JP2005007371A - Muddy water treatment apparatus - Google Patents

Muddy water treatment apparatus Download PDF

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Publication number
JP2005007371A
JP2005007371A JP2003177566A JP2003177566A JP2005007371A JP 2005007371 A JP2005007371 A JP 2005007371A JP 2003177566 A JP2003177566 A JP 2003177566A JP 2003177566 A JP2003177566 A JP 2003177566A JP 2005007371 A JP2005007371 A JP 2005007371A
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Japan
Prior art keywords
tank
water
agitation
stirring
muddy water
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JP2003177566A
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JP4173409B2 (en
Inventor
Katsuyoshi Harada
勝吉 原田
Shuichi Hieda
修一 稗田
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HARADA SOGO DOBOKU KK
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HARADA SOGO DOBOKU KK
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a muddy water treatment apparatus extending retention time of continuously supplied muddy water in an agitation tank without increasing the size of the tank, thereby obtaining a high agitation mixing efficiency. <P>SOLUTION: This muddy water treatment apparatus is provided with the agitation tank 10 in which an agitation shaft 15 is rotatably provided in an axial direction in a horizontally disposed water tank 11, a coagulant is supplied to the muddy water continuously supplied from one side of the water tank 11, and the muddy water and the coagulant are agitated and mixed by the agitation shaft 15 and discharged from the other side of the water tank 11 ; and a settling tank 30 of cascade structure composed of multiple settling chambers under the agitation tank 10. The muddy water continuously discharged from the agitation tank 10 falling down through a duct 20 is supplied to a settling chamber 31 at one end, and supernatant is discharged to the outside from a settling chamber 35 at the other end. The agitation shaft 15 has reverse flow agitation blades 19 generating a reverse flow against the flow of the muddy water supplied continuously, delaying the muddy water flow from one side of the shaft 15 toward the other side, thereby extending agitation time of the muddy water and the coagulant in the agitation tank 10. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

【0001】
【発明の属する技術分野】
本発明は、建設排水などの濁水中から浮遊物質を取り除くための濁水処理機に関する。
【0002】
【従来の技術】
従来、工事現場において発生する汚濁水や、破砕場において発生する洗い水を河川へ放流するための浄化方法として、凝集剤により土粒子を沈殿させ、分離した上澄み液を放流する方法がある。
【0003】
この凝集剤の混合・攪拌及び沈澱処理の従来の工法としては、攪拌槽に攪拌機をセットし、攪拌した汚濁水をこの攪拌槽からオーバーフローさせて沈殿槽へ送り込み、沈殿槽にて分離させている。
【0004】
例えば、特許文献1には、汚濁水が送り込まれ凝集剤が投入される第一攪拌槽と、上端部が解放された隔壁によって該第一攪拌槽と区分けされ、該第一攪拌槽からオーバーフローした汚濁水が送り込まれる第二攪拌槽とを有し、該第一及び第二攪拌槽にそれぞれ攪拌翼が設けられている構成について開示されている。
