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JP2006198571A - Precipitation device - Google Patents

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JP2006198571A
JP2006198571A JP2005015264A JP2005015264A JP2006198571A JP 2006198571 A JP2006198571 A JP 2006198571A JP 2005015264 A JP2005015264 A JP 2005015264A JP 2005015264 A JP2005015264 A JP 2005015264A JP 2006198571 A JP2006198571 A JP 2006198571A
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sludge
precipitation
raw water
tank body
pit
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Satoshi Miwa
聡志 三輪
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Kurita Water Industries Ltd
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Kurita Water Industries Ltd
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Abstract

【課題】工場で製作して容易に搬送することができ、現地での据付工期を大幅に短縮することができるとともに、沈殿槽本体底部に沈澱・濃縮された懸濁物質を、動力機付き掻取機を要することなく容易に排出することができ、沈殿槽本体内部に多数の傾斜板や充填材を設ける必要のない小型で低コストの沈澱装置を提供すること。
【解決手段】内部に隔壁を持たない矩形体状の沈殿槽本体2と、該沈殿槽本体2の一側面上部に設けられた入口トラフ(原水流入口)3と、同沈殿槽本体2の他側面上部に設けられた出口トラフ(処理水排出口)4とを有する沈澱装置1において、前記沈殿槽本体2の底部に、前記入口トラフ3から出口トラフ4の方向に複数のスラッジピット7を設ける。
【選択図】図1
[PROBLEMS] To easily manufacture and transport in a factory, greatly reduce the installation period at the site, and to scrape and concentrate suspended substances precipitated and concentrated at the bottom of the sedimentation tank body. To provide a small-sized and low-cost precipitation device that can be easily discharged without requiring a machine and does not require a large number of inclined plates or fillers inside the precipitation tank body.
A rectangular sedimentation tank body 2 having no partition wall inside, an inlet trough (raw water inlet) 3 provided on one side upper part of the sedimentation tank body 2, and other sedimentation tank body 2 In a sedimentation apparatus 1 having an outlet trough (treated water discharge port) 4 provided at an upper side surface, a plurality of sludge pits 7 are provided at the bottom of the sedimentation tank body 2 in the direction from the inlet trough 3 to the outlet trough 4. .
[Selection] Figure 1

Description

本発明は、凝集剤が添加された原水に含まれる懸濁物質(汚泥、スラッジ等)を沈澱させてこれを分離するための沈澱装置に関するものである。   The present invention relates to a precipitation apparatus for precipitating suspended substances (sludge, sludge, etc.) contained in raw water to which a flocculant has been added and separating them.

下水処理設備や化学工場等における廃水処理設備においては、工場廃水、河川水、湖沼水、井戸水等の原水を処理して清浄な水とし、その水を再利用したり、河川等に放流すること等が行われている。その処理工程の一部には、原水に凝集剤を添加し、該原水中に含まれる懸濁物質を沈澱させてこれを分離する沈澱装置が用いられる。   In wastewater treatment facilities such as sewage treatment facilities and chemical factories, raw water such as factory wastewater, river water, lake water, and well water is processed into clean water, and the water is reused or discharged into rivers, etc. Etc. are done. In a part of the treatment process, a precipitation apparatus is used in which a flocculant is added to raw water, and suspended substances contained in the raw water are precipitated and separated.

ところで、従来の沈澱装置としては、縦長の円筒部の底部に逆円錐状のスラッジピットを取り付けて成る沈殿槽本体のスラッジピットの少し上の側部から原水を供給し、上澄水を処理水として沈殿槽本体上部から排出する形式のものが一般的である。   By the way, as a conventional sedimentation apparatus, raw water is supplied from the side part slightly above the sludge pit of the main body of the sedimentation tank formed by attaching an inverted conical sludge pit to the bottom of the vertically long cylindrical part, and the supernatant water is used as treated water. The type of discharging from the upper part of the precipitation tank body is common.

又、立方体状や直方体状の矩形体形状の沈殿槽本体の一側面から原水を供給し、上澄水を処理水として同沈殿槽本体の他側面から排出する沈澱装置も提案されている(特許文献1〜3参照)。   In addition, a precipitation device has also been proposed in which raw water is supplied from one side of a cubic or rectangular parallelepiped shaped precipitation tank body, and the supernatant water is treated and discharged from the other side of the precipitation tank body (Patent Literature). 1-3).

特開2003−019403号公報JP 2003-019403 A 特開2003−024709号公報JP 2003-024709 A 特開2001−239106号公報JP 2001-239106 A

しかしながら、縦長の円筒状に成形された従来の沈澱装置においては、原水負荷量にもよるが、沈殿槽本体の円筒部の長さが4m以上、全体の高さが4〜6m以上となり、高さが高いために沈殿槽本体を工場で製作すると、これの容易な搬送手段がなかった。このため、装置を現地で製作してこれを据え付ける建設工事が必要となり、工期が長くなる他、本体形状が円筒形であるために現地の平面スペースを活用することができない等の問題があった。   However, in the conventional sedimentation device formed into a vertically long cylindrical shape, although depending on the raw water load, the length of the cylindrical portion of the sedimentation tank body is 4 m or more, and the overall height is 4 to 6 m or more. Due to its high height, when the sedimentation tank body was manufactured at the factory, there was no easy means for conveying it. For this reason, construction work to manufacture and install the device is necessary, and the construction period becomes longer, and the shape of the main body is cylindrical, so the local plane space cannot be used. .

他方、矩形体形状の沈殿槽本体を備える沈澱装置においても、原水負荷量によっては幅が4m以上、高さが4〜6m程度となり、又、懸濁物質の沈澱効率を高めるために槽内部に多数の傾斜板を設けたり、充填材を充填する必要がある他、槽内底部に沈澱・濃縮される懸濁物質を排出するための動力機付き掻取機が必要となり、装置全体の大型化やコストアップを招くという問題があった。   On the other hand, in a sedimentation apparatus equipped with a rectangular shaped sedimentation tank body, the width is 4 m or more and the height is about 4 to 6 m depending on the raw water load, and in order to increase the sedimentation efficiency of suspended matter, In addition to providing a large number of inclined plates and filling with fillers, a scraper with a motor for discharging suspended solids that are precipitated and concentrated at the bottom of the tank is required. There was a problem of incurring a cost increase.

