JP7734962B2 - Improved aquarium tank - Google Patents
Improved aquarium tankInfo
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- JP7734962B2 JP7734962B2 JP2021192892A JP2021192892A JP7734962B2 JP 7734962 B2 JP7734962 B2 JP 7734962B2 JP 2021192892 A JP2021192892 A JP 2021192892A JP 2021192892 A JP2021192892 A JP 2021192892A JP 7734962 B2 JP7734962 B2 JP 7734962B2
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Description
本発明は、工事現場等において、泥水を処理するために用いられる改良された水槽タンクに関する。 The present invention relates to an improved water tank used to treat muddy water at construction sites, etc.
都市部等において、建設工事を行う場合、工事に伴い泥水が発生するが、この泥水を処理して清澄化するために水槽タンクが用いられていた。この水槽タンクの容量は、一般的に1~40m3程度のタンクである。水槽タンクの代表的な構造は、例えば図1に示すように、長方形のタンク1の一方に泥水の給水口2が設けられ、他方に排水口3が設けられたものや、図2に示すように長方形のタンク1内の排水口3近傍に一つのV字形切欠部4を有するノッチ隔壁5が設けられたノッチタンクが挙げられる。
またこれらの水槽タンクは、泥水の処理によって発生した水槽タンク内の底部に溜まった汚濁物質は適宜抜いて処理されているものである。
これら従来の水槽タンクは、予定する泥水の処理量によってタンクの容量を決定していたが、近年のように狭い建設現場では、スペースの制約があることから、特に処理量が大幅に増大するような変動があっても水槽タンクを変えることが困難であった。
During construction work in urban areas, muddy water is generated during construction, and water tanks have been used to treat and clarify this muddy water. The capacity of these water tanks is generally about 1 to 40 m3 . Typical water tank structures include a rectangular tank 1 with a muddy water inlet 2 on one side and a drain outlet 3 on the other, as shown in Figure 1, and a notched tank with a notched partition wall 5 with a single V-shaped notch 4 near the drain outlet 3 inside the rectangular tank 1, as shown in Figure 2.
Furthermore, these water tanks are designed so that any contaminants that accumulate at the bottom of the tanks during the treatment of muddy water are removed and disposed of as needed.
The capacity of these conventional water tanks was determined based on the planned amount of muddy water to be treated, but in today's small construction sites, space constraints make it difficult to change water tanks, especially if there is a change in the treatment volume, such as a significant increase.
従来このような、泥水等の処理を行う方法が種々提案されている。例えば汚濁防止枠内に発生する汚濁水の処理において、汚濁水を取水して区画された小規模の滞留部を設け、該滞留域部に凝集剤を添加する原水の処理方法(特許文献1)、複数の沈殿池を同時に使用して濁水を清澄化処理する沈殿処理施設において、少なくとも一つの沈殿池を休止したときに、他の使用している沈殿池の少なくとも一つの沈殿池に、水流傾斜膜を各々隣接する水流傾斜膜との間に間隙を設けて連結した整流膜を複数条展張する、濁水の処理量を減少させることなく処理することができる濁水の連続処理運用方法(特許文献2)、汚濁水の流入部および流出部を有する沈降分離装置において、流出口部を遮蔽するようにラッシュ体を設けることを特徴とする沈降分離装置(特許文献3)、クラリファイヤーの流入口と流出口との間の中間部近傍に、水面下にその一部が水没する状態で断面形状か半円形、倒卵形等種々の形状からなるガータを設け、原水の流入口と流出口との中間位置近傍部の表層流部より取水する沈降分離装置の取水方法(特許文献4)等が知られている。 Various methods have been proposed to treat such muddy water. For example, known examples include a raw water treatment method for treating polluted water generated within a pollution prevention frame, in which polluted water is taken in, a small, partitioned retention area is created, and a flocculant is added to the retention area (Patent Document 1); a method for continuously treating turbid water in a sedimentation treatment facility that uses multiple settling tanks simultaneously to clarify turbid water, in which, when at least one settling tank is out of service, multiple streamlined membranes are deployed in at least one of the other settling tanks in use, with gaps between each adjacent membrane, allowing treatment without reducing the amount of turbid water being treated (Patent Document 2); a settling device having inlet and outlet ports for polluted water, in which a rush body is provided to shield the outlet port (Patent Document 3); and a water intake method for a settling device that takes water from the surface flow portion near the midpoint between the raw water inlet and outlet port of the clarifier, with a girder of various cross-sectional shapes such as semicircular or obovate, partially submerged below the water surface, provided near the midpoint between the inlet and outlet port of the clarifier (Patent Document 4).
