JP2006274101A - Method for recovering vinyl chloride resin and recovery treatment equipment therefor - Google Patents

Method for recovering vinyl chloride resin and recovery treatment equipment therefor Download PDF

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JP2006274101A
JP2006274101A JP2005097121A JP2005097121A JP2006274101A JP 2006274101 A JP2006274101 A JP 2006274101A JP 2005097121 A JP2005097121 A JP 2005097121A JP 2005097121 A JP2005097121 A JP 2005097121A JP 2006274101 A JP2006274101 A JP 2006274101A
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vinyl chloride
chloride resin
sheet
waste
solution
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JP4247196B2 (en
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Noriaki Ide
昇明 井出
Tatsuki Nagano
竜規 永野
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Shinko Pantec Co Ltd
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Kobelco Eco Solutions Co Ltd
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    • 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
    • B29B17/02Separating plastics from other materials
    • B29B2017/0213Specific separating techniques
    • B29B2017/0286Cleaning means used for separation
    • B29B2017/0289Washing the materials 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
    • B29B2017/0293Dissolving the materials in gases or liquids
    • 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
    • Y02W30/62Plastics recycling; Rubber recycling

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  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)

Abstract

<P>PROBLEM TO BE SOLVED: To provide an efficient recovery method for recovering a vinyl chloride resin by dissolving in a solvent a sheet-like waste product containing the vinyl chloride resin to which stains such as soil difficult to remove are sticking. <P>SOLUTION: The method for recovering the vinyl chloride resin from the sheet-like waste product comprises a washing step for throwing the sheet-like waste product into a washing tub, feeding water at 40-70°C and washing the waste product, a dissolution step for dissolving the washed sheet-like waste product in a solvent in which the vinyl chloride resin is soluble to obtain a vinyl chloride resin-containing solution, a separation step for separating insoluble from the vinyl chloride resin-containing solution, and a recovery step for recovering the vinyl chloride resin from the solution from which the insoluble has been removed. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は廃棄物から塩化ビニル系樹脂を回収する方法及び回収処理設備に関し、詳しくは塩化ビニル系樹脂を含有するシート状廃棄物からの回収方法及び回収処理設備に関する。   The present invention relates to a method and a recovery processing facility for recovering vinyl chloride resin from waste, and more particularly to a recovery method and a recovery processing facility from sheet-like waste containing vinyl chloride resin.

塩化ビニル樹脂、塩化ビニリデン樹脂などの塩化ビニル系樹脂は加工性に優れると共に安価なポリマーであるので、ポリエステルやポリオレフィン(例えば、ポリエチレンやポリプロピレンなど)等の他の汎用ポリマーと同様に様々な用途に使用されている。しかしながら、このような汎用ポリマーは、ライフサイクルの長い基素材分野だけでなく、日用品等の使用寿命の短い商品材料として大量生産され、従って大量廃棄に伴う環境汚染が問題となっている。   Since vinyl chloride resins such as vinyl chloride resin and vinylidene chloride resin are excellent in processability and inexpensive, they can be used in various applications like other general-purpose polymers such as polyester and polyolefin (for example, polyethylene and polypropylene). in use. However, such general-purpose polymers are mass-produced not only in the field of basic materials having a long life cycle, but also as commodity materials having a short service life such as daily necessities, and therefore, environmental pollution associated with mass disposal is a problem.

塩化ビニル系樹脂を主成分とする廃棄物としては、例えば廃電線被覆、建築資材での壁紙など以外に、家庭用のレジャーシート、グランドシート、あるいはハウス栽培に用いられる農業用ビニールシート、建築工事現場での建築物のカバーシートなどが挙げられる。このような廃棄物の大部分は埋立てあるいは焼却などにより処理されているが、塩化ビニル系樹脂は自然界では分解することができず、また良く知られているように焼却によりダイオキシンを生成する原因物質のひとつであるため、環境への影響も考慮する必要がある。   Wastes mainly composed of vinyl chloride resin include, for example, household electric leisure sheets, ground sheets, agricultural vinyl sheets used for house cultivation, and construction work, in addition to waste electric wire coverings and wallpaper for building materials. For example, a cover sheet for a building on site. Most of such waste is disposed of by landfill or incineration, but vinyl chloride resin cannot be decomposed in nature, and as is well known, the cause of dioxin formation by incineration Because it is one of the substances, it is necessary to consider the environmental impact.

このため、塩化ビニル系樹脂を主成分とする廃棄物から塩化ビニル系樹脂を回収し再利用するための種々の回収方法が検討されている。例えば、粉砕、遠心分離などによる機械的な回収方法以外に、最近では廃棄物を塩化ビニル系樹脂が溶解可能な溶媒に溶解し、溶液から塩化ビニル系樹脂を回収する方法が検討されている(例えば、特許文献1〜3)。
特開平11−310660号公報 特表2003−510436号公報 特開2004−292549号公報
For this reason, various recovery methods for recovering and reusing vinyl chloride resin from wastes mainly composed of vinyl chloride resin have been studied. For example, in addition to mechanical recovery methods such as pulverization and centrifugation, recently, a method has been studied in which waste is dissolved in a solvent in which vinyl chloride resin can be dissolved, and vinyl chloride resin is recovered from the solution ( For example, Patent Documents 1 to 3).
JP-A-11-310660 Special table 2003-510436 gazette JP 2004-292549 A

上記のような溶媒を用いた回収方法は安全性も高く高純度で塩化ビニル系樹脂を回収できるため好ましいが、廃棄物がシート状である場合には使用時に汚れが付着しやすく、特に農業用ビニールシートのようなものは屋外で使用されるものであるため土壌物の付着がひどく、付着物を簡単に除去することができない。このような付着物が存在すると回収される塩化ビニル系樹脂中に土壌物が混入し、塩化ビニル系樹脂の品質低下につながるという問題がある。このため溶解前に磁石などの磁気処理により付着物中の金属を除去することが考えられるが、非金属の土壌物は十分に除去することができない。また、溶媒を用いた回収方法では溶解処理時に生ずる不溶物を分離することが行われるが、過剰な付着物を有するシート状廃棄物では不溶物が大量に発生し分離工程で目詰まりなどを生じるため処理効率を低下させることとなる。さらに、溶解前に予めシート状廃棄物を洗浄処理することも考えられるが、単なる洗浄処理では付着力の弱い土壌物は除去できてもシートに強固に付着した土壌物は十分除去することが困難である。不純物量が少なく高純度の塩化ビニル系樹脂を回収しようとする場合、そのような除去され難い付着物が最終的な品質に大きく影響を与えることとなる。特に、塩化ビニル系樹脂を再生利用する場合、用途に応じて着色剤を添加し、着色後、製品として利用するが、土壌物が再利用品に混入した場合、再生品の見た目も悪く、着色剤を大量に添加する必要がある。そのため、再生品の用途が限定されるか、または、着色剤を大量に添加することによりコストが高くなるという問題があった。   The recovery method using the above solvent is preferable because it is highly safe and can collect vinyl chloride resin with high purity. However, when the waste is in the form of a sheet, dirt easily adheres to it during use. Since something like a vinyl sheet is used outdoors, the adhesion of the soil is bad and the deposit cannot be easily removed. If such deposits are present, there is a problem that soil matter is mixed into the recovered vinyl chloride resin, leading to deterioration of the quality of the vinyl chloride resin. For this reason, it is considered that the metal in the deposit is removed by magnetic treatment such as a magnet before melting, but the non-metallic soil cannot be removed sufficiently. In addition, in the recovery method using a solvent, insoluble matters generated during the dissolution treatment are separated. However, a large amount of insoluble matters are generated in a sheet-like waste having excessive deposits, and clogging occurs in the separation step. Therefore, the processing efficiency is lowered. Furthermore, it is conceivable to wash the sheet-shaped waste in advance before dissolution, but it is difficult to sufficiently remove the soil that is firmly attached to the sheet even if the soil with weak adhesion can be removed by simple washing. It is. In the case of collecting a high-purity vinyl chloride resin with a small amount of impurities, such a hard-to-remove deposit greatly affects the final quality. In particular, when recycling vinyl chloride resin, add a colorant according to the application and use it as a product after coloring, but when the soil is mixed in the recycled product, the recycled product looks bad and is colored. It is necessary to add a large amount of the agent. For this reason, there is a problem that the use of the recycled product is limited, or the cost is increased by adding a large amount of the colorant.

また、シート状廃棄物の場合チップ状で処理される廃電線被覆などと異なり、その嵩高さから溶媒への溶液濃度を高めることができず、溶液中でシート状廃棄物が凝集し溶解性が低下するなど廃棄物の処理効率が低下するという問題があった。   Also, in the case of sheet-like waste, unlike waste wire coating that is processed in the form of chips, the concentration of the solution in the solvent cannot be increased due to its bulkiness, and the sheet-like waste aggregates in the solution and has solubility. There has been a problem that the processing efficiency of the waste is lowered, for example, it is lowered.

