KR20170037733A - Soundinsulation materials using recycled PVC from waste plastic and manufactuing method thereof - Google Patents

Soundinsulation materials using recycled PVC from waste plastic and manufactuing method thereof Download PDF

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KR20170037733A
KR20170037733A KR1020150136517A KR20150136517A KR20170037733A KR 20170037733 A KR20170037733 A KR 20170037733A KR 1020150136517 A KR1020150136517 A KR 1020150136517A KR 20150136517 A KR20150136517 A KR 20150136517A KR 20170037733 A KR20170037733 A KR 20170037733A
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weight
parts
insulating material
polyvinyl chloride
sound insulating
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KR101740813B1 (en
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계형산
이종태
이일행
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목원대학교 산학협력단
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29DPRODUCING PARTICULAR ARTICLES FROM PLASTICS OR FROM SUBSTANCES IN A PLASTIC STATE
    • B29D99/00Subject matter not provided for in other groups of this subclass
    • B29D99/001Producing wall or panel-like structures, e.g. for hulls, fuselages, or buildings
    • 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
    • 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
    • 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
    • B29B2017/0262Specific separating techniques using electrical caracteristics
    • B29B2017/0265Electrostatic separation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B29WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
    • B29KINDEXING 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
    • B29K2027/00Use of polyvinylhalogenides or derivatives thereof as moulding material
    • B29K2027/06PVC, i.e. polyvinylchloride
    • 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
    • Y02W30/52Mechanical processing of waste for the recovery of materials, e.g. crushing, shredding, separation or disassembly
    • 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

Abstract

The present invention relates to an acoustic foam used in various industries, particularly, an acoustic foam using polyvinyl chloride (PVC) extracted from plastic wastes, and more specifically, to an acoustic foam which uses recycled PVC from plastic wastes and has excellent sound-blocking properties and heat-insulating properties, and a method of producing the same. According to the present invention, the method of producing an acoustic foam using recycled PVC from plastic wastes comprises the steps of: washing selected plastic wastes and crushing the same into particles of selected sizes; along with a pressurized air, passing mixed particles of the crushed plastic wastes through a pipe charging device (104) made of charging materials to charge the mixed particles; passing the mixed particles of crushed plastic wastes containing negatively-charged PVC particles between a negatively-charged negative electrode plate (105) and a positively-charged positive electrode plate (106) to collect the PVC particles onto the positive electrode plate (106); mixing 100-150 parts by weight of the collected PVC particles, 40-60 parts by weight of barium sulfate (BaSO_4), 5-40 parts by weight of expanded vermiculite, 5-40 parts by weight of expanded perlite, 2-10 parts by weight of Mg-Stearate, 5-15 parts by weight of butyl stearate, 30-60 parts by weight of DOP, and 3-10 parts by weight of epoxidized soybean oil; and molding the acoustic foam produced in the previous step into a sheet or a selected shape.

Description

폐플라스틱의 폴리염화비닐을 재활용한 차음재 및 그 제조방법 {Soundinsulation materials using recycled PVC from waste plastic and manufactuing method thereof}BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a sound insulation material recycled from polyvinyl chloride of a waste plastic and a manufacturing method thereof,

본 발명은 여러 산업 분야에서 사용되는 차음재에 관한 것으로서 특히, 폐 플라스틱으로부터 폴리염화비닐(PVC)를 추출하여 이를 이용한 차음재에 관한 것으로서 차음성과 단열성이 우수한 폐 플라스틱의 폴리염화비닐을 재활용한 차음재 및 그 제조방법에 관한 것이다.
The present invention relates to a sound insulating material used in various industrial fields. More particularly, the present invention relates to a sound insulating material using polyvinyl chloride (PVC) extracted from waste plastic, and more particularly to a sound insulating material which recycles polyvinyl chloride And a manufacturing method thereof.

차음재는 외부로부터 유입되는 소음이나 내부의 소음이 외부로 유출되는 것을 방지하는 소재로서 여러 산업분야에서 널리 사용되고 있다.The sound insulating material is widely used in various industrial fields as a material for preventing external noise or internal noise from flowing out.

일반적으로 차음재는 베이스수지와 여러 첨가제를 혼합하여 차음이 필요한 부분에 코팅, 도포 및 부착하여 소음을 차단하도록 구성된다. 베이스 수지로 여러 가지 합성수지가 사용되고 있는데, 대표적인 베이스 수지로는 폴리염화비닐(PVC)이 널리 사용되고 있다.Generally, the sound insulating material is constituted to mix the base resin and various additives and to block the noise by coating, applying and attaching to the parts requiring sound insulation. Various synthetic resins are used as a base resin, and polyvinyl chloride (PVC) is widely used as a typical base resin.

폴리염화비닐은 성형이 용이하고, 강도가 우수하며, 여러 기계적 물성이 우수한 특징이 있어 차음재의 베이스수지로 널리 사용되고 있다.Polyvinyl chloride is widely used as a base resin for a sound insulating material since it is easy to mold, has excellent strength, and has excellent mechanical properties.

상기 폴리염화비닐과 함께 PE, PP 등 다양한 합성수지가 나무, 금속 기타물질을 대체하는 매우 우수하고 유용한 물질로서 생활 및 산업 전반에 걸쳐 다양하게 사용되고 있다.Along with the above polyvinyl chloride, various synthetic resins such as PE and PP are used as various excellent materials for replacing wood, metal and other materials throughout life and industry.

그러나 이러한 폐플라스틱은 다른 폐기물들과 함께 매립되거나 소각되는 것이 일반적이었다. 그러나 폐플라스틱의 경우 일부 성분과 다량의 첨가물들로 인하여 소각이나 매립 시, 처리설비를 훼손하거나 다이옥신 및 유독가스 등을 배출하여 환경오염의 거시적 원인이 되고 있다.However, these waste plastics were generally buried or incinerated with other wastes. However, in the case of waste plastics, due to some components and a large amount of additives, the incineration or landfill is damaging the treatment facilities or discharging dioxin and toxic gas, which is a macro cause of environmental pollution.

근래에는 경제적, 환경적 문제로 폐플라스틱을 재활용하기 위한 여러 가지 방법이 모색되고 있다.Recently, various methods for recycling waste plastics have been sought for economic and environmental problems.

이러한 폐플라스틱을 재활용함에 있어 가장 큰 문제가 되는 것은 폴리염화비닐(PVC)이다. 폴리염화비닐은 환경문제뿐만 아니라 RPF, 소각, 유화, 물질재생 등 모든 분야에서 플라시특 재활용을 어렵게 한다.The biggest problem in recycling such waste plastic is polyvinyl chloride (PVC). Polyvinyl chloride makes it difficult to recycle plastics in all areas, such as RPF, incineration, emulsification, and material regeneration, as well as environmental problems.

