JPH0621434Y2 - Wastewater purification equipment for dry cleaning equipment - Google Patents

Wastewater purification equipment for dry cleaning equipment

Info

Publication number
JPH0621434Y2
JPH0621434Y2 JP1987090565U JP9056587U JPH0621434Y2 JP H0621434 Y2 JPH0621434 Y2 JP H0621434Y2 JP 1987090565 U JP1987090565 U JP 1987090565U JP 9056587 U JP9056587 U JP 9056587U JP H0621434 Y2 JPH0621434 Y2 JP H0621434Y2
Authority
JP
Japan
Prior art keywords
solvent
tank
water
aeration tank
aeration
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.)
Expired - Lifetime
Application number
JP1987090565U
Other languages
Japanese (ja)
Other versions
JPS63199792U (en
Inventor
信治 高木
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.)
Mitsubishi Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries 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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP1987090565U priority Critical patent/JPH0621434Y2/en
Publication of JPS63199792U publication Critical patent/JPS63199792U/ja
Application granted granted Critical
Publication of JPH0621434Y2 publication Critical patent/JPH0621434Y2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Description

【考案の詳細な説明】 (産業上の利用分野) 本考案は、ドライクリーニング装置に適用される排水浄
化装置に関するものである。
DETAILED DESCRIPTION OF THE INVENTION (Industrial field of application) The present invention relates to a waste water purification device applied to a dry cleaning device.

(従来の技術) まず、従来のドライクリーニング装置の概要を第3図を
用いて説明する。なお、ドライクリーニングに使用する
有機溶剤にはパークロルエチレン、1.1.1-トリクロルエ
タン、1.1.2-トリクロロ-1.2.2-トリフルオロエタン
(R113)、トリクロロモノフルオロメタン(R1
1)などがあるが、以下の説明ではパークロルエチレン
を例にとって説明する。
(Prior Art) First, an outline of a conventional dry cleaning device will be described with reference to FIG. The organic solvent used for dry cleaning is perchlorethylene, 1.1.1-trichloroethane, 1.1.2-trichloro-1.2.2-trifluoroethane (R113), trichloromonofluoromethane (R1).
1), etc., but in the following description, perchlorethylene will be taken as an example.

すなわち、図において1はドアであり、このドア1から
クリーニングすべき衣料2を投入しドア1を閉じて運転
を開始すると、通常は次の順序で工程が進行する。
That is, in the figure, reference numeral 1 is a door, and when the clothes 2 to be cleaned are put in from the door 1 and the door 1 is closed and the operation is started, the process normally proceeds in the following order.

(1)溶剤タンク3から溶剤4がバルブ5を介してポンプ
6で汲み上げられ、バルブ7、フィルタ8からなる経
路、またはバルブ9からなる経路によって処理槽10に溶
剤4が必要量送り込まれる。
(1) The solvent 4 is pumped up from the solvent tank 3 via the valve 5 by the pump 6, and the required amount of the solvent 4 is sent to the processing tank 10 through the path including the valve 7 and the filter 8 or the path including the valve 9.

(2)溶剤4が処理槽10内に必要量供給されると、次に処
理槽10内の処理ドラム11がゆっくり回転され、溶剤4は
処理槽10、ボタントラップ12、バルブ13、ポンプ6を経
て、バルブ7、フィルタ8からなる経路、またはバルブ
9からなる経路で循環されて衣料2が洗浄される。
(2) When the necessary amount of the solvent 4 is supplied into the processing tank 10, the processing drum 11 in the processing tank 10 is slowly rotated next, and the solvent 4 is supplied to the processing tank 10, the button trap 12, the valve 13 and the pump 6. After that, the clothes 2 are circulated through the path including the valve 7 and the filter 8 or the path including the valve 9 to wash the clothes 2.

