JPH0248091A - Waste water treating device - Google Patents

Waste water treating device

Info

Publication number
JPH0248091A
JPH0248091A JP19873688A JP19873688A JPH0248091A JP H0248091 A JPH0248091 A JP H0248091A JP 19873688 A JP19873688 A JP 19873688A JP 19873688 A JP19873688 A JP 19873688A JP H0248091 A JPH0248091 A JP H0248091A
Authority
JP
Japan
Prior art keywords
foam
air
water
flocs
septic tank
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP19873688A
Other languages
Japanese (ja)
Other versions
JP2558150B2 (en
Inventor
Kimifumi Miyao
宮尾 公文
Takeyuki Nagai
健之 永井
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.)
MK Seiko Co Ltd
Original Assignee
MK Seiko Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by MK Seiko Co Ltd filed Critical MK Seiko Co Ltd
Priority to JP63198736A priority Critical patent/JP2558150B2/en
Publication of JPH0248091A publication Critical patent/JPH0248091A/en
Application granted granted Critical
Publication of JP2558150B2 publication Critical patent/JP2558150B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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

Abstract

PURPOSE:To efficiently remove the flocs suspending in waste water to the outside of a cleaning tank by cascade-varying the amt. of the foam to be supplied into the waste water. CONSTITUTION:The compressed air supplied from an air compressor 5 is regulated by a regulator R1 to a desired air pressure. The air is connected to an air diffusion pipe 4 via a regulator R2 which reduces the pressure thereof and two pipelines; a pipeline 15 having a solenoid valve SV 1 and a pipeline 16 having a solenoid valve SV 2. The air reduced in pressure is, therefore, supplied to the air diffusion pipe 4 if the SV 1 is opened and the SV 2 is opened. The air of the desired pressure is supplied when the SV 2 is opened in this state. The more foam is generated when the air pressure is high than when the air pressure is low in this way. The switching of the amt. of the foam to be generated to two stages is possible by controlling the SV 1 and the SV 2.

Description

【発明の詳細な説明】 [産業上の利用分野1 本発明は主に洗車場から出る洗車排水を再利用可能な状
態までに浄化する排水処理装置に関する。
DETAILED DESCRIPTION OF THE INVENTION [Industrial Application Field 1] The present invention mainly relates to a wastewater treatment device for purifying car wash wastewater discharged from a car wash to a state where it can be reused.

[従来の問題点] 高圧スプレータイプの洗車機を備えるコイン洗車場や、
門形洗車機を備えるサービスステーションにおいては多
量の水を使用するものであり、夏期の水不足対処やラン
ニングコスト軽減の為に洗車排水を再利用可能状態まで
浄化する排水処理装置が従来よりある。
[Conventional problems] Coin-operated car washes equipped with high-pressure spray type car wash machines,
Service stations equipped with gate-type car wash machines use a large amount of water, and in order to deal with water shortages in the summer and reduce running costs, there have been conventional wastewater treatment devices that purify car wash wastewater to a state where it can be reused.

ところでこれらの装置は、排水を浄化槽に一度貯え浄化
処理して別タンクに送った後、再び浄化桁分だけ浄化処
理を行なういわゆるパンチ式によるものが主流を占めで
いる。しかしながら従来の装置は、−回の処理に要する
時間が比較的長く、その為−度に複数の洗車装置が稼動
した時や、連続して洗車が行なわれたような場合は浄化
処理が間に合わなくなるという問題点があった。
By the way, most of these devices are of the so-called punch type, in which wastewater is once stored in a septic tank, purified, sent to another tank, and then purified again by the amount of purification. However, with conventional equipment, the time required for each process is relatively long, so when multiple car wash machines are operated at the same time or when cars are washed consecutively, the purification process cannot be completed in time. There was a problem.

[発明の目的1 本発明は上記問題点に対処し、排水浄化処理時間を短縮
することを目的とするものであり、凝集薬品にて洗車排
水中に析出した懸濁物質のフロックを微細泡沫に付着さ
せて浮上除去する際に、排水中に供給する泡沫量(供給
空気圧)を段続もしくは数段階に可変し、排水中に浮遊
するフロックを効率よく浄化槽外に除去することを特徴
とするものである。
[Objective of the Invention 1] The present invention aims to address the above-mentioned problems and shorten the time for wastewater purification treatment, by using a flocculating chemical to turn flocs of suspended solids precipitated in car wash wastewater into fine foam. The flocs floating in the wastewater are efficiently removed from the septic tank by varying the amount of foam (supplied air pressure) supplied into the wastewater in a series or several stages when the flocs are attached and removed by flotation. It is.

