JPS6354407B2 - - Google Patents
Info
- Publication number
- JPS6354407B2 JPS6354407B2 JP55125331A JP12533180A JPS6354407B2 JP S6354407 B2 JPS6354407 B2 JP S6354407B2 JP 55125331 A JP55125331 A JP 55125331A JP 12533180 A JP12533180 A JP 12533180A JP S6354407 B2 JPS6354407 B2 JP S6354407B2
- Authority
- JP
- Japan
- Prior art keywords
- tank
- water
- raw water
- sedimentation tank
- overtank
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 104
- 238000004062 sedimentation Methods 0.000 claims description 38
- 238000002156 mixing Methods 0.000 claims description 29
- 239000000945 filler Substances 0.000 claims description 18
- 239000007787 solid Substances 0.000 claims description 9
- 239000002245 particle Substances 0.000 claims description 3
- 239000003795 chemical substances by application Substances 0.000 claims 1
- 238000005189 flocculation Methods 0.000 claims 1
- 230000016615 flocculation Effects 0.000 claims 1
- 239000004576 sand Substances 0.000 description 9
- 238000004140 cleaning Methods 0.000 description 8
- 239000000463 material Substances 0.000 description 7
- 238000012856 packing Methods 0.000 description 7
- 238000002347 injection Methods 0.000 description 4
- 239000007924 injection Substances 0.000 description 4
- 239000007788 liquid Substances 0.000 description 4
- 238000005406 washing Methods 0.000 description 4
- 239000000701 coagulant Substances 0.000 description 3
- 238000005345 coagulation Methods 0.000 description 2
- 230000015271 coagulation Effects 0.000 description 2
- 238000004891 communication Methods 0.000 description 2
- 238000010276 construction Methods 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 238000009434 installation Methods 0.000 description 2
- 239000010802 sludge Substances 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 239000004575 stone Substances 0.000 description 2
- 241001070941 Castanea Species 0.000 description 1
- 235000014036 Castanea Nutrition 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
Landscapes
- Filtration Of Liquid (AREA)
Description
【発明の詳細な説明】
本発明は原水に凝集剤を添加し、当該原水を直
接過槽に流入させて、原水中の懸濁物質を除去
し、原水を清澄化する過槽の改良に関するもの
である。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an improvement in a supertank in which a flocculant is added to raw water and the raw water is allowed to flow directly into the supertank to remove suspended matter in the raw water and clarify the raw water. It is.
従来、充填物の粒子径が異なる多層の充填層を
有する多層過槽や二方向過槽のような濁質捕
捉能力の大きな過槽において、原水に凝集剤を
添加して急速撹拌のみを行なつた後、当該原水を
直接過槽に流入させて原水中の懸濁物質を除去
し、原水の清澄化を行なつている。しかし、この
ような過槽は凝集剤の使用量が少量でよいとい
う利点がある反面、原水中の濁度が多い場合、た
とえば原水濁度20度以上であると、懸濁物質を除
去しきれず、清澄水を得ることができず、かつ
過槽の目詰りが早くなつたりする欠点があり、原
水の濁度が一時的にせよ、20度以上の高濁度とな
る場合は過槽だけによる処理はできなかつた。 Conventionally, in supertanks with high turbidity trapping capacity, such as multilayer supertanks and two-way supertanks that have multiple packed layers with different filler particle sizes, a flocculant is added to the raw water and only rapid stirring is performed. After that, the raw water is directly flowed into a filter tank to remove suspended matter in the raw water and clarify the raw water. However, while this type of supertank has the advantage of requiring only a small amount of flocculant to be used, if the raw water has a high turbidity, for example, if the raw water turbidity is 20 degrees or higher, suspended solids cannot be removed completely. , it is not possible to obtain clear water, and the overtank may become clogged quickly.If the turbidity of the raw water reaches 20 degrees or higher, even if it is temporary, only the overtank is used. I couldn't process it.
