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KR100666093B1 - Method for Retrieving PET and EVA from Laminating Film - Google Patents

Method for Retrieving PET and EVA from Laminating Film Download PDF

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KR100666093B1
KR100666093B1 KR20040048874A KR20040048874A KR100666093B1 KR 100666093 B1 KR100666093 B1 KR 100666093B1 KR 20040048874 A KR20040048874 A KR 20040048874A KR 20040048874 A KR20040048874 A KR 20040048874A KR 100666093 B1 KR100666093 B1 KR 100666093B1
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pet
eva
layer
punching
pulverized product
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KR20060000247A (en
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고병철
고승춘
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고병철
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    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J11/00Recovery or working-up of waste materials
    • C08J11/04Recovery or working-up of waste materials of polymers
    • C08J11/06Recovery or working-up of waste materials of polymers without chemical reactions
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29BPREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
    • B29B17/00Recovery of plastics or other constituents of waste material containing plastics
    • B29B17/04Disintegrating plastics, e.g. by milling
    • B29B17/0404Disintegrating plastics, e.g. by milling to powder
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J5/00Manufacture of articles or shaped materials containing macromolecular substances
    • C08J5/18Manufacture of films or sheets
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29BPREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
    • B29B17/00Recovery of plastics or other constituents of waste material containing plastics
    • B29B17/02Separating plastics from other materials
    • B29B2017/0213Specific separating techniques
    • B29B2017/0217Mechanical separating techniques; devices therefor
    • B29B2017/0237Mechanical separating techniques; devices therefor using density difference
    • B29B2017/0244Mechanical separating techniques; devices therefor using density difference in liquids
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29BPREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
    • B29B17/00Recovery of plastics or other constituents of waste material containing plastics
    • B29B17/02Separating plastics from other materials
    • B29B2017/0213Specific separating techniques
    • B29B2017/0286Cleaning means used for separation
    • B29B2017/0289Washing the materials in liquids
    • 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

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  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Manufacturing & Machinery (AREA)
  • Health & Medical Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Medicinal Chemistry (AREA)
  • Polymers & Plastics (AREA)
  • Materials Engineering (AREA)
  • Environmental & Geological Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Sustainable Development (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)

Abstract

본 발명은 PET층 위에 EVA층이 라미네이팅된 라이네이팅필름으로부터 PET와 EVA를 회수하는 방법에 관한 것으로, 특히 산화제로서 애용되며 무공해특성을 가지는 과산화수소용액을 이용해 짧은 시간내에 PET층과 EVA층을 분리시켜 PET와 EVA를 회수하는 방법에 관한 것이다. The present invention relates to a method for recovering PET and EVA from a laminating film in which an EVA layer is laminated on a PET layer. In particular, the PET layer and the EVA layer are separated from the PET layer and the EVA layer in a short time using a hydrogen peroxide solution that is used as an oxidizing agent and has a pollution-free property. And a method for recovering the EVA.

본 발명의 회수방법은, 분쇄기를 이용해 라미네이트필름을 분쇄하여 분쇄물을 형성하는 분쇄단계와,상기 분쇄물을 과산화수소가 저장된 침전조에 소정 시간동안 침전시키는 침전단계와, 상기 분쇄물을 상기 침전조로부터 타발기로 유입시켜 타격하는 타발단계와, 상기 타발기로부터 유출된 분쇄물을 침전분리조에 투입하고 비중차이로 인해 상층으로 부유한 EVA와 하층으로 침전된 PET를 분리하여 유출시키는 분리단계와, 분리된 EVA와 PET를 탈수하는 탈수단계를 포함하는 것을 특징으로 한다.The recovery method of the present invention includes a pulverizing step of pulverizing a laminate film using a pulverizer to form a pulverized product, a precipitation step of precipitating the pulverized product in a sedimentation tank containing hydrogen peroxide for a predetermined time, and obtaining the pulverized product from the sedimentation tank. The punching step of injecting and hitting with an erection, and a separating step of putting the pulverized product discharged from the punching machine into a sedimentation tank and separating and letting out the EVA suspended in the upper layer and the PET precipitated in the lower layer due to the specific gravity difference. It characterized in that it comprises a dehydration step of dehydrating EVA and PET.

