JP2007224082A - Method for recovering inorganic filler and inorganic filler - Google Patents

Method for recovering inorganic filler and inorganic filler Download PDF

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JP2007224082A
JP2007224082A JP2006043815A JP2006043815A JP2007224082A JP 2007224082 A JP2007224082 A JP 2007224082A JP 2006043815 A JP2006043815 A JP 2006043815A JP 2006043815 A JP2006043815 A JP 2006043815A JP 2007224082 A JP2007224082 A JP 2007224082A
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inorganic filler
liquid
recovering
decomposition
disk
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JP4736841B2 (en
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Kenji Oka
健司 岡
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Panasonic Electric Works Co Ltd
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Matsushita Electric Works Ltd
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    • 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
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for recovering an inorganic filler, by which the inorganic filler can be dried and recovered without wet-crushing the inorganic filler in a crushing liquid, while controlling the particle diameter of the inorganic filler. <P>SOLUTION: This method for recovering the inorganic filler is characterized by rotating a disk-like article having a plurality of openings 13 in the side surface in the circumferential direction, supplying a liquid containing the inorganic filler into a groove 12 communicated with the openings 13, gushing out the liquid from the openings 13, contacting the gushed liquid with hot air, and evaporating the liquid to separate and recover the inorganic filler. <P>COPYRIGHT: (C)2007,JPO&INPIT

Description

本発明は、無機充填材を含有するプラスチックを亜臨界水で分解することにより得られた分解物から無機充填材を回収する無機充填材の回収方法に関する。   The present invention relates to an inorganic filler recovery method for recovering an inorganic filler from a decomposition product obtained by decomposing a plastic containing an inorganic filler with subcritical water.

プラスチックは、軽量、高強度であり、防錆性、耐食性、電気絶縁性、成型性、着色性等に優れ、さらに大量生産が可能であるという利点を有することから、浴室材、自動車、航空機等の用途に多用されている。プラスチックの使用量の増加に伴い、使用済みのプラスチックの廃棄量も増加する傾向にあり、使用済みの廃プラスチックをリサイクルして環境への負荷を軽減するために、盛んに研究開発が進められている。   Plastics are lightweight, high-strength, have excellent rust prevention, corrosion resistance, electrical insulation, moldability, colorability, etc., and have the advantage of being capable of mass production. It is widely used for applications. As the amount of plastic used increases, the amount of used plastic discarded also tends to increase. In order to recycle used plastic waste and reduce the burden on the environment, research and development has been actively promoted. Yes.

プラスチックは、熱硬化性樹脂と熱可塑性樹脂とに大別されるが、樹脂単独での使用に加えて、強度が必要な場合には、基材となるエポキシ樹脂又はフェノール樹脂等にガラス繊維やカーボン繊維等の強化材を含めた繊維強化プラスチックス(FRP:Fiber Reinforced Plastics)が用いられている。   Plastics are broadly classified into thermosetting resins and thermoplastic resins. In addition to the use of the resin alone, if strength is required, glass fiber or Fiber reinforced plastics (FRP: Fiber Reinforced Plastics) including reinforcing materials such as carbon fibers are used.

熱可塑性樹脂は、加熱溶融することで比較的容易に処理されるが、熱硬化性樹脂あるいはFRP等のプラスチックは加熱溶融による処理が困難である。このため、廃プラスチックを粉砕した後、埋め立てて処理をしているが、将来、埋立地の不足が予想されている。また、廃プラスチックを燃料として利用するサーマルリサイクルも注目されているが、廃プラスチックの燃焼が不完全になると有害物質(例えば、ダイオキシン)が発生する。このため、廃プラスチックを処理する方法を確立することが急務となっている。   Thermoplastic resins are relatively easily processed by heating and melting, but thermosetting resins or plastics such as FRP are difficult to process by heating and melting. For this reason, waste plastic is crushed and then landfilled, but in the future, a shortage of landfill is expected. In addition, thermal recycling using waste plastic as fuel has attracted attention. However, when waste plastic is incompletely burned, harmful substances (for example, dioxins) are generated. For this reason, there is an urgent need to establish a method for treating waste plastic.