本発明は上記事情に鑑みなされたものであり、その目的は土壌物などの汚れが付着し、その除去が困難な塩化ビニル系樹脂を含有するシート状廃棄物を溶媒に溶解して塩化ビニル系樹脂を高純度で回収する場合の効率的な回収方法及び回収処理設備を提供することにある。   The present invention has been made in view of the above circumstances, and its purpose is to dissolve a sheet-like waste containing a vinyl chloride resin to which dirt such as soil matters adheres and which is difficult to remove, in a solvent. An object of the present invention is to provide an efficient recovery method and recovery processing facility for recovering a resin with high purity.

本発明の上記課題を解決するための塩化ビニル系樹脂を含有するシート状廃棄物から塩化ビニル系樹脂を回収する方法とは、前記シート状廃棄物を洗浄槽内に投入し温度40〜70℃の水を供給して洗浄する洗浄工程と、前記洗浄されたシート状廃棄物を前記塩化ビニル系樹脂が溶解可能な溶媒に溶解し、塩化ビニル系樹脂含有溶液を得る溶解工程と、前記塩化ビニル系樹脂含有溶液から不溶物を分離する分離工程と、前記不溶物を除去した溶液から前記塩化ビニル系樹脂を回収する回収工程を備えることを要旨とする。上記のような洗浄工程で予め処理されたシート状廃棄物は土壌物に由来する付着物を極めて低減することができる。このため溶媒に溶解した時に不溶物の混在を抑え、分離工程での効率化が図れるとともに、回収される塩化ビニル系樹脂の純度を上げることができる。   The method for recovering vinyl chloride resin from sheet waste containing a vinyl chloride resin for solving the above-mentioned problems of the present invention means that the sheet waste is put into a washing tank and the temperature is 40 to 70 ° C. A washing step of supplying water for washing, a washing step of dissolving the washed sheet waste in a solvent in which the vinyl chloride resin can be dissolved to obtain a vinyl chloride resin-containing solution, and the vinyl chloride The present invention includes a separation step of separating an insoluble matter from a resin-containing resin solution and a recovery step of collecting the vinyl chloride resin from the solution from which the insoluble matter has been removed. The sheet-like waste treated in advance in the washing step as described above can greatly reduce the deposits derived from soil. For this reason, when it melt | dissolves in a solvent, mixing of an insoluble matter can be suppressed, the efficiency in a separation process can be achieved, and the purity of the recovered vinyl chloride resin can be increased.

また、本発明は前記洗浄工程後、溶解工程の前に、前記洗浄されたシート状廃棄物を冷却し、裁断する工程をさらに備えることが好ましい。このような冷却、裁断工程を設けることによりシート状廃棄物を小片のフラフとし、処理の効率化を図ることができる。   Moreover, it is preferable that the present invention further includes a step of cooling and cutting the washed sheet-like waste after the washing step and before the dissolving step. By providing such a cooling and cutting step, the sheet-like waste can be made into small pieces of fluff, and the processing efficiency can be improved.

また、本発明は前記洗浄工程後、溶解工程の前に、前記洗浄されたシート状廃棄物を加熱溶融した後、造粒して塩化ビニル系樹脂含有造粒物とする造粒工程をさらに備えることが好ましい。シート状廃棄物を加熱溶融し、造粒することにより、処理物の比重を大きくすることができ、処理効率を向上できる。また、造粒物とすることにより溶解工程での溶液濃度をシート状廃棄物に比較して上げることができ、シート状廃棄物では溶液中に10〜15重量%程度までしか溶解することができなかったのに対し、造粒物では20重量%以上での処理も可能となる。   In addition, the present invention further includes a granulation step after the washing step and before the dissolution step, after the washed sheet-like waste is heated and melted, and granulated to obtain a vinyl chloride resin-containing granulated product. It is preferable. By heating and melting the sheet waste and granulating, the specific gravity of the processed product can be increased, and the processing efficiency can be improved. In addition, by using a granulated product, the concentration of the solution in the dissolution process can be increased compared to that of sheet waste, and in the case of sheet waste, only about 10 to 15% by weight can be dissolved in the solution. In contrast, the granulated product can be treated at 20% by weight or more.

また、本発明は前記洗浄工程後、造粒工程前に、脱水工程をさらに備えることが好ましい。このような脱水工程を造粒前に設けることにより、造粒工程での加熱溶融を円滑に行うことができる。   The present invention preferably further comprises a dehydration step after the washing step and before the granulation step. By providing such a dehydration step before granulation, heating and melting in the granulation step can be performed smoothly.

本発明の前記回収工程は前記不溶物を除去した溶液に熱水及び/またはスチーム(以下、単に「熱水等」ということがある)を接触させて塩化ビニル系樹脂を析出する工程を備えることが好ましい。このような回収工程により高純度で塩化ビニル系樹脂を回収することができる。   The recovery step of the present invention includes a step of depositing a vinyl chloride resin by bringing hot water and / or steam (hereinafter sometimes simply referred to as “hot water”) into contact with the solution from which the insoluble matter has been removed. Is preferred. By such a recovery step, the vinyl chloride resin can be recovered with high purity.

また本発明の前記回収工程は前記不溶物を除去した溶液に塩化ビニル系樹脂の非溶媒を添加して塩化ビニル系樹脂を析出する工程を備えることが好ましい。このような回収工程によっても高純度で塩化ビニル系樹脂を回収することができる。   Moreover, it is preferable that the said collection | recovery process of this invention is equipped with the process of adding the non-solvent of vinyl chloride resin to the solution which removed the said insoluble matter, and depositing vinyl chloride resin. The vinyl chloride resin can be recovered with high purity by such a recovery process.

また、本発明は上記回収方法を備えることを特徴とする塩化ビニル系樹脂回収処理設備である。本発明の回収処理設備によれば、シート状廃棄物から塩化ビニル系樹脂を高純度で、効率的に回収することができる。   In addition, the present invention is a vinyl chloride resin recovery treatment facility comprising the above recovery method. According to the recovery processing facility of the present invention, vinyl chloride resin can be efficiently recovered from sheet waste with high purity.

本発明の回収方法によれば、土壌物などの汚れが付着しやすく、その除去が困難な塩化ビニル系樹脂を含有するシート状廃棄物を処理対象とする場合であっても、洗浄工程で40〜70℃の洗浄水で洗浄されるためシート状廃棄物が軟化し強固に付着した土壌物に由来する付着物を効率的に除去することができる。従って、このシート状廃棄物を溶解工程により回収する方法に用いることにより、不純物の少ない塩化ビニル系樹脂を効率的に回収することができる。   According to the collection method of the present invention, even when a sheet-like waste containing a vinyl chloride resin, which is difficult to remove due to soil dirt or the like being attached thereto, is treated in the washing step. Since it is washed with washing water at ˜70 ° C., it is possible to efficiently remove the deposits derived from the soil that the sheet-like waste is softened and firmly adhered. Therefore, by using this sheet-like waste in a method of recovering by a dissolving step, vinyl chloride resin with less impurities can be recovered efficiently.

(実施の形態1)
図1は、実施の形態1に係る発明の洗浄工程から回収工程を示すフロー図である。本発明において処理される、例えば塩化ビニル樹脂や塩化ビニリデン樹脂などの塩化ビニル系樹脂を主成分として含有する原料には農業用ビニールシート、建築現場用シートなどのシート状廃棄物が挙げられる。このようなシート状廃棄物は、土壌物などによる付着物が多量にシート表面あるいはシート内部に含有されており、そのまま溶媒に投入して溶解すると不溶物が大量に発生し、処理効率が極めて低下するとともに、回収される塩化ビニル系樹脂の純度が低下することとなる。このため、本発明では所定条件の洗浄工程を経て溶解処理される。このシート状廃棄物の大きさは特に限定されるものではないが、長尺のシートなどは余りに大きいと洗浄を効率的に行うことができず、また洗浄装置も大型化する。一方、シート状廃棄物が小さすぎると、加水と摩擦により洗浄作用が低下するおそれがあることから、予め100〜400mm四方程度の大きさまで裁断することが好ましい。この裁断は従来公知のシート裁断機を使用することができる。なお、付着物量が少ないシート状廃棄物であっても、本発明を使用することによりさらに回収される塩化ビニル系樹脂中の不純物量を低下するために好ましく使用できることができる。
(Embodiment 1)
FIG. 1 is a flowchart showing a recovery process from a cleaning process according to the first embodiment. Examples of the raw material containing, as a main component, a vinyl chloride resin such as a vinyl chloride resin or a vinylidene chloride resin treated in the present invention include sheet-like waste such as agricultural vinyl sheets and construction site sheets. Such sheet-like waste contains a large amount of deposits due to soil, etc. on the surface of the sheet or inside the sheet, and when it is poured into a solvent and dissolved, a large amount of insoluble matter is generated, resulting in extremely low processing efficiency. At the same time, the purity of the recovered vinyl chloride resin decreases. For this reason, in this invention, it melt | dissolves through the washing | cleaning process of a predetermined condition. The size of the sheet-like waste is not particularly limited, but if a long sheet or the like is too large, cleaning cannot be performed efficiently, and the cleaning apparatus becomes large. On the other hand, if the sheet-like waste is too small, the cleaning action may be reduced due to water and friction. Therefore, it is preferable to cut the sheet waste to a size of about 100 to 400 mm square. For this cutting, a conventionally known sheet cutting machine can be used. In addition, even if it is a sheet-like waste with a small amount of deposits, it can be preferably used to reduce the amount of impurities in the vinyl chloride resin recovered by using the present invention.

