JPH11267409A - Precipitating type waste water treating tank - Google Patents

Precipitating type waste water treating tank

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Publication number
JPH11267409A
JPH11267409A JP7756798A JP7756798A JPH11267409A JP H11267409 A JPH11267409 A JP H11267409A JP 7756798 A JP7756798 A JP 7756798A JP 7756798 A JP7756798 A JP 7756798A JP H11267409 A JPH11267409 A JP H11267409A
Authority
JP
Japan
Prior art keywords
tank
wastewater
initial
sedimentation
settling tank
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.)
Pending
Application number
JP7756798A
Other languages
Japanese (ja)
Inventor
Tetsuaki Goto
徹朗 後藤
Yoshikazu Momotani
芳和 桃谷
Fumio Kodama
文雄 児玉
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.)
Sumitomo Metal Mining Co Ltd
Original Assignee
Sumitomo Metal Mining Co 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 Sumitomo Metal Mining Co Ltd filed Critical Sumitomo Metal Mining Co Ltd
Priority to JP7756798A priority Critical patent/JPH11267409A/en
Publication of JPH11267409A publication Critical patent/JPH11267409A/en
Pending legal-status Critical Current

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

PROBLEM TO BE SOLVED: To reduce the frequency of work for recovering a precipitate from an initial precipitation tank to improve work efficiency and to reduce the costs of waste water treatment by preventing slug from being biasted and precipitated near the inflow port part of the initial sedimentation tank and wide dispersing the slug in the initial sedimentation tank to precipitate it. SOLUTION: This precipitating type waste water treating tank has such a shape that from a waste water inflow port 1 toward the downstream, its width is gradually enlarged from width W1 equal to ore more than that of a waste water inflow port 1 to width W2 equal to that of the bottom surface of an initial sedimentation tank 2 and is provided with a floor surface 6 inclined downward and also three sides except the downstream side are covered with a wall surface 2b along the shape of the floor surface. Further, on the floor surface 6, a baffle 7 is provided so that the flow is divided into two by putting a wedge for the waste water flow.

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、微細な固形物粒子
を含む廃水から固形物粒子を自然沈降によって水と分離
して回収するための沈降式廃水処理槽に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a sedimentation type wastewater treatment tank for separating solid particles from wastewater containing fine solid particles by natural sedimentation and recovering the separated water.

【0002】[0002]

【従来の技術】非鉄金属乾式製錬で発生するスラグは水
砕設備で水砕された後、回収されている。この水砕処理
過程では水砕スラグと呼ばれる大量の微粒子状のスラグ
を含む廃水が発生する。この廃水からスラグを沈降させ
て回収するための装置の一つとして、従来より、沈降式
廃水処理装置が用いられている。図4は、従来の沈降式
廃水処理槽の基本構成を示す平面概略図、図5は、図4
のV−V線に沿う断面図である。
2. Description of the Related Art Slag generated in nonferrous metal dry smelting is granulated by a granulator and recovered. In this water granulation process, wastewater containing a large amount of fine slag called granulated slag is generated. As one of devices for sedimenting and collecting slag from this wastewater, a sedimentation type wastewater treatment device has been conventionally used. FIG. 4 is a schematic plan view showing a basic configuration of a conventional sedimentation type wastewater treatment tank, and FIG.
FIG. 5 is a sectional view taken along the line V-V of FIG.

【0003】この廃水処理槽は、廃水を最初に導いて水
砕スラグの大部分の粒子を沈殿させるための初期沈降槽
51と、その下流に配置されていて、残りの比較的微細
な粒子を沈殿させて清澄な水を得るための最終沈降槽5
2とで構成されている。また、初期沈降槽51と最終沈
降槽52との間には、初期沈降槽51内の廃水を整流し
て最終沈降槽52へと流れるようにするための複数の流
通孔53をその全面に均一に有する整流壁54が設けら
れている。
[0003] This wastewater treatment tank is provided with an initial settling tank 51 for conducting wastewater first to precipitate most of the granulated slag particles, and is disposed downstream thereof to remove the remaining relatively fine particles. Final settling tank 5 for sedimentation to obtain clear water
And 2. Further, between the initial settling tank 51 and the final settling tank 52, a plurality of flow holes 53 for rectifying wastewater in the initial settling tank 51 and flowing to the final settling tank 52 are uniformly formed on the entire surface. Are provided.

