JP2001321609A - Settling tank - Google Patents

Settling tank

Info

Publication number
JP2001321609A
JP2001321609A JP2000141054A JP2000141054A JP2001321609A JP 2001321609 A JP2001321609 A JP 2001321609A JP 2000141054 A JP2000141054 A JP 2000141054A JP 2000141054 A JP2000141054 A JP 2000141054A JP 2001321609 A JP2001321609 A JP 2001321609A
Authority
JP
Japan
Prior art keywords
treated water
tank
overflow
scum
water
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP2000141054A
Other languages
Japanese (ja)
Other versions
JP3882464B2 (en
Inventor
Tsuneo Suzuki
恒雄 鈴木
Naomichi Mori
直道 森
Hideo Koide
英夫 小出
Katsumi Shida
勝己 志田
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Hitachi Plant Technologies Ltd
Original Assignee
Hitachi Plant Technologies Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Hitachi Plant Technologies Ltd filed Critical Hitachi Plant Technologies Ltd
Priority to JP2000141054A priority Critical patent/JP3882464B2/en
Publication of JP2001321609A publication Critical patent/JP2001321609A/en
Application granted granted Critical
Publication of JP3882464B2 publication Critical patent/JP3882464B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To overflow only a clarified treated water without being accompanied by scum in the treated water. SOLUTION: In a settling tank constituted so that raw water containing a settleable suspended solid is supplied into the tank and the treated water after the suspended solid is settled and separated is discharged outside the tank from an overflow weir, the treated water is taken in from a flow-in port 40 provided in the underwater and opened in the vertical direction, introduced to the overflow weir through a communication passage 42 and discharged from a discharge gutter 36.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は沈殿槽に係り、特に
沈降性の懸濁物質を含む原水を槽内に供給し、前記懸濁
物質を沈殿分離した処理水を溢流堰から槽外へ排出する
ようにした沈殿槽に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a sedimentation tank, and in particular, feeds raw water containing a settling suspended substance into a tank, and discharges the treated water obtained by separating and separating the suspended substance from an overflow weir to the outside of the tank. The present invention relates to a sedimentation tank adapted to be discharged.

【0002】[0002]

【従来の技術】従来のこの種の沈殿槽としては図6に示
した円形型のものがよく知られている。沈殿槽10は円
筒状の側壁12と、中心に向かって下り勾配とされた底
面部14とを含む。側壁12の上端は溢流堰16とさ
れ、この溢流堰16から溢流した処理水は側壁12の上
部に設けられたリング状の排水樋18から槽外に排出さ
れる。槽中央には円筒状のセンタウェル20が設けられ
ており、このセンタウェル20内に沈降性の懸濁物質を
含む原水が供給される。槽中心にはモーター22によっ
て緩慢に回転される掻寄機24が配置されている。掻寄
機24は前記底面部14に沿って移動する掻寄板26を
備え、この掻寄板26によって沈殿物を底面部14中央
の集積部28に集めた後、沈殿物を槽外に排出する。
2. Description of the Related Art As a conventional sedimentation tank of this type, a circular one shown in FIG. 6 is well known. The sedimentation tank 10 includes a cylindrical side wall 12 and a bottom part 14 inclined downward toward the center. The upper end of the side wall 12 is formed as an overflow weir 16, and the treated water overflowing from the overflow weir 16 is discharged out of the tank from a ring-shaped drain gutter 18 provided on the upper part of the side wall 12. A cylindrical center well 20 is provided at the center of the tank, and raw water containing a settled suspended substance is supplied into the center well 20. A scraper 24 that is slowly rotated by a motor 22 is disposed at the center of the tank. The scraping machine 24 includes a scraping plate 26 that moves along the bottom portion 14. The scraping plate 26 collects the sediment in the collecting portion 28 at the center of the bottom portion 14, and then discharges the sediment out of the tank. I do.

【0003】ところで、この種の沈殿槽では、原水中に
スカムと称される浮上性の滓状物質が含まれることが多
く、通常これらの水面に浮上したスカムを除去するため
の手段が沈殿槽に付設されている。
In this type of sedimentation tank, raw water often contains floating scum called scum. Usually, a means for removing the scum floating on the water surface is provided by a sedimentation tank. It is attached to.