환경적 측면에서 유독가스 및 다이옥신은 유기염화물로서 주로 Cl(chlorine, 염소)를 함유하는 유기물을 소각할 때 발생된다. 폴리염화비닐은 그 무게에서 57%정도가 염소로 구성되어 있어 플라시트기 소재 중 가장 큰 다이옥신 방출 원인이 되고 있다.In terms of environment, toxic gas and dioxin are generated when incinerating organic matter containing mainly chlorine (chlorine) as an organic chloride. Polyvinyl chloride is composed of chlorine in 57% of the weight of polyvinyl chloride, which is the largest source of dioxins in plastic materials.

또한, 폴리염화비닐은 열가소성수지이지만 다량의 첨가물들로 인해 열분해가 심하게 일어나거나 새로운 화합물이 생성되기 때문에 폴리염화비질이 혼입된 폐플라스틱의 경우 PET용기는 물론 CO-PP, GPPS, HDPE 및 LDPE 등으로 이루어진 재질의 재생까지 불가능하게 하고, 재생이 되더라도 제품 또는 원료로서의 가치가 상실된다.
Polyvinyl chloride is a thermoplastic resin. However, due to the large amount of additives, pyrolysis occurs severely or a new compound is produced. Therefore, in case of waste plastics containing polychlorinated biphenyls, CO-PP, GPPS, HDPE and LDPE And the value as a product or a raw material is lost even if it is regenerated.

문헌 1. 대한민국특허청 공개특허공보 제10-2001-16543호, "공동주틱층간 바닥 충격차음재"Document 1: Korean Patent Application Publication No. 10-2001-16543, " 문헌 2. 대한민국특허청 등록실용신안공보 제20-0166900호, "흡.차음재"Document 2: Utility Model Registration No. 20-0166900, "Suction / sound insulating material" 문헌 3. 대한민국특허청 등록특허공보 제10-216424호, "차음재 조성물"Literature 3. KIPO No. 10-216424, "Sound Insulation Composition"

본 발명은 상기와 같은 문제점을 해결하기 위하여 안출한 것으로서 폐플라스틱으로부터 폴리염화비닐(PCV)을 효과적으로 분리 추출하고, 분리된 폴리염화비닐을 재활용하여 차음성과 단열성이 우수한 차음재를 제공할 수 있는 제조방법을 제공하는 것이 본 발명의 목적이다.
Disclosure of Invention Technical Problem [8] Accordingly, the present invention has been made in an effort to solve the above-mentioned problems, and an object of the present invention is to provide a sound insulation material which can effectively separate polyvinyl chloride (PCV) from waste plastic, recycle separated polyvinyl chloride It is an object of the present invention to provide a method.

상기의 목적을 달성하기 위하여 본 발명에 의한 폐플라스틱의 폴리염화비닐을 재활용한 차음재 제조방법은 선별된 폐플라스틱을 세척하고 소정 크기의 입도로 파쇄하는 단계; 파쇄된 폐플라스틱 혼합입자를 압축공기와 함께 하전물질로 이루어진 파이프 하전기(104)을 통과시켜 하전시키는 단계; (-)극성으로 하전된 폴리염화비닐 입자를 포함한 폐플라스틱 혼합입자를 (-)극성의 음극판(105)과 (+)극성의 양극판(106) 사이로 통과시켜 는 양극판(106)으로 폴리염화비닐 입자를 포집하는 단계; 상기 포집된 폴리염화비닐 100~150중량부, 황산바륨(BaSO4) 40~60중량부, 팽창질석(Expanded vermiculite) 5~40중량부, 팽창퍼라이트 5~40중량부, Mg-Stearate 2~10중량부, 부틸 스테아레이트 5~15중량부, DOP 30~60중량부, 에폭시화 대두유 3~10중량부를 혼합하는 단계; 상기와 같이 혼합된 차음재를 시트 또는 소정의 형태로 성형하는 단계;로 구성된다.According to another aspect of the present invention, there is provided a method of manufacturing a sound insulating material by recycling polyvinyl chloride of a waste plastic according to the present invention, comprising the steps of: washing selected waste plastic and crushing the waste plastic to a predetermined size; Charging the pulverized waste plastic mixed particles with compressed air through a pipe discharger 104 made of a charged material; (+) Polarity positive electrode plate 106 by passing the waste plastic mixed particles containing polyolefin resin particles charged with (-) polarity between the negative polar plate 105 and the positive polar plate 106, ; 100 to 150 parts by weight of the collected polyvinyl chloride, 40 to 60 parts by weight of barium sulfate (BaSO 4 ), 5 to 40 parts by weight of expanded vermiculite, 5 to 40 parts by weight of expanded perlite, 2 to 10 parts by weight of Mg- 5 to 15 parts by weight of butyl stearate, 30 to 60 parts by weight of DOP and 3 to 10 parts by weight of epoxidized soybean oil; And molding the sound insulating material mixed as described above into a sheet or a predetermined shape.

이때, 상기 혼합 단계에서 옥시던트(Oxidant) 40~50중량부가 더 혼합된 것을 특징으로 한다.At this time, 40 to 50 parts by weight of oxidant is further mixed in the mixing step.

또한, 상기 혼합 단계에서 글라스 탄화칩(Glass barbonize chip) 50~80중량부가 더 혼합된 것을 특징으로 한다.Further, in the mixing step, 50 to 80 parts by weight of glass barbonize chips are further mixed.

또한, 상기 혼합 단계에서 마이카(mica) 15~30중량부가 더 혼합된 것을 특징으로 한다.Also, 15 to 30 parts by weight of mica is further mixed in the mixing step.

또한, 상기 혼합 단계에서 에틸렌비닐아세테이트-염화비닐 5~12중량부가 더 혼합된 것을 특징으로 한다.Further, in the mixing step, 5 to 12 parts by weight of ethylene vinyl acetate-vinyl chloride is further mixed.

그리고 본 발명에 의한 폐플라스틱의 폴리염화비닐을 재활용한 차음재는 폐플라스틱으로부터 추출된 폴리염화비닐 100~150중량부, 황산바륨(BaSO4) 40~60중량부, 팽창질석(Expanded vermiculite) 5~40중량부, 팽창퍼라이트 5~40중량부, Mg-Stearate 2~10중량부, 부틸 스테아레이트 5~15중량부, DOP 30~60중량부, 에폭시화 대두유 3~10중량부로 구성된다.The sound insulating material recycled from the polyvinyl chloride of the waste plastic according to the present invention is composed of 100-150 parts by weight of polyvinyl chloride extracted from the waste plastic, 40-60 parts by weight of barium sulfate (BaSO 4 ), 5-80 parts by weight of expanded vermiculite, 40 to 40 parts by weight of expanded perlite, 2 to 10 parts by weight of Mg-stearate, 5 to 15 parts by weight of butyl stearate, 30 to 60 parts by weight of DOP and 3 to 10 parts by weight of epoxidized soybean oil.