【0005】
【特許文献1】
特開2001−347103号公報
【0006】
【発明が解決しようとする課題】
しかしながら、従来の方法では、攪拌効率が低く、処理能力を増大するためには攪拌槽を非常に大型にする必要がある。
【0007】
また、特許文献1に開示されている構成では、攪拌槽を複数個設けるとともに、攪拌翼及び該攪拌翼を駆動させるモータをそれぞれ複数個設けなければならない。そのため、装置が大型化し部品点数も多くなる。また、攪拌槽中の汚濁水の流れは一つの攪拌翼によって形成されることから、その流れ方向が比較的単純であり十分な攪拌が行われにくく、また、攪拌翼によって形成される流れ方向が一方方向となり、汚濁水を攪拌槽により長く滞留させることが難しい。
【0008】
本発明は、上記した従来の問題点を解決するためになされたもので、攪拌部を大型化することなく、攪拌部における濁水の滞留時間を長く取り、攪拌混合効率を高めることができる濁水処理機を提供することを目的とする。
【0009】
【課題を解決するための手段】
第1の発明は、請求項1に記載のように、筒形状に形成された水槽内に軸方向に沿って攪拌軸を回転可能に設け、前記水槽の一方から連続的に供給される濁水に対して凝集剤を供給し、前記攪拌軸により濁水と前記凝集剤とを攪拌混合して連続的に前記水槽の他方から排出する攪拌槽と、前記攪拌槽の下部に配置され、複数の沈殿室が区分けされ、一端の沈殿室に前記攪拌槽から連続的に排出された濁水が供給され、他端の沈殿室から上澄み液を槽外に排出する沈殿槽と、を有し、前記攪拌軸は、連続的に供給される濁水の流れに対して逆方向の流れを生じさせる逆流攪拌翼を有し、前記攪拌軸の一方から他方へ向けて流れる濁水の流れを遅くし、前記攪拌槽内での濁水と凝集剤との攪拌時間を長くすることを特徴とする濁水処理機にある。
【0010】
第2の発明は、請求項2に記載のように、上記した第1の発明で、前記攪拌軸には、前記濁水供給部に対応して濁水の流速を規制するスクリュー部が設けられ、且つ前記スクリュー部の下流側に前記逆流攪拌翼が設けられていて、前記スクリュー部のすぐ下流側の部分に対応して前記凝集剤が投入されることを特徴とするものである。
【0011】
【発明の実施の形態】
以下、本発明に係る実施の形態について図1から図4を参照して説明する。なお、本実施の形態における例示が本発明を限定することはない。
【0012】
図1は、本実施の形態に係る濁水処理機の一形態の断面図である。図2は該装置の上面図、図3は該装置の左側面図、及び図4は該装置の右側面図である。
【0013】
図1において、濁水処理機1は、供給される濁水と凝集剤とを混合する攪拌槽10と、攪拌槽10内の凝集剤との攪拌済みの濁水が排出される攪拌処理水落しダクト20と、攪拌槽10の下側に配置され攪拌処理水落しダクト20から送り込まれる濁水を一定量保持して濁水中の浮遊物質を沈殿させる沈殿槽30とを有する。
【0014】
なお、濁水処理機1における濁水の流れは、攪拌槽10において図中左側から右側をA方向、攪拌処理水落しダクト20において図中上から下向きをB方向、沈殿槽30において図中右側から左側方向をC方向とする。
(攪拌槽)
攪拌槽10は、円筒形状に形成されたある程度の長さを有する水槽部11を略水平状態に配置し、この円筒形状の水槽部11内に攪拌軸15を水平方向に回転可能に取り付けている。また、水槽部11の一端側の上部には濁水供給管12aが接続さている濁水供給部12が設けられており、水槽部11の他端には水槽部11の上方位置に排出口としての攪拌処理水出口部13が設けられている。そして、この攪拌処理水出口部13に攪拌処理水落しダクト20が装着され、該攪拌処理水出口部13からオーバーフローした攪拌済みの濁水が下方に向けて落下する。
【0015】
水槽部11には、濁水供給部12に近接して攪拌処理水落しダクト20側に凝集剤投入口14が形成され、不図示の凝集剤定量投入装置から所定量の液体又は粉体の凝集剤が水槽部11内に連続的に投入されるようになっている。
【0016】
攪拌槽10では、濁水供給部12から水槽部11に連続して濁水が落下供給され、反対側の攪拌処理水出口部13から凝集剤との攪拌処理済の濁水が排出されるため、濁水の流れは全体として図中A方向になる。
【0017】
また、攪拌処理水出口部13は水槽部11の下流側側面の上部に形成されているため、水槽部11内の濁水はこの攪拌処理水出口部13の位置まで液面が維持される。
【0018】
水槽部11内に水平方向に沿って配置されている攪拌軸15は、回転軸を水槽部11の軸心位置に有しており、沈殿槽30の上部に取り付けた減速機能付モータ16とタイミングベルト等を介して連結されて回転駆動される。
【0019】
この攪拌軸15には、回転軸部15aに濁水供給部12に対応して送りスクリュー部17が設けられている。送りスクリュー部17は、濁水供給部12から供給される濁水を掻き混ぜて、濁水中の浮遊物質が均質とする一方、送りスクリュー部17のピッチ角として、濁水を若干下流に送り込む程度、又はほとんど0°に近い構成とし、供給されたばかりの濁水が急激に下流側へ移動しないようにせき止める機能も有している。このため、供給されたばかりの濁水は送りスクリュー部17によって徐々に下流側に移動する。
【0020】
送りスクリュー部17のすぐ下流側の部分の軸部15aには何も設けていないが、この部分の上方に凝集剤投入口14が配置され、ここから適量の凝集剤が投入される。このとき、凝集剤投入口14の下側の濁水は、送りスクリュー部17からゆっくりとした流速で濁水が移動しているため、凝集剤と濁水とは効率良く混合される。なお、本実施の形態では、凝集剤と濁水との拡散及び混合が効率良く行われるため、凝集剤は液体及び固体の種類に関係なくいずれであっても使用することができる。
【0021】
また、凝集剤投入口14に設けた前記凝集剤定量投入装置によって凝集剤を濁水の流量に合わせて投入するように、液体の凝集剤用にはバルブ、固体の凝集剤用にはロードセル付のホッパーなどが設けられている。そして、濁水の供給量に応じて凝集剤の投入量が調整される。