(3)所定時間の洗浄が終了すると、処理槽10内の溶剤4
は処理槽10、ボタントラップ12、バルブ13、ポンプ6、
バルブ14の経路で蒸溜器15に排液され、続いて、処理ド
ラム11が高速回転して衣料2中の溶剤4を遠心分離し、
排液する。蒸溜器15に入った溶剤は蒸発してコンデンサ
27に導かれてここで凝縮された後、回収され、水分離器
22にて水分離され、溶剤配管23を通ってクリンタンク24
に入り、オーバフロー付仕切板28から溶剤タンク3に戻
る。
(3) After cleaning for a predetermined time, the solvent 4 in the processing tank 10
Is a processing tank 10, a button trap 12, a valve 13, a pump 6,
The liquid is discharged to the distiller 15 through the path of the valve 14, and then the processing drum 11 is rotated at a high speed to centrifuge the solvent 4 in the clothing 2.
Drain. The solvent in the distiller 15 evaporates and the condenser
After being led to 27 and condensed here, it is recovered and water separator
Water is separated at 22, and the cleaning tank 24 is passed through the solvent pipe 23.
Then, the partition plate with overflow 28 is returned to the solvent tank 3.

(4)上記(1)、(2)の工程を繰返して洗浄を行う。(4) The above steps (1) and (2) are repeated to perform washing.

(5)処理槽10、ボタントラップ12、バルブ13、バルブ5
の経路で溶剤タンク3に排液し、続いて、処理ドラム11
が高速回転して衣料2中の溶剤4を遠心分離して排液す
る。
(5) Processing tank 10, button trap 12, valve 13, valve 5
The liquid is drained to the solvent tank 3 through the path of, and then the processing drum 11
Rotates at a high speed to centrifuge the solvent 4 in the clothing 2 and drain it.

(6)再び処理ドラム11をゆっくり回し、ファン16、エア
クーラ17、エアヒータ18からなるリカバリエアダクト19
と処理槽10の間を矢印20の方向にエアを循環させて衣料
2を乾燥する。この時、衣料2から蒸発した溶剤ガス
は、リカバリエアダクト19内に設けられたエアクーラ17
が凝縮され、この凝縮液は回収経路21を経て水分離器22
に入り、ここで水分離された後、溶剤配管23を通ってク
リンタンク24に入る。
(6) Slowly rotate the processing drum 11 again to recover the recovery air duct 19 including the fan 16, the air cooler 17, and the air heater 18.
Air is circulated in the direction of arrow 20 between the processing tank 10 and the processing tank 10 to dry the garment 2. At this time, the solvent gas evaporated from the clothes 2 is cooled by the air cooler 17 provided in the recovery air duct 19.
Is condensed, and this condensate passes through the recovery path 21 and the water separator 22.
Then, after the water is separated here, it enters the clean tank 24 through the solvent pipe 23.

(7)乾燥が終了すると、リカバリエアダクト19のダンパ2
5,26が破線の如く開き、ダンパ25から新鮮な空気を取り
入れ、ダンパ26からエアクーラ17では回収できない未凝
縮溶剤ガスを排気し、衣料2中の溶剤臭を脱臭する。
(7) When drying is completed, the damper 2 of the recovery air duct 19
5, 26 open as shown by broken lines, fresh air is taken in from the damper 25, uncondensed solvent gas that cannot be recovered by the air cooler 17 is exhausted from the damper 26, and the solvent odor in the clothing 2 is deodorized.

以上の(1)〜(7)の1サイクルは第4図の如く区分され
る。
One cycle of the above (1) to (7) is divided as shown in FIG.

なお、第3図中の30は蒸気配管であって、エアヒータ18
に接続されてエアクーラ17を通過したエアを過熱するも
のであり、また31は冷却水配管であって、蒸溜器15で蒸
発した溶剤ガスを凝縮液化するものである。また、32は
蒸気配管であり、蒸溜器15に排液された溶剤を周囲から
加熱して蒸溜する(以下、これを傍熱蒸溜と称する)。
33は蒸気配管であり、この蒸気配管33は蒸溜器15に排液
された溶剤を直接加熱して蒸溜する(以下、これを直接
蒸溜と称する)。
In addition, 30 in FIG. 3 is a steam pipe, and the air heater 18
Is for heating the air that has passed through the air cooler 17 and is for cooling water piping for condensing and liquefying the solvent gas evaporated in the distiller 15. Further, 32 is a steam pipe, which heats and distills the solvent discharged to the distiller 15 from the surroundings (hereinafter referred to as "indirect heat distillation").
33 is a steam pipe, and this steam pipe 33 directly heats and distills the solvent discharged to the distiller 15 (hereinafter, this is referred to as direct distilling).

