JPS5814958A - Method and apparatus for treating waste film for regenerated stock material - Google Patents
Method and apparatus for treating waste film for regenerated stock materialInfo
- Publication number
- JPS5814958A JPS5814958A JP56114683A JP11468381A JPS5814958A JP S5814958 A JPS5814958 A JP S5814958A JP 56114683 A JP56114683 A JP 56114683A JP 11468381 A JP11468381 A JP 11468381A JP S5814958 A JPS5814958 A JP S5814958A
- Authority
- JP
- Japan
- Prior art keywords
- waste film
- cleaning
- film
- tank
- 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.)
- Granted
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/02—Separating plastics from other materials
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/02—Separating plastics from other materials
- B29B2017/0213—Specific separating techniques
- B29B2017/0286—Cleaning means used for separation
- B29B2017/0289—Washing the materials in liquids
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29K—INDEXING SCHEME ASSOCIATED WITH SUBCLASSES B29B, B29C OR B29D, RELATING TO MOULDING MATERIALS OR TO MATERIALS FOR MOULDS, REINFORCEMENTS, FILLERS OR PREFORMED PARTS, e.g. INSERTS
- B29K2105/00—Condition, form or state of moulded material or of the material to be shaped
- B29K2105/06—Condition, form or state of moulded material or of the material to be shaped containing reinforcements, fillers or inserts
- B29K2105/065—Condition, form or state of moulded material or of the material to be shaped containing reinforcements, fillers or inserts containing impurities
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29L—INDEXING SCHEME ASSOCIATED WITH SUBCLASS B29C, RELATING TO PARTICULAR ARTICLES
- B29L2007/00—Flat articles, e.g. films or sheets
- B29L2007/008—Wide strips, e.g. films, webs
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/62—Plastics recycling; Rubber recycling
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Mechanical Engineering (AREA)
- Cleaning By Liquid Or Steam (AREA)
- Processing Of Solid Wastes (AREA)
- Separation Of Solids By Using Liquids Or Pneumatic Power (AREA)
- Processing And Handling Of Plastics And Other Materials For Molding In General (AREA)
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
Abstract
Description
【発明の詳細な説明】
可塑性合成樹脂よりなるフィルム廃棄物孕再生利用する
ためにフィルムに付着・介在する夾雑物や汚染物等の異
物ケ分離・除去する方法ならびに該方法ケ実施するため
の装置に関するものである。[Detailed description of the invention] A method for separating and removing foreign substances such as impurities and contaminants adhering to or intervening in a film in order to recycle film waste made of plastic synthetic resin, and an apparatus for carrying out the method. It is related to.
近年省エネルギー問題、特に石油及びそれr、原料とす
る1次、2次製品の節約並びに、効率的利用の問題が頓
に表面化して来た。一方、園芸作物に対する需要の多様
化、高度化r反映した施設農芸の普及に伴ない、塩ビフ
ィルム紮主流とすぎ農業用フィルムの使用量が急激に伸
び、従ってその廃棄Mt%急速に増加しつつある。力・
がるプラスチックス製品の廃棄については前記の省エネ
ルギー問題及び公害問題の両面からの再検討を迫られ、
効果的に解決する為の有力な対策の一つとして廃棄物の
再生利用が挙げられている。In recent years, issues of energy conservation, particularly the conservation and efficient use of petroleum, its primary and secondary products as raw materials, have suddenly come to the fore. On the other hand, with the diversification of demand for horticultural crops and the spread of cultivated agriculture reflecting the increasing sophistication, the use of PVC film and agricultural film has rapidly increased, and as a result, the amount of waste Mt% has increased rapidly. be. Power·
We are forced to reconsider the disposal of plastic products from both the energy conservation and pollution issues mentioned above.
Recycling of waste has been cited as one of the effective measures to effectively solve the problem.
ところで、農家力・ら回収して集積される廃プラスチツ
クフイルム束の中には通常、土砂、小石。By the way, the waste plastic film bundles that are collected and accumulated by farmers usually contain earth, sand, and pebbles.
針金、釘、罐、ガラス等の夾雑物や汚泥、油力等の不純
物が介在、付着しており、従って先ずかかる異物の分離
除去ケ行なって清浄な素材とすることが、後続の粉砕、
精製、再生等の工程?効率良く安全に遂行する上で特に
重要であり、高度に清浄化されたプラスチック素材に効
率良く転換する方法の出現は大きな意義を産むものであ
る。Contaminants such as wires, nails, cans, and glass, as well as impurities such as sludge and oil, are present or adhered to the material. Therefore, it is important to first separate and remove such foreign materials to obtain a clean material, which can be used for subsequent crushing and
Processes such as refining and regeneration? This is especially important for efficient and safe execution, and the emergence of a method to efficiently convert to highly purified plastic materials is of great significance.
そこでかかる廃プラスチックスフィルム、特に農業・園
芸用ノゝウスやトンネルに汎用されている・ポリ塩化ビ
ニルやポリエチレンからなるフィルム廃棄物の処理に関
し従来より関心もたれ、その再生利用が試みられて来た
。Therefore, there has long been interest in the treatment of such waste plastic films, especially film waste made of polyvinyl chloride and polyethylene, which are widely used in agricultural and horticultural fields and tunnels, and attempts have been made to recycle them. .
この従来適用されている再生利用の方法は一般に先ず廃
フィルムr束ねて圧縮された塊状で粗砕工程に送り、裁
断機によって約5oWrIn程度の幅に粗砕した後、次
の異物分離工程で処理する方法であるが、この異物分離
工程は通常、水流の下方から気泡による攪拌洗浄を行な
うことによって小石。In this conventional recycling method, the waste film is first bundled and compressed into chunks and sent to a crushing process, and after being crushed into a width of about 5oWrIn by a cutting machine, it is processed in the next foreign matter separation process. However, this foreign matter separation process is usually carried out by stirring and cleaning with air bubbles from below the water stream to remove pebbles.
釘、砂、泥等が除去されている。そしてこれらのフィル
ム片は更に次の粉砕工程で13〜3 Otrrm W度
の大きさに裁断されると共に更にポリ分離工程で、混在
しているポリエチレンフィルム等をポリ塩化ビニル力為
ら分離して、ポリ塩化ビニルのみが次の脱水工程へ送ら
れている。Nails, sand, mud, etc. have been removed. These film pieces are further cut into pieces of 13 to 3 Otrrm W degrees in the next crushing process, and in a poly separation process, the mixed polyethylene films and the like are separated from the polyvinyl chloride. Only polyvinyl chloride is sent to the next dehydration step.