【0022】
攪拌軸15の軸部15aには、凝集剤投入口14の下側に対応する位置より下流側に、適当な間隔を有して複数個のパドル(第一の攪拌翼)18が設けられている。これらのパドル18は、それぞれ、軸部15aの軸方向に対してピッチ角を0°(軸方向と平行)として羽部が設けられている。本実施の形態では、パドル18は等間隔で3個設けている。攪拌軸15の軸部15aは水槽部11の中心軸と同一軸心上であるため、羽部の先端を水槽部11の内壁に近接する位置まで延ばすと、水槽部11内の濁水を円周方向全域に渡って効率良く掻き混ぜることができる。なお、前記羽部は、濁水を若干下流側に送るように、軸部15aの軸方向に対して下流側へ送る方向のピッチとすることもできる。
【0023】
また、攪拌軸15の軸部15aには、凝集剤投入口14に対応する位置より下流側に、適当間隔を有して複数個の攪拌翼(第二の攪拌翼)19を設けており、本実施の形態において、攪拌翼19はパドル18と交互になるように2個設けている。
【0024】
本実施の形態において、これらの攪拌翼19は、夫々軸部15aの軸方向上流側(送りスクリュー部17)に向かって濁水を移動させる方向のピッチ角を有している。この攪拌翼19の翼の直径は短く形成され、小さな水流を生じさせる程度としている。
【0025】
このため、送りスクリュー部17から下流に向かう濁水は、全体として攪拌処理水排出部13に向かって図中A方向に流れるが、これらの攪拌翼19によって下流側に向かう濁水の流速がより低速となるように制御して凝集剤と濁水との反応時間を長くして凝集剤との混合効率を高めると共に、逆向きの流れで対流を生じさせ、凝集剤と濁水との攪拌をより一層活発化させている。
【0026】
すなわち攪拌翼19の作用により、一端下流側に流された濁水が再び上流側に戻されることになるため、攪拌槽10での濁水の滞留時間が長くなる。また、濁水の流れが種々の方向性を持つため濁水中の浮遊物質及び凝集剤が均質な分布となる。これより、攪拌槽10において、濁水と凝集剤とを効率良く混合することができる。
【0027】
また、パドル18と攪拌翼19は軸方向に沿って交互に配置されているため、水槽部11中に種々の濁水の流れがより効率良く発生する。
【0028】
また、これらのパドル18及び攪拌翼19は、同じ軸部15aに設けられているため、このような攪拌は一つの駆動力で行うことができ、装置が小型化し部品点数が少なくなる。
【0029】
また、水槽部11に濁水が供給されない間では、濁水は図中A方向に流れないため、濁水の流れが一方向になり攪拌が十分に行われない可能性がある。しかし、本実施の形態では、攪拌翼19によって濁水が上流側に逆流する方向に流されるため、待機中も濁水は効率良く攪拌される。
【0030】
このように、濁水はパドル18及び攪拌翼19によって水槽部11の一端側から他端側へと移動する間に十分に凝集剤との混合が行われ、他端側の上位部に位置する攪拌処理水出口部13から連続的に排出され、攪拌処理水落しダクト20を介して下部の沈殿槽30へと供給される。
(攪拌処理水落しダクト)
攪拌処理水落しダクト20の下端部は、沈殿槽30の他端部において、沈殿槽30内まで挿入されている。
【0031】
攪拌処理水落しダクト20はダクト本体21の内部に複数のカスケード部材21が上下方向において先端部が重なり合うようにして互い違いに配設され、攪拌槽10から排出された凝集剤との混合処理済みの濁水が急激に落下しないようになっているの。このため、ダクト20から沈殿槽30に濁水が威勢良く落下したときに沈殿槽30内が掻き回され、底に溜まった浮遊物質が拡散しないようにし、また沈殿槽30中の沈殿物が再び浮遊しないようにしている。このような構成によれば、沈殿槽30における沈殿時間を短縮することができる。
(沈殿槽)
沈殿槽30は、複数の隔壁によって第1の沈殿室31、第2の沈殿室32、第3の沈殿室33、第4の沈殿室34、第5の沈殿室35を図中C方向に向かって区分けされたている。
【0032】
攪拌処理水落しダクト20から沈殿槽30に供給される濁水は、第1の沈殿室31から第5の沈殿室35まで緩やかに流されながら、第5の沈殿室35の側面上位部に設けられた上澄み液排出部36から排出される。
【0033】
第1の沈殿室31は、沈殿槽30の底面部から水位の略中間部まで立設された隔壁31aによって区分けされる。隔壁31aは上部が第1の沈殿室31の内方向に傾斜し、これより、第1の沈殿室31から第2の沈殿室32へ浮遊物質や沈殿物が流れ込むのを防いでいる。また、攪拌処理水落しダクト20と第一の沈殿室31との間には隔壁31bが設けられ、攪拌処理水落しダクト20の下部で濁流の落下で生じる濁水の対流により沈殿室31の上方に沈殿物等が舞い上がらないようにして沈殿効果を高めている。
【0034】
第1の沈殿室31に続く第2の沈殿室32は、沈殿槽30の底面から沈殿槽30の高さの略中間まで立設された隔壁32aによって区分けされる。隔壁32aは第2の沈殿室32の内方向に若干傾斜して設けられており、上端部が第二の沈殿室32内方向に略逆U字状に湾曲している。また、第2の沈殿室32には、沈殿槽30の天板部から下方に向け、且つ下流側に傾斜し、先端部が上流側に略U字状に湾曲した隔壁32bが設けられており、隔壁32a及び32bのそれぞれ上流側の壁面には板状に形成された突起板32a´及び32b´が設けられている。そして、突起板32a´によって、沈殿物の舞い上がりを抑え、また突起板32b´によって第1の沈殿室31から流れ込む上澄み液によって第2の沈殿室32内に対流が発生するのを抑え、底部に沈殿している沈殿物の舞い上がりを防ぐようにしている。
【0035】
第2の沈殿室32に続く第3の沈殿室33は、沈殿槽30の底面部から天板部まで略垂直に立設した隔壁33aが設けられている。この隔壁33aの上位部には、隣の第4の沈殿室34とこの第3の沈殿室33との間に跨って略逆U字形状の落し込み管37が設けられており、第3の沈殿室33側に開口する下向きの入口部37bは第3の沈殿室33の液位よりも低い位置に設けている。このため、第3の沈殿室33の液面に浮いた木片等を吸い込まず、第3の沈殿室33内の上澄み液のみを第4の沈殿室に流し込むことができるようになっている。