【0004】[0004]

【発明が解決しようとする課題】しかしながら、前記原
水が汚水を生物学的に処理した活性汚泥を含む原水であ
る場合にスカムが多量に発生する。特に汚水が畜産場か
ら排泄される屎尿系の汚水の場合、高濃度の有機物に対
応するべく前段の曝気槽で過度の曝気が行われる。この
過度の曝気によって汚泥に微細な気泡が付着し、これら
の汚泥が沈殿槽で沈降し難く、スカムとして多量に浮上
する。このため、通常のスカム除去手段では対応が困難
となり、スカムが処理水とともに前記溢流堰16から溢
流して、処理水の水質を悪化させるという問題点があっ
た。
However, when the raw water is raw water containing activated sludge obtained by biologically treating sewage, a large amount of scum is generated. In particular, in the case of human wastewater excreted from livestock farms, excessive aeration is performed in the aeration tank in the preceding stage to cope with high-concentration organic matter. Due to this excessive aeration, fine air bubbles adhere to the sludge, and these sludges hardly settle in the sedimentation tank, and float in large quantities as scum. For this reason, it is difficult to deal with the ordinary scum removing means, and there is a problem that the scum overflows from the overflow weir 16 together with the treated water to deteriorate the quality of the treated water.

【0005】本発明の目的は、上記従来技術の問題点を
解消し、多量のスカムが発生するような原水を供給した
場合においても、処理水中にスカムが同伴せず、清澄な
処理水のみを溢流させることができる沈殿槽を提供する
ことにある。
SUMMARY OF THE INVENTION An object of the present invention is to solve the above-mentioned problems of the prior art. Even when raw water that generates a large amount of scum is supplied, scum does not accompany the treated water and only clear treated water is used. It is an object of the present invention to provide a sedimentation tank which can overflow.

【0006】[0006]

【課題を解決するための手段】上記の目的を達成するた
めに、本発明に係る沈殿槽は沈降性の懸濁物質を含む原
水を槽内に供給し、前記懸濁物質を沈殿分離した処理水
を溢流堰から槽外へ排出するようにした沈殿槽におい
て、前記処理水を水面下に設けられて鉛直方向に開口し
た流入口から取り入れた後に、前記溢流堰に導くように
したことを特徴とする。なお、本発明において鉛直方向
とは水平方向に対して概略直角の方向であることを意味
し、具体的には30度以内の傾きを許容する範囲で解釈
し得るものとする。
In order to achieve the above object, a sedimentation tank according to the present invention supplies raw water containing a sedimentable suspended substance into a tank and precipitates and separates the suspended substance. In a sedimentation tank configured to discharge water from the overflow weir to the outside of the tank, the treated water is introduced below the water surface through an inlet vertically opened, and then guided to the overflow weir. It is characterized by. In the present invention, the vertical direction means a direction substantially perpendicular to the horizontal direction, and specifically, can be interpreted within a range in which a tilt of 30 degrees or less is allowed.

【0007】また、本発明に係る沈殿槽は前記流入口が
水面位置に設けられた溢流部と連通しており、この溢流
部は槽内の水面を遮断する仕切板と前記流入口から取り
入れた処理水の溢流堰とを具備したことを特徴とする。
In the sedimentation tank according to the present invention, the inflow port communicates with an overflow portion provided at a water surface position, and the overflow portion is connected to a partition plate that shuts off the water surface in the tank and the inflow port. And an overflow weir for taking in the treated water.

【0008】また、本発明に係る沈殿槽は前記流入口の
下側が上側に比べて外側に張り出ていることを特徴とす
る。
[0008] Further, the sedimentation tank according to the present invention is characterized in that the lower side of the inflow port is protruding outward compared to the upper side.

【0009】[0009]

【発明の実施の形態】図1は本発明の第1の実施形態を
示す要部断面図である。溢流部30は沈殿槽の側壁12
に沿って設けられており、槽内の水面Aを遮断する仕切
板32と溢流堰34とこの溢流堰34の下方に一体化し
て設けられた排水樋36とからなる。排水樋36下方の
側壁12には、側壁12に沿って断面が三角形状の整流
部材38が設けられている。前記仕切板32の下端と整
流部材38の先端が鉛直方向の開口を形成しており、こ
の水面下の開口が処理水の流入口40とされる。また、
排水樋36の外面、仕切板32の内面及び整流部材38
の上面に囲われた領域が前記溢流部30と流入口40と
の連通路42を形成している。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS FIG. 1 is a sectional view showing a main part of a first embodiment of the present invention. The overflow 30 is the side wall 12 of the settling tank.
, And comprises a partition plate 32 for blocking the water surface A in the tank, an overflow weir 34, and a drain gutter 36 integrally provided below the overflow weir 34. A straightening member 38 having a triangular cross section is provided on the side wall 12 below the drain gutter 36 along the side wall 12. The lower end of the partition plate 32 and the tip of the flow regulating member 38 form a vertical opening, and the opening below the water surface serves as an inlet 40 for the treated water. Also,
The outer surface of the drain gutter 36, the inner surface of the partition plate 32, and the rectifying member 38
A region surrounded by the upper surface of the upper surface forms a communication path 42 between the overflow portion 30 and the inlet 40.

