JP2006052620A - Minute substance removal device of intake facility - Google Patents
Minute substance removal device of intake facility Download PDFInfo
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- JP2006052620A JP2006052620A JP2004259017A JP2004259017A JP2006052620A JP 2006052620 A JP2006052620 A JP 2006052620A JP 2004259017 A JP2004259017 A JP 2004259017A JP 2004259017 A JP2004259017 A JP 2004259017A JP 2006052620 A JP2006052620 A JP 2006052620A
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Abstract
Description
本発明は、湖沼、河川、海域より水を取水する取水施設に於いて、微細な懸濁物質を除去する事に関する技術である。 The present invention relates to technology for removing fine suspended solids in a water intake facility that takes water from lakes, rivers, and sea areas.
従来の、湖沼、河川、海域より水を取水する取水施設の実施例を図5、図6に示す。尚、取水施設とは取水点の水位▲15▼と取水口水位▲13▼の水面が連続している流路(流れが停止した時、同一水面になる流路)で形成される。
従来の技術の取水施設では、流路内に沈砂池▲20▼を設置し、砂分を沈殿除去し、又、スクリーン▲16▼を設置し浮遊物を除去していた。この時、取水口水位▲21▼は、スクリーン▲16▼の圧力損失分、取水点の水位▲15▼より低下する。Examples of conventional water intake facilities that take water from lakes, rivers, and sea areas are shown in FIGS. The water intake facility is formed by a flow path in which the water level at the intake point (15) and the water level at the intake port (13) are continuous (a flow path that becomes the same water level when the flow stops).
In a conventional water intake facility, a sand basin (20) is installed in the flow path to remove sediment, and a screen (16) is installed to remove suspended matter. At this time, the intake water level (21) falls below the water level (15) at the intake point by the pressure loss of the screen (16).
従来の、湖沼、河川、海域より水を取水する取水施設の流路に設置する処理施設は、沈砂池▲20▼による沈殿処理、又はスクリーン▲16▼による除去処理であり、濾過処理を使用した例は無い。従って、取水口▲14▼より流出する水に微細な懸濁物質(アオコや濁質分)が含まれ、取水ポンプや発電機の羽根車を損傷する障害があった。 Conventional treatment facilities installed in the flow path of water intake facilities that take water from lakes, rivers, and sea areas are sedimentation treatment by a sand basin (20) or removal treatment by a screen (16), and filtration treatment is used. There is no example. Accordingly, the water flowing out from the intake port (14) contains fine suspended solids (aquatic and turbid components), and there is an obstacle that damages the intake pump and the impeller of the generator.
水面が連続している取水施設の流路中に、濾過池▲20▼を設置する。濾過池▲1▼に使用する濾過材▲2▼の粒径は、目づまりの少ない2mmφ以上とし、又、取水する水より微細な懸濁物質の除去が可能な50mmφ以下とする。又、ろ層厚は30mm以上とする。
通常のろ過池の場合、濾過材▲2▼の粒径は0.4mmφ〜0.6mmφを使用する。本発明における濾過材▲2▼の粒径は2mmφ〜50mmφを使用する。その場合、濾過速度が50〜150m/日の場合、濾過池▲1▼の圧力損失は濾過材▲2▼の目づまりが無ければ1〜3cmAqであり、流路中の圧力損失による障害は少ない。この事により、従来技術に於ける流路中の圧力損失が少ない利点を損なう事がない。
濾過方式は濾過材▲2▼の目づまりを考慮すると全層濾過が望ましい。又、流れ方向は下向流濾過でも、上向流濾過でもよい。A filtration basin (20) is installed in the channel of the water intake facility where the water surface is continuous. The particle size of the filter medium (2) used for the filter basin (1) should be 2 mmφ or less with less clogging, and 50 mmφ or less that can remove fine suspended solids from the water taken. The filter layer thickness is 30 mm or more.