과산화수소, PET, EVA, 회수방법Hydrogen peroxide, PET, EVA, Recovery method

Description

에틸렌 비닐 아세테이트 코폴리머와 폴리에틸렌테레프탈레이트로 이루어진 폐라미네이팅필름으로부터 에틸렌 비닐 아세테이트 코폴리머와 폴리에틸렌테레프탈레이트의 회수방법{Method for Retrieving PET and EVA from Laminating Film}Method for recovering ethylene vinyl acetate copolymer and polyethylene terephthalate from waste laminating film composed of ethylene vinyl acetate copolymer and polyethylene terephthalate

도 1은 본 발명의 회수방법을 구현하는 장치의 개략적인 블럭도.1 is a schematic block diagram of an apparatus implementing the recovery method of the present invention.

도 2는 도 1에 도시된 타발기의 개략 단면도.2 is a schematic cross-sectional view of the punching machine shown in FIG. 1.

도 3은 도 1에 도시된 침전분리조의 개략 단면도.3 is a schematic cross-sectional view of the sedimentation tank shown in FIG.

도 4는 본 발명의 일실시예에 따른 회수방법의 흐름도.4 is a flow chart of a recovery method according to an embodiment of the present invention.

도 5는 본 발명의 다른 실시예에 따른 회수방법의 흐름도.5 is a flow chart of a recovery method according to another embodiment of the present invention.

본 발명은 PET층 위에 EVA층이 라미네이팅된 라이네이팅필름으로부터 PET와 EVA를 회수하는 방법에 관한 것으로, 특히 산화제로서 애용되며 무공해특성을 가지는 과산화수소용액을 이용해 짧은 시간내에 PET층과 EVA층을 분리시켜 PET와 EVA를 회수하는 방법에 관한 것이다. The present invention relates to a method for recovering PET and EVA from a laminating film in which an EVA layer is laminated on a PET layer. In particular, the PET layer and the EVA layer are separated from the PET layer and the EVA layer in a short time using a hydrogen peroxide solution that is used as an oxidizing agent and has a pollution-free property. And a method for recovering the EVA.

PET층위에 EVA층을 적층한 라미네이트필름은 PET필름위에 EVA필름을 열압착시키거나 EVA수지를 용융도포하여 형성되는데 그 우수한 특성으로 인해 코팅필름, 인쇄소재 또는 라벨 등에 널리 사용되고 있지만, 사용후에는 재활용되지 못하고 버려지고 있어 자원의 재활용측면에서도 경제적이지 못하다는 지적이 있어왔고 무엇보다도 폐 필름으로 인한 환경오염의 문제와 이로 인한 사회적 비용의 손실이 크다는 지적을 받아왔다. Laminated film with EVA layer laminated on PET layer is formed by thermally compressing EVA film on PET film or by melt-coating EVA resin.It is widely used for coating film, printing material or label because of its excellent properties. It has been pointed out that it is not economical in terms of recycling of resources because it is not being discarded, and above all, it has been pointed out that the problem of environmental pollution caused by waste film and the loss of social cost due to it are large.

본 발명의 목적은 라미네이트필름을 분쇄한 후 분쇄물을 과산화수소용액에 담긴 침전조에 침전시키는 침전단계와 타발기를 이용해 상기 분쇄물을 타격해 박리를 촉진시키는 타발단계를 거쳐 단시간에 PET층과 EVA층을 박리시켜 회수하는 방법을 제공하는 것이다. The object of the present invention is the PET layer and EVA layer in a short time through the precipitating step of pulverizing the laminate film and then pulverizing the pulverized product in the sedimentation tank containing hydrogen peroxide solution and the punching step to strike the pulverized product by using a punching machine to promote peeling. It is to provide a method for peeling off and recovering.

본 발명은 앞서 본 목적을 달성하기 위하여 다음과 같은 구성을 가진 실시예에 의하여 구현된다. The present invention is implemented by the embodiment having the following configuration in order to achieve the above object.

본 발명의 제 1 실시예에 따르면, 본 발명의 회수방법은, 분쇄기를 이용해 라미네이트필름을 분쇄하여 분쇄물을 형성하는 분쇄단계와,상기 분쇄물을 과산화수소가 저장된 침전조에 소정 시간동안 침전시키는 침전단계와, 상기 분쇄물을 상기 침전조로부터 타발기로 유입시켜 타격하는 타발단계와, 상기 타발기로부터 유출된 분쇄물을 침전분리조에 투입하고 비중차이로 인해 상층으로 부유한 EVA와 하층으로 침전된 PET를 분리하여 유출시키는 분리단계와, 분리된 EVA와 PET를 탈수하는 탈수단계를 포함하는 것을 특징으로 한다.According to a first embodiment of the present invention, the recovery method of the present invention, a pulverization step of forming a pulverized product by pulverizing the laminate film using a pulverizer, and a precipitation step of precipitating the pulverized product in a precipitation tank in which hydrogen peroxide is stored for a predetermined time And, the punching step of injecting the crushed product from the sedimentation tank into the crusher, and the crushed product discharged from the crusher into the sedimentation separation tank and the PET precipitated in the upper layer and the EVA suspended in the lower layer due to the specific gravity difference Separation step to separate and discharge, characterized in that it comprises a dehydration step of dewatering the separated EVA and PET.