[発明の実施例1 以下図面を基に本考案実施例について詳細に説明する。[Embodiment 1 of the invention Embodiments of the present invention will be described in detail below with reference to the drawings.

第1図は本発明実施例に関わる排水処理装置のシステム
説明図である。1は洗車場などから排水される洗車排水
を一箇所に集め一時貯留する排水ビット、2は該排水を
ポンプで汲み上げ更に貯留する二次貯留槽である。該二
次貯留槽は互いに連通する複数槽から成り、排水中に含
まれる砂・塵埃といった不純物質を沈澱させ、排水をあ
る程度浄化する役割りを持つ。3は散気管4を備え、底
部を漏斗形状とする排水浄化槽である。前記散気管4は
コンプレッサ5に接続され、微細気泡を槽内に供給する
。6は浄化処理時に排水に凝集薬液を添加する凝集薬液
添加装置で、14は前記散気管からの泡沫発生量および
凝集薬液添加装置を制御する制御装置、7は浄化槽3を
包囲する外槽である。従って浄化処理時には排水中に形
成されるフロックを、散気管4より発生する泡沫で浮上
させ、排水水面に滞積するフロックと共に外槽にオーバ
ーフローさせる。8は浄化槽より圧送される処理水中に
含まれる残留70ンクを濾過するフィルター装置で、9
は処理水給口、10は清水給口、11は処理水及び清水
を貯える貯水槽である。]2は前記二次貯留槽2底部に
沈殿する不純物質や、浄化処理時に外槽7で受けるフロ
ック、及び浄化槽底部に堆積する不純物質を受けるフロ
ック脱水槽で、ここで摘出する水分は前記排水ピントに
戻される。
FIG. 1 is a system explanatory diagram of a wastewater treatment apparatus according to an embodiment of the present invention. Reference numeral 1 designates a drainage bit that collects and temporarily stores car wash wastewater discharged from a car wash, etc., and 2 designates a secondary storage tank that pumps up the wastewater with a pump and further stores it. The secondary storage tank is composed of a plurality of tanks communicating with each other, and has the role of precipitating impurities such as sand and dust contained in the wastewater and purifying the wastewater to some extent. 3 is a wastewater septic tank equipped with an aeration pipe 4 and having a funnel-shaped bottom. The air diffuser pipe 4 is connected to a compressor 5 and supplies fine bubbles into the tank. Reference numeral 6 denotes a flocculating chemical solution addition device that adds a flocculating chemical solution to wastewater during purification treatment, 14 a control device that controls the amount of foam generated from the aeration pipe and the flocculating chemical solution addition device, and 7 an outer tank that surrounds the septic tank 3. . Therefore, during the purification process, the flocs formed in the wastewater are floated by the foam generated from the aeration pipe 4, and are caused to overflow into the outer tank together with the flocs accumulated on the surface of the wastewater. 8 is a filter device that filters the remaining 70 ton of water contained in the treated water that is pumped from the septic tank;
10 is a treated water supply port, 10 is a fresh water supply port, and 11 is a water tank for storing treated water and fresh water. ] 2 is a floc dehydration tank which receives impurities precipitated at the bottom of the secondary storage tank 2, flocs received in the outer tank 7 during purification treatment, and impurities deposited at the bottom of the septic tank. brought back into focus.

なお、以上のシステム構成による排水浄化処理は、連続
的に行なわれるものではなく、浄化槽3を満水にしたら
一度排水の注水を止め、浄化を行なった後再び排水を注
水するというように、浄化槽の容量単位で不連続的にパ
ンチ処理し、その都度処理水を貯水槽に送水するもので
ある。
Note that the wastewater purification treatment with the above system configuration is not carried out continuously, but once the septic tank 3 is filled with water, the injection of wastewater is stopped, and after purification, the wastewater is injected again. Punch processing is performed discontinuously in units of capacity, and treated water is sent to a water tank each time.

次に以上の構成において行なわれる排水浄化処理の流れ
を$2図を基に説明する。
Next, the flow of the waste water purification process performed in the above configuration will be explained based on the $2 chart.

