JP2001347260A - Sewage purifying apparatus - Google Patents

Sewage purifying apparatus

Info

Publication number
JP2001347260A
JP2001347260A JP2000172317A JP2000172317A JP2001347260A JP 2001347260 A JP2001347260 A JP 2001347260A JP 2000172317 A JP2000172317 A JP 2000172317A JP 2000172317 A JP2000172317 A JP 2000172317A JP 2001347260 A JP2001347260 A JP 2001347260A
Authority
JP
Japan
Prior art keywords
sewage
mixing
stirring chamber
air
wastewater
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
JP2000172317A
Other languages
Japanese (ja)
Inventor
Rie Hiramoto
理恵 平本
Ichiro Oshima
一郎 大島
Shinya Takagi
真也 高木
Mugihei Ikemizu
麦平 池水
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.)
Sharp Corp
Original Assignee
Sharp Corp
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 Sharp Corp filed Critical Sharp Corp
Priority to JP2000172317A priority Critical patent/JP2001347260A/en
Priority to US10/031,084 priority patent/US6820446B2/en
Priority to KR1020027001179A priority patent/KR20020020800A/en
Priority to PCT/JP2001/004471 priority patent/WO2001091879A1/en
Priority to EP01934379A priority patent/EP1291057A4/en
Publication of JP2001347260A publication Critical patent/JP2001347260A/en
Pending legal-status Critical Current

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Landscapes

  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Physical Water Treatments (AREA)

Abstract

PROBLEM TO BE SOLVED: To provide a sewage purifying apparatus capable of being installed at any location, saving a space and purifying efficiently a large amount of sewage. SOLUTION: This sewage purifying device is provided with an aspirator 5 that mixes a coagulant solution 4 stored in a coagulant tank 2 and air from an air filter 3 with washing waste water 1 by a vacuum suction mechanism, an introduction pipe 17 that introduces the washing waste water 1a containing coagulate particles and the air into the inside or a cylindrical stirring chamber 18 in the tangential direction with respect to the horizontal cross section of the stirring chamber 18, a mixing cylinder 8 that sucks the washing waste water circling and going up along the inner wall of the stirring chamber 18, from the inlet part 8b of its upper end and makes the coagulate particles gravity-flow down as air bubbles are held in them, and a waste water collecting part 10 that stores the washing waste water 1d flowing out from the outlet part 8b of the lower end of the mixing cylinder 8 and discharges it together with the coagulate particles to the outside from an upper connection pipe 25.

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、汚水浄化装置に係
り、より詳しくは洗濯排水中の界面活性剤等の汚染物質
の濃度を低下させる汚水浄化装置に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a sewage purification apparatus, and more particularly, to a sewage purification apparatus for reducing the concentration of contaminants such as surfactants in laundry wastewater.

【0002】[0002]

【従来の技術】従来、電気洗濯機の洗濯排水はそのまま
排水されており、合成洗剤の主成分である直鎖アルキル
ベンゼンスルホン酸ナトリウム(LAS)やアルキル硫
酸エステル等の陰イオン界面活性剤は比較的生分解がし
にくいため、石けんと比べて河川等の水質を汚染させる
原因になっている。
2. Description of the Related Art Conventionally, washing wastewater from an electric washing machine is drained as it is, and anionic surfactants such as sodium linear alkylbenzenesulfonate (LAS) and alkylsulfate, which are the main components of the synthetic detergent, are relatively insoluble. Since it is difficult to biodegrade, it causes water pollution of rivers and the like as compared with soap.

【0003】今日、家庭から排出される洗濯排水が水質
汚染に最も大きな影響を与えていると言われている。こ
のため、洗濯排水中に含まれる界面活性剤等の汚染物質
の濃度を低下させてきれいな水を排水することが環境保
護の面で望まれている。
[0003] Today, it is said that laundry wastewater discharged from homes has the greatest effect on water pollution. For this reason, it is desired from the viewpoint of environmental protection to reduce the concentration of contaminants such as surfactants contained in washing wastewater and drain clean water.

【0004】このような要望に対し、特開平8−229
543号公報には排水中の微粒子等を効率よく迅速に浮
上分離させる排水処理装置が提案されている。この従来
の排水処理装置の構成を図4及び図5を参照して説明す
る。
In response to such a demand, Japanese Patent Application Laid-Open No. 8-229
Japanese Patent Application Publication No. 543 proposes a wastewater treatment apparatus that efficiently and quickly floats and separates fine particles and the like in wastewater. The configuration of this conventional wastewater treatment apparatus will be described with reference to FIGS.

【0005】被処理液102を流す流路156の一部を
絞った絞り部158と、絞り部158に続いて下流側に
設けられ流路156方向に断面積の等しい気体流入部1
60を設け、この気体流入部160に外部から空気を流
入させる気体流入口166を形成し、気体流入口166
の下流側に流路156を徐々に広げた広がり部162を
設ける。
A throttle 158 which narrows a part of a flow path 156 through which the liquid to be treated 102 flows, and a gas inlet 1 provided downstream of the throttle 158 and having the same cross-sectional area in the direction of the flow path 156.
60, and a gas inlet 166 through which air is introduced from the outside into the gas inlet 160 is formed.
A widened portion 162 in which the flow path 156 is gradually widened is provided on the downstream side.

【0006】広がり部162の下流に流路156中の被
処理液102と気体流入口166から流入した気体とを
加圧下で混合する加圧混合部108を設け、加圧混合部
108の出口側に凝集剤を注入する薬剤注入部120を
接続し、その下流に薬剤混合部122を形成し、その下
流にノズル部124と、浮上分離層128を備える。
Downstream of the expanding section 162, there is provided a pressurizing and mixing section 108 for mixing the liquid to be treated 102 in the flow path 156 and the gas flowing in from the gas inlet 166 under pressure. A drug injecting unit 120 for injecting an aggregating agent is connected thereto, a drug mixing unit 122 is formed downstream thereof, and a nozzle unit 124 and a floating separation layer 128 are provided downstream thereof.

【0007】[0007]

【発明が解決しようとする課題】しかしながら、この従
来の排水処理装置は小型とはいえ、吸引した被処理液へ
の気体と凝集剤の混合、これにより形成された凝集体を
含む被処理液の攪拌並びに凝集体の分離に至る各処理工
程を長い管路で連結しているため、装置全体としてはか
さばり、設置場所が制限されてしまう。即ち、家庭から
出る洗濯排水や台所排水といった生活排水を浄化するた
めに、洗濯機や流し台等の水回りにこのような装置の設
置スペースを充分に確保することが難しかった。
However, although this conventional wastewater treatment apparatus is small, it mixes a gas and a coagulant into the suctioned liquid to be treated, and removes the liquid to be treated containing the aggregate formed by this. Since the respective processing steps leading to agitation and separation of aggregates are connected by a long pipe, the whole apparatus is bulky and the installation place is restricted. That is, in order to purify household wastewater such as washing wastewater and kitchen wastewater from home, it has been difficult to secure a sufficient installation space for such a device around water such as a washing machine or a sink.