【0010】上記の構成において、処理水は流入口40
から連通路42を経て溢流部30に至り、溢流堰34を
溢流して排水樋36に排出される。処理水の流入口40
が鉛直方向の開口であるため、浮上するスカムが流入口
40から流入する可能性が低い。
In the above configuration, the treated water is supplied to the inlet 40
Then, the water reaches the overflow portion 30 through the communication passage 42, overflows the overflow weir 34, and is discharged to the drain gutter 36. Inflow 40 of treated water
Is an opening in the vertical direction, so that it is unlikely that the scum that floats will flow in from the inflow port 40.

【0011】図2は前記流入口40の好ましい位置関係
を示したものである。前記仕切板32の下端と整流部材
38の先端38Bによって形成される流入口40は整流
部材38の先端38Bが所定の寸法Lだけ外側に張り出
ていることが好ましい。整流部材38の下方から浮上す
るスカムSは整流部材38の下面38Aに沿って上昇し
つつ整流部材38の先端38Bに至る。ここでスカムS
の上昇速度をV1、処理水の流入口40における水平方
向の流入速度をV2とすると、スカムSはV3の方向に
斜行して上昇し、仕切板32の下端に到達する。その
後、スカムSは仕切板32の外面32Aに沿って上昇
し、図1に示した水面Aに浮上する。このため、スカム
Sが流入口40から処理水の連通路42側に流入する可
能性が低い。したがって、この実施形態によれば多量の
スカムが発生するような原水を供給した場合において
も、処理水中にスカムが同伴せず、清澄な処理水のみを
溢流堰34から溢流させることができる。
FIG. 2 shows a preferred positional relationship of the inlet 40. As shown in FIG. It is preferable that the inflow port 40 formed by the lower end of the partition plate 32 and the front end 38B of the straightening member 38 has the front end 38B of the straightening member 38 projecting outward by a predetermined dimension L. The scum S floating from below the rectifying member 38 rises along the lower surface 38A of the rectifying member 38 and reaches the tip 38B of the rectifying member 38. Where scum S
Assuming that the ascending speed is V1 and the horizontal inflow speed at the inflow port 40 of the treated water is V2, the scum S rises obliquely in the direction of V3 and reaches the lower end of the partition plate 32. Thereafter, the scum S rises along the outer surface 32A of the partition plate 32 and floats on the water surface A shown in FIG. Therefore, the possibility that the scum S flows from the inflow port 40 to the communication passage 42 side of the treated water is low. Therefore, according to this embodiment, even when raw water that generates a large amount of scum is supplied, scum does not accompany the treated water, and only the clear treated water can overflow from the overflow weir 34. .

【0012】前記寸法Lが過小であると、スカムSはV
3の方向に斜行して上昇した際に流入口40から処理水
の連通路42側に流入し易くなる。また、寸法Lが過大
であると、スカムSが連通路42側に流入する可能性は
より一層減少するが、整流部材38の上面38Cに沈殿
物Cが沈降、堆積する機会が増大するので好ましくな
い。整流部材38の上面38Cに沈降した沈殿物Cが上
面38Cの傾斜に沿って滑り落ち易いように上面38C
の傾斜角度をなるべく大きくすることが好ましい。流入
口40における水平方向の流入速度V2が大きいと、流
入口40に流入する処理水にスカムや懸濁物質が同伴し
易くなる。したがって、流入速度V2を小さくするため
に流入口40の開口面積が極力大きくなるように設計す
る。
If the dimension L is too small, the scum S becomes V
When it rises obliquely in the direction of 3, it becomes easier to flow from the inflow port 40 into the communication passage 42 side of the treated water. When the dimension L is excessively large, the possibility that the scum S flows into the communication passage 42 side is further reduced, but the chance of the sediment C to settle and deposit on the upper surface 38C of the rectifying member 38 is increased, which is preferable. Absent. The upper surface 38C is set so that the sediment C settled on the upper surface 38C of the rectifying member 38 easily slides down along the inclination of the upper surface 38C.
It is preferable to make the inclination angle of the as large as possible. When the inflow velocity V2 in the horizontal direction at the inflow port 40 is high, the scum and suspended matter are more likely to accompany the treated water flowing into the inflow port 40. Therefore, the opening area of the inflow port 40 is designed to be as large as possible to reduce the inflow velocity V2.