上記のようにして得られるシート状廃棄物を洗浄装置に投入して洗浄し、付着物の量を低減する。洗浄工程における条件としては特に温度の制御が付着物の除去量に大きく影響するため一定範囲に水温を制御することが肝要である。すなわち、農業用ビニールシートなどに使用されている塩化ビニル系樹脂は重合度が1,100〜1,300程度の塩化ビニル系樹脂であり、このような塩化ビニル系樹脂は40℃以上となると軟化してくる。この軟化によって表面に付着した土壌物だけでなく、内部に入り込んだ土壌物が水流により洗い流されやすくなり、多量の付着物を効率的に除去することができる。本発明者らの検討によれば、常温の水を用いた場合と比較して3倍量以上の付着物を除去する効果があることを確認している。一方、洗浄水の温度が余りに高くなりすぎるとシートが軟化し過ぎてしまい、付着物がシート内に取り込まれて除去量が減少することとなる。このため、洗浄に使用する水の温度は40〜70℃が好ましく、40〜60℃が最適である。   The sheet-like waste obtained as described above is put into a cleaning device for cleaning, and the amount of deposits is reduced. As a condition in the cleaning process, it is important to control the water temperature within a certain range, particularly because the temperature control greatly affects the amount of deposits removed. That is, the vinyl chloride resin used in agricultural vinyl sheets and the like is a vinyl chloride resin having a degree of polymerization of about 1,100 to 1,300, and such a vinyl chloride resin is softened at 40 ° C. or higher. Come on. By this softening, not only the soil attached to the surface but also the soil that has entered the interior is easily washed away by the water flow, and a large amount of attached matter can be efficiently removed. According to the study by the present inventors, it has been confirmed that there is an effect of removing adhering substances more than three times as much as in the case of using room temperature water. On the other hand, if the temperature of the washing water becomes too high, the sheet will be too soft, and deposits will be taken into the sheet and the removal amount will be reduced. For this reason, the temperature of water used for washing is preferably 40 to 70 ° C, and most preferably 40 to 60 ° C.

また、洗浄工程での装置内のシート状廃棄物の滞留時間は10〜50秒で、水の量は廃棄物1t当たり0.1〜0.5t供給することが好ましい。滞留時間が10秒未満であったり、水の供給量が0.1t未満である場合は廃棄物と水との接触する時間が少なすぎ、また水が廃棄物全体に行き渡らず十分な洗浄が行えない傾向にある。一方、滞留時間を長時間とすることや、水量を多くすることにより除去量は増えていくが、余りに長時間としても洗浄効果にそれほど差がなく経済的でない。   In addition, the residence time of the sheet-like waste in the apparatus in the cleaning process is preferably 10 to 50 seconds, and the amount of water is preferably 0.1 to 0.5 t per 1 t of waste. If the residence time is less than 10 seconds or the amount of water supply is less than 0.1 t, the contact time between the waste and the water is too little, and the water does not reach the entire waste and can be washed sufficiently. There is no tendency. On the other hand, the removal amount increases by increasing the residence time or increasing the amount of water, but even if it is too long, there is not much difference in the cleaning effect, which is not economical.

本発明の溶解処理により塩化ビニル系樹脂の回収処理を行う場合に、上記で得られる洗浄後のシート状廃棄物中の付着物の目安としては、廃棄物1t当たり0.05t以下とすることが好ましい。この程度まで付着物量を低減したシートであれば、後の処理工程における短縮化を十分に図れるとともに、回収される塩化ビニル系樹脂は土壌物による着色の弱い0.5重量%未満の不純物量まで減少できるため、再生塩化ビニル系樹脂として各種用途に使用することが可能となる。   When the vinyl chloride resin is collected by the dissolution treatment of the present invention, the standard of deposits in the sheet-like waste after washing obtained above is 0.05 t or less per 1 t of waste. preferable. If the amount of the adhering material is reduced to this level, the sheet can be sufficiently shortened in the subsequent processing step, and the recovered vinyl chloride resin is less than 0.5% by weight of impurities that are weakly colored by soil. Since it can be reduced, it can be used as a recycled vinyl chloride resin in various applications.

次に、上記のようにして得られる洗浄されたシート状廃棄物を溶解処理するが、予めシート状廃棄物を裁断して50mm四方以下のフラフとすることもできる。   Next, although the washed sheet-like waste obtained as described above is subjected to a dissolution treatment, the sheet-like waste can be preliminarily cut into a fluff of 50 mm square or less.

溶解処理にはシート中に含まれる塩化ビニル系樹脂が溶解可能な溶媒が用いられる。具体的には、例えば、極性溶媒、特にケトン類溶媒が好適に利用でき、これによってポリオレフイン類などのポリマーを含有する廃棄物からでも塩化ビニル系樹脂を選択溶解させることができる。しかも、ケトン類溶媒を用いると、高分子量の塩化ビニル系樹脂まで処理可能である。ケトン類溶媒としては、アセトン、メチルエチルケトン、ジエチルケトン、シクロヘキサノンなどが挙げられる。また、本発明においては塩化ビニル系樹脂の溶解性の高いテトラヒドロフランなどのエーテル類、N−メチルピロリドンなどの水溶性アミド化合物、γ−ブチロラクトンなどの水溶性ラクトン化合物も使用可能である。使用される溶媒は廃棄物中に含まれる塩化ビニル系樹脂の溶解性や、塩化ビニル系樹脂を回収処理する処理方法などによって適宜選択することができる。   For the dissolution treatment, a solvent capable of dissolving the vinyl chloride resin contained in the sheet is used. Specifically, for example, a polar solvent, particularly a ketone solvent, can be suitably used, whereby the vinyl chloride resin can be selectively dissolved even from waste containing a polymer such as polyolefins. In addition, when a ketone solvent is used, a high molecular weight vinyl chloride resin can be processed. Examples of the ketone solvent include acetone, methyl ethyl ketone, diethyl ketone, and cyclohexanone. In the present invention, ethers such as tetrahydrofuran with high solubility of vinyl chloride resin, water-soluble amide compounds such as N-methylpyrrolidone, and water-soluble lactone compounds such as γ-butyrolactone can also be used. The solvent used can be appropriately selected depending on the solubility of the vinyl chloride resin contained in the waste, the treatment method for recovering the vinyl chloride resin, and the like.

溶解処理時に溶媒を加熱する温度は使用する溶媒の種類によって異なるが、溶媒が揮発する温度未満であれば特に限定されず、安全に操業できる範囲で温度を制御すれば良い。なお溶解する方法としては特に限定されず、洗浄したシート状廃棄物を容器に予め投入し、そこへ溶媒を添加して加熱撹拌することもできるし、予め加熱した溶媒に廃棄物を混合して撹拌しても良い。   Although the temperature which heats a solvent at the time of a melt | dissolution process changes with kinds of solvent to be used, if it is less than the temperature which a solvent volatilizes, it will not specifically limit, What is necessary is just to control temperature in the range which can be operated safely. The method for dissolving is not particularly limited, and the washed sheet waste can be put into a container in advance, and a solvent can be added to the container and heated and stirred, or the waste can be mixed with the preheated solvent. You may stir.

次に、得られた溶液は塩化ビニル系樹脂などの溶解物と溶媒に不溶な不溶物に分離する。分離する手段は特に限定されず、スクリーン、遠心分離や沈澱法など公知の方法を利用することができる。   Next, the obtained solution is separated into a dissolved substance such as a vinyl chloride resin and an insoluble substance insoluble in a solvent. The means for separating is not particularly limited, and a known method such as a screen, centrifugal separation or precipitation can be used.