【0008】本発明は、上記従来の問題に鑑みてなされ
たものであり、更なる省スペース化が可能で効率よく大
量の汚水の浄化処理を行える汚水浄化装置を提供するこ
とを目的とする。
The present invention has been made in view of the above-mentioned conventional problems, and an object of the present invention is to provide a sewage purification apparatus capable of further saving space and efficiently purifying a large amount of sewage.

【0009】[0009]

【課題を解決するための手段】上記目的を達成するため
に、本発明は界面活性剤等の汚染物質を含む汚水に凝集
剤を混和して粗大化した凝集体粒子を捕集する汚水浄化
装置において、前記凝集剤の混和とともに前記汚水に空
気を混合する手段と、前記凝集体粒子及び前記空気を含
む前記汚水を円筒状の攪拌室の内部に該攪拌室の中心を
通らない角度でもって導入する手段と、前記攪拌室の内
壁に沿って旋回しながら上昇する前記汚水を吸い込んで
前記凝集体粒子に気泡を保持させる混合手段と、該混合
手段から流出する前記汚水を一旦貯留する排水捕集手段
とを有することを特徴とする汚水浄化装置。
SUMMARY OF THE INVENTION In order to achieve the above object, the present invention provides a sewage purification apparatus which collects coarse aggregate particles by mixing a flocculant with a sewage containing a pollutant such as a surfactant. And means for mixing air with the sewage together with mixing of the flocculant, and introducing the sewage containing the agglomerated particles and the air into a cylindrical stirring chamber at an angle that does not pass through the center of the stirring chamber. Means for sucking the sewage rising while rotating along the inner wall of the stirring chamber to retain bubbles in the agglomerated particles, and drainage collection for temporarily storing the sewage flowing out from the mixing means. And a means for purifying sewage.

【0010】この構成によると、汚染物質を含む汚水に
凝集体及び空気を混合し、汚染物質の凝集体粒子を形成
させるとともにそれを粗大化して捕集する機構がコンパ
クトな空間に集約される。
According to this configuration, a mechanism for mixing aggregates and air into sewage water containing contaminants, forming aggregate particles of the contaminants, and coarsening and collecting the particles is concentrated in a compact space.

【0011】また、本発明は界面活性剤等の汚染物質を
含む汚水に凝集剤を混和して粗大化した凝集体粒子を捕
集する汚水浄化装置において、前記凝集剤の混和ととも
に前記汚水に空気を混合する手段と、前記凝集体粒子及
び前記空気を含む前記汚水を円筒状の攪拌室の内部に該
攪拌室の水平断面に対して接線方向になるように導入す
る手段と、前記攪拌室の内壁に沿って旋回しながら上昇
する前記汚水を上端の入口部から吸い込んで前記凝集体
粒子に気泡を保持させながら自然流下させる混合手段
と、該混合手段の下端の出口部から流出する前記汚水を
一旦貯留して前記凝集体粒子とともに上方の排出口から
外部に排出する排水捕集手段とを有することを特徴とす
る。
The present invention also relates to a sewage purifying apparatus for collecting agglomerated aggregated particles by mixing a flocculant into a sewage containing a pollutant such as a surfactant. And a means for introducing the sewage containing the aggregated particles and the air into a cylindrical stirring chamber so as to be tangential to a horizontal cross section of the stirring chamber. A mixing means for sucking the sewage rising while rotating along the inner wall from an inlet at an upper end and allowing the aggregated particles to flow naturally while holding bubbles, and the sewage flowing out from an outlet at a lower end of the mixing means. A wastewater collecting means for temporarily storing the wastewater and discharging it together with the aggregated particles to the outside from an upper outlet.

【0012】この構成によると、汚染物質を含む汚水に
凝集体及び空気を混合し、汚染物質の凝集体粒子を形成
させるとともにそれを粗大化して捕集し、汚水を凝集体
粒子と共に外部に排出する機構がコンパクトな空間に集
約される。
According to this configuration, the aggregate and air are mixed with the sewage containing the pollutant to form the agglomerate particles of the contaminant, collect the coarse particles, and discharge the sewage to the outside together with the aggregate particles. Mechanism to be integrated in a compact space.

【0013】更に、前記排出口を介して前記排水捕集手
段と連通し前記汚水から前記凝集体粒子を分離・回収す
るとともに、前記凝集体粒子が排除された浄化水を排水
するろ過部を設けると、ろ過部に分離された凝集体粒子
を普通ゴミとして廃棄できるとともに、排水による河川
等の水質汚染を抑制できる。
Further, a filtration unit is provided which communicates with the wastewater collecting means through the discharge port to separate and collect the aggregated particles from the wastewater and drains purified water from which the aggregated particles have been removed. In addition, the aggregate particles separated by the filtration unit can be discarded as ordinary waste, and water pollution of rivers and the like due to drainage can be suppressed.

【0014】そして、前記攪拌室、前記排水捕集手段及
び前記ろ過部とを一体的に形成することにより、装置自
体がコンパクトになり、省スペース化が図られる。
Further, by integrally forming the stirring chamber, the drainage collecting means and the filtration section, the apparatus itself becomes compact and space is saved.

【0015】この場合、前記汚水への前記凝集剤の混和
及び前記空気の混合は、減圧吸引機構によってスムーズ
に行うことができる。減圧吸引機構としては、例えば、
アスピレータを利用でき、これは加圧水が流れることに
より負圧部が発生する方式であるため、空気の混合にエ
アポンプを設置する必要がなくシステムの簡素化、コス
ト削減の点で有利である。
In this case, the mixing of the coagulant into the sewage and the mixing of the air can be performed smoothly by a reduced-pressure suction mechanism. As the reduced pressure suction mechanism, for example,
An aspirator can be used, and this is a method in which a negative pressure section is generated by flowing pressurized water. Therefore, there is no need to install an air pump for mixing air, which is advantageous in terms of simplification of the system and cost reduction.

【0016】尚、前記混合筒の内部に、略正方形若しく
は略長方形をした板状部材の一対の向かい合う2辺のな
す角が所定の角度になるように捻られたものを直列に連
結したスパイラルフィンを設けると、螺旋状のスパイラ
ルフィンの表面を伝って前記汚水が前記混合筒内を自然
流下するので、凝集体粒子へ気泡を保持させてこれの粗
大化を促進できる。
A spiral fin in which a pair of substantially square or substantially rectangular plate-like members twisted so as to form a predetermined angle between two opposite sides thereof is connected in series in the mixing cylinder. Is provided, the sewage naturally flows down in the mixing cylinder along the surface of the spiral spiral fin, so that the aggregated particles can retain bubbles and promote the coarsening thereof.

【0017】また、ろ過部における上記凝集体粒子の分
離・回収に洗濯用ネットを用いることもできる。この場
合は、洗濯時に衣類の如き洗濯物の傷みを防止するため
に使用する洗濯用ネットを凝集体粒子のろ過にも併用で
きる。
Further, a washing net can be used for separating and collecting the aggregated particles in the filtration section. In this case, a washing net used to prevent damage to laundry such as clothes during washing can be used in combination with filtration of aggregated particles.