ここで、上記傍熱蒸溜は上記(3)の工程で自動的に実行
されるため、一般には連続蒸溜と称されている。傍熱蒸
溜によって固形汚れや油性汚れが蒸溜器15内に蒸溜カス
として蓄積されるが、たまり過ぎると蒸溜効果を悪くし
てついには蒸溜しなくなるので、毎日の作業終了時等を
見計らって除去する。
Here, since the indirectly heated distillation is automatically performed in the step (3), it is generally called continuous distillation. Solid dirt and oily dirt are accumulated as distillation residue in the distiller 15 by the indirect heat distillation, but if it accumulates too much, it diminishes the distillation effect and finally does not evaporate, so it should be removed at the end of daily work etc. .

また、直熱蒸溜は、前記に先立って蒸溜カスに含まれる
溶剤ガスを追出す場合等に蒸気管33のバルブを操作して
実行する。
Further, the direct heat distillation is performed by operating the valve of the steam pipe 33 when the solvent gas contained in the distillation residue is expelled prior to the above.

以上の装置において、上記した如く水分離器22に回収溶
剤の流入する形態が3通り((3)の工程、(6)の工程及び
直熱蒸溜時)あるが、水分離器22が溶剤中に含まれる水
をいずれも比重差によって分離し、この分離した水を配
管29から系外へ排出し、そのまま廃棄するようにしてい
る。従って、分離した水の中にはかなりの溶剤が含まれ
ている。例えば、ドライクリーナの1日当りの処理量と
して小形機を例にとると、被洗物10kgづつを10回程実施
したとして、上記した水分離器22からの系外排水量は約
6/日になるが、このうち傍熱蒸溜による排水量Q
=2/日、直熱蒸溜による排水量Q=4/日程度
の割合となる。そして、これら排水中の溶剤濃度はQ
の溶剤濃度=100ppm、Qの溶剤濃度=300ppmにもな
る。
In the above apparatus, there are three ways in which the recovered solvent flows into the water separator 22 as described above (the step (3), the step (6) and the direct heat distillation). All the water contained in is separated by the difference in specific gravity, the separated water is discharged from the pipe 29 to the outside of the system, and is discarded as it is. Therefore, the separated water contains a considerable amount of solvent. For example, taking a small machine as an example of the amount of dry cleaner to be processed per day, assuming that 10 kg of the object to be washed is carried out about 10 times, the amount of waste water discharged from the water separator 22 is about 6 / day. , Of which the amount of wastewater from indirect heat distillation Q 1
= 2 / day, and the amount of wastewater from direct heat distillation Q 2 = 4 / day. And the solvent concentration in these wastewater is Q 1
Solvent concentration = 100 ppm, and also a solvent concentration = 300 ppm of Q 2.

これを大量に集中稼動させた場合は、その地域の地下水
を排水に溶け込んでいる溶剤で汚染するという問題が起
る。特に最近、有機塩素化合物による水道水用地下水の
汚染が問題視され、関係省庁もその対策を打ち出し始め
ていることなどから、かかる汚染の問題を早急に解決す
る必要が生じ、既に第5図の様な排水浄化装置(例えば
特開昭60−222091号)が提案されている。
When a large amount of this is operated intensively, there arises a problem that the groundwater in the area is contaminated with the solvent dissolved in the wastewater. In particular, recently, pollution of tap water groundwater with organic chlorine compounds has been regarded as a problem, and related ministries and agencies have begun to take measures against it. Therefore, it is necessary to urgently solve the problem of pollution, as shown in Fig. 5. A waste water purification device (for example, Japanese Patent Laid-Open No. 60-222091) has been proposed.