In the case of a normal filter basin, the particle size of the filter medium (2) is 0.4 mmφ to 0.6 mmφ. The particle size of the filter medium (2) in the present invention is 2 mmφ to 50 mmφ. In that case, when the filtration speed is 50 to 150 m / day, the pressure loss of the filter basin (1) is 1 to 3 cmAq if there is no clogging of the filter medium (2), and there are few obstacles due to the pressure loss in the flow path. This does not impair the advantage of low pressure loss in the flow path in the prior art.
In consideration of the clogging of the filter medium (2), the filtration method is preferably full-layer filtration. The flow direction may be downflow filtration or upflow filtration.
次に本発明の実施形態について説明する。
図2は取水点の水位▲15▼の水を直接、濾過池▲1▼に流入させた場合の例を示す。濾過池▲1▼の前に沈砂池、スクリーンを別途設置しても良い。
濾過池▲1▼の主たる構成は、躯体▲4▼、濾過材▲2▼、集水装置▲3▼であり、その他の部品として、トラフ、表洗装置、逆洗装置が有る場合もある。
濾過池▲1▼に於ける通常の流れを図2に示す。尚、濾過池▲1▼への流入方向は図1の、D,E、F,のいずれでも良い。
取水点の水位▲15▼の水は濾過池▲1▼を通過し取水口▲14▼へ流出する。この場合、取水口水位▲13▼は濾過池▲1▼圧力損失分だけ低下する。
取水点の水位▲15▼の水は、濾過池▲1▼の上部に流入後、濾過材▲2▼を通過し集水装置▲3▼を経て取水口▲14▼へ流出する。微細な懸濁質は濾過作用により除去される。
図3は濾過池▲1▼が微細な懸濁物質により目づまりした場合、逆洗ポンプ▲8▼を使用して濾過池▲1▼を洗浄する方法を示す。洗浄は逆洗ポンプ▲8▼により洗浄水を吸上げて行う。
洗浄水の流れを図3に示す。洗浄水は、取水口水位▲13▼より集水装置▲3▼を経て濾過材▲2▼の下部より流入する。洗浄水が濾過材▲2▼中を通過することにより微細な懸濁物質を流出させ濾過材▲2▼が洗浄できる。尚、洗浄は他の方法で、濾過材▲2▼に水を通過にさせても良い。
図3の例では、洗浄水を濾過材▲2▼の表面より逆洗ポンプ▲8▼により集水口▲10▼、吸水管9▼を経て吸い上げる事により、洗浄水を濾過材▲2▼の中を通過させる。洗浄水は排水管▲11▼をへて排水トラフ▲12▼に微細な懸濁物質と共に排出する。逆洗ポンプ▲8▼は架台▲7▼上に設置する。架台▲7▼は濾過池▲1▼上に設置したレール▲5▼の上を車輪▲6▼により移動する。逆洗ポンプ▲8▼より吊り下げた集水口▲10▼は、濾過材▲2▼の全表面をカバーできるように移動させて濾過池▲1▼全面の濾過材▲2▼を洗浄する。
図4は濾過池▲1▼の前段に凝集混和池▲19▼を設置し濾過池▲1▼での微細な懸濁物質の除去効果を上昇させる例である。凝集混和池▲19▼には、急速攪拌機▲17▼を設置し、薬注設備▲18▼より添加された凝集剤を急速に混和させる。Next, an embodiment of the present invention will be described.
FIG. 2 shows an example in which the water at the water intake point (15) is directly introduced into the filtration basin (1). A sand basin and a screen may be separately installed before the filtration basin (1).
The main structure of the filter basin (1) is a housing (4), a filter medium (2), a water collecting device (3), and other parts may include a trough, a surface washing device, and a backwash device.
A normal flow in the filter basin (1) is shown in FIG. In addition, the inflow direction to the filter basin (1) may be any of D, E, and F in FIG.
The water at the water intake point (15) passes through the filter basin (1) and flows out to the water intake (14). In this case, the intake water level {circle around (13)} is lowered by the amount corresponding to the pressure loss of the filter {circle around (1)}.
The water at the water level {15} at the water intake point flows into the upper part of the filter basin (1), passes through the filter medium (2), and flows out to the water intake (14) through the water collecting device (3). Fine suspension is removed by filtration.
