JPH10235320A - Reuse of treatment solution used in coating film peeling treatment by immersion and stirring of coating film waste - Google Patents

Reuse of treatment solution used in coating film peeling treatment by immersion and stirring of coating film waste

Info

Publication number
JPH10235320A
JPH10235320A JP7876097A JP7876097A JPH10235320A JP H10235320 A JPH10235320 A JP H10235320A JP 7876097 A JP7876097 A JP 7876097A JP 7876097 A JP7876097 A JP 7876097A JP H10235320 A JPH10235320 A JP H10235320A
Authority
JP
Japan
Prior art keywords
treatment
coating film
activated carbon
liquid
waste
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
JP7876097A
Other languages
Japanese (ja)
Inventor
Mitsuko Kadoma
光子 門間
Takahiro Minami
恭廣 南
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.)
HOKOKU ENJINIARINGUZU KK
SHIN KENSETSU KK
Original Assignee
HOKOKU ENJINIARINGUZU KK
SHIN KENSETSU KK
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 HOKOKU ENJINIARINGUZU KK, SHIN KENSETSU KK filed Critical HOKOKU ENJINIARINGUZU KK
Priority to JP7876097A priority Critical patent/JPH10235320A/en
Publication of JPH10235320A publication Critical patent/JPH10235320A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Water Treatment By Sorption (AREA)
  • Manufacture Of Porous Articles, And Recovery And Treatment Of Waste Products (AREA)
  • Processing And Handling Of Plastics And Other Materials For Molding In General (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • ing And Chemical Polishing (AREA)

Abstract

PROBLEM TO BE SOLVED: To repeatedly reuse an alkali aq. soln. used in coating film peeling treatment due to the immersion and stirring of waste of a coating film such as a magnetic film or a photosensitive film. SOLUTION: An aftertreatment soln. left after the coating film peeling treatment by an alkali aq. soln. being an initial treatment soln. is brought into contact with a corresponding amt. of active carbon to adsorb the solute such as the binder or gelatin dissolved in the aftertreatment soln. by active carbon to remove the same, and the filtrate restored in the effect of a chemical agent is used as the treatment soln. of the next peeling operation. In the same way, the treatment soln. for peeling treatment is repeated reused by the contact operation with active carbon.

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、磁気フィルムや感
光性フィルムのようにポリエチレンテレフタレートなど
の樹脂からなるベースフィルムに塗膜を塗工した塗膜フ
ィルムの廃棄物よりその塗膜を浸漬・攪拌によって剥離
処理する方法、より詳しくはその剥離処理に使用する処
理液の再利用に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method of immersing and agitating a coating film from the waste of a coating film obtained by applying a coating film to a base film made of a resin such as polyethylene terephthalate such as a magnetic film or a photosensitive film. More particularly, the present invention relates to a method for performing a stripping treatment, and more particularly, to a reuse of a treatment liquid used for the stripping treatment.

【0002】[0002]

【従来の技術】磁気フィルム廃棄物(使用済みの磁気カ
ード及びその製造過程で発生する該カードフィルムの打
抜き屑・切断屑(以下磁気カードという)、フロッピー
デイスクの使用済み磁気フィルム及びその製造過程で発
生する該フィルムの打抜き屑・切断屑(以下FD用磁気
フィルムという)、及び廃棄ビデオテープや録音テープ
及びその製造過程で発生する該フィルムの切断屑(以下
磁気テープという)などで、以下、単に磁気フィルムと
もいう)より磁性鉄粉及びその接着剤であるバインダー
から形成されている磁性塗膜を剥離し、ポリエチレンテ
レフタレート等の樹脂からなるベースフィルム(以下、
単にベースフィルムという)を回収する方法は、適正な
容器に磁気フィルムと適切な処理液とを入れ、これらを
適切な温度で適切に攪拌することによってなすものであ
る(以下、磁気フィルムや後述の感光性フィルムのよう
にベースフィルムに塗膜が塗工されているフィルムを塗
膜フィルムといい、塗膜フィルムを処理液に浸漬しなが
ら攪拌して塗膜を剥離する処理を、浸漬・攪拌による塗
膜剥離処理、浸漬・攪拌剥離処理、塗膜剥離処理、剥離
処理叉は単に処理という)が、ここで使用する処理液に
は、塩基性水溶液、とりわけ苛性ソーダを含むアルカリ
水溶液が有効である。
2. Description of the Related Art Magnetic film waste (used magnetic cards and punching and cutting wastes (hereinafter referred to as magnetic cards) of the card films generated during the manufacturing process thereof), used magnetic films of floppy disks and manufacturing processes thereof. In the following, there will be simply generated cutting waste and cutting waste of the film (hereinafter referred to as FD magnetic film), and waste video tape and recording tape and the cutting waste of the film generated during the manufacturing process (hereinafter referred to as magnetic tape). A magnetic film formed of a magnetic iron powder and a binder as an adhesive is peeled off from a magnetic film, and a base film made of a resin such as polyethylene terephthalate (hereinafter, referred to as a magnetic film).
The method of collecting the base film) is a method in which a magnetic film and an appropriate processing solution are put in an appropriate container and are appropriately stirred at an appropriate temperature (hereinafter, a magnetic film and an after-mentioned method). A film in which a coating is applied to a base film such as a photosensitive film is referred to as a coating film, and a process of removing the coating by stirring while dipping the coating film in a processing solution is performed by dipping and stirring. (Coating film peeling treatment, immersion / stirring peeling treatment, coating film peeling treatment, peeling treatment or simply treatment), but a basic aqueous solution, particularly an alkaline aqueous solution containing caustic soda, is effective as the treatment liquid used here.

【0003】本発明者の技術によれば、水酸化ナトリウ
ムを1.5重量%と炭酸ナトリウムを0.2重量%とを
含む水溶液に磁気フィルムを適正容器の中で浸漬し、こ
れらを適切に加温したうえで適切に攪拌すると、磁気フ
ィルム表面の磁性塗膜は、薄い膜状の叉は粉状の片(以
下、薄磁膜粉叉は浮遊沈澱物という)となってベースフ
ィルムより剥離し処理液中に浮遊叉は沈澱する。ベース
フィルムは、処理液中から回収の後、洗浄すれば、樹脂
として再利用可能である。
According to the technique of the present inventor, a magnetic film is immersed in an aqueous solution containing 1.5% by weight of sodium hydroxide and 0.2% by weight of sodium carbonate in an appropriate container, and these are appropriately immersed. When heated and stirred appropriately, the magnetic coating on the surface of the magnetic film peels off from the base film as thin film or powdery pieces (hereinafter referred to as thin magnetic film powder or floating precipitate). Floating or settling occurs in the processing solution. The base film can be reused as a resin if washed after being recovered from the processing solution.

【0004】しかし、上述のような磁気フィルムの再生
処理技術も、実用化については未だ問題があり、その一
つが、剥離処理を終えた処理液(以下、処理後液とい
う)を再使用できないという問題であった。即ち、浸漬
・攪拌による塗膜剥離処理において、磁性塗膜のバイン
ダーは、当初、処理液としたアルカリ水溶液(以下、剥
離処理に使用する前のアルカリ水溶液をバージン液とい
う)中にかなりの程度溶解するが、このバインダーを含
む処理後液は、同液内に浮遊し叉は沈澱する薄磁膜粉を
濾しても、そのままで次の磁気フィルムの剥離処理に使
用すると、初めのバージン液を使った処理に較べ、格段
に剥離効率が落ち、事実上、処理後液の次回処理への使
用は困難であった。そして、この理由から、処理後液は
処理の都度、廃液とされるのが実状であった。
However, there is still a problem in the practical use of the above-described magnetic film reproduction processing technology, and one of the problems is that a processing solution after peeling (hereinafter referred to as a post-processing solution) cannot be reused. It was a problem. That is, in the coating film peeling treatment by immersion and stirring, the binder of the magnetic coating film is initially dissolved to a considerable extent in an alkaline aqueous solution used as a treatment liquid (hereinafter, the alkaline aqueous solution before being used for the peeling treatment is referred to as a virgin liquid). However, if the liquid after treatment containing this binder is used for the next magnetic film peeling treatment even if the thin magnetic film powder that floats or precipitates in the liquid is filtered, the first virgin liquid will be used. The peeling efficiency was remarkably reduced as compared with the conventional treatment, and it was practically difficult to use the post-treatment liquid for the next treatment. For this reason, the post-treatment liquid is actually a waste liquid every time the treatment is performed.

【0005】例えば、本発明者の技術による適正な実験
容器を使用する場合、剥離処理する対象が磁気カードの
裁断物666gであるとき(以下、剥離処理の対象とす
る塗膜フィルムを処理物ともいう)は、適切加温及び適
切攪拌を条件として、同処理物のベースフィルムから磁
性塗膜及び印刷インク層が完全に剥離された状態(以
下、これを適正剥離叉は適正処理という)を得るには、
前記の薬品組成と濃度によるバージン液が4l必要であ
り、以上の条件の下で適正処理に要する時間は45分で
ある(以下、バージン液を用い適正及び適切な条件下で
適正剥離に要する時間を標準処理時間という)が、この
初回処理の処理後液3.7lを使用して、初回処理と同
じ条件下で、再度、同処理物616gを処理すると、こ
の2回目処理の適正剥離には2時間15分が必要であっ
た。次に、この2回目の処理後液の再度使用(バージン
液の3回使用)を試みたが、3時間を経ても剥離が進行
していない処理物が殆どで、事実上、適正剥離は困難で
あった。
[0005] For example, when an appropriate experimental container according to the technique of the present inventor is used, when the object to be peeled is 666 g of a cut piece of a magnetic card (hereinafter, a coated film to be peeled is referred to as a processed material. Is a condition in which the magnetic coating film and the printing ink layer are completely peeled off from the base film of the processed material under the conditions of appropriate heating and appropriate stirring (hereinafter, this is referred to as proper peeling or proper processing). In
4 liters of the virgin solution depending on the chemical composition and concentration is required, and the time required for proper treatment under the above conditions is 45 minutes (hereinafter, the time required for proper peeling under the proper and appropriate conditions using the virgin solution) Is referred to as a standard treatment time). When 616 g of the same treated material is treated again under the same conditions as in the first treatment by using 3.7 l of the liquid after the treatment in the first treatment, the proper peeling in the second treatment is required. Two hours and fifteen minutes were required. Next, an attempt was made to use the liquid after the second processing again (using the virgin liquid three times). However, most of the processed materials did not undergo peeling even after 3 hours, and in practice, it was difficult to properly peel off. Met.