不溶物を分離した溶液は次に回収工程に移送される。この回収工程においては従来から公知の回収方法を利用することができる。例えば、(a)溶液に熱水及び/またはスチームを接触させて溶媒を蒸発させながら塩化ビニル系樹脂を沈殿により析出させ回収する方法、(b)溶液を加熱して溶媒を蒸発させることにより塩化ビニル系樹脂を析出させ加熱溶融して回収する方法などを用いることができる。図1は上記のうち(a)の析出工程を備えた回収方法を利用するものであり、この方法によれば塩化ビニル系樹脂の回収と溶媒の蒸発を同時に行うことができるため好ましい。以下は、この回収方法に用いられる処理方法の一例である。なお、上記方法としては、例えば特開平11−310660号などに記載の方法を参考にすることができる。   The solution from which insoluble matter has been separated is then transferred to a recovery step. In this recovery step, a conventionally known recovery method can be used. For example, (a) a method in which hot water and / or steam is brought into contact with the solution to evaporate the solvent and the vinyl chloride resin is precipitated and recovered by precipitation; (b) chlorination is performed by evaporating the solvent by heating the solution. For example, a method in which a vinyl resin is deposited, melted by heating, and recovered can be used. FIG. 1 utilizes the recovery method including the precipitation step (a) among the above, and this method is preferable because recovery of the vinyl chloride resin and evaporation of the solvent can be performed simultaneously. The following is an example of the processing method used for this collection method. In addition, as said method, the method as described in Unexamined-Japanese-Patent No. 11-310660 etc. can be referred, for example.

まず、不溶物を分離した溶液と熱水等を接触させると溶媒に対する塩化ビニル系樹脂の溶解度が極端に低下すると共に、溶液中の溶媒が揮発し、溶液から塩化ビニル系樹脂を順次粒子状の沈殿物として析出させることができる。そして、沈澱物を分離し粒子状の塩化ビニル系樹脂を含む溶液から残存溶剤を除去することにより塩化ビニル系樹脂を回収することができる。   First, when the solution from which the insoluble matter has been separated is brought into contact with hot water, the solubility of the vinyl chloride resin in the solvent is drastically reduced, and the solvent in the solution is volatilized. It can be deposited as a precipitate. Then, the vinyl chloride resin can be recovered by separating the precipitate and removing the residual solvent from the solution containing the particulate vinyl chloride resin.

本発明では溶液と熱水等を接触させる方法は特に限定されるものではないが、熱水等を前記溶液に注入する方法が推奨される。この方法であれば、塩化ビニル系樹脂を溶解している溶液の注入量が一定でない場合や操業を突然停止した場合などでも、塩化ビニル系樹脂が一時的に析出しないという事態を招くに止まり、溶液注入量を厳密に制御することなく操業できる。   In the present invention, the method of bringing the solution into contact with hot water or the like is not particularly limited, but a method of injecting hot water or the like into the solution is recommended. If this method is used, even when the injection amount of the solution dissolving the vinyl chloride resin is not constant or when the operation is suddenly stopped, the vinyl chloride resin does not temporarily precipitate, Operation is possible without strictly controlling the amount of solution injected.

本発明では前記溶液から析出した塩化ビニル系樹脂を残存溶剤などから分離することによって、塩化ビニル系樹脂を回収することができる。分離方法は、特に限定されず公知の方法が採用でき、例えば、スクリーンや遠心分離が例示できる。そして、分離された水は必要に応じて析出工程に戻すことができる。   In the present invention, the vinyl chloride resin can be recovered by separating the vinyl chloride resin precipitated from the solution from the residual solvent or the like. The separation method is not particularly limited, and a known method can be employed. Examples thereof include a screen and centrifugation. And the isolate | separated water can be returned to a precipitation process as needed.

次に、本発明の目的を達成することのできる塩化ビニル系樹脂の回収処理設備の一形態について説明する。図2は本発明の洗浄工程において用いられる洗浄装置1の概略図であり、図3は洗浄されたシート状廃棄物を溶解し、溶液から塩化ビニル系樹脂を回収する溶解、分離、回収工程の各構成を示す概略図である。   Next, an embodiment of a vinyl chloride resin recovery treatment facility that can achieve the object of the present invention will be described. FIG. 2 is a schematic view of a cleaning apparatus 1 used in the cleaning process of the present invention, and FIG. 3 is a dissolution, separation, and recovery process for dissolving the washed sheet waste and recovering the vinyl chloride resin from the solution. It is the schematic which shows each structure.

図2の洗浄装置1は外槽12と内槽13を備える2槽式の横置き洗浄装置であり、内槽13は効率的な洗浄が行えるよう縦方向に回転自在なドラムとなっている。また内槽13の内壁面には突起部14が形成されており、その突起部14は移送手段L1により投入口17から投入されたシート状廃棄物(図示せず)を排出口18へ内部を搬送するよう螺旋状に形成されている。   The cleaning device 1 in FIG. 2 is a two-tank horizontal cleaning device that includes an outer tub 12 and an inner tub 13, and the inner tub 13 is a drum that is rotatable in the vertical direction so that efficient cleaning can be performed. Further, a protrusion 14 is formed on the inner wall surface of the inner tub 13, and the protrusion 14 passes the inside of the sheet-like waste (not shown) input from the input port 17 by the transfer means L <b> 1 to the output port 18. It is formed in a spiral shape to be conveyed.

内槽13の内部には水管15が導入され、配管L2から40〜70℃に制御された温水16を内部に供給する構造を有しており、この温水16により内槽13内を進むシート状廃棄物が洗浄される。そして図示はされていないが内槽13の壁面には多数の穴が穿設されており、温水16が洗浄装置の内部に供給され、シート状廃棄物を洗浄した後、壁面の穴から汚水が排水されるようになっている。この形態におけるドラムの回転速度は前述の滞留時間を確保するように適宜選択すれば良く、特に限定されるものではないが、通常10〜30rpmとすることが好ましい。なお、この形態では外槽12と内槽13の2槽構造としているが、必ずしも2槽にする必要はなく排水できる構造を有していれば1槽でもよい。また、洗浄装置は所定の滞留時間とすることができ、洗浄のための水を供給できる構造であれば特に限定されるものではない。   A water pipe 15 is introduced into the inner tank 13 and has a structure for supplying hot water 16 controlled to 40 to 70 ° C. from the pipe L2 to the inside. Waste is cleaned. Although not shown, the wall of the inner tub 13 has a large number of holes, and hot water 16 is supplied to the inside of the cleaning device, and after cleaning the sheet waste, sewage is discharged from the holes in the wall. It is supposed to be drained. The rotational speed of the drum in this embodiment may be appropriately selected so as to ensure the above-described residence time, and is not particularly limited, but is preferably 10 to 30 rpm. In this embodiment, the outer tank 12 and the inner tank 13 have a two-tank structure, but it is not always necessary to have two tanks. In addition, the cleaning device can have a predetermined residence time and is not particularly limited as long as it has a structure capable of supplying water for cleaning.

上記の洗浄工程により洗浄されたシート状廃棄物は、次に溶解工程に搬送される。図3は、主として溶解装置2、分離装置3、析出装置4及びそれらの間に配置された移送ベルト、配管などから構成されている。   The sheet-like waste cleaned by the above-described cleaning process is then conveyed to the dissolution process. FIG. 3 mainly includes a dissolution apparatus 2, a separation apparatus 3, a precipitation apparatus 4, a transfer belt disposed between them, a pipe, and the like.

上記の洗浄工程により洗浄されたシート状廃棄物は、水を除去した後、移送手段L3により溶解装置2に投入される。この溶解装置2は塩化ビニル系樹脂を溶解可能な溶媒を供給する配管L4、撹拌機21を備えている。そして、投入されたシート状廃棄物は溶媒と撹拌混合することにより塩化ビニル系樹脂が溶解しスラリー状の溶液22となる。この時溶解を促進するため溶解装置2はヒーターなどの加熱装置を備えているものが使用される。なお、溶液はさらにスタティックミキサーなどを用いて完全に塩化ビニル系樹脂を溶解させることもできる。   The sheet-like waste cleaned by the above-described cleaning process is removed from the water, and then charged into the dissolving device 2 by the transfer means L3. The dissolving device 2 includes a pipe L4 for supplying a solvent capable of dissolving the vinyl chloride resin and a stirrer 21. The charged sheet-like waste is stirred and mixed with a solvent to dissolve the vinyl chloride resin to form a slurry-like solution 22. At this time, in order to promote the melting, the melting device 2 having a heating device such as a heater is used. The solution can further dissolve the vinyl chloride resin completely using a static mixer or the like.