【0004】処理される廃水は、排水路55を通り、廃
水流入口56から初期沈降槽51内に流れ込む。この初
期沈降槽51の流出側は、流通孔53を除く整流壁54
の壁面に阻まれている。また、初期沈降槽51は、廃水
流入口56の幅に比べて遙かに大きな幅を有する、上が
空いた箱状に形成されていて、大量の廃水を入れること
が可能な容積を有している。このため、排水路55を流
れる廃水は、初期沈降槽51へ流れ込んだ直後に流速が
急激に弱められる。そして、廃水中のスラグの粒子の大
部分は、初期沈降槽51内で、沈降し堆積する。このと
き、廃水流入口56付近では粒子の大きなスラグが堆積
し、下流に向かうにしたがって堆積するスラグの粒子は
小さくなる。また、スラグの沈降量も下流に向かうにし
たがって次第に少なくなる。なお、初期沈降槽51に流
れ込んだときの廃水は、スラグと水が完全に混合してお
り、下流に向かうにしたがって、廃水中のスラグの混合
割合が徐々に少なくなる。初期沈降槽51を流れる廃水
は、整流壁54中の流通孔53を通り最終沈降槽52へ
流れ込む。流れは流通孔54を通ることによって整流さ
れる。最終沈降槽52では、初期沈降槽51で沈降しき
れなかった廃水中の比較的微細な粒子を下流へ向かう流
れの中で沈降させる。そして、最終沈降槽52の放流側
へ流れるまでの間に、ほぼ清澄な水が得られる。最終沈
降槽52を経て得られた清澄流は、図示省略した放流口
から放流される。
The wastewater to be treated passes through a drainage channel 55 and flows into a primary sedimentation tank 51 from a wastewater inlet 56. The outflow side of this initial settling tank 51 is provided with a rectifying wall
Is blocked by the wall. Further, the initial settling tank 51 is formed in an open box shape having a width much larger than the width of the wastewater inlet 56, and has a volume capable of containing a large amount of wastewater. ing. For this reason, the flow rate of the wastewater flowing through the drainage channel 55 is rapidly reduced immediately after flowing into the initial settling tank 51. Most of the slag particles in the wastewater settle and accumulate in the initial settling tank 51. At this time, slag with large particles accumulates near the wastewater inlet 56, and the particles of the slag accumulate smaller as going downstream. In addition, the amount of slag settled gradually decreases toward the downstream. In the wastewater flowing into the initial settling tank 51, the slag and the water are completely mixed, and the mixing ratio of the slag in the wastewater gradually decreases toward the downstream. The wastewater flowing through the initial settling tank 51 flows into the final settling tank 52 through the flow hole 53 in the straightening wall 54. The flow is rectified by passing through the flow holes 54. In the final sedimentation tank 52, relatively fine particles in the wastewater that have not completely settled in the initial sedimentation tank 51 are settled in a stream flowing downstream. Then, almost clear water is obtained before flowing to the discharge side of the final settling tank 52. The clarified stream obtained through the final settling tank 52 is discharged from a discharge port not shown.

【0005】一方、初期沈降槽51に沈殿したスラグA
は、図6(a) ,(b) に示すように、例えば、グラブバケ
ットと呼ばれる開閉式の荷役用具を備えたクレーン57
を自動運転させて、グラブバケット58ですくい上げて
トラック59に積載して回収する。また、最終沈殿槽5
2に沈殿したスラグは、整流壁付近に沈降したものにつ
いては、上記グラブバケットを備えたクレーンにより回
収する。放流側付近に沈殿したスラグは数十ヶ月ごとに
槽内の水を抜いた後、図示省略したローダーと呼ばれ
る、その前面に大きなショベルを持つ車両を用いて回収
する。なお、堆積するスラグの大部分は初期沈降槽51
に沈降するため、初期沈降槽51でのスラグの回収作業
頻度は、最終沈殿槽52に比べて遙かに多い。このよう
にスラグの回収作業では、沈降槽の大きさに合わせて非
常に大がかりな装置を使用するので、コスト負担が大き
くなる。コストを低減するには、可能な限り回収作業頻
度を減らすことが望まれる。そのためには、スラグの大
部分が沈降する初期沈降槽で、スラグの堆積範囲を槽全
体に可能な限り均等に広げる必要がある。
On the other hand, slag A precipitated in the initial settling tank 51
As shown in FIGS. 6 (a) and 6 (b), for example, a crane 57 equipped with an openable and
Is automatically operated, picked up by the grab bucket 58, loaded on the truck 59, and collected. In addition, the final sedimentation tank 5
The slag that has settled in 2 is settled in the vicinity of the rectifying wall and collected by a crane equipped with the above-mentioned grab bucket. Slag that has settled near the discharge side is drained from the tank every several tens of months, and then collected using a vehicle called a loader (not shown) having a large shovel in front of it. Most of the slag to be deposited is in the initial settling tank 51.
Therefore, the frequency of the slag collection operation in the initial settling tank 51 is much higher than that in the final settling tank 52. As described above, in the slag collecting operation, a very large apparatus is used in accordance with the size of the settling tank, so that the cost burden is increased. In order to reduce costs, it is desirable to reduce the frequency of collection work as much as possible. For this purpose, it is necessary to spread the slag accumulation area as uniformly as possible over the entire tank in an initial settling tank in which most of the slag is settled.