【0006】処理後液は薄磁膜粉をフィルターで取り除
く過程で目減りしているので、これにバージン液をつぎ
足して次の処理液とすることが現実的であるが、こうし
ても、初回のバージン液使用の処理に較べ、剥離効率が
大きく落ちることは否めない。例えば、初回の処理は上
記と同じとした実験で、2回目の処理(処理物は666
g)において、標準処理時間45分で、適正剥離の状態
を得るには、初回処理の処理後液にどの程度バージン液
をつぎ足す必要があるかを調べたところ、2回目には6
0%のつぎ足し(処理後液1.6lにバージン液2.4
lの追加)が必要であった。この2回目の剥離処理の処
理後液に80%のつぎ足し(同0.8lに同3.2lの
追加)を行い3回目の剥離処理を行ったが、標準処理時
間ではまだ未剥離フィルムが残り、処理液は結局は全部
取り替えた方が現実的であると判断された。
Since the post-treatment liquid is reduced in the process of removing the thin magnetic film powder with a filter, it is practical to add a virgin solution to the treatment liquid to prepare the next treatment liquid. It cannot be denied that the peeling efficiency is greatly reduced as compared with the treatment using a liquid. For example, in an experiment in which the first processing was the same as the above, the second processing (processing object was 666)
In g), it was examined how much virgin liquid needs to be added to the liquid after the initial processing in order to obtain a proper peeling state in the standard processing time of 45 minutes.
0% addition (1.6 liters of virgin solution to 1.6 liters of solution after treatment)
1 addition) was required. After the processing of the second peeling treatment, the liquid was added by 80% (3.2 l added to the same 0.8 l) and the third peeling treatment was performed, but the unpeeled film still remains in the standard processing time. In the end, it was determined that it would be more practical to replace all of the treatment liquid.

【0007】処理液が再使用出来ない、即ち、処理毎に
バージン液を使うということは、処理の度毎、薬品コス
トが嵩むという問題とともに、実際上は処理後液をその
都度中和して凝集剤により溶解バインダーを除去するか
叉は活性汚泥処理をする工程が必要でこれらに要する装
置と薬剤のコストが嵩むことから、本格的な実用化を行
う上で大きな障害となっていると考えられていた。
The fact that the processing solution cannot be reused, that is, the use of a virgin solution for each process, means that the chemical cost increases each time the process is performed, and in practice, the post-process solution is neutralized each time. It is necessary to remove the dissolved binder with a coagulant or perform a process of activated sludge treatment, and the cost of equipment and chemicals required for these processes increases, which is considered to be a major obstacle to full-scale practical use. Had been.

【0008】感光性フィルム廃棄物(廃棄されたX線フ
ィルム、同写真フィルム、同撮影・映写用フィルム、同
印画紙及びこれらの製造過程で発生する裁断屑などで、
以下、単に感光性フィルムともいう)から銀粉とベース
フィルムを回収するための浸漬・攪拌剥離処理において
も、上述した磁気フィルムの処理とほぼ同様の問題が残
っていた。即ち、感光性フィルムは、ベースフィルム上
に臭化銀を混入したゼラチンを塗工したもの(現像・定
着後は臭化銀は黒化銀に変化している)であるが、ベー
スフィルムとゼラチン層との間に、ベースフィルムとは
異なる樹脂からなる下塗層が設けられている。感光性フ
ィルムを、塗膜剥離処理する場合、銀粉の回収だけな
ら、使用する容器が適正ならば、感光性フィルムを単に
温水に浸漬し、適切に攪拌するだけで目的を達せられる
が、この下塗層も剥離除去して適正なベースフィルムを
銀分とともに分離回収するには、上述の磁気フィルムと
同様に、塩基性水溶液、とりわけ苛性ソーダを含むアル
カリ水溶液による処理が有効である。
[0008] Photosensitive film waste (waste X-ray film, photographic film, photographic / projection film, photographic paper, and cutting waste generated during the production process, etc.
In the immersion / stirring treatment for recovering the silver powder and the base film from the photosensitive film (hereinafter simply referred to as a photosensitive film), almost the same problems as those of the magnetic film described above remain. In other words, the photosensitive film is a base film coated with gelatin mixed with silver bromide (silver bromide is changed to blackened silver after development and fixing). An undercoat layer made of a resin different from that of the base film is provided between the layers. When the photosensitive film is subjected to coating film peeling treatment, if the container to be used is appropriate only for collecting the silver powder, if the container to be used is appropriate, the objective can be achieved simply by immersing the photosensitive film in warm water and stirring appropriately. In order to separate and collect an appropriate base film together with silver by peeling off the coating layer, treatment with a basic aqueous solution, particularly an alkaline aqueous solution containing caustic soda, is effective as in the case of the above-mentioned magnetic film.

【0009】例えば、本発明者の技術による実験用適正
容器を用いたとき、裁断された使用済みX線フィルム6
66gより下塗層を含めて塗膜を剥離処理する場合は、
水酸化ナトリウムを0.5重量%を含む水溶液4lを処
理液として、適切加温で適切攪拌すれば、標準処理時間
20分をもって、適正剥離されたベースフィルムが得ら
れる。
For example, when an appropriate container for experiment according to the technique of the present inventor is used, the used X-ray film 6 which has been cut is used.
When peeling off the coating film including the undercoat layer from 66 g,
If 4 l of an aqueous solution containing 0.5% by weight of sodium hydroxide is used as a treatment liquid and the mixture is appropriately stirred while being appropriately heated, a properly peeled base film can be obtained in a standard treatment time of 20 minutes.

【0010】処理後液中の黒化銀は沈澱するので容易に
回収できる。下塗層の樹脂も細膜片として剥離し沈澱す
るので、濾布等で濾し除去できる(以下、剥離した銀粉
及び下塗層樹脂を銀粉等、叉は浮遊沈澱物ともいう)。
しかし、こうして混入物を回収・除去しても、残る溶解
ゼラチンを含む処理後液は、次の処理ではその剥離効率
が大きく低下することから実際には使用できず、結局は
処理の都度、処理液はバージン液とせざるを得ないのが
実状であった。即ち、感光性フィルム廃棄物の処理にお
いても、磁気フィルム廃棄物ほどではないにせよ、薬品
のコストが嵩み、また、大量の処理後液についてこれを
中和し、活性汚泥処理を行ったのち排水するというコス
トのかかる処置が必要であった。
After processing, the blackened silver in the solution precipitates and can be easily recovered. The resin of the undercoat layer also separates and precipitates as a thin film piece, and thus can be removed by filtration with a filter cloth or the like (hereinafter, the peeled silver powder and the undercoat layer resin are also referred to as silver powder or floating precipitates).
However, even if the contaminants are collected and removed in this way, the post-treatment liquid containing the remaining dissolved gelatin cannot be actually used because the peeling efficiency is greatly reduced in the next treatment. In fact, the liquid had to be a virgin liquid. That is, even in the treatment of photosensitive film waste, the cost of chemicals increases, though not as much as that of magnetic film waste, and after a large amount of treated liquid is neutralized and activated sludge treatment is performed. Costly treatment of draining was needed.

【0011】[0011]

【発明が解決しようとする課題】本発明は、磁気フィル
ム廃棄物処理及び感光性フィルム廃棄物処理の以上のよ
うな問題点を考慮しなされたものであって、その目的と
するところは、磁気フィルム及び感光性フィルムを含む
塗膜フィルムの浸漬・攪拌剥離処理の処理液として使用
するアルカリ水溶液で、剥離処理の過程で、磁気フィル
ムにあってはバインダー、感光性フィルムにあってはゼ
ラチンが溶け込んだ同水溶液の処理後液を廃液とせず、
次の剥離処理の処理液として使用できるようにし、以下
同じようにして当初の処理液を繰り返し再使用をする方
法を提供しようとするものである。
SUMMARY OF THE INVENTION The present invention has been made in consideration of the above-mentioned problems of magnetic film waste treatment and photosensitive film waste treatment. Alkaline aqueous solution used as a treatment solution for immersion and stirring peeling of coated films including films and photosensitive films. In the process of peeling, binder dissolves in magnetic films and gelatin dissolves in photosensitive films. After the treatment of the same aqueous solution, the liquid is not used as waste liquid.
It is an object of the present invention to provide a method for allowing the treatment liquid to be used as a treatment liquid for the next stripping treatment and for repeatedly reusing the original treatment liquid in the same manner.

【0012】[0012]

【課題を解決するための手段】上記目的を達成するため
に、本発明における方法は、磁気フィルム及び感光性フ
ィルムを含む塗膜フィルム廃棄物の浸漬・攪拌剥離処理
において、当初、処理液として使用するアルカリ水溶液
による剥離処理を終えて残る処理後液を、相当量の活性
炭に接触操作して、処理後液に溶解しているバインダー
等叉はゼラチン(以下溶質ともいう)を活性炭に吸着さ
せて該液中から除去し、以て該液の薬剤の効力を復する
ことにより、該液を次の剥離処理に使用できるように
し、以下同様の方法によって当初の処理液を繰り返し再
使用しようとするものである。
Means for Solving the Problems To achieve the above object, the method of the present invention is used as a treatment liquid in immersion and agitation peeling of coating film waste including a magnetic film and a photosensitive film. After the stripping treatment with the aqueous alkali solution, the remaining solution after the treatment is brought into contact with a considerable amount of activated carbon to adsorb the binder or gelatin (hereinafter also referred to as a solute) dissolved in the solution after the treatment to the activated carbon. By removing the liquid from the liquid and restoring the efficacy of the drug in the liquid, the liquid can be used for the next stripping treatment, and thereafter, the original processing liquid is repeatedly reused by the same method. Things.

【0013】[0013]

【発明の実施の形態】発明者は、今まで廃液とされてい
た磁気フィルムや感光性フィルムの処理後液を活性炭接
触操作により再生・再利用することを試行錯誤のうえ発
見したものであるが、そもそも塗膜フィルム廃棄物にあ
っては、塗膜の厚み、塗膜物質の組成、磁性鉄粉や銀粉
との混合割合、塗工の仕方など廃棄物の再生処理に重要
な技術情報が殆ど開示されておらず、従って、アルカリ
水溶液中の溶質の濃度からして不明であって活性炭吸着
前後の溶質濃度自体が測定できない等の困難から、本方
法の確立には後述するような多岐に亘る実験の積み重ね
が必要であった。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The inventor has found through trial and error that a liquid after processing a magnetic film or a photosensitive film, which has been a waste liquid, has been reproduced and reused by a contact operation with activated carbon. In the first place, in the case of paint film waste, most of the technical information that is important for waste recycling treatment, such as the thickness of the paint film, the composition of the paint film material, the mixing ratio with magnetic iron powder and silver powder, and the method of coating. It is not disclosed, and therefore, it is unknown from the concentration of the solute in the aqueous alkali solution, and it is difficult to measure the solute concentration itself before and after activated carbon adsorption. Experiments needed to be stacked.