第5図において、43はドライクリーニング装置本体34内
の水分離器22にて分離された水を配管29を介して受けて
貯留するタンクであり、例えばポリ容器が用いられてい
る。44はこのタンク43の貯留水が導かれてこれを曝気す
る。例えばポリ容器による曝気槽であり、曝気用のエア
又はガスを気泡状に発生する多孔性通気体を内蔵する。
45はバルブであり、タンク43と曝気槽44を連通する配管
に設けた開閉弁である。46はバルブであり、曝気槽44の
排水管に設けた開閉弁である。47は配管であり、本体34
の脱臭口36に連なる排気ダクトと曝気槽44とを連通させ
ており、本体34のリカバリエアダクト19内に設けられた
ファン16を回転させ、且つダンパ25,26を開いて外部よ
り本体34内に新鮮な空気を送り込んだ際、ダンパ26の脱
臭口36より排気される空気を多孔性通気体に送り込むも
のである。
In FIG. 5, 43 is a tank for receiving and storing the water separated by the water separator 22 in the main body 34 of the dry cleaning device through the pipe 29, and for example, a plastic container is used. 44 stores the water stored in the tank 43 and aerates it. For example, it is an aeration tank using a plastic container, and has a built-in porous aeration body that generates air or gas for aeration in the form of bubbles.
Reference numeral 45 is a valve, which is an opening / closing valve provided in a pipe connecting the tank 43 and the aeration tank 44. Reference numeral 46 is a valve, which is an opening / closing valve provided in the drainage pipe of the aeration tank 44. 47 is a pipe, and the main body 34
The exhaust duct connected to the deodorizing port 36 and the aeration tank 44 are communicated with each other, the fan 16 provided in the recovery air duct 19 of the main body 34 is rotated, and the dampers 25 and 26 are opened to externally enter the main body 34. When fresh air is sent, the air exhausted from the deodorizing port 36 of the damper 26 is sent to the porous aeration body.

1次に上記構成の作用について説明する。Next, the operation of the above configuration will be described.

洗浄の工程については既述したとおりであるので、ここ
では排水処理について説明する。
Since the cleaning process is as described above, the wastewater treatment will be described here.

本装置においてはタンク43に本体34の水分離器22より
排水される、例えば1日分の排水を貯える。
In this device, the tank 43 stores, for example, one-day drainage discharged from the water separator 22 of the main body 34.

当日の終業時又は翌日の始業時にタンク43内の排水を
バルブ45の操作で曝気槽44に移す。
The drainage in the tank 43 is transferred to the aeration tank 44 by operating the valve 45 at the end of the day or at the start of the next day.

バルブ45,46が閉の状態で本体34が運転されると、水
分離器22から分離された排水がタンク43内に蓄積され、
また、洗浄工程終了の際にダンパ25,26を開いて外気を
本体34内に送り込み、脱臭する時、本体34のリカバリエ
アダクトの脱臭口36からの排気の一部が配管47の回路で
曝気槽44の多孔性通気体に供給され、槽内の排水を曝気
して溶剤ガスを放出する。これにより曝気槽44内の貯留
水の含有溶剤は曝気されて蒸発し、貯留水の溶剤濃度は
極めて小さくなる。
When the main body 34 is operated with the valves 45 and 46 closed, the waste water separated from the water separator 22 is accumulated in the tank 43,
Further, when the cleaning process is completed, the dampers 25 and 26 are opened to send the outside air into the main body 34 to deodorize. It is supplied to 44 porous aerators to aerate the waste water in the tank and release the solvent gas. As a result, the solvent contained in the stored water in the aeration tank 44 is aerated and evaporated, and the solvent concentration of the stored water becomes extremely small.

その日の終業時又は翌日の始業時に曝気槽44内の排水
をバルブ46の操作で抜き、排出した後、ここへタンク43
内の排水をバルブ45を操作して移す。
At the end of the day or at the start of the next day, drain the drainage from the aeration tank 44 by operating the valve 46 and discharge it.
Operate valve 45 to transfer the drainage inside.