そこで本発明者は、泥水の処理量の変動にも水槽タンクを交替することなく処理できる、小型にして処理能力を高めた水槽タンクについて種々検討を行い、本発明を完成するに至った。 The inventor therefore conducted extensive research into a compact water tank with high processing capacity that can process muddy water even when the processing volume fluctuates without the need to replace the tank, and has now completed this invention.
すなわち、本発明は、水槽タンクの排水口が設けられた側壁に密着および/または離間させた状態で上縁部に切欠部を複数有する集水トラフを設け、該集水トラフの前面(取水口側)に隣接して繊維状の集合体からなるラッシュ体を設け、かつ取水口が設けられたタンク側壁と前記ラッシュ体の間に前記集水トラフと平行に水流傾斜膜を多重に展張する、水槽タンクである。 In other words, the present invention is an aquarium tank that has a water collection trough with multiple cutouts on its upper edge, attached to and/or spaced from the side wall of the tank where the drain outlet is located, a rush body made of a fibrous aggregate attached to the front surface (intake side) of the water collection trough, and multiple water flow gradient membranes stretched parallel to the water collection trough between the tank side wall where the intake is located and the rush body.
本発明の水槽タンクは、集水トラフに複数の切欠部が設けられていることから、水流が拡散して流れるので流速が減速し、水槽タンクのデッドスペースがなくなり、水槽タンクの効率が高まる等、流線の多様化で水槽タンクの集水・排水が改善され、汚濁物質の沈降を促進することができる。また泥水の処理量の変動にも一台の小型の水槽タンクで対応することができるので、建設スケジュールにも影響を与えない利点がある。さらに既存の水槽タンクでも簡単な改良を加えることによって、本発明の水槽タンクに改良することができる。 The water tank of the present invention has multiple notches in the collection trough, which allows the water flow to diffuse and slow down, eliminating dead space in the water tank and increasing the efficiency of the water tank. This diversifies the flow lines, improving water collection and drainage in the water tank and promoting the settling of pollutants. Another advantage is that a single small water tank can handle fluctuations in the amount of muddy water to be treated, which does not affect the construction schedule. Furthermore, existing water tanks can be easily modified to become the water tank of the present invention.
次に本発明を図面を参照しながら説明をするが、本発明は以下の説明のみに限定されるものではない。
図3は本発明の水槽タンクの一態様を示す斜視図である。
水槽タンク1は一方に泥水の取水口2を設け、他方には排出口3が設けられている。この排水口3の側壁および/または上流側の位置に離間させて、複数の切欠部4を有する集水トラフ5を設ける。
Next, the present invention will be described with reference to the drawings, but the present invention is not limited to the following description.
FIG. 3 is a perspective view showing one embodiment of the water tank of the present invention.
The water tank 1 has a muddy water intake 2 on one side and a discharge outlet 3 on the other side. A water collecting trough 5 having a plurality of notches 4 is provided on the side wall of the discharge outlet 3 and/or at a position upstream of the discharge outlet 3, spaced apart.
排水口3の側壁から離間して設けられた集水トラフ5´は、集水して清澄化された処理水を直接水槽タンク外に排出するための排出口が設けられている(図示せず)。別の態様として、集水トラフ5´と集水トラフ5とを樋でつなぎ(図示せず)、集水トラフ5´で集水して清澄化された処理水を集水トラフ5に流し、集水トラフ5で集水して清澄化された処理水と共に排水口3から水槽タンク外に排出する。更に図4に示すように集水トラフ5´と集水トラフ5の底部を配管で結び集水トラフ5´で集水して清澄化された処理水を集水トラフ5に流し、集水トラフ5で集水して清澄化された処理水と共に排水口3から水槽タンク外に排出することも好ましい。
また排出口3が設けられた側壁に密着して設けられている集水トラフ5は、清澄化された処理水は直接排出口3から系外に排出される。他の態様として、排出口3が設けられた側壁から離間させて設けられている集水トラフ5´は、集水面が集水トラフ5の取水口2側と排出口3側の2面に切欠部を設けることもでき、このようにすることによって、越流する処理水の速度が緩やかになるため好ましい。
The water collection trough 5', which is provided at a distance from the side wall of the drain outlet 3, is provided with a drain outlet (not shown) for directly discharging the collected and clarified treated water out of the water tank. In another embodiment, the water collection trough 5' and the water collection trough 5 are connected by a gutter (not shown), and the treated water collected and clarified in the water collection trough 5' flows into the water collection trough 5, and is discharged out of the water tank from the drain outlet 3 together with the treated water collected in the water collection trough 5. Furthermore, as shown in Figure 4, it is also preferable to connect the bottom of the water collection trough 5' and the water collection trough 5 with a pipe, so that the treated water collected and clarified in the water collection trough 5' flows into the water collection trough 5, and is discharged out of the water tank from the drain outlet 3 together with the treated water collected in the water collection trough 5.