【0014】これら実験結果によると、濾過材・吸着材
として製造された活性炭(植物系活性炭、石炭系活性
炭、石油系活性炭、骨炭、叉はこれらを成形したものを
含む)、燃料用本炭、叉は以上のものを混合したものを
含めて活性炭は、処理後液の再生に非常に有用である。
即ち、磁気フィルムや感光性フィルムなどのように、ポ
リエチレンテレフタレート等の樹脂からなるベースフィ
ルムに塗膜を塗工した塗膜フィルムを、容器の中で処理
液に浸漬しながら攪拌することにより、ベースフィルム
より塗膜を剥離する塗膜剥離処理において、当初、アル
カリ水溶液を用いて塗膜剥離処理を終えベースフィルム
を回収した後に、使用済みの液として残る処理後液を、
叉は該処理後液から浮遊沈澱物を除去した後の液体を、
相当量の活性炭に後述の濾過器通液法叉は混合固液分離
法によって接触操作すれば、以て得る濾過液を該塗膜剥
離処理に使用すると、当初のバージン液での標準処理時
間で、処理物の適正剥離の状態を得ることができる(以
下、活性炭との接触操作による濾過液を用いて剥離処理
を行う場合に、当初のバージン液での標準処理時間で適
正処理が得られるとき、該濾過液は「充分に使用でき
る」といい、この時用いた活性炭及びその量は「有効で
ある」という。そして、処理後液1l当りに換算して、
有効な活性炭のg重量を相当量といい、活性炭の飽和吸
着状態の下でそれ以上量を減らすと濾過液が充分に使用
できなくなる処理後液1l当り活性炭g重量を相当量下
限値という)。
According to the results of these experiments, activated carbon (including plant-based activated carbon, coal-based activated carbon, petroleum-based activated carbon, bone charcoal, or those obtained by molding them) produced as a filter material / adsorbent, Activated carbon, including those obtained by mixing the above, is very useful for regenerating the liquid after treatment.
That is, a coating film obtained by coating a coating film on a base film made of a resin such as polyethylene terephthalate, such as a magnetic film or a photosensitive film, is agitated while being immersed in a processing solution in a container, thereby forming a base. In the coating film peeling treatment to peel the coating film from the film, initially, after collecting the base film after finishing the coating film peeling treatment using an aqueous alkali solution, the post-treatment liquid remaining as a used liquid,
Alternatively, the liquid after removing suspended precipitates from the liquid after the treatment is
If a considerable amount of activated carbon is contacted with a filter passing method or a mixed solid-liquid separation method described below, and the resulting filtrate is used for the coating film peeling treatment, the standard treatment time with the initial virgin solution is used. It is possible to obtain a state of proper peeling of the processed material (hereinafter, when performing a peeling process using a filtrate by an operation of contacting with activated carbon, when a proper process can be obtained in a standard processing time with an initial virgin solution) The filtrate is said to be "sufficiently usable", and the activated carbon used at this time and its amount are said to be "effective."
The effective g weight of activated carbon is referred to as a considerable amount, and if the amount is further reduced under the saturated adsorption state of activated carbon, the filtrate cannot be sufficiently used.

【0015】処理後液の再生使用に必要な活性炭の相当
量は、(a)処理物の種類、とりわけ塗膜の厚さ、
(b)バージン液中の水酸化ナトリウムの濃度、(c)
剥離処理の時間、(d)使用する活性炭の種類、及び
(e)活性炭との接触方法によって変わってくる。しか
し、これらのうち(b)及び(c)は、本発明者の技術
においては適正値が適正濃度及び標準処理時間として概
ね決まっており、従ってこの適正剥離処理を前提とした
場合、その処理後液の再生に要する活性炭の相当量は、
処理物の種類、活性炭の種類及び接触方法に依存して決
まる。
The considerable amount of activated carbon necessary for reusing the post-treatment liquid is as follows: (a) the type of the treated product, especially the thickness of the coating film;
(B) concentration of sodium hydroxide in the virgin solution, (c)
It depends on the time of the peeling treatment, (d) the type of activated carbon used, and (e) the method of contacting with activated carbon. However, among these (b) and (c), in the technique of the present inventor, appropriate values are generally determined as appropriate densities and standard processing times. The amount of activated carbon required to regenerate the liquid is
It is determined depending on the type of the treated material, the type of the activated carbon and the contact method.

【0016】磁気フィルムの中で、塗膜が薄く溶解バイ
ンダーも少ないのはオーデオ用磁気テープの処理後液で
ある。逆に、バインダー量が多く叉印刷インクも処理液
に溶解して最も再生使用が難しいのが磁気カード処理後
液で、その相当量は該磁気テープの3倍以上必要であ
る。感光性フィルムも、そのゼラチン塗膜が剥離処理で
の加温により処理後液に全量が溶解するのでその溶質濃
度はかなり高く、活性炭相当量は該磁気テープの2倍程
度必要である。活性炭相当量が少なくて済むオーデオ用
磁気テープ処理後液の再生で最も効率が良かった活性炭
は、椰子殻炭をベースとした液相精製用の造粒活性炭で
あって、同活性炭を混合固液分離法で1時間かけて飽和
吸着させた場合、同処理後液1l当り同活性炭1gまで
有効であった。
Among the magnetic films, the one having a thin coating film and a small amount of a dissolved binder is a solution after processing a magnetic tape for audio. Conversely, the most difficult to reproduce and use is because the amount of binder is large and the printing ink is also dissolved in the processing liquid, and the most difficult to use is the post-magnetic-card processing liquid. The photosensitive film also has a considerably high solute concentration because the gelatin coating is completely dissolved in the liquid after the treatment by heating in the peeling treatment, and the equivalent amount of activated carbon is about twice that of the magnetic tape. The most effective activated carbon in the regeneration of the liquid after the magnetic tape treatment for audio, which requires a small amount of activated carbon, is granulated activated carbon for liquid phase purification based on coconut shell charcoal. When the saturated adsorption was carried out for 1 hour by the separation method, it was effective up to 1 g of the same activated carbon per liter of the liquid after the treatment.

【0017】最も一般的に使用される浄水用の粒状椰子
殻活性炭について、同様に、その飽和吸着状態での相当
量下限値を調べると、磁気カード処理後液で同液1l当
り3.4g程度、FD用磁気フィルムで同1.4g程
度、X線フィルムで同2.2g程度である。しかし、こ
の下限値は、活性炭との接触時間を1時間にとっての限
界値であって、濾過処理の時間効率を考えると、実際は
これより大きな値を相当量とせざるを得ない。とりわ
け、接触法が活性炭層への定圧通水であれば、活性炭の
相当量は上記下限値の1.5倍から2倍程度が必要であ
る。粒状椰子殻活性炭を用いた濾過器の場合、充填する
相当量は、磁気カード処理後液については同活性炭が同
液1l当り4.5〜6.5g、FD用磁気フィルム及び
磁気テープについては同2.5〜3.5g、及びX線フ
ィルムでは3〜5gとするのが好ましい(以下、これら
を粒状炭の濾過標準値という)。活性炭の種類による好
ましい相当量の差は、濾過材・吸着材として製造された
活性炭ではそれほど大きくはなく、せいぜい処理後液1
l当り1gの範囲内である。尤も、椰子殻活性炭と燃料
用の木炭では、必要とされる相当量に2倍程度の差があ
る。
In the same manner, the most commonly used granular coconut shell activated carbon for water purification was examined for its lower limit in its saturated adsorption state, and found to be about 3.4 g per liter of the liquid after magnetic card treatment. , About 1.4 g for FD magnetic films, and about 2.2 g for X-ray films. However, this lower limit is a limit for the contact time with activated carbon of one hour, and in view of the time efficiency of the filtration treatment, a value larger than this actually has to be considerable. In particular, if the contact method is constant-pressure water flow to the activated carbon layer, the equivalent amount of activated carbon needs to be about 1.5 to 2 times the lower limit. In the case of a filter using granular coconut shell activated carbon, the amount to be filled is 4.5 to 6.5 g per liter of the liquid after magnetic card treatment, and the same for FD magnetic film and magnetic tape. It is preferable that the weight is 2.5 to 3.5 g and that of an X-ray film is 3 to 5 g (hereinafter, these are referred to as filtration standard values of granular charcoal). The difference of the preferable equivalent amount depending on the type of the activated carbon is not so large in the activated carbon manufactured as the filtering material and the adsorbing material, and is at most 1% after treatment.
It is in the range of 1 g per liter. However, the required amount of the coconut shell activated carbon and the charcoal for fuel has a difference of about twice.

【0018】活性炭の相当量は、接触操作において、多
孔質繊維など活性炭以外の濾過材叉は珪藻土やパーライ
トなどの濾過補材を活性炭とともに併用すれば低く押さ
えることもできるが、処理後液の再生は活性炭で十分で
あり、また濾過材叉は濾過補材の後処理とコストを考慮
すると、活性炭単独使用の方が効率はよいとみられる。
The amount of activated carbon can be kept low by using a filter medium other than activated carbon such as porous fiber or a filter supplement such as diatomaceous earth or perlite in combination with activated carbon in the contacting operation. Activated carbon alone is sufficient, and considering the post-treatment and cost of the filter media or filter supplement, the use of activated carbon alone seems to be more efficient.

【0019】活性炭との接触方法としては、容器に活性
炭を充填した層を設け、処理後液を該層中を通過させる
濾過通液法と、槽叉は池(プール)に処理後液を導き貯
めた同液に活性炭を投入し、攪拌等による混合を行った
後、その液をフィルターで濾し、結果として活性炭によ
る濾過液を得る混合固液分離法があるが、実施にはどち
らを採用してもよい。また、これら二つの方法を併用し
てもよい。
As a method for contacting with activated carbon, a vessel filled with activated carbon is provided in a container and a filtered liquid is passed through the layer after the treatment, or the treated liquid is introduced into a tank or pond (pool). Activated carbon is poured into the stored liquid, mixed by stirring, etc., and then the liquid is filtered with a filter.As a result, there is a mixed solid-liquid separation method in which a filtered liquid with activated carbon is obtained. You may. Further, these two methods may be used in combination.