【0018】ところで、前記凝集剤の混和とともに前記
汚水に空気を混合する手段から前記ろ過部に至る前記汚
水の排水経路の内壁の表面に非粘着加工を施すと、汚水
の浄化処理時に形成される凝集体粒子が排水経路の内壁
に付着するのを防止できる。
By the way, if the surface of the inner wall of the drainage route of the sewage from the means for mixing air with the sewage together with the mixing of the flocculant is subjected to non-adhesive processing, the sewage is formed during the purification treatment of the sewage. Aggregate particles can be prevented from adhering to the inner wall of the drainage passage.

【0019】そして、前記排水捕集手段を前記攪拌室に
対し着脱自在に設けると、必要に応じて排水捕集手段を
取り外してその内部の洗浄等のメンテナンスを行える。
If the drainage collecting means is provided detachably with respect to the stirring chamber, the drainage collecting means can be removed as necessary to perform maintenance such as cleaning of the inside thereof.

【0020】[0020]

【発明の実施の形態】<第1の実施形態>本発明の第1
の実施形態について図面を参照して説明する。まず、本
実施形態に係る汚水浄化装置の構成を説明する。図1に
示すように、減圧吸引機構であるアスピレータ5は、導
入管17を介して後述する攪拌筒18の下方に連通接続
されている。更に、アスピレータ5には、Y字状に分岐
した分岐管15の根本側の一端が連通接続されている。
そして、この分岐管15の二股に分岐した他端には、そ
れぞれ凝集剤溶液4を収容する凝集剤タンク2と、外気
から吸引された空気のろ過を行うエアフィルタ3が接続
されている。16は、凝集剤溶液4の流量調整バルブで
ある。
DESCRIPTION OF THE PREFERRED EMBODIMENTS <First Embodiment> A first embodiment of the present invention
An embodiment will be described with reference to the drawings. First, the configuration of the sewage purification apparatus according to the present embodiment will be described. As shown in FIG. 1, the aspirator 5, which is a reduced-pressure suction mechanism, is connected through an introduction pipe 17 to a portion below a stirring cylinder 18 described below. Further, one end on the root side of a branch pipe 15 branched in a Y-shape is connected to the aspirator 5.
The other end of the branch pipe 15 is connected to a coagulant tank 2 for storing a coagulant solution 4 and an air filter 3 for filtering air sucked from outside air. Reference numeral 16 denotes a flow control valve for the coagulant solution 4.

【0021】上面が閉塞された攪拌筒18の内部には、
円筒状の空間である攪拌室6が形成されている。導入管
17は、図2に示すように例えば、略円形をした攪拌室
6の水平断面に対して接線方向になるように攪拌筒18
と連結されている。従って、攪拌室6内に導入管17を
経由して導入される洗濯排水1aは、攪拌室6の内壁に
沿った旋回水流fを作り、攪拌されながら攪拌室6内を
上昇する。
Inside the stirring cylinder 18 whose upper surface is closed,
A stirring chamber 6, which is a cylindrical space, is formed. As shown in FIG. 2, the introduction pipe 17 is, for example, a stirring cylinder 18 so as to be tangential to a horizontal section of the substantially circular stirring chamber 6.
Is linked to Therefore, the washing drainage 1a introduced into the stirring chamber 6 via the introduction pipe 17 forms a swirling water flow f along the inner wall of the stirring chamber 6, and rises inside the stirring chamber 6 while being stirred.

【0022】攪拌筒18の下方には、隔離され該攪拌筒
18より内径の大きな円筒状の排水捕集部10が同心的
に設けられている。そして、攪拌筒18及び排水捕集部
10の内部の略中央部には、所定の長さを有する内径の
比較的小さな混合筒8が長手方向に挿通されている。こ
の混合筒8の内部には、後述するスパイラルフィン7が
配設されている。
Below the agitating cylinder 18, a cylindrical drainage collecting section 10 which is isolated and has a larger inner diameter than the agitating cylinder 18 is provided concentrically. A mixing tube 8 having a predetermined length and a relatively small inner diameter is inserted in a substantially central portion of the inside of the stirring tube 18 and the drainage collection unit 10 in the longitudinal direction. A spiral fin 7, which will be described later, is provided inside the mixing cylinder 8.

【0023】スパイラルフィン7は、例えば、縦横比
1.5:1又は1:1程度の大きさのプレートを対向す
る2辺のなす角が180°になるように捻ったものを1
セルとし、このセルの複数個を直列に連結することによ
り螺旋状に形成されている。尚、この場合のセル数は特
に限定されない。また、スパイラルフィン7の材質は金
属若しくは樹脂のどちらでもよいが、成形加工性の点で
樹脂の方が好ましい。
The spiral fin 7 is formed, for example, by twisting a plate having an aspect ratio of about 1.5: 1 or 1: 1 such that the angle between two opposing sides is 180 °.
The cells are spirally formed by connecting a plurality of cells in series. The number of cells in this case is not particularly limited. The material of the spiral fin 7 may be either a metal or a resin, but a resin is more preferable in terms of moldability.

【0024】混合筒8の上端の入口部8aは攪拌筒18
の上面に近接しており、攪拌室6内を旋回水流fとなっ
て上昇してきた洗濯排水1bは入口部8aから混合筒8
内に流入し、螺旋状のスパイラルフィン7の表面を伝っ
て自然流下する。
The inlet 8a at the upper end of the mixing cylinder 8 is
The washing drainage 1b, which is in the vicinity of the upper surface and rises in the stirring chamber 6 as a swirling water flow f, flows through the inlet 8a through the mixing cylinder 8
And flows down the surface of the spiral spiral fin 7 naturally.

【0025】19は上面が開放した箱形状に形成された
ろ過部であり、19aはその上面開口部を開閉する蓋で
ある。このろ過部19の内部には、その内壁に沿う形状
をした金網等からなる脱水かご20が着脱自在に配設さ
れている。更に、この脱水かご20の内部には通水性の
ある袋状の洗濯用ネット21が保持されている。また、
ろ過部19の側面下方には洗濯用ネット21を通過した
浄化水の排水のための排水管22が設けられている。
Reference numeral 19 denotes a filtering section formed in a box shape having an open upper surface, and 19a denotes a lid for opening and closing the upper opening. Inside the filtration unit 19, a dewatering basket 20 made of a wire mesh or the like shaped along the inner wall is detachably provided. Further, inside the dewatering basket 20, a bag-like washing net 21 having water permeability is held. Also,
A drain pipe 22 for draining purified water that has passed through the washing net 21 is provided below the side surface of the filtration unit 19.