【0013】流入口40の水面Aからの深さは、水面A
と沈殿物の界面との中間部位であることが好ましい。水
面Aから沈殿物の界面までの深さを予め経験的に把握し
ておけば、流入口40の深さを容易に求めることができ
る。
The depth of the inlet 40 from the water surface A is
It is preferably an intermediate site between the interface and the precipitate. If the depth from the water surface A to the interface of the sediment is grasped empirically in advance, the depth of the inlet 40 can be easily obtained.

【0014】図3は本発明の第2の実施形態を示す要部
断面図である。溢流部44は沈殿槽の側壁12に沿って
設けられており、槽内の水面Aを遮断する仕切板46と
溢流堰48とこの溢流堰48の外側に設けられた排水樋
50とからなる。前記仕切板46の底面52には連通管
54の一端が接続されている。また、連通管54の他端
は鉛直方向の開口を形成しており、この水面下の開口が
処理水の流入口56とされる。このような連通管54が
所定の間隔で仕切板46の底面52に多数本接続されて
いる。
FIG. 3 is a sectional view showing a main part of a second embodiment of the present invention. The overflow portion 44 is provided along the side wall 12 of the sedimentation tank, and includes a partition plate 46 for blocking the water surface A in the tank, an overflow weir 48, and a drain gutter 50 provided outside the overflow weir 48. Consists of One end of a communication pipe 54 is connected to the bottom surface 52 of the partition plate 46. Further, the other end of the communication pipe 54 forms a vertical opening, and the opening below the water surface is an inlet 56 for the treated water. A large number of such communication tubes 54 are connected to the bottom surface 52 of the partition plate 46 at predetermined intervals.

【0015】この実施形態においても、処理水の流入口
56が水面下に、かつ鉛直方向に開口しているので、ス
カムや懸濁物質が流入口56から処理水とともに連通管
54内に流入する可能性が低い。したがって、多量のス
カムが発生するような原水を供給した場合においても、
処理水中にスカムが同伴せず、清澄な処理水のみを前記
連通管54を経由して溢流堰48から溢流させることが
できる。
Also in this embodiment, since the inflow port 56 of the treated water is opened below the water surface and in the vertical direction, scum and suspended matter flow into the communication pipe 54 from the inflow port 56 together with the treated water. Unlikely. Therefore, even when supplying raw water that generates a large amount of scum,
The scum does not accompany the treated water, and only the clean treated water can overflow from the overflow weir 48 via the communication pipe 54.

【0016】この実施形態において、前記連通管54端
部を図4に示すようにラッパ状に拡大させた流入口58
とし、この流入口58の下側が上側に比べて外側に張り
出た構造にすることが好ましい。このような構造によれ
ば流入口58での処理水の流入速度が小さくなるので、
スカムが処理水の流入速度に抗して上方に浮上し易い。
このため、スカムや懸濁物質が流入口56から処理水と
ともに連通管54内に流入する可能性がより一層低くな
る。
In this embodiment, the end of the communication pipe 54 is formed as a trumpet-shaped inlet 58 as shown in FIG.
It is preferable to adopt a structure in which the lower side of the inflow port 58 protrudes outward compared to the upper side. According to such a structure, the inflow speed of the treated water at the inflow port 58 is reduced.
The scum tends to float upward against the inflow speed of the treated water.
For this reason, the possibility that scum or suspended matter flows into the communication pipe 54 together with the treated water from the inflow port 56 is further reduced.

【0017】図5は本発明の第3の実施形態を示す要部
断面図である。溢流部60は沈殿槽の任意の位置に設け
られており、槽内の水面Aを遮断する仕切板62と溢流
堰64とこの溢流堰64の外側に設けられた排水樋66
とからなる。前記仕切板62の底面68には連通管70
の一端が接続されている。また、連通管70の他端は処
理水の流入部72とされる。この流入部72は円錐状の
上部部材74と、この上部部材72の下方にギャップG
を空けて設けた逆円錐状の下部部材76とからなる。下
部部材76の下端には開孔78が設けられている。
FIG. 5 is a sectional view showing a main part of a third embodiment of the present invention. The overflow portion 60 is provided at an arbitrary position in the sedimentation tank, and includes a partition plate 62 for blocking the water surface A in the tank, an overflow weir 64, and a drain gutter 66 provided outside the overflow weir 64.
Consists of A communication pipe 70 is provided on the bottom surface 68 of the partition plate 62.
Are connected at one end. The other end of the communication pipe 70 is an inflow portion 72 of the treated water. The inflow portion 72 has a conical upper member 74 and a gap G below the upper member 72.
And a lower member 76 having an inverted conical shape. An opening 78 is provided at a lower end of the lower member 76.