このような背景から、FRP等に代表されるプラスチックを超臨界流体又は亜臨界流体で分解することによって、プラスチックの樹脂成分を樹脂のモノマー又はオリゴマーに分解し、炭酸カルシウム,水酸化アルミニウム,及びガラス繊維の無機物を回収,再利用する方法が提案されている(特許文献1参照)。
特開平11−140224号公報
From such a background, by decomposing plastics such as FRP with a supercritical fluid or subcritical fluid, the resin component of the plastic is decomposed into resin monomers or oligomers, and calcium carbonate, aluminum hydroxide, and glass. A method for recovering and reusing inorganic fibers has been proposed (see Patent Document 1).
JP-A-11-140224

しかしながら、上述の方法により回収された無機物は、残渣として各成分が各種の割合で混合した状態で存在しており、また臨界流体によって表面状態が変化している。従って、無機物を充填材として再利用する場合には、無機物を樹脂に混合させるために乾燥及び粉砕処理を行う必要がある。また特に、再成形後の強度低下を防止するために無機充填材の粒度を小さくしなければならない場合があるが、このような作業を単純に行うと、臨界流体分解後の分解液を濾過し、残渣として得た無機物を乾燥し、乾燥後の無機物の固形物を粉砕,分級して所望の粒径の無機充填材とする必要がある。このため、調整する無機充填材の粒径毎に工程条件を設定しなければならず、無機充填材の回収率が低下してしまう。   However, the inorganic substance recovered by the above-described method exists as a residue in which various components are mixed in various proportions, and the surface state is changed by the critical fluid. Therefore, when the inorganic material is reused as the filler, it is necessary to perform drying and pulverization treatment in order to mix the inorganic material with the resin. In particular, it may be necessary to reduce the particle size of the inorganic filler in order to prevent a decrease in strength after reshaping. However, if this operation is simply performed, the decomposition solution after the critical fluid decomposition is filtered. It is necessary to dry the inorganic substance obtained as a residue and to pulverize and classify the inorganic solid substance after drying to obtain an inorganic filler having a desired particle size. For this reason, process conditions must be set for each particle size of the inorganic filler to be adjusted, and the recovery rate of the inorganic filler is reduced.

本発明は、上記課題を解決するためになされたものであり、その目的は、分解液中の無機物を湿式粉砕することなく無機物の粒径を調整しつつ無機充填材を乾燥,回収することが可能な無機充填材の回収方法を提供することにある。   The present invention has been made to solve the above-mentioned problems, and its purpose is to dry and recover the inorganic filler while adjusting the particle size of the inorganic substance without wet-grinding the inorganic substance in the decomposition solution. It is to provide a method for recovering a possible inorganic filler.

上記課題を解決するために、本発明に係る無機充填材の回収方法は、周方向に沿って複数の開口部を側面に有する円盤状物を回転させ、円盤状物に設けられ、開口部に連通する溝に無機充填材を含有する液体を供給し、液体を円盤状物の前記開口部から噴出させ、噴出した液体を熱風に接触させ、液体を蒸発させることにより無機充填材を分離,回収する。なお、円盤状物の回転速度は5000[rpm]以上50000[rpm]以下の範囲内にあることが望ましい。また、液体が噴出,乾燥される領域の雰囲気温度は100[℃]以上300[℃]以下の温度範囲内に調整されていることが望ましい。   In order to solve the above problems, the method for recovering an inorganic filler according to the present invention rotates a disk-shaped object having a plurality of openings on its side surface along the circumferential direction, and is provided on the disk-shaped object. A liquid containing an inorganic filler is supplied to the communicating groove, the liquid is ejected from the opening of the disk-shaped object, the ejected liquid is brought into contact with hot air, and the liquid is evaporated to separate and collect the inorganic filler. To do. In addition, it is desirable that the rotational speed of the disk-shaped object is in the range of 5000 [rpm] to 50000 [rpm]. In addition, it is desirable that the atmospheric temperature in the region where the liquid is ejected and dried is adjusted within a temperature range of 100 [° C.] to 300 [° C.].