上記を繰返して運転し、曝気により溶剤をほとん
ど含まない排水を系外に排出する。
The above operation is repeated to discharge the waste water containing almost no solvent to the outside of the system by aeration.

(考案が解決しようとする問題点) ところで、タンク43に貯えられた排水中に粒状の溶剤が
存在する場合には、排水をタンク43から曝気槽44に移し
てから、同槽内へ空気等を供給して曝気しても、前記粒
状の溶剤は破壊されずに同槽の底部に沈澱する傾向にあ
り、粒状の溶剤を破壊するには曝気に長時間を必要とし
ていた。
(Problems to be solved by the invention) By the way, when a granular solvent is present in the wastewater stored in the tank 43, the wastewater is transferred from the tank 43 to the aeration tank 44, and then air or the like is fed into the tank. Even if the gas was supplied and aerated, the granular solvent tended to settle at the bottom of the tank without being destroyed, and a long period of aeration was required to destroy the granular solvent.

本考案は以上の点を解決すべくなされたもので、排水を
曝気槽に移す前に排水中に含まれる粒状の溶剤を分離除
去し、速やかに曝気がなされるようにした排水の効率的
な浄化装置を提供しようとするものである。
The present invention has been made to solve the above-mentioned problems, and the granular solvent contained in the wastewater is separated and removed before the wastewater is transferred to the aeration tank, so that the wastewater can be efficiently aerated efficiently. It is intended to provide a purification device.

(問題点を解決するための手段) このため本考案は、ドライクリーニング装置からの排水
中に含まれる溶剤を除去するための、水分離器と曝気槽
を有する曝気式排水浄化装置において、前記水分離器と
曝気槽の間に、同水分離器からの排水を貯留する安全分
離器を設け、同安全分離器の曝気槽への入口部に、同曝
気槽に接続する漏斗と、同漏斗に着脱可能に装着した親
水性フィルタを内蔵して、排水中に浮遊する粒状の溶剤
を通過させないようにしてなるもので、これを問題点解
決のための手段とするものである。
(Means for Solving Problems) Therefore, the present invention provides an aeration-type wastewater purification apparatus having a water separator and an aeration tank for removing a solvent contained in wastewater from a dry cleaning apparatus. A safety separator that stores the wastewater from the water separator is installed between the separator and the aeration tank, and the funnel connected to the aeration tank and the funnel are installed at the inlet of the safety separator to the aeration tank. A hydrophilic filter that is detachably attached is built in so that the particulate solvent floating in the drainage does not pass through, and this is a means for solving the problem.

(作用) ドライクリーナの排水中に浮遊する溶剤があり、この浮
遊した溶剤が曝気槽に入ると、曝気によって溶剤が沈澱
する。また曝気槽内に溶剤粒が一粒でも沈澱している
と、浄化した水に溶剤が溶け込み、3ppm以下にはなら
ない。本考案では、 水分離器からの排水を親水性フィルタで一旦濾過してか
ら曝気槽へ供給することにより、曝気槽内に送られる排
水からは粒状の溶剤が安全に除去され、短時間で排水の
完全な浄化が計られる。
(Function) There is a solvent floating in the drain of the dry cleaner, and when this floating solvent enters the aeration tank, the solvent is precipitated by aeration. In addition, if even one particle of solvent is precipitated in the aeration tank, the solvent will dissolve into the purified water and the amount will not drop below 3 ppm. In the present invention, the wastewater from the water separator is first filtered with a hydrophilic filter and then supplied to the aeration tank, so that the particulate solvent is safely removed from the wastewater sent to the aeration tank, and the wastewater is drained in a short time. The complete purification of is measured.

(実施例) 以下、本考案を図面に示す実施例により具体的に説明す
る。
(Embodiment) The present invention will be specifically described below with reference to an embodiment shown in the drawings.

第1図は本考案の代表的な実施例を示すもので、図中第
5図と同一の符号が付してある部分は実質的に従来のも
のと同一であるので、以下第5図との相違点を中心に説
明する。
FIG. 1 shows a typical embodiment of the present invention. In the figure, the parts denoted by the same reference numerals as those in FIG. 5 are substantially the same as the conventional ones. The differences will be mainly described.