이때, 상기 차음재에 옥시던트(Oxidant) 40~50중량부가 더 혼합된 것을 특징으로 한다.In this case, 40 to 50 parts by weight of oxidant is further mixed in the sound insulating material.

또한, 상기 차음재에 글라스 탄화칩(Glass barbonize chip) 50~80중량부가 더 혼합된 것을 특징으로 한다.Further, 50 to 80 parts by weight of glass barbonize chips are further mixed with the sound insulating material.

또한, 상기 차음재에 마이카(mica) 15~30중량부가 더 혼합된 것을 특징으로 한다.Also, 15 to 30 parts by weight of mica is further mixed with the sound insulating material.

또한, 상기 차음재에 에틸렌비닐아세테이트-염화비닐 5~12중량부가 더 혼합된 것을 특징으로 한다.
Further, the sound insulating material is further mixed with 5 to 12 parts by weight of ethylene vinyl acetate-vinyl chloride.

상기와 같이 구성된 본 발명에 의한 폴리염화비닐을 재활용한 차음재는 여러 가지 합성수지가 혼합된 폐플라스틱으로부터 폴리염화비닐을 효과적으로 추출하고, 추출된 폴리염화비닐을 이용하여 차음성과 단열성이 우수한 차음재를 생산할 수 있다.The sound insulating material recycled with polyvinyl chloride according to the present invention thus constructed effectively extracts polyvinyl chloride from waste plastics mixed with various synthetic resins and uses the extracted polyvinyl chloride to produce a sound insulating material excellent in sound insulation and heat insulation .

또한, 폐플라스틱을 재활용하기 어렵게하는 요인인 폴리염화비닐을 추출하여 분리함으로써, 폴리염화비닐이 추출된 폐플라스틱으로부터 여러 가지 다양한 합성수지 재활용이 용이하게 이루어지는 효과가 있다.
Further, by extracting and separating polyvinyl chloride, which is a factor that makes it difficult to recycle the waste plastic, it is possible to easily recycle various synthetic resins from waste plastic from which polyvinyl chloride is extracted.

도 1은 정전선별장치를 도시한 도면.BRIEF DESCRIPTION OF THE DRAWINGS FIG.

이하 본 발명에 의한 폐플라스틱의 폴리염화비닐을 재활용한 차음재 및 그 제조방법에 대하여 상세하게 설명한다.Hereinafter, a sound insulating material recycled from polyvinyl chloride of waste plastics according to the present invention and a method for producing the same will be described in detail.

먼저, 재활용하기 위하여 회수한 폐플라스틱을 세척하고 폴리염화비닐(PVC)가 함유된 폐플라스틱을 파쇄하여 PVC입자와 다른 합성수지 입자가 혼합된 혼합입자를 제조한다.First, waste plastics recovered for recycling are washed and waste plastic containing polyvinyl chloride (PVC) is crushed to prepare mixed particles in which PVC particles and other synthetic resin particles are mixed.

상기 폐플라스틱을 파쇄하여 제조된 혼합입자를 도 1에 도시한 선별기(100)의 주입구(103)에 공급하고, 공기압축기(101)에 전원을 인가하여 공기압축기(101)에서 발생하는 압축공기를 이용하여 주입구(103)에 공급된 폐플라스틱 혼합입자를 파이프 하전기(104)로 불어 공급한다.The mixed particles produced by crushing the waste plastic are supplied to the injection port 103 of the sorter 100 shown in FIG. 1 and the compressed air generated in the air compressor 101 is supplied to the air compressor 101 The waste plastic mixed particles supplied to the injection port 103 are blown to the pipe charge 104. [

주입구(103)로 공급된 폐플라스틱 혼합입자는 압축공기와 함께 파이프 하전기(104)로 이동한다.The waste plastic mixed particles supplied to the injection port 103 moves to the pipe charge 104 together with compressed air.

파이프 하전기(104)로 이동한 폐플라스틱 혼합입자는 파이프 하전기(104) 내에서 공기에 의해 유동하면서 하전물질로 이루어진 파이프 하전기(104)의 내벽과 마찰 또는 충돌하면서 폴리염화비닐 입자는 (-)극성을 하전되고, 다른 페플라스틱 입자는 (+)극성으로 하전된다.The waste plastic mixed particles that have moved to the pipe charge 104 flow by air in the pipe charge 104 and collide with or collide with the inner wall of the pipe charge 104 made of the charged material so that the polyvinyl chloride particles -) polarity is charged and the other plastic particles are charged with (+) polarity.

상기와 같이 파이프 하전기(104)를 통해 (-)극성 또는 (+)극성으로 하전된 폐플라스틱 혼합입자는 분류탱크(108)로 공급되어 분류탱크(108) 내부를 낙하한다.As described above, the waste plastic mixed particles charged with (-) polarity or (+) polarity through the pipe charge 104 is supplied to the fractionation tank 108 and drops inside the fractionation tank 108.

상기 분류탱크(108)의 내부에는 폐플라스틱 혼합입자가 낙하하는 경로 양 측에 대칭구조로 각각 (-)극성의 음극판(105)과 (+)극성의 양극판(106)이 설치되어 있다.(-) polarity anode plate 105 and a (+) polarity anode plate 106 are provided symmetrically on both sides of the path where the waste plastic mixed particles fall down.

따라서, 분류탱크(108) 내부를 낙하하는 폐플라스틱 혼합입자에서 (-)극성으로 하전된 폴리염화비닐 입자는 양극판(106)으로 이동하고, (+)극성으로 하전된 다른 폐플라스틱 입자는 음극판(105)으로 이동하며 낙하한다.Therefore, the polyvinyl chloride particles charged with (-) polarity from the waste plastic mixed particles falling inside the separation tank 108 move to the positive electrode plate 106 and other waste plastic particles charged with positive polarity move to the negative electrode plate 105).