本発明に係る無機充填材の回収方法によれば、分解液中の無機物を湿式粉砕することなく無機物の粒径を調整しつつ無機充填材を乾燥,回収することができる。   According to the method for recovering an inorganic filler according to the present invention, the inorganic filler can be dried and recovered while adjusting the particle size of the inorganic substance without wet-grinding the inorganic substance in the decomposition solution.

〔臨界流体分解工程〕
臨界流体分解工程において、耐熱,耐圧性がある容器に容器の大きさに合わせて切断又は粗粉砕したプラスチックと臨界流体を入れ、加熱,加圧することにより、プラスチックを樹脂のモノマー又はオリゴマーと,無機充填材の炭酸カルシウム,水酸化アルミニウム,ガラス繊維に分解する。なお、プラスチックとしては、熱硬化性樹脂及び熱可塑性樹脂のいずれかの樹脂を用いたプラスチックも対象とすることができる。
[Critical fluid decomposition process]
In the critical fluid decomposition process, a plastic that has been cut or coarsely pulverized according to the size of the container and a critical fluid are placed in a heat-resistant and pressure-resistant container, and heated and pressurized to make the plastic a monomer or oligomer of resin and inorganic. Decomposes into filler calcium carbonate, aluminum hydroxide and glass fiber. In addition, as a plastic, the plastic using any resin of a thermosetting resin and a thermoplastic resin can also be made into object.

具体的には、熱硬化性樹脂としては、不飽和ポリエステル樹脂,アクリル樹脂,エポキシ樹脂,ポリウレタン樹脂,アミノ樹脂,フェノール樹脂等を例示することができる。また、熱可塑性樹脂としては、塩ビ樹脂,ポリエチレン樹脂,ポリスチレン樹脂,ポリプロピレン樹脂,ポリブタジエン樹脂,アルキド樹脂,ポリカーボネート樹脂,ポリアミド樹脂等を例示することができる。   Specifically, examples of the thermosetting resin include unsaturated polyester resins, acrylic resins, epoxy resins, polyurethane resins, amino resins, and phenol resins. Examples of the thermoplastic resin include vinyl chloride resin, polyethylene resin, polystyrene resin, polypropylene resin, polybutadiene resin, alkyd resin, polycarbonate resin, polyamide resin, and the like.

また、臨界流体としては、水,一価アルコール,多価アルコール等やこれらの混合物を用いることができるが、これらのものに限定されることはない。また、臨界流体として水を用いる場合には、予め脱塩したものを用いることが好ましく、さらには、分解を促進させるためにアルカリ金属の水酸化物の水溶液を臨界流体として用いてもよい。また、臨界流体の混合量が、プラスチック100重量部に対して100重量部未満であるとプラスチックを安定して分解することができず、逆に500重量部以上であると分解後の流体の廃液処理コストが高くなるので、プラスチック100重量部に対する臨界流体の配合量は、プラスチック100重量部に対し100〜500重量部の範囲内とすることが好ましい。   As the critical fluid, water, monohydric alcohol, polyhydric alcohol, and the like, or a mixture thereof can be used, but are not limited to these. In addition, when water is used as the critical fluid, it is preferable to use a salt that has been desalted in advance, and an alkali metal hydroxide aqueous solution may be used as the critical fluid in order to promote decomposition. Further, if the mixing amount of the critical fluid is less than 100 parts by weight with respect to 100 parts by weight of the plastic, the plastic cannot be stably decomposed, and conversely if it is 500 parts by weight or more, the waste fluid of the fluid after the decomposition Since processing cost becomes high, it is preferable to make the compounding quantity of the critical fluid with respect to 100 weight part of plastics into the range of 100-500 weight part with respect to 100 weight part of plastic.