脱水は回転するコーンとコーン内で回転するスクリュー
とによって構成されている遠心脱水機が普通使用されて
おり、フィルム片はコーンの中央に送入され遠心力の作
用r受けてコーン壁面に押し付けられ、水分はコーンの
直径の大きい下方向に除去される。かくして脱水された
フィルム片はスクリュー、によって掻き上げられ、次の
乾燥工程で乾燥されて最終製品である所謂フランとなる
。For dehydration, a centrifugal dehydrator is usually used, which consists of a rotating cone and a screw rotating inside the cone, and the film pieces are fed into the center of the cone and pressed against the wall of the cone under the action of centrifugal force. , water is removed in the downward direction of the larger diameter of the cone. The thus dehydrated film pieces are scraped up by a screw and dried in the next drying step to form the final product, so-called furan.
フランは例えば塩化ビニルパイプの成型用原料として再
生利用される。Furan is recycled, for example, as a raw material for molding vinyl chloride pipes.
ところが、上記従来の方法において異物分離工程の分離
作用は主として水中における空気攪拌によっているため
、小石、金属、砂等、比重の大きい異物は除去されるも
のの、フィルム面にこび9着いた比較的比重の軽い汚泥
物は除去し難く、殊に油力等は殆ど除去できない状況で
ある。However, in the conventional method described above, the separation action in the foreign matter separation step is mainly based on air agitation in the water, so although foreign matter with a high specific gravity such as pebbles, metal, sand, etc. It is difficult to remove light sludge, especially when using oil or the like.
又処理前のフィルム片は経年変化によって稍々硬化して
いる上に、圧縮して束ねられ、堆積貯蔵中に更に加圧さ
れ、皺、折目、襞等の変形が固定された状態になってお
り、水中でも充分に伸展しないため、それら変形の間に
介在、付着する異物や汚水は更に脱落し難い。この工程
における清浄度の不足は、最終製品の品質r低下させる
ばかりでなく、後続工程に種々の悪影響r及ぼす。即ち
、次の粉砕工程では、油脂分が残留していると裁断刃の
切れを悪くし、汚泥分が残っていると刃葡損傷したり、
摩耗ケ早めたりすることになる。又、汚泥が次の脱水工
程迄残留しでいるとコーンの内壁面に砂泥が沈積し、ス
クリューと壁面にフランが挾まれて、スクリューの羽根
r曲損させたり、脱水効率を低下せしめる′等の不都合
ケ生ずる。In addition, the unprocessed film pieces have become slightly hardened due to aging, are compressed and bundled, and are further pressurized during stacking and storage, so that deformations such as wrinkles, folds, and folds are fixed. Since it does not fully expand even in water, it is even more difficult for foreign matter and sewage that are interposed or attached during the deformation to fall off. Insufficient cleanliness in this process not only reduces the quality of the final product, but also has various negative effects on subsequent processes. In other words, in the next crushing process, residual oil and fat will make the cutting blades difficult to cut, and residual sludge will damage the cutting blades.
This will lead to faster wear. In addition, if sludge remains until the next dewatering process, sand and mud will settle on the inner wall of the cone, and the flan will get caught between the screw and wall, causing the screw blades to become bent and reducing dewatering efficiency. Other inconveniences may occur.
そしてこれらの汚水r除去せんとして、粉砕工程やポリ
分離工程で充分な水洗を行なっても好結果は得られない
。In order to remove these sewage r, good results cannot be obtained even if sufficient washing with water is carried out in the crushing process or polyseparation process.
そこで本発明者は斯かる従来技術の問題点ケ解消すべく
鋭意研究を行ない、その結果、超音波の洗浄効果に着目
し、これケ利用し、同時に加熱ケ行なうことにより、清
浄効果が相乗的に増大し、前記の汚水や夾雑物r極めて
短時間内に完全に除去し得ること〒知見し、さきに熱可
塑性合成樹脂よりなる廃フィルム塊状物ケ粗砕後、洗浄
液中に浸漬し、洗浄液中の廃フィルムが柔軟状態となっ
て該フィルム上に形成固定された皺、襞等の変形が伸展
し実質的に消滅する程度の液流に洗浄液r保持し、この
適温下節浄液の流動ケ利用して廃フィルム片の塊状物γ
液中で解舒泳動せしめつつ柔軟化し、上記変形ケ実質的
に伸展除去すると共に、廃フィルム片に対して超音波r
照射してフィルム上の異物ケ分離除去する方法葡提案し
た。Therefore, the present inventor conducted intensive research to solve the problems of the conventional technology, and as a result, focused on the cleaning effect of ultrasonic waves, and by using this and heating at the same time, the cleaning effect is synergistic. It was discovered that the above-mentioned sewage and impurities could be completely removed within an extremely short period of time. The cleaning liquid R is maintained at such a level that the waste film inside becomes flexible and deformations such as wrinkles, folds, etc. formed and fixed on the film are extended and virtually eliminated, and the flow of the cleaning liquid at an appropriate temperature is maintained.・Use the waste film fragments γ
The waste film pieces are softened while being unrolled and migrated in the liquid, and the above deformation is substantially removed by stretching, and the waste film pieces are subjected to ultrasonic waves.
A method of separating and removing foreign substances on the film by irradiation was proposed.
しかしながら、この方法は、従来の方法に比較し確かに
優れた洗浄効果に%つものであったが、洗浄槽内におい
て、一方向に移行する廃フィルム片の移送方向への流出
に伴なう液流状態と、槽内滞溜時間との関係、更には攪
拌の不充分ζもあって塊状ケなしている廃フィルム片の
内奥までの浸透が充分でなく、予期した程の効果ケ挙げ
るに至らなかった。However, although this method certainly had a superior cleaning effect compared to the conventional method, the waste film fragments that migrate in one direction flow out in the cleaning tank, causing liquid to flow out in the direction of transport. Due to the relationship between flow conditions and residence time in the tank, as well as insufficient agitation, the penetration of the waste film fragments that had formed into lumps into the depths was insufficient, and the results were not as effective as expected. It didn't work out.
勿論、洗浄槽内の滞溜時間葡長くするため、槽長を長く
すれば成程度の解決は図られるにしても据付面積が広大
となV実際的であるとは云えない。Of course, it would be possible to solve this problem by increasing the length of the tank in order to increase the residence time in the cleaning tank, but this would require a large installation area and would not be practical.
殊に前記超音波の利用にあってI′f、振動子が槽底の
両側に配置され槽底よV斜上方へ向けlて超音波r興射
するようになっているので波振動は付与されても廃フィ
ルムに充分な解舒効果r与えることはできず、これも予
期する効果の半減ケもたらしていた1つの原因であると
考えられる。In particular, when using the above-mentioned ultrasonic waves, the oscillators are arranged on both sides of the tank bottom, and the ultrasonic waves are emitted diagonally upward from the tank bottom, so wave vibrations are imparted. However, it was not possible to impart a sufficient unraveling effect to the waste film, and this is thought to be one of the reasons why the expected effect was halved.