【0020】濾過器は、後述の実験で使用したような、
広口径のステンレスパイプの一方の口を下にしてそこに
活性炭粒が通過できない程度のメッシュのフィルターを
取付け、該フィルター上のパイプ内に活性炭を充填し、
上部の口より処理後液を注ぎ込む形の極く単純なもので
も十分である。勿論、工業用の濾過器で、活性炭を充填
したカートリッジを装脱着でき、通水液の量とその液圧
が容易に調節できるものを使用することが望ましい。ま
た、活性炭層が、固定層ではなく移動層若しくは流動層
となっている濾過器でもよい。
[0020] The filter, as used in the experiments described below,
A wide-diameter stainless steel pipe is attached with a filter of a mesh that does not allow activated carbon particles to pass through with one port facing down, and the pipe on the filter is filled with activated carbon.
An extremely simple one in which the solution after treatment is poured from the upper port is sufficient. Needless to say, it is desirable to use an industrial filter that can attach and detach a cartridge filled with activated carbon and that can easily adjust the amount of flowing water and the pressure thereof. Further, a filter in which the activated carbon layer is not a fixed bed but a moving bed or a fluidized bed may be used.

【0021】濾過器に充填する活性炭の相当量は、前記
の粒状炭の濾過標準値に、使用する活性炭の吸着特性を
加味して準備されることが好ましい。こうして準備した
活性炭濾過器の中を、当初、バージン液で剥離処理を行
った後に残る処理後液を、活性炭の種類・粒度・粒度の
均一性・充填密度・細孔分布によって異なる吸着速度を
考慮し、同液の活性炭層の通過速度が活性炭層の吸着速
度を上回らない状態で通過させる。こうすると、該濾過
器を通過して出てくる濾過液は、次の剥離処理の処理液
として充分に使用可能である。
It is preferable that a considerable amount of the activated carbon to be filled in the filter is prepared in consideration of the above-mentioned filtration standard value of the granular coal and the adsorption characteristics of the activated carbon to be used. In the activated carbon filter prepared in this way, the post-treatment liquid remaining after performing the stripping treatment with the virgin liquid is initially taken into account the adsorption speed that differs depending on the type, particle size, particle size uniformity, packing density, and pore distribution of activated carbon. Then, the liquid is passed in a state where the passage speed of the activated carbon layer does not exceed the adsorption speed of the activated carbon layer. In this case, the filtrate coming out of the filter can be sufficiently used as a treatment liquid for the next stripping treatment.

【0022】なお、浸漬・攪拌剥離処理においては、通
常、剥離処理を終えた後、処理液中からまずベースフィ
ルムを回収し、更に同液中の浮遊沈澱物を適切なメッシ
ュのフィルターをもって除去する処置を行うが、処理後
液の活性炭による濾過もこれらの処置を行った後の液に
ついて行うことが妥当である。浮遊沈澱物は、除去して
おかないと活性炭層の目詰まりの原因となる。
In the immersion / stirring stripping process, usually, after the stripping process is completed, first, the base film is recovered from the processing solution, and the suspended precipitate in the solution is removed with a filter having an appropriate mesh. Although treatment is performed, it is appropriate that filtration of the liquid after treatment with activated carbon is also performed on the liquid after these treatments. If the floating precipitates are not removed, they cause clogging of the activated carbon layer.

【0023】また、上記処置等により、処理後液は当初
の処理液に較べ7〜12%ほど目減りしており、活性炭
濾過器の通液においても若干のロスがあるため、濾過液
を使用する際は、同液にバージン液を12〜20%ほど
追加混合して次の剥離処理の処理液とするのが現実的で
あるが、実用化ではこの方式をとるものとみられる。
Also, due to the above treatments and the like, the treated liquid is reduced by about 7 to 12% as compared with the original treated liquid, and there is a slight loss in the passage through the activated carbon filter. In this case, it is practical to add a virgin solution to the same solution in an amount of about 12 to 20% to obtain a processing solution for the next stripping process. However, it is considered that this method will be used in practical use.

【0024】濾過器に充填する活性炭の相当量を、当初
から十分大きくとっておけば、濾過液の次回処理液とし
ての不足分はバージン液で補って同じ処理物について次
回の剥離処理を適正に行い、その処理後液で浮遊沈澱物
の除去処置を行った後の液を、一度使用した活性炭濾過
器を再度通過させて2回目の濾過液を得、これを更に次
の剥離処理に充分に使用することができる。同様にし
て、濾過器内の活性炭の相当量を十分にとっておけば、
叉はこれを更新すれば、処理後液を同じ活性炭を使って
濾過し、濾過液の処理液としての不足分はバージン液で
補いながら、適正な剥離処理を何回も繰り返し行ってい
くことができる。こうして、この処理液の繰り返し使用
を行っていくことにより、実質的に処理後液を廃液とす
る処置は不要となる。
If a sufficient amount of the activated carbon to be filled in the filter is set to be sufficiently large from the beginning, the shortage of the filtrate as the next treatment liquid is supplemented with a virgin liquid so that the next stripping treatment of the same treated material can be properly performed. After the treatment, the liquid after the treatment of removing suspended precipitates was passed through the activated carbon filter used once again to obtain a second filtrate, which was sufficiently used for the next stripping treatment. Can be used. Similarly, if a sufficient amount of activated carbon in the filter is reserved,
Alternatively, if this is renewed, it is possible to filter the solution after treatment using the same activated carbon, and repeat the appropriate peeling treatment many times while supplementing the deficiency of the filtrate with the virgin solution. it can. In this way, by repeatedly using the treatment liquid, there is no need to substantially treat the treated liquid as a waste liquid.

【0025】なお、処理後液の再生を濾過器をもって行
う場合、使用する活性炭は、活性炭自体をも再生処理で
きるものが望ましい。即ち、750〜950℃の高温で
焼成された活性炭は、使用により溶質吸着力が失われて
も、培焼再賦活法により吸着力を回復させること(再
生)が可能であり、処理後液を再生・使用するととも
に、そのための濾過材も再生・使用でき、廃棄物処理に
おいて一つの閉じた系を構築できるからである。
When the liquid after the treatment is regenerated with a filter, the activated carbon used is preferably one that can also regenerate the activated carbon itself. That is, activated carbon fired at a high temperature of 750 to 950 ° C. can recover (regenerate) the adsorptive power by the cultivation reactivation method even if the solute adsorptive power is lost by use, and the treated liquid is This is because, together with the recycling and use, the filter medium for that can be recycled and used, and one closed system can be constructed in the waste treatment.

【0026】混合固液分離法による方法は、例えば、後
述する実験では、混合槽としてステンレス製の缶を使
い、処理後液から浮遊沈澱物を除去した後の液をこの缶
の中に注入し、同時に活性炭を缶に投入して攪拌棒で攪
拌混合してのち、その液を濾布で濾し、その濾過液を次
の剥離処理に使用している。勿論、混合槽は、処理後液
の注入、活性炭の投入、攪拌が自動化され、固液分離も
自動的に行えるものが望ましい。また、混合槽では、活
性炭以外の溶質吸着材及び凝集剤のいずれか叉はこれら
両方と活性炭を併用混合して効果を高めてもよい。
In the method based on the mixed solid-liquid separation method, for example, in an experiment to be described later, a stainless steel can is used as a mixing tank, and the liquid after removing suspended precipitates from the treated liquid is poured into this can. At the same time, activated carbon is put into a can and stirred and mixed with a stirring rod, and the liquid is filtered with a filter cloth, and the filtrate is used for the next peeling treatment. Needless to say, it is desirable that the mixing tank is one in which the injection of the post-treatment liquid, the charging of the activated carbon, the stirring, and the solid-liquid separation can be performed automatically. In addition, in the mixing tank, the effect may be enhanced by mixing a solute adsorbent other than activated carbon and / or a coagulant or both together with activated carbon.

【0027】混合槽で活性炭を処理液に混合する場合
も、その必要な相当量は、処理物の種類、使用する活性
炭の種類と混合時間に依存するが、これも前述の粒状炭
濾過標準値を基準として考えればよい。混合固液分離法
で有用な粉末活性炭の飽和吸着での相当量下限値は、前
記粒状炭の下限値とは処理後液1l当り0.5g以内の
差もないと判断されるからである。混合の時間の取り方
と固液分離を適切に行えば、以て得る濾過液は、同じ処
理物の次の剥離処理に充分に使用できる。なお、混合槽
より固液分離して回収した活性炭濾過液を、次の剥離処
理の処理液として使用するに際し、バージン液を追加し
てもよいことは、前記濾過器使用の場合と同じである。
When the activated carbon is mixed with the treatment liquid in the mixing tank, the required substantial amount depends on the type of the treated material, the type of the activated carbon to be used, and the mixing time. Should be considered as a reference. This is because it is determined that the lower limit of the amount of powdered activated carbon useful in the mixed solid-liquid separation method in saturated adsorption is not less than 0.5 g per liter of the liquid after treatment from the lower limit of the granular carbon. If the mixing time is properly set and the solid-liquid separation is properly performed, the filtrate obtained as described above can be sufficiently used for the next stripping treatment of the same processed material. When the activated carbon filtrate obtained by solid-liquid separation and recovery from the mixing tank is used as a treatment liquid for the next stripping treatment, a virgin solution may be added in the same manner as in the case of using the filter. .

【0028】磁気フィルム処理では、処理後液からベー
スフィルムを回収した後、薄磁膜粉を除去せずそのまま
混合槽に導き、活性炭でバインダーを吸着させた後、液
は濾過して次の剥離処理に使用し、一方、残りの薄磁膜
粉及び活性炭は自然乾燥の後焼却し、この残灰を水洗す
るなどしてマグネットにより磁性鉄粉を回収するのが効
率的である。この場合は、再生には適さないが安い粉末
活性炭を利用できるので、コスト面での効率は上がるも
のと推定される。
In the magnetic film treatment, after the base film is recovered from the liquid after the treatment, the thin magnetic film powder is not removed and the mixture is directly guided to a mixing tank, the binder is adsorbed by activated carbon, and the liquid is filtered and then separated. On the other hand, it is efficient that the remaining thin magnetic film powder and activated carbon are incinerated after being naturally dried, and the residual ash is washed with water or the like to collect the magnetic iron powder with a magnet. In this case, it is presumed that the cost-effectiveness is improved because cheap powdered activated carbon, which is not suitable for regeneration, can be used.

【0029】感光性フィルムも同様であって、ベースフ
ィルムを回収後の処理後液を銀粉等を含んだまま混合槽
に導き、活性炭を混合した後、適切なフィルターで濾
し、濾過液は次の処理に使用するとともに、フィルター
に残った活性炭を含む固体分は乾燥のうえ焼却して銀粉
を回収するのが効率的である。
The same applies to the photosensitive film. The liquid after treatment after collecting the base film is led to a mixing tank containing silver powder and the like, mixed with activated carbon, and filtered with a suitable filter. It is efficient that the solid content containing activated carbon remaining in the filter is dried and incinerated to collect silver powder while being used for the treatment.