またこのような原水を処理する場合、過槽の
前段に凝集沈殿装置を設置して、原水中の濁度が
少ない時は原水に凝集剤を添加した後直接過槽
に流入させて過処理し、原水中の濁度が高い時
は凝集沈殿装置において凝集フロツクを沈殿させ
たのち、その流出水を過装置で処理することも
行なわれている。しかし凝集沈殿装置の処理容量
は同一の設置面積で比較すると、過装置より小
さく、したがつてその設置規模が大きくなり、多
額の建設費を必要とするので、原水中の濁度が一
時的に多くなつた時のみに使用する目的だけで凝
集沈殿装置を設置することは極めて不経済であ
り、また凝集沈殿装置は凝集剤の注入率が大き
く、維持費の増大や発生汚泥量が増加するという
欠点を有する。 In addition, when treating such raw water, a coagulation sedimentation device is installed before the overtank, and when the turbidity in the raw water is low, a coagulant is added to the raw water and then the water is allowed to flow directly into the overtank for overtreatment. When the turbidity of the raw water is high, the flocs are precipitated in a coagulation-sedimentation device, and then the effluent is treated in a filtration device. However, when comparing the processing capacity of coagulation sedimentation equipment with the same installation area, it is smaller than that of filtration equipment, and therefore the installation scale is larger and a large amount of construction cost is required. It is extremely uneconomical to install a coagulation-sedimentation device only for the purpose of using it when the amount increases, and the coagulation-sedimentation device requires a high injection rate of flocculant, which increases maintenance costs and the amount of sludge generated. It has its drawbacks.
本発明は従来のこのような過槽における欠点
を解決するものであり、過槽の前段に特殊な接
触沈殿槽を付設することによつて、濁度が大きく
変動する原水を、濁度が多い時は接触沈殿槽、続
いて過槽に流入させ、また濁度が少ない時は直
接過槽に流入させるように、濁度の変動によつ
て流路を切り換えながら効率よく処理することが
できる新規な過槽を提供することを目的とす
る。 The present invention solves these drawbacks of conventional overtanks, and by attaching a special contact sedimentation tank before the overtank, it is possible to convert raw water with large fluctuations in turbidity to water with high turbidity. A new technology that enables efficient treatment by switching the flow path depending on turbidity fluctuations, such as flowing into the contact sedimentation tank, then into the supertank, and directly into the supertank when the turbidity is low. The purpose is to provide a suitable overtank.
すなわち本発明は過槽の上方部に、混合槽
と、槽内を1対のスクリーンで3室に縦割すると
ともに、当該スクリーンの間の空間部に少なくと
も直径25mm以上の充填物を充填した接触沈殿槽と
を設け、当該混合槽と過槽をたとえばバイパス
管で接続するとともに、当該混合槽と前記接触沈
殿槽を、たとえば混合槽出口管で接続し、さらに
当該接触沈殿槽と過槽を、たとえば接触沈殿槽
出口管で接続し、原水中に存在する懸濁物質の量
が少ない時は凝集剤を添加した原水を混合槽で混
合したのち当該混合水をバイパス管を経て水頭差
で直接過槽に流入させて過処理し、また原水
中に存在する懸濁物質の量が多い時は当該混合水
を混合槽出口管を経て接触沈殿槽内の充填物層に
水平に通過させ、当該充填物層内においてフロツ
クを成長させるとともに比較的大きな粒径のフロ
ツクを沈殿させ、次いでその流出水を接触沈殿槽
出口管を経て水頭差で過槽に流入させて過処
理するように構成したことを特徴とする接触沈殿
槽を付設した過槽に関するものである。 That is, the present invention includes a mixing tank in the upper part of the tank, a pair of screens vertically dividing the inside of the tank into three chambers, and a space between the screens filled with a filler having a diameter of at least 25 mm. A settling tank is provided, the mixing tank and the overtank are connected, for example, by a bypass pipe, the mixing tank and the contact settling tank are connected, for example, with a mixing tank outlet pipe, and the contact settling tank and the overtank are connected, for example, by a mixing tank outlet pipe. For example, when connecting with a contact sedimentation tank outlet pipe, and when the amount of suspended solids present in the raw water is small, raw water to which a flocculant has been added is mixed in the mixing tank, and then the mixed water is passed through a bypass pipe and directly filtered by the water head difference. When the amount of suspended solids present in the raw water is large, the mixed water is passed horizontally through the mixing tank outlet pipe to the packing layer in the contact sedimentation tank to remove the filling. The structure is such that flocs are allowed to grow in the material layer and flocs with a relatively large particle size are precipitated, and then the effluent water is passed through the contact sedimentation tank outlet pipe and flowed into the overtreatment tank with a water head difference for overtreatment. This invention relates to an overtank equipped with a characteristic contact sedimentation tank.