【0036】
なお、落しこみ管37の入り口部37bの下方に遮蔽板37が設けられ、第3の沈殿室33の底部側の水等を直接吸い込まないようにしている。このように、第三の沈殿室33では、沈澱処理がかなり進み、上澄み液も相当浄化されているため、第4の沈殿室34へは極力汚染されていない処理された上澄み液を送り込むようにしており、第4の沈殿室34側における落し込み管37は遮蔽板37に沿って底部近くまで下方に延びており、落し込み管37の出口37cから排出される第3の沈殿室33からの上澄み液によって第4の沈殿室34内に対流が発生するのを極力防ぎ、清澄された上面の上澄み液に影響を与えないようにしている。
【0037】
最終の沈殿室である第5の沈殿室の一つ手前の第4の沈殿室34は、沈殿槽30の底面部から所定の高さまで上流側に傾斜した隔壁34aによって区分けされており、上澄み液は殆ど浮遊物が混ざっておらず、きれいな上澄み液が隔壁34aの上端部から第5の沈殿室35に送り込まれることになる。
【0038】
第5の沈殿室35の下流側側壁面の上部には、上澄み液排出開口部36が形成されており、この上澄み液排出開口部36は隔壁34aよりも低い位置とし、第5の沈殿室35から第4の沈殿室34に処理水が逆流しないようになっている。そして、第5の沈殿室35内の処理水の上澄液が上澄み液排出開口部36から不図示の排水管を通して河川等に連続的に排出される。このように排出される上澄み液の中には殆ど浮遊物質や沈殿物が含まれず、安全に排水することができる。
【0039】
一方、最初の沈殿室である第1の沈殿室31では、攪拌処理水落しダクト20から送り込まれる濁水中に含まれる浮遊物質のうち大部分が沈殿され、次の第2の沈殿室32で残りの浮遊物質の殆どが沈殿されたことが知見された。これは、攪拌槽10において濁水と凝集剤とが十分に混合されているためより効率良く沈殿が行われたものと思われる。
【0040】
そこで、本実施の形態では、第1の沈殿室31の底部に沈殿した沈殿物40aを除去するために、第1の沈殿室31の底部にスクリューコンベア38を設けている。このスクリューコンベア38は、ケーシング内にスクリュー軸を設けたもので、第1の沈殿室31内において該ケーシングの一部が開口し、この開口を通して該ケーシング内に沈殿物が取り込まれ、該スクリュー軸の回転により沈殿物が軸方向の一方に移送される。沈殿物の移送側の端部には、沈殿物排出管が取り付けられ、この沈殿物排出管を通して沈殿物が沈殿物処理槽等に送られる。なお、スクリュー38のスクリュー軸はスクリュー用モータ38aにより回転駆動される。
【0041】
次に、第2の沈殿室32で生じる沈殿物40bは、少量であり、かつ小さい粒子のものがほとんどであるため、第2の沈殿室の底部にドレイン管(不図示)を取り付け、不図示のドレインコックを開放して定期的に抜き取り、上記した沈殿物処理槽等に送れば良い。
【0042】
なお、本実施の形態の濁水処理機1は、砂利・破石プラントから発生する濁水、ダム・トンネルなどの建設工事から排出される濁水、土木・建設工事から発生する濁水、染色・食品・薬品・養魚場などから排出される濁水などを処理するのに適用することができる。
【0043】
【発明の効果】
以上説明したように、本発明によれば、攪拌槽を大型化することなく、攪拌槽内に連続供給される濁水の滞留時間を長くとり、攪拌混合効率を高めることができ、連続的に処理水を排出することができる。
【図面の簡単な説明】
【図1】本発明の実施の形態に係る濁水処理機の断面図である。
【図2】図1の濁水処理機の上面図である。
【図3】図1の濁水処理機の左側面図である。
【図4】図1の濁水処理機の右側面図である。
【符号の説明】
1…濁水処理機
10…攪拌槽
11…水槽部
12…濁水供給部
13…攪拌処理水出口部
14…凝集剤投入口
15…攪拌軸
16…減速機能付モータ
17…送りスクリュー部
18…パドル
19…攪拌翼
20…攪拌処理水落しダクト
21…カスケード部材
30…沈殿槽
31…第1の沈殿室
31a、b…隔壁
32…第2の沈殿室
32a、b…隔壁
32a´、b´…突起板
33…第3の沈殿室
33a、b…隔壁
34…第4の沈殿室
34a…隔壁
35…第5の沈殿室
36…上澄み液排出部
37…落し込み管
37a…遮蔽板
38…スクリュー
38a…スクリュー用モータ
40a、b…沈殿物
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a muddy water treatment machine for removing suspended substances from muddy water such as construction wastewater.
[0002]
[Prior art]
Conventionally, as a purification method for discharging polluted water generated at a construction site and washing water generated at a crushing site to a river, there is a method of precipitating soil particles with a flocculant and discharging separated supernatant.
[0003]
As a conventional method for mixing / stirring and precipitating the flocculant, a stirrer is set in a stirring tank, and the stirred turbid water is overflowed from the stirring tank and sent to the precipitation tank, where it is separated in the precipitation tank. .
