JPH06322023A - Production of brominated polystyrene from recovered polystyrene foam - Google Patents

Production of brominated polystyrene from recovered polystyrene foam

Info

Publication number
JPH06322023A
JPH06322023A JP11312193A JP11312193A JPH06322023A JP H06322023 A JPH06322023 A JP H06322023A JP 11312193 A JP11312193 A JP 11312193A JP 11312193 A JP11312193 A JP 11312193A JP H06322023 A JPH06322023 A JP H06322023A
Authority
JP
Japan
Prior art keywords
polystyrene
brominated
solvent
recovered
foam
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP11312193A
Other languages
Japanese (ja)
Inventor
Toshiki Ikeda
敏喜 池田
Kenichi Kamata
健一 鎌田
Shinichi Monno
晋一 門野
Kiyoshi Mishima
清志 三島
Atsushi Sakabayashi
淳 酒林
Akihisa Takahashi
明久 高橋
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Manac Inc
Sekisui Kasei Co Ltd
Original Assignee
Manac Inc
Sekisui Plastics Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Manac Inc, Sekisui Plastics Co Ltd filed Critical Manac Inc
Priority to JP11312193A priority Critical patent/JPH06322023A/en
Publication of JPH06322023A publication Critical patent/JPH06322023A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08FMACROMOLECULAR COMPOUNDS OBTAINED BY REACTIONS ONLY INVOLVING CARBON-TO-CARBON UNSATURATED BONDS
    • C08F8/00Chemical modification by after-treatment
    • C08F8/18Introducing halogen atoms or halogen-containing groups
    • C08F8/20Halogenation

Abstract

PURPOSE:To effectively utilize a recovered waste polystyrene foam by pulverizing or pelletizing it or reducing its volume. dissolving it in a halogenated hydrocarbon solvent to remove impurities, and brominating the soln. to produce a brominated polystyrene. CONSTITUTION:A recovered polystyrene foam, pref. contg. 80wt.% or higher styrene units and from which foreign matters have been removed, is granulated, then pulverized or pelletized by melt extrusion with an extruder followed by cutting, and dissolved in a halogenated hydrocarbon solvent (e.g. ethylene dichloride). From the resulting soln. are removed solvent-insol. matters by filtration, etc., and pref. by further filtration after adsorbing the insol. matters with an adsorbent, e.g. diatom earth. Polystyrene dissolved in the solvent is brominated with bromine, etc., at -20 to 100 deg.C using a catalyst, e.g. anhydrous aluminum chloride. After the completion of bromination, the reaction soln. is washed with water, neutralized, and distilled to remove the solvent, thus giving a brominated polystyrene.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、回収発泡ポリスチレン
から可燃性樹脂の難燃剤として有用な臭素化ポリスチレ
ンを製造する方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for producing brominated polystyrene useful as a flame retardant for combustible resins from recovered expanded polystyrene.

【0002】[0002]

【従来の技術及び発明が解決しようとする課題】発泡ポ
リスチレンは、断熱性に優れ、硬度が高く、吸水率が小
さく、耐水性に優れており、衝撃吸収性に優れている。
また外観も美しい白色であり、着色も容易で、しかも比
較的安価であることから、家庭用包材や水産用魚箱に使
用されるビーズ発泡成形品、食品用トレーやカップ麺な
ど食品容器などに使用される発泡シート、断熱材を主体
とする建材用途などに使用される発泡ボード、包装緩衝
材用のバラ状緩衝材などに、幅広く使用されている。
BACKGROUND OF THE INVENTION Expanded polystyrene has excellent heat insulating properties, high hardness, small water absorption, excellent water resistance, and excellent impact absorption.
In addition, because it has a beautiful white appearance, is easy to color, and is relatively inexpensive, it is a foamed bead product used for household packaging and fish boxes for fisheries, food containers such as food trays and cup noodles. It is widely used for foamed sheets used for, foamed boards used for building materials mainly composed of heat insulating materials, and loose cushioning materials for packaging cushioning materials.

【0003】しかしながら、発泡ポリスチレンも他のプ
ラスチックと同様に、プラスチック廃棄物の処理、再生
化が環境問題の重要課題となっている。しかも、発泡ポ
リスチレンはゴミとして容積が大きいため、廃棄物処理
のターゲットになっており、ようやく関連業界が一体と
なってリサイクル活動に着手しはじめた現況にある。
However, in the case of expanded polystyrene, like other plastics, the treatment and recycling of plastic waste has become an important environmental issue. Moreover, since expanded polystyrene has a large volume as waste, it has become a target for waste treatment, and the related industries have finally begun to start recycling activities together.

【0004】[0004]

【課題を解決するための手段】本発明は、発泡ポリスチ
レンの廃棄物の活用方法であり、回収した発泡ポリスチ
レンを粉砕または減容、あるいはペレット化した後、ハ
ロゲン化炭化水素系溶媒に溶解して不溶物を除去し、次
いででこの溶液を臭素化して、臭素化ポリスチレンを製
造する方法に関するものである。
The present invention is a method of utilizing expanded polystyrene waste, in which the recovered expanded polystyrene is pulverized or reduced in volume, or pelletized, and then dissolved in a halogenated hydrocarbon solvent. The present invention relates to a method for producing brominated polystyrene by removing insoluble matters and then brominating this solution.

