上記のように構成された第1、第2実施態
様に係る凝集沈澱装置1、41においては、サイクロン
20から分級塔25や浮上分離槽42に導入される前の
段階で、汚泥に高分子凝集剤31、57が添加されるの
で、汚泥引抜ポンプ19やサイクロン20で破壊、微細
化されたフロックが添加された高分子凝集剤により再凝
集され、フロックが大きく密に成長された形態にて分級
塔25や浮上分離槽42に送られることになる。したが
って、分級塔25や浮上分離槽42における汚泥濃縮性
が大幅に向上され、そこから排出される濃縮汚泥の濃度
が大幅に高められる。
In the coagulating sedimentation apparatuses 1 and 41 according to the first and second embodiments configured as described above, the sludge is removed before being introduced from the cyclone 20 into the classification tower 25 or the flotation tank 42. Since the polymer flocculants 31 and 57 are added, the floc is broken down by the sludge extraction pump 19 and the cyclone 20 and reagglomerated by the polymer flocculant to which the fine floc has been added, and the floc has grown greatly and densely. At the classification tower 25 and the flotation tank 42. Therefore, the sludge concentration in the classification tower 25 and the flotation tank 42 is greatly improved, and the concentration of the concentrated sludge discharged therefrom is greatly increased.

【0028】その結果、後段に設けられる汚泥貯槽の容
量は小さくて済み、脱水機に移送するポンプも大型化す
る必要はなくなる。また、この後段の処理で高分子凝集
剤を添加する場合、たとえば脱水機直前で高分子凝集剤
を添加する場合には、その高分子凝集剤の添加量も少な
くて済むことになる。
As a result, the capacity of the sludge storage tank provided at the subsequent stage can be small, and the pump for transferring to the dehydrator does not need to be large. In addition, when the polymer flocculant is added in the subsequent treatment, for example, when the polymer flocculant is added immediately before the dehydrator, the amount of the polymer flocculant added may be small.

【0029】[0029]

【実施例】図1に示したのと同等の構成の試験機を用
い、懸濁物質としてカオリンを原水に添加した人工濁水
に、無機凝集剤としてPAC(ポリ塩化アルミニウム)
を注入し、凝集槽に砂および高分子凝集剤を注入し、以
下の条件で実験した。濃縮汚泥は、濃縮手段からの抜き
出し量を調節し、濃縮汚泥濃度が最大となるときの濃度
を測定した。 〔実験機〕 予備凝集槽容量:200リットル 凝集槽容量 :500リットル 沈澱槽 :500mm□×3000mmH(傾斜板付き) 濃縮槽(濃縮手段):300mmΦ×2500mmH 〔運転条件〕 原水流量 :10m3 /h 汚泥引き抜き量:0.45m3 /h サイクロン上部出口からの流量:0.32m3 /h カオリン添加量:20mg/l 実験結果を表1に示す。
EXAMPLE Using a tester having the same configuration as that shown in FIG. 1, an artificial turbid water in which kaolin was added as a suspending substance to raw water, and PAC (polyaluminum chloride) as an inorganic coagulant were used.
, And sand and a polymer flocculant were poured into the flocculation tank, and the experiment was performed under the following conditions. The concentration of the concentrated sludge extracted from the concentration means was adjusted, and the concentration at which the concentration of the concentrated sludge was maximized was measured. [Experimental equipment] Pre-coagulation tank capacity: 200 liter Coagulation tank capacity: 500 liter Precipitation tank: 500 mm □ × 3000 mmH (with inclined plate) Concentration tank (concentration means): 300 mmΦ × 2500 mmH [Operating conditions] Raw water flow rate: 10 m 3 / h Sludge withdrawal amount: 0.45 m 3 / h Flow rate from the cyclone upper outlet: 0.32 m 3 / h Kaolin addition amount: 20 mg / l The experimental results are shown in Table 1.