まず前記二次貯留[2に貯えられる洗車排水を浄化槽3
に規定量注水したら■、前記凝集薬液添加装置6にて、
排水中の懸濁物質をフロック状に固める凝集薬液を添加
し攪拌する■。この凝集薬液は、アニオン界面活性材等
を成分とする凝集助剤と、水道用硫酸バンド等を成分と
する凝集剤と、ノニオン界面活性材等を成分とする高分
子凝集剤との3液から成り、これらの添加順序と攪拌時
間を次の第1表に示す。
First, the car wash wastewater stored in the secondary storage [2] is transferred to the septic tank 3.
After pouring a specified amount of water into
Add a flocculating chemical solution that solidifies suspended solids in the wastewater into a floc-like form and stir ■. This flocculant solution is made up of three liquids: a flocculating aid containing an anionic surfactant, a flocculant containing tap water sulfuric acid, etc., and a polymer flocculant containing a nonionic surfactant, etc. The order of addition and stirring time are shown in Table 1 below.

第1表 初めに凝集助剤を添加し、それと同時に前記散気管4よ
り泡沫を30秒flll連続して発生させ、浄化槽内排
水の攪拌を行なう。その後泡沫の発生をストップして3
0秒間放置した後、凝集剤を添加して上記同様に攪拌9
0秒、放置30秒を実施する。そして最後に高分子凝集
剤を添加して60秒間攪押し、凝集薬液の添加を終了す
る。この3液目の高分子凝集剤を添加した時点で排水中
懸濁質の凝集化が始まり、その凝集粒子が水中で相互に
衝突を繰り返して集塊を大幅に進行させフロックとして
析出し始め、高分子凝集剤添加後の放置時間15分の間
にほぼ完全に成長して、透明な処理水中に70ンクが浮
遊した状態になる。このようにして凝集薬液添加及び攪
拌を行ない、次に浮遊しているフロックを除去すべく泡
沫処理を行なう■。この泡沫処理は前記散気管4からフ
ロックを含む処理水中に泡沫を発生させることにより行
なわれるもので、浄化槽底部に位置する散気管より発生
した微細泡沫が、水中に浮遊するフロックに付着してそ
のままフロックを水面に浮トさせると共に、処理水中に
含まれる洗剤成分を発泡させで、水面に滞積するフロッ
クを浄化槽外に排出するよう作用する。
At the beginning of Table 1, a coagulation aid is added, and at the same time, bubbles are continuously generated from the aeration pipe 4 for 30 seconds to stir the wastewater in the septic tank. After that, stop the generation of foam and
After leaving for 0 seconds, add the flocculant and stir in the same manner as above 9
0 seconds and leave for 30 seconds. Finally, a polymer flocculant is added and stirred for 60 seconds to complete the addition of the flocculant solution. When this third liquid polymer flocculant is added, the suspended solids in the wastewater begin to flocculate, and the flocculated particles repeatedly collide with each other in the water, significantly progressing agglomeration, and begin to precipitate as flocs. During the 15 minutes of standing time after addition of the polymer flocculant, almost complete growth occurs, leaving 70 inks floating in the transparent treated water. In this way, the flocculating chemical solution is added and stirred, and then foam treatment is performed to remove floating flocs. This foam treatment is carried out by generating foam in the treated water containing flocs from the aeration tube 4. The fine bubbles generated from the aeration tube located at the bottom of the septic tank adhere to the flocs floating in the water and remain as they are. It causes the flocs to float on the water surface, foams the detergent components contained in the treated water, and discharges the flocs accumulated on the water surface out of the septic tank.

こうして処理水中の浮遊フロックを除去したら、前記貯
水槽11にその処理水を圧送し■、一連の排水浄化処理
サイクルを終了する。
After the floating flocs in the treated water are removed in this way, the treated water is pumped to the water storage tank 11 (1), and a series of wastewater purification treatment cycles are completed.