以下に本発明を図面にしたがつて詳細に説明す
る。 The present invention will be explained in detail below with reference to the drawings.
図は本発明の接触沈殿槽を付設した過槽の実
施態様の一例を示した縦断説明図であり、二方向
過槽1の下方に設けた床板5の上方に砂利層
3、さらにその上方に砂層4を積層する。また砂
利層3はその下部に直径が比較的大きな砂利を充
填し、その上部には直径が比較的小さな砂利を充
填するように構成するとよい。また砂利層3の上
部に下部集水管6を挿入し、当該集水管6を連通
管7を介して砂層4より上方の過槽1の上部に
接続する。また砂層4の中間部位に上部集水管8
を挿入し、当該集水管8に処理水流出管9を接続
する。また過槽1の上方に液面検出計14を設
けるとともに、洗浄排水管10を接続する。さら
に過槽1の床板5の下方に洗浄水流入管13
を接続するとともに、空気分配管11を挿入し、
当該管11に空気流入管12を接続する。 The figure is a longitudinal cross-sectional view showing an example of an embodiment of a tank equipped with a contact sedimentation tank according to the present invention. Layer the sand layer 4. The gravel layer 3 may be configured such that the lower part thereof is filled with gravel having a relatively large diameter, and the upper part thereof is filled with gravel having a relatively small diameter. Further, a lower water collection pipe 6 is inserted into the upper part of the gravel layer 3, and the water collection pipe 6 is connected to the upper part of the filter tank 1 above the sand layer 4 via a communication pipe 7. In addition, an upper water collection pipe 8 is located in the middle of the sand layer 4.
is inserted, and the treated water outflow pipe 9 is connected to the water collection pipe 8. Further, a liquid level detector 14 is provided above the overflow tank 1, and a cleaning drain pipe 10 is connected thereto. Furthermore, a wash water inflow pipe 13 is located below the floor plate 5 of the cleaning tank 1.
At the same time, insert the air distribution pipe 11,
An air inflow pipe 12 is connected to the pipe 11.
また当該過槽1の上方に混合槽16と接触沈
殿槽18を設ける。当該混合槽16に撹拌機17
を付設するとともに、凝集剤注入管30を接続し
た原水管31を接続する。 Further, a mixing tank 16 and a contact settling tank 18 are provided above the filter tank 1. A stirrer 17 is installed in the mixing tank 16.
At the same time, a raw water pipe 31 to which a flocculant injection pipe 30 is connected is connected.
