JP3650571B2 - Drain purification device - Google Patents

Drain purification device Download PDF

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Publication number
JP3650571B2
JP3650571B2 JP2000199659A JP2000199659A JP3650571B2 JP 3650571 B2 JP3650571 B2 JP 3650571B2 JP 2000199659 A JP2000199659 A JP 2000199659A JP 2000199659 A JP2000199659 A JP 2000199659A JP 3650571 B2 JP3650571 B2 JP 3650571B2
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Japan
Prior art keywords
drain
tank
water
specific gravity
gravity difference
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JP2002011474A (en
Inventor
彰 沢井
哲也 稲生
隆一 巻渕
正人 板垣
公男 齋藤
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株式会社 日立インダストリイズ
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  • Removal Of Floating Material (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Physical Water Treatments (AREA)

Description

【0001】
【発明の属する技術分野】
本発明はドレン浄化装置に係り、特に、空気圧縮機より排出されるドレンから油を分離回収し、清浄な水を公共下水道に放出するのに好適なドレン浄化装置に関する。
【0002】
【従来の技術】
産業界で一般に広く使われている空気圧縮機では、圧縮のプロセスの中において空気中の水分が凝縮し、その水に圧縮機の潤滑油などが懸濁した状態となって混じり合ったドレンが排出される。
【0003】
大型の往復動式圧縮機や油冷式スクリュー圧縮機などはドレン中に含まれる油の濃度が高くなっており、このドレンを一般下水道に放出することは水質の汚濁・汚染の原因となり、水質汚濁防止法の排水基準(n−ヘキサン含有量5ppm以下)に違反することとなる。そこで、このドレン中の主な有害物質である油を水と分離して集めリサイクル・焼却などの処理を行い、清浄となった水(n−ヘキサン含有量5ppm以下)のみを一般下水道に放出することが必要となる。
【0004】
従来、水と油の比重差を利用した重力分離法が用いられている。
【0005】
重力分離においては、油の分離速度は油滴径の二乗に比例するため、浮上分離可能すなわち水と混合しないで遊離できる油滴径は60μm以上であり、油滴径は60μm以下の場合は乳化の状態となる。特に油滴径1〜5μmの場合は、殆ど浮上せず乳化の状態を維持し続ける。
【0006】
水中の油滴がごく小さい乳化油の場合の油水分離法として、電解浮上法(「排水処理技術 施設管理マニュアル −含油排水編−」 神奈川県環境部 昭和57-3-31 発行)がある。
【0007】
電解浮上法で油水分離を実行する従来の電解槽を、図4にて説明する。
空気圧縮機から排出されたドレンDは、電解槽1の下部より流入する。電解槽1内には複数対の正負の各電極2,3が対向配置され、電気分解することにより油分が凝集し、凝集した油分と発生した水素ガスなどが付着し、クリーム状のスカム4となって浮上する。
【0008】
浮上したスカム4は、スキーマ5により間欠的にスカム受け6に掻き出され、廃棄物7として定期的に排出(Ex)される。また、電気分解されたドレンDaは、新しく流入してくるドレンDに押されて、電解槽1から比重差分離槽8に入る。
【0009】
正極の電極金属としてアルミニウム合金を用いるが、その理由は電解で溶け出したアルミニウムイオンが乳化油を破壊し、油分を凝集する効果を持っていることにある。
【0010】