本発明は叙上の如き諸事情に鑑み、前記方法ケ更に改善
し、より一層の洗浄効果を発揮し、処理能力の大巾な向
上ケ達成する廃フィルムの処理方法r提供することr目
的とするものである。In view of the above-mentioned circumstances, the present invention has been made to provide a method for processing waste film that further improves the method described above, exhibits further cleaning effects, and achieves a significant improvement in processing capacity. It is something to do.
し力)して、かかる目的に適合する本発明方法及び装置
は前述の超音波利用の方法において洗浄液中の廃フィル
ム片に対し、両側面より対向して進゛行方向に直交する
如く超音波を照射すること、そして同時に廃フィルム片
移送に伴なう移送方向の液流に対し、逆方向の水流2強
制的に付与し、移送する廃フィルム片に移送方向前後へ
の循環水流接触の機会r多くすること、更にロータリー
スクリーンの圧力シャワーで清洗し、異物分離rより促
進することの各手段ケ付加することによって特徴づけら
れる。Accordingly, the method and apparatus of the present invention, which are suitable for such purposes, apply ultrasonic waves to the waste film pieces in the cleaning solution from both sides in a direction perpendicular to the traveling direction in the above-mentioned method using ultrasonic waves. At the same time, a water stream 2 in the opposite direction is forcibly applied to the liquid flow in the transfer direction accompanying the transfer of the waste film pieces, giving the waste film pieces being transferred an opportunity to come into contact with the circulating water flow in the forward and backward directions of transfer. It is characterized by adding measures such as increasing the number of particles, washing with a pressure shower on a rotary screen, and promoting the separation of foreign substances.
以下、上記本発明の具体的態様r添付図面に示す装置例
に従って、更に詳述する。Hereinafter, specific aspects of the present invention will be described in further detail according to the apparatus examples shown in the accompanying drawings.
第1図は本発明装置の概要r示す説明図、第2図は本発
明装置の要部rなす洗浄槽の平面概要図、第3図は同洗
浄槽の第2図における長手方向に垂直な面における断面
図、第4図は第3図X−X線矢視断面図である。Fig. 1 is an explanatory diagram showing an outline of the apparatus of the present invention, Fig. 2 is a schematic plan view of a cleaning tank which is the main part of the apparatus of the present invention, and Fig. 3 is a view perpendicular to the longitudinal direction of the washing tank in Fig. 2. 4 is a sectional view taken along the line X--X in FIG. 3.
これら図において、先ず、本発明は目選別された合成樹
脂廃フィルム塊状物r搬送コンベア(1)により粗砕機
(2)へ送り、該粗砕機(2ンで前゛記廃フィルム塊状
物孕粗砕、裁断した後、第2の搬送手段(3)葡利用し
ホッパー(5)より洗浄槽(4)内へ順次、粗砕された
廃フイルム片ケ供給する。この場合、第1の搬送コンベ
ア(1)は特に必要ではなく、手動操作によって粗砕機
(2)へ供給してもよく、又、第2の搬送手段(3)は
図示の如きコンベア利用に限らず、圧送機ならびにダク
トホース盆利用した圧送機構ケもって代えてもよい。In these figures, the present invention first transports the screened synthetic resin waste film lumps r to the coarse crusher (2) by the conveyor (1), After crushing and cutting, the coarsely crushed waste film pieces are sequentially supplied from the second conveying means (3) to the hopper (5) into the cleaning tank (4).In this case, the first conveyor (1) is not particularly necessary and may be supplied to the crusher (2) by manual operation, and the second conveying means (3) is not limited to the use of a conveyor as shown in the figure; The pumping mechanism used may be replaced.
洗浄槽(4)は第1図乃至第3図で図示されているよう
にホッパー(5)下部に案内車(6)が設けられて仏る
と共に、該案内車(6)下部位置より洗浄槽(41排出
部に向かって端部に伸張調節具Qlr4つネットコンベ
ア03)が各ロール(R+)、 (RJ、 (R3)に
わたってモータCMO)で駆動可能に装設されており、
槽内の後尾には誘導板(71p frしてその後方に槽
内の液流r推進するためモータ(9M)により駆動され
る攪拌機(9)が取り付けられている。As shown in FIGS. 1 to 3, the cleaning tank (4) is equipped with a guide wheel (6) at the bottom of the hopper (5), and the cleaning tank (4) is opened from the lower position of the guide wheel (6). (Net conveyor 03 with four extension adjusters Qlr at the end toward the 41 discharge section) is installed so that it can be driven by a motor CMO across each roll (R+), (RJ, and (R3)).
At the rear of the tank, a guide plate (71p fr) is attached, and a stirrer (9) driven by a motor (9M) is attached behind the guide plate (71p fr) to propel the liquid flow in the tank.
そして、この後方には更に洗浄剤タンク側にポンプ(P
I) ’に介して連結された洗浄剤供給管(101’の
先端ならびに槽(4)内に加熱竿体r注入し、又、液温
r調節するためボイラーUυに連結された注液管αυ′
の先端が夫々開口して、洗浄槽(4)内の洗浄液の調製
7図っていると共に、更に後述する洗浄槽の排出側前端
下部に設けられた排水槽吐にポンプ(P4)會介して連
結されている還流管(2Dの端部(8)が開口している
。一方、又、洗浄槽(4)はその両側壁に夫々対向して
互いに内方に向かって超音波が照射されるように超音波
振動子(121が一対以上、図ではゐ対設けられていて
、槽外近傍に設置されている超音波周波発振器(12A
)に夫々連結され、該発振器(12A)k駆動すること
により発振される30キロヘルツ前後の低周波振動によ
って構内の液に振動ケ付与し、槽内における廃フィルム
に固着した汚泥等を脱離する。Behind this, there is a pump (P) on the cleaning agent tank side.
I) The tip of the cleaning agent supply pipe (101') connected through ' and the heating rod r injected into the tank (4), and the liquid injection pipe αυ connected to the boiler Uυ to adjust the liquid temperature r. ′
The tips of each are opened to prepare the cleaning liquid in the cleaning tank (4), and are further connected to a drain tank outlet provided at the lower part of the front end of the cleaning tank on the discharge side, which will be described later, via a pump (P4). The end (8) of the reflux pipe (2D) is open. On the other hand, the cleaning tank (4) has its both side walls facing each other so that ultrasonic waves are irradiated inwardly from each other. At least one pair of ultrasonic transducers (121, in the figure, two pairs are provided), and an ultrasonic frequency oscillator (12A) installed near the outside of the tank.
) and are connected to the oscillators (12A) and oscillated by driving the oscillator (12A) to vibrate the liquid in the premises using low frequency vibrations of around 30 kilohertz, thereby removing sludge, etc. stuck to the waste film in the tank. .
ここで前記振動子(121が両側の側壁に対向して設け
られていることは本発明の1つの特徴であり、下方より
振動音付与するのに対し著しい効果の向上ケ認めること
ができるのである。Here, the fact that the vibrators (121) are provided facing the side walls on both sides is one of the features of the present invention, and it can be seen that the effect is significantly improved when applying vibration noise from below. .