また前記接触沈殿槽18内に、水は通すが後述
する充填物22および23は通過させない1対の
スクリーン19および19′を間隔を置いて垂直
に設け、槽内を3室に縦割し、当該槽18を構成
する側壁とスクリーン19および19′によつて
構成される両端の2室をそれぞれ流入路27およ
び流出路28とし、さらに当該スクリーン19お
よび19′の間の空間部の下方に、たとえば多孔
板あるいはスリツトからなる水は通すが充填物2
2および23を支持する支持板24を設けるとと
もに、当該空間部をスクリーン20によつてさら
に2室に縦割し、流入路27側の一方の室に直径
50mm以上の充填物22を充填し、他方の室に直径
25〜30mmの充填物23を充填する。 In addition, a pair of screens 19 and 19' that allow water to pass through but not fillers 22 and 23, which will be described later, are vertically installed in the contact sedimentation tank 18 at intervals, vertically dividing the tank into three chambers, The two chambers at both ends constituted by the side walls and screens 19 and 19' of the tank 18 are defined as an inflow passage 27 and an outflow passage 28, respectively, and further below the space between the screens 19 and 19', For example, a perforated plate or slit that allows water to pass through but is filled with 2
In addition to providing a support plate 24 that supports 2 and 23, the space is further vertically divided into two chambers by a screen 20, and one chamber on the inflow path 27 side has a diameter
Fill the other chamber with a filling material 22 with a diameter of 50 mm or more.
A filling material 23 of 25 to 30 mm is filled.
また前記混合槽16と過槽1を、たとえばバ
イパス管21で接続し、当該混合槽16からの混
合水を水頭差で過槽1に流入できるように構成
する。 Further, the mixing tank 16 and the overtank 1 are connected, for example, by a bypass pipe 21, so that the mixed water from the mixing tank 16 can flow into the overtank 1 with a water head difference.
また当該混合槽16と接触沈殿槽18の流入路
27を、たとえば混合槽出口管15で接続し、さ
らに当該槽18の流出路28と過槽1を、たと
えば接触沈殿槽出口管2で接続し、接触沈殿槽1
8からの流出水を水頭差で過槽1に流入できる
ように構成する。 Further, the mixing tank 16 and the inflow passage 27 of the contact sedimentation tank 18 are connected, for example, by the mixing tank outlet pipe 15, and the outflow passage 28 of the tank 18 and the overflow tank 1 are connected, for example, by the contact sedimentation tank outlet pipe 2. , contact settling tank 1
The structure is such that the outflow water from 8 can flow into the overtank 1 with a water head difference.
また接触沈殿槽18の充填物22および23の
上方に洗浄ノズル25を付設するとともに、当該
槽18の底部に洗浄排水管29を付設する。また
混合槽16の上方に液面検出計26を付設する。 Further, a cleaning nozzle 25 is attached above the fillers 22 and 23 of the contact sedimentation tank 18, and a cleaning drain pipe 29 is attached to the bottom of the tank 18. Further, a liquid level detector 26 is attached above the mixing tank 16.
このような接触沈殿槽18を付設した過槽1
において懸濁物質を含む原水を処理するにあた
り、たとえば原水の濁度が20度以上の高濁度の時
は、あらかじめ原水に凝集剤注入管30より、た
とえば硫酸バン土あるいはポリ塩化アルミニウム
などから選ばれる凝集剤を、たとえば10〜20ppm
注入し、当該原水を原水管31より混合槽16に
流入させ、当該混合槽16において撹拌機17に
よつて原水を急速に撹拌し、小さなフロツクを形
成させる。この混合水を混合槽16から混合槽出
口管15を経て接触沈殿槽18の流入路27へ流
入させ、充填物22および23内を水平に通過さ
せる。 A supertank 1 equipped with such a contact sedimentation tank 18
When treating raw water containing suspended solids, for example, when the raw water has a high turbidity of 20 degrees or more, a coagulant selected from, for example, van sulfate or polyaluminum chloride is added to the raw water from the flocculant injection pipe 30. For example, add a flocculant of 10 to 20 ppm.
The raw water is injected into the mixing tank 16 through the raw water pipe 31, and the raw water is rapidly stirred by the stirrer 17 in the mixing tank 16 to form small flocs. This mixed water is caused to flow from the mixing tank 16 through the mixing tank outlet pipe 15 into the inflow path 27 of the contact sedimentation tank 18, and is passed horizontally through the fillings 22 and 23.