Furthermore, in the case of the water collection trough 5, which is provided in close contact with the side wall on which the outlet 3 is provided, the clarified treated water is directly discharged to the outside of the system from the outlet 3. In another embodiment, in the case of the water collection trough 5', which is provided away from the side wall on which the outlet 3 is provided, notches can be provided on two surfaces of the water collection surface, one on the intake 2 side and the other on the outlet 3 side of the water collection trough 5, which is preferable because this reduces the speed of the overflowing treated water.
集水トラフ5および集水トラフ5´の切欠部4を複数個設けることによって切欠部4を越流する処理水の速度が緩やかになり、より一層清澄効果が向上される。なお該切欠部4は集水トラフ5および集水トラフ5´の上縁部全体に設けることが好ましい。
集水トラフ5および集水トラフ5´の切欠部4の形状は、従来のV字形状の外、上向き開放コの字形、半円形等の種々の形状とすることができる。
尚、集水トラフ5及び集水トラフ5´の側壁との間に、複数個の開口部を設け、該開口部(図示せず)に横方向にスライド可能な扉を設けた改良された開口部を設けることができる。この開口部の扉は、上部に設けられたスライド棒に連結されており、スライド棒を左右に動かすことによってすべての扉を同時に移動させ、開口部の開閉を行うことができる。
また集水トラフ5´は、図5に示すように集水トラフ5´の下部に下縁壁6を設けることが好ましい。下縁壁6の取付位置は特に限定されない。
By providing a plurality of notches 4 in the water collecting troughs 5 and 5', the speed of the treated water overflowing the notches 4 is slowed down, further improving the clarification effect. It is preferable to provide the notches 4 over the entire upper edge of the water collecting troughs 5 and 5'.
The shape of the notch 4 of the water collecting trough 5 and the water collecting trough 5' can be various shapes such as a conventional V-shape, an upwardly open U-shape, a semicircular shape, etc.
An improved opening can be provided by providing a plurality of openings between the side walls of the water collecting trough 5 and the water collecting trough 5' and providing doors that can slide laterally at the openings (not shown). The doors of the openings are connected to a slide rod provided at the top, and by moving the slide rod left and right, all the doors can be moved simultaneously to open and close the openings.
Furthermore, it is preferable that the water collecting trough 5' has a lower edge wall 6 at the bottom of the water collecting trough 5' as shown in Figure 5. The attachment position of the lower edge wall 6 is not particularly limited.
また本発明は、集水トラフ5および集水トラフ5´の上流側(取水口2側)に繊維状の集水体からなるラッシュ体7(以下ラッシュ体という)を隣接して平行に設ける。
本発明におけるラッシュ体7とは
図6に示すような、芯体8から左右にループ状繊維体9が突出した状態で設けられたものである。
またラッシュ体7の他の態様としては、図7に示すように、ロープ等の挿通口10を有するフロート11にネット12を吊下し、該ネット12の下縁部に重錘13を設け、次にネット12の片面あるいは両面にラッシュ体7を一体に設けたフロート付膜状ラッシュ体14としても好適に使用できる。
Furthermore, in the present invention, rush bodies 7 (hereinafter referred to as rush bodies) made of fibrous water collecting material are provided adjacent to and in parallel with the water collecting troughs 5 and 5' on the upstream side (the water intake 2 side) of the water collecting troughs 5 and 5'.
The rush body 7 in the present invention is, as shown in FIG . 6, a core body 8 from which loop-shaped fibrous bodies 9 protrude on both sides.