本排水浄化装置には、曝気槽44の排水入口部にバルブ51
を介して安全分離器50が設けられる。安全分離器50は排
出貯留槽と同槽内に延設された配管49とからなり、同配
管49の槽内側端部には漏斗48が取り付けられ、他端部は
前記バルブ51に連結されている。
This wastewater purifier has a valve 51 at the drainage inlet of the aeration tank 44.
A safety separator 50 is provided via. The safety separator 50 consists of a discharge storage tank and a pipe 49 extending in the same tank, a funnel 48 is attached to the inner end of the pipe 49, and the other end is connected to the valve 51. There is.

前記漏斗48の大径開口部には親水性のフィルタ52が着脱
可能に装着され、その一部又は全部が排水中に浸漬され
る。同親水性フィルタ52は水分を通過させるが、粒子状
の溶剤を分離する機能を有し、例えば木綿、レーヨン等
の親水性繊維からなる布、不織布で構成されている。
A hydrophilic filter 52 is detachably attached to the large-diameter opening of the funnel 48, and a part or all of the hydrophilic filter 52 is immersed in the drainage. The hydrophilic filter 52 has a function of separating the particulate solvent while allowing water to pass therethrough, and is made of, for example, a cloth or non-woven fabric made of hydrophilic fibers such as cotton and rayon.

本実施例装置では、上記各装置に加えて曝気槽44の排気
口と配管55を介して連結される活性炭槽53が設置され
る。この活性炭槽53には活性炭54が装填され、同活性炭
54内には前記曝気槽44に接続する配管55の開放端が挿入
されている。また、同配管55の途中にはヒータ56が取り
付けられ、曝気槽44から活性炭槽53へ導入する溶剤ガス
を加熱する。
In the device of the present embodiment, in addition to the above devices, an activated carbon tank 53 connected to the exhaust port of the aeration tank 44 via a pipe 55 is installed. This activated carbon tank 53 is loaded with activated carbon 54,
An open end of a pipe 55 connected to the aeration tank 44 is inserted into the inside of 54. A heater 56 is attached in the middle of the pipe 55 to heat the solvent gas introduced from the aeration tank 44 to the activated carbon tank 53.

次に、その作用について述べる。Next, its operation will be described.

洗浄の工程については従来例と同じであるので、ここで
は本考案の排水浄化装置による排水の処理について説明
する。
Since the washing process is the same as that of the conventional example, the treatment of waste water by the waste water purification apparatus of the present invention will be described here.

まずタンク43に本体34の水分離器22より排水される、
例えば1日分の排水を貯える。
First, the water is drained from the water separator 22 of the main body 34 to the tank 43,
For example, store drainage for one day.

当日の終業時又は翌日の始業時にタンク43内の排水を
バルブ45の操作で安全分離器50に移す。
The drainage in the tank 43 is transferred to the safety separator 50 by operating the valve 45 at the end of the day or at the start of the next day.

安全分離器50には、予め排水が溜められており、親水
性フィルタ52は毛細管現象で全体に水分を含んだ状態に
あり、バルブ51を開くと共に、親水性フィルタ52を介し
て曝気槽44に排水する。これにより、溶剤粒子が曝気槽
44に入らない様に濾過される。
In the safety separator 50, wastewater is stored in advance, and the hydrophilic filter 52 is in a state of containing water entirely due to a capillary phenomenon, and while the valve 51 is opened, the hydrophilic filter 52 opens the aeration tank 44 through the hydrophilic filter 52. Drain. As a result, solvent particles are aerated
It is filtered so that it does not go into 44.

バルブ45が閉の状態でドライクリーナ本体34が運転さ
れると、水分離器22から分離された排水がタンク43内に
蓄積される。
When the dry cleaner main body 34 is operated with the valve 45 closed, the waste water separated from the water separator 22 is accumulated in the tank 43.

一方、曝気槽44の多孔性通気体に空気を供給し、同槽44
内の排水を曝気して溶剤ガスを放出する。
On the other hand, air is supplied to the porous aeration body of the aeration tank 44,
Aeration of the wastewater inside releases the solvent gas.