また、分解温度が180[℃]未満であると分解に長い時間を要し、逆に270[℃]以上になると熱分解の影響が大きくなり、樹脂をモノマー又はオリゴマーとして回収することができなくなる恐れがあるので、分解温度は180〜270[℃]の温度範囲内にすることが望ましい。また、分解時間及び分解圧力は、特に限定されることはないが、上記分解温度範囲内においてはそれぞれ、1〜4[時間],2〜15[MPa]の範囲内にすることが望ましい。また、アルカリ金属の水酸化物の水溶液を臨界水として用いる場合には、アルカリ金属の水酸化物をプラスチック100重量部に対して20〜100重量部の範囲内で添加することが好ましい。   In addition, if the decomposition temperature is less than 180 [° C.], it takes a long time to decompose, and conversely if it exceeds 270 [° C.], the influence of thermal decomposition increases and the resin cannot be recovered as a monomer or oligomer. Since there exists a possibility, it is desirable to make decomposition temperature into the temperature range of 180-270 [degreeC]. Further, the decomposition time and the decomposition pressure are not particularly limited, but it is desirable to set them within the range of 1 to 4 [hours] and 2 to 15 [MPa], respectively, within the above decomposition temperature range. Moreover, when using the aqueous solution of an alkali metal hydroxide as critical water, it is preferable to add the alkali metal hydroxide within a range of 20 to 100 parts by weight with respect to 100 parts by weight of the plastic.

〔分解液から無機充填材を回収する工程〕
無機充填材は図1に示すような回収システム1を用いることにより回収される。すなわち、図1に示す回収システム1では、始めに、熱風供給装置5から乾燥室2内に加熱した空気(熱風)を供給し、乾燥室2内を乾燥温度に高める。次に、分解液供給装置4から高速回転させたディスク式スプレードライヤー乾燥機3の溝上に分解液を滴下し、分解液をディスク式スプレードライヤー乾燥機3の円周上側面に設けられた開口部から外方に噴出させ、分解液中の無機物をディスク式スプレードライヤー乾燥機3により破壊、且つ、分解液を霧状にする。
[Step of recovering inorganic filler from decomposition solution]
The inorganic filler is recovered by using a recovery system 1 as shown in FIG. That is, in the collection system 1 shown in FIG. 1, first, heated air (hot air) is supplied from the hot air supply device 5 into the drying chamber 2 to raise the drying chamber 2 to the drying temperature. Next, the decomposition liquid is dropped onto the groove of the disk-type spray dryer dryer 3 rotated at a high speed from the decomposition liquid supply device 4, and the decomposition liquid is provided on the circumferential upper side surface of the disk-type spray dryer dryer 3. The inorganic substance in the decomposition liquid is destroyed by the disc type spray dryer dryer 3 and the decomposition liquid is made into a mist.

次に、回収装置6において、乾燥室2の下部から無機充填材を吸引し、粒径の大きい無機充填材を分離し、所定の粒径範囲の無機充填材を回収することにより、無機充填材を回収する。この回収工程により、熱風に接触させた際に分解液中の液分を瞬時に蒸発させ、無機物を無機充填材として効率よく、乾燥,回収することができる。なお、ディスク式スプレードライヤー乾燥機3の回転速度は5000[rpm]以上50000[rpm]以下の範囲内にすることが望ましい。また、分解液が噴出,乾燥される領域の雰囲気温度は100[℃]以上300[℃]以下の温度範囲内に調整されていることが望ましい。   Next, in the recovery device 6, the inorganic filler is sucked from the lower portion of the drying chamber 2, the inorganic filler having a large particle size is separated, and the inorganic filler having a predetermined particle size range is recovered. Recover. By this recovery step, the liquid content in the decomposition liquid is instantly evaporated when brought into contact with hot air, and the inorganic substance can be efficiently dried and recovered as an inorganic filler. The rotational speed of the disk-type spray dryer dryer 3 is preferably in the range of 5000 [rpm] to 50000 [rpm]. In addition, it is desirable that the atmospheric temperature in the region where the decomposition liquid is ejected and dried is adjusted within a temperature range of 100 [° C.] to 300 [° C.].