なお、この洗浄槽(4)において上記振動子の配置も重
要な要素であるが更に他の特徴として、槽内の液に対し
循環水流音形成する強制的な手段が設けられている。Although the arrangement of the vibrator is an important element in this cleaning tank (4), another feature is that a means for forcing the liquid in the tank to generate circulating water sound is provided.
即ち、前記洗浄槽後尾の攪拌機(9)はその1つである
が、更にこれに対向して洗浄槽(4)の前方寄りに前記
下部に設けられた排水槽a8にポンプ(PJ) k介し
て連結された配管a9が形成され、その先端が洗浄槽(
4)内で前方より後方へ、即ち槽の後尾方向へ向かって
水を噴射する噴射嘴■となって移送力□向とは逆方向へ
水流?形成している。That is, the agitator (9) at the rear of the cleaning tank is one of them, and a pump (PJ) is also connected to the drain tank a8 provided at the lower part of the cleaning tank (4), facing forward. A pipe a9 is formed which is connected to the cleaning tank (
4) The inside becomes a jet beak ■ that sprays water from the front to the rear, that is, toward the rear of the tank, and the water flows in the opposite direction to the transport force □ direction? is forming.
そのため、洗浄槽(4)内では第3図に示すように攪拌
機(9)及び還流管(211による還流力島ら発生する
水流(籾、案内車(6)によって発生する水流(0)、
前記噴射嘴(2)より噴射され発生する逆水流(D)の
各水流によって(勾で示す如き循環水流が起生され、こ
れが/
超音波振動子α2周辺で存在し廃フィルムに対する超音
波洗浄の効果ケ一層高める役割ケ果すのである。Therefore, in the washing tank (4), as shown in FIG.
Each water flow of the reverse water flow (D) that is ejected and generated from the jet beak (2) generates a circulating water flow as shown by the gradient, which exists around the ultrasonic vibrator α2 and is effective for ultrasonic cleaning of the waste film. It plays a role in further increasing effectiveness.
この洗浄槽(4)は上記の即き各役割ケ有するが、更に
その下部にはネットコンベア03)の耳部7通じて沈下
する各種塵埃、砂1石、鉄片類などの汚泥分子凝集し沈
降する凝集槽Q51が配設されており、これは、その−
側にスクリューコンベア(Iηが横設されていて前記沈
降した汚泥分子コンベアαDの排出端よりその下部の汚
泥タンクQ61へ集積するようになっている。なお、集
積されるこれら汚泥分は適宜ポンプ(P2)により別途
、配置された汚泥槽に他の各部で搬出される汚泥分と共
に一括して集められるように配管が設けられている。This cleaning tank (4) has the above-mentioned roles, but in addition, in the lower part of the cleaning tank (4), sludge molecules such as various dust, sand, iron pieces, etc. that settle through the ears 7 of the net conveyor 03) coagulate and settle. A flocculation tank Q51 is installed, which
A screw conveyor (Iη) is installed horizontally on the side, and the settled sludge molecules are collected from the discharge end of the conveyor αD into the sludge tank Q61 located below.The collected sludge is pumped as appropriate ( According to P2), piping is provided so that the sludge is collected together with the sludge carried out from other parts into a separately arranged sludge tank.
洗浄槽(4J l′i叙上の如くであるが、前記洗浄槽
(4)に続き、その前方にはフィルム−水混合槽(22
1r介して前記洗浄槽(4)内で洗浄されたフィルムw
更によく洗浄すべく清洗装置が配置される。Washing tank (4J l'iAs described above, following the washing tank (4) and in front of it, there is a film-water mixing tank (22).
The film w washed in the washing tank (4) through 1r
A cleaning device is provided for better cleaning.
清洗装置は通常、ロータリースクリーンのによって構成
されてiv、円筒状金網が配設されるが、これと共に筒
内のフィルムに対し洗浄水?噴射する水噴射手段例が併
設される。The cleaning device usually consists of a rotary screen, and a cylindrical wire mesh is installed, and along with this, cleaning water is applied to the film inside the cylinder. An example of water jetting means is also provided.
水噴射手段例は、通常如何なる水源−の利用も可能であ
るが、本発明装置の1連の水系統r充実させるため本発
明では別に配置した貯蔵タンクに連結されている。Although any water source can be used as the water injection means, in the present invention, it is connected to a separately arranged storage tank in order to enrich the continuous water system of the apparatus of the present invention.
図中、の)は同清洗装置における排水槽である。In the figure, ) is the drainage tank in the cleaning equipment.
かくして、清洗された廃フィルムはその後、前記清洗装
置に連設されている一連の取出機構によって再生される
。The cleaned waste film is then recycled by a series of take-out mechanisms connected to the cleaning device.
図示例ではかかる取出機構として、コンベア囚)。In the illustrated example, such a take-out mechanism is a conveyor (conveyor).
案内部材−,排水部材例、圧送ブロワ−の、サイクロン
@)からなる各装置が使用されており最終的に乾燥され
た再生フィルム材としてサイクロン艶より取り出される
。ここで各部材は夫々、公知の、各装置が使用され、当
業者において容易に設計さ′れるであらう。Each device consisting of a guide member, a drainage member, a pressure blower, and a cyclone is used, and is finally removed from the cyclone as a dried recycled film material. Here, each member uses a known device and can be easily designed by a person skilled in the art.
一方、前記本発明の装置は付随して、種々の水処理装置
が併設使用されるが第1図下部に示す部分は力・力・ろ
水処理装置である。On the other hand, the apparatus of the present invention is accompanied by various water treatment apparatuses, and the part shown in the lower part of FIG. 1 is a power/force/filtration treatment apparatus.
ここでは貯蔵タンクGυ、第1沈澱槽C32,第2沈澱
槽(331、汚泥槽(34)が夫々設けられており5各
沈澱槽(321,儲の上澄液ケ貯蔵タンク(3])に還
水してポンプにより前記洗浄、清洗各部分への活用ケ図
っており、同時に沈澱物は夫々前記沈澱槽(321,(
33+より濃縮槽09へ移してポンプr使用し、又は使
用することなしに排出させている。Here, a storage tank Gυ, a first sedimentation tank C32, a second sedimentation tank (331, and a sludge tank (34) are provided, respectively, and five sedimentation tanks (321, a storage tank for supernatant liquid (3)) are provided. The water is returned and pumped for use in the cleaning and cleaning parts, and at the same time, the sediment is removed from the sedimentation tank (321, (
33+ to the concentration tank 09 and discharged using pump r or without using it.
又、汚泥槽(341に集められた汚泥分は夫々適宜必要
に応じ攪拌装置r備えた膠着剤収容タンクC361。In addition, the sludge collected in the sludge tank (341) is stored in a glue storage tank C361 equipped with an agitation device r as needed.