こうして曝気槽44内にある貯留水の含有溶剤は曝気され
て蒸発し、貯留水の溶剤濃度は極めて小さくなる。
In this way, the solvent contained in the stored water in the aeration tank 44 is aerated and evaporated, and the solvent concentration of the stored water becomes extremely small.

曝気して放出された溶剤ガスを配管55を通して活性炭
槽53に送り、活性炭54に溶剤ガスを吸着させ、溶剤ガス
をほとんど含まない空気だけを放出する。活性炭槽53に
溶剤ガスを送る際に、ヒータ56に電気を通電し、溶剤ガ
スの相対温度を低くして、例えば50%以下になる様に
して活性炭の吸気寿命を長くしている。
The solvent gas released by aeration is sent to the activated carbon tank 53 through the pipe 55, and the activated carbon 54 adsorbs the solvent gas, and only the air containing almost no solvent gas is released. When the solvent gas is sent to the activated carbon tank 53, electricity is supplied to the heater 56 to lower the relative temperature of the solvent gas to, for example, 50% or less, thereby prolonging the intake life of the activated carbon.

その日の終業的又は翌日の始業時に曝気槽44内の排水
をバルブ46の操作で抜き、排出する。
At the end of the day or at the beginning of the next day, the drainage in the aeration tank 44 is drained by operating the valve 46 and discharged.

上記〜を繰返して運転することにより、曝気され
て溶剤をほとんど含まない排水を系外に排出できる。
By repeating the above operations, the waste water that is aerated and contains almost no solvent can be discharged to the outside of the system.

なお、活性炭槽53の活性炭54が破過して吸着能力が無く
なった場合は、活性炭54を新しいものと交換する。
If the activated carbon 54 in the activated carbon tank 53 breaks through and the adsorption capacity is lost, the activated carbon 54 is replaced with a new one.

なお、上記構成において、各バルブ45,46,51を自動弁に
変更すると共に、タイマ等を設けた制御装置を追加すれ
ば上記〜の操作を自動化することができる。
It should be noted that, in the above-mentioned configuration, the above-mentioned operations can be automated by changing the valves 45, 46, 51 to automatic valves and adding a control device provided with a timer or the like.

また、曝気槽44から放出される溶剤ガスを活性炭槽53へ
導く代りに、ドライクリーニング装置本体34側に設置す
る活性炭溶剤回収装置等へ導くようにしてもよい。
Further, instead of guiding the solvent gas discharged from the aeration tank 44 to the activated carbon tank 53, it may be guided to an activated carbon solvent recovery device or the like installed on the dry cleaning device main body 34 side.

漏斗48は、親水性フィルタ52の装填される開口部は可能
な限り大面積を有する構造であることが望ましく、例え
ば截頭錐体状、円筒体状等その形状は問わない。更に第
2図の如く漏斗48の開口部を下方へ向けて設置してもよ
い。
The funnel 48 preferably has a structure in which the opening into which the hydrophilic filter 52 is loaded has a large area as much as possible, and may have any shape such as a truncated cone shape or a cylindrical shape. Further, as shown in FIG. 2, the funnel 48 may be installed with its opening facing downward.

(考案の効果) ドライクリーナの排水中には浮遊する溶剤があり、この
浮遊した溶剤が曝気槽に入ると、曝気によって溶剤が沈
澱する。また曝気槽内に溶剤粒が一粒でも沈澱している
と、浄化した水に溶剤が溶け込み、3ppm以下にはなら
ない。本考案では、洗浄に使用した溶剤中に含まれる水
分を分離するための水分離器からの排水を貯留して曝気
する曝気装置を設けると共に、水分離器からの排水を安
全分離器に内蔵した親水性のフィルタで濾過してから曝
気槽へ供給する様にしたので、粒状の溶剤は完全に除去
されて排水の浄化が図られ、地下水の汚染防止が達成さ
れる。
(Effect of the Invention) There is a floating solvent in the wastewater of the dry cleaner, and when this floating solvent enters the aeration tank, the solvent is precipitated by aeration. In addition, if even one particle of solvent is precipitated in the aeration tank, the solvent will dissolve into the purified water and the amount will not drop below 3 ppm. In the present invention, an aerator for storing and aerating the drainage from the water separator for separating the water contained in the solvent used for cleaning is provided, and the drainage from the water separator is built into the safety separator. Since it is supplied to the aeration tank after being filtered with a hydrophilic filter, the particulate solvent is completely removed, the wastewater is purified, and the groundwater is prevented from being contaminated.