양극판(106)으로 이동하며 낙하하는 폴리염화비닐 입자와, 음극판(105)으로 이동하며 낙하하는 다른 폐플라스틱 입자는 각각 양극판(106)과 음극판(105)에 의해 분류되며 낙하하고, 분류탱크(108)의 하부에 설치된 포집기(107)에 의해 폴리염화비닐 입자와 다른 폐플라스틱 입자로 분류되어 포집된다.The polyvinyl chloride particles falling and moving to the positive electrode plate 106 and the other waste plastic particles falling and moving to the negative electrode plate 105 are separated and fall by the positive electrode plate 106 and the negative electrode plate 105, The waste plastic particles other than the polyvinyl chloride particles are collected and collected.

이때, 상기 파이프 하전기(104)는 도 1과 같이 나선형 형태로 성형하여 폐플라스틱 혼합입자가 하전물질로 성형된 긴 경로의 파이프 하전기(104)를 통과하면서 충분히 마찰 및 충돌하면서 하전되도록 구성하는 것이 바람직하다.At this time, the pipe charge 104 is formed into a spiral shape as shown in FIG. 1, so that the waste plastic mixed particles are charged with sufficient friction and collision while passing through the long-path pipe charge 104 formed of a charge material .

또한, 상기 공기압축기(101)와 주입구(103) 사이에는 공기건조기(102)를 설치함으로써, 공기압축기(101)에서 공급되는 압축공기 내부에 포함된 수분을 제거하는 것이 바람직하다.It is preferable that the air dryer 102 is installed between the air compressor 101 and the injection port 103 to remove moisture contained in the compressed air supplied from the air compressor 101.

압축공기 내부에 수분이 포함되면 폐플라스틱 혼합입자의 하전 및 선별효율에 악영향을 미치기 때문이다.This is because the presence of moisture in the compressed air adversely affects the charging and sorting efficiency of the waste plastic mixed particles.

폴리염화비닐을 상기와 같이 선별기(100)를 통해 선별된 폴리염화비닐 입자를 이용하여 차음재를 제조하기 위하여 포집기(107)에 선별된 폴리염화비닐 입자를 수거한다.The polyvinyl chloride particles collected in the collector 107 are collected in order to produce the sound insulating material using the polyvinyl chloride particles selected through the separator 100 as described above.

상기와 같은 방법으로 폐플라스틱으로부터 분류 수거된 폴리염화비닐 입자를 용융시킨 폴리염화비닐 수지(PVC) 100~150중량부에 대해, 황산바륨(Barium Sulfate, BaSO4) 40~60중량부, 팽창질석(Expanded Vermiculite) 5~40중량부, 팽창 퍼라이트(Peal stone) 5~40중량부, 안정제로서 Mg-St(Magnesium Stearate) 2~10중량부, 활제로서 부틸 스테아레이트 5~15중량부, 가소제로서 DOP 30~60중량부 및 에폭시화 대두유(EOS) 3~10중량부를 혼합하여 본 발명의 차음재가 구성된다.40 to 60 parts by weight of barium sulfate (BaSO 4 ) is added to 100 to 150 parts by weight of polyvinyl chloride resin (PVC) obtained by melting polyvinyl chloride particles classified and collected from the waste plastics in the same manner, 5 to 40 parts by weight of expandable Vermiculite, 5 to 40 parts by weight of expanded stone, 2 to 10 parts by weight of Mg-St (Magnesium Stearate) as stabilizer, 5 to 15 parts by weight of butyl stearate as a lubricant, 30 to 60 parts by weight of DOP and 3 to 10 parts by weight of epoxidized soybean oil (EOS) are mixed to constitute the sound insulating material of the present invention.

폴리염화비닐 수지 100~150중량부에 대해, 황산바륨(BaSO4) 40~60중량부를 혼합한다.40 to 60 parts by weight of barium sulfate (BaSO 4 ) are mixed with 100 to 150 parts by weight of the polyvinyl chloride resin.

황산바륨(Barium Sulfate, BaSO4)은 일정 수준의 난연성을 차음재에 부여하기 위한 것으로서 폴리염화비닐 수지 100~150중량부에 대해 황산바륨을 40~60중량부를 혼합한다. 황산바륨이 40중량부 미만이면 난연성이 저하되고 60중량부를 초과하면 차음재의 연질성이 저하되어 조직이 부스러질 가능성이 높으므로 황산바륨을 40~60중량부 혼합한다.Barium sulfate (BaSO 4 ) is used to impart a certain level of flame retardancy to a sound insulating material, and 40 to 60 parts by weight of barium sulfate is mixed with 100 to 150 parts by weight of a polyvinyl chloride resin. If the barium sulfate is less than 40 parts by weight, the flame retardancy is lowered. If it exceeds 60 parts by weight, the softness of the sound insulating material is deteriorated and the possibility of the structure being broken is high, so 40 to 60 parts by weight of barium sulfate is mixed.

그리고 폴리염화비닐 수지 100~150중량부에 대해 팽창질석(Expanded vermiculite) 5~40중량부를 혼합한다.Then, 5 to 40 parts by weight of expanded vermiculite is mixed with 100 to 150 parts by weight of the polyvinyl chloride resin.

질석(Vermiculite)은 일반적으로 금운모나 흑운모의 변질 산물인 함수 운모를 말하는 것으로서 유일하게 흡수수와 층간수 및 결정수의 3가지 수분을 함유하고 있는 특유의 광물이다.Vermiculite is a unique mineral containing water, which is the only water mica that is the alteration product of phlogopite and biotite.

이것을 급격한 고열로 가열할 경우 질석의 층간에 있는 수분이 수증기로 기화되어 압력이 발생하고, 이 압력이 방출되면서 질석이 발기팽창하여 팽창질석이 된다.When it is heated with a sudden high heat, the water in the layer of vermiculite is vaporized by steam and pressure is generated, and as the pressure is released, the vermiculite expands and becomes the expanding vermiculite.

이렇게 열에 의해 박리팽창된 팽창질석(Expanded vermiculite)은 수지와의 결합력이 우수하고, 비중이 매우 낮고 우수한 단열성 및 불연성, 소음 차단효과 및 수분 흡수효과, 물리적 충격 흡수효과가 있다.Expanded vermiculite, which is exfoliated by heat, has excellent bonding strength with resin, very low specific gravity, excellent heat insulating property and nonflammability, noise shielding effect, moisture absorbing effect and physical shock absorbing effect.

상기와 같은 팽창질석은 5~40중량부가 혼합되는데 5중량부 미만으로 혼합되면 팽창질석에 의한 단열성, 불연성 및 차음성 성능을 기대할 수 없고, 40중량부를 초과하여 혼합하면 차음재의 물리적 강도가 저하되고, 자연스러운 표면 마감이 어려워지므로 팽창질석은 5~40중량부를 혼합하는 것이 바람직하다.5 to 40 parts by weight of the above-described expanded vermiculite is mixed. When the mixture is mixed in an amount of less than 5 parts by weight, it is impossible to expect heat insulation, incombustibility and sound insulation performance by the expanded vermiculite. , And natural surface finish becomes difficult, it is preferable to mix 5 to 40 parts by weight of expanded vermiculite.