【0026】25は排水捕集部10の上方から引き出さ
れた連結管であり、その他端はろ過部19の蓋19aを
貫通して洗濯用ネット21内に導かれている。これによ
り、排水捕集部10とろ過部19とは連結管25を介し
て連通接続される。尚、ろ過部19を連結管25に対し
着脱可能に設けると、必要に応じてろ過部19を汚水浄
化装置から分離して清掃等のメンテナンスを行えるの
で、製品寿命の短縮を抑制できる。
Reference numeral 25 denotes a connecting pipe drawn from above the drainage collecting section 10, and the other end thereof is guided through the lid 19 a of the filtering section 19 into the washing net 21. Thus, the drainage collection unit 10 and the filtration unit 19 are connected to each other through the connection pipe 25. In addition, if the filtration part 19 is provided detachably with respect to the connection pipe 25, the filtration part 19 can be separated from the sewage purification device and maintenance such as cleaning can be performed as needed, so that shortening of the product life can be suppressed.

【0027】次に、以上の構成を有する汚水浄化装置の
使用形態について図1及び図2を参照して説明する。ま
ず、ポンプ等の加圧供給手段(図示せず)によって洗濯
排水1がアスピレータ5に導入されると、その水流によ
って負圧部が生じ、負圧部に連通する分岐管15に連結
された凝集剤タンク2及びエアフィルタ3から凝集剤溶
液4及び空気が洗濯排水1に混和される。尚、凝集剤溶
液4の混合量は、洗濯排水1の流量に応じて流量調整バ
ルブ16の開閉具合を加減することによって適切に調整
できるようになっている。
Next, the usage of the sewage purification apparatus having the above configuration will be described with reference to FIGS. First, when the washing drainage 1 is introduced into the aspirator 5 by pressurizing and supplying means (not shown) such as a pump, a negative pressure portion is generated by the water flow, and coagulation is connected to the branch pipe 15 communicating with the negative pressure portion. The coagulant solution 4 and air are mixed into the washing drainage 1 from the agent tank 2 and the air filter 3. The mixing amount of the coagulant solution 4 can be appropriately adjusted by adjusting the opening / closing state of the flow control valve 16 in accordance with the flow rate of the washing drainage 1.

【0028】このとき添加する凝集剤としては、一般的
に汚水の浄化処理に用いられる無機系のポリ塩化アルミ
ニウム、硫酸アルミニウム等を好適に使用でき、更に凝
集体粒子の粗大化を図るためには、例えば、ポリアクリ
ルアミド等の有機系の高分子凝集剤を使用するとよい。
本実施形態では、図示しない槽にて無機凝集剤を添加済
みの洗濯排水1をアスピレータ5内にに圧送する。そし
て、凝集剤タンク2には高分子凝集剤溶液を準備してお
き、アスピレータ5の吸引作用によって洗濯排水1中に
空気と高分子凝集剤を混和させる。
As the coagulant to be added at this time, inorganic polyaluminum chloride, aluminum sulfate and the like generally used for sewage purification treatment can be suitably used. In order to further increase the size of the aggregate particles, For example, an organic polymer flocculant such as polyacrylamide may be used.
In the present embodiment, the washing drainage 1 to which the inorganic coagulant has been added is pumped into the aspirator 5 in a tank (not shown). Then, a polymer coagulant solution is prepared in the coagulant tank 2, and the air and the polymer coagulant are mixed into the washing drainage 1 by the suction action of the aspirator 5.

【0029】凝集剤溶液4と空気が混合された洗濯排水
1aは、上述したように導入管17を経由して攪拌筒1
8内に導入され、攪拌室6の内壁に沿った旋回水流fを
作り、攪拌されながら攪拌室6内を上昇する。このと
き、洗濯排水1aは速やかに攪拌されるため、凝集剤の
働きと相俟って洗濯排水1a中の界面活性剤や洗濯物か
ら分離した汚れ成分等の汚染物質が凝集して数十〜数百
μmに粗大化した凝集体が形成される。このようにして
粗大化した凝集体を含む洗濯排水1bは入口部8aから
混合筒8内に流入し、螺旋状のスパイラルフィン7の表
面を伝って自然流下する。
The washing wastewater 1a in which the coagulant solution 4 and the air are mixed is passed through the introduction pipe 17 through the introduction pipe 17 as described above.
The swirling water flow f is introduced into the stirring chamber 8 along the inner wall of the stirring chamber 6 and rises inside the stirring chamber 6 while being stirred. At this time, since the washing wastewater 1a is rapidly stirred, contaminants such as a surfactant and a dirt component separated from the laundry in the washing wastewater 1a are aggregated together with the action of the coagulant, and several tens to Aggregates coarsened to several hundred μm are formed. The washing wastewater 1b containing the aggregates thus coarsened flows into the mixing cylinder 8 from the inlet 8a, and flows down the surface of the spiral spiral fin 7 naturally.

【0030】ところで、攪拌室6内で洗濯排水1aが旋
回攪拌される際、遠心力の作用で軽い空気は混合筒8の
外周面近傍に集中するが、混合筒8内を通過させること
で洗濯排水1b中の空気と凝集体が均一に混合されるた
め、混合筒8内では気泡を保持した凝集体粒子の粗大化
が促進される。
When the washing drain 1a is swirled and stirred in the stirring chamber 6, light air is concentrated near the outer peripheral surface of the mixing cylinder 8 due to the action of centrifugal force. Since the air and the aggregate in the waste water 1b are uniformly mixed, the coarsening of the aggregate particles holding the bubbles in the mixing cylinder 8 is promoted.

【0031】そして、混合筒8の出口部8bから凝集体
粒子を含む洗濯排水1cが排水捕集部10内に落下し、
ここに徐々に蓄えられていく。このとき、洗濯排水1c
は重力により噴流となって勢いよく滴下するので、その
まま洗濯排水1cから凝集体粒子をフィルタ等を用いて
分離しようとすると、せっかく粗大化された凝集体粒子
が噴流により砕けて再び細かい粒子となってしまう。そ
こで、排水捕集部10内で一旦洗濯排水1cを貯留し噴
流の勢いを緩衝させることで、粗大化させた凝集体粒子
が粉砕されることなくろ過部19まで導くことが可能と
なる。
Then, the washing wastewater 1c containing the aggregated particles falls from the outlet part 8b of the mixing cylinder 8 into the wastewater collecting part 10,
It is gradually stored here. At this time, washing drainage 1c
Becomes a jet due to gravity and drops vigorously. If it is attempted to separate the aggregated particles from the washing wastewater 1c using a filter or the like, the aggregated particles that have become coarser are crushed by the jet and become fine particles again. Would. Therefore, by temporarily storing the washing wastewater 1c in the wastewater collecting unit 10 and buffering the flow of the jet, the coarsened aggregate particles can be guided to the filtering unit 19 without being crushed.