このように混合水を充填物22および23の空
隙を通過させることにより、混合水は充填物22
および23によつて緩速撹拌され、フロツクをさ
らに成長させることができるとともに、比較的大
きいフロツクを充填物22および23の空隙に沈
殿させることができる。 By passing the mixed water through the gaps between the fillers 22 and 23, the mixed water flows through the fillers 22 and 23.
and 23, the flocs can be further grown, and relatively large flocs can be precipitated in the voids of the fillers 22 and 23.
このように当該接触沈殿槽18に混合水を水平
に通過させることにより比較的大きなフロツクを
沈殿させ、原水中の濁度を、たとえば20度程度ま
で低下させることができるので、後段の過槽1
の負荷を減少させることができる。なお充填物2
2および23は直径25mm以上の栗石あるいは砕石
などを用いるとよい。また充填物22および23
を同一の径を有するものを用いても所期の目的を
達成することができるが、本実施態様のように充
填物22を比較的大きな径で、好ましくは直径50
mm以上のもの、また充填物23を比較的小さな径
で、好ましくは25〜30mmのものを用いるとよく、
このようにすると充填物22において主に緩速撹
拌を行なつて、フロツクを十分に成長させ、そし
て充填物23において主に比較的沈降しやすい大
きなフロツクを効率よく沈殿させるという役割を
分担させることができ、より効果的となる。 By passing the mixed water horizontally through the contact sedimentation tank 18 in this way, relatively large flocs can be precipitated and the turbidity in the raw water can be reduced to, for example, about 20 degrees.
load can be reduced. In addition, filling 2
For 2 and 23, it is recommended to use chestnut stone or crushed stone with a diameter of 25 mm or more. Also, the fillings 22 and 23
Although it is possible to achieve the intended purpose by using fillers 22 having the same diameter, as in this embodiment, the filler 22 has a relatively large diameter, preferably a diameter of 50 mm.
mm or more, and the filler 23 has a relatively small diameter, preferably 25 to 30 mm.
In this way, the filling material 22 mainly performs slow stirring to allow the flocs to grow sufficiently, and the filling material 23 mainly performs the role of efficiently settling large flocs that are relatively easy to settle. can be done and become more effective.
本発明の要件となつている接触沈殿槽18は、
当該槽内の充填物22および23に混合水を水平
に通過させる構造とするが、この理由は混合水を
上昇流で通水させると充填物の直径が大きく、そ
の空隙が大きいので、フロツクが充填物に沈殿せ
ずに浮上して、過槽に流入しやすく、また混合
水を下降流で通水しても、やはりフロツクが充填
物層を落下して過槽に流入しやすいという問題
が生ずるからである。 The contact sedimentation tank 18, which is a requirement of the present invention, is
The structure is such that the mixed water passes horizontally through the packings 22 and 23 in the tank.The reason for this is that when the mixed water is passed through in an upward flow, the diameter of the packings is large and the gaps between them are large, so that flocs do not form. The problem is that the flocs float to the surface without settling on the packing and flow into the overtank, and even if the mixed water is passed in a downward flow, the flocs tend to fall down the packing layer and flow into the overtank. This is because it occurs.
本発明のように接触沈殿槽18に充填物22お
よび23を充填するとともに混合水を水平に通過
させると、フロツクの分離効率がよく、混合水
を、たとえば30〜80m/hの高流速で処理するこ
とができるので、接触沈殿槽18は極めて小さな
容量とすることができる。 When the contact sedimentation tank 18 is filled with the fillers 22 and 23 and the mixed water is passed horizontally as in the present invention, floc separation efficiency is high, and the mixed water is processed at a high flow rate of, for example, 30 to 80 m/h. Therefore, the contact settling tank 18 can have an extremely small capacity.