【0006】[0006]

【発明が解決しようとする課題】しかし、従来の沈降式
廃水処理槽では、図4および図5に示すように初期沈降
槽51が、排水路55の出口すなわち初期沈降槽51の
廃水流入口56から直ぐに幅が広い、上が空いた箱状の
槽として連なるように構成されていたため、廃水に含ま
れるスラグの大部分が初期沈降槽51の廃水流入口56
付近にのみ偏って沈降するといった現象が起き、廃水流
入口56付近がすぐに堆積物で埋まってしまうという結
果になっていた。他方、廃水流入口56付近の堆積物は
廃水流入の障害となるため、初期沈降槽51の全体の沈
降物回収可能量に満たない量の堆積物であっても、上で
述べたような大がかりな堆積物の除去作業を行わなけれ
ばならない。このため、従来の沈降式廃水処理槽では、
初期沈降槽に堆積したスラグの回収作業を頻繁に行わな
ければならず、回収作業効率が悪くなり廃水処理のコス
ト負担が大きくなっていた。本発明は、上記の問題点を
解決するためになされたものであり、初期沈降槽の流入
口付近にスラグが偏って沈降することがないようにし、
初期沈降槽内に広く分散させてスラグを沈降させること
によって、初期沈降槽から沈降物を回収する作業頻度を
低減させて作業効率を向上させ、廃水処理のコストを低
減させることができる沈降式廃水処理槽の提供を課題と
する。
However, in the conventional settling type wastewater treatment tank, as shown in FIGS. 4 and 5, the initial settling tank 51 is provided with an outlet of a drainage channel 55, that is, a wastewater inlet 56 of the initial settling tank 51. The slag contained in the wastewater was mostly discharged from the wastewater inlet 56 of the initial settling tank 51 because the slag contained in the wastewater was largely connected to a box-shaped tank having a wide width and an open top.
A phenomenon such that the sedimentation was deviated only in the vicinity occurred, and the result was that the vicinity of the wastewater inlet 56 was immediately filled with sediment. On the other hand, the sediment in the vicinity of the wastewater inlet 56 obstructs the inflow of the wastewater. Therefore, even if the amount of sediment is less than the total sediment recoverable amount of the initial sedimentation tank 51, the scale described above is large. Work must be performed to remove the sediment. For this reason, in the conventional settling type wastewater treatment tank,
The slag collected in the initial settling tank has to be collected frequently, and the efficiency of the collection operation has deteriorated and the cost burden of wastewater treatment has increased. The present invention has been made in order to solve the above problems, to prevent the slag is settled near the inlet of the initial settling tank,
Sedimentation wastewater that can be dispersed widely in the initial sedimentation tank to settle slag, thereby reducing the frequency of work for collecting sediment from the initial sedimentation tank, improving work efficiency, and reducing wastewater treatment costs. The task is to provide a processing tank.

【0007】[0007]

【課題を解決するための手段】上述の課題を解決するた
め、本発明の沈降式廃水処理槽は、廃水流入口が開口す
る初期沈降槽と、その下流に配置される沈降槽と、初期
沈降槽とその下流に配置される沈降槽との間に配置され
ていて、初期沈降槽の流れを整流して下流に配置される
沈降槽に送り込むための複数の流通孔を有する整流壁と
を備えた沈降式廃水処理槽において、廃水流入口から下
流に向けて、廃水流入口と同程度以上の幅から初期沈降
槽の底面と同程度の幅にまで徐々に幅を広げた形状をな
し、かつ、下向きに傾斜する床面を設けると共に、その
床面形状に沿って下流側以外の三方が壁面で覆われるよ
うにし、さらに、その床面上に、廃水流に対し楔を入れ
て流れを二分するようにバッフル(邪魔板)を設けるよ
うにする。
In order to solve the above-mentioned problems, a sedimentation type wastewater treatment tank according to the present invention comprises an initial sedimentation tank having an open wastewater inlet, a sedimentation tank disposed downstream thereof, and an initial sedimentation tank. A rectifying wall disposed between the tank and a settling tank disposed downstream thereof, and having a plurality of flow holes for rectifying the flow of the initial settling tank and sending the flow to the settling tank disposed downstream. In the sedimentation type wastewater treatment tank, the width is gradually increased from the wastewater inlet to the downstream from the width approximately equal to or larger than the wastewater inlet to the width similar to the bottom of the initial sedimentation tank, and In addition to providing a downwardly inclined floor surface, three sides other than the downstream side are covered with wall surfaces along the floor surface shape, and further, on the floor surface, wedges are inserted into the wastewater flow to divide the flow into two. A baffle (baffle) is provided so that

【0008】また、本発明は、好ましくは、バッフル
(邪魔板)が枠組と、それを支える支柱と、枠組の外側
に取り付けられた平板とからなり、これらを構成する材
料が金属、プラスチック、またはそれらの複合材料で構
成される。
In the present invention, preferably, the baffle (baffle plate) comprises a frame, a support for supporting the frame, and a flat plate attached to the outside of the frame, and the material constituting these is metal, plastic, or It is composed of these composite materials.