【0030】バージン液における水酸化ナトリウムの濃
度は低い方が望ましい。水酸化ナトリウムの濃度が高い
と、とりわけ磁気フィルム処理の場合、溶解バインダー
の濃度が高くなり、それだけ速く活性炭は吸着力を喪失
するからである。しかし、水酸化ナトリウムの濃度が2
重量%以下で、その処理後液が標準処理時間でのものな
らば、同液は、前記粒状炭の濾過標準値を基準とした適
当な量の活性炭で再生でき、その濾過液を次の剥離処理
に充分に使用することができる。なお、処理後液を活性
炭で濾過しても、その濾過液のpH値は、同液温での比
較では、濾過前の処理後液と殆ど変化がなく、従って、
水酸化ナトリウム濃度が低い水溶液の場合でも、それを
活性炭で濾過したがためにその濾過液が使用できなくな
るということはない。磁気フィルム及び感光性フィルム
の浸漬・攪拌剥離処理で必要な水酸化ナトリウムの濃度
範囲0.2〜2重量%の全ての濃度について、その処理
後液は活性炭濾過により充分に使用可能である。
It is desirable that the concentration of sodium hydroxide in the virgin solution is low. The higher the concentration of sodium hydroxide, especially in the case of magnetic film processing, the higher the concentration of the dissolved binder, the faster the activated carbon loses its adsorptive power. However, when the concentration of sodium hydroxide is 2
% By weight or less, and if the liquid after the treatment is at the standard treatment time, the liquid can be regenerated with an appropriate amount of activated carbon based on the filtration standard value of the granular carbon, and the filtrate is subjected to the next peeling. Can be used sufficiently for processing. In addition, even if the liquid after treatment is filtered with activated carbon, the pH value of the filtrate is almost the same as the liquid after treatment before filtration in comparison at the same liquid temperature.
Even in the case of an aqueous solution having a low sodium hydroxide concentration, the filtrate is not unusable because it is filtered with activated carbon. For all concentrations in the concentration range of 0.2 to 2% by weight of sodium hydroxide required for the immersion and agitation peeling treatment of the magnetic film and the photosensitive film, the solution after the treatment can be sufficiently used by filtration with activated carbon.

【0031】磁気フィルムの処理液としては、水酸化ナ
トリウムに炭酸ナトリウムを僅かに添加した水溶液が有
用であるが、この処理後液の活性炭濾過液を使用しても
その剥離効果は殆ど変わらない。即ち、活性炭はこの炭
酸ナトリウムに対しても中立とみられる。使用する同薬
品の濃度範囲0.05〜0.5重量%と上記水酸化ナト
リウムの濃度範囲0.2〜2重量%の全ての組み合わせ
について、その処理後液は適当な相当量をもって活性炭
に接触操作すれば、その濾過液は充分に使用可能であ
る。
As a treatment solution for the magnetic film, an aqueous solution obtained by adding a little sodium carbonate to sodium hydroxide is useful. However, even if an activated carbon filtrate as a solution after the treatment is used, the stripping effect is hardly changed. That is, activated carbon is considered to be neutral with respect to this sodium carbonate. For all combinations of the concentration range of 0.05 to 0.5% by weight of the same chemical used and the concentration range of 0.2 to 2% by weight of the above sodium hydroxide, the treated liquid was brought into contact with activated carbon in an appropriate considerable amount. If operated, the filtrate is fully usable.

【0032】本発明は、浸漬・攪拌による塗膜剥離処理
に使ったアルカリ水溶液を活性炭に適切な相当量で接触
操作して、その濾過液を次の剥離処理に使うと、当初の
バージン液使用と殆ど変わらず剥離の適正処理ができ
る、というごく単純なものであるが、極めて効果が大き
く、且つ銀分叉は磁性鉄粉の回収をも含め廃棄塗膜フィ
ルムの再生回収処理を効率化する。尤も、未解明な点も
多く、とりわけ、活性炭が溶解しているバインダー叉は
ゼラチンを吸着していることは明かであるにしても、こ
れらを吸着除去した後の液体が、なぜ当初に使用するバ
ージン液とほぼ変わらない効力をもって剥離処理に使用
できるのか、という理由−これは、アルカリ水溶液の塗
膜剥離のメカニズムとも関係するが−は、発明者におい
ても明かではない。以下、本発明の基礎となった諸実験
を実施例として説明する。
According to the present invention, when the alkali aqueous solution used for the coating film peeling treatment by dipping and stirring is brought into contact with activated carbon in an appropriate amount and the filtrate is used for the next peeling treatment, the initial virgin liquid Although it is a very simple thing that the proper treatment of peeling can be performed almost as it is, it is extremely effective, and the efficiency of the recycling and recovery processing of the waste coating film including the recovery of silver or magnetic iron powder is improved. . However, there are many unclear points, especially if it is clear that the binder or gelatin in which the activated carbon is dissolved is adsorbed, but the liquid after adsorption and removal of these is why the liquid is used initially. The reason that the virgin liquid can be used for the peeling treatment with almost the same effect as the virgin liquid-which is related to the mechanism of peeling off the coating film of the alkaline aqueous solution-is not clear even to the inventor. Hereinafter, various experiments on which the present invention is based will be described as examples.

【0033】[0033]

【実施例1】処理物がフロッピーデイスクを製造する過
程で発生する磁気フィルムの打抜き枠(FD打抜枠)
で、バージン液が水酸化ナトリウムを1.5重量%と炭
酸ナトリウムを0.2重量%とを含む水溶液で、これに
よる標準処理時間が40分の剥離処理において、その初
回処理の処理後液を濾過器通液法により活性炭に接触操
作し、その濾過液を次回の剥離処理に使用する実験を行
った。ここで、活性炭濾過器は、上部口径120%のス
テンレス製漏斗を準備し、その内側に濾布を敷き、ここ
に粒状椰子殻活性炭を30g入れたものとした(使用し
た活性炭については表1参照、同表に以下の実験で使用
した活性炭の仕様を一覧する)。
Embodiment 1 Punching frame for magnetic film (FD punching frame) generated in the process of manufacturing a floppy disk
The virgin solution is an aqueous solution containing 1.5% by weight of sodium hydroxide and 0.2% by weight of sodium carbonate, and in the stripping treatment for a standard treatment time of 40 minutes, the liquid after the first treatment is used. An experiment was performed in which the activated carbon was brought into contact with a filter by a filter passing method, and the filtrate was used for the next stripping treatment. Here, as the activated carbon filter, a stainless steel funnel having an upper diameter of 120% was prepared, a filter cloth was laid inside the funnel, and 30 g of granular coconut shell activated carbon was put therein (see Table 1 for the activated carbon used). The table lists the specifications of the activated carbon used in the following experiments.)

【0034】[0034]

【表1】 [Table 1]

【0035】本実験を説明すると、まず、処理物666
gを実験用の適正容器に入れバージン液4lに浸漬し
て、適切に加温のうえ適切に攪拌して、初回の磁性塗膜
の剥離処理を行った。この条件下では、通常、処理物は
標準処理時間40分をもって適正に剥離処理されるが、
この初回処理でもその通りの適正処理の結果を得た。
The experiment will be described.
g was placed in an appropriate container for experiments, immersed in 4 l of virgin solution, heated appropriately, and stirred appropriately to perform the first peeling treatment of the magnetic coating film. Under these conditions, the processed product is normally properly peeled with a standard processing time of 40 minutes.
In this initial processing, the result of the appropriate processing was obtained.

【0036】初回の剥離処理を終えた処理後液からベー
スフィルムを回収した後、同液を濾布で濾して、浮遊す
る叉は沈澱している薄磁膜粉を除去した。ここまでの過
程で同液は、容器及び濾布への付着と除去物の吸着によ
り、3.62lに減っていた。この処理後液を、上記活
性炭濾過器に静かに注ぎ、流出する濾過液を回収した。
なお、濾過器へ注入した処理後液の温度は45℃であっ
た。そして、回収した濾過液3.60lをそのまま次の
剥離処理の処理液とし、処理液が初回より足らない分、
処理物を同割合減らして次回の剥離処理を行った。この
次回処理も、初回のバージン液での標準処理時間と同じ
40分で処理を終え、ベースフィルムの剥離状態を検査
した。即ち、処理済みベースフィルムから検査サンプル
を10重量%抽出し、これらサンプル片について一つ一
つ、未剥離塗膜、叉は、バインダー及び印刷インクの未
剥離による色斑が残っていないかどうかを目視により検
査した。この結果、上記活性炭濾過器に通液して得た濾
過液を処理液とした処理は、全く問題のない適正な剥離
状態であった。
After recovering the base film from the liquid after the first peeling treatment, the liquid was filtered with a filter cloth to remove floating or precipitated thin magnetic film powder. In the process so far, the liquid has been reduced to 3.62 liters due to adhesion to the container and the filter cloth and adsorption of the removed matter. The liquid after this treatment was gently poured into the activated carbon filter, and the filtrate flowing out was collected.
In addition, the temperature of the solution after the treatment injected into the filter was 45 ° C. Then, 3.60 l of the collected filtrate is used as it is as a treatment liquid for the next stripping treatment, and the treatment liquid is smaller than the first treatment liquid.
The next stripping process was performed with the processed material reduced by the same ratio. This next processing was also completed in 40 minutes, which is the same as the standard processing time with the first virgin liquid, and the peeling state of the base film was inspected. That is, 10% by weight of the test sample was extracted from the treated base film, and each of these sample pieces was checked for any unremoved coating film or whether there was any color spot due to unremoved binder and printing ink. Inspection was made visually. As a result, the treatment using the filtrate obtained by passing through the activated carbon filter as the treatment liquid was in a proper peeling state without any problem.