次に泡沫処理について更に詳しく説明する。上記泡沫処
理において、浄化槽内に供給する泡沫量は2段階に調節
できるものとしでいる。第4図のエアー配管図に示すよ
うに、エアーコンプレンサ5から供給される圧縮空気は
まずレギュレータ旧で4Kgf/cm2の空気圧に調整
される。そしてその後は更に空気圧をIKgf/cm2
に減圧するレギュレータR2と電磁弁SVIを備える管
路15と、電磁弁SV2を備える管路16との2管路を
介して散気管4に接続される。従ってSVIを開弁しS
V2を閉弁すれば、散気管4にはIK)(f/cm2の
圧力で空気が供給され、その状態でSV2を開弁すれば
散気管4には4Kgf/cm2の圧力で空気が供給され
ることになる。このとき散気管から噴出する泡沫量を比
べると、空気圧の高い時の方が低い時よりも当然多くの
泡沫を発生するので、SVIとSV2を制御することで
泡沫発生量を強弱の2段階と発生停止状態を自在に切換
えることが可能である。この強弱2段階の泡沫発生状態
を示したのが13図である。(a)は]Kgf/cm2
の圧力をかけた状態つまり弱状態である。このように発
生する泡沫量が少ないと、処理水を攪拌する効果は少な
いが、微細泡沫が処理水中にまんべんなく広がり浮上し
た泡は水面全体を覆う。このような状態においては、処
理水中に浮遊するフロックが泡沫に付着し易く、また水
面の乱れが少ないので浮−ヒしたフロックの塊が破壊さ
れることなく、層状に滞積しやすいものである。一方4
KHf/cm”の圧力をかけた状態を示すのが(b)で
ある。この時泡沫は多量に勢いよく発生するので、水面
中央部を山状に押し上げてから浄化槽壁に向かって下降
するように水流を形成し、従って泡沫は中火がら涌き出
で周囲に流れ、浄化槽壁に水流が衝突したところでまた
新たに形成される泡と共に外観上浄化槽内壁に沿って泡
沫が集まっているように確認される。つまり、このこと
は泡沫に付着したフロックも周囲の浄化槽壁に押し流さ
れるということであり、従って中央から周囲に流される
激しい水流で時間を迫って成長する泡沫と共にフロック
が浄化槽外にオーバーフローすることになる。
Next, foam processing will be explained in more detail. In the above foam treatment, the amount of foam supplied into the septic tank can be adjusted in two stages. As shown in the air piping diagram of FIG. 4, compressed air supplied from the air compressor 5 is first adjusted to an air pressure of 4 Kgf/cm2 by a regulator. After that, further increase the air pressure to IKgf/cm2.
It is connected to the diffuser pipe 4 through two pipes: a pipe 15 including a regulator R2 and a solenoid valve SVI, and a pipe 16 including a solenoid valve SV2. Therefore, SVI is opened and S
If V2 is closed, air is supplied to the diffuser pipe 4 at a pressure of IK) (f/cm2, and if SV2 is opened in that state, air is supplied to the diffuser pipe 4 at a pressure of 4Kgf/cm2. At this time, when comparing the amount of foam ejected from the air diffuser pipe, it is obvious that more foam is generated when the air pressure is high than when it is low, so by controlling SVI and SV2, the amount of foam generated can be reduced. It is possible to freely switch between two strong and weak stages and a state where foam generation is stopped.Figure 13 shows the two strong and weak foam generation states.(a) is ]Kgf/cm2
This is the state where the pressure is applied, that is, the weak state. When the amount of foam generated is small in this way, the effect of stirring the treated water is small, but the fine foam spreads evenly in the treated water and the bubbles that float to the surface cover the entire water surface. Under these conditions, the flocs floating in the treated water tend to adhere to the foam, and since there is little turbulence on the water surface, the floating flocs tend to accumulate in layers without being destroyed. . On the other hand 4
(b) shows the state in which a pressure of KHf/cm" is applied. At this time, a large amount of foam is generated with great force, so it pushes up the center of the water surface in a mountain shape and then descends toward the septic tank wall. A water stream is formed, and the foam flows around the area from the medium heat, and when the water stream collides with the septic tank wall, new bubbles are formed and the foam appears to be gathering along the inner wall of the septic tank. In other words, this means that the flocs attached to the foam are also washed away to the surrounding walls of the septic tank, and therefore, the flocs overflow out of the septic tank along with the foam that grows over time due to the strong water flow flowing from the center to the periphery. I will do it.

泡沫処理の行程はこのように泡沫噴出量を強・弱・停止
3段階の組み合わせとするものであり、次の第2表にそ
の組み合わせの一例を示す。
The foam treatment process thus sets the foam ejection amount in three stages: strong, weak, and stopped, and Table 2 below shows an example of the combinations.

