JPS6336839B2 - - Google Patents

Info

Publication number
JPS6336839B2
JPS6336839B2 JP12101780A JP12101780A JPS6336839B2 JP S6336839 B2 JPS6336839 B2 JP S6336839B2 JP 12101780 A JP12101780 A JP 12101780A JP 12101780 A JP12101780 A JP 12101780A JP S6336839 B2 JPS6336839 B2 JP S6336839B2
Authority
JP
Japan
Prior art keywords
sludge
solvent
tank
heated
liquid
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
Application number
JP12101780A
Other languages
Japanese (ja)
Other versions
JPS5745899A (en
Inventor
Masataka Mizutani
Hayami Nagano
Shinji Kato
Yasuhiro Tsubaki
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 JP12101780A priority Critical patent/JPS5745899A/en
Publication of JPS5745899A publication Critical patent/JPS5745899A/en
Publication of JPS6336839B2 publication Critical patent/JPS6336839B2/ja
Granted legal-status Critical Current

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  • Treatment Of Sludge (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

本発明はドライクリーニング機のスラツジの処
理方法に関し、特に有価物を回収すると共にスラ
ツジを無公害化するドライクリーニング機より排
出されるスラツジの処理方法に関する。 ドライクリーニング機において洗浄溶剤(例え
ば、ベンジン、四塩化炭素、トリクロロエチレ
ン、テトラクロロエチレンなど)の貯槽に蓄積さ
れるスラツジ(主としてフイルタースラツジ及び
衣類から同伴されるゴミ、油分、繊維などからな
る油泥)は、洗浄溶剤を含んでいるため、有価物
の回収、有毒性などの面から、そのまゝでは廃棄
処理ができないという問題をかゝえている。すな
わち、従来は洗浄済みの溶剤貯槽に蓄積するスラ
ツジは定期的に装置を停止し、人力によりかき出
した後、別途処理するのが通例であつたが、かき
出し時の悪臭発生の問題、別途処理時の悪臭発生
及び処理費用などの問題があり、スラツジ処理対
策の検討が急がれていた。 そこで本発明者らはドライクリーニング機から
排出されるスラツジの性質を詳細に検討、試験
し、かつ多くの実験の結果、貯槽に蓄積されたス
ラツジをある温度レベルに加温した後、空気を流
通させてスラツジ中の洗浄溶剤を完全に回収した
後、得られる油分と界面活性剤を含む残渣は5000
〜7000Kcal/Kgの熱を発し300℃程度で燃えるこ
とから、これを焼却灰化して1/5程度に減容し、
無害な灰として廃棄できることを見出し、本発明
に到達したものである。 すなわち、本発明は洗濯ドラムから排出される
油状スラツジとフイルタから排出されるフイルタ
材に由来するスラツジとを回収タンクに蓄積し、
同蓄積されたスラツジを一定時間放置して液分と
固形分とに分離し、同分離した液分を蒸発器に導
き加熱し、同液分に含まれる溶剤と油とを分離し
て溶剤を回収し、その後上記回収タンク内に残留
する固形分を加熱しながら空気を吹きつけて同固
形分に含まれる溶剤を放散、回収し、そしてその
残渣を上記回収タンク内で燃してなることを特徴
とするドライクリーニング機のスラツジ処理方法
に関する。 本発明を、洗浄溶剤としてパークレン(テトラ
クロロエチレン)を用いた場合を例にとつて、第
1図のフローシートに基き具体的に説明する。 衣料等を洗濯槽Wに投入し、次いでタンクT2
より弁V1、ポンプP1、弁V3、ラインL1を経て清
浄な洗浄溶剤パークレン1、および/または洗剤
S(ABS、DBS等の陽イオン、陰イオン、非イオ
ン界面活性剤)を供給し撹拌洗濯する。洗濯の進
行に伴つて汚れる洗浄溶剤はポンプP2により弁
V4を経てフイルタFに送つて、固型物、繊維等
を除き、洗濯終了と同時に洗濯槽W内脱臭、乾燥
に先立つて弁V5を経てタンクT1に抜きとられる。
この汚染洗浄溶剤を一定時間放置後、タンクT1
底部に蓄積されたスラツジは第1表に示すような
組成を有す。
The present invention relates to a method for treating sludge from a dry cleaning machine, and more particularly to a method for treating sludge discharged from a dry cleaning machine, which recovers valuables and makes the sludge pollution-free. Sludge (mainly filter sludge and oil sludge consisting of dust, oil, fibers, etc. entrained from filter sludge and clothing) that accumulates in the storage tank of cleaning solvents (e.g., benzine, carbon tetrachloride, trichlorethylene, tetrachlorethylene, etc.) in dry cleaning machines is Because it contains cleaning solvents, it poses problems such as recovery of valuables and toxicity, making it impossible to dispose of it as is. In other words, in the past, it was customary to periodically stop the equipment, manually scrape out the sludge that accumulated in the cleaned solvent storage tank, and then process it separately. There were problems such as the generation of bad odors and treatment costs, and there was an urgent need to consider measures to treat the sludge. Therefore, the present inventors investigated and tested the properties of the sludge discharged from dry cleaning machines in detail, and as a result of many experiments, they found that after heating the sludge accumulated in the storage tank to a certain temperature level, air was circulated. After completely recovering the cleaning solvent in the sludge, the resulting residue containing oil and surfactant is 5000
Since it emits ~7000Kcal/Kg of heat and burns at around 300℃, it is incinerated into ash to reduce its volume to around 1/5.
The present invention was achieved by discovering that it can be disposed of as harmless ash. That is, the present invention accumulates oily sludge discharged from a washing drum and sludge derived from filter material discharged from a filter in a collection tank,
The accumulated sludge is left for a certain period of time to separate into liquid and solid content, and the separated liquid content is led to an evaporator and heated to separate the solvent and oil contained in the liquid content and remove the solvent. After that, the solids remaining in the recovery tank are heated and blown with air to dissipate and recover the solvent contained in the solids, and the residue is burned in the recovery tank. The present invention relates to a method for treating sludge in a dry cleaning machine. The present invention will be specifically explained based on the flow sheet of FIG. 1, taking as an example the case where percrene (tetrachlorethylene) is used as a cleaning solvent. Put clothes, etc. into washing tub W, then into tank T 2
Clean cleaning solvent Perclean 1 and/or detergent S (cationic, anionic, nonionic surfactants such as ABS, DBS, etc.) are supplied via valve V 1 , pump P 1 , valve V 3 , and line L 1 Then stir and wash. The cleaning solvent that becomes dirty as the washing progresses is removed by the pump P2 .
It is sent to filter F via V 4 to remove solid matter, fibers, etc., and at the same time as washing is completed, the washing tub W is deodorized and, prior to drying, it is extracted to tank T 1 via valve V 5 .
After leaving this contaminated cleaning solvent for a certain period of time, tank T 1
The sludge accumulated at the bottom has a composition as shown in Table 1.