【0018】上記の構成においては、前記ギャップGの
部分が鉛直方向に開口した処理水の流入口80となる。
流入口80から流入した処理水は連通管70内を上昇
し、溢流部60で溢流堰64を溢流して排水樋66から
槽外に排出される。
In the above configuration, the portion of the gap G serves as the inflow port 80 of the treated water which is opened in the vertical direction.
The treated water flowing from the inflow port 80 rises in the communication pipe 70, overflows the overflow weir 64 at the overflow section 60, and is discharged out of the tank from the drain gutter 66.

【0019】この実施形態においても、処理水の流入口
80が水面下に、かつ鉛直方向に開口しているので、ス
カムや懸濁物質が流入口80から処理水とともに連通管
70内に流入する可能性が低い。したがって、多量のス
カムが発生するような原水を供給した場合においても、
処理水中にスカムが同伴せず、清澄な処理水のみを前記
連通管70を経由して溢流堰64から溢流させることが
できる。
Also in this embodiment, since the inflow port 80 of the treated water is opened below the water surface and in the vertical direction, scum and suspended matter flow into the communication pipe 70 together with the treated water from the inflow port 80. Unlikely. Therefore, even when supplying raw water that generates a large amount of scum,
The scum does not accompany the treated water, and only the clear treated water can overflow from the overflow weir 64 via the communication pipe 70.

【0020】なお、この実施形態では流入部72の内部
が懐の広いそろばん球の形状とされているので、処理水
に同伴して流入した懸濁物質Cはこの流入部72の内部
で沈降し、下部部材76の傾斜面に沿って移動しつつ、
開孔78から落下する。したがって、清澄な処理水を得
やすく、かつ、流入部72や連通管70に懸濁物質が堆
積して閉塞するといった運転操作上のトラブルを未然に
防止できる。
In this embodiment, since the inside of the inflow portion 72 is formed in the shape of a large abacus ball, the suspended solids C that have flowed in with the treated water settle inside the inflow portion 72. While moving along the inclined surface of the lower member 76,
It falls from the opening 78. Therefore, it is possible to easily obtain clear treated water, and it is possible to prevent troubles in operation such as suspended substances accumulating and blocking the inflow portion 72 and the communication pipe 70.

【0021】前記の各実施形態は主に円形型沈殿槽を想
定して説明したが、本発明は方形型の沈殿槽にも適用で
きる。また、本発明に係る沈殿槽とは常識的な範囲で広
義に解釈し得るものとし、いわゆる沈殿池をも含む。
Although the above embodiments have been described mainly on the assumption of a circular sedimentation tank, the present invention can also be applied to a square type sedimentation tank. The sedimentation tank according to the present invention can be interpreted in a broad sense within a common sense, and includes a so-called sedimentation tank.

【0022】[0022]

【発明の効果】上述のとおり、本発明に係る沈殿槽によ
れば多量のスカムが発生するような原水を供給した場合
においても、処理水中にスカムが同伴せず、清澄な処理
水のみを溢流させることができる。
As described above, according to the sedimentation tank of the present invention, even when raw water that generates a large amount of scum is supplied, scum does not accompany the treated water, and only clear treated water overflows. Can be washed away.

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

【図1】本発明の第1の実施形態を示す要部断面図であ
る。
FIG. 1 is a cross-sectional view of a main part showing a first embodiment of the present invention.

【図2】第1の実施形態の流入口における好ましい位置
関係を示す説明図である。
FIG. 2 is an explanatory diagram showing a preferred positional relationship at an inflow port of the first embodiment.

【図3】本発明の第2の実施形態を示す要部断面図であ
る。
FIG. 3 is a sectional view of a main part showing a second embodiment of the present invention.

【図4】第2の実施形態の変形例を示す要部断面図であ
る。
FIG. 4 is a sectional view of a main part showing a modification of the second embodiment.

【図5】本発明の第3の実施形態を示す要部断面図であ
る。
FIG. 5 is a sectional view of a main part showing a third embodiment of the present invention.