그리고 폴리염화비닐 수지 100~150중량부에 대해 팽창퍼라이트(Pearl stone) 5~40중량부를 혼합한다.Then, 5 to 40 parts by weight of expanded pearlite is mixed with 100 to 150 parts by weight of the polyvinyl chloride resin.

팽창퍼라이트는 정석(화산암의 일종)을 1,000~1,300의 온도로 소성 팽창하여 만들어진 천연 무기재료로서, 소성 팽창 가공을 통해 발생한 수많은 기공들로 인하여 수지와의 결합성이 우수하고, 단열성 및 차음성이 우수해진다.Expansion Perlite is a natural inorganic material made by plastic expansion and expansion at a temperature of 1,000 ~ 1,300. It is excellent in bonding with resin due to numerous pores generated by plastic expansion processing, It is excellent.

팽창퍼라이트는 5~40중량부가 혼합되는데, 5중량부 미만으로 혼합되면 팽창퍼라이트의 단열성 및 차음성을 기대할 수 없고, 40중량부를 초과하여 혼합하면 차음재의 자연스러운 표면 마감이 어려워지는 문제가 있으므로 팽창퍼라이트는 5~40중량부를 혼합하는 것이 바람직하다.When the amount of the expanded peroxide is less than 5 parts by weight, the thermal insulation and sound insulation of the expanded peroxide can not be expected. When the amount of the expanded peroxide is more than 40 parts by weight, the natural surface finish of the sound insulating material becomes difficult. Is preferably mixed with 5 to 40 parts by weight.

그리고 Mg-Stearate(Magnesium stearate) 2~10중량부를 혼합한다.And 2 to 10 parts by weight of Mg-Stearate (Magnesium stearate).

폴리염화비닐을 가공할 때 필연적으로 HCl이 발생하는데 상기 Mg-Stearate가 혼합되어 폴리염화비닐을 가공할 때 발생하는 HCl을 제거한다. 폴리염화비닐을 가공할 때 발생하는 HCl은 폴리염화비닐의 분해를 촉진하는 역할을 하기 때문에 이 HCl을 얼마나 제거하느냐에 따라 폴리염화비닐 수지의 안정성이 결정된다.In the process of polyvinyl chloride, HCl is inevitably generated, and the Mg-stearate is mixed to remove HCl generated when polyvinyl chloride is processed. Since the HCl generated in the processing of polyvinyl chloride promotes the decomposition of polyvinyl chloride, the stability of the polyvinyl chloride resin depends on how much HCl is removed.

Mg-Stearate를 2~10중량부를 혼합하는데, 이 혼합범위를 벗어나면 제품각격, 내후성과 활성 및 플로우 밸런스에 악영향을 미치므로 Mg-Stearate를 2~10중량부 혼합하는 것이 바람직하다.2 to 10 parts by weight of Mg-stearate is mixed. If the mixing range is out of the range, product stiffness, weather resistance, activity and flow balance are adversely affected. Therefore, it is preferable to mix 2 to 10 parts by weight of Mg-stearate.

그리고 폴리염화비닐 100~150중량부에 대해 활제로서 부틸 스테아레이트 5~15중량부를 혼합한다. 부틸 스테아레이트는 상용성과 내부 활성이 우수한 장점이 있다. 상기 부틸 스테아레이트는 5~15중량부를 혼합하는데 이 범위를 벗어나면 제품가격, 유동성, 내후성, 내충격성에 영향을 주게 된다.And 5 to 15 parts by weight of butyl stearate as a lubricant are mixed with 100 to 150 parts by weight of polyvinyl chloride. Butyl stearate has an advantage of being excellent in compatibility and internal activity. The butyl stearate is mixed in an amount of 5 to 15 parts by weight, and if it is out of this range, the product price, fluidity, weather resistance and impact resistance are affected.

그리고 가소제로서 디옥틸프탈레이트(Dioctylphthalate:DOP) 30~60중량부를 혼합하고, 에폭시화 대두유(EOS) 3~10중량부를 혼합한다.And 30 to 60 parts by weight of dioctyl phthalate (DOP) as a plasticizer are mixed and 3 to 10 parts by weight of epoxidized soybean oil (EOS) are mixed.

상기 에폭시화 대두유가 혼합됨으로써 차음재의 표면 오염물 부착과 긁힘을 방지하는 효과가 있다.By mixing the epoxidized soybean oil, adhesion of surface contaminants and scratching of the sound insulating material are prevented.

상술한 바와 같이 폐플라스틱으로부터 분류 수거된 폴리염화비닐 입자를 용융시킨 폴리염화비닐 수지(PVC) 100~150중량부에 대해, 황산바륨(Barium Sulfate, BaSO4) 40~60중량부, 팽창질석(Expanded Vermiculite) 5~40중량부, 팽창 퍼라이트(Peal stone) 5~40중량부, 안정제로서 Mg-St(Magnesium Stearate) 2~10중량부, 활제로서 부틸 스테아레이트 5~15중량부, 가소제로서 DOP 30~60중량부 및 에폭시화 대두유(EOS) 3~10중량부를 혼합하여 본 발명의 차음재가 구성된다.40 to 60 parts by weight of barium sulfate (BaSO 4 ) and 40 to 60 parts by weight of expanded vermiculite (PVC) are added to 100 to 150 parts by weight of polyvinyl chloride resin (PVC) obtained by melting polyvinyl chloride particles classified and collected from waste plastics, 5 to 40 parts by weight of expandable Vermiculite, 5 to 40 parts by weight of expanded stone, 2 to 10 parts by weight of Mg-St (Magnesium Stearate) as stabilizer, 5 to 15 parts by weight of butyl stearate as a lubricant, 30 to 60 parts by weight and epoxidized soybean oil (EOS) 3 to 10 parts by weight are mixed to constitute the sound insulating material of the present invention.

여기에 차음재의 인장강도를 높이기 위하여 옥시던트(Oxidant) 40~50중량부를 더 혼합하여 차음재를 구성할 수 있고, 차음성능의 증대를 위해 글라스 탄화칩(Glass Carbonize chip)을 50~80중량부를 더 혼합할 수 있다.In order to increase the tensile strength of the sound insulating material, 40 to 50 parts by weight of oxidant may be further mixed to form a sound insulating material. To increase the sound insulating performance, 50 to 80 parts by weight of a glass carbon chip is further mixed can do.