電解中に溶出したアルミニウムイオンはその後酸化アルミニウムとなり、油と分離させた水(電気分解されたドレンDa)と一緒に廃棄しては環境汚染となるので、水との比重差を利用して比重差分離槽8の底に酸化アルミニウムと油分が混合した浮遊物体(以下、SSと略記)9を沈殿させて排出(Ex)するようにしている。また、電解槽1の底部にもSS10が沈殿するので、比重差分離槽8のSS9とともに排出(Ex)し処分する。
【0011】
比重差分離槽8のドレン(水)Daは、比重差分離槽8の上部の設けた浄水取り込み口11から排出(Ex)され、後処理の吸着・フィルタ部を経て廃棄する。尚、負電極としては、ステンレススチールを用いることが多い。
【0012】
【発明が解決しようとする課題】
上記した従来装置の比重差分離槽8では比重差を利用して水と酸化アルミニウムを沈殿分離しているので、確実なる分離のためには時間が必要である。
そのために比重差分離槽8はU字型(逆サイホンの形)の空間構成とし一方の縦空間の上部で該電解槽から水を受けて該水から該電気分解の過程で溶け出す電極金属を下方に向かう流れに乗せて沈殿させ他方の縦空間の上部から水を排出させ、流路を長くすることにより比重差分離槽8での該水の滞留時間を持たせて凝集効果が出るようにしている。
【0013】
SSは、時間経過とともに槽底に堆積していく。しかしながら、処理すべきドレンD量が多い場合には、逆サイホンの形を取っているために浄水取り込み口11からの排出も多くなり、比重差分離槽8での流速が増し、滞留時間が短くなって比重差を利用した水との分離が不充分になるだけでなく、SSは水と比重が近いために、微細なものは水流で、浄水取り込み口11から排出され、後段の図示していない吸着・フィルタ部に至る分量が増加し、吸着・フィルタ部で目詰りを起こし、フィルタを交換しなければならない。
特に、小型化のために比重差分離槽8を小さくしていくと、槽底に堆積した微細なSSは流水で捲き上げられやすくなって、下流の、吸着・フィルタ部で目詰りを起こしやすくなる。
【0014】
それゆえ発明の目的は、比重差分離槽でも回収できない溶け出した電極金属や油分が混合したものを確実に分離・回収することができるドレン浄化装置を提供することにある。
【0015】
【課題を解決するための手段】
上記課題を解決する本発明ドレン浄化装置の特徴とするところは、内部にドレンを電気分解して油と水を分離させる少なくとも1対の正負各電極及び上部に該電気分解の過程で発生し浮上するスカムを排出するスキーマを備えた電解槽と、U字型の空間を有しその一方の縦空間の上部で該電解槽で油水分離された水を受けて該水から該電気分解の過程で溶け出す電極金属を沈殿させ他方の縦空間の上部から水を排出する比重差分離槽とを有するドレン浄化装置において、槽壁中段に該比重差分離槽から排出される水の流入口を有し該流入口より上部に槽内の水を排出する排出口を有する沈殿槽を設けたことにある。
【0016】
【発明の実施の形態】
図1は本発明の一実施形態になるドレン浄化装置の全体構成を示し、図2は図1の要部を拡大して示している。
尚、図4に示したものと同一物あるいは相当物には同一符号を用い、説明の重複を避ける。
【0017】
圧縮機21から排出されるドレンDは、ポンプ22により電解槽1に供給される。供給されたドレンDは電解槽1内において、直流電源23から電流が供給され電極2,3間で電気分解される。電気分解により分離浮上したスカム4はスキーマ5により電解槽1の外に掻き出され、スカム受け6を経て廃棄物7として定期的に排出される。分離後の油濃度の低くなったドレンDaは比重差分離槽8に入り、浄水取り込み口11から沈殿槽31を経てフィルタユニット41に導入される。
フィルタユニット41には油吸着剤が充填されており、残存する油分などを取り去り、浄化された水Wが排出される。
【0018】
次に、電解槽1と比重差分離槽8の構成を説明する。
電解槽1と比重差分離槽8の間の流路Pは両槽1,8の仕切板の上部中位置にある。浮上して電解槽1の液面に溜まったスカム4の下層部が流路Pの上部に到らない内に浮上したスカム4をスキーマ5で掻き出す。それで、電解槽1の液面に浮上したスカム4は比重差分離槽8の液面に広がらない。流路Pの断面は、ここでの流速がスカム4の浮上速度より遅くなるようなものとする。すると、浮上中のスカム4が比重差分離槽8に直接流れ込むことはなく、スカム4は比重差分離槽8の液面に広がらない。
【0019】
ポンプ22で電解槽1に供給するドレンDは、電解槽1の底部から浮いた位置に各正負電極2,3の下端部に対向するように直線状,十字状あるいは放射状に設けたパイプ26から均等に供給する。それで、パイプ26から電解槽1に吹き出るドレンDの流速は低下し、沈殿してくる酸化アルミニウム10は巻き上げられることなく、そのままパイプ26より下の電解槽1の槽底に沈降堆積していく。