【0009】[0009]

【発明の実施形態】以下、本発明による沈降式廃水処理
槽について図を用いて説明する。図1は本発明による沈
降式廃水処理槽の一実施形態を示す平面概略図、図2は
図1のII−II線に沿う断面図である。図3は本実施形態
におけるバッフルをそれぞれ示し、(a) は図2の要部拡
大図、(b) は枠組みの構成概要を示す斜視図、(c) はそ
の平面図である。本実施形態による沈降式廃水処理槽
は、廃水流入口1が開口する初期沈降槽2と、その下流
に配置される最終沈降槽3と、初期沈降槽2と最終沈降
槽3との間に配置された、複数の流通孔4をその全面に
均一に有する整流壁5とから構成されている。整流壁5
は、流通孔4を介して初期沈降槽2の流れを整流して最
終沈降槽3に送り込むようになっている。なお、初期沈
降槽2は、図中省略したバケットクレーンなどを用いた
沈降物の回収作業が容易となるように、その深さを最終
沈降槽3の深さよりも深くしておくとよい。
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS A sedimentation type wastewater treatment tank according to the present invention will be described below with reference to the drawings. FIG. 1 is a schematic plan view showing an embodiment of a sedimentation type wastewater treatment tank according to the present invention, and FIG. 2 is a cross-sectional view taken along line II-II of FIG. 3A and 3B show the baffles in the present embodiment, respectively. FIG. 3A is an enlarged view of a main part of FIG. 2, FIG. 3B is a perspective view showing the outline of the configuration of the framework, and FIG. The sedimentation type wastewater treatment tank according to the present embodiment is provided with an initial sedimentation tank 2 in which a wastewater inlet 1 is opened, a final sedimentation tank 3 disposed downstream thereof, and an initial sedimentation tank 2 and a final sedimentation tank 3. And a flow regulating wall 5 having a plurality of flow holes 4 uniformly on the entire surface thereof. Rectification wall 5
The rectifier rectifies the flow of the initial settling tank 2 through the circulation hole 4 and sends it to the final settling tank 3. The depth of the initial sedimentation tank 2 may be greater than the depth of the final sedimentation tank 3 so that the sediment collection operation using a bucket crane or the like omitted in the figure is facilitated.

【0010】本実施形態の沈降式廃水処理槽では、図2
に示すように廃水流入口1から下流に向けて、下向きに
傾斜する床面6を設けている。床面6は、図1に示すよ
うに廃水流入口1と同程度以上の幅W1 から初期沈降槽
2の底面2aと同程度の幅W2 にまで徐々に幅を広げて
形成してある。また、その床面6の形状に沿って下流側
以外の三方は壁面2bで覆われている。但し、この構成
だけでは、沈降物は初期沈降槽2の廃水流入口1付近に
その多くが偏って堆積してしまう。廃水入口部1付近で
の偏った沈降を防止するためには、廃水流を初期沈降槽
2の底面2aと同程度の幅W2 に拡がるようにして導入
しなければならない。そこで、本実施形態では、床面6
の上に流れに対して楔を入れるようにバッフル(邪魔
板)7を設置して、バッフル7で廃水流を二分するよう
にしている。
In the sedimentation type wastewater treatment tank of this embodiment, FIG.
As shown in the figure, a floor surface 6 which is inclined downward from the wastewater inlet 1 to the downstream is provided. As shown in FIG. 1, the floor 6 is formed so as to gradually increase in width from a width W 1 equal to or larger than the wastewater inlet 1 to a width W 2 equal to the bottom 2 a of the initial settling tank 2. . Further, three sides other than the downstream side along the shape of the floor surface 6 are covered with the wall surface 2b. However, with this configuration alone, most of the sediment accumulates unevenly near the wastewater inlet 1 of the initial settling tank 2. In order to prevent uneven sedimentation in the vicinity of the wastewater inlet 1, the wastewater flow must be introduced so as to spread to a width W 2 approximately equal to the bottom surface 2 a of the initial sedimentation tank 2. Therefore, in this embodiment, the floor 6
A baffle (baffle plate) 7 is installed on the top so as to insert a wedge for the flow, and the baffle 7 divides the wastewater stream into two.