[0004]
For example, in Patent Document 1, the first agitation tank into which the polluted water is fed and the flocculant is charged is separated from the first agitation tank by a partition wall whose upper end is released, and overflows from the first agitation tank. It has disclosed about the structure which has a 2nd stirring tank into which polluted water is sent, and is provided with the stirring blade in each of this 1st and 2nd stirring tank.
[0005]
[Patent Document 1]
Japanese Patent Laid-Open No. 2001-347103
[Problems to be solved by the invention]
However, in the conventional method, the stirring efficiency is low, and it is necessary to make the stirring tank very large in order to increase the processing capacity.
[0007]
In the configuration disclosed in Patent Document 1, a plurality of stirring tanks and a plurality of stirring blades and motors for driving the stirring blades must be provided. This increases the size of the apparatus and the number of parts. In addition, since the flow of the polluted water in the stirring tank is formed by one stirring blade, the flow direction is relatively simple and it is difficult to perform sufficient stirring, and the flow direction formed by the stirring blade is It becomes one direction and it is difficult to retain polluted water for a long time in the stirring tank.
[0008]
The present invention was made in order to solve the above-described conventional problems, and without increasing the size of the stirring section, the turbid water treatment in which the turbid water stays longer in the stirring section and the stirring and mixing efficiency can be increased. The purpose is to provide a machine.
[0009]
[Means for Solving the Problems]
According to a first aspect of the present invention, as described in claim 1, a stirring shaft is rotatably provided along an axial direction in a water tank formed in a cylindrical shape, and turbid water continuously supplied from one of the water tanks is provided. A stirring tank for supplying a flocculant, stirring and mixing the turbid water and the flocculant with the stirring shaft, and continuously discharging the other from the other of the water tanks; A turbid water continuously discharged from the agitation tank to the settling chamber at one end, and a settling tank for discharging the supernatant from the settling chamber at the other end to the outside of the tank. , Having a reverse stirring blade for generating a flow in the opposite direction to the flow of turbid water supplied continuously, slowing the flow of turbid water flowing from one side of the stirring shaft to the other, and in the stirring tank The turbid water treatment machine is characterized in that the stirring time of the turbid water and the flocculant is lengthened.
[0010]
According to a second aspect of the present invention, as described in the second aspect, in the first aspect described above, the stirring shaft is provided with a screw portion that regulates a flow rate of turbid water corresponding to the turbid water supply portion, and The counterflow agitating blade is provided on the downstream side of the screw part, and the flocculant is introduced corresponding to the part immediately downstream of the screw part.
[0011]
DETAILED DESCRIPTION OF THE INVENTION
Embodiments according to the present invention will be described below with reference to FIGS. In addition, the illustration in this Embodiment does not limit this invention.
[0012]
FIG. 1 is a cross-sectional view of an embodiment of a muddy water treatment machine according to the present embodiment. 2 is a top view of the apparatus, FIG. 3 is a left side view of the apparatus, and FIG. 4 is a right side view of the apparatus.
[0013]
In FIG. 1, the turbid water treatment machine 1 includes a stirring tank 10 that mixes the supplied turbid water and a flocculant, and a stirring treatment water dropping duct 20 that discharges the agitated turbid water from the flocculant in the stirring tank 10. And a sedimentation tank 30 that is disposed below the agitation tank 10 and retains a certain amount of turbid water that is fed from the agitation treatment duct 20 and precipitates suspended substances in the turbid water.
[0014]
The flow of muddy water in the muddy water treatment machine 1 is the direction A from the left side in the drawing in the stirring tank 10, the direction B from the top to the bottom in the drawing in the stirring treatment water dropping duct 20, and the left side from the right side in the drawing in the precipitation tank 30. Let the direction be the C direction.
(Stirring tank)
The agitation tank 10 has a water tank part 11 formed in a cylindrical shape and having a certain length in a substantially horizontal state, and a stirring shaft 15 is mounted in the cylindrical water tank part 11 so as to be rotatable in the horizontal direction. . Further, a muddy water supply unit 12 to which a muddy water supply pipe 12 a is connected is provided at the upper part on one end side of the water tank unit 11, and the other end of the water tank unit 11 is agitated as a discharge port above the water tank unit 11. A treated water outlet portion 13 is provided. Then, the agitation treated water dropping duct 20 is attached to the agitation treated water outlet part 13, and the agitated muddy water overflowing from the agitation treated water outlet part 13 falls downward.
[0015]
In the water tank unit 11, the agitation treatment water is dropped near the muddy water supply unit 12, and a flocculant inlet 14 is formed on the duct 20 side. Is continuously fed into the water tank 11.
[0016]
In the agitation tank 10, turbid water is continuously dropped from the turbid water supply part 12 to the water tank part 11, and the turbid water that has been agitated with the flocculant is discharged from the agitation water outlet part 13 on the opposite side. The flow is generally in the direction A in the figure.
[0017]
Further, since the agitation water outlet 13 is formed at the upper part of the downstream side surface of the water tank 11, the liquid level of the turbid water in the water tank 11 is maintained up to the position of the agitation water outlet 13.
[0018]
The stirring shaft 15 disposed in the water tank unit 11 along the horizontal direction has a rotation axis at the axial center position of the water tank unit 11, and a timing with the motor 16 with a deceleration function attached to the upper part of the settling tank 30. It is connected via a belt or the like and is driven to rotate.