그리고 마이카(mica) 15~30중량부를 더 혼합하는 것이 바람직하다.And 15 to 30 parts by weight of mica are further mixed.

상기 마이카는 PVC수지의 분산성을 일정하게 보장하여 제품 성형시 수지의 유동을 원활하게 하여 치수안정성 및 생산성을 높인다. 그리고 마이카의 함유랑에 따라 차음효과와 충격강도 및 인장강도 등의 강도를 높일 수 있으므로 완성된 차음재의 외부 충격에 대한 변형과 파손을 방지할 수 있다.The mica ensures the dispersibility of the PVC resin to be constant, which smoothes the flow of the resin during the molding of the product, thereby improving dimensional stability and productivity. According to the content of the mica, the strength of the sound insulation effect, the impact strength and the tensile strength can be increased, so that the deformation and breakage of the finished sound insulating material against the external impact can be prevented.

특히, 차음재가 상,하수도 배관의 외면에 도포된 경우 차음재를 파이프에 접합성을 증대시켜서 그 경계면이 박리되어 차음성이 저하되는 것을 방지하는 역할을 한다. 이러한 마이카는 제품 성형과 원료의 단가를 고려하여 15~40중량부를 혼합하는 것이 바람직하다.Particularly, when the sound insulating material is applied to the outer surface of the upper and the sewer pipe, the sound insulating material is increased in the bonding property to the pipe, and the interface is peeled off to prevent the car sound from being deteriorated. It is preferable that such a mica is mixed with 15 to 40 parts by weight in consideration of product molding and unit cost of raw materials.

그리고 충격보강제로서 에틸렌비닐아세테이트-염화비닐(EVA-VC) 5~12중량부를 혼합한다.And 5 to 12 parts by weight of ethylene vinyl acetate-vinyl chloride (EVA-VC) as an impact modifier.

상기와 같이 구성된 본 발명에 의한 차음재는 시트 형태로 성형되어 차음이 필요한 곳에 부착되거나, 파이프나 연결관을 제조할 때 파이프나 연결관 외면에 형성되어 소음을 차음하도록 구성된다.
The sound insulating material according to the present invention configured as described above is formed in the form of a sheet to be attached to a place where sound insulation is required or is formed on the outer surface of a pipe or a connecting pipe when a pipe or a connecting pipe is manufactured.

<실시예><Examples>

폴리염화비닐(PVC) 100중량부, 황산바륨 50중량부, 옥시던트 40중량부, 글라스 탄화칩 60중량부, 마이카 20중량부, 팽창질석 20중량부, 팽창퍼라이트 20중량부, EVA-VC 7중량부, Mg-Stearate 7중량부, 부틸 스테아레이트 10중량부, DOP 30중량부 및 에폭시화 대두유 5중량부를 혼합하여 시트 형태로 차음재를 성형하였다.100 parts by weight of polyvinyl chloride (PVC), 50 parts by weight of barium sulfate, 40 parts by weight of oxidant, 60 parts by weight of glass carbonized chips, 20 parts by weight of mica, 20 parts by weight of expanded vermiculite, 20 parts by weight of expanded peroxide, 7 parts by weight of Mg-stearate, 10 parts by weight of butyl stearate, 30 parts by weight of DOP and 5 parts by weight of epoxidized soybean oil were mixed to form a sound insulating material in a sheet form.

그리고 캘린더에서 제품의 표면을 매끈하게 다듬고 광택을 낸 후, 냉각공정을 거쳐 제품의 신축과 팽창의 변형이 최소화되도록 차음재 시트를 제조하였다.
Then, the surface of the product was smoothly polished and calendered on a calendar, and a sound insulating sheet was manufactured through a cooling process so as to minimize deformation of expansion and contraction of the product.

소음비교시험Noise comparison test
시험항목


Test Items

시험결과Test result
철판 3mmSteel plate 3mm 철판 3mm + 본 발명 차음시트 2mmSteel plate 3 mm + inventive soundproof sheet 2 mm 주파수
(Hz)
frequency
(Hz)
음압레벨
(dB)
Sound pressure level
(dB)
주파수
(Hz)
frequency
(Hz)
음압레벨
(dB)
Sound pressure level
(dB)
주파수
(Hz)
frequency
(Hz)
음압레벨
(dB)
Sound pressure level
(dB)
주파수
(Hz)
frequency
(Hz)
음압레벨
(dB)
Sound pressure level
(dB)



음압

레벨

조사




Sound pressure

level

Research

5050 60.660.6 630630 66.666.6 5050 51.751.7 630630 60.160.1
6363 58.058.0 800800 65.065.0 6363 50.750.7 800800 58.858.8 8080 57.757.7 1,0001,000 60.860.8 8080 51.051.0 10001000 54.354.3 100100 67.767.7 12501250 56.156.1 100100 52.752.7 12501250 51.151.1 125125 65.165.1 16001600 57.057.0 125125 62.062.0 16001600 52.052.0 160160 74.774.7 20002000 57.857.8 160160 70.470.4 20002000 49.749.7 200200 77.277.2 25002500 55.255.2 200200 71.771.7 25002500 48.248.2 250250 64.464.4 31503150 52.152.1 250250 62.562.5 31503150 41.541.5 315315 66.566.5 40004000 59.959.9 315315 61.961.9 40004000 41.341.3 400400 67.367.3 50005000 51.851.8 400400 62.862.8 50005000 38.038.0 500500 66.066.0 -- -- 500500 61.961.9 -- --

- 시험방법 : KS A ISO 3744:2002 (음향-음압법에 의한 소음원의 음원파워레벨 측정방법-반사면강 준자유음장에서의 실용측정 방법)을 준용하여 2개의 사각 구조물 내부에 음원을 넣고 한 개의 구조물에는 본 발명의 차음재로 성형한 시트를 부착하고 다른 한 개의 구조물에는 방음시트를 부착하지 않은 상태에서 외부의 소음을 측정하였다.- Test method: According to KS A ISO 3744: 2002 (Measurement method of source power level of noise source by acousto-sound pressure method - Practical measurement method on reflection surface rough free sound field), sound source is put in two rectangular structures and one Noise was measured in a state in which a sheet molded from the sound insulating material of the present invention was attached to the structure and no soundproof sheet was attached to the other structure.

상기 표 1에서와 같이 본 발명의 차음재를 소재로 성형된 시트를 부착하였을 때와 부착하지 않았을 때 외부 소음에 큰 차이가 있는 것을 알 수 있다.
As shown in Table 1, it can be seen that there is a large difference in the external noises when the seat formed of the sound insulating material of the present invention is attached and when the seat is not attached.