【0032】やがて、排水捕集部10内で満水近くまで
洗濯排水1cの水位が達すると、オーバーフローして連
結管25を通って、洗濯排水1dが廃棄凝集体23と共
にろ過部19内に導かれる。そして、廃棄凝集体23が
洗濯用ネット21でろ過・分離され、洗濯用ネット21
を通過することにより自然脱水された浄化水1eが脱水
かご20を経由して排水管22から外部に排水される。
When the water level of the washing wastewater 1c reaches near full water in the wastewater collecting part 10, the washing wastewater 1d overflows through the connecting pipe 25 and is guided into the filtering part 19 together with the waste aggregate 23. . Then, the waste aggregate 23 is filtered and separated by the washing net 21, and the washing net 21 is removed.
, The purified water 1e that has been naturally dehydrated is drained to the outside from the drain pipe 22 via the dehydrating basket 20.

【0033】洗濯用ネット21内に廃棄凝集体23があ
る程度溜まった場合は、ろ過部19の蓋19aを開いて
洗濯用ネット21を取り出せば、溜まった廃棄凝集体2
3を捨てられる。同時に、脱水かご20も取り外せるた
め、必要に応じて洗濯用ネット21及び脱水かご20を
洗浄することにより、脱水かご20を含むろ過部19の
内部を衛生状態を確保できる。
When the waste agglomerates 23 accumulate in the washing net 21 to a certain extent, the lid 19a of the filtering unit 19 is opened and the washing net 21 is taken out.
Discard 3 At the same time, since the dewatering basket 20 can also be removed, the inside of the filtration unit 19 including the dewatering basket 20 can be maintained in a sanitary state by washing the washing net 21 and the dewatering basket 20 as necessary.

【0034】尚、アスピレータ5から連結管25に至る
排水経路の内壁に非粘着加工(例えば、フッ素コーティ
ング等)を施しておくと、凝集体粒子の混在した洗濯排
水が排水経路を通過する際、その内壁に凝集体粒子がこ
びり付く恐れがないため、度重なる洗濯排水の浄化処理
にも、排水経路の清掃の手間が不要となる。
If the inner wall of the drainage passage from the aspirator 5 to the connecting pipe 25 is subjected to non-adhesive processing (for example, fluorine coating), the washing wastewater mixed with aggregate particles passes through the drainage passage. Since there is no danger of the aggregate particles sticking to the inner wall, the trouble of cleaning the drainage passage is unnecessary even in the repeated washing water purification treatment.

【0035】本発明に係る汚水浄化装置による洗濯排水
の浄化試験の一例を示す。使用した汚水浄化装置の各部
の内径及び高さの寸法は、攪拌筒18が50mm×200
mm、混合筒8が20mm×360mm、排水捕集部10が6
6mm×250mmである。このような汚水浄化装置に、洗
濯排水を供給流量約4.8L/分で流すとともに、空気
吸入流量3.0L/分で洗濯排水中に混和させた。
An example of a cleaning test for washing wastewater by the sewage purification apparatus according to the present invention will be described. The dimensions of the inner diameter and the height of each part of the used sewage purification apparatus were such that the stirring cylinder 18 was 50 mm × 200.
mm, the mixing cylinder 8 is 20 mm x 360 mm, and the drainage collecting section 10 is 6
It is 6 mm x 250 mm. Washing wastewater was supplied to such a sewage purification device at a supply flow rate of about 4.8 L / min and mixed with the washing wastewater at an air intake flow rate of 3.0 L / min.

【0036】界面活性剤として花王製粉末洗剤アタック
(商標)を使用し、初期濃度240ppm、濁度100NTU
になるよう洗濯排水を調製した。また、無機凝集剤には
多木化学製ポリ塩化アルミニウム水溶液PAC300A
((商標)、ポリ塩化アルミニウム濃度33%)を使用
し、洗濯排水1Lあたり1.7mLを添加した。
Using Kao powder detergent Attack (trademark) as a surfactant, initial concentration 240 ppm, turbidity 100 NTU
The washing drainage was prepared so that The inorganic flocculants include poly aluminum chloride aqueous solution PAC300A manufactured by Taki Kagaku.
((Trademark), poly aluminum chloride concentration 33%), and 1.7 mL was added per 1 L of washing drainage.

【0037】更に、凝集剤タンク2内には東亜合成製ノ
ニオン高分子凝集剤N110(商標)の0.3%水溶液
を充填し、洗濯排水1Lに対し4.0mL混合されるよう
に調製した。このような実験条件で排水口22から排水
される浄化水1e中の界面活性剤濃度を測定したとこ
ろ、処理前の洗濯排水1における240ppmから8ppm程
度に低下しており、透明度の指標である濁度は1〜2NT
Uとなり充分な浄化処理能力が得られた。
Further, the flocculant tank 2 was filled with a 0.3% aqueous solution of a nonionic polymer flocculant N110 (trade name) manufactured by Toagosei Co., Ltd., and was prepared so that 4.0 mL was mixed with 1 L of washing wastewater. When the concentration of the surfactant in the purified water 1e drained from the drain port 22 was measured under such experimental conditions, the concentration was lowered from 240 ppm in the washing wastewater 1 before the treatment to about 8 ppm, and the turbidity which is an index of the transparency was measured. The degree is 1-2NT
It became U and sufficient purification treatment capacity was obtained.

【0038】<第2の実施形態>本発明の第2の実施形
態について図面を参照して説明する。図3は、本実施形
態に係る汚水浄化装置の概略断面図である。尚、この図
において、図1に示す上記第1の実施形態に係る汚水浄
化装置と共通の部材には同一の符号を付し、その詳細な
説明を省略する。
<Second Embodiment> A second embodiment of the present invention will be described with reference to the drawings. FIG. 3 is a schematic sectional view of the sewage purification device according to the present embodiment. In this figure, the same members as those of the sewage purification device according to the first embodiment shown in FIG. 1 are denoted by the same reference numerals, and detailed description thereof will be omitted.

【0039】本実施形態に特徴的な構成は、図3に示す
ように、排水捕集部10の外側にろ過部19を攪拌筒1
8に対し一体的に設け、排水浄化処理のすべての工程が
集約された汚水浄化装置としたことである。尚、ろ過部
19は攪拌筒18に対し、フック式クランプ26にて着
脱可能になっている。
As shown in FIG. 3, a characteristic configuration of the present embodiment is that a filtering section 19 is provided outside the drainage collecting section 10 with a stirring cylinder 1.
8 is provided integrally with the sewage water purification apparatus in which all the steps of the wastewater purification treatment are integrated. The filtering unit 19 is detachable from the stirring tube 18 by a hook type clamp 26.

【0040】そして、ろ過部19の上面と攪拌筒18の
底面との間には水漏れ防止のためのパッキン27が混合
筒8の挿通部分を避けて配設されている。また、排水捕
集部10はろ過部19の上面に接着等により固定されて
いる。28は排水捕集部10の側面上部に設けられた排
出管である。
A packing 27 for preventing water leakage is provided between the upper surface of the filtration unit 19 and the bottom surface of the stirring tube 18 so as to avoid the portion where the mixing tube 8 is inserted. Further, the drainage collecting section 10 is fixed to the upper surface of the filtering section 19 by bonding or the like. Reference numeral 28 denotes a discharge pipe provided at an upper part of the side surface of the drainage collection unit 10.