第2表 上表に示したようにまず弱で泡沫処理工程をスタートし
、最初に処理水中に微細泡沫をまんべんなく発生させ、
水面全体を浮上した泡沫で覆う状態にする。このことに
より処理水中に多量に浮遊するフロックが泡沫と共に浮
上し、水面」二に泡に付着しで滞積することになる。そ
してその後短時間(30秒)停止時間をおき、浮上しき
らない泡沫が完全に浮上するのを待ち、フロックが水面
上に集まるのを待つ。この停止時間が過ぎると、−転し
て今度は強で泡沫を発生させる。すると浄化槽内には前
記したような水流が発生し、それまで水面上で泡沫と共
に静かに滞積していたフロックが、強い水流変化で次々
に成長する泡に押し上げられ浄化槽外にオーバーフロー
する。この時に処理水中に浮遊しているフロックを、泡
沫に付着させて浮上させる作用をなすことはもちろん、
前記凝集薬液では除去できず処理水中に残留している洗
剤成分を発泡させて槽外に除去することも行なう。
As shown in the upper table of Table 2, first start the foam treatment process at low temperature, first generate fine foam evenly in the treated water,
The entire surface of the water is covered with floating foam. As a result, a large amount of flocs floating in the treated water rises to the surface together with the foam, adheres to the foam and accumulates on the water surface. Thereafter, there is a short pause (30 seconds), and the bubbles that have not surfaced completely rise to the surface, and the flocs gather on the water surface. After this stopping time has passed, it is turned back to high and generates foam. Then, the above-mentioned water flow is generated in the septic tank, and the flocs that had been quietly accumulating on the water surface along with the foam are pushed up by the bubbles that grow one after another due to the strong water flow change and overflow outside the septic tank. At this time, the flocs floating in the treated water are attached to the foam and floated, of course.
Detergent components remaining in the treated water that cannot be removed by the flocculating chemical solution are also removed from the tank by foaming.

この状態を5分連続した後、再び弱で泡沫を発生させる
。これは上記の処理でも除去しきれず処理水中に残留し
ているフロックを水面に浮上させる目的と、オーバーフ
ロー時において浄化槽内壁に付着したフロックのうち、
処理水に触れて再び水中に戻る分の70ンクを浮上させ
る目的を持つ。
After this state continues for 5 minutes, foam is generated again at low temperature. This is to float the flocs remaining in the treated water that could not be removed even with the above treatment to the water surface, and also to remove the flocs that adhered to the inner wall of the septic tank during overflow.
The purpose is to float the 70 ink that comes into contact with the treated water and returns to the water.

その後前記同様に泡沫発生状態“強”で、処理水中の残
留フロックと残留洗剤成分をほぼ完全に除去し、泡沫処
理行程を終了する。
Thereafter, in the same manner as described above, the residual flocs and residual detergent components in the treated water are almost completely removed under the "strong" foam generation state, and the foam treatment process is completed.

以上本発明の方法による結果と、泡沫発生量を一定に固
定して処理する方法による結果を次に示す。
The results obtained by the method of the present invention and the results obtained by the method in which the amount of foam generated is fixed at a constant level are shown below.

第3表 注)但し処理水量は2001で、透明度30度以上は測
定しないものとする。
Table 3 Note) However, the amount of treated water is 2001, and the transparency is not over 30 degrees.

このように本発明法による結果と泡沫量を一定で処理す
る方法による結果を比較すると、洗J17用水の水質と
して十分な透明度30度以−ヒ・ローへキサン抽出量5
ppmまで浄化するのに、本発明法では泡沫量を一定で
処理した場合の半分の時間しか要しないことがわかる。
Comparing the results of the method of the present invention and the method of treating the amount of foam at a constant level, we find that the water quality is sufficient for washing J17 water, with a transparency of 30 degrees or higher, and a high-low hexane extraction amount of 5.
It can be seen that the method of the present invention requires only half the time to purify the foam to ppm compared to the case where the amount of foam is kept constant.

[発明の効果1 本発明は以上のように構成されるので次のような効果か
得られる。
[Effect 1 of the Invention Since the present invention is configured as described above, the following effects can be obtained.