【0037】[0037]

【実施例2及び比較例】次に、処理物を使用済みの磁気
カードを2分の1に裁断したもの666gとし、バージ
ン液の薬品組成と濃度及びこれによる初回液量は実施例
1に同じであるが、標準処理時間が45分である剥離処
理についで、活性炭濾過液と非濾過液の剥離処理の差を
確認するため次の二つの実験を行った。即ち、一方は処
理後液を活性炭濾過せず、処理後液から薄磁膜粉を10
0メッシュのフィルターで除去した液のうち3.2l
に、バージン液を0.8lを加えて次回の処理液とし、
これで剥離処理を行う実験(比較例)、他方は処理後液
を実施例1と同じ漏斗型の活性炭濾過器を通過させ、そ
の濾過液のうち3.2lに0.2lのバージン液を足し
てこれにより次回の剥離処理を行う実験(実施例2)で
ある。なお、実施例2で漏斗型濾過器に入れる活性炭
は、3〜15メッシュに粉砕した未加工椰子殻活性炭3
0gを用いた。
EXAMPLE 2 AND COMPARATIVE EXAMPLE Next, the used magnetic card was cut into half, and the processed material was cut into 666 g. The chemical composition and concentration of the virgin liquid and the initial amount of the liquid were the same as in Example 1. However, following the stripping treatment in which the standard treatment time was 45 minutes, the following two experiments were performed to confirm the difference between the stripping treatments of the activated carbon filtrate and the non-filtrate. That is, one does not filter the solution after the treatment with activated carbon, and removes the thin magnetic film powder from the solution after the treatment by 10%.
3.2 l of the liquid removed by the 0 mesh filter
, 0.8 l of virgin solution was added to make the next processing solution,
In the experiment (comparative example) in which the peeling treatment is performed, the treated liquid is passed through the same funnel-type activated carbon filter as in Example 1, and 0.2 l of virgin liquid is added to 3.2 l of the filtrate. This is an experiment (Example 2) in which the next peeling process is performed. In addition, the activated carbon put into the funnel-type filter in Example 2 was a raw coconut shell activated carbon 3 ground to 3 to 15 mesh.
0 g was used.

【0038】比較例と実施例2の結果は表2の如くで、
活性炭濾過液を使用した実施例2では、標準処理時間4
5分で問題のない適正剥離の結果を得たが、比較例の活
性炭濾過をしない処理後液の使用では、20%のバージ
ン液を追加したにもかかわらず、45分では処理物の6
6%が、磁性塗膜が未だ剥落していない叉はバインダー
や印刷インクが未だ薄く残った非適正剥離の状態であっ
た。ちなみに、検査のフィルムサンプルを剥離処理の容
器に戻し、適正剥離の状態になるまで検査を繰り返しな
がら剥離処理を続けたところ、この処理液で適正剥離の
状態に達するには丁度2時間が必要であった。
The results of Comparative Example and Example 2 are as shown in Table 2.
In Example 2 using the activated carbon filtrate, the standard treatment time was 4 hours.
Although the result of proper peeling without any problem was obtained in 5 minutes, in the case of using the post-treatment liquid without the activated carbon filtration of the comparative example, 6% of the processed material was obtained in 45 minutes despite the addition of 20% virgin solution.
6% was in an improper peeling state in which the magnetic coating film had not yet peeled off, or the binder and the printing ink had still remained thinly. By the way, the film sample of the inspection was returned to the container of the peeling process, and the peeling process was continued while repeating the inspection until the proper peeling state was reached. It took just 2 hours to reach the proper peeling state with this processing solution. there were.

【0039】[0039]

【実施例3】感光性フィルム廃棄物の処理後液について
の実験をほぼ実施例1に準じた仕様で行った。まず、処
理物は約20m/m×30m/mの矩形に裁断された使
用済みX線フィルム(X線FLM)666gで、初回処
理液としてのバージン液は水酸化ナトリウム0.5重量
%を含む水溶液4.0l、これによる標準処理時間は2
0分、剥離状態の検査は、処理後洗浄したベースフィル
ムを5重量%抽出し、ルーペにより、未剥離の銀含有ゼ
ラチン塗膜叉は下塗層によるベースフィルムの非透明度
合を検査する方法である。
Example 3 An experiment on a liquid after treatment of a photosensitive film waste was carried out in substantially the same manner as in Example 1. First, the processed material is 666 g of used X-ray film (X-ray FLM) cut into a rectangle of about 20 m / m × 30 m / m, and the virgin liquid as the first processing liquid contains 0.5% by weight of sodium hydroxide. 4.0 liters of aqueous solution, the standard processing time of which is 2
Inspection of the peeling state for 0 minute is performed by extracting 5% by weight of the washed base film after the treatment, and inspecting the non-transparency of the base film by the unstripped silver-containing gelatin coating film or the undercoat layer using a loupe. is there.

【0040】濾過器は実施例1及び2に同じで、使った
活性炭は石炭系粒状活性炭30gである。処理後液は、
剥離した銀粉及び下塗層樹脂の細膜片を濾布で濾して除
去した液で、同液を漏斗型濾過器に静かに注いで得た濾
過液をそのまま次回の処理液とした(バージン液を追加
しない代わりに処理物を減らすことは実施例1に同
じ)。この濾過液の次回処理使用も、初回バージン液で
の標準処理時間で、全く問題のない適正剥離の結果を得
た。
The filter was the same as in Examples 1 and 2, and the activated carbon used was 30 g of coal-based granular activated carbon. After treatment,
A solution obtained by filtering the exfoliated silver powder and thin film pieces of the undercoat layer resin with a filter cloth and gently pouring the solution into a funnel-type filter to obtain a filtrate as it is as the next treatment solution (virgin solution) Is the same as in Example 1 in that the number of processing objects is reduced instead of not adding). In the next treatment use of the filtrate, the result of proper peeling without any problem was obtained in the standard treatment time with the first virgin solution.

【0041】[0041]

【表2】 [Table 2]

【0042】[0042]

【実施例4〜7】様々な塗膜フィルム廃棄物処理で、そ
の処理後液に対する活性炭の相当量下限値を見極めるた
めに諸実験を行ったが、これら諸実験の中から重要な結
果を抜粋し以下説明する。
Examples 4 to 7 In various coating film waste treatments, various experiments were conducted to determine the lower limit of the amount of activated carbon in the liquid after the treatment, and important results were extracted from these experiments. This will be described below.

【0043】実験で対象としたのは、磁気カード(仕様
は実施例2に同じ)、FD用磁気フィルム(同1に同
じ)、磁気テープ(使用済みのオーデオテープを50m
/mに裁断したもの)、及びX線フィルム(仕様は実施
例3に同じ)であり、使用するバージン液は、発明者の
浸漬・攪拌塗膜剥離技術において各処理物に必要とされ
る適正濃度(磁気フィルム及び感光性フィルムともに水
酸化ナトリウム0.2〜2.0重量%と、及び、叉は炭
酸ナトリウム0.05〜0.5重量%の範囲)とした。
標準処理時間は、磁気カードが45分、FD用磁気フィ
ルム40分、磁気テープ35分、及びX線フィルムが2
0分である。
In the experiment, a magnetic card (specifications were the same as in Example 2), a magnetic film for FD (same as in Example 1), a magnetic tape (used audio tape of 50 m) were used.
/ M) and an X-ray film (the specifications are the same as in Example 3). Concentration (in the range of 0.2 to 2.0% by weight of sodium hydroxide and 0.05 to 0.5% by weight of sodium carbonate for both the magnetic film and the photosensitive film).
The standard processing time is 45 minutes for magnetic card, 40 minutes for FD magnetic film, 35 minutes for magnetic tape, and 2 minutes for X-ray film.
0 minutes.

【0044】使用する活性炭は、粒状椰子殻活性炭と木
質系粉末活性炭の2種類(以下、粒状炭、粉末炭と略
す)で、これら活性炭との接触操作は、槽に入れた処理
後液に活性炭を投入し混合したのち同混合液を固液分離
する混合固液分離法とした。これは、本実験では活性炭
の飽和吸着状態での相当量下限値をみる必要から、活性
炭が吸着平衡の状態に達する大体1時間という比較的長
い時間、処理後液と接触させる必要があるためである。
混合槽としてはステンレス製の12l缶を用い、活性炭
との混合攪拌は攪拌棒で行い、活性炭を投入して1時間
経過した混合液を濾布で濾し、濾過液を得ることとし
た。濾過液の次回使用については、その有効性の限界を
みる目的から、バージン液は追加せず、同液のうち3.
5lを次回処理に使用することとした。なお、その分、
処理物の重量を減らして剥離処理を行った。
The activated carbon used is of two types, granular coconut shell activated carbon and wood-based powdered activated carbon (hereinafter abbreviated as granular charcoal and powdered charcoal). Was added and mixed, and then the mixed liquid was subjected to solid-liquid separation. This is because, in this experiment, it is necessary to see the lower limit of the amount of activated carbon in the saturated adsorption state, and it is necessary to make the activated carbon come into contact with the liquid after treatment for a relatively long time of about 1 hour to reach the state of adsorption equilibrium. is there.
A 12-liter stainless steel can was used as a mixing tank, and mixing and stirring with activated carbon was performed with a stirring rod. The activated carbon was charged, and the mixed solution after one hour had passed was filtered through a filter cloth to obtain a filtrate. For the next use of the filtrate, the virgin solution was not added for the purpose of checking the limit of its effectiveness.
5 l was used for the next processing. In addition,
The peeling treatment was performed by reducing the weight of the treated material.

【0045】上記仕様に基ずく活性炭の相当量下限値の
探索実験は、各活性炭について処理後液1lに対するそ
れらの量を減らしながら、初回・次回の剥離処理を重ね
る単純なものであるが、例えば磁気カード処理後液の粒
状炭では、同液1l当り6gから1gずつ減らしていく
と、同液1l当り3gで処理物は5%の非適正剥離とな
った。しかし、同3.5gでは適正剥離が得られた。即
ち、磁気カード処理後液の粒状炭についての相当量下限
値は同液1l当り3.5gを少し切った辺りと考えられ
る。表3の実施例4として磁気カードでの結果をまとめ
る(以下、処理後液1l当り活性炭重量をg/lとも表
記する)。粒状炭及び粉末炭ともに3.4g/l程度と
みておくのが妥当である。
The search experiment for the lower limit of the equivalent amount of activated carbon based on the above specifications is a simple one in which the first and next peeling treatments are repeated while reducing the amount of each activated carbon per 1 liter of the treated liquid. As for the granular charcoal of the liquid after the magnetic card treatment, when the amount was reduced by 1 g from 6 g per liter of the liquid, the processed material was improperly peeled by 5% at 3 g per liter of the liquid. However, at 3.5 g, proper peeling was obtained. That is, it is considered that the lower limit of the amount of the granular coal in the liquid after the magnetic card processing is slightly less than 3.5 g per liter of the liquid. Table 3 summarizes the results of a magnetic card as Example 4 (hereinafter, the weight of activated carbon per liter of the treated liquid is also expressed as g / l). It is appropriate to consider that both the granular coal and the powdered coal are about 3.4 g / l.