【0041】次に、以上の構成を有する汚水浄化装置の
使用形態について図3を参照して説明する。まず、ポン
プ等の加圧供給手段(図示せず)によって洗濯排水1が
アスピレータ5に導入されると、その水流によって負圧
部が生じ、負圧部に連通する分岐管15に連結された凝
集剤タンク2及びエアフィルタ3から凝集剤溶液4及び
空気が洗濯排水1に混和される。尚、凝集剤溶液4の混
合量は、洗濯排水1の流量に応じて流量調整バルブ16
の開閉具合を加減することによって適切に調整できるよ
うになっている。
Next, a usage mode of the sewage purification apparatus having the above configuration will be described with reference to FIG. First, when the washing drainage 1 is introduced into the aspirator 5 by pressurizing and supplying means (not shown) such as a pump, a negative pressure portion is generated by the water flow, and coagulation is connected to the branch pipe 15 communicating with the negative pressure portion. The coagulant solution 4 and air are mixed into the washing drainage 1 from the agent tank 2 and the air filter 3. The mixing amount of the coagulant solution 4 depends on the flow rate of the washing drainage 1 and the flow control valve 16.
It can be adjusted appropriately by adjusting the opening / closing degree of.

【0042】このとき添加する凝集剤としては、一般的
に汚水の浄化処理に用いられる無機系のポリ塩化アルミ
ニウム、硫酸アルミニウム等を好適に使用でき、更に凝
集体粒子の粗大化を図るためには、例えば、ポリアクリ
ルアミド等の有機系の高分子凝集剤を使用するとよい。
本実施形態では、図示しない槽にて無機凝集剤を添加済
みの洗濯排水1をアスピレータ5内に圧送する。そし
て、凝集剤タンク2には高分子凝集剤溶液を準備してお
き、アスピレータ5の吸引作用によって洗濯排水1中に
空気と高分子凝集剤を混和させる。
As the coagulant to be added at this time, inorganic polyaluminum chloride, aluminum sulfate and the like generally used for purification treatment of sewage can be suitably used. For example, an organic polymer flocculant such as polyacrylamide may be used.
In the present embodiment, the washing wastewater 1 to which the inorganic coagulant has been added is pumped into the aspirator 5 in a tank (not shown). Then, a polymer coagulant solution is prepared in the coagulant tank 2, and the air and the polymer coagulant are mixed into the washing drainage 1 by the suction action of the aspirator 5.

【0043】凝集剤溶液4と空気が混合された洗濯排水
1aは、上述したように導入管17を経由して攪拌筒1
8内に導入され、攪拌室6の内壁に沿った旋回水流fを
作り、攪拌されながら攪拌室6内を上昇する。このと
き、洗濯排水1aは速やかに攪拌されるため、凝集剤の
働きと相俟って洗濯排水1a中の界面活性剤や洗濯物か
ら分離した汚れ成分等の汚染物質が凝集して数十〜数百
μmに粗大化した凝集体が形成される。このようにして
粗大化した凝集体を含む洗濯排水1bは入口部8aから
混合筒8内に流入し、螺旋状のスパイラルフィン7の表
面を伝って自然流下する。
The washing wastewater 1a in which the coagulant solution 4 and the air are mixed is supplied to the stirring tube 1 via the introduction pipe 17 as described above.
The swirling water flow f is introduced into the stirring chamber 8 along the inner wall of the stirring chamber 6 and rises inside the stirring chamber 6 while being stirred. At this time, since the washing wastewater 1a is rapidly stirred, contaminants such as a surfactant and a dirt component separated from the laundry in the washing wastewater 1a are aggregated together with the action of the coagulant, and several tens to Aggregates coarsened to several hundred μm are formed. The washing wastewater 1b containing the aggregates thus coarsened flows into the mixing cylinder 8 from the inlet 8a, and flows down the surface of the spiral spiral fin 7 naturally.

【0044】ところで、攪拌室6内で洗濯排水1aが旋
回攪拌される際、遠心力の作用で軽い空気は混合筒8の
外周面近傍に集中するが、混合筒8内を通過させること
で洗濯排水1b中の空気と凝集体が均一に混合されるた
め、混合筒8内では気泡を保持した凝集体粒子の粗大化
が促進される。
When the washing drainage 1a is swirled and stirred in the stirring chamber 6, light air is concentrated near the outer peripheral surface of the mixing cylinder 8 by the action of centrifugal force. Since the air and the aggregate in the waste water 1b are uniformly mixed, the coarsening of the aggregate particles holding the bubbles in the mixing cylinder 8 is promoted.

【0045】そして、混合筒8の出口部8bから凝集体
粒子を含む洗濯排水1cが排水捕集部10内に落下し、
ここに徐々に蓄えられていく。このとき、洗濯排水1c
は重力により噴流となって勢いよく滴下するので、その
まま洗濯排水1cから凝集体粒子をフィルタ等を用いて
分離しようとすると、せっかく粗大化された凝集体粒子
が噴流により砕けて再び細かい粒子となってしまう。そ
こで、排水捕集部10内で一旦洗濯排水1cを貯留し噴
流の勢いを緩衝させることで、粗大化させた凝集体粒子
が粉砕されることなくろ過部19まで導くことが可能と
なる。
Then, the washing drainage 1c containing the aggregated particles falls from the outlet 8b of the mixing cylinder 8 into the drainage collector 10,
It is gradually stored here. At this time, washing drainage 1c
Becomes a jet due to gravity and drops vigorously. If it is attempted to separate the aggregated particles from the washing wastewater 1c using a filter or the like, the aggregated particles that have become coarser are crushed by the jet and become fine particles again. Would. Therefore, by temporarily storing the washing wastewater 1c in the wastewater collecting unit 10 and buffering the flow of the jet, the coarsened aggregate particles can be guided to the filtering unit 19 without being crushed.

【0046】やがて、排水捕集部10内で満水近くまで
洗濯排水1cの水位が達すると、オーバーフローして排
出管28を通って、洗濯排水1dが廃棄凝集体23と共
にろ過部19内に導かれる。そして、廃棄凝集体23が
洗濯用ネット21でろ過・分離され、洗濯用ネット21
を通過することにより自然脱水された浄化水1eが脱水
かご20を経由して排水管22から外部に排水される。
When the water level of the washing drainage 1c reaches near full water in the drainage collecting part 10, the laundry drainage 1d overflows through the discharge pipe 28 and is guided into the filtering part 19 together with the waste aggregate 23. . Then, the waste aggregate 23 is filtered and separated by the washing net 21, and the washing net 21 is removed.
, The purified water 1e that has been naturally dehydrated is drained to the outside from the drain pipe 22 via the dehydrating basket 20.