【表】 タンクT1にスラツジから分離されて貯留され
た汚染洗浄溶剤は、弁V6、ポンプP1、弁V2を経
て蒸発器Eに送られる。ここでヒータH2により
加熱して洗浄溶剤を気化させ、弁V7、コンデン
サCを経てデカンタDに導き、ここで共存する水
分をライン10から排出し、洗浄溶剤分はライン
11からライン1を経てタンクT2に戻し再利用
される。 蒸発器E底部に残る油分、界面活性剤等の液状
物は数サイクルの操作後、または一定量以上にな
れば、弁V8から油タンクT3に抜きとるか、また
は/ライン5よりタンクT1に戻される。 このように液状分を分離した後のタンクT1
の油泥状スラツジをT1底部のヒータH1により加
熱し、次いで空気ブロアBから空気加熱器H3
経て送られる加熱空気をT1スラツジ面に吹きつ
けてパークレンを空気放散により気化させライン
2、弁V9、コンデンサC、デカンタDから前述
のようにして回収する。前記蒸発及び空気放散に
より回収された洗浄溶剤は第2表に示す組成を有
しており、このものは存在する水分によるエマル
ジヨン生成がみとめられる。表から高純度でパー
クレンが回収されることが判る。
[Table] The contaminated cleaning solvent separated from the sludge and stored in the tank T 1 is sent to the evaporator E via the valve V 6 , the pump P 1 and the valve V 2 . Here, the cleaning solvent is heated by heater H 2 to vaporize it, and is led to decanter D via valve V 7 and condenser C, where the coexisting moisture is discharged from line 10, and the cleaning solvent is transferred from line 11 to line 1. It is then returned to Tank T 2 for reuse. Liquid substances such as oil and surfactants remaining at the bottom of the evaporator E are drained from valve V 8 to oil tank T 3 after several cycles of operation or when the amount exceeds a certain level, or are drained from tank T through line 5. Returned to 1 . The oily sludge in the tank T1 after the liquid content has been separated in this way is heated by the heater H1 at the bottom of T1 , and then the heated air sent from the air blower B through the air heater H3 is heated to the T1 sludge. The perclean is vaporized by air dissipation and recovered from line 2, valve V 9 , condenser C, and decanter D as described above. The cleaning solvent recovered by the evaporation and air dissipation had the composition shown in Table 2, and emulsion formation was observed due to the presence of moisture. It can be seen from the table that perclene is recovered with high purity.