次に充填物22および23を通過させて、原水
中の濁度を低下させた流出水を、流出路28から
接触沈殿槽出口管2を経て過槽1の底部へ水頭
差で流入させる。当該過槽1において接触沈殿
槽18からの流出水を、たとえば10〜20m/hの
流速で砂利層3を上昇させることにより、再び緩
速撹拌し、接触沈殿槽18より流出した小さなブ
ロツクを成長させるとともに、砂利層3で比較的
大きなフロツクを接触Hz過する。次に砂利層3を
上昇した水の約半分量をそのまま砂層4に上昇さ
せ、他の約半分量を下方集水管6および連通管7
を経て砂層4の上方から下降流で通水させて、砂
層4に水を正反対の2方向から通水させながら砂
利層3から流出した小さなフロツクを除去する。
そしてこの2方向からの水を上部集水管8より集
水し、処理水を処理水流出管9より得る。 Next, the effluent water, which has been passed through the fillers 22 and 23 to reduce the turbidity in the raw water, is caused to flow from the outflow path 28 through the contact sedimentation tank outlet pipe 2 to the bottom of the overtank 1 with a difference in water head. In the filter tank 1, the water flowing out from the contact settling tank 18 is slowly stirred again by raising the gravel layer 3 at a flow rate of, for example, 10 to 20 m/h, and the small blocks flowing out from the contact settling tank 18 are grown. At the same time, relatively large flocs are passed through the contact Hz in the gravel layer 3. Next, about half of the water that has risen through the gravel layer 3 is allowed to rise directly to the sand layer 4, and the other half is transferred to the lower water collection pipe 6 and the communication pipe 7.
Water is passed downward from above the sand layer 4 through the sand layer 4, and small flocs flowing out from the gravel layer 3 are removed while water is passed through the sand layer 4 from two opposite directions.
Water from these two directions is collected through the upper water collection pipe 8, and treated water is obtained through the treated water outflow pipe 9.
次に、原水の濁度が、たとえば20度以下のよう
に低濃度の時は、あらかじめ原水に凝集剤注入管
30より前述したような凝集剤を、たとえば数
ppm注入し、当該原水を原水管31より混合槽1
6に流入させ、撹拌機17で原水と凝集剤とを急
速に撹拌し、小さなフロツクを形成させた後、混
合槽16からの混合水をバイパス管21を経て
過槽1の底部に直接流入させて前述したと同様に
過処理を行ない、清澄な処理水を得る。 Next, when the turbidity of the raw water is low concentration, for example, 20 degrees or less, a flocculant as described above is added to the raw water through the flocculant injection pipe 30 in advance, for example, several times.
ppm is injected, and the raw water is passed through the raw water pipe 31 into the mixing tank 1.
6, the raw water and flocculant are rapidly stirred by the stirrer 17 to form small flocs, and then the mixed water from the mixing tank 16 is directly flowed into the bottom of the mixing tank 1 via the bypass pipe 21. Then, perform overtreatment in the same manner as described above to obtain clear treated water.
また接触沈殿槽18の充填物22および23が
目詰りを起こすと、混合槽16の水位が上昇する
が、当該水位が液面検出計26のBの位置まで達
したら原水の流入を中断し、洗浄排水管29より
当該槽18内の水を抜き、次に洗浄ノズル25よ
り洗浄水を噴射して充填物22および23を洗浄
し、充填物22および23に沈殿したフロツクを
洗浄排水管29より除去する。 Furthermore, when the fillers 22 and 23 in the contact sedimentation tank 18 become clogged, the water level in the mixing tank 16 rises, but when the water level reaches position B on the liquid level detector 26, the inflow of raw water is interrupted. The water in the tank 18 is drained from the cleaning drain pipe 29, and then cleaning water is injected from the cleaning nozzle 25 to wash the fillers 22 and 23, and the flocs precipitated on the fillers 22 and 23 are removed from the cleaning drain pipe 29. Remove.