【0020】
比重差分離槽8では、ドレンDaに含まれる油分は僅かで酸化アルミニウムと混合したSS9はその分量が従来装置よりも少なく槽底に沈降堆積する。
ドレン量Dが増えても、浄水取り込み口11から沈殿槽31に排出するドレンDbに含まれるSSの量は大幅に低下する。
【0021】
沈殿槽31は円筒形であり、図2に示すように、槽壁中段に比重差分離槽8から排出される水の流入口32を有し、流入口32より上部に槽内の水を排出する排出口33を有する。また、流入口と排出口33の間に排出口33に向う水流の障害になるじゃま板34を設けている。
【0022】
35は傾斜した槽底、36は槽底35の最低部に設けた排出管、37は排出管36に設けた閉止弁である。
【0023】
沈殿槽31では、流入口32が槽壁に横向に開口していて、流入するドレンDbは槽内を水平に流れる。閉止弁37は閉じられていて流入口32から槽底35に至る間のドレンDcに槽底35に向かうほど流れが消えて、謂わば、死水状態にある。そのため、流入したドレンDb中のSSは時間を掛けてゆっくり凝集沈降し、SS38として堆積する。
【0024】
沈殿槽31内での流れは、流入口32から上方に存在する排出口33に向かう上昇流になる。この流れが流入口32から直ちに発生すると排出口33から流出するSSが増加するから、上昇流に対し障害となるじゃま板34が下方に向かう流れを起こして、沈殿槽31内でのドレンDbの滞留時間を一層長くしている。
【0025】
一定量のSS38が貯まると、閉止弁37を開放してSSを除去するが、槽底35は排出管36に向って傾斜しているので、殆どのSSを回収することができる。
【0026】
本発明者等の実験によれば、n−ヘキサン含有量が50ppm程度のドレン原水について、図4の従来装置では吸着・フィルタ部の流入口においてn−ヘキサン含有量は5ppm以上であったが、図1に示す本発明装置ではフィルタユニット41の流入口においてn−ヘキサン含有量は2ppm程度、フィルタユニット41の流出口において1ppm以下であり、水質汚濁防止法の排水基準を充分満足できることを確認している。
【0027】
また、閉止弁37を通して取出したSSを含む排水の成分分析をしてみたところ、重量%で油分30%−酸化アルミニウム20%−残り水他であり、沈殿槽31でのSS凝集による油分分離効果も確かめられた。それで、フィルタユニット41における吸着剤交換の頻度は著しく低下し、ランニングコストの低減効果がある。
【0028】
図3は、図2に示した沈殿槽31の傾斜した槽底を比重差分離槽8に適用したものである。SS9の排出が確実であることのほかに、流れで巻き上げる微細なSSの量が減って、沈殿槽31に流出し難くなる。
【0029】
傾斜した槽底は、比重差分離槽8では流れの関係から図3のように下流に向かう片流れがよいが、沈殿槽31では漏斗状でも良いし、槽が箱型であれば、四角錘状などでも構わない。
【0030】
閉止弁の操作は、電磁弁としてタイマーを利用しての自動開閉でもよいし、手動開閉でも良い。
【0031】
【発明の効果】
以上説明したように本発明ドレン浄化装置によれば、比重差分離槽でも回収できない溶け出した電極金属や油分を確実に分離・回収することができる。
【図面の簡単な説明】
【図1】本発明の一実施形態になるドレン浄化装置の全体構成を示す図である。
【図2】図1のドレン浄化装置における沈殿槽の断面図である。
【図3】図1のドレン浄化装置における比重差分離槽の断面図である。
【図4】従来のドレン浄化装置における要部を拡大して示す図である。
【符号の説明】
D,Da〜Dc…ドレン
P…流路
1…電解槽
2,3…電極
4…スカム
5…スキーマ
8…比重差分離槽
9,10,38…溶け出した電極金属の酸化物や油分の混合物(SS)
11…浄水取り込み口
31…沈殿槽
32…流入口
33…排出口
34…じゃま板
8a,35…槽底
36…排出管
37…閉止弁
41…フィルタユニット
[0001]
BACKGROUND OF THE INVENTION
The present invention relates to a drain purification device, and more particularly, to a drain purification device suitable for separating and recovering oil from drain discharged from an air compressor and discharging clean water to a public sewer.