C37)より膠着剤の付与ケ受けて攪拌装置(34a)
で攪拌しつつ漸次膠着させている。After receiving the adhesive from C37), the stirring device (34a)
While stirring, the mixture is gradually brought to a stalemate.
しかしこれら水処理装置は必らずしも上記の如き装置構
成に限るものではなく適宜、設計変更ケ施し得ることは
云うまでもないことである。However, it goes without saying that these water treatment apparatuses are not necessarily limited to the above-mentioned apparatus configurations and may be modified in design as appropriate.
上述の如き一連の装置において、次に合成樹脂廃フィル
ムr洗浄する場合について説明すると、洗浄槽(4)内
に先ずボイラー0υにより加温された温水葡注入し、洗
浄剤タンク00)より適量の洗浄剤ケ滴下し洗浄波音調
製する。Next, in the series of apparatuses described above, to explain the case of cleaning the synthetic resin waste film r, first, hot water heated by the boiler 0υ is poured into the cleaning tank (4), and an appropriate amount is poured from the cleaning agent tank 00). Drop the cleaning agent and adjust the cleaning wave sound.
超このとき水ケ注入するときは適宜、加熱する□音波洗
浄に伴なう洗浄液の温度は化学的洗浄カケ重視する力為
、物理的洗浄力を重視するかによって一概に定められず
、変ってぐるが、通常、水の場合は約50℃位に物理的
洗浄力の最大値が認められる。従って、約50℃のとき
に超音波振動の効果は最大となるが、ここでは本発明装
置の前記振動子の耐熱温度との関係全考慮し、40〜4
5℃位で洗浄2行なうことが良好である。When injecting water at this time, heat it appropriately. □The temperature of the cleaning solution associated with sonic cleaning cannot be determined unconditionally and varies depending on whether the emphasis is on chemical cleaning or physical cleaning power. However, in the case of water, the maximum physical detergency is usually found at about 50°C. Therefore, the effect of ultrasonic vibration is maximum at about 50°C, but here, taking into account the relationship with the heat-resistant temperature of the vibrator of the device of the present invention,
It is best to perform two washings at about 5°C.
即ち、この液温は廃フイルム塊状物する熱可塑性合成樹
・脂の種類1組成、老化度、変形の固定状態Xは廃フイ
ルム塊状物の凝集、膠着、交絡などの程度によって異な
るが廃フイルム上に形成、固定されている皺、折目、襞
などの変形が伸展し、実質的に消滅する程度であること
が要求され、ポリ塩化ビニルの場合には前記40〜45
℃位が、又、高圧法ポリエチレンの場合には30〜35
℃位が適切である。しかし、これは必らずしも固定的な
ものではなく、各条件に即応して決められる。In other words, the temperature of this liquid varies depending on the type of thermoplastic synthetic resin/resin that forms the waste film agglomerates, the degree of aging, the fixed state of deformation X, etc. It is required that deformations such as wrinkles, creases, folds, etc. that are formed and fixed in the polyvinyl chloride are stretched to such an extent that they are virtually eliminated, and in the case of polyvinyl chloride, the
°C, and in the case of high-pressure polyethylene, it is 30 to 35
Approximately ℃ is appropriate. However, this is not necessarily fixed and can be determined in response to each condition.
〃・くして洗浄槽(4)内ケ適温に保持すると、廃フィ
ルム塊状物?粗砕機(2)で粗砕し、順次ホッパー(5
)r通じて案内車(6)によって廃フィルムr順次、洗
浄槽内へ投入供給する。〃・If the inside of the cleaning tank (4) is kept at an appropriate temperature, lumps of waste film will form. It is coarsely crushed by the crusher (2) and sequentially transferred to the hopper (5).
) The waste film r is sequentially fed into the cleaning tank by the guide wheel (6).
このとき槽内は案内車(6)及びオーバーフローによる
排水槽賭より循環されて、くる還水ならびに攪拌機(9
)の作°動により第3図(B)、((りの如き矢示水流
が起り、一方、前方の噴射嘴(20)よりの水の噴射に
より第3図における逆水流(D)が発生する。At this time, the inside of the tank is circulated through the guide wheel (6) and the drainage tank due to overflow, and the returned water and the agitator (9)
), an arrow-shaped water flow similar to that shown in Fig. 3 (B) and (() occurs, while a reverse water flow (D) in Fig. 3 occurs due to the jet of water from the front jet beak (20). do.
このような状態で両側面より超音波周波発振器葡作動さ
せ、超音波振動子(12+ k通じて約30キロヘルツ
程度の超音波ケ廃フイ・ルム片に照射すると、槽(4)
内でネットコンベア(13)に載って移行す□る廃フィ
ルムは超音波による洗浄r受けつつ前記(B) 、 (
0) 。In this state, the ultrasonic frequency oscillator is activated from both sides, and when the ultrasonic wave of about 30 kHz is irradiated through the ultrasonic vibrator (12+K) to the waste film piece, the tank (4)
The waste film transferred on the net conveyor (13) is subjected to ultrasonic cleaning while being transferred to the above (B), (
0).
(D)各水流による強制的な循環水流によって槽内で充
分滞溜させら扛、効果的な洗浄?受ける。(D) Forced circulation of each water flow ensures sufficient retention in the tank, resulting in effective cleaning. receive.
このようにして投入された廃フイルム上(4)内で約3
分間洗浄さ′れると、前記ネットコンベアα3によって
槽外へ搬出され、次のフィルム−水混合槽のへ送られた
後、清洗工程であるロータリースクリーンの)の圧力シ
ャワーで洗浄は完了し一連の取出機構を経てサイクロン
(30)より搬出される。、一方、排水処理につ′いて
は、前記洗浄槽(4)より降下する汚泥などはネットコ
ンベア03)の耳部r通って下方の凝集槽(15)へ集
められ、スクリューコンベア(lηによって随時、汚泥
タンク(161に搬出された後、排水受汚泥槽C341
へ送られ水処理される。Approximately 3
After being washed for 1 minute, it is carried out of the tank by the net conveyor α3 and sent to the next film-water mixing tank, whereupon the washing is completed by the pressure shower (of the rotary screen) in the washing process, and a series of steps are carried out. It is carried out from the cyclone (30) through a take-out mechanism. On the other hand, regarding wastewater treatment, the sludge that descends from the cleaning tank (4) passes through the ears r of the net conveyor 03) and is collected into the flocculation tank (15) below, and is transported as needed by the screw conveyor (lη). , After being carried out to the sludge tank (161), the wastewater receiving sludge tank C341
The water is sent to the water treatment facility.