Another embodiment of the rush body 7 is a membrane-like rush body 14 with a float, as shown in FIG. 7, in which a net 12 is suspended from a float 11 having an insertion port 10 for a rope or the like, a weight 13 is attached to the lower edge of the net 12, and the rush body 7 is then integrally attached to one or both sides of the net 12.
また、図8に示す様な、フロート11に2枚のネット12を吊下し、該2枚のネット12にラッシュ体7を一体に設け、フロート付膜状ラッシュ体14を構成し、取水口2側のラッシュ体7を吊下し、集水トラフ5側のラッシュ体7の下縁部を集水トラフ5に固定する。
取水口2側に吊下したラッシュ体7は通水断面を流れる粒子を捕捉し、集水トラフ5側のラッシュ体7は、集水トラフ5向かって上昇する流れの粒子を捕捉し、効果的である。
ラッシュ体7に捕捉された粒子は、肥大化した後、剥離し、再度新たに粒子を捕捉するが、水槽タンク1の泥水処理を止めた際に、ラッシュ体7に捕捉された粒子をたたき落とすことで、泥水処理を再開した場合ラッシュ体7は新たに汚濁粒子を捕捉することができるようになり、水槽タンク内に堆積したそれらの汚濁物質を抜き出して、水槽タンク内の容量を確保する。
Also, as shown in Figure 8, two nets 12 are suspended from a float 11, and rush bodies 7 are integrally attached to the two nets 12 to form a membrane-like rush body 14 with a float, in which the rush body 7 on the water intake 2 side is suspended and the lower edge of the rush body 7 on the water collection trough 5 side is fixed to the water collection trough 5.
The lash body 7 suspended on the intake 2 side effectively captures particles flowing through the cross section of the water flow, while the lash body 7 on the water collection trough 5 side effectively captures particles in the flow rising toward the water collection trough 5.
The particles captured by the rush body 7 become enlarged, then peel off and capture new particles again, but when the muddy water treatment in the water tank 1 is stopped, the particles captured by the rush body 7 are knocked off, so that when the muddy water treatment is resumed, the rush body 7 can capture new polluted particles, and the polluted substances accumulated in the water tank are extracted, thereby ensuring the capacity of the water tank.
また本発明の水槽タンク1は、取水口2が設けられた水槽タンクの側壁と集水トラフ5´の間および/または集水トラフ5´と集水トラフ5の間に、図9に示すような、フロート11にシート膜15を吊下し、該シート膜15の下縁部に重錘16を設けた遮蔽体を、隣接する遮蔽体のシート膜15との間に間隔を有するように連接した水流傾斜膜17を形成させ、該水流傾斜膜17をラッシュ体7と平行して多重に展張する。水流傾斜膜17を多重に展張すると、水流が水流傾斜膜17の流体抵抗を感知して、乱流、制止流、層流、移流、縮流、カルマン流を繰り返して、水流が蛇行するので水流が水槽タンク内を広く流れ、水槽タンク1の四隅のデットスペースが生じない。
さらに、水流傾斜膜17を多重展張した水槽タンク1は、水槽タンク1の通水断面積の増加、集水距離の延長、滞留時間の増加、デッドスペースの改善、初期粒子群の沈降促進、粒子群の接触ろ過・付着・沈降の促進、処理量の増加、沈殿池のコンパクト化等の多機能効果が向上する。
なお、水流傾斜膜17を多重展張する場合、前後の水流傾斜膜17を左右に交互ずらして同じ位置に重ならないように展張することが好ましい。
In addition, the water tank 1 of the present invention has a water flow gradient membrane 17 formed by suspending a sheet membrane 15 from a float 11 between the side wall of the water tank where the water intake 2 is provided and the water collection trough 5' and/or between the water collection trough 5' and the water collection trough 5, and by connecting shields each having a weight 16 attached to the lower edge of the sheet membrane 15 so as to leave a gap between the sheet membrane 15 of adjacent shields, and the water flow gradient membranes 17 are extended in multiple layers parallel to the rush body 7. When the water flow gradient membranes 17 are extended in multiple layers, the water flow senses the fluid resistance of the water flow gradient membranes 17 and alternates between turbulent flow, blocked flow, laminar flow, advection flow, contraction flow and Karman flow, causing the water flow to meander, allowing the water to flow widely within the water tank and preventing dead space from being generated at the four corners of the water tank 1.