[0002]
[Prior art]
In air compressors that are widely used in the industry, moisture in the air is condensed during the compression process, and the lubricating oil of the compressor is suspended in the water and mixed with the drain. Discharged.
[0003]
Large reciprocating compressors and oil-cooled screw compressors, etc., have high oil concentrations in the drain, and releasing this drain into the general sewer causes water pollution and contamination. This would violate the wastewater standards of the Pollution Control Act (n-hexane content of 5 ppm or less). Therefore, the oil, which is the main harmful substance in the drain, is separated from water and collected, treated for recycling and incineration, and only purified water (with n-hexane content of 5 ppm or less) is discharged into the general sewer. It will be necessary.
[0004]
Conventionally, a gravity separation method using a specific gravity difference between water and oil has been used.
[0005]
In gravity separation, since the oil separation speed is proportional to the square of the oil droplet diameter, the oil droplet diameter that can be floated and separated, that is, can be released without mixing with water is 60 μm or more, and emulsification is performed when the oil droplet diameter is 60 μm or less. It becomes the state of. In particular, in the case of an oil droplet diameter of 1 to 5 μm, it hardly floats and maintains the emulsified state.
[0006]
As an oil-water separation method for emulsified oil with very small oil droplets in water, there is an electrolytic flotation method (“Wastewater Treatment Technology Facility Management Manual-Oil-Containing Drainage” published by Kanagawa Prefectural Environment Department, Showa 57-3-31).
[0007]
A conventional electrolytic cell that performs oil-water separation by the electrolytic levitation method will be described with reference to FIG.
The drain D discharged from the air compressor flows from the lower part of the electrolytic cell 1. A plurality of pairs of positive and negative electrodes 2, 3 are disposed opposite to each other in the electrolytic cell 1, and oil components are aggregated by electrolysis, and the aggregated oil components and generated hydrogen gas adhere to the cream-like scum 4. And emerge.
[0008]
The floating scum 4 is scraped intermittently to the scum receiver 6 by the schema 5 and is periodically discharged (Ex) as waste 7. Further, the electrolyzed drain Da is pushed by the newly flowing drain D and enters the specific gravity difference separation tank 8 from the electrolytic cell 1.
[0009]
An aluminum alloy is used as the electrode metal of the positive electrode because the aluminum ions dissolved by electrolysis have the effect of destroying the emulsified oil and aggregating the oil.
[0010]
Aluminum ions eluted during electrolysis then become aluminum oxide, and if discarded together with oil separated from water (electrolyzed drain Da), it becomes environmental pollution. A floating object (hereinafter abbreviated as SS) 9 in which aluminum oxide and oil are mixed is precipitated at the bottom of the difference separation tank 8 and discharged (Ex). Moreover, since SS10 also precipitates at the bottom of the electrolytic cell 1, it is discharged (Ex) together with SS9 in the specific gravity difference separation tank 8 and disposed.
[0011]
The drain (water) Da in the specific gravity difference separation tank 8 is discharged (Ex) from the purified water intake port 11 provided at the upper part of the specific gravity difference separation tank 8, and is discarded through a post-treatment adsorption / filter unit. Stainless steel is often used as the negative electrode.