【0047】洗濯用ネット21内に廃棄凝集体23があ
る程度溜まった場合は、クランプ26によるろ過部19
の係止を解除し、取り外したろ過部19から洗濯用ネッ
ト21を取り出せば、溜まった廃棄凝集体23を捨てら
れる。同時に、脱水かご20も取り外せるため、必要に
応じて洗濯用ネット21及び脱水かご20を洗浄するこ
とにより、脱水かご20を含むろ過部19の内部を衛生
状態を確保できる。
When the waste agglomerates 23 have accumulated in the washing net 21 to some extent, the filtration unit 19
Is released, and the washing net 21 is taken out from the removed filtration unit 19, and the accumulated waste aggregates 23 can be discarded. At the same time, since the dewatering basket 20 can also be removed, the inside of the filtration unit 19 including the dewatering basket 20 can be maintained in a sanitary state by washing the washing net 21 and the dewatering basket 20 as necessary.

【0048】尚、本発明の上記各実施形態では、汚水と
して洗濯排水を使用する場合について説明したが、食器
洗浄機からの排水等の家庭から出る生活排水でも同様の
効果が期待できることは勿論である。
In each of the above embodiments of the present invention, the case where washing wastewater is used as wastewater has been described. However, it is needless to say that the same effect can be expected with household wastewater such as wastewater from a dishwasher. is there.

【0049】[0049]

【発明の効果】以上説明したように本発明によると、界
面活性剤等の汚染物質を含む汚水に凝集剤を混和して粗
大化した凝集体粒子を捕集する汚水浄化装置において、
前記凝集剤の混和とともに前記汚水に空気を混合する手
段と、前記凝集体粒子及び前記空気を含む前記汚水を円
筒状の攪拌室の内部に該攪拌室の中心を通らない角度で
もって導入する手段と、前記攪拌室の内壁に沿って旋回
しながら上昇する前記汚水を吸い込んで前記凝集体粒子
に気泡を保持させる混合手段と、該混合手段から流出す
る前記汚水を一旦貯留する排水捕集手段とを有する構成
としたことにより、各手段を連結する配管が省略できる
ため、その分、汚水浄化装置自体のコンパクト化が図ら
れる。従って、家庭用の洗濯機等にもこの汚水浄化装置
を省スペースに搭載でき、効率よく大量の汚水を浄化し
てきれいな水を排水できる。
As described above, according to the present invention, there is provided a sewage purification apparatus which collects coarse aggregate particles by mixing a flocculant into a sewage containing a contaminant such as a surfactant.
Means for mixing air with the sewage together with mixing of the flocculant, and means for introducing the sewage containing the agglomerated particles and the air into a cylindrical stirring chamber at an angle which does not pass through the center of the stirring chamber. Mixing means for sucking the sewage rising while rotating along the inner wall of the stirring chamber to retain bubbles in the agglomerated particles, and wastewater collecting means for temporarily storing the sewage flowing out of the mixing means. With this configuration, the piping connecting each means can be omitted, and the wastewater purification device itself can be made more compact accordingly. Therefore, this sewage purification apparatus can be mounted in a small space in a home-use washing machine and the like, and a large amount of sewage can be efficiently purified and clean water can be drained.

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

【図1】 本発明の第1の実施形態に係る汚水浄化装
置の概略断面図である。
FIG. 1 is a schematic sectional view of a sewage purification device according to a first embodiment of the present invention.

【図2】 図1におけるx−x線断面図である。FIG. 2 is a sectional view taken along line xx in FIG.

【図3】 本発明の第2の実施形態に係る汚水浄化装
置の概略断面図である。
FIG. 3 is a schematic sectional view of a sewage purification apparatus according to a second embodiment of the present invention.

【図4】 従来の排水処理装置を示す概略図である。FIG. 4 is a schematic diagram showing a conventional wastewater treatment device.

【図5】 その排水処理装置の吸引器の正面図(A)
と縦断面図(B)である。
FIG. 5 is a front view of the suction device of the wastewater treatment device (A).
And a longitudinal sectional view (B).

【符号の説明】[Explanation of symbols]

1,1a,1b,1d 洗濯排水 1e 浄化水 2 凝集剤タンク 3 エアフィルタ 4 凝集剤溶液 5 アスピレータ 6 攪拌室 7 スパイラルフィン 8 混合筒 10 排水捕集部 15 分岐管 16 流量調整バルブ 18 攪拌筒 19 ろ過部 20 脱水かご 21 洗濯用ネット 22 排水管 23 廃棄凝集体 25 連結管 26 フック式クランプ 27 パッキン 28 排出管 1, 1a, 1b, 1d Laundry drainage 1e Purified water 2 Coagulant tank 3 Air filter 4 Coagulant solution 5 Aspirator 6 Stirring chamber 7 Spiral fin 8 Mixing cylinder 10 Drain collection unit 15 Branch pipe 16 Flow control valve 18 Stirring cylinder 19 Filtration unit 20 Dehydration basket 21 Laundry net 22 Drain pipe 23 Waste aggregate 25 Connecting pipe 26 Hook clamp 27 Packing 28 Discharge pipe

───────────────────────────────────────────────────── フロントページの続き (72)発明者 高木 真也 大阪府大阪市阿倍野区長池町22番22号 シ ャープ株式会社内 (72)発明者 池水 麦平 大阪府大阪市阿倍野区長池町22番22号 シ ャープ株式会社内 Fターム(参考) 4D037 AA12 AB02 AB16 BA01 BA06 BA07 BB03 BB04 BB07 BB08 BB09 CA02 CA08 4D062 BA19 BA22 BA29 BB09 BB12 CA07 DA04 DA05 DB02 DC02 DC06 EA03 EA08 EA33 FA02 FA16  ──────────────────────────────────────────────────続 き Continuing on the front page (72) Inventor Shinya Takagi 22-22, Nagaikecho, Abeno-ku, Osaka-shi, Osaka Inside Sharp Co., Ltd. (72) Inventor Muheidaira 22-22, Nagaikecho, Abeno-ku, Osaka-shi, Osaka 4D037 AA12 AB02 AB16 BA01 BA06 BA07 BB03 BB04 BB07 BB08 BB09 CA02 CA08 4D062 BA19 BA22 BA29 BB09 BB12 CA07 DA04 DA05 DB02 DC02 DC06 EA03 EA08 EA33 FA02 FA16

Claims (9)