次に、上記の溶液を配管L5を介して分離装置3に導入し、不溶物を配管L6から排出し、溶解物を配管L7により析出装置4に供給する。この分離装置には例えばスクリーンなどの分離装置を用いることができる。   Next, the above solution is introduced into the separation device 3 through the pipe L5, the insoluble matter is discharged from the pipe L6, and the dissolved matter is supplied to the precipitation device 4 through the pipe L7. As this separation device, for example, a separation device such as a screen can be used.

析出装置4は溶解装置2と同様に撹拌機41及び装置内に熱水等を供給する配管L8を備えている。この熱水等を溶液42内に供給することにより、溶媒が蒸発しつつ溶媒に対する塩化ビニル系樹脂の溶解量が下がるので粒子状の沈殿物が析出する。蒸発した溶媒は所望により配管L9を介して凝縮され、溶解装置2での溶媒として再利用される。   The precipitation apparatus 4 includes a stirrer 41 and a pipe L8 for supplying hot water or the like into the apparatus as in the dissolution apparatus 2. By supplying this hot water or the like into the solution 42, the amount of the vinyl chloride resin dissolved in the solvent decreases while the solvent evaporates, so that a particulate precipitate is deposited. The evaporated solvent is condensed through the pipe L9 as desired, and is reused as the solvent in the dissolving apparatus 2.

析出した塩化ビニル系樹脂を含む溶液は配管L10を介してポンプ(図示せず)に送られ、さらに残存溶剤と塩化ビニル系樹脂に分離するための分離機43に導入される。この分離機43には例えばフィルターや遠心分離機などを用いることができる。残存溶剤は水を主成分とするものであるため配管L11を介して、所望により蒸留等を行った後、析出装置4で再利用される。   The solution containing the precipitated vinyl chloride resin is sent to a pump (not shown) via the pipe L10, and further introduced into a separator 43 for separating the residual solvent and the vinyl chloride resin. For example, a filter or a centrifuge can be used as the separator 43. Since the residual solvent is mainly composed of water, it is reused in the precipitation device 4 after performing distillation or the like as desired via the pipe L11.

そして、回収された塩化ビニル系樹脂は配管L12を介して移送され、必要により乾燥処理などを行い再生塩化ビニル系樹脂が得られる。   Then, the recovered vinyl chloride resin is transferred through the pipe L12 and, if necessary, is subjected to a drying process to obtain a regenerated vinyl chloride resin.

以上の洗浄工程、溶解工程、分離工程及び回収工程の一連の工程によりシート状廃棄物に含まれる塩化ビニル系樹脂を高純度で効率的に回収することが可能となる。   The vinyl chloride resin contained in the sheet-like waste can be efficiently recovered with high purity through a series of steps including the above-described washing step, dissolving step, separation step, and recovery step.

(実施の形態2)
本発明は実施の形態1において洗浄工程の後、溶解工程前に洗浄されたシート状廃棄物を冷却、裁断する工程を設けることも好ましい形態である。
(Embodiment 2)
In the present invention, it is also preferable to provide a step of cooling and cutting the sheet-like waste washed after the washing step and before the dissolving step in the first embodiment.

シート状廃棄物が大きな場合、溶解工程での取り扱いが煩雑で装置が大型化するため予めシート状廃棄物を裁断してさらに小片のフラフとすることが好ましい。また、後で述べる実施の形態3の造粒を行う場合にも、小片とした方が溶融が速やかとなるため好ましい。   When the sheet-like waste is large, it is preferable to cut the sheet-like waste in advance into smaller fluffs because the handling in the melting step is complicated and the apparatus becomes large. Also, when performing granulation according to Embodiment 3 to be described later, it is preferable to use small pieces because melting becomes quicker.

図4は本実施の形態のフローを示す図であり、冷却、裁断工程が洗浄工程の後に設けられている以外は、実施の形態1と同様である。このため、実施の形態1と同じ部分については説明を省略し、冷却、裁断工程について以下に述べる。   FIG. 4 is a diagram showing the flow of the present embodiment, which is the same as that of the first embodiment except that the cooling and cutting steps are provided after the cleaning step. For this reason, the description of the same parts as those of the first embodiment is omitted, and the cooling and cutting processes are described below.

洗浄工程での洗浄時にシート状廃棄物は温水で加熱され軟化しているため、小片のフラフを作製するのに直接破砕機に投入すると機械の噛み込みが生じやすい。例えば農業用ビニールシートでは30℃以上に加温されたシート状廃棄物の場合、破砕時に装置の噛み込みが確認された。このため、洗浄後に冷却を行うことにより農業用ビニールシートのような軟質の破砕しにくいシートであっても効率的に破砕することができる。この場合、洗浄後のシート状廃棄物を室温で放置することにより冷却することもできるが、処理速度の低下をもたらすため、洗浄工程後、空冷あるいは水冷により室温〜10℃程度まで冷却を行なうことが好ましい。   Since the sheet-like waste is heated and softened with warm water at the time of washing in the washing step, the machine is likely to be bitten if it is directly put into a crusher to produce a small piece of fluff. For example, in the case of a sheet-like waste heated to 30 ° C. or more in the vinyl sheet for agriculture, biting of the apparatus was confirmed at the time of crushing. For this reason, by cooling after washing, even a soft and difficult-to-crush sheet such as an agricultural vinyl sheet can be efficiently crushed. In this case, the washed sheet-like waste can be cooled by allowing it to stand at room temperature. However, in order to reduce the processing speed, it is cooled to room temperature to about 10 ° C. by air cooling or water cooling after the washing step. Is preferred.

次に、冷却されたシート状廃棄物を裁断する。裁断には通常のフラフを作製するのに用いられる破砕機を利用することができる。このフラフの大きさは50mm四方以下とすることが好ましい。なお、本裁断工程においても、シート状廃棄物に付着した土壌等の汚染物の除去を行い洗浄性を高めるために、加水を行いながら裁断を行うのが好ましい。   Next, the cooled sheet-like waste is cut. For the cutting, a crusher used to produce a normal fluff can be used. The size of the fluff is preferably 50 mm square or less. In this cutting process, it is preferable to perform cutting while adding water in order to remove contaminants such as soil adhering to the sheet-like waste and improve the washing performance.

(実施の形態3)
本発明は実施の形態1において洗浄工程の後、溶解工程前に洗浄されたシート状廃棄物を予め造粒することも好ましい形態である。このような造粒により、溶解工程ではシート状廃棄物のまま処理した場合、溶液濃度を15重量%までしか上げることができなかったが、造粒によって20重量%以上の濃度でも利用することができるようになり、さらに回収処理の効率化を図ることが可能となる。
(Embodiment 3)
In the first embodiment of the present invention, it is also preferable to granulate the sheet-like waste that has been washed after the washing step and before the dissolving step. With such granulation, the solution concentration could only be increased up to 15% by weight when treated as a sheet waste in the dissolution process, but it can be used even at a concentration of 20% by weight or more by granulation. It becomes possible to further improve the efficiency of the recovery process.

図5は本実施の形態のフローを示す図であり、シート状廃棄物を加熱溶融し、造粒する造粒工程が洗浄工程の後に設けられている以外は、実施の形態1と同様である。このため、実施の形態1と同じ部分については説明を省略し、造粒工程について以下に述べる。   FIG. 5 is a diagram showing a flow of the present embodiment, which is the same as that of the first embodiment except that a granulation step for heating and melting the sheet waste and granulating is provided after the cleaning step. . For this reason, description is abbreviate | omitted about the same part as Embodiment 1, and a granulation process is described below.

造粒工程では、まず洗浄されたシート状廃棄物を加熱溶融する。溶融温度は120〜150℃が好ましい。温度が余りに低いと溶融状態とならず均一な造粒物が得られにくくなる。一方、溶融温度が高すぎると塩化ビニル系樹脂の特質として分解が生じやすくなり、塩化水素ガスなどが発生するという問題がある。溶融時間は塩化ビニル系樹脂の種類にもよるが、1バッチ当たりの処理量が10〜30kgの場合、2〜20分とすることが好ましい。次に、溶融物を造粒するが、その際溶融状態から造粒し、さらにそれを冷却し、固化して塩化ビニル系樹脂含有造粒物とする。冷却条件としては2〜5分で60℃以下まで急冷することが好ましい。   In the granulation step, the washed sheet waste is first heated and melted. The melting temperature is preferably 120 to 150 ° C. If the temperature is too low, it will not be in a molten state and it will be difficult to obtain a uniform granulated product. On the other hand, if the melting temperature is too high, decomposition tends to occur as a characteristic of the vinyl chloride resin, and there is a problem that hydrogen chloride gas or the like is generated. Although the melting time depends on the type of the vinyl chloride resin, it is preferably 2 to 20 minutes when the processing amount per batch is 10 to 30 kg. Next, the melt is granulated. At that time, the melt is granulated from the melted state, further cooled and solidified to obtain a vinyl chloride resin-containing granulated product. As cooling conditions, it is preferable to rapidly cool to 60 ° C. or less in 2 to 5 minutes.