本発明は上記問題に鑑みてなされたもので、その目的とする処は、工場で製作して容易に搬送することができ、現地での据付工期を大幅に短縮することができるとともに、沈殿槽本体底部に沈澱・濃縮された懸濁物質を、動力機付き掻取機を要することなく容易に排出することができ、沈殿槽本体内部に多数の傾斜板や充填材を設ける必要のない小型で低コストの沈澱装置を提供することにある。   The present invention has been made in view of the above problems, and the intended process is that it can be manufactured and transported easily at the factory, and the installation period at the site can be greatly shortened, and the settling tank Suspended matter precipitated and concentrated at the bottom of the main body can be easily discharged without the need for a powered scraper, and it is small and low in the number of inclined plates and fillers that do not need to be provided inside the precipitation tank body. It is to provide a cost settling device.

上記目的を達成するため、請求項1記載の発明は、内部に隔壁を持たない矩形体状の沈殿槽本体と、該沈殿槽本体の一側面上部に設けられた原水流入口と、同沈殿槽本体の他側面上部に設けられた処理水排出口とを有する沈澱装置において、前記沈殿槽本体の底部に、前記原水流入口から前記処理水排出口の方向に複数のスラッジピットを設けたことを特徴とする。   In order to achieve the above-mentioned object, the invention described in claim 1 includes a rectangular sedimentation tank body having no partition wall inside, a raw water inlet provided on one side upper part of the precipitation tank body, and the sedimentation tank. In the sedimentation apparatus having a treated water discharge port provided on the other side upper part of the main body, a plurality of sludge pits are provided at the bottom of the settling tank body from the raw water inlet to the treated water discharge port. Features.

請求項2記載の発明は、請求項1記載の発明において、前記各スラッジピットは、前記原水流入口側から前記処理水排出口側に向かって下る第1の傾斜部と、前記処理水排出口から前記原水流入口に向かって下る第2の傾斜部を有することを特徴とする。   According to a second aspect of the present invention, in the first aspect of the invention, each sludge pit includes a first inclined portion that descends from the raw water inlet side toward the treated water discharge port side, and the treated water discharge port. It has the 2nd inclination part which goes down toward the said raw | natural water inflow port, It is characterized by the above-mentioned.

請求項3記載の発明は、請求項2記載の発明において、前記各スラッジピットの前記第1の傾斜部と前記第2の傾斜部の傾斜角度を30°〜70°に設定したことを特徴とする。   The invention according to claim 3 is characterized in that, in the invention according to claim 2, the inclination angle of the first inclined portion and the second inclined portion of each sludge pit is set to 30 ° to 70 °. To do.

請求項4記載の発明は、請求項1〜3の何れかに記載の発明において、前記各スラッジピットの深さhを前記沈殿槽本体内の水位Hに対してh=(0.2〜0.8)Hに設定したことを特徴とする。   The invention according to claim 4 is the invention according to any one of claims 1 to 3, wherein the depth h of each sludge pit is h = (0.2 to 0) with respect to the water level H in the settling tank body. .8) It is characterized by being set to H.

請求項5記載の発明は、請求項2〜4の何れかに記載の発明において、何れかのスラッジピットの前記第2の上端部に、汚泥の乗り越えを防ぐための返し部を設けたことを特徴とする。   The invention according to claim 5 is the invention according to any one of claims 2 to 4, wherein a return portion for preventing the sludge from getting over is provided at the second upper end portion of any sludge pit. Features.

請求項6記載の発明は、請求項1〜5の何れかに記載の発明において、前記各スラッジピットの底部に、汚泥を引き抜くための汚泥引抜管をそれぞれ接続し、前記原水流入口に近い汚泥引抜管ほど汚泥引き抜き量が多くなるよう制御することを特徴とする。   The invention according to claim 6 is the invention according to any one of claims 1 to 5, wherein a sludge extraction pipe for extracting the sludge is connected to the bottom of each sludge pit, and the sludge close to the raw water inlet It is characterized by controlling so that the amount of sludge extraction increases as the drawing tube.

請求項7記載の発明は、請求項6記載の発明において、前記各汚泥引抜管にバルブを設け、各バルブの開度を前記原水流入口に近いものほど大きく設定したことを特徴とする。   A seventh aspect of the invention is characterized in that, in the sixth aspect of the invention, a valve is provided in each sludge extraction pipe, and the opening degree of each valve is set to be larger as it is closer to the raw water inlet.

請求項8記載の発明は、請求項6記載の発明において、前記各汚泥引抜管の口径を前記原水流入口に近いものほど大きく設定したことを特徴とする。   The invention according to claim 8 is characterized in that, in the invention according to claim 6, the diameter of each sludge extraction pipe is set to be larger as it is closer to the raw water inlet.

請求項1記載の発明によれば、沈殿槽本体を立方体状や直方体状の矩形体形状としたため、これを工場で製作して現地まで容易に搬送することができるとともに、現地の平面スペースを活用して短期間でこれを据え付けることができ、工期を大幅に短縮することができる。又、沈殿槽本体内に多数の傾斜板や充填材を設ける必要がないため、沈殿槽本体の構造が単純化し、その小型化とコストダウンが図られる。更に、沈殿槽本体の底部に、原水流入口から処理水排出口の方向に沿って設けられた複数のスラッジピットの各底部に沈澱・濃縮された懸濁物質を各スラッジピットの底部からそれぞれ排出することができるため、動力機付き掻取機を要することなく懸濁物質を容易に排出することができる。   According to the first aspect of the present invention, since the precipitation tank main body has a rectangular shape such as a cube or a rectangular parallelepiped, it can be manufactured at the factory and easily transported to the site, and the plane space on the site can be utilized. This can be installed in a short period of time, and the construction period can be greatly shortened. In addition, since it is not necessary to provide a large number of inclined plates and fillers in the settling tank body, the structure of the settling tank body is simplified, and the size and cost can be reduced. Furthermore, suspended substances precipitated and concentrated at the bottom of each sludge pit provided along the direction from the raw water inlet to the treated water outlet at the bottom of the settling tank body are discharged from the bottom of each sludge pit. Therefore, suspended substances can be easily discharged without requiring a scraper with a motor.