また過槽1の砂利層3および砂層4が目詰り
を起こし、当該槽1の水位が上昇して液面検出計
14のAの位置まで達したら、原水の流入を中断
し、空気を空気流入管12および空気分配管11
を経て流入させるとともに洗浄水を洗浄水流入管
13より高流速の上昇流で流入させ、砂利層3お
よび砂層4に捕捉させた懸濁物質を除去し、その
洗浄排水を洗浄排水管10より排出する。また
過槽1はどのような形式のものも用いることがで
きるが、好ましくは本実施態様のように二方向
過槽あるいは多層過槽、上昇流過槽など、比
較的懸濁物質の捕捉能力の大きな過槽を用いる
とよい。 Furthermore, if the gravel layer 3 and sand layer 4 in the tank 1 become clogged and the water level in the tank 1 rises and reaches position A on the liquid level detector 14, the inflow of raw water is interrupted and air is injected. Pipe 12 and air distribution pipe 11
At the same time, the washing water is made to flow upward through the washing water inflow pipe 13 at a high flow rate to remove the suspended solids trapped in the gravel layer 3 and the sand layer 4, and the washing water is discharged from the washing drainage pipe 10. . Although any type of tank 1 can be used, it is preferably a two-way tank, a multilayer tank, an upflow tank, etc. as in this embodiment, which has a relatively high ability to capture suspended solids. It is best to use a large tank.
以上説明したように、本発明は過槽の前段に
混合槽と特殊な接触沈殿槽を付設したものであ
り、原水の濁度が比較的少ない時は原水に凝集剤
を添加し、そのまま過槽に通水して過処理を
し、清澄な処理水を得ることができるとともに、
原水の濁度が多い時は凝集剤を添加した原水を接
触沈殿槽に通水し、あらかじめ当該槽において懸
濁物質を所定の濃度まで沈殿除去し、過槽への
負荷を減少させてから当該過槽において過処
理するので、原水の濁度が大きく変動するような
原水であつても、効率よく懸濁物質を除去し、清
澄な処理水を一定して得ることができる。 As explained above, the present invention is equipped with a mixing tank and a special contact sedimentation tank before the overtank, and when the turbidity of the raw water is relatively low, a flocculant is added to the raw water and it is directly transferred to the overtank. It is possible to obtain clear treated water by passing water through and over-treating it, as well as
When the raw water has high turbidity, the raw water with a coagulant added is passed through a contact sedimentation tank, and the suspended solids are precipitated and removed in that tank to a predetermined concentration to reduce the load on the overtank. Since overtreatment is carried out in the overtank, suspended matter can be efficiently removed and clear treated water can be consistently obtained even if the raw water has a large turbidity fluctuation.
また本発明の接触沈殿槽は充填物を有し、かつ
当該充填物に原水を水平に通過させるという特殊
な構造となつているので、効率よくフロツクを沈
殿させることができ、しかも高流速で処理するこ
とができるという作用を有し、従来の凝集沈殿装
置に比べ小さな装置でよく、その建設費も少ない
という利点があり、さらに凝集剤の注入量も凝集
沈殿装置に比べ少量でよく、発生汚泥量を少ない
という利点がある。 In addition, the contact sedimentation tank of the present invention has a special structure in which it has a packing material and raw water is passed horizontally through the packing material, so flocs can be precipitated efficiently and treated at a high flow rate. It has the advantage of requiring a smaller device and lower construction costs than conventional coagulation-sedimentation equipment.Furthermore, the amount of flocculant injected is smaller than that of coagulation-sedimentation equipment, which reduces the amount of sludge produced. It has the advantage of being small in quantity.
図は本発明の接触沈殿槽を付設した過槽の実
施態様の一例を示す縦断説明図である。
1……過槽、2……接触沈殿槽出口管、16
……混合槽、18……接触沈殿槽、19……スク
リーン、21……バイパス管、22,23……充
填物、24……支持板、31……原水管。
The figure is a longitudinal sectional view showing an example of an embodiment of a supertank equipped with a contact sedimentation tank according to the present invention. 1...Target tank, 2...Contact sedimentation tank outlet pipe, 16
... Mixing tank, 18 ... Contact sedimentation tank, 19 ... Screen, 21 ... Bypass pipe, 22, 23 ... Filler, 24 ... Support plate, 31 ... Raw water pipe.