上記ディスク式スプレードライヤー乾燥機3は、具体的には図2や図3に示すような構成を有し、回転軸が取り付けられる軸受部11と、軸受部11の周部に設けられた溝部12と、周方向に沿って設けられ、溝部12と連通する開口部13とを備える。そして、このような構成を有するディスク式スプレードライヤー乾燥機3では、回転時に溝部12に分解液が供給されると、開口部13から分解液が噴出される。   Specifically, the disk-type spray dryer dryer 3 has a configuration as shown in FIGS. 2 and 3, and includes a bearing portion 11 to which a rotating shaft is attached, and a groove portion 12 provided on a peripheral portion of the bearing portion 11. And an opening 13 provided along the circumferential direction and communicating with the groove 12. And in the disc type spray dryer dryer 3 which has such a structure, if a decomposition liquid is supplied to the groove part 12 at the time of rotation, a decomposition liquid will be ejected from the opening part 13. FIG.

なお、スプレードライヤー乾燥機には、ディスクを用いるディスク式と2流体ノズルを用いるノズル式とがあるが、ノズル式スプレードライヤー乾燥機では、分解液中の無機物の粒径が1[mm]を超えるようなものとなると、分解液の噴霧時にノズル先端部において分解液が詰まり、無機物の乾燥ができない上に、ディスク式を用いた時のような無機物の破壊もほとんど期待することができなくなり、所望の無機充填材を回収することができない。従って、乾燥機としては、ディスク式スプレードライヤー乾燥機を用いることが望ましい。   There are two types of spray dryer dryers: a disk type using a disk and a nozzle type using a two-fluid nozzle. In the nozzle type spray dryer dryer, the particle size of the inorganic substance in the decomposition liquid exceeds 1 [mm]. If this happens, the decomposition solution is clogged at the nozzle tip during spraying of the decomposition solution, and the inorganic material cannot be dried. In addition, it is difficult to expect the destruction of the inorganic material when using the disk type. The inorganic filler cannot be recovered. Therefore, it is desirable to use a disk type spray dryer dryer as the dryer.

また、アルカリ金属の水酸化物の水溶液を臨界流体として用いる場合には、分解後の分解液にはアルカリ金属の水酸化物が存在していることから、濾過を行うことにより、樹脂のモノマー又はオリゴマー、炭酸カルシウム,水酸化アルミニウム,及びガラス繊維とに分離し、さらに無機物に付着しているアルカリ金属の水酸化物を水で洗浄した後に無機物を含有するスラリーをディスク式スプレードライヤーで乾燥してもよい。そして、分解液を滴下する際に、ディスク式スプレードライヤーの円盤状物の回転数,分解液を噴出させる雰囲気温度を制御することによって、所望の粒径を有する無機充填材を回収することができる。   In addition, when an aqueous solution of an alkali metal hydroxide is used as a critical fluid, since the alkali metal hydroxide is present in the decomposition solution after decomposition, by filtration, the monomer of the resin or After separating into oligomer, calcium carbonate, aluminum hydroxide, and glass fiber, and further washing the alkali metal hydroxide adhering to the inorganic substance with water, the slurry containing the inorganic substance is dried with a disc spray dryer. Also good. And when dripping a decomposition liquid, the inorganic filler which has a desired particle size can be collect | recovered by controlling the rotation speed of the disk shaped thing of a disk type spray dryer, and the atmospheric temperature which spouts a decomposition liquid. .