[0019]
The stirring shaft 15 is provided with a feed screw portion 17 corresponding to the muddy water supply portion 12 on the rotating shaft portion 15a. The feed screw unit 17 stirs the turbid water supplied from the turbid water supply unit 12 to make the suspended substances in the turbid water homogeneous, while the pitch angle of the feed screw unit 17 feeds the turbid water slightly downstream or almost. It has a structure close to 0 °, and has a function of clogging the turbid water just supplied so that it does not move rapidly downstream. For this reason, the muddy water just supplied is gradually moved downstream by the feed screw portion 17.
[0020]
Nothing is provided in the shaft portion 15a in the portion immediately downstream of the feed screw portion 17, but the flocculant inlet 14 is disposed above this portion, and an appropriate amount of the flocculant is charged therefrom. At this time, the turbid water below the flocculant inlet 14 is moving from the feed screw portion 17 at a slow flow rate, so that the flocculant and the turbid water are efficiently mixed. In the present embodiment, since the flocculant and turbid water are efficiently diffused and mixed, the flocculant can be used regardless of the type of liquid or solid.
[0021]
In addition, a flocculant is provided for the liquid flocculant and a load cell is attached for the solid flocculant so that the flocculant is introduced in accordance with the flow rate of the turbid water by the flocculant quantitative introduction device provided at the flocculant inlet 14. A hopper is provided. The amount of flocculant charged is adjusted according to the amount of turbid water supplied.
[0022]
A plurality of paddles (first stirring blades) 18 are provided on the shaft portion 15 a of the stirring shaft 15 at an appropriate interval downstream from a position corresponding to the lower side of the flocculant inlet 14. Yes. Each of these paddles 18 is provided with a wing portion with a pitch angle of 0 ° (parallel to the axial direction) with respect to the axial direction of the shaft portion 15a. In the present embodiment, three paddles 18 are provided at equal intervals. Since the shaft portion 15 a of the stirring shaft 15 is on the same axis as the central axis of the water tank portion 11, when the tip of the wing portion is extended to a position close to the inner wall of the water tank portion 11, the turbid water in the water tank portion 11 is circled. It can be stirred efficiently over the entire direction. In addition, the said wing | blade part can also be set as the pitch of the direction sent to a downstream with respect to the axial direction of the axial part 15a so that muddy water may be sent a little downstream.
[0023]
Further, the shaft portion 15a of the stirring shaft 15 is provided with a plurality of stirring blades (second stirring blades) 19 with an appropriate interval downstream from the position corresponding to the flocculant inlet 14; In the present embodiment, two stirring blades 19 are provided so as to alternate with the paddle 18.
[0024]
In the present embodiment, these stirring blades 19 each have a pitch angle in a direction in which muddy water is moved toward the axial upstream side (feed screw portion 17) of the shaft portion 15a. The diameter of the agitating blade 19 is made short so that a small water flow is generated.
[0025]
Therefore, the turbid water flowing downstream from the feed screw portion 17 flows in the direction A in the figure toward the agitation water discharge portion 13 as a whole, but the flow rate of turbid water toward the downstream side by these agitating blades 19 is lower. The reaction time between the flocculant and turbid water is increased by controlling so that the mixing efficiency of the flocculant is increased, and convection is generated in the reverse flow to further agitate the flocculant and turbid water. I am letting.
[0026]
In other words, the action of the stirring blade 19 causes the turbid water that has flowed downstream at one end to be returned to the upstream side again, so that the residence time of the turbid water in the stirring tank 10 becomes longer. Moreover, since the flow of muddy water has various directions, the suspended matter and the flocculant in muddy water have a homogeneous distribution. Thus, the turbid water and the flocculant can be efficiently mixed in the stirring tank 10.
[0027]
Further, since the paddles 18 and the stirring blades 19 are alternately arranged along the axial direction, various muddy water flows are generated more efficiently in the water tank section 11.
[0028]
Further, since the paddle 18 and the agitating blade 19 are provided on the same shaft portion 15a, such agitation can be performed with one driving force, and the apparatus is downsized and the number of parts is reduced.
[0029]
Moreover, since the muddy water does not flow in the direction A in the figure while the muddy water is not supplied to the water tank unit 11, the muddy water flows in one direction and the agitation may not be sufficiently performed. However, in this embodiment, since the turbid water is caused to flow backward in the upstream direction by the stirring blade 19, the turbid water is efficiently stirred even during standby.
[0030]
In this way, the muddy water is sufficiently mixed with the flocculant while moving from one end side to the other end side of the water tank unit 11 by the paddle 18 and the stirring blade 19, and the stirring located at the upper portion on the other end side. The water is continuously discharged from the treated water outlet 13 and supplied to the lower sedimentation tank 30 through the stirring treated water dropping duct 20.
(Agitated water drain duct)
The lower end of the agitation treatment water dropping duct 20 is inserted into the settling tank 30 at the other end of the settling tank 30.
[0031]
The agitation treatment water dropping ducts 20 are alternately arranged in the duct main body 21 such that a plurality of cascade members 21 are overlapped at the top and bottom in the vertical direction and mixed with the flocculant discharged from the agitation tank 10. The muddy water doesn't fall suddenly. For this reason, when turbid water drops from the duct 20 to the settling tank 30 violently, the inside of the settling tank 30 is agitated to prevent the floating substance accumulated at the bottom from diffusing, and the sediment in the settling tank 30 is floated again. I try not to. According to such a configuration, the sedimentation time in the sedimentation tank 30 can be shortened.