본 발명의 제 2 실시예에 따르면, 본 발명의 회수방법은, 제 1 실시예에 있 어서, 상기 분리단계는 세척단계를 추가로 포함하며, 상기 세척단계는 타발기로부터 유출된 분쇄물이 물을 함유하는 침전분리조에 침전됨으로서 이루어지는 것을 특징으로 한다.According to a second embodiment of the present invention, in the recovery method of the present invention, in the first embodiment, the separating step further includes a washing step, wherein the washing step is a crushed water discharged from the punching machine It is characterized by consisting of being precipitated in the precipitation separation tank containing.

본 발명의 제 3 실시예에 따르면, 본 발명의 회수방법은, 제 2 실시예에 있어서, 상기 타발단계는 1차타발기에 의한 1차타발단계와, 2차타발기에 의한 2차타발단계로 이루어지는 것을 특징으로 한다. According to a third embodiment of the present invention, in the recovery method of the present invention, in the second embodiment, the punching step includes a first punching step by a primary punching machine and a second punching step by a secondary punching machine. It is characterized by.

본 발명의 제 4 실시예에 따르면, 본 발명의 회수방법은, 제 3 실시예에 있어서, 상기 탈수단계는 PET를 탈수하는 PET탈수단계와, EVA를 세척하는 EVA탈수단계로 이루어진 것을 특징으로 한다.According to a fourth embodiment of the present invention, the recovery method of the present invention, in the third embodiment, characterized in that the dehydration step consists of a PET dehydration step to dehydrate the PET, and EVA dehydration step to wash the EVA. .

본 발명의 제 5 실시예에 따르면, 본 발명의 회수방법은, 제 4 실시예에 있어서, 상기 분리단계와 PET탈수단계 사이에 PET를 PET타발기에 유입시켜 타격하는 PET타발단계와 상기 PET타발기로부터 유출된 PET를 PET침전조에 침전시켜 잔유 EVA를 박리시키는 PET침전단계를 추가로 포함하는 것을 특징으로 한다.According to a fifth embodiment of the present invention, the recovery method of the present invention, in the fourth embodiment, the PET punching step and the PET hitting the PET is introduced into the PET punching machine between the separating step and the PET dehydration step It is characterized in that it further comprises a PET precipitation step of precipitating the PET outflow from the erection in the PET precipitation tank to peel off the residual EVA.

출원인은 첨부도면을 참조하여 앞서 본 실시예들을 상세하게 설명한다.Applicants will now describe the above embodiments in detail with reference to the accompanying drawings.

본 발명의 회수방법은, 도 4 내지 도 5에 도시된 바와 같이, 크게는 분쇄단계(S1), 침전단계(S2), 타발단계(S3), 분리단계(S4), PET탈수단계(S6), EVA탈수단계(S8), PET저장단계(S7)와 EVA저장단계(S9)로 이루어진다. 4 to 5, the recovery method of the present invention, the grinding step (S1), the precipitation step (S2), punching step (S3), separation step (S4), PET dehydration step (S6) largely , EVA dehydration step (S8), PET storage step (S7) and consists of EVA storage step (S9).

상기 분쇄단계(S3)는 PET층에 EVA층이 라미네이팅된 폐 라미네이트필름을 공지된 분쇄기(100)에 넣고 잘게 분쇄하여 소정 크기의 분쇄물을 형성하는 단계이다. 위 분쇄단계는, 분쇄물을 형성함과 동시에 분쇄물은 분쇄과정동안 타격을 받아 크 랙이 발생하고 크랙 사이로 아래에서 설명하는 과산화수소액이 침투할 수 있게 되어 PET층과 EVA층의 박리를 가능하게 한다. The crushing step (S3) is a step of forming a pulverized product of a predetermined size by putting the waste laminate film laminated EVA layer on the PET layer in a known crusher 100 and finely pulverized. In the above crushing step, the pulverized product is formed at the same time as the crushed product is hit during the crushing process, cracks are generated, and the hydrogen peroxide solution described below can penetrate between the cracks, thereby enabling the peeling of the PET layer and the EVA layer. do.