浄化槽の容量単位で不連続的にバッチ処理するこの種の
方式の排水浄化装置においで、浄化処理に要する時間の
大部分を占める泡沫処理時間が泡沫量を一定で処理した
場合の約半分まで短Mdされるので、−回の浄化処理に
要する時間も短くなり、単位時間あたりの浄化処理量か
増大して浄化処理効率が大幅に向上する。従って複数の
洗車機が同時に稼働した時や、連続して洗沖が行なわれ
た時でも浄化処理か開に合わなくなり積木でそれを補う
というケースが少なくなる。
In this type of wastewater purification equipment, which performs batch processing discontinuously in units of septic tank capacity, the foam processing time, which accounts for most of the time required for purification, is reduced to about half that of when the foam volume is treated at a constant rate. Since the Md is applied, the time required for the second purification process is shortened, the amount of purification treatment per unit time is increased, and the purification treatment efficiency is greatly improved. Therefore, even when multiple car wash machines are operated at the same time or when washing is carried out continuously, there are fewer cases where the purification process becomes inadequate and the problem is compensated for with building blocks.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は本発明実施例に関わる覗1水処理装置のシステ
ム説明図。 第2図は本発明実施例による排水浄化処理の流れを示す
70−シート。 第3図は処理水中に泡沫を発生させた状態を示す説明図
。 第4図はエアー配管図。 3は浄化槽、4は散気管、6は凝集薬液添加装置、7は
外槽、14は制御装置。
FIG. 1 is a system explanatory diagram of a water treatment device according to an embodiment of the present invention. FIG. 2 is a 70-sheet showing the flow of wastewater purification treatment according to an embodiment of the present invention. FIG. 3 is an explanatory diagram showing a state in which foam is generated in the treated water. Figure 4 is an air piping diagram. 3 is a septic tank, 4 is an aeration pipe, 6 is a flocculating chemical addition device, 7 is an outer tank, and 14 is a control device.

Claims (1)

【特許請求の範囲】[Claims] 空気供給源に接続され処理水中に泡沫を発生する散気管
と、該散気管に供給する空気圧を切換え泡沫発生量を可
変する手段と、散気管を内方に備える浄化槽と、該浄化
槽の周囲を覆う外槽と、浄化槽内に凝集薬液を添加する
凝集薬液添加装置と、前記散気管からの泡沫発生量およ
び凝集薬液添加装置を制御する制御装置とを備え、排水
中の懸濁物質をフロック状にして泡沫で浮上除去すると
共に、凝集薬液添加後のフロックを含む処理水に供給す
る泡沫量を可変することを特徴とする排水処理装置。
An aeration pipe that is connected to an air supply source and generates foam in the treated water, a means for changing the amount of foam generated by switching the air pressure supplied to the aeration pipe, a septic tank that is equipped with the aeration pipe inside, and The septic tank is equipped with an outer tank for covering, a flocculating chemical addition device that adds a flocculant chemical into the septic tank, and a control device that controls the amount of foam generated from the aeration pipe and the flocculating chemical adding device. A wastewater treatment device characterized in that the foam is floated and removed using foam, and the amount of foam supplied to treated water containing flocs after addition of a coagulating chemical solution is varied.
JP63198736A 1988-08-09 1988-08-09 Wastewater treatment equipment Expired - Lifetime JP2558150B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP63198736A JP2558150B2 (en) 1988-08-09 1988-08-09 Wastewater treatment equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63198736A JP2558150B2 (en) 1988-08-09 1988-08-09 Wastewater treatment equipment

Publications (2)

Publication Number Publication Date
JPH0248091A true JPH0248091A (en) 1990-02-16
JP2558150B2 JP2558150B2 (en) 1996-11-27

Family

ID=16396128

Family Applications (1)

Application Number Title Priority Date Filing Date
JP63198736A Expired - Lifetime JP2558150B2 (en) 1988-08-09 1988-08-09 Wastewater treatment equipment

Country Status (1)

Country Link
JP (1) JP2558150B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006289313A (en) * 2005-04-14 2006-10-26 Matsushita Electric Ind Co Ltd Apparatus and method for treating organic waste water

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS516358A (en) * 1974-07-04 1976-01-19 Hitachi Construction Machinery GANYUHAISUISHORIHOHOOYOBI SOCHI
JPS56155683A (en) * 1980-05-03 1981-12-01 Kazutoyo Sugihara Floating separator

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS516358A (en) * 1974-07-04 1976-01-19 Hitachi Construction Machinery GANYUHAISUISHORIHOHOOYOBI SOCHI
JPS56155683A (en) * 1980-05-03 1981-12-01 Kazutoyo Sugihara Floating separator

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006289313A (en) * 2005-04-14 2006-10-26 Matsushita Electric Ind Co Ltd Apparatus and method for treating organic waste water

Also Published As

Publication number Publication date
JP2558150B2 (en) 1996-11-27

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