請求項2記載の発明によれば、沈殿槽本体の各スラッジピットにおいては、原水流入口側から処理水排出口側に向かって下る第1の傾斜部によって、入口部での懸濁物質の沈降距離が短縮されるため、懸濁物質の沈澱時間も短縮されて沈澱効率が高められる。又、処理水排出口から原水流入口に向かって下る第2の傾斜部によって、出口部での懸濁物質の該第2の傾斜部との衝突が促され、懸濁物質のキャリーオーバーが防がれて沈澱効率が高められる。そして、各スラッジピットの入口部の第1の傾斜部と出口部の第2の傾斜部によって、懸濁物質をスラッジピットの底部中央に自然沈降濃縮させることができるため、各スラッジピットの底部に沈殿した懸濁物質を容易且つ効率良く排出することができる。   According to invention of Claim 2, in each sludge pit of a sedimentation tank main body, sedimentation of suspended solids in an inlet part is carried out by the 1st inclination part which goes down toward a treated water discharge port side from a raw | natural water inlet side. Since the distance is shortened, the sedimentation time of the suspended substance is shortened and the precipitation efficiency is increased. In addition, the second inclined portion that descends from the treated water discharge port toward the raw water inlet facilitates the collision of the suspended substance at the outlet with the second inclined portion, thereby preventing the suspended substance from carrying over. This improves the precipitation efficiency. Since the suspended substance can be naturally settled and concentrated at the center of the bottom of the sludge pit by the first inclined portion of the inlet portion and the second inclined portion of the outlet portion of each sludge pit, The precipitated suspended matter can be discharged easily and efficiently.

請求項3記載の発明によれば、各スラッジピットの第1の傾斜部と第2の傾斜部の傾斜角度を30°〜70°に設定したため、沈澱槽本体の高さを抑えつつ、懸濁物質の沈澱濃縮を良好に行うことができる。尚、傾斜角度が小さ過ぎると懸濁物質の自然沈降濃縮が良好になされず、逆に大き過ぎると槽の高さを高くする必要がある。従って、傾斜角度としては、30°〜70°が好ましく、40°〜60°であることがより好ましい。   According to invention of Claim 3, since the inclination angle of the 1st inclination part of each sludge pit and the 2nd inclination part was set to 30 degrees-70 degrees, it suspended, suppressing the height of a precipitation tank main body. Precipitation concentration of the substance can be performed well. If the tilt angle is too small, the natural sedimentation and concentration of the suspended solids is not good. Conversely, if the tilt angle is too large, the height of the tank needs to be increased. Accordingly, the inclination angle is preferably 30 ° to 70 °, and more preferably 40 ° to 60 °.

請求項4記載の発明によれば、各スラッジピットの深さhを沈殿槽本体の水位Hに対してh=(0.2〜0.8)Hに設定したため、懸濁物質のキャリーオーバーを抑えつつ、各スラッジピットへの懸濁物質の沈澱量の偏りを防ぐことができる。尚、スラッジピットの深さhの沈殿槽本体の水位Hに対する比率h/Hが小さ過ぎると、懸濁物質のキャリーオーバーが発生し易く、逆に大き過ぎると第2の傾斜部の上端部と水面との間が狭くなるため、第2の傾斜部を乗り越える水の線速度が大きくなり、懸濁物質が巻き込まれてキャリーオーバーが発生し易くなる。従って、比率h/Hとしては0.2〜0.8が好ましく、0.3〜0.5であることがより好ましい。   According to invention of Claim 4, since the depth h of each sludge pit was set to h = (0.2-0.8) H with respect to the water level H of a sedimentation tank main body, the carry over of a suspended solid was carried out. While suppressing, it is possible to prevent unevenness of the amount of suspended matter precipitated in each sludge pit. If the ratio h / H of the sludge pit depth h to the water level H of the sedimentation tank main body is too small, the suspended matter is likely to carry over, and conversely if too large, the upper end of the second inclined portion Since the gap with the water surface is narrowed, the linear velocity of the water over the second inclined portion is increased, and the suspended matter is entrained and carry-over easily occurs. Therefore, the ratio h / H is preferably 0.2 to 0.8, and more preferably 0.3 to 0.5.

請求項5記載の発明によれば、スラッジピットの第2の傾斜部の上端部に返し部を設けたため、懸濁物質のキャリーオーバーが抑えられて沈澱効率が高められる。   According to the fifth aspect of the present invention, since the return portion is provided at the upper end portion of the second sloping portion of the sludge pit, the carry-over of suspended substances is suppressed and the precipitation efficiency is increased.

請求項6記載の発明によれば、原水流入口に近い汚泥引抜管、つまり懸濁物質の沈澱量が多いスラッジピットに接続された汚泥引抜管ほど汚泥の引抜量が多くなるよう制御するため、各スラッジピットに沈澱する懸濁物質を確実に引き抜いて排出することができる。   According to the invention of claim 6, in order to control the sludge extraction pipe close to the raw water inlet, that is, the sludge extraction pipe connected to the sludge pit with a large amount of suspended solids, so that the amount of sludge extraction increases. Suspended substances that settle in each sludge pit can be reliably pulled out and discharged.