상기 침전단계(S2)는 과산화수소액이 저장된 분쇄물침전조(102)에 분쇄물을 투입하여 소정 시간 방치함으로서 PET층과 EVA층을 1차적으로 박리시키는 단계이다. 분쇄물침전조(102)에는 과산화수소액이 저장되어 있고, 분쇄물을 분쇄물침전조에 넣게 되면 분쇄물에 형성된 크랙사이로 과산화수소액이 침투하게 된다. 그리고 과산화수소는 유기물과 접촉하면 분해가 촉진되어 다음 반응식과 같이 산소와 함께 분해열을 발생시킨다. The precipitation step (S2) is a step of first peeling the PET layer and the EVA layer by leaving the pulverized product in the pulverized product precipitate tank 102 in which the hydrogen peroxide solution is stored for a predetermined time. Hydrogen peroxide solution is stored in the pulverized precipitate settlement tank 102, and when the pulverized substance is put into the pulverized precipitate settlement tank, the hydrogen peroxide solution penetrates between cracks formed in the pulverized substance. Hydrogen peroxide promotes decomposition when it comes into contact with organics, and generates heat of decomposition with oxygen as shown in the following reaction formula.

H2O2 -> H20+1/2O2+23.45KcalH 2 O 2- > H 2 0 + 1 / 2O 2 + 23.45Kcal

여기서 발생된 산소가스는 PET층과 EVA층을 산화시키고 분해열은 PET층와 EVA층의 접착력을 약화시킴으로써, PET와 EVA를 박리시키게 된다. 일반적으로, 35%과산화수소액이 적합하지만, 필요에 따라서는 50%과산화수소액이 사용될 수도 있다.Oxygen gas generated here oxidizes the PET layer and the EVA layer, and decomposition heat weakens the adhesion between the PET layer and the EVA layer, thereby peeling off the PET and EVA. Generally, 35% hydrogen peroxide solution is suitable, but 50% hydrogen peroxide solution may be used if necessary.

상기 타발단계(S3)는 분쇄물을 도 2에 도시된 타발기(104)에 넣어서 타격함으로서 박리 효율을 높이고자 하는 단계이다. 상기 타발기(104)는 하우징(5)과, 모터(M)에 직결된 축(3)에 원주방향으로 취부된 타결날개(4)를 가진 타격부로 이루어져 있으며, 하우징(5)에는 분쇄물이 유입되는 입구(2)와 분쇄물이 유출되는 출구(6)가 존재하고 물이 유입되는 입구(1)가 부설되어 있다. 분쇄물이 입구로 유입되면, 분쇄물은 모터(M)에 직결되어 회동하는 축(3)에 부설된 타격날개(4)에 의 해 타격되면서 출구(6)로 이동하여 배출된다. 이러한 일련의 과정을 통해 PET층과 EVA층의 박리가 촉진된다. 도 1 및 도 5에 도시된 바와 같이, 필요에 따라서는 복수의 타발기(104,106)를 직렬적으로 구성하여, 박리의 효율을 높일 수도 있다. The punching step (S3) is a step to increase the peeling efficiency by putting the crushed product into the punching machine 104 shown in FIG. The punching machine 104 is composed of a hitting portion having a housing 5 and a screwing wing 4 circumferentially mounted on a shaft 3 directly connected to the motor M. There is an inlet 2 for inflow and an outlet 6 for outflow of crushed products, and an inlet 1 for inflow of water is provided. When the pulverized material flows into the inlet, the pulverized material is discharged by moving to the outlet 6 while being hit by the strike blades 4 attached to the rotating shaft 3 directly connected to the motor M. This series of processes promotes the separation of the PET layer and the EVA layer. As shown in FIG. 1 and FIG. 5, if necessary, a plurality of punching machines 104 and 106 may be configured in series to increase the efficiency of peeling.