공지된 종래의 폴리염화비닐을 베이스로 하는 차음재와 본 발명의 차음재의 차음성능 비교는 다음과 같다.A comparison of known sound insulation performance between a conventional soundproofing material based on polyvinyl chloride and the sound insulating material of the present invention is as follows.

<비교예><Comparative Example>

폴리염화비닐(PVC) 100중량부, DOP 30중량부, Mg-Stearate 7중량부, 황산바륨 80중량부, EVC-VC 10중량부를 혼합하여 시트 형태로 차음재를 성형하고, 캘린더에서 제품의 표면을 매끈하게 다듬고 광택을 낸 후, 냉각공정을 거쳐 제품의 신축과 팽창의 변형이 최소화되도록 차음재 시트를 제조하였다.
100 parts by weight of polyvinyl chloride (PVC), 30 parts by weight of DOP, 7 parts by weight of Mg-stearate, 80 parts by weight of barium sulfate and 10 parts by weight of EVC-VC were mixed to form a sound insulating material. After smoothly polished and polished, a sound insulating sheet was manufactured through a cooling process so as to minimize deformation of expansion and contraction of the product.

소음비교시험Noise comparison test
시험항목


Test Items

시험결과Test result
철판 3mm + 비교예 차음시트 2mmSteel plate 3mm + Comparative example Soundproof sheet 2mm 철판 3mm + 본 발명 차음시트 2mmSteel plate 3 mm + inventive soundproof sheet 2 mm 주파수
(Hz)
frequency
(Hz)
음압레벨
(dB)
Sound pressure level
(dB)
주파수
(Hz)
frequency
(Hz)
음압레벨
(dB)
Sound pressure level
(dB)
주파수
(Hz)
frequency
(Hz)
음압레벨
(dB)
Sound pressure level
(dB)
주파수
(Hz)
frequency
(Hz)
음압레벨
(dB)
Sound pressure level
(dB)



음압

레벨

조사




Sound pressure

level

Research

5050 55.855.8 630630 63.663.6 5050 51.751.7 630630 60.160.1
6363 54.254.2 800800 62.162.1 6363 50.750.7 800800 58.858.8 8080 54.954.9 10001000 58.758.7 8080 51.051.0 10001000 54.354.3 100100 61.161.1 12501250 54.254.2 100100 52.752.7 12501250 51.151.1 125125 64.264.2 16001600 54.954.9 125125 62.062.0 16001600 52.052.0 160160 72.372.3 20002000 53.553.5 160160 70.470.4 20002000 49.749.7 200200 75.075.0 25002500 52.052.0 200200 71.771.7 25002500 48.248.2 250250 63.163.1 31503150 48.348.3 250250 62.562.5 31503150 41.541.5 315315 64.564.5 40004000 50.450.4 315315 61.961.9 40004000 41.341.3 400400 64.764.7 50005000 45.845.8 400400 62.862.8 50005000 38.038.0 500500 64.264.2 -- -- 500500 61.961.9 -- --

- 시험방법 : KS A ISO 3744:2002 (음향-음압법에 의한 소음원의 음원파워레벨 측정방법-반사면강 준자유음장에서의 실용측정 방법)을 준용하여 2개의 사각 구조물 내부에 음원을 넣고 한 개의 구조물에는 본 발명의 차음재로 성형한 시트를 부착하고 다른 한 개의 구조물에는 공지의 방음시트를 부착힌 상태에서 외부의 소음을 측정하였다.- Test method: According to KS A ISO 3744: 2002 (Measurement method of source power level of noise source by acousto-sound pressure method - Practical measurement method on reflection surface rough free sound field), sound source is put in two rectangular structures and one The exterior noise was measured in a state in which a sheet formed of the sound insulating material of the present invention was attached to the structure and a known soundproof sheet was attached to the other structure.

상기 표 2에서와 같이 본 발명의 차음재를 소재로 성형된 시트를 부착하였을 때와 공지의 차음재 시트를 부착하여 비교한 외부 소음 측정결과 본 발명의 차음재가 공지의 차음재보다 차음성능이 우수한 것을 알 수 있다. 이러한 차음성능 차이의 주원인은 본 발명에 혼합된 다공성 팽창질석과 팽창퍼라이트가 차음성을 향상시기기 때문이다.
As shown in Table 2, when the seat made of the sound insulating material of the present invention was attached and the known sound insulating sheet was attached, the sound insulating performance of the sound insulating material of the present invention was found to be superior to that of a known sound insulating material have. The main reason for such difference in sound insulation performance is that the porous expanded ceramics mixed with the expanded perlite improve the sound insulation.

상기와 같이 구성된 본 발명에 의한 폴리염화비닐을 재활용한 차음재는 여러 가지 합성수지가 혼합된 폐플라스틱으로부터 폴리염화비닐을 효과적으로 추출하고, 추출된 폴리염화비닐을 이용하여 차음성과 단열성이 우수한 차음재를 생산할 수 있다.The sound insulating material recycled with polyvinyl chloride according to the present invention thus constructed effectively extracts polyvinyl chloride from waste plastics mixed with various synthetic resins and uses the extracted polyvinyl chloride to produce a sound insulating material excellent in sound insulation and heat insulation .

이상, 본 발명에 의한 폐플라스틱의 폴리염화비닐을 재활용한 차음재 및 그 제조방법에 대해 설명하였다.The sound insulating material recycled from the polyvinyl chloride of the waste plastic according to the present invention and the method for producing the same were described above.

상기 본 발명의 기술적 구성은 본 발명이 속하는 기술분야의 당업자가 그 기술적 사상이나 필수적 특징을 변경하지 않고서 다른 구체적인 형태로 실시될 수 있다는 것을 이해할 수 있을 것이다.It will be understood by those skilled in the art that the technical features of the present invention may be embodied in other specific forms without departing from the spirit or essential characteristics thereof.

그러므로, 이상에서 기술한 실시 예들은 모든 면에서 예시적인 것이며 한정적인 것이 아닌 것으로서 이해되어야 하고, 본 발명의 범위는 전술한 상세한 설명보다는 후술하는 특허청구범위에 의하여 나타내어지며, 특허청구범위의 의미 및 범위 그리고 그 등가 개념으로부터 도출되는 모든 변경 또는 변형된 형태가 본 발명의 범위에 포함되는 것으로 해석되어야 할 것이다.
Therefore, it should be understood that the above-described embodiments are to be considered in all respects as illustrative and not restrictive, the scope of the invention being indicated by the appended claims rather than the foregoing description, Ranges and equivalents thereof are to be construed as being included within the scope of the present invention.