【0046】[0046]

【表3】 [Table 3]

【0047】上記磁気カードと同じように実験して得た
FD用磁気フィルムの結果は、表4の実施例5のようで
ある。FD用磁気フィルムの相当量下限値は、粒状炭で
1.5g/lくらい、粉末炭でこれを少し切る辺りと判
断できる。
The results of the magnetic film for FD obtained by conducting the experiment in the same manner as the magnetic card are as shown in Example 5 of Table 4. The lower limit of the equivalent amount of the magnetic film for FD can be determined to be about 1.5 g / l for granular charcoal and to cut it slightly with powdered charcoal.

【0048】[0048]

【表4】 [Table 4]

【0049】表5の実施例6にみるように、磁気テープ
の処理後液は処理物の中で最も相当量下限値が低い。粉
末炭は1g/lで3%の非適正剥離の状態となったが、
粒状炭ではごく僅かな非適正剥離フィルムがみられただ
けであった。両炭での下限値は、1.2g/lから1.
4g/lの辺りとみられる。なお、椰子殻炭をベースと
した液相精製用の造粒活性炭を同じ条件で飽和吸着させ
た場合、この磁気テープ処理後液で1g/lまで有効で
あった。
As shown in Example 6 in Table 5, the liquid after treatment of the magnetic tape has the lowest lower limit in the amount of the treated material. Powdered charcoal was 3% improper peeling at 1g / l,
Only a few improper release films were seen with the granular coal. The lower limit for both coals is from 1.2 g / l to 1.
It seems to be around 4 g / l. In addition, when granulated activated carbon for liquid phase purification based on coconut shell charcoal was saturated and adsorbed under the same conditions, the liquid after the magnetic tape treatment was effective up to 1 g / l.

【0050】[0050]

【表5】 [Table 5]

【0051】X線フィルムの実験結果は表6の実施例7
の如くであり、この結果から、X線フィルムの処理後液
の活性炭の相当量下限値は2.2g/l程度と判断され
る。
The experimental results of the X-ray film are shown in Table 6 in Example 7.
From this result, it is determined that the lower limit of the amount of activated carbon in the liquid after the treatment of the X-ray film is about 2.2 g / l.

【0052】[0052]

【表6】 [Table 6]

【0053】[0053]

【実施例8】活性炭の相当量を充分に多くとった場合、
その同じ活性炭を使って初回使用のバージン液を何回ま
で再使用していけるかを、磁気カード剥離処理におい
て、また接触操作を濾過器通液法により実験した。実験
の仕様は表7の如くである。即ち、まず、内径57m/
mのステンレス製パイプの底に30メッシュのステンレ
ス製フィルターを取り付け、パイプ内に浄水用の粒状椰
子殻活性炭を190g充填した活性炭濾過器を作成し
た。該濾過器内の活性炭の充填密度は0.44g/cm
であった。処理物は実施例2に同じ磁気カードの1/
2裁断物・666gで、当初のバージン液は水酸化ナト
リウム1.5重量%と炭酸ナトリウム0.2重量%を含
む水溶液4l、標準処理時間は45分である。処理後液
の上記濾過器への通液は、パイプ上部に処理後液を全て
注ぎ、液圧により自然通過させる形にした。なお、通液
は薄磁膜粉を除去した後の液について行なった。また、
処理後液の液温は35℃にして通液した。濾過液の全量
回収には時間がかかるので、次回使用の濾過液は3.2
lとし、剥離処理の都度、0.8lのバージン液をつぎ
足していくこととした。
Example 8 When a considerable amount of activated carbon was taken sufficiently,
The number of times the virgin solution used for the first time can be reused using the same activated carbon was tested in the magnetic card peeling treatment and the contact operation was conducted by a filter passing method. Table 7 shows the specifications of the experiment. That is, first, the inner diameter 57m /
A stainless steel filter of 30 mesh was attached to the bottom of a stainless steel pipe having a length of m, and an activated carbon filter was prepared in which 190 g of granular coconut shell activated carbon for water purification was filled in the pipe. The packing density of activated carbon in the filter is 0.44 g / cm.
It was 3 . The processed material was 1 / of the same magnetic card as in Example 2.
Two cut pieces, 666 g, the initial virgin solution was 4 l of an aqueous solution containing 1.5% by weight of sodium hydroxide and 0.2% by weight of sodium carbonate, and the standard processing time was 45 minutes. The liquid after the treatment was passed through the above-mentioned filter, and all the liquid after the treatment was poured into the upper portion of the pipe, and the liquid was allowed to pass naturally by the liquid pressure. The liquid was passed through the liquid after removing the thin magnetic film powder. Also,
The liquid temperature of the liquid after the treatment was 35 ° C., and the liquid was passed. Since it takes time to collect the whole amount of the filtrate, the filtrate to be used next time is 3.2.
1 and 0.8 l of virgin liquid was added each time the peeling treatment was performed.

【0054】[0054]

【表7】 [Table 7]

【0055】以上の実験仕様のもと、初回の剥離処理の
みをバージン液で行い、次回以降の処理は80%の活性
炭濾過液に20%のバージン液を追加した処理液で行
い、同じ活性炭190g濾過器を繰り返し使用して剥離
処理とその検査を繰り返した訳であるが、この実験の結
果は、表8の実施例8のようである。この処理液の繰り
返し再使用実験では、粒状椰子殻活性炭190gを充填
した濾過器で10回通液の濾過液まで充分使用が可能で
あった(これは、累積注入液量叉は回収液量でみて同活
性炭5.1〜5.3g/lの段階である)。即ち、12
回目の剥離処理(11回通液での濾過液を使用)では4
%の非適正剥離の状態が現れた。更に実験を続けたとこ
ろ、濾過器を14回使用したところで濾過器の目詰まり
状態が顕著になり(濾過に要する時間が極端に長くな
り)、16回目の濾過では、該濾過器は濾過の初めから
液の滴下状態が延々と続くほぼ完全な目詰まり状態をき
たした。この粒状活性炭は16回目の通液でほぼ飽和吸
着に近い状態に達したものとみられるが、ここまでの累
積注入液量は約56lで、同液1l当り同活性炭3.4
g、非剥離分を液量換算し差し引いたベースでは約52
l、同3.7gであった。
Based on the above experimental specifications, only the first stripping treatment was performed with a virgin solution, and the subsequent treatment was performed with a treatment solution obtained by adding a 20% virgin solution to an 80% activated carbon filtrate, and 190 g of the same activated carbon was used. The stripping process and the inspection were repeated using the filter repeatedly. The results of this experiment are as shown in Example 8 of Table 8. In the re-use experiment of this treatment solution, it was possible to sufficiently use the filtrate which was passed 10 times with a filter filled with 190 g of granular coconut shell activated carbon (this was due to the cumulative amount of the injected liquid or the amount of the recovered liquid). The activated carbon is at a stage of 5.1 to 5.3 g / l). That is, 12
In the fourth stripping process (using the filtrate after 11 passages)
% Improper peeling appeared. When the experiment was further continued, the clogged state of the filter became remarkable when the filter was used 14 times (the time required for the filtration became extremely long). In the 16th filtration, the filter was used at the beginning of the filtration. The liquid was almost completely clogged, where the dripping state of the liquid continued for a long time. This granular activated carbon is considered to have reached a state close to almost saturated adsorption on the 16th passage, but the cumulative injection volume up to this point is about 56 l, and the activated carbon is 3.4 per 1 l of the same liquid.
g, about 52
1, 3.7 g.

【0056】本実験での濾過は自然液圧によるものであ
るが、9回目の通液から液の回収時間が急速に長くなっ
た。実際には定圧通液を採ることになるので、仮に、こ
の9回及び10回目の濾過液も定圧下では充分使用でき
ない可能性もあるとみても、8回まで繰り返し使用が充
分に可能であったと判断することができる。
In this experiment, the filtration was performed by natural hydraulic pressure, but the recovery time of the liquid from the 9th passage was rapidly increased. Actually, a constant-pressure flow is employed, so even if the ninth and tenth filtrates may not be sufficiently used under a constant pressure, they can be repeatedly used up to eight times. Can be determined.

【0057】[0057]

【表8】 [Table 8]

【0058】[0058]

【発明の効果】本発明は、以上のような方法であるの
で、以下に記載されるような効果を奏する。
According to the present invention, since the method is as described above, the following effects can be obtained.

【0059】従来、廃液とし、中和したのち、液中の溶
質を高分子凝集剤を投与して除去するか叉は活性汚泥処
理を行うか、場合によってはこの双方の処置を講じざる
を得なかった、磁気フィルム廃棄物や感光性フィルム廃
棄物のような塗膜フィルム廃棄物の浸漬・攪拌剥離処理
で使用するアルカリ水溶液の処理後液を、次の剥離処理
に充分に使用することができる。また、この再使用の処
理液も更に次の剥離処理に再使用することができる。
Conventionally, after the waste liquid is neutralized, the solute in the liquid is removed by administering a polymer coagulant or activated sludge treatment, and depending on the case, both treatments have to be taken. The post-treatment liquid of the alkaline aqueous solution used in the immersion and agitation peeling treatment of the coating film waste such as the magnetic film waste and the photosensitive film waste can be sufficiently used for the next peeling treatment. . In addition, this reused processing solution can be reused in the next stripping process.

【0060】処理後液を再生する決め手である活性炭の
相当量を充分に大きく取っておけば、処理後液の濾過を
同じ活性炭への接触操作で行い、その濾過液の処理液と
しての不足分はバージンのアルカリ水溶液で補いなが
ら、当初のアルカリ水溶液を何回も繰り返し再使用して
いくことができる。また、活性炭が飽和吸着の状態にな
ったとき、これを更新していけば、実質的に、処理後液
を廃液として処置するということがなくなる。
If a sufficient amount of activated carbon, which is a decisive factor for regenerating the liquid after treatment, is sufficiently large, filtration of the liquid after treatment is carried out by the same operation as that of activated carbon, and the shortage of the filtrate as a treatment liquid is reduced. The original alkaline aqueous solution can be reused many times repeatedly while supplementing with virgin alkaline aqueous solution. In addition, when the activated carbon is in a state of saturated adsorption, if the activated carbon is renewed, the treated liquid is not substantially treated as a waste liquid.

【0061】このように、活性炭濾過液を次回の処理液
として充分に使用できたことによって、剥離処理の都度
のバージン液使用が不用となり、塗膜フィルム廃棄物の
処理に要するアルカリ薬品のコストが大幅に削減され
る。
As described above, since the activated carbon filtrate can be sufficiently used as the next processing liquid, the use of a virgin liquid every time of the stripping treatment becomes unnecessary, and the cost of the alkali chemicals required for the treatment of the coating film waste is reduced. It is greatly reduced.