[実施例1]
実施例1では、始めに、2[mm]の粒径に粗粉砕したFRP(松下電工(株)製FRPバスタブ,炭酸カルシウム及びガラス繊維含有品)600[g]、濃度1[mol/L]の水酸化カリウム水溶液2400[g]を圧力容器に投入し、ヒーターによって槽内の水を230[℃]に加熱し、槽内の水を亜臨界状態(臨界点(臨界温度374[℃],臨界圧力22.1[MPa])以下の状態)にした。そして、この状態で2時間放置することによりFRPを分解した後、室温まで冷却することによりFRPの分解液を得た。本分解液は、樹脂成分のモノマー又はオリゴマーと炭酸カルシウムとガラス繊維の混合品である。最後に、分解液をディスク式スプレードライヤー乾燥機に滴下することにより分解液を乾燥し、実施例1の無機充填材を得た。なお、ディスク式スプレードライヤー乾燥機は、乾燥室の塔径2[m]、ディスク径65[cm],回転数12000[rpm]、乾燥室入口温度200[℃]、乾燥室出口温度100[℃]の条件で運転した。
[Example 1]
In Example 1, first, FRP (FRP bathtub manufactured by Matsushita Electric Works Co., Ltd., calcium carbonate and glass fiber-containing product) 600 [g] coarsely pulverized to a particle size of 2 [mm], concentration 1 [mol / L] 2400 [g] of potassium hydroxide was put into a pressure vessel, the water in the tank was heated to 230 [° C.] with a heater, and the water in the tank was subcritical (critical point (critical temperature 374 [° C.], The critical pressure was 22.1 [MPa]) or less). And after decomposing | disassembling FRP by standing in this state for 2 hours, the decomposition liquid of FRP was obtained by cooling to room temperature. The decomposition solution is a mixture of a resin component monomer or oligomer, calcium carbonate, and glass fiber. Finally, the decomposition solution was dried by dropping the decomposition solution into a disk-type spray dryer dryer to obtain the inorganic filler of Example 1. The disk-type spray dryer dryer has a drying chamber tower diameter of 2 [m], a disk diameter of 65 [cm], a rotational speed of 12000 [rpm], a drying chamber inlet temperature of 200 [° C.], and a drying chamber outlet temperature of 100 [° C. ] Was operated under the conditions of].

[実施例2]
実施例1の亜臨界分解処理工程を行った後、分解液をフィルタープレス濾過器によって樹脂成分のモノマー又はオリゴマー,炭酸カルシウム、水酸化アルミニウム、及びガラス繊維に分離した。その後、続けてフィルタープレス濾過器による無機物のケーキ洗浄を行い、濾液のpHが10.5になった状態で無機物を14[wt%]含有するスラリーを3000[g]回収した。次に、スラリーを実施例1と同様の条件のディスク式スプレードライヤー乾燥機により乾燥することによって実施例2の無機充填材を得た。
[Example 2]
After performing the subcritical decomposition treatment step of Example 1, the decomposition solution was separated into a resin component monomer or oligomer, calcium carbonate, aluminum hydroxide, and glass fiber by a filter press filter. Subsequently, the inorganic cake was washed with a filter press filter, and 3000 [g] of a slurry containing 14 [wt%] of the inorganic substance was recovered in a state where the pH of the filtrate was 10.5. Next, the inorganic filler of Example 2 was obtained by drying the slurry with a disk-type spray dryer dryer under the same conditions as in Example 1.

[実施例3]
実施例1の分解液をディスク式スプレードライヤー乾燥機の回転数を30000[rpm]とした以外は実施例1ど同様の条件で乾燥することにより、実施例3の無機充填材を得た。
[Example 3]
The inorganic filler of Example 3 was obtained by drying the decomposition solution of Example 1 under the same conditions as in Example 1 except that the rotational speed of the disk spray dryer was changed to 30000 [rpm].

[実施例4]
実施例1の亜臨界分解処理工程を行った後、120φmmポットミルに、分解したFRP分解液250[g]、5mmボール400[g]を入れ、200[rpm]の回転数にて4時間、無機物の湿式粉砕を行う作業を繰り返し行った。その後、分解液を実施例1と同様の条件でディスク式スプレードライヤー乾燥機で乾燥することによって実施例4の無機充填材を得た。
[Example 4]
After performing the subcritical decomposition treatment step of Example 1, the decomposed FRP decomposition solution 250 [g] and 5 mm ball 400 [g] were placed in a 120 φmm pot mill, and the inorganic substance was rotated for 4 hours at a rotation speed of 200 [rpm]. The operation of performing wet pulverization was repeated. Then, the inorganic filler of Example 4 was obtained by drying a decomposition liquid with the disk type spray dryer drier on the conditions similar to Example 1. FIG.