100 : 선별기
101 : 공기압축기
102 : 공기건조기
103 : 주입구
104 : 파이프 하전기
105 : 음극판
106 : 양극판
107 : 포집기
108 : 분류탱크
100: selector
101: air compressor
102: air dryer
103: inlet
104: Pipelayer electric
105: cathode plate
106: positive electrode plate
107: Collector
108: Classification tank

Claims (10)

선별된 폐플라스틱을 세척하고 소정 크기의 입도로 파쇄하는 단계;
파쇄된 폐플라스틱 혼합입자를 압축공기와 함께 하전물질로 이루어진 파이프 하전기(104)을 통과시켜 하전시키는 단계;
(-)극성으로 하전된 폴리염화비닐 입자를 포함한 폐플라스틱 혼합입자를 (-)극성의 음극판(105)과 (+)극성의 양극판(106) 사이로 통과시켜 는 양극판(106)으로 폴리염화비닐 입자를 포집하는 단계;
상기 포집된 폴리염화비닐 100~150중량부, 황산바륨(BaSO4) 40~60중량부, 팽창질석(Expanded vermiculite) 5~40중량부, 팽창퍼라이트 5~40중량부, Mg-Stearate 2~10중량부, 부틸 스테아레이트 5~15중량부, DOP 30~60중량부, 에폭시화 대두유 3~10중량부를 혼합하는 단계;
상기와 같이 혼합된 차음재를 시트 또는 소정의 형태로 성형하는 단계;로 구성된 것을 특징으로 하는 폐플라스틱의 폴리염화비닐을 재활용한 차음재 제조방법.
Washing the selected waste plastic and crushing it to a predetermined size of particle size;
Charging the pulverized waste plastic mixed particles with compressed air through a pipe discharger 104 made of a charged material;
(+) Polarity positive electrode plate 106 by passing the waste plastic mixed particles containing polyolefin resin particles charged with (-) polarity between the negative polar plate 105 and the positive polar plate 106, ;
100 to 150 parts by weight of the collected polyvinyl chloride, 40 to 60 parts by weight of barium sulfate (BaSO 4 ), 5 to 40 parts by weight of expanded vermiculite, 5 to 40 parts by weight of expanded perlite, 2 to 10 parts by weight of Mg- 5 to 15 parts by weight of butyl stearate, 30 to 60 parts by weight of DOP and 3 to 10 parts by weight of epoxidized soybean oil;
And molding the sound insulating material mixed as described above into a sheet or a predetermined shape. The method of manufacturing a sound insulating material recycled with polyvinyl chloride of waste plastic.
제1항에 있어서,
상기 혼합 단계에서 옥시던트(Oxidant) 40~50중량부가 더 혼합된 것을 특징으로 하는 폐플라스틱의 폴리염화비닐을 재활용한 차음재 제조방법.
The method according to claim 1,
And 40 to 50 parts by weight of an oxidant is further mixed in the mixing step.
제1항에 있어서,
상기 혼합 단계에서 글라스 탄화칩(Glass barbonize chip) 50~80중량부가 더 혼합된 것을 특징으로 하는 폐플라스틱의 폴리염화비닐을 재활용한 차음재 제조방법.
The method according to claim 1,
And 50 to 80 parts by weight of glass barbonize chips are further mixed in the mixing step.
제1항에 있어서,
상기 혼합 단계에서 마이카(mica) 15~30중량부가 더 혼합된 것을 특징으로 하는 폐플라스틱의 폴리염화비닐을 재활용한 차음재 제조방법.
The method according to claim 1,
And 15 to 30 parts by weight of mica is further mixed in the mixing step. The method for manufacturing a sound insulating material recycled with polyvinyl chloride of waste plastic.
제1항에 있어서,
상기 혼합 단계에서 에틸렌비닐아세테이트-염화비닐 5~12중량부가 더 혼합된 것을 특징으로 하는 폐플라스틱의 폴리염화비닐을 재활용한 차음재 제조방법.
The method according to claim 1,
And 5 to 12 parts by weight of ethylene vinyl acetate-vinyl chloride is further mixed in the mixing step.
폐플라스틱으로부터 추출된 폴리염화비닐 100~150중량부, 황산바륨(BaSO4) 40~60중량부, 팽창질석(Expanded vermiculite) 5~40중량부, 팽창퍼라이트 5~40중량부, Mg-Stearate 2~10중량부, 부틸 스테아레이트 5~15중량부, DOP 30~60중량부, 에폭시화 대두유 3~10중량부로 구성된 것을 특징으로 하는 폐플라스틱의 폴리염화비닐을 재활용한 차음재.
100 to 150 parts by weight of polyvinyl chloride extracted from waste plastic, 40 to 60 parts by weight of barium sulphate (BaSO 4 ), 5 to 40 parts by weight of expanded vermiculite, 5 to 40 parts by weight of expanded perlite, Mg-Stearate 2 To 10 parts by weight of butyl stearate, 5 to 15 parts by weight of butyl stearate, 30 to 60 parts by weight of DOP and 3 to 10 parts by weight of epoxidized soybean oil.
제6항에 있어서,
상기 차음재에 옥시던트(Oxidant) 40~50중량부가 더 혼합된 것을 특징으로 하는 폐플라스틱의 폴리염화비닐을 재활용한 차음재.
The method according to claim 6,
And 40 to 50 parts by weight of an oxidant is further mixed in the sound insulating material.
제6항에 있어서,
상기 차음재에 글라스 탄화칩(Glass barbonize chip) 50~80중량부가 더 혼합된 것을 특징으로 하는 폐플라스틱의 폴리염화비닐을 재활용한 차음재.
The method according to claim 6,
And 50 to 80 parts by weight of glass barbonize chips are further mixed in the sound insulating material.
제6항에 있어서,
상기 차음재에 마이카(mica) 15~30중량부가 더 혼합된 것을 특징으로 하는 폐플라스틱의 폴리염화비닐을 재활용한 차음재.
The method according to claim 6,
And 15 to 30 parts by weight of mica is further mixed in the sound insulating material.
제6항에 있어서,
상기 차음재에 에틸렌비닐아세테이트-염화비닐 5~12중량부가 더 혼합된 것을 특징으로 하는 폐플라스틱의 폴리염화비닐을 재활용한 차음재.
The method according to claim 6,
Wherein the sound insulating material is further mixed with 5 to 12 parts by weight of ethylene vinyl acetate-vinyl chloride, and recycled polyvinyl chloride of the waste plastic.
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