請求項7記載の発明によれば、各汚泥引抜管にバルブを設け、各バルブの開度を原水流入口に近いものほど大きく設定し、請求項8記載の発明によれば、各汚泥引抜管の口径を原水流入口に近いものほど大きく設定したため、各スラッジピットにおける懸濁物質の沈澱量に応じた引抜量を確保することができ、各スラッジピットに沈澱する懸濁物質を確実に引き抜いて排出することができる。   According to the seventh aspect of the present invention, each sludge extraction pipe is provided with a valve, and the opening degree of each valve is set to be larger as it is closer to the raw water inlet. According to the eighth aspect of the invention, each sludge extraction pipe is set. As the diameter of the water is closer to the raw water inlet, it is possible to secure a drawing amount corresponding to the amount of suspended matter settled in each sludge pit, and to ensure that the suspended matter settled in each sludge pit is pulled out. Can be discharged.

以下に本発明の実施の形態を添付図面に基づいて説明する。   Embodiments of the present invention will be described below with reference to the accompanying drawings.

図1は本発明に係る沈澱装置の側断面図、図2は同沈澱装置の沈殿槽本体の平面図、図3(a)〜(i)は返し部の種々の形態を示す斜視図である。   1 is a side sectional view of a precipitation apparatus according to the present invention, FIG. 2 is a plan view of a precipitation tank body of the precipitation apparatus, and FIGS. 3A to 3I are perspective views showing various forms of a return portion. .

図1に示す沈澱装置1は、内部に隔壁を持たない直方体状の沈殿槽本体2と、該沈殿槽本体2の一側面上部(図1及び図2の左側面上部)に設けられた原水流入口としての入口トラフ3と、同沈殿槽本体2の他側面上部(図1及び図2の右側面上部)に設けられた処理水排出口としての出口トラフ4を備えている。そして、図1に示すように、沈殿槽本体2の前記入口トラフ3には原水供給管5が接続され、前記出口トラフ4には処理水排出管6が接続されている。   The precipitation apparatus 1 shown in FIG. 1 includes a rectangular parallelepiped precipitation tank body 2 that does not have a partition inside, and a raw water flow provided on one side upper part (the left side upper part in FIGS. 1 and 2) of the precipitation tank body 2. An inlet trough 3 as an inlet and an outlet trough 4 as a treated water discharge port provided at the other side upper part (upper right side in FIGS. 1 and 2) of the same sedimentation tank main body 2 are provided. As shown in FIG. 1, a raw water supply pipe 5 is connected to the inlet trough 3 of the settling tank body 2, and a treated water discharge pipe 6 is connected to the outlet trough 4.

ところで、本実施の形態に係る沈澱装置1においては、前記沈殿槽本体2の底部に、前記入口トラフ3から前記出口トラフ4の方向(図1及び図2の左から右方向)に3つのスラッジピット7が並設されており、沈殿槽本体2は三槽型沈澱槽を構成している。   By the way, in the sedimentation apparatus 1 according to the present embodiment, three sludges in the direction from the inlet trough 3 to the outlet trough 4 (from the left to the right in FIGS. 1 and 2) are provided at the bottom of the sedimentation tank body 2. The pits 7 are juxtaposed, and the settling tank body 2 constitutes a three tank type settling tank.

上記各スラッジピット7は、下方に向かって先細に成形され、その入口側(図1の左側)には、入口側から平坦な底部7cに向かって(図1の左から右に向かって)下がる第1の傾斜部7aが設けられ、出口側(図1の右側)には、底部7cから出口側に向かって(図1の左から右に向かって)立ち上がる(出口から入口(図1の右から左)に向かって下がる)第2の傾斜部7bが設けられている。   Each of the sludge pits 7 is tapered downward, and descends from the entrance side (left side in FIG. 1) toward the flat bottom 7c (from left to right in FIG. 1) on the entrance side. A first inclined portion 7a is provided, and rises from the bottom portion 7c toward the outlet side (from the left to the right in FIG. 1) on the outlet side (the right side in FIG. 1) (from the outlet to the inlet (the right side in FIG. 1) The second inclined portion 7b is provided, which is lowered from the left to the left).

ここで、各スラッジピット7の第1の傾斜部7aの傾斜角度θ1と第2の傾斜部7bの傾斜角度θ2は、共に30°〜70°に設定されている。又、各スラッジピット7の深さhは、沈殿槽本体2内の水位Hに対してh=(0.2〜0.8)Hに設定されている。   Here, the inclination angle θ1 of the first inclined portion 7a and the inclination angle θ2 of the second inclined portion 7b of each sludge pit 7 are both set to 30 ° to 70 °. The depth h of each sludge pit 7 is set to h = (0.2 to 0.8) H with respect to the water level H in the sedimentation tank body 2.

又、何れかのスラッジピット7の第2の傾斜部7bの上端部には、懸濁物質(以下、「汚泥」と称する)のキャリーオーバーを防ぐための返し部8が設けられている。図1においては、出口トラフ4に最も近いスラッジピット7の第2の傾斜部7bの上端部においても、出口トラフ4への汚泥のキャリーオーバーを防ぐための返し部8が設けられており、処理水へのキャリーオーバーの防止を確実に行うようにしている。   A return portion 8 is provided at the upper end portion of the second inclined portion 7b of any sludge pit 7 to prevent carry-over of suspended matter (hereinafter referred to as “sludge”). In FIG. 1, a return portion 8 is provided at the upper end portion of the second sloping portion 7 b of the sludge pit 7 closest to the outlet trough 4 to prevent carry of sludge to the outlet trough 4. It is sure to prevent carry-over into water.