FIG. 3 shows a method of washing the filter basin (1) using the backwash pump (8) when the filter basin (1) is clogged with fine suspended substances. Washing is performed by sucking up washing water with a backwash pump (8).
The flow of washing water is shown in FIG. The washing water flows from the lower part of the filter medium (2) through the water collecting device (3) from the intake water level (13). When the washing water passes through the filter medium (2), fine suspended substances are allowed to flow out and the filter medium (2) can be washed. In addition, you may make water pass through the filter medium (2) by another method.
In the example of FIG. 3, the washing water is sucked up from the surface of the filter medium (2) by the backwash pump (8) through the water collection port (10) and the water absorption pipe (9), so that the washing water is contained in the filter medium (2). Pass through. The washing water is discharged through the drain pipe (11) to the drain trough (12) together with fine suspended substances. The backwash pump (8) is installed on the stand (7). The gantry (7) moves on the rail (5) installed on the filtration basin (1) by wheels (6). The water collecting port (10) suspended from the backwash pump (8) is moved so as to cover the entire surface of the filter medium (2) to wash the filter medium (1) over the entire surface of the filter tank (1).
FIG. 4 shows an example in which a coagulation / mixing basin (19) is installed in front of the filtration basin (1) to increase the effect of removing fine suspended solids in the filtration basin (1). In the agglomeration mixing tank (19), a rapid stirrer (17) is installed, and the flocculant added from the chemical injection facility (18) is rapidly mixed.
水面が連続している取水施設の流路中に、濾過池▲20▼を設置する事により、従来技術に於ける流路中の圧力損失が少ない利点を損なう事がなく、取水する水より微細な懸濁物質が除去できる。その為、取水ポンプや発電機の羽根車を損傷する障害が低減できる。 By installing the filtration basin (20) in the flow path of the water intake facility where the water surface is continuous, the advantage of low pressure loss in the flow path in the prior art is not impaired, and it is finer than the water to be taken in. Suspended matter can be removed. Therefore, the damage which damages an intake pump and the impeller of a generator can be reduced.
▲1▼は濾過池、▲2▼は濾過材、▲3▼は集水装置、▲4▼は躯体、▲5▼はレール、▲6▼は車輪 ▲7▼は架台、▲8▼は逆洗ポンプ、▲9▼は吸水管、▲10▼は集水口、▲11▼は排水管、▲12▼は排水トラフ、▲13▼は取水口水位、▲14▼は取水口、▲15▼は取水点の水位、▲16▼はスクリーン、▲17▼は急速攪拌機、▲18▼は薬注設備、▲19▼は凝集混和池、▲20▼は沈砂池、▲21▼は取水口水位 (1) is a filtration pond, (2) is a filter medium, (3) is a water collecting device, (4) is a housing, (5) is a rail, (6) is a wheel, (7) is a stand, and (8) is reverse Wash pump, (9) is water intake pipe, (10) is water collection port, (11) is drainage pipe, (12) is drainage trough, (13) is intake water level, (14) is water intake, and (15) is water intake Water level at intake point, (16) is a screen, (17) is a rapid stirrer, (18) is a chemical injection facility, (19) is an agglomeration mixing basin, (20) is a sand basin, and (21) is a water level at the intake port
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JP2004259017A JP2006052620A (en) | 2004-08-10 | 2004-08-10 | Minute substance removal device of intake facility |
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JP2004259017A JP2006052620A (en) | 2004-08-10 | 2004-08-10 | Minute substance removal device of intake facility |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR101047112B1 (en) * | 2011-01-20 | 2011-07-06 | 서용섭 | Artificial recharge apparatus |
KR101282974B1 (en) * | 2011-04-19 | 2013-07-08 | 서용섭 | Artificial recharge apparatus |
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2004
- 2004-08-10 JP JP2004259017A patent/JP2006052620A/en active Pending
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR101047112B1 (en) * | 2011-01-20 | 2011-07-06 | 서용섭 | Artificial recharge apparatus |
KR101282974B1 (en) * | 2011-04-19 | 2013-07-08 | 서용섭 | Artificial recharge apparatus |
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