Furthermore, the water tank 1 with multiple water flow gradient membranes 17 spread over it has improved multi-functional effects such as an increase in the cross-sectional water flow area of the water tank 1, an extension of the water collection distance, an increase in retention time, an improvement in dead space, promotion of settling of initial particle groups, promotion of contact filtration, adhesion and settling of particle groups, an increase in processing volume, and a compact sedimentation tank.
When the water flow gradient membranes 17 are deployed in multiple locations, it is preferable to deploy the front and rear water flow gradient membranes 17 alternately to the left and right so that they do not overlap at the same position.
また本発明の水槽タンク1を用いて発生する泥水を凝集剤を使用して短時間で処理する場合には図10に示すような、水槽タンク1の上部の側壁に沿って水路18を設け、泥水の流入部(取水口に相当する)19に凝集剤の流入部20を設けて泥水に凝集剤を加えると良好に処理が可能となる。
水路18は水槽タンク1の4辺を囲み、水路18の内側側壁21に迂流撹拌板22を設ける。
該迂流撹拌板22は、水路18の内側の左右の側壁21に交互に設け、泥水が蛇行するようにする。
この迂流撹拌板22は、泥水の入口側を急速混合させるために迂流撹拌板22の間隔を狭くし、徐々に緩慢混合とするために迂流撹拌板22の間隔を離すことが好ましい。
水槽タンク1の上部に水路18を設ける他の態様としては、図11に示すような、水槽タンク1の上部の側壁から内側に水路18を設けることも好ましい。
使用する凝集剤は、液状物および固形状物とあり、液状物は直ちに溶けるため絶えず添加が必要であり、固形状物は徐々に溶け出すので1日1回の添加で済むため運転管理が簡単である。
Furthermore, when using the water tank 1 of the present invention to treat the muddy water generated in a short time using a flocculant, a water channel 18 can be provided along the upper side wall of the water tank 1, as shown in Figure 10, and a flocculant inlet 20 can be provided at the muddy water inlet (corresponding to the water intake) 19, allowing the flocculant to be added to the muddy water, thereby enabling good treatment.
The water channel 18 surrounds the four sides of the water tank 1, and a tortuous flow stirring plate 22 is provided on the inner side wall 21 of the water channel 18.
The tortuous flow mixing plates 22 are provided alternately on the left and right side walls 21 inside the water channel 18 to make the muddy water meander.
It is preferable that the spacing between the contiguous flow agitating plates 22 be narrow to rapidly mix the muddy water on the inlet side, and that the spacing between the contiguous flow agitating plates 22 be wide to gradually slow down the mixing.
As another embodiment of providing the water channel 18 in the upper part of the water tank 1, it is also preferable to provide the water channel 18 inward from the side wall of the upper part of the water tank 1, as shown in FIG.
The flocculants used are in liquid and solid form. The liquid dissolves immediately and needs to be added constantly, while the solid dissolves gradually and only needs to be added once a day, making operation and management simple.
1・・・水槽タンク
5・・・切欠部を有する集水トラフ
5´・・・切欠部を有する集水トラフ
7・・・ラッシュ体
17・・・水流傾斜膜
1... Water tank 5... Water collecting trough with cutout 5'... Water collecting trough with cutout 7... Rush body 17... Water flow inclined membrane
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Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2018038949A (en) | 2016-09-06 | 2018-03-15 | 日本ソリッド株式会社 | Maintaining treatment environment in outdoor sedimentation basin |
| JP2019089025A (en) | 2017-11-15 | 2019-06-13 | 日本ソリッド株式会社 | Water intake method of precipitator |
| JP2020157269A (en) | 2019-03-28 | 2020-10-01 | 日本ソリッド株式会社 | Upward flow type cross flow sedimentation basin |
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Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2018038949A (en) | 2016-09-06 | 2018-03-15 | 日本ソリッド株式会社 | Maintaining treatment environment in outdoor sedimentation basin |
| JP2019089025A (en) | 2017-11-15 | 2019-06-13 | 日本ソリッド株式会社 | Water intake method of precipitator |
| JP2020157269A (en) | 2019-03-28 | 2020-10-01 | 日本ソリッド株式会社 | Upward flow type cross flow sedimentation basin |
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