ここで、本実施の形態では、各返し部8として、図3(a)に示すような屋根型の物を使用した(但し、出口トラフ4に最も近いスラッジピット7の第2の傾斜部7bの上端部においては、図3(a)に示すような屋根型のものを側面視で左右半分にして成る図3(i)に示すものを使用した)が、返し部8としては、汚泥が第2の傾斜部7bを乗り越えるのを阻止することができる構造のものであれば良く、図3(b)に示すような円柱型のもの、同図(c)及び(d)に示すような楕円柱型のもの、同図(e)及び(f)に示すような角柱型のもの、同図(g)に示すような傾斜板型のもの、同図(h)に示すような輪切型のもの等が採用される。一方、出口トラフ4に最も近いスラッジピット7の第2の傾斜部7bの上端部に設ける返し部8としては、図3(i)に示すものの他、図3(a)〜(h)に示した構造のものを側面視で左右半分にした形状のものを用いることができる。   Here, in the present embodiment, a roof-type object as shown in FIG. 3A is used as each return portion 8 (however, the second inclined portion 7b of the sludge pit 7 closest to the exit trough 4). 3 (a) in which the roof type as shown in FIG. 3 (a) is made into a left and right half in a side view), but the return portion 8 is made of sludge. Any structure can be used as long as it can prevent the second inclined portion 7b from being overcome, such as a cylindrical type as shown in FIG. 3B, as shown in FIGS. Elliptical column type, prismatic type as shown in FIGS. 5 (e) and (f), inclined plate type as shown in FIG. 5 (g), and ring slice as shown in FIG. A type or the like is adopted. On the other hand, as the return portion 8 provided at the upper end portion of the second inclined portion 7b of the sludge pit 7 closest to the exit trough 4, in addition to the one shown in FIG. 3 (i), the return portion 8 shown in FIGS. The thing of the shape which made the right-and-left half the thing of the structure from the side view can be used.

他方、沈殿槽本体2の各スラッジピット7の底部7cには汚泥引抜管9がそれぞれ接続されており、各汚泥引抜管9にはバルブV1,V2,V3と流量計10がそれぞれ設けられている。そして、各スラッジピット7の底部7cから下方へ延びる計3本の汚泥引抜管9は、排泥管11に合流し、この排泥管11の途中にはポンプ12が設けられている。尚、本実施の形態では、3本の汚泥引抜管9としては同一口径のものが使用されている。   On the other hand, a sludge extraction pipe 9 is connected to the bottom 7c of each sludge pit 7 of the sedimentation tank body 2, and each sludge extraction pipe 9 is provided with valves V1, V2, V3 and a flow meter 10, respectively. . A total of three sludge extraction pipes 9 extending downward from the bottom 7 c of each sludge pit 7 merge into the sludge pipe 11, and a pump 12 is provided in the middle of the sludge pipe 11. In the present embodiment, the three sludge extraction pipes 9 have the same diameter.

次に、以上の構成を有する沈澱装置1の作用を説明する。   Next, the operation of the precipitation apparatus 1 having the above configuration will be described.

凝集剤が添加されて混和された工場廃水や河川水等の原水は、原水供給管5から沈澱装置1の入口トラフ3を経て沈殿槽本体2内に供給され、出口トラフ4に向かって流れる間に、これに含まれる汚泥が重力によって自然沈降し、沈殿槽本体2の底部に並設された3つのスラッジピット7に沈澱濃縮されていく。   Raw water such as factory waste water or river water mixed with a flocculant is supplied from the raw water supply pipe 5 through the inlet trough 3 of the settling device 1 into the settling tank body 2 and flows toward the outlet trough 4. In addition, the sludge contained therein is naturally settled by gravity, and is precipitated and concentrated in three sludge pits 7 arranged in parallel at the bottom of the settling tank body 2.

即ち、各スラッジピット7においては、自然沈降する汚泥が入口側の第1の傾斜部7aと出口側の第2の傾斜部7bに沿って底部7cの中央に集められて沈殿し、この沈殿した汚泥は、ポンプ12が駆動されることによって各汚泥引抜管9からそれぞれ引き抜かれて排出される。そして、計3本の汚泥引抜管9によって引き抜かれた各汚泥は排泥管11へと流れて合流し、排泥管11から不図示の汚泥処理施設へと送られて処理に供される。   That is, in each sludge pit 7, the sludge that naturally settles is collected and precipitated at the center of the bottom 7c along the first inclined portion 7a on the inlet side and the second inclined portion 7b on the outlet side. The sludge is extracted from each sludge extraction tube 9 and discharged by driving the pump 12. And each sludge extracted by the three sludge extraction pipe | tubes 9 in total flows into the sludge pipe | tube 11, merges, is sent to the sludge treatment facility not shown from the sludge pipe | tube 11, and is used for a process.

他方、汚泥が分離除去された原水は、処理水として沈殿槽本体2の出口トラフ4から処理水排出管6へと排出されて再利用されたり、河川に放流されたりする。   On the other hand, the raw water from which sludge has been separated and removed is discharged as treated water from the outlet trough 4 of the settling tank body 2 to the treated water discharge pipe 6 and reused or discharged into the river.

ところで、汚泥の沈澱量は、入口トラフ3に近い(即ち、原水の流れ方向に対して上流側の)スラッジピット7ほど多いため、本実施の形態では、汚泥引抜管9からの単位時間当たりの汚泥引抜量も入口トラフ3に近い汚泥引抜管9ほど多くなるように制御している。具体的には、汚泥引抜管9にそれぞれ設けられたバルブV1,V2,V3の開度を入口トラフ3に近いものほど大きく設定した。つまり、バルブV1,V2,V3の開度をこの順に次第に小さくなるよう設定した。このように設定することによって、各スラッジピット7における汚泥の沈澱量に応じた引抜量を確保することができ、各スラッジピット7に沈澱する汚泥を確実に引き抜いて排出することができる。   By the way, the amount of sludge settled is as large as the sludge pit 7 which is close to the inlet trough 3 (that is, upstream of the flow direction of the raw water). The sludge extraction amount is also controlled so as to increase as the sludge extraction pipe 9 close to the inlet trough 3. Specifically, the opening degree of the valves V1, V2, and V3 provided in the sludge extraction pipe 9 is set to be larger as it is closer to the inlet trough 3. That is, the opening degrees of the valves V1, V2, and V3 are set to gradually decrease in this order. By setting in this way, it is possible to secure a drawing amount corresponding to the amount of sludge settling in each sludge pit 7, and it is possible to reliably draw out and discharge the sludge settling in each sludge pit 7.