以上により得られた実施例1〜4の無機充填材の平均粒径を計測した結果を以下の表1に示す。なお、平均粒径は、粒度分布測定装置(SALD−2000,島津製作所(株)製)を用いて計測した。

Figure 2007224082
The results of measuring the average particle diameter of the inorganic fillers of Examples 1 to 4 obtained as described above are shown in Table 1 below. The average particle size was measured using a particle size distribution measuring device (SALD-2000, manufactured by Shimadzu Corporation).
Figure 2007224082

表1に示すように、実施例1〜4の無機充填材によれば、亜臨界分解後の分解液から微粒径の無機充填材を回収できることがわかる。また特に、実施例3の無機充填材によれば、ディスク式スプレードライヤー乾燥機を実施例1,2よりも高速回転にすることによって、実施例1,2の無機充填材よりも微粒径の無機充填材が得られることがわかる。さらに、実施例4の無機充填材によれば、実施例1〜3の分解液を予め湿式分解した後に無機充填材を回収したが、微粒径の無機充填材を回収することができるものの、実施例1〜3と比較すると、平均粒径の大きい無機充填材しか回収することができなかった。これは、予め湿式粉砕して無機物の粒径を小さくした分解液をディスク式スプレードライヤー乾燥機において噴霧すると、無機物が円盤状物により破壊される効果よりも、1次粒子同士が密着し2次粒子化する効果の方が大きくなり、2次粒子化したままの状態で熱風下に噴霧され瞬間的に乾燥が行われるためであると考えられる。   As shown in Table 1, according to the inorganic fillers of Examples 1 to 4, it can be seen that the inorganic filler with a fine particle diameter can be recovered from the decomposition solution after subcritical decomposition. In particular, according to the inorganic filler of Example 3, the disk-type spray dryer dryer is rotated at a higher speed than Examples 1 and 2, so that the particle size is smaller than that of the inorganic filler of Examples 1 and 2. It turns out that an inorganic filler is obtained. Furthermore, according to the inorganic filler of Example 4, although the inorganic filler was recovered after wet decomposition of the decomposition liquids of Examples 1 to 3 in advance, the inorganic filler having a fine particle diameter can be recovered, Compared with Examples 1 to 3, only inorganic fillers having a large average particle diameter could be recovered. This is because the primary particles are in close contact with each other rather than the effect that the inorganic material is destroyed by the disk-like material when the decomposition liquid in which the particle size of the inorganic material is reduced by spraying in a disk-type spray dryer drier is wet. It is considered that the effect of making particles becomes larger, and the particles are sprayed under hot air in the state of being made into secondary particles and dried instantaneously.

以上、本発明者らによってなされた発明を適用した実施の形態について説明したが、この実施の形態による本発明の開示の一部をなす論述及び図面により本発明は限定されることはない。すなわち、上記実施の形態に基づいて当業者等によりなされる他の実施の形態、実施例及び運用技術等は全て本発明の範疇に含まれることは勿論であることを付け加えておく。   As mentioned above, although embodiment which applied the invention made by the present inventors was described, this invention is not limited by the description and drawing which make a part of indication of this invention by this embodiment. That is, it should be added that other embodiments, examples, operation techniques, and the like made by those skilled in the art based on the above-described embodiments are all included in the scope of the present invention.

本発明の実施形態となる無機充填材の回収システムの構成を示す模式図である。It is a schematic diagram which shows the structure of the collection | recovery system of the inorganic filler used as embodiment of this invention. 図1に示す乾燥機の構成を示す模式図である。It is a schematic diagram which shows the structure of the dryer shown in FIG. 図1に示す乾燥機の他の構成を示す模式図である。It is a schematic diagram which shows the other structure of the dryer shown in FIG.

符号の説明Explanation of symbols

1:回収システム
2:乾燥室
3:ディスク式スプレードライヤー乾燥機
4:分解液供給装置
5:熱風供給装置
6:回収装置
1: Recovery system 2: Drying chamber 3: Disc type spray dryer dryer 4: Decomposition liquid supply device 5: Hot air supply device 6: Recovery device

Claims (4)