又、前記フィルム−水混合槽の、ロータリースクリーン
囚)での排水は別途、排水槽(25)に通され、水処理
ケ経て再処理用水として使用される。この場合、各排水
槽の水は第1.第2の沈澱槽(321,(331で凝集
沈澱法によV水処理された後、濾過槽へ通され各機器へ
再処理水として循環される。Further, the waste water from the film-water mixing tank (rotary screen) is separately passed through a drainage tank (25), and is used as water for reprocessing after water treatment. In this case, the water in each drainage tank is the first one. After the water is treated by coagulation and sedimentation in the second sedimentation tanks (321, 331), it is passed through a filtration tank and circulated as reprocessed water to each device.
殊に前記粗砕工程で裁断処理されたフィルム片の塊は約
50ttrm幅のリボン状フィルム片が凝集した不規則
な塊状rなし、静電気r帯びている為容易に解離するこ
となく、固定された複雑な変形と共に各種の夾雑物r包
蔵し不純物や汚水が頑薗に付着しており、従って従来の
方法ではそnらの異物を完全に分離除去することは極め
て困難であった0し力パシ乍ら本発明方法によれば、塊
状の廃フィルム片は洗浄液中に投入された瞬間、液温に
より軟化し、加熱液の前゛記強制循環・水流動によって
急速に解舒され、液中r泳動じつつ更に柔軟化し、前記
変形が伸展し実質的に除去消滅した状態で超音波エネル
ギ〒の照射r受け、し力・も洗浄液の液温により超音波
の洗浄効果は倍加されるから、フィルム面に付着した汚
泥は秒単位の゛時間で急速に分離脱落し槽底に沈澱堆積
される。又油脂分も超音波エネルギーが有する脱脂作用
により除去され、洗剤の併用によって完全に除去するこ
とができる。In particular, the chunks of film pieces cut in the above-mentioned coarse crushing process were irregular lumps of ribbon-like film pieces with a width of about 50 ttrm, and were fixed without being easily separated because they were charged with static electricity. In addition to complex deformation, various impurities and sewage are also stubbornly attached, making it extremely difficult to completely separate and remove these foreign substances using conventional methods. However, according to the method of the present invention, the lumpy waste film pieces are softened by the liquid temperature the moment they are put into the cleaning liquid, and are rapidly unraveled by the aforementioned forced circulation and water flow of the heated liquid. The film becomes more flexible as it migrates, and is irradiated with ultrasonic energy in a state where the deformation is extended and substantially eliminated. The sludge adhering to the surface is rapidly separated and fallen off in seconds, and is deposited on the bottom of the tank. In addition, fats and oils are also removed by the degreasing action of ultrasonic energy, and can be completely removed by using a detergent in combination.
以上、の説明力・ら既に明らかな通り、本発明方法によ
れば、洗浄液の加熱昇温によって、超音波の洗浄効果ケ
著しく向上せしめるのみならず、熱可塑性合成樹脂より
なる廃フィルム片の塊状物の解舒7扶け、フィルム片r
伸展せしめて、より洗浄し易い形態となす相乗的効果ケ
遺憾なく発揮し短時間の内に完全に全ての汚水や夾雑物
ケ除去することができ、更にフィルムに付着した雑菌も
同時に超音波によって殺菌し得るという符帯効果ケ奏す
る。As is clear from the above explanation, according to the method of the present invention, by heating the cleaning liquid to a higher temperature, not only the ultrasonic cleaning effect is significantly improved, but also the waste film fragments made of thermoplastic synthetic resin are reduced to lumps. Unraveling the object 7. Hold the film piece r.
The synergistic effect of stretching the film to make it easier to clean is fully demonstrated, and all sewage and impurities can be completely removed in a short period of time, and bacteria attached to the film can also be removed by ultrasonic waves. It has the added benefit of being able to sterilize.
従って、本発明方法ケ適用した異物分離工程から送り出
されるフィルム片は非常に綺麗な状態に清浄化されてい
るので、更に追加の水洗x9することなく、後続の粉砕
工程や脱水工程に於いても、粉砕機の刃や脱水機のスク
リュー等の機械部品r損傷摩耗することなく処理能力を
同上させると共に、製品であるフラノの品質を高水準に
保つことができる。Therefore, the film pieces sent out from the foreign matter separation process using the method of the present invention are cleaned in a very clean state, so they can be used in the subsequent crushing process and dehydration process without additional washing with water. It is possible to increase processing capacity without damaging or abrading mechanical parts such as crusher blades and dehydrator screws, and to maintain the quality of the flannel product at a high level.
次に本発明の実施例r述べる。Next, an embodiment of the present invention will be described.
実施例
巾りn、長さ4m、深さ1mの洗浄槽r有する第1図乃
至第4図に示す如き装置ケ用いてポリ塩化ビニル廃フィ
ルムの異物分離ケ行なった。洗浄槽に温水r満し、市販
のアルカリ性洗剤1.’ 51 ’77添加した後、攪
拌機r運転しつつ一方、噴射呪よV噴射して洗浄液を循
環させた。液温が45″C−の時点で粗砕された塩ビ廃
フィルム片の塊状物20Kgr投入し、30 KH2の
超音波r照射して3分間洗浄?行なった。洗浄槽に投入
する前の廃フイルム片塊状物はフィルム重量に対して4
7.1%の土砂等の異物ケ含んでいたが、洗浄後の異物
残存量i1: 0.4%に減り異物除去率は99,2%
であった。EXAMPLE Foreign matter separation from a waste polyvinyl chloride film was carried out using an apparatus as shown in FIGS. 1 to 4 having a washing tank r having a width n, a length of 4 m, and a depth of 1 m. Fill the washing tank with warm water and add commercially available alkaline detergent 1. After adding '51'77, while operating the stirrer R, the cleaning liquid was circulated by spraying V jets. When the liquid temperature was 45''C-, 20kg of coarsely crushed PVC waste film pieces were put into the tank, and irradiated with 30KH2 ultrasonic waves for 3 minutes of cleaning.The waste film before being put into the cleaning tank. The amount of lumps is 4 to the weight of the film.
It contained 7.1% of foreign matter such as earth and sand, but the amount of foreign matter remaining after cleaning decreased to 0.4%, and the foreign matter removal rate was 99.2%.
Met.
次に本装置による洗浄効果に数値的に°表示できるもの
として種々検討の結果、フィルムの分光透過率r測定す
ることにした。Next, as a result of various studies, we decided to measure the spectral transmittance r of the film as a means of numerically indicating the cleaning effect of this device.
その結果はフィルムの光線透過率は可視部から0゜5μ
までの赤外部には大差なく安定がみられフィルムの透過
率が安定している波長で測定しなければならないことか
ら分光させる波長ケ550mμに合わせ測定r行なった
。The result was that the light transmittance of the film was 0°5μ from the visible region.
There was no significant difference in the infrared region up to 100 nm, and since it was necessary to measure at a wavelength at which the transmittance of the film was stable, measurements were carried out at a wavelength of 550 mμ.