本発明のシート状廃棄物を溶融し、造粒する装置としては合成樹脂を通常製造する場合に用いられるヘンシェルミキサー、アドオンミキサー等を用いることができる。このような装置を用いると、同一ミキサー内で溶融及び造粒が可能となる。そして、造粒後にクーラーミキサーなどの冷却装置に供給し、冷却、固化することにより塩化ビニル系樹脂含有造粒物を得ることができる。   As an apparatus for melting and granulating the sheet-like waste of the present invention, a Henschel mixer, an add-on mixer, or the like, which is used when a synthetic resin is usually produced, can be used. When such an apparatus is used, melting and granulation can be performed in the same mixer. And after granulation, it supplies to cooling devices, such as a cooler mixer, and a vinyl chloride resin containing granulated material can be obtained by cooling and solidifying.

本発明の塩化ビニル系樹脂含有造粒物は粒径が10mm以下で、みかけ比重が0.1g/cm以上、好ましくは0.3〜0.5g/cmとすることが望ましい。上記みかけ比重はJIS K 6720−2に記載の測定方法に従って測定したものである。このようなみかけ比重の造粒物とすることにより溶解工程において溶媒への溶解速度がシート状の場合と比較して遜色ない速度で溶解し、かつ、溶液濃度を20重量%以上とすることができる。従って、シート状の場合と比較して回収処理全体の処理効率を格段に上げることができる。なお、みかけ比重をさらに高くすれば溶解工程での溶液濃度を高めることができるが、造粒物を完全に溶解させるために長時間を要する傾向にある。 Vinyl chloride resin containing granulated product of the present invention is a particle diameter at 10mm or less, an apparent specific gravity of 0.1 g / cm 3 or more, preferably it is desirable that the 0.3 to 0.5 g / cm 3. The apparent specific gravity is measured according to the measuring method described in JIS K 6720-2. By making such a granulated product with an apparent specific gravity, the dissolution rate in the solvent in the dissolution step can be dissolved at a speed comparable to that in the sheet form, and the solution concentration can be 20% by weight or more. it can. Therefore, the processing efficiency of the entire recovery process can be significantly increased compared to the case of a sheet form. If the apparent specific gravity is further increased, the solution concentration in the dissolving step can be increased, but it tends to require a long time to completely dissolve the granulated product.

(実施の形態4)
本発明は実施の形態3において、洗浄工程後、造粒工程前に脱水工程を設けることも好ましい形態である。このような脱水工程を造粒工程前に設けることにより、造粒のための加熱溶融を効率的に行うことができる。
(Embodiment 4)
In the third embodiment, it is also preferable to provide a dehydration step after the washing step and before the granulation step. By providing such a dehydration step before the granulation step, heating and melting for granulation can be performed efficiently.

図6は本実施の形態のフローを示す図であり、洗浄工程後に脱水工程、造粒工程が設けられている以外は、実施の形態1と同様である。このため、実施の形態1及び3と同じ部分については説明を省略し、脱水工程について以下に述べる。   FIG. 6 is a diagram showing a flow of the present embodiment, which is the same as that of the first embodiment except that a dehydration process and a granulation process are provided after the cleaning process. For this reason, the description of the same parts as those in Embodiments 1 and 3 is omitted, and the dehydration process will be described below.

脱水工程では、まず洗浄されたシート状廃棄物に付着した水を脱水機により脱水を行う。この際、脱水洗浄と脱水の2工程を行うことが好ましい。脱水洗浄を行うことにより、シート状廃棄物の付着物をさらに低減することができる。この洗浄には常温の水を用いることができる。脱水洗浄後の脱水工程では、例えば遠心脱水などにより水を除去することができる。このようにして得られるシート状廃棄物の水の量は、造粒工程での効率化を図るため、シート状廃棄物1t当たり0.1t以下とすることを目安とする。   In the dehydration process, first, water adhering to the washed sheet-like waste is dehydrated by a dehydrator. At this time, it is preferable to perform two steps of dehydration washing and dehydration. By performing dehydration washing, the deposits of sheet-like waste can be further reduced. Normal temperature water can be used for this cleaning. In the dehydration step after dehydration washing, water can be removed by, for example, centrifugal dehydration. The amount of water in the sheet-like waste thus obtained is set to 0.1 t or less per 1 t of the sheet-like waste in order to improve efficiency in the granulation process.

(実施の形態5)
本発明は実施の形態4において、実施の形態2の冷却、裁断工程を洗浄工程後、脱水工程前に行うことも好ましい形態である。このような冷却、裁断工程を経て作製されるフラフは脱水が容易であるとともに、造粒工程時の加熱溶融も容易に行うことができるため、さらに処理効率を向上することができる。そして、造粒工程により造粒された塩化ビニル系樹脂造粒物は溶解工程での溶媒への溶解速度がシート状やそれを小片に破砕したフラフと同程度に速く、また溶液濃度を20重量%以上まで向上することができるので、処理効率を格段に向上することができる。
(Embodiment 5)
In the fourth embodiment, the cooling and cutting process of the second embodiment is preferably performed after the cleaning process and before the dehydration process in the fourth embodiment. The fluff produced through such cooling and cutting steps can be easily dehydrated and can be easily heated and melted during the granulation step, so that the processing efficiency can be further improved. And the vinyl chloride resin granulated product granulated by the granulation process has a dissolution rate in the solvent in the dissolution process as fast as a sheet or a fluff obtained by crushing it into small pieces, and the solution concentration is 20 weight. %, The processing efficiency can be remarkably improved.

図7は本実施の形態のフローを示す図であり、洗浄工程後に冷却、裁断工程、脱水工程、造粒工程が設けられている以外は、実施の形態1と同様であり、各工程で使用される条件は上記の実施の形態1〜4と同様である。   FIG. 7 is a diagram showing a flow of the present embodiment, which is the same as that of the first embodiment except that a cooling, a cutting process, a dehydration process, and a granulation process are provided after the cleaning process. The conditions to be performed are the same as those in the first to fourth embodiments.

(実施の形態6)
本発明は実施の形態1において、回収工程で塩化ビニル系樹脂含有溶液に塩化ビニル系樹脂の非溶媒を接触させて溶液中で塩化ビニル系樹脂を析出させ、析出した塩化ビニル系樹脂を分離して回収する方法を用いることも好ましい形態である。実施の形態1では熱水等による回収工程を用いる場合については説明したが、このような回収工程によっても塩化ビニル系樹脂を高純度で回収することができる。
(Embodiment 6)
In the first embodiment of the present invention, the vinyl chloride resin-containing solution is brought into contact with the vinyl chloride resin-containing solution in the recovery step to precipitate the vinyl chloride resin in the solution, and the precipitated vinyl chloride resin is separated. It is also a preferred form to use a method of recovering in this manner. In the first embodiment, the case of using a recovery process using hot water or the like has been described, but the vinyl chloride resin can also be recovered with high purity by such a recovery process.

図8は本実施の形態のフローを示す図であり、回収工程で熱水等の代わりに比較的温度の低い、例えば常温の非溶媒を用いて塩化ビニル系樹脂を沈殿させる以外は、実施の形態1と同様である。このため、実施の形態1と同じ部分については説明を省略し、回収工程について以下に述べる。   FIG. 8 is a diagram showing the flow of the present embodiment. In the recovery step, except that the vinyl chloride resin is precipitated using a non-solvent having a relatively low temperature, for example, room temperature, instead of hot water or the like. This is the same as the first embodiment. For this reason, the description of the same parts as those in the first embodiment is omitted, and the recovery process will be described below.

本実施の形態の回収工程では塩化ビニル系樹脂を溶解しない非溶媒として、水や、メタノール、エタノール、プロパノール等の低級アルコールを用いることができ、これらの中でも取り扱いが容易であり、かつ、コストの面から水が好ましい。なお、この実施の形態において塩化ビニル系樹脂を溶解するために用いられる溶媒としては、他の実施の形態と同様の溶媒を利用できる。   In the recovery step of the present embodiment, water or a lower alcohol such as methanol, ethanol, propanol or the like can be used as a non-solvent that does not dissolve the vinyl chloride resin, and among these, handling is easy and cost is low. From the viewpoint of water, water is preferable. In this embodiment, as the solvent used for dissolving the vinyl chloride resin, the same solvent as in the other embodiments can be used.