[0012]
[Problems to be solved by the invention]
In the specific gravity difference separation tank 8 of the above-described conventional apparatus, water and aluminum oxide are precipitated and separated using the specific gravity difference, so that time is required for reliable separation.
For this purpose, the specific gravity difference separation tank 8 has a U-shaped (reverse siphon-shaped) space configuration, and receives electrode metal from the electrolytic cell at the upper part of one vertical space and dissolves electrode metal that melts from the water during the electrolysis process. The water is drained from the upper part of the other vertical space by being deposited on the downward flow, and the flow path is lengthened so that the residence time of the water in the specific gravity difference separation tank 8 is given so that the coagulation effect is produced. ing.
[0013]
SS accumulates on the bottom of the tank over time. However, when the amount of the drain D to be processed is large, since it takes the shape of a reverse siphon, discharge from the clean water intake port 11 increases, the flow velocity in the specific gravity difference separation tank 8 increases, and the residence time is short. Not only is the separation from water using the specific gravity difference insufficient, but SS has a specific gravity close to that of water, so the fine one is a water stream and is discharged from the clean water intake port 11 and is shown in the subsequent figure. The amount to reach the suction / filter section increases, the suction / filter section becomes clogged, and the filter must be replaced.
In particular, if the specific gravity difference separation tank 8 is made smaller for miniaturization, the fine SS deposited on the bottom of the tank is easily sprinkled with running water, and is likely to be clogged in the adsorption / filter section downstream. Become.
[0014]
Therefore, an object of the present invention is to provide a drain purifying apparatus capable of reliably separating and recovering a mixture of dissolved electrode metal and oil that cannot be recovered even in a specific gravity difference separation tank.
[0015]
[Means for Solving the Problems]
A feature of the drain purification apparatus of the present invention that solves the above-described problem is that at least a pair of positive and negative electrodes that electrolyze the drain to separate oil and water and float on the top during the electrolysis process An electrolyzer having a schema for discharging scum and a U-shaped space, and water separated in the electrolyzer at the top of one of the vertical spaces is received in the process of electrolysis from the water. In the drain purification device having a specific gravity difference separation tank for precipitating the electrode metal to be melted and discharging water from the upper part of the other vertical space, the drain wall has an inlet for water discharged from the specific gravity difference separation tank in the middle of the tank wall. A precipitation tank having a discharge port for discharging water in the tank is provided above the inlet.
[0016]
DETAILED DESCRIPTION OF THE INVENTION
FIG. 1 shows an overall configuration of a drain purifying apparatus according to an embodiment of the present invention, and FIG. 2 shows an enlarged main part of FIG.
In addition, the same code | symbol is used for the same thing as what was shown in FIG. 4, or an equivalent thing, and duplication of description is avoided.
[0017]
The drain D discharged from the compressor 21 is supplied to the electrolytic cell 1 by the pump 22. The supplied drain D is electrolyzed between the electrodes 2 and 3 by supplying a current from the DC power source 23 in the electrolytic cell 1. The scum 4 separated and levitated by electrolysis is scraped out of the electrolytic cell 1 by the schema 5 and is periodically discharged as waste 7 through the scum receiver 6. The drain Da having a low oil concentration after separation enters the specific gravity difference separation tank 8 and is introduced into the filter unit 41 from the purified water intake port 11 through the precipitation tank 31.
The filter unit 41 is filled with an oil adsorbent, and the remaining oil is removed and the purified water W is discharged.
[0018]
Next, the structure of the electrolytic cell 1 and the specific gravity difference separation tank 8 will be described.
The flow path P between the electrolytic cell 1 and the specific gravity difference separation tank 8 is located at the upper middle position of the partition plates of both tanks 1 and 8. The scum 4 that floats up while the lower layer of the scum 4 that floats and accumulates on the liquid surface of the electrolytic cell 1 does not reach the upper part of the flow path P is scraped out by the schema 5. Therefore, the scum 4 that has floated to the liquid surface of the electrolytic cell 1 does not spread to the liquid surface of the specific gravity difference separation tank 8. The cross section of the flow path P is such that the flow velocity here is slower than the flying speed of the scum 4. Then, the floating scum 4 does not flow directly into the specific gravity difference separation tank 8, and the scum 4 does not spread over the liquid surface of the specific gravity difference separation tank 8.