【0011】バッフル7は、図3(a) ,(b) および(c)
に示すように棒状部材を三角形状に組み上げてなる枠組
8を支柱9で支え、枠組8の外側に平板10を取り付け
て構成されている。これらの材質は金属、プラスチッ
ク、またはそれらの複合材料のいずれであってもよい。
廃水が金属腐食性の高い海水であることを考慮して、鉄
材などの金属材の表面をプラスチックでコートするなど
の防錆処理を施した複合材を用いることが好ましい。そ
して、バッフル7は、例えば支柱9の下端を床面6に埋
め込み、その上端に例えば網を張りめぐらしてその上か
ら沈降槽内を観察できるようにした点検枠11の一部に
備えられたH鋼(図示省略)などに嵌め込むようにして
固定されている。図1および図2においては、点検枠1
1は省略してある。
The baffle 7 is shown in FIGS. 3 (a), 3 (b) and 3 (c).
As shown in FIG. 1, a frame 8 formed by assembling rod-shaped members in a triangular shape is supported by columns 9, and a flat plate 10 is attached to the outside of the frame 8. These materials may be any of metal, plastic, or a composite material thereof.
Considering that wastewater is seawater having high metal corrosivity, it is preferable to use a composite material that has been subjected to a rust-proof treatment such as coating the surface of a metal material such as an iron material with a plastic. The baffle 7 is provided on a part of an inspection frame 11 in which, for example, the lower end of the column 9 is embedded in the floor surface 6 and the upper end thereof is covered with, for example, a net so that the inside of the settling tank can be observed from above. It is fixed so as to be fitted into steel (not shown). In FIG. 1 and FIG.
1 is omitted.

【0012】なお、本実施形態の初期沈降槽2は、底面
2aと同程度の幅W2 をした床面6の縁部6aから、底
面2aに向かって垂直に掘り下げられている。また、図
2に示すように本実施形態の初期沈降槽2では、傾斜す
る床面6の設置箇所を予め階段状に形成しておき、そこ
に断面が三角形状で床面6に相当する斜面が図1に示す
ような形状の部材が嵌め込まれている。但し、床面6の
縁部6aから、底面2aに至るまでの形態および床面6
の設置態様は、必ずしも本実施形態に限定されるもので
はない。その他、各沈降槽の長さ、幅、深さなどの寸法
および床面6の傾斜角度などは、廃水中のスラグの所定
の粒径における沈降速度、沈降時間、水平移動距離、最
終沈降槽の出口付近の液中のスラグの許容濃度などを勘
案して、設計されている。
[0012] The initial settling tank 2 of the present embodiment, the edge portion 6a of the floor surface 6 in which the width W 2 of the same level as the bottom surface 2a, are dug vertically toward the bottom surface 2a. In addition, as shown in FIG. 2, in the initial settling tank 2 of the present embodiment, the installation location of the inclined floor surface 6 is formed in advance in a step-like manner, and a slope having a triangular cross section corresponding to the floor surface 6 is formed there. However, a member having a shape as shown in FIG. 1 is fitted. However, the form from the edge 6a of the floor 6 to the bottom 2a and the floor 6
Is not necessarily limited to this embodiment. In addition, the length, width, depth and other dimensions of each sedimentation tank and the inclination angle of the floor 6 are settled at a predetermined particle size of the slag in the wastewater, the settling time, the settling time, the horizontal movement distance, and the final settling tank. It is designed in consideration of the allowable concentration of slag in the liquid near the outlet.

【0013】次に、このように構成された本実施例の沈
降式廃水処理槽における廃水処理について説明する。処
理される廃水は、排水路12を通り、廃水流入口1から
初期沈降槽2内に流れ込む。排水路12を流れる廃水
は、初期沈降槽2へ流れ込んだとき流速が急激に弱めら
れる。そして、廃水中のスラグの粒子の大部分は、初期
沈降槽2内で、沈降し堆積する。このとき、廃水流入口
1側では粒子の大きなスラグが堆積し、下流に向かうに
したがって堆積するスラグの粒子は小さくなる。また、
スラグの沈降量も下流に向かうにしたがって次第に少な
くなる。なお、初期沈降槽2に流れ込んだときの廃水
は、スラグと水が完全に混合しており、下流に向かうに
したがって、廃水中のスラグの混合割合が徐々に少なく
なる。初期沈降槽2を流れる廃水は、整流壁5中の流通
孔4を通り最終沈降槽3へ流れ込む。流れは流通孔4を
通ることによって整流される。最終沈降槽3では、初期
沈降槽2で沈降しきれなかった廃水中の比較的微細な粒
子を下流へ向かう流れの中で沈降させる。そして、最終
沈降槽3の放流側へ流れるまでの間に、ほぼ清澄な水が
得られる。最終沈降槽3を経て得られた清澄流は、図示
省略した放流口から放流される。
Next, the wastewater treatment in the sedimentation type wastewater treatment tank of the present embodiment configured as described above will be described. The wastewater to be treated flows through the drainage channel 12 from the wastewater inlet 1 into the initial settling tank 2. When the wastewater flowing through the drainage channel 12 flows into the initial settling tank 2, the flow velocity is rapidly reduced. Most of the slag particles in the wastewater settle and accumulate in the initial settling tank 2. At this time, slag with large particles accumulates at the wastewater inlet 1 side, and the particles of the slag accumulate smaller as going downstream. Also,
The amount of slag settling also decreases gradually toward the downstream. In the wastewater flowing into the initial settling tank 2, the slag and the water are completely mixed, and the mixing ratio of the slag in the wastewater gradually decreases toward the downstream. The wastewater flowing in the initial settling tank 2 flows into the final settling tank 3 through the flow hole 4 in the flow regulating wall 5. The flow is rectified by passing through the flow holes 4. In the final sedimentation tank 3, relatively fine particles in the wastewater that could not be settled in the initial sedimentation tank 2 are settled in a stream flowing downstream. Then, almost clear water is obtained before flowing to the discharge side of the final settling tank 3. The clarified stream obtained through the final settling tank 3 is discharged from a discharge port not shown.