尚、汚泥引抜管9からの単位時間当たりの汚泥引抜量を入口トラフ3に近い汚泥引抜管9ほど多くなるように制御する他の形態としては、例えば図4、図5に示すようなものが考えられる。図4及び図5においては、図1に示したものと同一要素には同一符号を付している。   In addition, as another form which controls so that the sludge extraction amount per unit time from the sludge extraction pipe | tube 9 may increase so that the sludge extraction pipe | tube 9 close | similar to the entrance trough 3 may have a thing as shown, for example in FIG. Conceivable. 4 and 5, the same elements as those shown in FIG. 1 are denoted by the same reference numerals.

図4に示す形態では、各汚泥引抜管9−1,9−2,9−3の口径φd1,φd2,φd3を入口に近いものほど大きく設定している(φd1>φd2>φd3)。尚、図4において、Vはバルブである。   In the embodiment shown in FIG. 4, the diameters φd1, φd2, and φd3 of the sludge extraction tubes 9-1, 9-2, and 9-3 are set larger as they are closer to the inlet (φd1> φd2> φd3). In FIG. 4, V is a valve.

又、図5に示す形態では、各汚泥引抜管9にポンプP1,P2,P3とバルブV1,V2,V3及び流量計10をそれぞれ設け、バルブV1,V2,V3の開度を入口トラフ3に近いものほど大きく設定し、或はポンプP1,P2,P3の容量を入口トラフ3に近いものほど大きく設定している。   In the form shown in FIG. 5, pumps P1, P2, P3, valves V1, V2, V3 and a flow meter 10 are provided in each sludge extraction pipe 9, and the opening degree of the valves V1, V2, V3 is set to the inlet trough 3. The closer one is set larger, or the capacity of the pumps P 1, P 2, P 3 is set closer to the inlet trough 3.

而して、図4及び図5に示す形態によっても、各スラッジピット7における汚泥の沈澱量に応じた引抜量を確保することができ、各スラッジピット7に沈澱する汚泥を確実に引き抜いて排出することができる。   4 and FIG. 5, it is possible to secure an amount of extraction corresponding to the amount of sludge settled in each sludge pit 7, and the sludge settled in each sludge pit 7 is reliably extracted and discharged. can do.

又、図1及び図5に示す構成においては、各スラッジピット7からの汚泥の引抜量を制御するために、各スラッジピット7内にそれぞれ汚泥界面計(図示せず)を設置することができる。汚泥界面計により各スラッジピット7内の沈降汚泥量を計測し、計測された沈降汚泥量に応じて、バルブV1,V2,V3の開度を調節することができ、各スラッジピット7内の汚泥量を効率的に制御することができる。   In the configuration shown in FIGS. 1 and 5, a sludge interface meter (not shown) can be installed in each sludge pit 7 in order to control the amount of sludge drawn from each sludge pit 7. . The amount of settled sludge in each sludge pit 7 is measured by a sludge interface meter, and the opening degree of the valves V1, V2, V3 can be adjusted according to the measured amount of settled sludge, and the sludge in each sludge pit 7 can be adjusted. The amount can be controlled efficiently.

更に、各スラッジピット7においては、第1の傾斜部7aによって、入口部での汚泥の沈降距離が短縮されるため、汚泥の沈澱時間も短縮されて沈澱効率が高められる。又、第2の傾斜部7bによって、出口部での汚泥の該第2の傾斜部7bとの衝突が促されるため、汚泥のキャリーオーバーが防がれ、これによっても沈澱効率が高められる。   Furthermore, in each sludge pit 7, since the sludge settling distance at the inlet is shortened by the first inclined portion 7a, the sludge settling time is shortened and the settling efficiency is increased. Moreover, since the second sloping portion 7b promotes the collision of sludge with the second sloping portion 7b at the outlet portion, the sludge carry-over is prevented, and this also increases the precipitation efficiency.

そして、本実施の形態では、隣接するスラッジピット7の第2の傾斜部7bと第1の傾斜部7aとの接続部(頂部)に返し部8を設けたため、汚泥のキャリーオーバー(乗り越え)が該返し部8によって抑えられ、このことによっても沈澱効率が高められる。   And in this Embodiment, since the return part 8 was provided in the connection part (top part) of the 2nd inclination part 7b of the adjacent sludge pit 7, and the 1st inclination part 7a, the carry over (climbing) of sludge is carried out. It is restrained by the return portion 8, and this also increases the precipitation efficiency.

ところで、各スラッジピット7の第1の傾斜部7aと第2の傾斜部7bの傾斜角度θ1,θ2が小さ過ぎると汚泥の自然沈降濃縮が良好になされず、逆に大き過ぎると沈澱槽本体2の高さを高くする必要がある。従って、傾斜角度θ1,θ2としては、30°〜70°が好ましく、40°〜60°であることがより好ましい。本実施の形態では、傾斜角度θ1,θ2を30°〜70°に設定したため、沈澱槽本体2の高さを抑えつつ、汚泥の沈澱濃縮を良好に行うことができた。   By the way, if the slant angles θ1 and θ2 of the first sloping portion 7a and the second sloping portion 7b of each sludge pit 7 are too small, the natural sedimentation and concentration of sludge will not be good. It is necessary to increase the height. Accordingly, the inclination angles θ1 and θ2 are preferably 30 ° to 70 °, and more preferably 40 ° to 60 °. In this Embodiment, since inclination-angle (theta) 1 and (theta) 2 were set to 30 degrees-70 degrees, the precipitation concentration of sludge was able to be performed favorably, suppressing the height of the sedimentation tank main body 2. FIG.