【図6】円形型沈殿槽の一般的な構造を示す断面図であ
る。
FIG. 6 is a sectional view showing a general structure of a circular settling tank.

【符号の説明】 12……側壁 30、44、60……溢流部 32、4
2、62……仕切板 34、48、64……溢流堰 36、50、66……排
水樋 40、56、58、80……流入口 42……連通路
54、70……連通管
[Explanation of Signs] 12 ... side wall 30, 44, 60 ... overflow section 32, 4
2, 62 Partition plate 34, 48, 64 Overflow weir 36, 50, 66 Drain gutter 40, 56, 58, 80 Inlet 42 Communication passage
54, 70 …… Communication pipe

───────────────────────────────────────────────────── フロントページの続き (72)発明者 志田 勝己 東京都千代田区内神田一丁目1番14号 日 立プラント建設株式会社内 ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Katsumi Shida 1-1-1 Uchikanda, Chiyoda-ku, Tokyo Inside Hitachi Plant Construction Co., Ltd.

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】沈降性の懸濁物質を含む原水を槽内に供給
し、前記懸濁物質を沈殿分離した処理水を溢流堰から槽
外へ排出するようにした沈殿槽において、前記処理水を
水面下に設けられて鉛直方向に開口した流入口から取り
入れた後に、前記溢流堰に導くようにしたことを特徴と
する沈殿槽。
In a sedimentation tank, raw water containing a suspended solid is supplied into a tank, and treated water obtained by separating and separating the suspended substance is discharged from an overflow weir to the outside of the tank. A sedimentation tank, wherein water is introduced from an inflow port provided below the water surface and opened in a vertical direction, and then guided to the overflow weir.
【請求項2】前記流入口は水面位置に設けられた溢流部
と連通しており、この溢流部は槽内の水面を遮断する仕
切板と前記流入口から取り入れた処理水の溢流堰とを具
備したことを特徴とする請求項1に記載の沈殿槽。
2. The inflow port communicates with an overflow portion provided at a water surface position. The overflow portion is a partition plate for shutting off the water surface in the tank and an overflow of the treated water introduced from the inflow port. The sedimentation tank according to claim 1, further comprising a weir.
【請求項3】前記流入口の下側が上側に比べて外側に張
り出ていることを特徴とする請求項1に記載の沈殿槽。
3. The sedimentation tank according to claim 1, wherein a lower side of the inflow port projects outward compared to an upper side.
JP2000141054A 2000-05-15 2000-05-15 Sedimentation tank Expired - Fee Related JP3882464B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000141054A JP3882464B2 (en) 2000-05-15 2000-05-15 Sedimentation tank

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000141054A JP3882464B2 (en) 2000-05-15 2000-05-15 Sedimentation tank

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Publication Number Publication Date
JP2001321609A true JP2001321609A (en) 2001-11-20
JP3882464B2 JP3882464B2 (en) 2007-02-14

Family

ID=18648230

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP3882464B2 (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100920462B1 (en) 2009-07-13 2009-10-08 주식회사삼영이앤티 The sediment equipment with inclined plates for water treatment
JP2010110726A (en) * 2008-11-10 2010-05-20 Act:Kk Wastewater treatment apparatus
KR101254946B1 (en) * 2013-03-12 2013-04-16 주식회사삼영이앤티 Circular thicker sedimentation tank
CN107253817A (en) * 2017-08-15 2017-10-17 安尼康(福建)环保设备有限公司 Groove is closed in a kind of square flocculation for realizing uniform divided flows
ES2760149A1 (en) * 2019-08-06 2020-05-13 Acuinge Gestion S L DECANTER FOR WATER TREATMENT AND TREATMENT PROCESSES (Machine-translation by Google Translate, not legally binding)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010110726A (en) * 2008-11-10 2010-05-20 Act:Kk Wastewater treatment apparatus
KR100920462B1 (en) 2009-07-13 2009-10-08 주식회사삼영이앤티 The sediment equipment with inclined plates for water treatment
KR101254946B1 (en) * 2013-03-12 2013-04-16 주식회사삼영이앤티 Circular thicker sedimentation tank
CN107253817A (en) * 2017-08-15 2017-10-17 安尼康(福建)环保设备有限公司 Groove is closed in a kind of square flocculation for realizing uniform divided flows
ES2760149A1 (en) * 2019-08-06 2020-05-13 Acuinge Gestion S L DECANTER FOR WATER TREATMENT AND TREATMENT PROCESSES (Machine-translation by Google Translate, not legally binding)

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