[0019]
The drain D supplied to the electrolytic cell 1 by the pump 22 is from a pipe 26 provided in a linear shape, a cross shape, or a radial shape so as to face the lower ends of the positive and negative electrodes 2 and 3 at a position floating from the bottom of the electrolytic cell 1. Supply evenly. Accordingly, the flow rate of the drain D that blows out from the pipe 26 to the electrolytic cell 1 is reduced, and the precipitated aluminum oxide 10 is settled and deposited on the bottom of the electrolytic cell 1 below the pipe 26 without being rolled up.
[0020]
In the specific gravity difference separation tank 8, the amount of oil contained in the drain Da is small, and the amount of SS9 mixed with aluminum oxide is less than that of the conventional apparatus and settles on the tank bottom.
Even if the drain amount D increases, the amount of SS contained in the drain Db discharged from the clean water intake port 11 to the settling tank 31 is significantly reduced.
[0021]
As shown in FIG. 2, the sedimentation tank 31 has an inlet 32 for water discharged from the specific gravity difference separation tank 8 in the middle of the tank wall, and discharges water in the tank above the inlet 32. A discharge port 33 is provided. Further, a baffle plate 34 is provided between the inlet and the outlet 33 to obstruct the water flow toward the outlet 33.
[0022]
Reference numeral 35 denotes an inclined tank bottom, 36 denotes a discharge pipe provided at the lowest part of the tank bottom 35, and 37 denotes a closing valve provided on the discharge pipe 36.
[0023]
In the sedimentation tank 31, the inflow port 32 opens laterally in the tank wall, and the drain Db that flows in flows horizontally in the tank. The shut-off valve 37 is closed and the flow disappears toward the drain bottom Dc between the inlet 32 and the tank bottom 35 as it goes to the tank bottom 35, so to speak, it is in a so-called dead water state. For this reason, the SS in the drained drain Db slowly aggregates and settles over time and accumulates as SS38.
[0024]
The flow in the settling tank 31 becomes an upward flow from the inflow port 32 toward the discharge port 33 existing above. If this flow is generated immediately from the inlet 32, the SS flowing out from the outlet 33 increases, so that the baffle plate 34 that becomes an obstacle to the upward flow causes a downward flow, and the drain Db in the sedimentation tank 31 flows. The residence time is further increased.
[0025]
When a certain amount of SS 38 is accumulated, the shut-off valve 37 is opened to remove SS, but since the tank bottom 35 is inclined toward the discharge pipe 36, most of the SS can be recovered.
[0026]
According to the experiments by the present inventors, about the raw drain water having an n-hexane content of about 50 ppm, the n-hexane content was 5 ppm or more at the inlet of the adsorption / filter unit in the conventional apparatus of FIG. In the apparatus of the present invention shown in FIG. 1, the n-hexane content is about 2 ppm at the inlet of the filter unit 41 and 1 ppm or less at the outlet of the filter unit 41, and it is confirmed that the drainage standard of the water pollution control method can be sufficiently satisfied. ing.
[0027]
Moreover, when the component analysis of the wastewater containing SS taken out through the shut-off valve 37 was performed, the oil content was 30% by weight, the aluminum oxide was 20%, the remaining water, and the like. Was also confirmed. Therefore, the frequency of adsorbent replacement in the filter unit 41 is remarkably reduced, and there is an effect of reducing running costs.
[0028]
FIG. 3 shows a case where the inclined tank bottom of the settling tank 31 shown in FIG. In addition to the reliable discharge of SS9, the amount of fine SS wound up by the flow is reduced and it is difficult to flow out into the sedimentation tank 31.