無機充填材を含有するプラスチックを亜臨界水で分解することにより得られた分解物から無機充填材を回収する無機充填材の回収方法であって、
周方向に沿って複数の開口部を側面に有する円盤状物を回転させ、円盤状物に設けられ、開口部に連通する溝に前記無機充填材を含有する液体を供給し、液体を開口部から噴出させ、噴出した液体を熱風に接触させ、液体を蒸発させることにより無機充填材を分離,回収することを特徴とする無機充填材の回収方法。
A method of recovering an inorganic filler that recovers an inorganic filler from a decomposition product obtained by decomposing a plastic containing an inorganic filler with subcritical water,
A disk-shaped object having a plurality of openings on its side surface is rotated along the circumferential direction, and the liquid containing the inorganic filler is supplied to the groove provided in the disk-shaped object and communicating with the opening, and the liquid is opened. A method for recovering an inorganic filler, characterized in that the inorganic filler is separated and recovered by causing the liquid to be ejected from the container, contacting the ejected liquid with hot air, and evaporating the liquid.
請求項1に記載の無機充填材の回収方法であって、
前記円盤状物の回転速度は5000[rpm]以上50000[rpm]以下の範囲内にあることを特徴とする無機充填材の回収方法。
It is the collection | recovery method of the inorganic filler of Claim 1, Comprising:
The method for recovering an inorganic filler, wherein a rotational speed of the disk-shaped material is in a range of 5000 [rpm] to 50000 [rpm].
請求項1又は請求項2に記載の無機充填材の回収方法であって、
前記液体が噴出,蒸発される領域の雰囲気温度は100[℃]以上300[℃]以下の温度範囲内に調整されていることを特徴とする無機充填材の回収方法。
A method for recovering an inorganic filler according to claim 1 or 2,
The method for recovering an inorganic filler, wherein an ambient temperature in a region where the liquid is ejected and evaporated is adjusted to a temperature range of 100 [° C.] to 300 [° C.].
請求項1乃至請求項3のうち、いずれか1項に記載の無機充填材の回収方法によって回収された無機充填材。   The inorganic filler collect | recovered by the collection | recovery method of the inorganic filler of any one of Claims 1 thru | or 3.
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Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56129001A (en) * 1980-03-13 1981-10-08 Nippon Kokan Kk <Nkk> Spray dryer
JPH06277567A (en) * 1993-03-29 1994-10-04 Mitsubishi Heavy Ind Ltd Rotary atomizer
JPH08155203A (en) * 1991-07-10 1996-06-18 Kihachiro Osawa Centrifugal spray for spray drier
JPH1087872A (en) * 1996-09-09 1998-04-07 Agency Of Ind Science & Technol Method for recovering and reusing fiber from fiber-reinforced plastic
JPH11140224A (en) * 1997-11-07 1999-05-25 Hitachi Ltd Treatment of waste thermosetting plastic
JPH11138057A (en) * 1997-11-14 1999-05-25 Nippon Sharyo Seizo Kaisha Ltd Atomizing plate for rotary atomizer
JP2005336323A (en) * 2004-05-26 2005-12-08 Matsushita Electric Works Ltd Method for recovering inorganic substance from plastic
JP2005336320A (en) * 2004-05-26 2005-12-08 Matsushita Electric Works Ltd Method for recovering inorganic substance from plastic

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56129001A (en) * 1980-03-13 1981-10-08 Nippon Kokan Kk <Nkk> Spray dryer
JPH08155203A (en) * 1991-07-10 1996-06-18 Kihachiro Osawa Centrifugal spray for spray drier
JPH06277567A (en) * 1993-03-29 1994-10-04 Mitsubishi Heavy Ind Ltd Rotary atomizer
JPH1087872A (en) * 1996-09-09 1998-04-07 Agency Of Ind Science & Technol Method for recovering and reusing fiber from fiber-reinforced plastic
JPH11140224A (en) * 1997-11-07 1999-05-25 Hitachi Ltd Treatment of waste thermosetting plastic
JPH11138057A (en) * 1997-11-14 1999-05-25 Nippon Sharyo Seizo Kaisha Ltd Atomizing plate for rotary atomizer
JP2005336323A (en) * 2004-05-26 2005-12-08 Matsushita Electric Works Ltd Method for recovering inorganic substance from plastic
JP2005336320A (en) * 2004-05-26 2005-12-08 Matsushita Electric Works Ltd Method for recovering inorganic substance from plastic

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