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

第1図は本考案の代表的な実施例を示す概略構成図、第
2図は同じく他の実施例を示す要部構成図、第3図は従
来のドライクリーニング装置の概略構成図、第4図は同
装置の1サイクルを示す図、第5図は従来の排水浄化処
理装置の概略構成図である。 図の主要部分の説明 22……水分離器 34……本体 43……タンク 44……曝気槽 48……漏斗 50……安全分離器 52……親水性フィルタ 53……活性炭槽
FIG. 1 is a schematic configuration diagram showing a typical embodiment of the present invention, FIG. 2 is a configuration diagram of essential parts of another embodiment, and FIG. 3 is a schematic configuration diagram of a conventional dry cleaning device. FIG. 1 is a diagram showing one cycle of the device, and FIG. 5 is a schematic configuration diagram of a conventional wastewater purification treatment device. Description of the main parts of the figure 22 …… Water separator 34 …… Main body 43 …… Tank 44 …… Aeration tank 48 …… Funnel 50 …… Safety separator 52 …… Hydrophilic filter 53 …… Activated carbon tank

Claims (1)

【実用新案登録請求の範囲】[Scope of utility model registration request] 【請求項1】ドライクリーニング装置からの排水中に含
まれる溶剤を除去するための、水分離器と曝気槽を有す
る曝気式排水浄化装置において、前記水分離器と曝気槽
の間に、同水分離器からの排水を貯留する安全分離器を
設け、同安全分離器の曝気槽への入口部に、同曝気槽に
接続する漏斗と、同漏斗に着脱可能に装着した親水性フ
ィルタを内蔵して、排水中に浮遊する粒状の溶剤を通過
させないようにしたことを特徴とするドライクリーニン
グ装置の排水浄化装置。
1. An aeration type waste water purification apparatus having a water separator and an aeration tank for removing a solvent contained in the waste water from a dry cleaning apparatus, wherein the water is separated between the water separator and the aeration tank. A safety separator that stores the wastewater from the separator is provided, and a funnel that connects to the aeration tank and a hydrophilic filter that is detachably attached to the funnel are built into the safety separator at the entrance to the aeration tank. The drain cleaning device of the dry cleaning device is characterized in that the particulate solvent floating in the drain is prevented from passing through.
JP1987090565U 1987-06-12 1987-06-12 Wastewater purification equipment for dry cleaning equipment Expired - Lifetime JPH0621434Y2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1987090565U JPH0621434Y2 (en) 1987-06-12 1987-06-12 Wastewater purification equipment for dry cleaning equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1987090565U JPH0621434Y2 (en) 1987-06-12 1987-06-12 Wastewater purification equipment for dry cleaning equipment

Publications (2)

Publication Number Publication Date
JPS63199792U JPS63199792U (en) 1988-12-22
JPH0621434Y2 true JPH0621434Y2 (en) 1994-06-08

Family

ID=30950547

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1987090565U Expired - Lifetime JPH0621434Y2 (en) 1987-06-12 1987-06-12 Wastewater purification equipment for dry cleaning equipment

Country Status (1)

Country Link
JP (1) JPH0621434Y2 (en)

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS60222091A (en) * 1984-04-20 1985-11-06 三菱重工業株式会社 Drycleaning apparatus
JPS6175802U (en) * 1984-10-25 1986-05-22
JPS6248404U (en) * 1985-09-11 1987-03-25

Also Published As

Publication number Publication date
JPS63199792U (en) 1988-12-22

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