又、スラッジピット7の深さhの沈殿槽本体2内の水位Hに対する比率h/Hが小さ過ぎると、汚泥のキャリーオーバーが発生し易く、逆に大き過ぎると第2の傾斜部7bの上端部と水面との間が狭くなるため、第2の傾斜部7bを乗り越える水の線速度が大きくなり、汚泥が巻き込まれてキャリーオーバーが発生し易くなる。従って、比率h/Hとしては0.2〜0.8が好ましく、0.3〜0.5であることがより好ましい。本実施の形態では、比率h/Hを0.2〜0.8に設定したため、汚泥のキャリーオーバーを抑えて、良好な水質の処理水を得ることができた。   Also, if the ratio h / H of the depth h of the sludge pit 7 to the water level H in the sedimentation tank body 2 is too small, sludge carryover is likely to occur, and conversely if too large, the upper end of the second inclined portion 7b. Since the space between the portion and the water surface is narrowed, the linear velocity of the water over the second inclined portion 7b is increased, and sludge is caught and the carry-over easily occurs. Therefore, the ratio h / H is preferably 0.2 to 0.8, and more preferably 0.3 to 0.5. In this Embodiment, since ratio h / H was set to 0.2-0.8, the carry over of sludge was suppressed and the treated water of favorable water quality was able to be obtained.

更に、本実施の形態においては、沈殿槽本体2を直方体状の矩形体形状としたため、これを工場で製作して現地まで容易に搬送することができるとともに、現地の平面スペースを活用して短期間でこれを据え付けることができ、工期を大幅に短縮することができる。尚、本実施の形態では、沈殿槽本体2の形状を直方体状としたが、立方体状としても良いことは勿論である。   Furthermore, in this embodiment, since the sedimentation tank main body 2 has a rectangular parallelepiped shape, it can be manufactured at the factory and easily transported to the site, and the local plane space can be used for a short period of time. This can be installed in between, and the construction period can be greatly shortened. In this embodiment, the shape of the sedimentation tank body 2 is a rectangular parallelepiped, but it is needless to say that it may be a cube.

又、本発明に係る沈澱装置1においては、沈殿槽本体2内に多数の傾斜板や充填材を設ける必要がないため、沈殿槽本体2の構造が単純化し、その小型化とコストダウンが図られる。   Further, in the precipitation apparatus 1 according to the present invention, since it is not necessary to provide a large number of inclined plates and fillers in the precipitation tank main body 2, the structure of the precipitation tank main body 2 is simplified, and the downsizing and cost reduction are achieved. It is done.

更に、沈殿槽本体2の底部に、入口トラフ3から出口トラフ4の方向に沿って設けられた3つのスラッジピット7の各底部に沈澱・濃縮された汚泥を各スラッジピット7の底部7cから汚泥引抜管9によってそれぞれ引き抜いて排出することができるため、動力機付き掻取機を要することなく、汚泥を容易に排出することができる。   Further, sludge precipitated and concentrated on the bottom of each of the three sludge pits 7 provided along the direction of the inlet trough 3 to the outlet trough 4 at the bottom of the settling tank body 2 is sludge from the bottom 7c of each sludge pit 7. Since each can be pulled out and discharged by the drawing tube 9, sludge can be easily discharged without requiring a scraper with a power machine.

尚、本実施の形態では、沈殿槽本体2の底部に3つのスラッジピット7を設けた三槽型の沈殿槽について説明したが、スラッジピット7の数は任意であって、4つ以上並設しても良い。   In the present embodiment, a three-tank settling tank in which three sludge pits 7 are provided at the bottom of the settling tank body 2 has been described. However, the number of sludge pits 7 is arbitrary, and four or more sludge pits are arranged in parallel. You may do it.

又、本実施の形態では、各スラッジピット7の底部7cに1つの孔を形成し、この孔に汚泥引抜管9を接続したが、複数の孔を形成し、或はスラッジピット7の底部7c全体を孔とし、これらの孔に落下した汚泥を汚泥引抜管9に導くようにしても良い。   In this embodiment, one hole is formed in the bottom portion 7c of each sludge pit 7, and the sludge extraction pipe 9 is connected to this hole. However, a plurality of holes are formed, or the bottom portion 7c of the sludge pit 7 is formed. The whole may be holes, and the sludge falling into these holes may be guided to the sludge extraction pipe 9.

次に、具体的な実施例について概説する。   Next, specific examples will be outlined.

図1及び図2に示す三槽型の沈殿槽本体を備える沈澱装置において、無機系の懸濁物質を濃度190[mg/L]程度含む原水を54[m3
/h]の流量で処理した結果、出口トラフでの処理水中に含まれる懸濁物質の濃度を安定して15[mg/L]以下にすることができた。
1 and FIG. 2, the precipitation apparatus having a three-tank settling tank main body contains 54 [m3] of raw water containing a concentration of about 190 [mg / L] of an inorganic suspended substance.
As a result of the treatment at a flow rate of / h], the concentration of suspended solids contained in the treated water at the outlet trough could be stably reduced to 15 mg / L or less.

本発明は、原水中の懸濁物質を重力による自然沈降によって分離するための沈澱装置全般に対して適用可能である。   The present invention can be applied to all precipitation apparatuses for separating suspended substances in raw water by natural sedimentation by gravity.

本発明に係る沈澱装置の側断面図である。It is side sectional drawing of the precipitation apparatus which concerns on this invention. 本発明に係る沈澱装置の沈殿槽本体の平面図である。It is a top view of the sedimentation tank main body of the sedimentation apparatus which concerns on this invention. (a)〜(i)は本発明に係る沈澱装置における返し部の種々の形態を示す斜視図である。(A)-(i) is a perspective view which shows the various form of the return part in the precipitation apparatus which concerns on this invention. 本発明に係る沈澱装置の別形態を示す側断面図である。It is a sectional side view which shows another form of the precipitation apparatus which concerns on this invention. 本発明に係る沈澱装置の別形態を示す側断面図である。It is a sectional side view which shows another form of the precipitation apparatus which concerns on this invention.