【0014】一方、初期沈降槽2に沈殿したスラグは、
図6(a) ,(b) に示すように、例えば、グラブバケット
と呼ばれる開閉式の荷役用具を備えたクレーン57を自
動運転させて、グラブバケット58ですくい上げてトラ
ック59に積載して回収する。また、最終沈降槽3に沈
殿したスラグは、整流壁5付近に沈降したものについて
は、上記グラブバケットを備えたクレーンにより回収す
る。放流側付近に沈殿したスラグは数十ヶ月ごとに最終
沈降槽3内の水を抜いた後、図示省略したローダーを用
いて回収する。
On the other hand, the slag precipitated in the initial settling tank 2 is:
As shown in FIGS. 6 (a) and 6 (b), for example, a crane 57 equipped with an openable cargo handling device called a grab bucket is automatically operated, picked up by a grab bucket 58, loaded on a truck 59, and collected. . The slag settled in the final settling tank 3 is settled in the vicinity of the straightening wall 5 and collected by a crane equipped with the above-mentioned grab bucket. The slag that has settled near the discharge side is drained from the final settling tank 3 every several tens of months, and then collected using a loader (not shown).

【0015】このとき、本実施形態の沈降式廃水処理装
置は、廃水流入口1から下流に向けて、床面6を下向き
に傾斜するように設けたので、沈降物が初期沈降槽2の
内部にまで流れ込み易くなる。このとき、床面6は、廃
水流入口1と同程度以上の幅W1 から初期沈降槽2の底
面2aと同程度の幅W2 にまで徐々に幅を広げて形成
し、その床面6の形状に沿って下流側以外の三方を壁面
2bで覆い、さらに、床面6の上に流れに対して楔を入
れるようにバッフル7を設置している。このため、初期
沈降槽2への廃水流が廃水流入口1正面の整流壁5の方
向ではなく、初期沈降槽2の両側壁2cの方向に分流さ
れるため、沈降物は廃水流入口1付近ではなく、さらに
奥の初期沈降槽2内部で幅W2 にわたって広範囲に沈
降、堆積する。
At this time, the sedimentation type wastewater treatment apparatus of the present embodiment is provided so that the floor 6 is inclined downward from the wastewater inlet 1 to the downstream. It becomes easy to flow to. In this case, the floor 6 is formed by expanding the width gradually from the width W 1 and the same level or more of the wastewater inlet 1 to the width W 2 of the bottom surface 2a and the same degree of initial settling tank 2, the floor 6 The three sides other than the downstream side are covered with the wall surface 2b according to the shape of, and a baffle 7 is provided on the floor surface 6 so as to insert a wedge for the flow. For this reason, the wastewater flow to the initial settling tank 2 is divided not in the direction of the straightening wall 5 in front of the wastewater inlet 1 but in the direction of the side walls 2 c of the initial settling tank 2, and the sediment is in the vicinity of the wastewater inlet 1. Instead, the sedimentation and sedimentation spread over a wide area in the inner initial sedimentation tank 2 over the width W2.

【0016】したがって、本実施形態の沈降式廃水処理
装置によれば、従来、初期沈降槽内の廃水流入口付近に
偏って沈降、堆積していたスラグを槽全体に分散させて
沈降堆積させることができる。このため、廃水流入口1
付近がすぐにスラグで埋まってしまうことはなく、廃水
流入口56付近に堆積するスラグが廃水流入の障害とな
るまでの間に従来の初期沈降槽に比べて遙かに多くのス
ラグが槽内に堆積する。その結果、本実施形態の沈降式
廃水処理装置によれば、大がかりな堆積物の除去作業を
行なう頻度を大幅に減少させることができる。
Therefore, according to the sedimentation type wastewater treatment apparatus of the present embodiment, the slag which has been settled and deposited near the wastewater inlet in the initial settling tank is dispersed and settled throughout the tank. Can be. Therefore, the wastewater inlet 1
The area is not immediately filled with slag, and much more slag is stored in the tank until the slag deposited near the wastewater inlet 56 hinders the inflow of wastewater compared to the conventional initial settling tank. Deposited on As a result, according to the sedimentation type wastewater treatment apparatus of the present embodiment, the frequency of performing a large-scale sediment removal operation can be significantly reduced.