상기 분리단계(S4)는, 타발기(104,106)로부터 배출된 분쇄물을 물이 저장된 침전분리조(108)에 담구어 비중차를 이용해 PET를 바닥으로 침전시키고 그리고 EVA를 상층으로 부유시켜 상호 분리하는 단계이다. 상기 침전분리조(108)은 침전조(30), EVA회수부(10), PET회수부(20)와 격판(40)으로 구성되는데, 상기 침전조(30)는 물(32)을 함유한다. 상기 EVA회수부(10)는 관(13)과 관(13)내에 설치되며 모터(M)에 직결된 스크류(12)로 이루어지며, 스크류의 회전을 이용해 상층으로 부유된 EVA(51)를 회수하여 침전분리조 외부로 배출한다. 그리고, 상기 PET회수부(20)도 마찬가지로 관(23)과, 관(23)내에 설치되며 모터(M)에 직결된 스크류(12)로 이루어지며, 스크류의 회전을 이용해 바닥에 침전된 PET(52)를 수거하여 외부로 배출한다. 상기 격판(40)은 도 3에 도시된 바와 같이 침전분리조(30)의 상층의 소정 위치에 설치되는데, 상층으로 부유한 EVA가 EVA회수부(10)의 단부를 지나 침전분리조의 엣지로 흘러가는 것을 차단함으로서 EVA의 회수율을 높이는 역할을 한다. 또한, 도시되지는 않지만, 침전분리조의 상층 일단에 설치된 블로우로 상층으로 부유한 EVA를 EVA회수부(10)의 단부로 블로윙할 수도 있다. 위 침전분리조를 이용하게 되면, EVA와 PET는 분리되어 배출될 수 있다. 또한, 위 침전분리조에는 물이 저장되어 있기 때문에, 분쇄물이 침전분리조에 담구어지면 분쇄물상의 과산화수소가 자동으로 세척되므로, 별도의 세척장치를 이용할 필요가 없다는 장점 을 가진다. In the separation step (S4), the pulverized product discharged from the punching machine (104, 106) is immersed in the sedimentation separation tank (108) in which water is stored, and the PET is precipitated to the bottom by using a specific gravity difference and the EVA is floated to the upper layer to separate each other. It's a step. The sedimentation separation tank 108 is composed of a sedimentation tank 30, EVA recovery portion 10, PET recovery portion 20 and the diaphragm 40, the sedimentation tank 30 contains water (32). The EVA recovery part 10 is installed in the tube 13 and the tube 13 and consists of a screw 12 directly connected to the motor M, and recovers the EVA 51 suspended in the upper layer by rotating the screw. To the outside of the sedimentation tank. In addition, the PET recovery unit 20 is also made of a pipe 23 and a screw 12 installed in the pipe 23 and directly connected to the motor M, and the PET deposited on the floor by rotating the screw ( 52) Collect and discharge to the outside. The diaphragm 40 is installed in a predetermined position of the upper layer of the sedimentation separation tank 30, as shown in Figure 3, the EVA floating in the upper layer flows to the edge of the sedimentation separation tank past the end of the EVA recovery portion (10) Blocks the increase of the recovery rate of EVA. In addition, although not shown, it is also possible to blow the EVA floating in the upper layer to the end of the EVA recovery portion 10 by a blow provided at one end of the upper layer of the sedimentation separation tank. Using the above sedimentation tank, EVA and PET can be separated and discharged. In addition, since the water is stored in the sedimentation tank, when the pulverized product is immersed in the sedimentation tank, the hydrogen peroxide on the pulverized product is automatically washed, so there is no need to use a separate washing device.

상기 PET탈수단계(S6)는 공지의 PET탈수기(114)를 이용해 회수된 PET표면의 물을 탈수하는 단계이며, 상기 EVA탈수단계(S8)는 EVA탈수기(118)를 이용해 회수된 EVA표면의 물을 탈수하는 단계이다. The PET dehydration step (S6) is a step of dehydrating the water of the PET surface recovered using the known PET dehydrator 114, the EVA dehydration step (S8) is the water of the EVA surface recovered using the EVA dehydrator 118 Dehydration step.

상기 PET저장단계(S7)는 탈수된 PET를 PET저장조(116)에 저장하는 단계이며, EVA저장단계(S9)는 탈수된 EVA를 EVA저장조(120)에 저장하는 단계이다. The PET storage step (S7) is a step of storing the dehydrated PET in the PET storage tank 116, the EVA storage step (S9) is a step of storing the dehydrated EVA in the EVA storage tank (120).