この透過率はフィルムの状態によって値の差が大きく、
例えばフィルムが湿潤していたり、表面にキズ及び曲折
していたりすると光線透過率の低下の原因となるが、前
記ポリ塩化ビニル廃フィルムについて透過率r測定し洗
浄率換算ケ行なったところ、原料フィルムの透過率が4
0%であり、洗浄率に換算すると約45%であったもの
が本発明による超音波洗浄ケ約60秒行なった後の洗浄
率では95〜96%になっていることが確認された。This transmittance varies greatly depending on the condition of the film.
For example, if the film is wet or has scratches or bends on the surface, it will cause a decrease in light transmittance. However, when we measured the transmittance r of the above-mentioned PVC waste film and converted it to the cleaning rate, we found that the raw material film The transmittance of
It was confirmed that the cleaning rate after approximately 60 seconds of ultrasonic cleaning according to the present invention was 95 to 96%, which was approximately 45% when converted into a cleaning rate.
因に洗浄率は新しいフィルムの透過率’11o。Incidentally, the cleaning rate is the transmittance of the new film '11o.
%として透過率より換算したものである。It is calculated from the transmittance as %.
なお、比較のため、従来公知の曝気流水移動式異物分離
槽音用いて槽底に設けられた3本の空気送入用パイプよ
り曝気して液r攪拌する以外は前記と同様な条件で洗浄
ケ行なったところその異物除去率は96.2%であり、
透過率換算による洗浄率では70〜13%程度であった
。For comparison, cleaning was carried out under the same conditions as above, except that the liquid was agitated and aerated through three air supply pipes installed at the bottom of the tank using a conventional aeration flowing water moving type foreign matter separation tank. The foreign matter removal rate was 96.2%.
The cleaning rate calculated in terms of transmittance was about 70 to 13%.
又、本発明の強制循環水流による滞留時間の増加方式に
%だない超音波洗浄ケ同様にして行なったところ、その
透過率換算の洗浄率は83〜85%程度で顕著な相違〒
有していた。In addition, when the method of increasing residence time using forced circulation water flow of the present invention was carried out in the same way as ultrasonic cleaning, the cleaning efficiency in terms of transmittance was about 83 to 85%, which was a remarkable difference.
had.
以上のように本発明によれば、超音波洗浄により水型の
洗浄槽でありながら従来のプラントに比し約3倍以上の
処理能力が可能であり、洗浄能力の効率7717図9得
ると共に装置面積を略半分程度で足り、しかも超音波エ
ネルギーによる洗浄r主体とするので使用電力も従来に
比し極めて節減され、電力の省エネルギー化?達成する
ことができる。As described above, according to the present invention, although it is a water-type cleaning tank, it is possible to achieve a processing capacity of about 3 times or more compared to a conventional plant by ultrasonic cleaning. It suffices to use approximately half the surface area, and since cleaning is mainly performed using ultrasonic energy, the amount of power used is significantly reduced compared to conventional methods, resulting in energy savings. can be achieved.
殊に洗浄されたフィルムについても洗浄槽内での強制循
環水流と、その後の情況により従来方式より電力)に異
物の少ない高純度のものが得らf、広範囲の再生有効利
用が可能で従来の埋立、焼却によって生ずる公害の未然
防止にも極めて大きな期待がもたれる。In particular, with regard to the washed film, due to the forced circulation of water in the washing tank and the subsequent circumstances, a product of high purity with less foreign substances than the conventional method can be obtained. There are also great expectations for preventing pollution caused by landfilling and incineration.
更に本発明の場合には廃水処理に関しても洗浄排水は凝
集沈澱方式が採用可能ですべて循環再利用によるため公
共用水域への排水量は少量で済み影響を殆ど及ぼすこと
がない。Furthermore, in the case of the present invention, the coagulation and sedimentation method can be used for wastewater treatment, and since all of the wastewater is recycled and recycled, the amount of water discharged into public water bodies is small and has almost no impact.
かぐして合成樹脂廃フ□イルムの品質の向上、維持がで
き水流の循環移動による水槽滞留゛時間の増加更にその
後の情況と相俟つことによって超音波洗浄はより確実に
廃フィルムに作用し、塩化ビ二ル廃フィルムに限らず、
あらゆる熱可塑性合成樹脂廃フィルムの■効利用の技術
改善としてその効−果は極めて大きく、今後における実
用化が大いに期待されるものである。By smelling, the quality of synthetic resin waste film can be improved and maintained.The retention time in the water tank is increased due to the circulation movement of the water flow.In combination with the subsequent situation, ultrasonic cleaning acts more reliably on the waste film. , not limited to PVC waste film,
The effectiveness of this technology as an improvement in the effective utilization of all kinds of thermoplastic synthetic resin waste films is extremely large, and there are great expectations for its practical application in the future.
第1図は本発明方法?実施する装置の概要r示 。
す説明図、第2図は同装置の洗浄槽の平面概要図、第3
図は第2図における洗浄槽の側断面図、第4図は第3図
X−X線矢視断面図である。
(2)・・・粗砕機、(3)・・・搬送手段。
(4)・・・洗浄槽、(6)・・・案内車。
(91・・・攪拌機、 (12+・・・超音波振動子
。
03)・・・ネットコンベア、(19・・・汚泥凝集槽
。
(17)・・・スクリューフンベア、 (20+・・
・逆流lit 射嘴−(231・・・ロータリースクリ
ーン。
例・・・水噴射手段。Is Fig. 1 the method of the present invention? An overview of the equipment used. Figure 2 is a schematic plan view of the cleaning tank of the same equipment, Figure 3 is an explanatory diagram of
The figure is a side sectional view of the cleaning tank in FIG. 2, and FIG. 4 is a sectional view taken along the line X--X in FIG. 3. (2)...Crushing machine, (3)...Transportation means. (4)...Cleaning tank, (6)...Guide car. (91... Stirrer, (12+... Ultrasonic vibrator. 03)... Net conveyor, (19... Sludge coagulation tank. (17)... Screw feeder, (20+...
・Backflow lit injection beak (231...Rotary screen. Example...Water injection means.