【0017】実施例 水砕スラグ廃水を処理するために、図1と同じ構成の沈
降式廃水処理槽を以下のような仕様とし、その初期沈降
槽中のスラグの堆積状態を観察した。 (1) 初期沈降槽 幅:10メートル、長さ:5メート
ル、深さ:5メートル (2) 最終沈降槽 幅:10メートル、長さ:25メー
トル、深さ:4メートル 初期沈降槽は堆積物の収容量を増加させるために最終沈
降槽よりも約1メートル深く設けた。整流壁は初期沈降
槽と最終沈降槽との間に設置されており、壁には直径1
50ミリメートルの丸穴を全面にわたって均一に多数開
孔させている。廃水流入口から初期沈降槽の底部に至る
床面には約45度の傾斜を設け、流入口付近でスラグが
沈降しても下流へ移動し、流入口が閉塞することのない
ようにした。流入する廃水流に対するバッフルはこの斜
面上に廃水流に対して楔を入れるように設けて、流れが
二分されるようにした。その結果、廃水流入口から初期
沈降槽へ流れ込む廃水流はバッフル( 邪魔板)で二分さ
れて、初期沈降槽の側壁に沿って内部にまで至るため、
水砕スラグの堆積が初期沈降槽の入り口付近に偏って堆
積することはなく、槽底面に広く分散して堆積するよう
になった。
[0017] To process the Example granulated slag waste water, and specifications as follows sedimentation waste water treatment tank of the same configuration as FIG. 1, was observed slag condition of deposition of the initial settling vessel. (1) Initial settling tank Width: 10 meters, length: 5 meters, depth: 5 meters (2) Final settling tank Width: 10 meters, length: 25 meters, depth: 4 meters Initial settling tank is sediment Was installed about 1 meter deeper than the final settling tank in order to increase the storage capacity of the final settling tank. The rectification wall is installed between the initial settling tank and the final settling tank, and the wall has a diameter of 1 mm.
A large number of 50 mm round holes are uniformly formed over the entire surface. The floor from the wastewater inlet to the bottom of the initial settling tank was provided with an inclination of about 45 degrees so that even if the slag settled near the inlet, it moved downstream and the inlet was not blocked. A baffle for the incoming wastewater stream was provided on this slope to wedge the wastewater stream so that the stream was bisected. As a result, the wastewater flow that flows from the wastewater inlet to the initial settling tank is bisected by baffles (baffles) and reaches the inside along the side wall of the initial settling tank,
Granulated slag did not accumulate in the vicinity of the entrance of the initial settling tank, but spread widely on the bottom of the tank.

【0018】[0018]

【発明の効果】本発明の沈降式廃水処理槽によれば、沈
降物を初期沈降槽の底面全域に広く堆積させることがで
きるため、沈降物を初期沈降槽から排出する作業頻度を
減らすことができ、廃水処理費を大幅に低減させること
ができる。
According to the sedimentation type wastewater treatment tank of the present invention, the sediment can be widely deposited on the entire bottom surface of the initial sedimentation tank, so that the frequency of discharging the sediment from the initial sedimentation tank can be reduced. Wastewater treatment costs can be greatly reduced.

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

【図1】本発明による沈降式廃水処理槽の一実施形態を
示す平面概略図である。
FIG. 1 is a schematic plan view showing an embodiment of a settling type wastewater treatment tank according to the present invention.

【図2】図1のII−II線に沿う断面図である。FIG. 2 is a cross-sectional view taken along the line II-II of FIG.

【図3】本実施形態におけるバッフルをそれぞれ示し、
(a) は図2の要部拡大図、(b)は枠組みの概要を示す斜
視図、(c) はその平面図である。
FIG. 3 shows baffles in the present embodiment,
(a) is an enlarged view of a main part of FIG. 2, (b) is a perspective view showing an outline of a framework, and (c) is a plan view thereof.

【図4】従来の沈降式廃水処理槽の基本構成を示す平面
概略図である。
FIG. 4 is a schematic plan view showing a basic configuration of a conventional sedimentation type wastewater treatment tank.

【図5】図4のV−V線に沿う断面図である。FIG. 5 is a sectional view taken along line VV in FIG. 4;

【図6】沈降式廃水処理槽におけるスラグのグラブバケ
ットを備えたクレーンにより回収する設備の概要をそれ
ぞれ示し、(a) は正面図、(b) は側面図である。
FIGS. 6A and 6B respectively show an outline of facilities for collecting slag by a crane equipped with a grab bucket in a settling type wastewater treatment tank, wherein FIG. 6A is a front view and FIG. 6B is a side view.