본 발명의 다른 실시예에 따르면, 상기 분리단계(S4)와 PET탈수단계(S6)사이에, PET타발단계(S51)와 PET침전단계(S52)가 추가될 수도 있다. 이는 분리단계(S4)에서 분리된 PET에 남아 있을 지 모를 EVA를 추가적으로 박리하기 위함이다. 상기 PET타발단계(S51)는 침전분리조(108)로부터 배출된 PET를 PET타발기(110, 도2 참조)에 넣어 추가로 타격하여 EVA를 박리하는 단계이며 PET침전단계(S52)는 PET타발기(110)으로부터 배출된 PET를 물이 저장된 PET침전조(112)에 담구어 EVA를 상층으로 부유시키고 PET를 바닥으로 침전시켜 PET를 PET탈수기(114)로 배출하는 단계이다. PET침전조(112)는 도시되지는 않지만 도 3에 도시된 침전분리조의 구조를 가질 수도 있고, 아니면 침전분리조에서 EVA회수부를 가지지 않고 PET회수부만을 가진 구성일 수도 있다. According to another embodiment of the present invention, a PET punching step (S51) and a PET precipitation step (S52) may be added between the separating step (S4) and the PET dehydration step (S6). This is to additionally peel off the EVA may remain in the PET separated in the separation step (S4). The PET punching step (S51) is a step of peeling the EVA by additionally putting the PET discharged from the sedimentation separator 108 into the PET punching machine (110, see Fig. 2) and PET precipitation step (S52) The PET discharged from the erection 110 is immersed in the PET settling tank 112 in which water is stored, and the EVA is suspended in the upper layer and the PET is precipitated to the bottom to discharge the PET to the PET dehydrator 114. Although not shown, PET sedimentation tank 112 may have a structure of a sedimentation separation tank shown in FIG. 3, or may have a configuration of only PET recovery portion without EVA recovery portion in the sedimentation separation tank.

출원인은 이하에서 과산화수소액을 사용하는 경우와, 물을 사용하는 경우에 박리에 소요되는 시간을 측정하여 본 발명의 효과를 보이도록 한다.Applicants to demonstrate the effects of the present invention by measuring the time required for peeling when using a hydrogen peroxide solution and when using water.

실험조건 Experimental condition

30HP 분쇄기, 길이가 1M이고 직경이 0.45M인 원통형 타발기, 길이가 6M이고 높이가 1M이며 폭이 1.2M인 사각 분쇄물침전조, 길이가 6M이고 높이가 2.2M이며 폭이 1.2M인 침전분리조를 이용해 도 4에 도시된 공정에 따라 실험한다. 그리고, 투입한 폐 라미네이팅필름의 총량에서 분리되지 않고 배출되는 폐라미네이팅필름의 량을 감한 것을 백분율로 나타내어 이를 회수율이라 칭하며, 회수율이 90%, 70%, 50%가 되는데 까지 소요되는 시간을 물인 경우와, 35%과산화수소액인 경우를 나누어서 측정한다. 그리고, 35%과산화수소액을 사용하는 경우라도 과산화수소액을 침전조에 풀고 곧바로 분쇄물을 침전시킨 경우와(시험예 1 내지 3), 소정의 시간이 흐른 뒤에 침전시킨 경우(비교예4)에 회수율이 70%에 이르기까지 소요된 시간을 각각 측정한다. 30HP grinder, cylindrical punching machine 1M in length and 0.45M in diameter, square mill settling tank 6M in length, 1M in height and 1.2M in width, sedimentation separation 6M in length, 2.2M in height and 1.2M in width Experiment using the bath according to the process shown in FIG. 4. In addition, when the amount of waste laminating film discharged without being separated from the total amount of waste laminating film added is expressed as a percentage, this is called a recovery rate, and the time required for recovery to be 90%, 70%, and 50% is water. And measure by dividing the case of 35% hydrogen peroxide solution. And even in the case of using 35% hydrogen peroxide solution, the recovery rate is reduced when the hydrogen peroxide solution is dissolved in the settling tank and the pulverized product is immediately precipitated (Test Examples 1 to 3), and when precipitated after a predetermined time has passed (Comparative Example 4). Each time is measured up to 70%.

시험예1Test Example 1

폐 라미네티이팅필름 6톤을 10톤의 35%과산화수소액이 저장된 침전조에 넣고 회수율이 90%에 도달하는 시간을 측정하면, 대략 8시간 정도가 소요된다. 6 tons of waste laminating film is placed in a sedimentation tank containing 10 tons of 35% hydrogen peroxide solution and the recovery time reaches 90%. It takes about 8 hours.

시험예2Test Example 2

폐 라미네티이팅필름 6톤을 10톤의 35%과산화수소액이 저장된 침전조에 넣고 회수율이 70%에 도달하는 시간을 측정하면, 대략 시간에서 6시간 정도가 소요되었다. 6 tons of the waste laminating film was placed in a sedimentation tank containing 10 tons of 35% hydrogen peroxide solution and the recovery time reached 70%.