【表】 一方、不凝縮の空気のみは、ライン3より、空
気ブロアBに戻され循環し、完全にパークレンが
回収される。 上記スラツジの加熱最適温度をみるため、加熱
温度を変えて空気放散を行ない、それによるスラ
ツジの乾燥減量を測定した。その結果、常温で
は、80分後でも20%程度の減量にすぎず、乾燥が
遅いに対し、120℃程度まで加熱するとわずか20
分で低沸成分約33%が揮散し、300℃程度で大き
な発熱(発火)が生じ、前者と併せて約70%の減
量となり灰として30%が残ることが確認された。 上記スラツジの加熱は処理時間が十分な場合に
は、ヒータH1、空気加熱器H3のいずれか一方だ
けを用いることもできる。 このように液状分を分離した後のタンクT1
は第3表に示す性状、組成のスラツジが残つてい
る。この表から判るように120℃程度まで加熱し
て空気放散を行うことによりパークレンは殆んど
除去できる。
[Table] On the other hand, only the non-condensed air is returned to the air blower B through line 3 and circulated, and the perclean is completely recovered. In order to determine the optimum temperature for heating the sludge, the heating temperature was changed to allow air to diffuse, and the resulting drying loss of the sludge was measured. As a result, at room temperature, the weight loss is only about 20% even after 80 minutes, and drying is slow, but when heated to about 120℃, the weight loss is only about 20%.
It was confirmed that approximately 33% of the low-boiling components were volatilized in minutes, and large heat generation (ignition) occurred at around 300℃, and when combined with the former, the weight was reduced by approximately 70% and 30% remained as ash. If the processing time is sufficient for heating the sludge, only one of the heater H 1 and the air heater H 3 may be used. After the liquid components have been separated in this way, sludge with the properties and composition shown in Table 3 remains in tank T1 . As can be seen from this table, most of the percrene can be removed by heating to about 120°C and dissipating the air.

【表】 放散条件:空気流速0.5/min、2時間放
散 このスラツジを点火装置Pにより発炎させ、同
時に排ガスダンパDEから排気しスラツジを燃焼
灰化させる。このようにして得られた灰はスラツ
ジ中の固形分のみが残ることから初期の約1/5に
減容し、かつ第4表の分析結果に示す通り無害化
されるので、容易に廃棄可能で必要に応じて処理
される。
[Table] Dispersion conditions: Air flow rate 0.5/min, dissipation for 2 hours This sludge is ignited by the igniter P, and at the same time it is exhausted from the exhaust gas damper D E to burn and ash the sludge. The ash thus obtained can be easily disposed of since only the solid content in the sludge remains, reducing the volume to about 1/5 of the initial volume and rendering it harmless as shown in the analysis results in Table 4. will be processed as necessary.

【表】【table】

【表】【table】

【表】 燃焼時の排ガス組成はCO2 16%、H2O 10%、
N2残、HCl 0.02%程度であつた。
[Table] The exhaust gas composition during combustion is CO 2 16%, H 2 O 10%,
The remaining N 2 and HCl were approximately 0.02%.

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

添付の図面は本発明の一実施態様を示すフロー
シートである。
The accompanying drawing is a flow sheet illustrating one embodiment of the invention.

Claims (1)

【特許請求の範囲】[Claims] 1 洗濯ドラムから排出される油状スラツジとフ
イルタから排出されるフイルタ材に由来するスラ
ツジとを回収タンクに蓄積し、同蓄積されたスラ
ツジを一定時間放置して液分と固形分とに分離
し、同分離した液分を蒸発器に導き加熱し、同液
分に含まれる溶剤と油とを分離して溶剤を回収
し、その後上記回収タンク内に残留する固形分を
加熱しながら空気を吹きつけて同固形分に含まれ
る溶剤を放散、回収し、そしてその残渣を上記回
収タンク内で燃してなることを特徴とするドライ
クリーニング機のスラツジ処理方法。
1. The oily sludge discharged from the washing drum and the sludge derived from the filter material discharged from the filter are accumulated in a collection tank, and the accumulated sludge is left for a certain period of time to separate into liquid and solid components. The separated liquid is guided to an evaporator and heated, the solvent and oil contained in the liquid are separated and the solvent is recovered, and then the solid remaining in the recovery tank is heated and blown with air. A method for treating sludge in a dry cleaning machine, characterized in that the solvent contained in the solid content is diffused and recovered, and the residue is burned in the recovery tank.
JP12101780A 1980-09-03 1980-09-03 Method of treating sludge in solvent tank of dry cleaning machine Granted JPS5745899A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP12101780A JPS5745899A (en) 1980-09-03 1980-09-03 Method of treating sludge in solvent tank of dry cleaning machine

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP12101780A JPS5745899A (en) 1980-09-03 1980-09-03 Method of treating sludge in solvent tank of dry cleaning machine

Publications (2)

Publication Number Publication Date
JPS5745899A JPS5745899A (en) 1982-03-16
JPS6336839B2 true JPS6336839B2 (en) 1988-07-21

Family

ID=14800734

Family Applications (1)

Application Number Title Priority Date Filing Date
JP12101780A Granted JPS5745899A (en) 1980-09-03 1980-09-03 Method of treating sludge in solvent tank of dry cleaning machine

Country Status (1)

Country Link
JP (1) JPS5745899A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63177898A (en) * 1987-01-19 1988-07-22 三洋電機株式会社 Apparatus for recovering solvent in distillation residue

Also Published As

Publication number Publication date
JPS5745899A (en) 1982-03-16

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