[0029]
In the specific gravity difference separation tank 8, the inclined tank bottom is good in a single flow going downstream as shown in FIG. 3, but in the sedimentation tank 31, a funnel shape may be used. It doesn't matter.
[0030]
The operation of the shut-off valve may be automatic opening / closing using a timer as an electromagnetic valve or manual opening / closing.
[0031]
【The invention's effect】
As described above, according to the drain purification device of the present invention, it is possible to reliably separate and recover the dissolved electrode metal and oil that cannot be recovered even in the specific gravity difference separation tank.
[Brief description of the drawings]
FIG. 1 is a diagram showing an overall configuration of a drain purification apparatus according to an embodiment of the present invention.
2 is a cross-sectional view of a sedimentation tank in the drain purification device of FIG.
FIG. 3 is a cross-sectional view of a specific gravity difference separation tank in the drain purification device of FIG. 1;
FIG. 4 is an enlarged view showing a main part of a conventional drain purification device.
[Explanation of symbols]
D, Da to Dc ... Drain P ... Flow path 1 ... Electrolytic cell 2, 3 ... Electrode 4 ... Scum 5 ... Schema 8 ... Specific gravity difference separation tank 9, 10, 38 ... Melted electrode metal oxide and oil mixture (SS)
DESCRIPTION OF SYMBOLS 11 ... Purified water intake port 31 ... Precipitation tank 32 ... Inlet port 33 ... Discharge port 34 ... Baffle plate 8a, 35 ... Tank bottom 36 ... Drain pipe 37 ... Shut-off valve 41 ... Filter unit

Claims (4)

内部にドレンを電気分解して油と水を分離させる少なくとも1対の正負各電極及び上部に該電気分解の過程で発生し浮上するスカムを排出するスキーマを備えた電解槽と、U字型の空間を有しその一方の縦空間の上部で該電解槽で油水分離された水を受けて該水から該電気分解の過程で溶け出す電極金属を沈殿させ他方の縦空間の上部から水を排出する比重差分離槽とを有するドレン浄化装置において、
槽壁中段に該比重差分離槽から排出される水の流入口を有し該流入口より上部に槽内の水を排出する排出口を有する沈殿槽を設けたことを特徴とするドレン浄化装置。
An electrolyzer having at least one pair of positive and negative electrodes for electrolyzing the drain to separate oil and water, and a schema for discharging a scum generated and floated in the upper part of the electrolysis process; It has a space and receives the water separated in the electrolytic cell at the upper part of one vertical space, precipitates the electrode metal that melts from the water during the electrolysis process, and discharges the water from the upper part of the other vertical space. In a drain purification device having a specific gravity difference separation tank
A drain purification apparatus comprising a precipitation tank having an inlet for discharging water from the specific gravity difference separation tank in a middle stage of the tank wall and having an outlet for discharging water in the tank above the inlet. .
上記請求項1において、該沈殿槽はその流入口と排出口の間に該排出口に向う水流の障害になるじゃま板を備えていることを特徴とするドレン浄化装置。2. The drain purifier according to claim 1, wherein the settling tank is provided with a baffle plate between the inlet and the outlet, which obstructs the water flow toward the outlet. 上記請求項1において、該比重差分離槽または沈殿槽の槽底に閉止弁を有する排出管が連通しており、該槽底は該排出管に向って傾斜を有することを特徴とするドレン浄化装置。2. A drain purifier according to claim 1, wherein a discharge pipe having a shut-off valve communicates with the bottom of the specific gravity difference separation tank or the settling tank, and the tank bottom has an inclination toward the discharge pipe. apparatus. 上記請求項3において、該比重差分離槽における該排出管は他方の縦空間の下部に連通していることを特徴とするドレン浄化装置。4. The drain purifier according to claim 3, wherein the discharge pipe in the specific gravity difference separation tank communicates with a lower portion of the other vertical space.
JP2000199659A 2000-06-30 2000-06-30 Drain purification device Expired - Fee Related JP3650571B2 (en)

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