시험예3Test Example 3

폐 라미네티이팅필름 6톤을 10톤의 35%과산화수소액이 저장된 침전조에 넣고 회수율이 50%에 도달하는 시간을 측정하면, 대략 5시간 정도가 소요되었다. 6 tons of the waste laminating film was placed in a sedimentation tank containing 10 tons of 35% hydrogen peroxide solution, and the recovery time reached 50%. It took about 5 hours.

비교예1Comparative Example 1

폐 라미네티이팅필름 6톤을 10톤의 물이 저장된 침전조에 넣고 회수율이 90%에 도달하는 시간을 측정하고자 하였으나 72시간이 지나도 90%에는 도달하지 아니하였다.6 tons of waste laminating film was placed in a sedimentation tank containing 10 tons of water, and the recovery time reached 90%, but after 72 hours, it did not reach 90%.

비교예2Comparative Example 2

폐 라미네티이팅필름 6톤을 10톤의 물이 저장된 침전조에 넣고 회수율이 70%에 도달하는 시간을 측정하고자 하였으나 72시간이 지나도 70%에는 도달하지 아니하였다.6 tons of waste laminating film was placed in a sedimentation tank containing 10 tons of water, and the recovery time reached 70%. However, it did not reach 70% even after 72 hours.

비교예3Comparative Example 3

폐 라미네티이팅필름 6톤을 10톤의 물이 저장된 침전조에 넣고 회수율이 50%에 도달하는 시간을 측정하면, 대략 24시간 정도가 소요되었다.6 tons of the waste laminating film was placed in a sedimentation tank containing 10 tons of water, and the time required for the recovery to reach 50% was approximately 24 hours.

비교예4Comparative Example 4

10톤의 35%과산화수소액을 침전조에 풀고 7시간 흐른 뒤 6톤의 폐 라미네이팅필름을 투입하여 회수율이 70%에 이르는데 소요되는 시간을 측정하면, 대략 9시간 정도가 소요되었다. After 10 tons of 35% hydrogen peroxide solution was dissolved in the settling tank and flowed for 7 hours, 6 tons of waste laminating film was added to measure the time taken for the recovery to reach 70%, which took approximately 9 hours.

앞서 본 시험예1 내지 3과 비교예1 내지 3을 비교검토해보면, 물을 사용하는 비교예 1 내지 2에서는 회수율이 90%,70%에 도달하지 아니하였고, 회수율이 50%인 비교예3에 비해 과산화수소액을 사용하는 시험예 1 내지 3의 경우가, 박리시간을 현저하게 줄일 수 있음을 확인할 수 있었다. In the comparative examples 1 to 3 and Comparative Examples 1 to 3, the recovery rate in Comparative Examples 1 to 2 using water did not reach 90%, 70%, and compared to Comparative Example 3 having a recovery rate of 50%. In the case of Test Examples 1 to 3 using a hydrogen peroxide solution, it was confirmed that the peeling time can be significantly reduced.

또한, 시험예2와 비교예4를 비교해보면, 과산화수소액을 침전조에 풀고 소정시간 지나서 폐 라미네이팅필름을 투입하게 되면, 시험예2에 비해 박리시간이 현저히 늘어남을 확인할 수 있었는데, 이는 과산화수소가 대기중에 노출되는 순간 발생기 산소와 분해열을 발생시키기 때문에, 노출된 이후로 일정 시간이 지나면 과산화수소의 산화력이 떨어지고 분해열의 발생량이 줄어들기 때문인 것으로 보인다. In addition, comparing Test Example 2 with Comparative Example 4, when the hydrogen peroxide solution in the settling tank and put the waste laminating film after a predetermined time, it was confirmed that the peeling time is significantly increased compared to Test Example 2, which is hydrogen peroxide in the atmosphere Since the generator generates oxygen and heat of decomposition at the time of exposure, it seems that the hydrogen peroxide oxidizes and the amount of heat of decomposition decreases after a certain time since exposure.

출원인은 이상에서 본 발명의 실시예를 설명하였지만, 본 발명의 다양한 변경예와 수정예도 본 발명의 기술적 사상을 구현하는 한 본 발명의 범위에 속하는 것으로 해석되어야 한다. Applicants have described the embodiments of the present invention, but various modifications and variations of the present invention should also be construed as falling within the scope of the present invention as long as the technical spirit of the present invention is embodied.