【特許請求の範囲】[Claims] 【請求項1】 界面活性剤等の汚染物質を含む汚水に凝
集剤を混和して粗大化した凝集体粒子を捕集する汚水浄
化装置において、 前記凝集剤の混和とともに前記汚水に空気を混合する手
段と、前記凝集体粒子及び前記空気を含む前記汚水を円
筒状の攪拌室の内部に該攪拌室の中心を通らない角度で
もって導入する手段と、前記攪拌室の内壁に沿って旋回
しながら上昇する前記汚水を吸い込んで前記凝集体粒子
に気泡を保持させる混合手段と、該混合手段から流出す
る前記汚水を一旦貯留する排水捕集手段とを有すること
を特徴とする汚水浄化装置。
1. A sewage purification device for collecting flocculated particles which are made coarse by mixing a flocculant into a sewage containing a contaminant such as a surfactant, wherein air is mixed with the sewage together with mixing of the flocculant. A means for introducing the sewage containing the agglomerated particles and the air into the interior of the cylindrical stirring chamber at an angle that does not pass through the center of the stirring chamber; and while rotating along the inner wall of the stirring chamber. A sewage purification apparatus comprising: mixing means for sucking the rising sewage to retain bubbles in the aggregated particles; and drainage collecting means for temporarily storing the sewage flowing out of the mixing means.
【請求項2】 界面活性剤等の汚染物質を含む汚水に凝
集剤を混和して粗大化した凝集体粒子を捕集する汚水浄
化装置において、 前記凝集剤の混和とともに前記汚水に空気を混合する手
段と、前記凝集体粒子及び前記空気を含む前記汚水を円
筒状の攪拌室の内部に該攪拌室の水平断面に対して接線
方向になるように導入する手段と、前記攪拌室の内壁に
沿って旋回しながら上昇する前記汚水を上端の入口部か
ら吸い込んで前記凝集体粒子に気泡を保持させながら自
然流下させる混合手段と、該混合手段の下端の出口部か
ら流出する前記汚水を一旦貯留して前記凝集体粒子とと
もに上方の排出口から外部に排出する排水捕集手段とを
有することを特徴とする汚水浄化装置。
2. A sewage purifying apparatus for collecting flocculent particles which are made coarse by mixing a flocculant into a sewage water containing a contaminant such as a surfactant, and mixing air with the sewage together with the flocculant. Means, means for introducing the sewage containing the aggregated particles and the air into a cylindrical stirring chamber so as to be tangential to a horizontal cross section of the stirring chamber, and along an inner wall of the stirring chamber. A mixing means for sucking the sewage that rises while swirling from the inlet at the upper end and allowing the aggregated particles to flow naturally while holding bubbles, and temporarily storing the sewage flowing out from the outlet at the lower end of the mixing means. Wastewater purifying apparatus, further comprising a drainage collecting means for discharging the aggregated particles together with the aggregated particles from an upper discharge port to the outside.
【請求項3】 更に、前記排出口を介して前記排水捕集
手段と連通し前記汚水から前記凝集体粒子を分離・回収
するとともに、前記凝集体粒子が排除された浄化水を排
水するろ過部を設けたことを特徴とする請求項2に記載
の汚水浄化装置。
3. A filtration unit which communicates with the wastewater collecting means through the discharge port to separate and collect the aggregated particles from the wastewater and drain purified water from which the aggregated particles have been removed. The sewage purification apparatus according to claim 2, further comprising:
【請求項4】 前記攪拌室、前記排水捕集手段及び前記
ろ過部とを一体的に形成したことを特徴とする請求項2
又は請求項3に記載の汚水浄化装置。
4. The apparatus according to claim 2, wherein the stirring chamber, the wastewater collecting means, and the filtration unit are integrally formed.
Or the sewage purification device according to claim 3.
【請求項5】 前記汚水への前記凝集剤の混和及び前記
空気の混合を減圧吸引機構によって行うことを特徴とす
る請求項1〜請求項4のいずれかに記載の汚水浄化装
置。
5. The sewage purification apparatus according to claim 1, wherein the mixing of the coagulant into the sewage and the mixing of the air are performed by a reduced-pressure suction mechanism.
【請求項6】 前記混合手段の内部には、略正方形若し
くは略長方形をした板状部材の一対の向かい合う2辺の
なす角が所定の角度になるように捻られたものを直列に
連結したスパイラルフィンが配設されていることを特徴
とする請求項1〜請求項5のいずれかに記載の汚水浄化
装置。
6. A spiral in which a pair of substantially square or substantially rectangular plate-like members twisted so that an angle formed by a pair of opposite sides thereof becomes a predetermined angle is connected in series inside the mixing means. The sewage purification device according to any one of claims 1 to 5, wherein fins are provided.
【請求項7】 前記ろ過部における上記凝集体粒子の分
離・回収に洗濯用ネットを用いることを特徴とする請求
項3〜請求項6のいずれかに記載の汚水浄化装置。
7. The sewage purification apparatus according to claim 3, wherein a net for washing is used for separating and recovering the aggregated particles in the filtration section.
【請求項8】 前記凝集剤の混和とともに前記汚水に空
気を混合する手段から前記ろ過部に至る前記汚水の排水
経路の内壁の表面に非粘着加工を施したことを特徴とす
る請求項3〜請求項7のいずれかに記載の汚水浄化装
置。
8. A non-adhesive process is applied to a surface of an inner wall of a drainage path of the sewage from the means for mixing air to the sewage together with the mixing of the coagulant and the filtration section. The sewage purification device according to claim 7.
【請求項9】 前記排水捕集手段を前記攪拌室に対し着
脱自在に設けたことを特徴とする請求項1〜請求項8の
いずれかに記載の汚水浄化装置。
9. The sewage purification apparatus according to claim 1, wherein said drainage collecting means is provided detachably with respect to said stirring chamber.
JP2000172317A 2000-05-29 2000-06-08 Sewage purifying apparatus Pending JP2001347260A (en)

Priority Applications (5)

Application Number Priority Date Filing Date Title
JP2000172317A JP2001347260A (en) 2000-06-08 2000-06-08 Sewage purifying apparatus
US10/031,084 US6820446B2 (en) 2000-05-29 2001-05-28 Sewage disposal agent, sewage purifier, washing machine with purifier, and sewage purifying method
KR1020027001179A KR20020020800A (en) 2000-05-29 2001-05-28 Sewage disposal agent, sewage purifier, washing machine with purifier, and sewage purifying method
PCT/JP2001/004471 WO2001091879A1 (en) 2000-05-29 2001-05-28 Sewage disposal agent, sewage purifier, washing machine with purifier, and sewage purifying method
EP01934379A EP1291057A4 (en) 2000-05-29 2001-05-28 Sewage disposal agent, sewage purifier, washing machine with purifier, and sewage purifying method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000172317A JP2001347260A (en) 2000-06-08 2000-06-08 Sewage purifying apparatus

Publications (1)

Publication Number Publication Date
JP2001347260A true JP2001347260A (en) 2001-12-18

Family

ID=18674734

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2000172317A Pending JP2001347260A (en) 2000-05-29 2000-06-08 Sewage purifying apparatus

Country Status (1)

Country Link
JP (1) JP2001347260A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100798455B1 (en) 2007-10-18 2008-01-28 대지정공주식회사 Recycling devicd and method of wastewater for cleaning underground facilities
KR101134037B1 (en) 2004-06-24 2012-04-13 가부시키가이샤 미이케 텍코쇼 Apparatus for processing polluted water containing organic material

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101134037B1 (en) 2004-06-24 2012-04-13 가부시키가이샤 미이케 텍코쇼 Apparatus for processing polluted water containing organic material
KR100798455B1 (en) 2007-10-18 2008-01-28 대지정공주식회사 Recycling devicd and method of wastewater for cleaning underground facilities

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