【0030】[0030]

【表1】 [Table 1]

【0031】表1に示したように、実施例1、2では、
比較例1、2よりも濃縮汚泥濃度が高くなり、原水のS
Sに対してPAC添加量が多い方がその効果は大きかっ
た。実施例3では、比較例3と高分子凝集剤の使用量が
ほぼ同量であるが、濃縮汚泥濃度は高くなった。実施例
4では、サイクロン上部出口側に添加する高分子凝集剤
がアニオン性高分子凝集剤の時(実施例2)より、濃縮
汚泥濃度が高くなった。
As shown in Table 1, in Examples 1 and 2,
Concentrated sludge concentration was higher than Comparative Examples 1 and 2,
The effect was greater when the amount of PAC added to S was larger. In Example 3, the amount of the polymer flocculant used was almost the same as that of Comparative Example 3, but the concentration of the concentrated sludge was high. In Example 4, the concentrated sludge concentration was higher than when the polymer flocculant added to the cyclone upper outlet side was an anionic polymer flocculant (Example 2).

【0032】なお、本発明において使用される無機凝集
剤や高分子凝集剤については、とくに限定されないが、
無機凝集剤としては、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
子凝集剤としては、たとえばノニオン性、アニオン性、
カチオン性あるいはノニオン性とアニオン性、ノニオン
性とカチオン性の両性の高分子凝集剤を用いることがで
きる。これら高分子凝集剤の代表的なものとしては、た
とえば、ポリアクリルアミド系のアニオン性あるいはカ
チオン性の高分子凝集剤を挙げることができる。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。
The inorganic coagulant and polymer coagulant used in the present invention are not particularly limited,
Examples of the inorganic coagulant include polyaluminum chloride (PAC), ferric chloride, and ferric sulfate. Examples of the polymer coagulant include nonionic, anionic,
A cationic or nonionic and anionic, and a nonionic and cationic amphoteric polymer flocculant can be used. Representative examples of these polymer flocculants include polyacrylamide-based anionic or cationic polymer flocculants. 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.

【0033】[0033]

【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、分離器で分離された汚泥を分級手段や浮
上分離手段等の濃縮手段で濃縮する前に高分子凝集剤を
添加し、それによって濃縮手段でより濃度の高い濃縮汚
泥へと濃縮できるようにしたので、後段での処理を容易
化でき、汚泥貯槽の容量を小さく抑えることができると
ともに、脱水機等への移送ポンプを小型化することがで
きる。
As described above, according to the coagulation / sedimentation apparatus of the present invention, a polymer flocculant is added before the sludge separated by the separator is concentrated by a concentration means such as a classification means or a flotation separation means. As a result, the concentrated sludge can be concentrated by the concentration means to a higher concentration sludge, so that the treatment in the subsequent stage can be facilitated, the capacity of the sludge storage tank can be reduced, and the transfer pump to the dehydrator etc. Can be reduced in size.

【0034】また、濃縮汚泥の濃度が高いので、たとえ
ば脱水機直前で高分子凝集剤を添加する場合等において
は、その添加量を低減することもできる。
Further, since the concentration of the concentrated sludge is high, for example, when the polymer flocculant is added immediately before the dehydrator, the amount of the polymer flocculant can be reduced.

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

【図1】本発明の第1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 a first embodiment of the present invention.

【図2】本発明の第2実施態様に係る凝集沈澱装置の全
体構成図である。
FIG. 2 is an overall configuration diagram of a coagulation / sedimentation apparatus according to a second embodiment of the present invention.

【図3】本出願人が先に提案した凝集沈澱装置(特開2
000−317220号)の全体構成図である。
FIG. 3 shows a coagulation / sedimentation apparatus previously proposed by the present applicant (JP-A-2
000-317220).