본 발명은 앞서 본 구성에 의하여 다음과 같은 효과를 가진다. The present invention has the following effects by the above configuration.

본 발명의 회수방법은 과산화수소액과 타발단계를 이용해 PET층과 EVA층으로 이루어진 라미네이팅 필름을 짧은 시간에 박리할 수 있어서 버려지는 폐 라미네이팅필름을 효율적으로 재활용할 수 있다는 점에서 경제적으로 유익하며 환경오염의 문제도 함께 해결할 수 있다는 효과를 얻을 수 있다. The recovery method of the present invention is economically advantageous in that it can efficiently recycle the waste laminating film that is discarded by peeling the laminating film composed of the PET layer and the EVA layer using hydrogen peroxide solution and the punching step in a short time, and environmental pollution The problem can be solved together.

본 발명의 회수방법은 무공해특성을 가진 과산화수소액을 사용하기 때문에 사용후 폐수처리단계에서 환경오염의 문제를 줄일 수 있다는 효과를 얻을 수 있다.



Since the recovery method of the present invention uses a hydrogen peroxide solution having pollution-free characteristics, it is possible to obtain an effect of reducing the problem of environmental pollution in the wastewater treatment step after use.



Claims (5)

분쇄기를 이용해 라미네이트필름을 분쇄하여 분쇄물을 형성하는 분쇄단계와PET층과 EVA층을 1차적으로 박리시키기 위하여 상기 분쇄물을 과산화수소가 저장된 분쇄물침전조에 침전시키는 침전단계와, 상기 분쇄물을 상기 분쇄물침전조로부터 타발기로 유입시켜 타격하는 타발단계와, 상기 타발기로부터 유출된 분쇄물을 침전분리조에 투입하고 비중차이로 인해 상층으로 부유한 EVA와 하층으로 침전된 PET를 분리하여 유출시키는 분리단계와, 분리된 EVA와 PET를 탈수하는 탈수단계를 포함하는 것을 특징으로 하는 회수방법.A pulverizing step of pulverizing the laminate film using a pulverizer to form a pulverized product, and a precipitation step of precipitating the pulverized product in a pulverized precipitate settling tank in which hydrogen peroxide is stored so as to first peel the PET layer and the EVA layer, The punching step of injecting and crushing the pulverized product from the crushing tank, and putting the pulverized product discharged from the crusher into the sedimentation separation tank and separating and discharging the PET suspended in the upper layer and the PET precipitated in the lower layer due to the specific gravity difference. And a dehydration step of dehydrating the separated EVA and PET. 제 1 항에 있어서, 상기 분리단계는 세척단계를 추가로 포함하며, 상기 세척단계는 타발기로부터 유출된 분쇄물이 물을 함유하는 침전분리조에 침전됨으로서 이루어지는 것을 특징으로 하는 회수방법.The method of claim 1, wherein the separating step further comprises a washing step, wherein the washing step is characterized in that the pulverized product discharged from the punching machine is precipitated in a sedimentation separation tank containing water. 제 2 항에 있어서, 상기 타발단계는 1차타발기에 의한 1차타발단계와, 2차타발기에 의한 2차타발단계로 이루어지는 것을 특징으로 하는 회수방법.The recovery method according to claim 2, wherein the punching step comprises a first punching step by a first punching machine and a second punching step by a second punching machine. 제 3 항에 있어서, 상기 탈수단계는 PET를 탈수하는 PET탈수단계와, EVA를 탈수하는 EVA탈수단계로 이루어진 것을 특징으로 하는 회수방법.4. The method of claim 3, wherein the dehydration step comprises a PET dehydration step of dehydrating PET and an EVA dehydration step of dehydrating EVA. 제 4 항에 있어서, 상기 분리단계와 PET탈수단계 사이에 PET를 PET타발기에 유입시켜 타격하는 PET타발단계와 상기 PET타발기로부터 유출된 PET를 PET침전조에 침전시켜 잔유 EVA를 박리시키는 PET침전단계를 추가로 포함하는 것을 특징으로 하는 회수방법.5. The PET precipitation step of claim 4, wherein the PET punching step of injecting PET into the PET punching machine and the PET spilled from the PET punching machine are separated from the PET punching tank between the separation step and the PET dehydration step to separate the residual EVA. Recovery method characterized in that it further comprises a step.
KR20040048874A 2004-06-28 2004-06-28 Method for Retrieving PET and EVA from Laminating Film KR100666093B1 (en)

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