Claims (1)
後、洗浄液中に浸漬し、液中で該廃フィルム片に対して
超音波ケ照射し洗浄液の流動r利用して前記粉砕された
廃フィルムの塊状物r液中で解舒泳動せしめつつ柔軟化
し、廃フイルム上に形成固定された皺、襞などの変形會
実質的に伸展除去すると共に該フィルム上の異物ケ分離
除去する方法において、前記超音波ケ廃フィルム片に対
して両側面より互いに対向的に照射すると共に前記洗浄
液に廃フイルム移送方向に対し前後方向の循環水流r強
制的に形成しつつ洗浄r行ない、次いで、更に圧カシャ
′ワーで1精洗すること忙特徴とする再生原料用廃フイ
ルム処理方法。 2、 洗浄液の液温が40〜45℃である特許請求の範
囲第1項記載の再生原料用廃フイルム処理方法。 3 熱可塑性合成樹脂よりなる廃フィルムがポリ、塩化
ビニルフィル′ムである特許請求の範囲第1項又は第2
項記載の再生原料用廃フイルム処理方法。 t 処理すべき合成樹脂廃フィルム塊状物r粗砕する手
段、前記手段によって粗砕された廃フィルムr洗浄槽へ
搬送、供給する手段、前記廃フィルムを液中で洗浄する
洗浄手段、前記手段によって洗浄された廃フィルムを更
に清洗する手段の各手段ケ有して構成され、前記洗浄手
段はその中に洗浄液ケ収容する洗浄槽4含み、該洗浄槽
はその両側壁に互いに対向する超音波振動子4有し、か
つ洗浄槽入口側に液流推進攪拌機?、一方、出口側に廃
フイルム移送方向に逆らって液体r噴射する手段を備え
ていると共に洗浄槽内部には供給手段下部より検出口に
至りネットコンベヤが設けられ、ネットコンベヤ下部に
は分離された汚舛紫排出する搬出手段?有していること
ケ特徴とする再生原料用廃フイルム処理方法。[Scope of Claims] l After crushing waste film chunks made of thermoplastic synthetic resin, immersing them in a cleaning solution, irradiating the waste film pieces with ultrasonic waves in the solution, and utilizing the flow of the cleaning solution. The crushed waste film lumps are unraveled and migrated in the liquid, softened, and deformed wrinkles, folds, etc. formed and fixed on the waste film are substantially removed by stretching, and foreign substances on the film are separated. In the method of removing the waste film, the waste film piece is irradiated with ultrasonic waves from both sides facing each other, and the washing liquid is forcibly formed with a circulating water flow in the front and back direction with respect to the waste film transport direction. The method for treating waste film for recycled raw materials is characterized in that it is then further thoroughly washed with a pressure shower. 2. The method for treating waste film for recycled raw materials according to claim 1, wherein the cleaning liquid has a liquid temperature of 40 to 45°C. 3. Claims 1 or 2 in which the waste film made of thermoplastic synthetic resin is a polyvinyl chloride film.
A method for processing waste film for recycled raw materials as described in . t means for crushing the synthetic resin waste film lumps to be treated; means for conveying and supplying the waste film coarsely crushed by the means to a cleaning tank; a cleaning means for cleaning the waste film in a liquid; The cleaning means further includes means for cleaning the washed waste film, and the cleaning means includes a cleaning tank 4 containing a cleaning liquid therein, and the cleaning tank has ultrasonic vibrations opposite to each other on both side walls thereof. Is there a liquid flow propelling agitator on the cleaning tank inlet side? On the other hand, the outlet side is equipped with means for injecting liquid r against the direction of waste film transport, and inside the cleaning tank there is provided a net conveyor extending from the lower part of the supply means to the detection port, and a separate conveyor is provided at the lower part of the net conveyor. A means of discharging dirty purple? A method for processing waste film for recycled raw materials.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56114683A JPS5814958A (en) | 1981-07-21 | 1981-07-21 | Method and apparatus for treating waste film for regenerated stock material |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56114683A JPS5814958A (en) | 1981-07-21 | 1981-07-21 | Method and apparatus for treating waste film for regenerated stock material |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5814958A true JPS5814958A (en) | 1983-01-28 |
| JPS6123027B2 JPS6123027B2 (en) | 1986-06-04 |
Family
ID=14644024
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP56114683A Granted JPS5814958A (en) | 1981-07-21 | 1981-07-21 | Method and apparatus for treating waste film for regenerated stock material |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5814958A (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS62297112A (en) * | 1986-06-17 | 1987-12-24 | Nippon Flash Kk | Manufacture of woodflour pellet utilizing waste resin film |
| KR100765852B1 (en) | 2007-01-26 | 2007-10-12 | (주)디테코 | Construction Waste Recycling Equipment |
| JP2013173239A (en) * | 2012-02-23 | 2013-09-05 | Wisconsin Film & Bag Inc | Post-use scrap film recycling process |
-
1981
- 1981-07-21 JP JP56114683A patent/JPS5814958A/en active Granted
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS62297112A (en) * | 1986-06-17 | 1987-12-24 | Nippon Flash Kk | Manufacture of woodflour pellet utilizing waste resin film |
| KR100765852B1 (en) | 2007-01-26 | 2007-10-12 | (주)디테코 | Construction Waste Recycling Equipment |
| JP2013173239A (en) * | 2012-02-23 | 2013-09-05 | Wisconsin Film & Bag Inc | Post-use scrap film recycling process |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6123027B2 (en) | 1986-06-04 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US4379724A (en) | Method for reclaiming waste thermoplastic resin film | |
| JP4750997B2 (en) | Method for recycling PET composition and apparatus for carrying out the method | |
| US5292075A (en) | Disposable diaper recycling process | |
| EP2969443B1 (en) | Post-consumer scrap film recycling process and system | |
| US4436104A (en) | Method of treatment for recycling a waste film as a raw material and apparatus therefor | |
| CS199626B2 (en) | Continuous method of washing and treatment of very contaminated plastics products and equipment for execution of this method | |
| CN106351049A (en) | An easy-to-clean graded pulping equipment for papermaking | |
| CN203346480U (en) | Drum-type cleaning machine | |
| US5203359A (en) | Unitary system for recycling used contaminated material for re-use | |
| JPH066292B2 (en) | Waste plastic film recycling apparatus and method | |
| JP2002096329A (en) | Grinding/cleaning device for waste plastics and grinding/ cleaning method | |
| CN119704445A (en) | A recycling process for waste plastics and mineral bottles | |
| JP2004202758A (en) | Method and apparatus for regenerating waste plastic film and pre-sorting machine, rough cutter, ultrasonic washing device and rotary type dryer used in them | |
| CN204874220U (en) | Fatlute separation processing equipment | |
| JP2002320932A (en) | Method for cleaning recycled PET flakes and apparatus for cleaning recycled PET flakes | |
| JPS6316977B2 (en) | ||
| JPS6123027B2 (en) | ||
| KR880000020B1 (en) | Method and apparatus for treating exhausted film for using as reclaimed raw material | |
| CN113334633A (en) | Cleaning and flotation separation process and equipment for mixed materials | |
| CN213194840U (en) | A concrete waste recycling device | |
| JPH0631733A (en) | Treating method for making plastic waste materials resources again and its apparatus | |
| JP2001170937A (en) | Regeneration-processing installation for film waste and method for regeneration-processing film waste | |
| CN114434686B (en) | Plastic crushing, cleaning and sorting equipment and application method | |
| US3387793A (en) | Process and system for treating rubber | |
| KR910011414A (en) | Waste plastic film recycling processing method and apparatus therefor |