【符号の説明】[Explanation of symbols]

1,56 廃水流入口 2,51 初期沈降槽 2a 底面 2b 壁面 2c 側壁 3,52 最終沈降槽 4,53 流通孔 5,54 整流壁 6 床板 6a 縁部 7 バッフル(邪魔板) 8 枠組み 9 支柱 10 平板 11 点検枠 12,55 排水路 57 クレーン 58 グラブバケット 59 トラック 1,56 Wastewater inlet 2,51 Initial sedimentation tank 2a Bottom surface 2b Wall surface 2c Side wall 3,52 Final sedimentation tank 4,53 Flow hole 5,54 Rectification wall 6 Floor plate 6a Edge 7 Baffle (baffle plate) 8 Frame 9 Column 10 Flat plate 11 Inspection frame 12, 55 Drainage channel 57 Crane 58 Grab bucket 59 Truck

───────────────────────────────────────────────────── フロントページの続き (72)発明者 児玉 文雄 愛媛県新居浜市西原町3−5−3 住友金 属鉱山株式会社別子事業所設備技術センタ ー内 ──────────────────────────────────────────────────の Continuing on the front page (72) Inventor Fumio Kodama 3-5-3 Nishihara-cho, Niihama-shi, Ehime Pref.

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 廃水流入口が開口する初期沈降槽と、そ
の下流に配置される沈降槽と、初期沈降槽とその下流に
配置される沈降槽との間に配置されていて、初期沈降槽
の流れを整流して下流に配置される沈降槽に送り込むた
めの複数の流通孔を有する整流壁とを備えた沈降式廃水
処理槽において、 廃水流入口から下流に向けて、廃水流入口と同程度以上
の幅から初期沈降槽の底面と同程度の幅にまで徐々に幅
を広げた形状をなし、かつ、下向きに傾斜する床面を設
けると共に、その床面形状に沿って下流側以外の三方が
壁面で覆われるようにし、さらに、その床面上に、廃水
流に対し楔を入れて流れを二分するようにバッフル(邪
魔板)を設けたことを特徴とする沈降式廃水処理槽。
An initial sedimentation tank which is disposed between an initial sedimentation tank having an open wastewater inlet, a sedimentation tank disposed downstream thereof, and an initial sedimentation tank and a sedimentation tank disposed downstream thereof. A rectifying wall having a plurality of flow holes for rectifying the flow of the wastewater and sending the rectified flow to a sedimentation tank disposed downstream, in the same manner as the wastewater inlet from the wastewater inlet to the downstream. It has a shape that is gradually widened from a width not less than about to the same width as the bottom of the initial settling tank, and a floor surface that slopes downward is provided, and along the floor shape other than the downstream side A sedimentation type wastewater treatment tank characterized in that three sides are covered with a wall surface, and a baffle (baffle plate) is provided on the floor surface so as to divide the wastewater flow into two by inserting a wedge.
【請求項2】 バッフル(邪魔板)が枠組と、それを支
える支柱と、枠組の外側に取り付けられた平板とからな
り、これらを構成する材料が金属、プラスチック、また
はそれらの複合材料からなることを特徴とする請求項に
記載の沈降式廃水処理槽。
2. The baffle (baffle) comprises a framework, a support for supporting the same, and a flat plate attached to the outside of the framework, and the material constituting these is metal, plastic, or a composite material thereof. The sedimentation type wastewater treatment tank according to claim 11, characterized in that:
JP7756798A 1998-03-25 1998-03-25 Precipitating type waste water treating tank Pending JPH11267409A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP7756798A JPH11267409A (en) 1998-03-25 1998-03-25 Precipitating type waste water treating tank

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP7756798A JPH11267409A (en) 1998-03-25 1998-03-25 Precipitating type waste water treating tank

Publications (1)

Publication Number Publication Date
JPH11267409A true JPH11267409A (en) 1999-10-05

Family

ID=13637603

Family Applications (1)

Application Number Title Priority Date Filing Date
JP7756798A Pending JPH11267409A (en) 1998-03-25 1998-03-25 Precipitating type waste water treating tank

Country Status (1)

Country Link
JP (1) JPH11267409A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2016131922A (en) * 2015-01-19 2016-07-25 日本ソリッド株式会社 Aggregation cross flow precipitator of waste water containing heavy metal
CN110721501A (en) * 2019-10-30 2020-01-24 山东华通环境科技股份有限公司 Clear water flow collecting device of lateral flow inclined plate sedimentation tank

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2016131922A (en) * 2015-01-19 2016-07-25 日本ソリッド株式会社 Aggregation cross flow precipitator of waste water containing heavy metal
CN110721501A (en) * 2019-10-30 2020-01-24 山东华通环境科技股份有限公司 Clear water flow collecting device of lateral flow inclined plate sedimentation tank

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