【0062】剥離処理の都度廃液とせざるを得なかった
処理後液の中和剤及び凝集剤投与の処置並びに活性汚泥
処理の必要がなくなることから、塗膜剥離によるベース
フィルムの回収、及び磁性鉄粉叉は銀粉の回収のコスト
が大幅に低減する。
Since the necessity of a neutralizing agent and a coagulant administration treatment and an activated sludge treatment of the post-treatment liquid, which had to be used as a waste liquid every time of the stripping treatment, is eliminated, the recovery of the base film by the coating film stripping and the magnetic iron The cost of collecting powder or silver powder is greatly reduced.

【0063】活性炭として再賦活再生ができるものを使
用すれば、塗膜剥離処理での処理液を再使用していける
のみならず、これを可能ならしめる活性炭も、再生の目
減り分を補いながら、再使用して行けるという意味で、
塗膜フィルム廃棄物処理において一つの閉じた系を構築
することができる。
If the activated carbon that can be reactivated and regenerated is used, not only can the processing solution in the coating film peeling treatment be reused, but also the activated carbon that makes this possible, while compensating for the loss in regeneration, In the sense that it can be reused,
One closed system can be constructed in coating film waste treatment.

フロントページの続き (51)Int.Cl.6 識別記号 FI C23F 1/46 B09B 5/00 ZABR Continued on the front page (51) Int.Cl. 6 Identification code FI C23F 1/46 B09B 5/00 ZABR

Claims (12)

【特許請求の範囲】[Claims] 【請求項1】 ベースフィルムに塗膜を塗工した塗膜フ
ィルムの廃棄物を容器の中で処理液に浸漬しながら攪拌
することによりベースフィルムより塗膜を剥離する塗膜
剥離処理において、処理液として、当初、アルカリ水溶
液を用いて塗膜剥離処理を終えベースフィルムを回収し
た後に、使用済みの液として残る処理後液を、相当量の
活性炭に接触操作し、以て得る濾過液を該塗膜剥離処理
の処理液として使用することを特徴とする塗膜フィルム
廃棄物の浸漬・攪拌による塗膜剥離処理で使用する処理
液を再使用する方法。
In a coating film peeling treatment for peeling a coating film from a base film by agitating while immersing a waste of the coating film in which a coating film is applied to a base film in a processing solution in a container, As a liquid, after the coating film peeling treatment is completed using an alkaline aqueous solution and the base film is recovered, the post-treatment liquid remaining as a used liquid is contacted with a considerable amount of activated carbon to obtain a filtrate obtained by the operation. A method for reusing a treatment liquid used in a coating film peeling treatment by immersing and stirring coating film waste, which is used as a treatment liquid for a coating film peeling treatment.
【請求項2】 前記塗膜フィルムは、磁気カード、フロ
ッピーデイスク用磁気フィルム、及び磁気テープのいず
れか1つである請求項1に記載の塗膜フィルム廃棄物の
浸漬・攪拌による塗膜剥離処理で使用する処理液を再使
用する方法。
2. The coating film peeling treatment according to claim 1, wherein the coating film is one of a magnetic card, a magnetic film for a floppy disk, and a magnetic tape. To reuse the processing solution used in the process.
【請求項3】 前記塗膜フィルムは、X線フィルム、写
真フィルム、撮影・映写用フィルム、及び印画紙のいず
れか1つである請求項1に記載の塗膜フィルム廃棄物の
浸漬・攪拌による塗膜剥離処理で使用する処理液を再使
用する方法。
3. The coating film waste according to claim 1, wherein the coating film is one of an X-ray film, a photographic film, a photographing / projection film, and a photographic paper. A method of reusing the treatment liquid used in the coating film peeling treatment.
【請求項4】 前記アルカリ水溶液は、0.2〜2重量
%の水酸化ナトリウムと0.05〜0.5重量%の炭酸
ナトリウムを含む水溶液である請求項1及び2に記載の
塗膜フィルム廃棄物の浸漬・攪拌による塗膜剥離処理で
使用する処理液を再使用する方法。
4. The coating film according to claim 1, wherein the aqueous alkali solution is an aqueous solution containing 0.2 to 2% by weight of sodium hydroxide and 0.05 to 0.5% by weight of sodium carbonate. A method of reusing a treatment liquid used in a coating film peeling treatment by immersing and stirring waste.
【請求項5】 前記アルカリ水溶液は、0.2〜2重量
%の水酸化ナトリウムを含む水溶液である請求項1、及
び2叉は3に記載の塗膜フィルム廃棄物の浸漬・攪拌に
よる塗膜剥離処理で使用する処理液を再使用する方法。
5. The coating film obtained by immersing and agitating a coating film waste according to claim 1, wherein the alkaline aqueous solution is an aqueous solution containing 0.2 to 2% by weight of sodium hydroxide. A method of reusing the processing solution used in the stripping process.
【請求項6】 前記活性炭に接触操作することは、活性
炭を充填した濾過器に、叉は活性炭に加え、活性炭以外
の濾過材及び濾過補材の双方叉はいずれかを充填した濾
過器に、通液することである請求項1に記載の塗膜フィ
ルム廃棄物の浸漬・攪拌による塗膜剥離処理で使用する
処理液を再使用する方法。
6. The contact operation with the activated carbon may be performed by using a filter filled with activated carbon or a filter filled with a filter material other than activated carbon and / or a filter supplement other than activated carbon. The method for reusing a treatment liquid used in a coating film peeling treatment by immersion and stirring of the coating film waste according to claim 1, wherein the liquid is passed.
【請求項7】 前記活性炭に接触操作することは、活性
炭とともに混合する槽に、叉は活性炭に加え、活性炭以
外の吸着材及び凝集剤の双方叉はいずれかとともに混合
する槽に、導液し該混合をおこなったのち、適切なフィ
ルターをもって個体と液体を分離することである請求項
1に記載の塗膜フィルム廃棄物の浸漬・攪拌による塗膜
剥離処理で使用する処理液を再使用する方法。
7. The contact operation with the activated carbon may be performed by introducing the liquid into a tank mixed with the activated carbon or into a tank mixed with an adsorbent other than the activated carbon and / or a coagulant in addition to the activated carbon. The method for reusing a treatment liquid used in a coating film peeling treatment by immersion and stirring of a coating film waste according to claim 1, wherein after the mixing is performed, the solid and the liquid are separated with a suitable filter. .
【請求項8】 前記活性炭に接触操作することは、請求
項6に記載のことと請求項7に記載のことを併用して行
うことである請求項1に記載の塗膜フィルム廃棄物の浸
漬・攪拌による塗膜剥離処理で使用する処理液を再使用
する方法。
8. The immersion of the coated film waste according to claim 1, wherein the operation of contacting the activated carbon is performed by using both the operations described in claim 6 and 7. A method of reusing a treatment liquid used in a coating film peeling treatment by stirring.
【請求項9】 前記活性炭は、椰子殻炭を含む植物系活
性炭、燃料用本炭、石炭系活性炭、石油系活性炭、骨
炭、これらを成形したもの、及びこれらを混合したもの
のいずれか1つである請求項1、及び2叉は3、及び4
叉は5、及び6叉は7叉は8に記載の塗膜フィルム廃棄
物の浸漬・攪拌による塗膜剥離処理で使用する処理液を
再使用する方法。
9. The activated carbon is any one of plant-based activated carbon including coconut shell charcoal, main fuel for fuel, coal-based activated carbon, petroleum-based activated carbon, bone charcoal, a molded product thereof, and a mixture thereof. Certain claims 1 and 2 or 3 and 4
Or a method of reusing a treatment liquid used in a coating film peeling treatment by immersion and agitation of the coating film waste described in 5 or 6 or 7 or 8.
【請求項10】 前記相当量は、処理後液1l当り活性
炭1g以上である請求項1、及び2叉は3、及び4叉は
5、及び6叉は7叉は8、及び9に記載の塗膜フィルム
廃棄物の浸漬・攪拌による塗膜剥離処理で使用する処理
液を再使用する方法。
10. The method according to claim 1, wherein the equivalent amount is 1 g or more of activated carbon per liter of the treated liquid. 1 or 2 or 3 or 4 or 5 and 6 or 7 or 8 or 9. A method of reusing a treatment liquid used in a coating film peeling treatment by dipping and stirring coating film waste.
【請求項11】 前記処理後液は、塗膜より剥離した薄
磁膜粉叉は銀粉等の浮遊物叉は沈澱物を除去した後の液
体である請求項1、及び2叉は3、及び4叉は5、及び
6叉は7叉は8、及び9、及び10に記載の塗膜フィル
ム廃棄物の浸漬・攪拌による塗膜剥離処理で使用する処
理液を再使用する方法。
11. The liquid after treatment is a liquid after removing suspended matters or precipitates such as thin magnetic film powder or silver powder peeled from a coating film, and the liquid after the treatment is two or three, and 4. A method for reusing a treatment liquid used in a coating film peeling treatment by immersion and agitation of a coating film waste described in 4 or 5, and 6 or 7 or 8, 9 and 10.
【請求項12】 前記処理液として、次回以降の塗膜剥
離処理においては、濾過液、叉は濾過液にアルカリ水溶
液を追加混合した液体を用いる請求項1、及び2叉は
3、及び4叉は5、及び6叉は7叉は8、及び9、及び
10、叉は11に記載の塗膜フィルム廃棄物の浸漬・攪
拌による塗膜剥離処理で使用する処理液を再使用する方
法。
12. The treatment liquid used in the next and subsequent coating film peeling treatments is a filtrate or a liquid obtained by additionally mixing an alkaline aqueous solution with the filtrate. 5. A method for reusing a treatment liquid used in a coating film peeling treatment by immersion and agitation of coating film waste as described in 5, 6 or 7, or 8, 9 and 10, or 11.
JP7876097A 1997-02-24 1997-02-24 Reuse of treatment solution used in coating film peeling treatment by immersion and stirring of coating film waste Pending JPH10235320A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
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Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
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Publications (1)

Publication Number Publication Date
JPH10235320A true JPH10235320A (en) 1998-09-08

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Country Link
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPWO2005049710A1 (en) * 2003-11-21 2007-06-07 株式会社クレハ Recycling method for laminated moldings
KR101133651B1 (en) 2011-05-11 2012-04-10 (주)삼흥금속 The methode for acquisition of pet and silver from the waste x-ray film

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPWO2005049710A1 (en) * 2003-11-21 2007-06-07 株式会社クレハ Recycling method for laminated moldings
JP4571587B2 (en) * 2003-11-21 2010-10-27 株式会社クレハ Recycling method of laminated moldings
KR101133651B1 (en) 2011-05-11 2012-04-10 (주)삼흥금속 The methode for acquisition of pet and silver from the waste x-ray film

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