(Settling tank)
The settling tank 30 has a first settling chamber 31, a second settling chamber 32, a third settling chamber 33, a fourth settling chamber 34, and a fifth settling chamber 35 in a direction C in the figure by a plurality of partition walls. Have been separated.
[0032]
The turbid water supplied to the settling tank 30 from the stirring treatment water dropping duct 20 is provided at the upper part of the side surface of the fifth settling chamber 35 while being gently flown from the first settling chamber 31 to the fifth settling chamber 35. Then, it is discharged from the supernatant liquid discharge portion 36.
[0033]
The first sedimentation chamber 31 is divided by a partition wall 31a erected from the bottom surface of the sedimentation tank 30 to a substantially middle portion of the water level. The upper part of the partition wall 31a is inclined inward of the first sedimentation chamber 31, thereby preventing floating substances and sediments from flowing from the first sedimentation chamber 31 into the second sedimentation chamber 32. In addition, a partition wall 31b is provided between the stirring treatment water dropping duct 20 and the first sedimentation chamber 31, and above the sedimentation chamber 31 due to turbulent water convection generated by dropping of turbid flow at the lower part of the stirring treatment water dropping duct 20. The sedimentation effect is enhanced by preventing sediments from flying up.
[0034]
The second sedimentation chamber 32 that follows the first sedimentation chamber 31 is divided by a partition wall 32 a that stands from the bottom surface of the sedimentation tank 30 to approximately the middle of the height of the sedimentation tank 30. The partition wall 32 a is provided with a slight inclination inward of the second sedimentation chamber 32, and its upper end is curved in a substantially inverted U shape inward of the second sedimentation chamber 32. Further, the second sedimentation chamber 32 is provided with a partition wall 32b which is inclined downward from the top plate portion of the sedimentation tank 30 and is inclined downstream, and a tip portion thereof is curved in a substantially U shape upstream. Projection plates 32a 'and 32b' formed in a plate shape are provided on the upstream wall surfaces of the partition walls 32a and 32b, respectively. Then, the protruding plate 32a ′ suppresses the rising of the precipitate, and the protruding plate 32b ′ suppresses the occurrence of convection in the second sedimentation chamber 32 by the supernatant liquid flowing from the first sedimentation chamber 31. The soaking of the sediment that has been precipitated is prevented.
[0035]
The third sedimentation chamber 33 following the second sedimentation chamber 32 is provided with a partition wall 33a erected substantially vertically from the bottom surface of the sedimentation tank 30 to the top plate. A substantially inverted U-shaped drop pipe 37 is provided between the adjacent fourth precipitation chamber 34 and the third precipitation chamber 33 at the upper portion of the partition wall 33a. A downward inlet portion 37 b that opens to the precipitation chamber 33 side is provided at a position lower than the liquid level of the third precipitation chamber 33. For this reason, only the supernatant liquid in the 3rd sedimentation chamber 33 can be poured into the 4th sedimentation chamber, without sucking the wooden piece etc. which floated on the liquid level of the 3rd sedimentation chamber 33.
[0036]
A shielding plate 37 is provided below the inlet 37b of the drop tube 37 so that water or the like on the bottom side of the third sedimentation chamber 33 is not directly sucked. Thus, in the third sedimentation chamber 33, the sedimentation process has progressed considerably, and the supernatant liquid has been considerably purified, so that the treated supernatant liquid, which is not contaminated as much as possible, is fed into the fourth sedimentation chamber 34. The drop tube 37 on the fourth settling chamber 34 side extends downward to the bottom along the shielding plate 37, and is discharged from the third settling chamber 33 discharged from the outlet 37 c of the drop tube 37. Convection is prevented from occurring in the fourth sedimentation chamber 34 by the supernatant liquid as much as possible, so that the supernatant liquid on the clarified upper surface is not affected.
[0037]
The fourth sedimentation chamber 34 immediately before the fifth sedimentation chamber, which is the final sedimentation chamber, is divided by a partition wall 34a inclined upstream from the bottom surface of the sedimentation tank 30 to a predetermined height. There is almost no suspended matter mixed, and a clean supernatant liquid is fed into the fifth sedimentation chamber 35 from the upper end of the partition wall 34a.
[0038]
A supernatant liquid discharge opening 36 is formed in the upper part of the downstream side wall surface of the fifth sedimentation chamber 35, and the supernatant liquid discharge opening 36 is positioned lower than the partition wall 34a. Thus, the treated water does not flow back to the fourth sedimentation chamber 34. And the supernatant liquid of the treated water in the 5th sedimentation chamber 35 is continuously discharged | emitted from the supernatant liquid discharge opening part 36 to a river etc. through the drain pipe not shown. The supernatant liquid thus discharged contains almost no suspended solids or precipitates and can be drained safely.
[0039]
On the other hand, in the first sedimentation chamber 31 which is the first sedimentation chamber, most of the suspended solids contained in the muddy water sent from the stirring-treated water drop duct 20 is precipitated and remains in the next second sedimentation chamber 32. It was found that most of the suspended solids were precipitated. This is probably because the turbid water and the flocculant were sufficiently mixed in the stirring tank 10 so that precipitation was performed more efficiently.