このような非溶媒を不溶物を分離した塩化ビニル系樹脂含有溶液中に供給することにより溶媒に対する塩化ビニル系樹脂の溶解度が低下し、塊状の塩化ビニル系樹脂を沈殿物として析出させることができる。極力小さな塊状の塩化ビニル系樹脂を得たい場合は非溶媒の添加を撹拌下で行うことが好ましい。また、非溶媒を供給する際の溶液の温度としては、特に限定されず、常温で添加しても良い。   By supplying such a non-solvent into the vinyl chloride resin-containing solution from which the insoluble matter has been separated, the solubility of the vinyl chloride resin in the solvent decreases, and the bulk vinyl chloride resin can be deposited as a precipitate. . When it is desired to obtain a lumped vinyl chloride resin as small as possible, it is preferable to add the non-solvent with stirring. Moreover, it does not specifically limit as a temperature of the solution at the time of supplying a non-solvent, You may add at normal temperature.

本実施の形態では、実施の形態1と同様に沈澱物を分離し塊状の塩化ビニル系樹脂を含む溶液から残存溶剤を除去することにより塩化ビニル系樹脂を回収することができる。   In the present embodiment, the vinyl chloride resin can be recovered by separating the precipitate and removing the residual solvent from the solution containing the bulk vinyl chloride resin, as in the first embodiment.

本実施の形態に用いられる回収処理設備としては、実施の形態1と同様の設備を使用することができるが、析出装置では溶媒を揮発しないため得られる塩化ビニル系樹脂を固液分離後、回収した塩化ビニル系樹脂を加熱することにより、塩化ビニル系樹脂中に残存している溶媒を蒸発除去させる装置を別途設ける必要がある。その際に、混練を行い、ペレット化を行っても良い。   As the recovery processing equipment used in the present embodiment, the same equipment as in the first embodiment can be used. However, since the solvent is not volatilized in the precipitation apparatus, the obtained vinyl chloride resin is recovered after solid-liquid separation. It is necessary to separately provide a device for evaporating and removing the solvent remaining in the vinyl chloride resin by heating the vinyl chloride resin. In that case, you may knead | mix and pelletize.

(その他の実施の形態)
上記で説明された各実施の形態はいずれも一例であり、上記実施の形態で説明されていない各形態を組み合わせた形態とすることもできる。また、本発明は以下の工程をさらに採用することもできる。
(1)磁気処理工程
本発明では溶解工程前に磁気処理工程を設けることも好ましい形態である。例えば、洗浄工程前に磁石などにより磁気処理工程を行い、シート状廃棄物から金属類を除去することができる。
(2)振動スクリーン工程
本発明ではさらに溶解工程前に振動スクリーン工程を設けることも好ましい形態である。例えば、洗浄工程前に振動スクリーンでシート状廃棄物を振動させて付着物を除去することもできる。
(3)前洗浄工程
本発明ではまた、上記洗浄工程の前に常温の水でシート状廃棄物を予め洗浄することも好ましい形態である。例えば、付着力の弱い土壌物を除去するため常温の水で予め洗浄することもできる。
(Other embodiments)
Each of the embodiments described above is an example, and the embodiments not described in the above embodiments may be combined. In addition, the present invention can further employ the following steps.
(1) Magnetic processing step In the present invention, it is also a preferred embodiment to provide a magnetic processing step before the melting step. For example, it is possible to remove the metals from the sheet waste by performing a magnetic treatment step with a magnet or the like before the cleaning step.
(2) Vibrating screen process In the present invention, it is also a preferred embodiment to provide a vibrating screen process before the melting process. For example, the adhering material can be removed by vibrating the sheet-like waste with a vibrating screen before the cleaning process.
(3) Pre-cleaning step In the present invention, it is also a preferred embodiment that the sheet-like waste is pre-cleaned with water at room temperature before the cleaning step. For example, in order to remove soil substances having weak adhesion, it can be washed in advance with water at room temperature.

以下本発明を実施例によってさらに詳細に説明するが、下記実施例は単なる一例であり本発明を限定する性質のものでなく、前・後記の趣旨に基づき設計変更することはいずれも本発明の技術的範囲に含まれるものである。   Hereinafter, the present invention will be described in more detail by way of examples. However, the following examples are merely examples and are not intended to limit the present invention, and any design changes based on the gist of the present invention will be described below. It is included in the technical scope.

実施の形態5の処理工程を利用し、約100mm四方の大きさに裁断し、予備処理して予め付着力の弱い土壌物を除去した農業用ビニールシートの廃棄物(土壌物の付着量:廃棄物1t当たり約0.055t)から塩化ビニル樹脂(重合度:1,300)の回収処理を行った。各工程の処理条件は以下の通りである。   Agricultural vinyl sheet waste that has been cut into a size of about 100 mm square using the treatment process of the fifth embodiment and pre-treated to remove soil matter with weak adhesion in advance (adhesion amount of soil matter: disposal The vinyl chloride resin (degree of polymerization: 1,300) was recovered from about 0.055 t per 1 t of the product. The processing conditions for each step are as follows.

(洗浄工程)
洗浄水の温度を表1に示す温度にそれぞれ変更し、滞留時間30秒、内槽の回転速度20rpm、水を0.3t/廃棄物1tの量で供給しながら洗浄を行なった。
(Washing process)
The temperature of the washing water was changed to the temperatures shown in Table 1, respectively, and washing was performed while the residence time was 30 seconds, the inner tank rotation speed was 20 rpm, and water was supplied in an amount of 0.3 t / waste 1 t.

(冷却、裁断工程及び脱水工程)
洗浄工程で加温された各シート状廃棄物を室温まで冷却し、破砕機を用いて約30mm四方のフラフを作製し、常温の水を0.3t/廃棄物1tの量で供給しながら脱水洗浄を行い、さらに遠心脱水を行って水を除去した。
(Cooling, cutting process and dehydration process)
Each sheet-like waste heated in the washing process is cooled to room temperature, and a crusher is used to produce a 30 mm square fluff, which is dehydrated while supplying room-temperature water in an amount of 0.3 t / waste 1 t. Washing was performed, and further water was removed by centrifugal dehydration.

(造粒工程)
次に、得られたフラフをヘンシェルミキサーに供給し、130〜140℃に加熱溶融して5〜10分撹拌した後造粒し、これをクーラーミキサーに供給して2分で50〜60℃まで冷却しながら塩化ビニル樹脂含有造粒物(粒径3.0mm、みかけ比重:0.3〜0.5g/cm)を作製した。
(Granulation process)
Next, the obtained fluff is supplied to a Henschel mixer, heated and melted to 130 to 140 ° C., stirred for 5 to 10 minutes, granulated, and then supplied to a cooler mixer to 50 to 60 ° C. in 2 minutes. While cooling, a vinyl chloride resin-containing granulated product (particle size: 3.0 mm, apparent specific gravity: 0.3 to 0.5 g / cm 3 ) was produced.

(溶解工程)
上記で作製した塩化ビニル樹脂含有造粒物を溶解装置に投入し、溶液濃度が20重量%となるスラリー状の溶液を作製した。溶媒にはメチルエチルケトン(沸点:79.6℃)を用い、溶解は装置を70℃、0.5時間加熱撹拌して行った。
(Dissolution process)
The granulated product containing the vinyl chloride resin prepared above was put into a dissolution apparatus to prepare a slurry solution having a solution concentration of 20% by weight. Methyl ethyl ketone (boiling point: 79.6 ° C.) was used as the solvent, and dissolution was performed by heating and stirring the apparatus at 70 ° C. for 0.5 hours.

(分離工程)
上記溶液をポンプで送りながら、100μmのナイロン製メッシュフィルタを使用して不溶物を除去した。
(Separation process)
While the solution was being pumped, insoluble matter was removed using a 100 μm nylon mesh filter.

(回収工程)
上記分離工程から得られた溶液をポンプで連続的に析出装置に送り、析出装置内に投入した。溶液を50〜60℃に加温しながらスチーム(100℃)を溶液中に供給し、メチルエチルケトンを蒸発させながら塩化ビニル樹脂を沈殿させた。得られた粒子状の沈殿物を含む溶液をさらに残存溶剤を除去するため遠心分離を行ない、乾燥させて塩化ビニル樹脂を回収した。
(Recovery process)
The solution obtained from the separation step was continuously sent to the precipitation apparatus by a pump and charged into the precipitation apparatus. Steam (100 ° C.) was supplied into the solution while heating the solution to 50 to 60 ° C., and vinyl chloride resin was precipitated while evaporating methyl ethyl ketone. The resulting solution containing the particulate precipitate was further centrifuged to remove the residual solvent, and dried to recover the vinyl chloride resin.