符号の説明Explanation of symbols

1 沈澱装置
2 沈殿槽本体
3 入口トラフ(原水流入口)
4 出口トラフ(処理水排出口)
5 原水供給管
6 処理水排出管
7 スラッジピット
7a 第1の傾斜部
7b 第2の傾斜部
7c 底部
8 返し部
9 汚泥引抜管
10 流量計
11 排泥管
12 ポンプ
h スラッジピットの高さ
H 沈殿槽本体内の水位
P1〜P3 ポンプ
V1〜V3 バルブ
θ1 第1の傾斜部の傾斜角度
θ2 第2の傾斜部の傾斜角度
1 Precipitation device 2 Precipitation tank body 3 Inlet trough (raw water inlet)
4 outlet trough (treated water outlet)
DESCRIPTION OF SYMBOLS 5 Raw water supply pipe 6 Treated water discharge pipe 7 Sludge pit 7a 1st inclination part 7b 2nd inclination part 7c Bottom part 8 Return part 9 Sludge extraction pipe 10 Flowmeter 11 Drainage pipe 12 Pump h Sludge pit height H Precipitation Water level in tank body P1 to P3 Pump V1 to V3 Valve θ1 Inclination angle of first inclined portion θ2 Inclination angle of second inclined portion

Claims (8)

内部に隔壁を持たない矩形体状の沈殿槽本体と、該沈殿槽本体の一側面上部に設けられた原水流入口と、同沈殿槽本体の他側面上部に設けられた処理水排出口とを有する沈澱装置において、
前記沈殿槽本体の底部に、前記原水流入口から前記処理水排出口の方向に複数のスラッジピットを設けたことを特徴とする沈澱装置。
A rectangular precipitation tank main body having no partition wall inside, a raw water inlet provided on one side upper part of the precipitation tank main body, and a treated water discharge outlet provided on the other side upper part of the precipitation tank main body. Having a precipitation device,
A sedimentation apparatus, wherein a plurality of sludge pits are provided in the bottom of the sedimentation tank body from the raw water inlet to the treated water outlet.
前記各スラッジピットは、前記原水流入口側から前記処理水排出口側に向かって下る第1の傾斜部と、前記処理水排出口から前記原水流入口に向かって下る第2の傾斜部を有することを特徴とする請求項1記載の沈澱装置。   Each sludge pit has a first inclined portion that descends from the raw water inlet side toward the treated water discharge port side, and a second inclined portion that falls from the treated water discharge port toward the raw water inlet. The precipitation apparatus according to claim 1. 前記各スラッジピットの前記第1の傾斜部と前記第2の傾斜部の傾斜角度を30°〜70°に設定したことを特徴とする請求項2記載の沈澱装置。   The precipitation apparatus according to claim 2, wherein an inclination angle of the first inclined portion and the second inclined portion of each sludge pit is set to 30 ° to 70 °. 前記各スラッジピットの深さhを前記沈殿槽本体内の水位Hに対してh=(0.2〜0.8)Hに設定したことを特徴とする請求項1〜3の何れかに記載の沈澱装置。   The depth h of each sludge pit is set to h = (0.2 to 0.8) H with respect to the water level H in the settling tank main body. Precipitation equipment. 何れかのスラッジピットの前記第2の傾斜部の上端部に、汚泥の乗り越えを防ぐための返し部を設けたことを特徴とする請求項2〜4の何れかに記載の沈澱装置。   The sedimentation apparatus according to any one of claims 2 to 4, wherein a return portion for preventing sludge from getting over is provided at an upper end portion of the second inclined portion of any sludge pit. 前記各スラッジピットの底部に、汚泥を引き抜くための汚泥引抜管をそれぞれ接続し、前記原水流入口に近い汚泥引抜管ほど汚泥引き抜き量が多くなるよう制御することを特徴とする請求項1〜5の何れかに記載の沈澱装置。   6. A sludge extraction pipe for extracting sludge is connected to the bottom of each sludge pit, and control is performed so that the amount of sludge extraction increases as the sludge extraction pipe is closer to the raw water inlet. The precipitation apparatus in any one of. 前記各汚泥引抜管にバルブを設け、各バルブの開度を前記原水流入口に近いものほど大きく設定したことを特徴とする請求項6記載の沈澱装置。   7. A sedimentation apparatus according to claim 6, wherein a valve is provided in each sludge extraction pipe, and an opening degree of each valve is set to be larger as it is closer to the raw water inlet. 前記各汚泥引抜管の口径を前記原水流入口に近いものほど大きく設定したことを特徴とする請求項6記載の沈澱装置。   7. A sedimentation apparatus according to claim 6, wherein the diameter of each sludge extraction pipe is set to be larger as it is closer to the raw water inlet.
JP2005015264A 2005-01-24 2005-01-24 Precipitation device Pending JP2006198571A (en)

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105170312A (en) * 2015-08-14 2015-12-23 昆明理工大学 Tailing classifying and ore drawing device
CN106734291A (en) * 2016-12-27 2017-05-31 安徽江南鸣放电子科技有限公司 A kind of wire drawing machine wire drawing oil oil return apparatus
CN113185051A (en) * 2021-04-28 2021-07-30 昆山元魁机电工程有限公司 Sewage treatment device based on variable-frequency electromagnetic adsorption technology
CN114570074A (en) * 2022-03-30 2022-06-03 湖南蓬源鸿达矿业有限公司 Mining enrichment facility based on it is multi-functional

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105170312A (en) * 2015-08-14 2015-12-23 昆明理工大学 Tailing classifying and ore drawing device
CN106734291A (en) * 2016-12-27 2017-05-31 安徽江南鸣放电子科技有限公司 A kind of wire drawing machine wire drawing oil oil return apparatus
CN113185051A (en) * 2021-04-28 2021-07-30 昆山元魁机电工程有限公司 Sewage treatment device based on variable-frequency electromagnetic adsorption technology
CN114570074A (en) * 2022-03-30 2022-06-03 湖南蓬源鸿达矿业有限公司 Mining enrichment facility based on it is multi-functional
CN114570074B (en) * 2022-03-30 2023-01-03 湖南蓬源鸿达矿业有限公司 Mining enrichment facility based on it is multi-functional

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