[0040]
Therefore, in the present embodiment, a screw conveyor 38 is provided at the bottom of the first sedimentation chamber 31 in order to remove the sediment 40 a that has settled at the bottom of the first sedimentation chamber 31. The screw conveyor 38 is provided with a screw shaft in a casing. A part of the casing is opened in the first sedimentation chamber 31, and the sediment is taken into the casing through the opening. The precipitate is transferred to one of the axial directions by the rotation of. A sediment discharge pipe is attached to the end of the sediment transfer side, and the precipitate is sent to a sediment treatment tank or the like through this sediment discharge pipe. The screw shaft of the screw 38 is rotationally driven by a screw motor 38a.
[0041]
Next, since the precipitate 40b generated in the second sedimentation chamber 32 is a small amount and most of the particles are small particles, a drain pipe (not shown) is attached to the bottom of the second sedimentation chamber. The drain cock may be opened and extracted periodically and sent to the above-described sediment processing tank or the like.
[0042]
The muddy water treatment machine 1 of the present embodiment includes muddy water generated from a gravel / fracture plant, muddy water discharged from construction work such as a dam / tunnel, muddy water generated from civil engineering / construction work, dyeing / food / chemicals.・ It can be applied to the treatment of turbid water discharged from fish farms.
[0043]
【The invention's effect】
As described above, according to the present invention, without increasing the size of the stirring tank, the residence time of the muddy water continuously supplied into the stirring tank can be increased, and the stirring and mixing efficiency can be increased. Water can be discharged.
[Brief description of the drawings]
FIG. 1 is a cross-sectional view of a muddy water treatment machine according to an embodiment of the present invention.
2 is a top view of the muddy water treatment machine of FIG. 1. FIG.
FIG. 3 is a left side view of the muddy water treatment machine of FIG.
FIG. 4 is a right side view of the muddy water treatment machine of FIG.
[Explanation of symbols]
DESCRIPTION OF SYMBOLS 1 ... Turbid water treatment machine 10 ... Stirring tank 11 ... Water tank part 12 ... Turbid water supply part 13 ... Stir processing water outlet part 14 ... Coagulant inlet 15 ... Stirring shaft 16 ... Motor 17 with a deceleration function ... Feed screw part 18 ... Paddle 19 ... Agitating blade 20 ... Draining water dropping duct 21 ... Cascade member 30 ... Sedimentation tank 31 ... First sedimentation chamber 31a, b ... Partition wall 32 ... Second sedimentation chamber 32a, b ... Partition wall 32a ', b' ... Projection plate 33 ... 3rd sedimentation chamber 33a, b ... partition wall 34 ... 4th sedimentation chamber 34a ... partition wall 35 ... 5th sedimentation chamber 36 ... supernatant liquid discharge part 37 ... dropping pipe 37a ... shielding plate 38 ... screw 38a ... screw Motors 40a, b ... precipitates

Claims (2)

筒形状に形成された水槽内に軸方向に沿って攪拌軸を回転可能に設け、前記水槽の一方から連続的に供給される濁水に対して凝集剤を供給し、前記攪拌軸により濁水と前記凝集剤とを攪拌混合して連続的に前記水槽の他方から排出する攪拌槽と、
前記攪拌槽の下部に配置され、複数の沈殿室が区分けされ、一端の沈殿室に前記攪拌槽から連続的に排出された濁水が供給され、他端の沈殿室から上澄み液を槽外に排出する沈殿槽と、
を有し、
前記攪拌軸は、連続的に供給される濁水の流れに対して逆方向の流れを生じさせる逆流攪拌翼を有し、前記攪拌軸の一方から他方へ向けて流れる濁水の流れを遅くし、前記攪拌槽内での濁水と凝集剤との攪拌時間を長くすることを特徴とする濁水処理機。
A stirring shaft is rotatably provided along the axial direction in a water tank formed in a cylindrical shape, and a flocculant is supplied to muddy water continuously supplied from one of the water tanks. A stirring tank for stirring and mixing the flocculant and continuously discharging from the other of the water tanks;
Located in the lower part of the agitation tank, a plurality of sedimentation chambers are divided, the muddy water continuously discharged from the agitation tank is supplied to the sedimentation chamber at one end, and the supernatant liquid is discharged from the precipitation chamber at the other end to the outside of the tank A sedimentation tank,
Have
The stirring shaft has a reverse flow stirring blade that generates a flow in a reverse direction to the flow of turbid water continuously supplied, and slows the flow of turbid water flowing from one side of the stirring shaft to the other. A turbid water treatment machine characterized in that the stirring time of turbid water and a flocculant in a stirring tank is lengthened.
前記攪拌軸には、前記濁水供給部に対応して濁水の流速を規制するスクリュー部が設けられ、且つ前記スクリュー部の下流側に前記逆流攪拌翼が設けられていて、前記スクリュー部のすぐ下流側の部分に対応して前記凝集剤が投入されることを特徴とする請求項1に記載の濁水処理機。The agitation shaft is provided with a screw part that regulates the flow rate of turbid water corresponding to the turbid water supply part, and is provided with the back-flow agitation blade on the downstream side of the screw part, immediately downstream of the screw part. 2. The muddy water treatment machine according to claim 1, wherein the flocculant is introduced corresponding to a portion on the side.
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