Claims (1)
スクリーンで3室に縦割するとともに当該スクリ
ーンの間の空間部に少なくとも直径25mm以上の充
填物を充填した接触沈殿槽とを設け、当該混合槽
と過槽を接続するとともに、当該混合槽と前記
接触沈殿槽と過槽を順に接続し、原水中に存在
する懸濁物質の量が少ない時は凝集剤を添加した
原水を混合槽で混合したのち当該混合水を水頭差
で過槽に直接流入させて過処理し、また原水
中に存在する懸濁物質の量が多い時は当該混合水
を接触沈殿槽内の充填物層に水平に通過させ、当
該充填物層内においてフロツクを成長させるとと
もに比較的大きな粒径のフロツクを沈殿させ、次
いでその流出水を水頭差で過槽に流入させて
過処理するように構成したことを特徴とする接触
沈殿槽を付設した過槽。 2 接触沈殿槽のスクリーン間の空間部をさらに
スクリーンで2室に縦割し、一方の室に直径50mm
以上の充填物を充填し、他方の室に25〜35mmの充
填物を充填し、混合水を一方の室から他方の室へ
水平に通過させることを特徴とする特許請求の範
囲第1項記載の接触沈殿槽を付設した過槽。[Claims] 1. In the upper part of the tank, there is a mixing tank, the inside of the tank is vertically divided into three chambers by a pair of screens, and the space between the screens is filled with a filler having a diameter of at least 25 mm. At the same time, the mixing tank is connected to the contact sedimentation tank and the overtank, and the mixing tank is connected to the contact sedimentation tank and the overtank in order, and when the amount of suspended solids present in the raw water is small, flocculation After mixing the raw water to which the agent has been added in a mixing tank, the mixed water is directly flowed into a supertank with a difference in water head for overtreatment, and when there is a large amount of suspended solids in the raw water, the mixed water is The water is allowed to pass horizontally through a packed layer in a sedimentation tank, allowing flocs to grow in the packed layer and flocs with a relatively large particle size are precipitated, and then the effluent water is allowed to flow into a sedimentation tank using a head difference. An overtank equipped with a contact sedimentation tank, characterized in that it is configured to carry out treatment. 2 The space between the screens of the contact sedimentation tank is further vertically divided into two chambers with a screen, and one chamber has a diameter of 50 mm.
Claim 1, characterized in that the other chamber is filled with a 25-35 mm filler, and the mixed water is passed horizontally from one chamber to the other chamber. An overtank equipped with a contact sedimentation tank.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP55125331A JPS5750513A (en) | 1980-09-11 | 1980-09-11 | Filtration tank added with contact settling tank |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP55125331A JPS5750513A (en) | 1980-09-11 | 1980-09-11 | Filtration tank added with contact settling tank |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5750513A JPS5750513A (en) | 1982-03-25 |
| JPS6354407B2 true JPS6354407B2 (en) | 1988-10-27 |
Family
ID=14907459
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP55125331A Granted JPS5750513A (en) | 1980-09-11 | 1980-09-11 | Filtration tank added with contact settling tank |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5750513A (en) |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP3640285B2 (en) * | 1997-12-26 | 2005-04-20 | オルガノ株式会社 | Coagulation sedimentation equipment |
| JP2006218388A (en) * | 2005-02-10 | 2006-08-24 | Shimizu Gokin Seisakusho:Kk | Water treat method and water treatment apparatus |
| JP2006297438A (en) * | 2005-04-19 | 2006-11-02 | Seiji Kobayashi | Wire rod connection tool |
| US10550018B2 (en) * | 2015-05-04 | 2020-02-04 | DOOSAN Heavy Industries Construction Co., LTD | Media filter having nonpowered mixing and coagulation basin, and seawater desalination plant and dissolved air floatation apparatus using same |
-
1980
- 1980-09-11 JP JP55125331A patent/JPS5750513A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5750513A (en) | 1982-03-25 |
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