表1に洗浄工程における温度ごとの付着物の除去量(洗浄工程前のシート状廃棄物に含まれる付着物の重量を基準とし、洗浄工程後の付着物の重量と比較したときの、その減少割合)、回収された塩化ビニル樹脂に含まれていた不純物量をまとめて示す。なお、本実施例においては、不純物量は回収した塩化ビニル樹脂を一旦溶剤に溶解させた後、さらに遠心分離法により分離し測定を行ったものである。   Table 1 shows the amount of deposit removal at each temperature in the cleaning process (based on the weight of the deposit included in the sheet waste before the cleaning process, and the reduction when compared with the weight of the deposit after the cleaning process) Ratio) and the amount of impurities contained in the recovered vinyl chloride resin. In this example, the amount of impurities is measured by dissolving the recovered vinyl chloride resin once in a solvent and further separating it by a centrifugal separation method.

Figure 2006274101
Figure 2006274101

上記表1に示すように、洗浄工程で40〜70℃、特に40〜60℃の温水で洗浄したシート状廃棄物は付着物が大量に除去されていることが分かる。また、そのシート状廃棄物を造粒して造粒物とし、これを溶解し、析出を行って回収された塩化ビニル樹脂は土壌物による着色の弱い不純物量が0.4重量%以下の純度の高い塩化ビニル樹脂が得られている。   As shown in Table 1 above, it can be seen that a large amount of deposits have been removed from the sheet-like waste washed with warm water at 40 to 70 ° C., particularly 40 to 60 ° C. in the washing step. In addition, the vinyl chloride resin recovered by granulating the sheet-like waste, dissolving it, and precipitating it has a purity of 0.4% by weight or less of impurities that are weakly colored by soil. A high vinyl chloride resin is obtained.

参考として予備処理だけを行い、洗浄工程により付着物を除去していないシート状廃棄物のまま溶解工程に供した場合、溶液中の汚れが激しく、またシート状廃棄物を15重量%以上溶媒に添加すると溶液中にシート状廃棄物が固形物として残存した。   For reference, only pre-treatment is performed, and if the sheet-like waste from which the deposits have not been removed by the washing step is used for the dissolution step, the solution is heavily soiled, and the sheet-like waste is used in a solvent of 15% by weight or more. When added, sheet waste remained as a solid in the solution.

以上説明したように、本発明の洗浄工程あるいはそれととともに冷却、裁断工程、脱水工程及び造粒工程を行うことにより、溶解によりシート状廃棄物から塩化ビニル系樹脂を回収する場合に効率的な処理が可能となり、また付着物の量を極めて低減することができる。従って、本発明をシート状廃棄物からの塩化ビニル系樹脂の回収に利用すれば処理効率の向上が図れるとともに、高純度の塩化ビニル系樹脂を回収することができる。   As described above, the cleaning process of the present invention or the cooling process, the cutting process, the dehydration process and the granulation process together with the cleaning process of the present invention enables efficient treatment when recovering vinyl chloride resin from sheet-like waste by dissolution. And the amount of deposits can be greatly reduced. Therefore, if the present invention is used for recovery of vinyl chloride resin from sheet-like waste, it is possible to improve the processing efficiency and recover high purity vinyl chloride resin.

本発明の実施の形態1の各工程を示すフロー図である。It is a flowchart which shows each process of Embodiment 1 of this invention. 本発明の洗浄工程に使用される洗浄装置の一例を示す概略図である。It is the schematic which shows an example of the washing | cleaning apparatus used for the washing | cleaning process of this invention. 本発明の溶解工程、分離工程及び回収工程の一構成例を示す概略図である。It is the schematic which shows one structural example of the melt | dissolution process of this invention, a isolation | separation process, and a collection | recovery process. 本発明の実施の形態2の各工程を示すフロー図である。It is a flowchart which shows each process of Embodiment 2 of this invention. 本発明の実施の形態3の各工程を示すフロー図である。It is a flowchart which shows each process of Embodiment 3 of this invention. 本発明の実施の形態4の各工程を示すフロー図である。It is a flowchart which shows each process of Embodiment 4 of this invention. 本発明の実施の形態5の各工程を示すフロー図である。It is a flowchart which shows each process of Embodiment 5 of this invention. 本発明の実施の形態6の各工程を示すフロー図である。It is a flowchart which shows each process of Embodiment 6 of this invention.

符号の説明Explanation of symbols

1 洗浄装置
2 溶解装置
3 分離装置
4 析出装置
21 41 撹拌機
22 42 溶液
DESCRIPTION OF SYMBOLS 1 Cleaning apparatus 2 Dissolving apparatus 3 Separating apparatus 4 Deposition apparatus 21 41 Stirrer 22 42 Solution

Claims (7)

塩化ビニル系樹脂を含有するシート状廃棄物から塩化ビニル系樹脂を回収する方法であって、
前記シート状廃棄物を洗浄槽内に投入し温度40〜70℃の水を供給して洗浄する洗浄工程と、
前記洗浄されたシート状廃棄物を前記塩化ビニル系樹脂が溶解可能な溶媒に溶解し、塩化ビニル系樹脂含有溶液を得る溶解工程と、
前記塩化ビニル系樹脂含有溶液から不溶物を分離する分離工程と、
前記不溶物を除去した溶液から前記塩化ビニル系樹脂を回収する回収工程と、
を備える塩化ビニル系樹脂の回収方法。
A method of recovering vinyl chloride resin from sheet-like waste containing vinyl chloride resin,
A washing step in which the sheet-like waste is put into a washing tank and water is supplied at a temperature of 40 to 70 ° C. for washing;
Dissolving the washed sheet waste in a solvent in which the vinyl chloride resin can be dissolved to obtain a vinyl chloride resin-containing solution; and
A separation step of separating insoluble matter from the vinyl chloride resin-containing solution;
A recovery step of recovering the vinyl chloride resin from the solution from which the insoluble matter has been removed;
A method for recovering a vinyl chloride resin.
前記洗浄工程後、溶解工程の前に、前記洗浄されたシート状廃棄物を冷却し、裁断する工程を備える請求項1に記載の塩化ビニル系樹脂の回収方法。   The method for recovering a vinyl chloride resin according to claim 1, further comprising a step of cooling and cutting the washed sheet-like waste after the washing step and before the dissolving step. 前記洗浄工程後、溶解工程の前に、前記洗浄されたシート状廃棄物を加熱溶融した後、造粒して塩化ビニル系樹脂含有造粒物とする造粒工程を備える請求項1に記載の塩化ビニル系樹脂の回収方法。   2. The method according to claim 1, further comprising a granulation step after the washing step and before the dissolution step, after the washed sheet-like waste is heated and melted, and granulated to obtain a vinyl chloride resin-containing granulated product. Collection method of vinyl chloride resin. 前記洗浄工程後、造粒工程前に、脱水工程を備える請求項3に記載の塩化ビニル系樹脂の回収方法。   The method for recovering a vinyl chloride resin according to claim 3, further comprising a dehydration step after the washing step and before the granulation step. 前記回収工程が、前記不溶物を除去した溶液に熱水及び/またはスチームを接触させて塩化ビニル系樹脂を析出する工程を備える請求項1〜4のいずれかに記載の塩化ビニル系樹脂の回収方法。   The recovery of the vinyl chloride resin according to any one of claims 1 to 4, wherein the recovery step includes a step of bringing a solution from which the insoluble matter has been removed into contact with hot water and / or steam to precipitate a vinyl chloride resin. Method. 前記回収工程が、前記不溶物を除去した溶液に塩化ビニル系樹脂の非溶媒を添加して塩化ビニル系樹脂を析出する工程を備える請求項1〜4のいずれか1項に記載の塩化ビニル系樹脂の回収方法。   The vinyl chloride system according to any one of claims 1 to 4, wherein the recovery step includes a step of adding a non-solvent of a vinyl chloride resin to the solution from which the insoluble matter has been removed to precipitate a vinyl chloride resin. Resin recovery method. 請求項1〜6のいずれか1項に記載の塩化ビニル系樹脂の回収方法を備えることを特徴とする塩化ビニル系樹脂回収処理設備。   A vinyl chloride resin recovery treatment facility comprising the vinyl chloride resin recovery method according to any one of claims 1 to 6.
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009144031A (en) * 2007-12-13 2009-07-02 Kobelco Eco-Solutions Co Ltd Method of recovering vinyl chloride based resin and recovery treatment apparatus
CN101367957B (en) * 2008-09-28 2011-09-21 浙江大学 Method for recycling polyvinyl chloride or polyvinylidene chloride plastic

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2009144031A (en) * 2007-12-13 2009-07-02 Kobelco Eco-Solutions Co Ltd Method of recovering vinyl chloride based resin and recovery treatment apparatus
CN101367957B (en) * 2008-09-28 2011-09-21 浙江大学 Method for recycling polyvinyl chloride or polyvinylidene chloride plastic

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