【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 予備凝集槽 8 モータ 9 攪拌機 10 高分子凝集剤 11 粒状物としての砂 12 モータ 13 攪拌機 14 凝集フロック 15 越流ぜき 16 処理水 17 傾斜板 18 引抜ライン 19 汚泥引抜ポンプ 20 分離器としてのサイクロン 21 濃縮前の汚泥 22 サイクロンの下部出口 23 サイクロンの上部出口 24 汚泥導出ライン 25 濃縮手段としての分級塔 26 濃縮汚泥 27 循環処理水 28 汚泥送給ライン 29 返送ライン 30 高分子凝集剤添加手段 31 高分子凝集剤 41 凝集沈澱装置 42 濃縮手段としての浮上分離槽 43 汚泥の導出ライン 44 浮上分離用水供給ライン 45 内筒 46 外筒 47 槽壁 48 スカム 49 濃縮汚泥 50 沈降汚泥 51 浮上分離処理水 52 浮上分離処理水返送ライン 53 注入空気 54 加圧ポンプ 55 加圧タンク 56 高分子凝集剤添加手段 57 高分子凝集剤 DESCRIPTION OF SYMBOLS 1 Coagulation sedimentation apparatus 2 Coagulation tank 3 Precipitation tank 4 Raw water supply line 5 Raw water 6 Inorganic coagulant 7 Pre-coagulation tank 8 Motor 9 Stirrer 10 Polymer coagulant 11 Granular sand 12 Motor 13 Stirrer 14 Coagulation floc 15 Overflow 16 Treatment water 17 Inclined plate 18 Extraction line 19 Sludge extraction pump 20 Cyclone 21 as separator 21 Sludge before concentration 22 Lower exit of cyclone 23 Upper exit of cyclone 24 Sludge outlet line 25 Classification tower as concentration means 26 Concentrated sludge 27 Circulating treatment water 28 Sludge feed line 29 Return line 30 Polymer flocculant adding means 31 Polymer flocculant 41 Coagulant sedimentation device 42 Floating / separation tank as concentration means 43 Sludge lead-out line 44 Floating / separating water supply line 45 Inner cylinder 46 Outer cylinder 47 Tank wall 48 Scum 49 Condensed sludge 50 Settling sludge 51 Flotation treatment water 52 Flotation treatment water return line 53 Injected air 54 Pressurized pump 55 Pressurized tank 56 Polymer coagulant adding means 57 Polymer coagulant

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 原水中の懸濁物質を粒状物と凝集剤の添
加によりフロックとして凝集させる凝集槽と、凝集槽か
らの導入水中のフロックを沈降させ処理水とスラリーと
に分離する沈澱槽と、沈澱槽から抜き出したスラリーを
汚泥と粒状物とに分離し、分離した粒状物を凝集槽に戻
す分離器とを備えた凝集沈澱装置において、分離器で分
離した汚泥をさらに濃縮汚泥と循環処理水とに分離し、
循環処理水を原水側に戻す濃縮手段を設けるとともに、
該濃縮手段と前記分離器の間に、高分子凝集剤添加手段
を設け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 as a floc by adding a particulate matter and a flocculant, and a sedimentation tank for sedimenting floc in water introduced from the flocculation tank and separating it into treated water and slurry. In the coagulation sedimentation apparatus equipped with a separator that separates the slurry extracted from the sedimentation tank into sludge and particulate matter and returns the separated particulate matter to the coagulation tank, the sludge separated by the separator is further subjected to concentrated sludge and circulation treatment. Separated into water and
Concentration means to return the circulated treated water to the raw water side is provided,
A coagulation / sedimentation apparatus comprising a polymer coagulant adding means provided between the concentration means and the separator.
【請求項2】 前記濃縮手段が、重力により濃縮汚泥と
循環処理水とに分級する分級手段からなる、請求項1の
凝集沈澱装置。
2. The coagulation sedimentation apparatus according to claim 1, wherein said concentration means comprises a classification means for classifying into concentrated sludge and circulating treated water by gravity.
【請求項3】 前記濃縮手段が、気泡の浮上により濃縮
汚泥と循環処理水とに分離する浮上分離手段からなる、
請求項1の凝集沈澱装置。
3. The flotation means comprises flotation separation means for separating concentrated sludge and circulating treated water by flotation of bubbles.
The coagulation sedimentation device according to claim 1.
JP2001164968A 2001-05-31 2001-05-31 Coagulation sedimentation equipment Expired - Fee Related JP4535419B2 (en)

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