【0005】本発明で用いる発泡ポリスチレンとして
は、ポリスチレン、スチレン−無水マレイン酸共重合
体、ポリエチレン−スチレングラフト共重合体、スチレ
ン−ブタンジエン共重合体、アクリロニトリル−スチレ
ン共重合体、アクリロニトリル−ブタジエン−スチレン
共重合体などの発泡体を用いることができ、少なくとも
スチレン成分を80重量%以上含有することが望まし
い。
The expanded polystyrene used in the present invention includes polystyrene, styrene-maleic anhydride copolymer, polyethylene-styrene graft copolymer, styrene-butanediene copolymer, acrylonitrile-styrene copolymer, acrylonitrile-butadiene-styrene. A foam such as a copolymer can be used, and it is desirable that the foam contains at least 80% by weight of a styrene component.

【0006】発泡ポリスチレンは成形品であってもよ
く、家庭用包材や水産用魚箱などのビーズ発泡成形品、
食品用トレーやカップ麺などの食器容器などの発泡シー
ト、断熱材など建材として用いられる発泡ボード、バラ
状緩衝材などが用いられる。また、着色または印刷され
た発泡製品も使用することができる。さらには、発泡ビ
ーズの粒径が規格をはずれたカット品あるいは成形時の
バリの回収品も使用することができる。
The expanded polystyrene may be a molded product, such as a bead foam molded product such as a household packaging material or a fish box for fisheries,
A foam sheet such as a food tray or a tableware container such as cup noodles, a foam board used as a building material such as a heat insulating material, or a loose cushioning material is used. Foamed products that are colored or printed can also be used. Furthermore, a cut product in which the particle diameter of the expanded beads is out of the standard or a burr collected product at the time of molding can be used.

【0007】回収された発泡ポリスチレンが、例えば梱
包材や二次加工された発泡成形品である場合には、ラベ
ル、結束紐、ゴム材等の異物が含まれていることが多
い。また異物が発泡ポリスチレン以外の成分、ポリプロ
ピレン、ポリエチレンテレフタレート、塩化ビニル樹脂
等の樹脂材及びその発泡体、更にはアルミニウムのよう
な金属体であることも多い。そこで、回収発泡ポリスチ
レンの再生処理に先立ち、異物を分離選別する作業が必
要である。
When the recovered expanded polystyrene is, for example, a packaging material or a secondary processed expanded molded article, it often contains foreign substances such as a label, a binding cord, and a rubber material. In addition, the foreign matter is often a component other than expanded polystyrene, a resin material such as polypropylene, polyethylene terephthalate, or vinyl chloride resin and its foam, or a metal body such as aluminum. Therefore, it is necessary to separate and sort the foreign matter prior to the regeneration treatment of the recovered expanded polystyrene.

【0008】本発明で使用する回収発泡ポリスチレン
は、粉砕または減容、あるいはペレット化する必要があ
り、本発明の臭素化ポリスチレンの原料として使用する
ことができる。回収発泡ポリスチレンは粉砕または減
容、あるいはペレット化の処理をせずにそのまま臭素化
ポリスチレンの原料として使用することは可能である
が、輸送、貯蔵および工業化レベルでの製造を考えた場
合、嵩が大きく扱いにくいため、粉砕または減容、ある
いはペレット化して比重を大きくする必要がある。異物
を分離選別した後の発泡ポリスチレンを、粗粉砕し、更
に微粉砕して粉砕品を得る。あるいは、粗粉砕後押出機
で溶融、押出し後、裁断してペレット状の樹脂に戻すこ
とができる。また、回収発泡ポリスチレン中に、上記の
ような異物がさほど混在していない場合には、分離選別
作業を行わずに、異物が混在したまま押出機で溶融し、
押出機の出口付近に設けられた金網で異物を濾過した後
に、ノズル金型等より押出し、裁断を行い、ペレット化
することもできる。また、回収発泡ポリスチレン中に異
物が一定量以下しか含まれない場合には、そのまま機械
的に粗粉砕し、該粗粉砕物に再度機械的に剪断力を加え
ることにより微粉砕化すると共に、摩擦熱によりポリス
チレンの軟化温度以上に昇温して軟化させ、大部分の気
泡を脱気して減容させる。さらに、この脱気した微粉砕
物をポリスチレンの軟化温度以下で、衝撃式粉砕機によ
り不定形樹脂粒子に粉砕することができる。例えば、1
0重量%以下の異物が混在した回収発泡ポリスチレンで
は、機械的に粗粉砕し、該粗粉砕物に再度機械的に剪断
力を加えて微粉砕化すると共に、摩擦熱によりポリスチ
レンの軟化温度以上に昇温して軟化させ、大部分の気泡
を脱気して減容して発泡体の容積を約1/5以下とし、
さらに、該脱気した微粉砕物をポリスチレンの軟化温度
以下で衝撃式粉砕機により不定形樹脂粒子に粉砕したも
のを好適に使用することができる。
The recovered expanded polystyrene used in the present invention must be pulverized, reduced in volume, or pelletized, and can be used as a raw material for the brominated polystyrene of the present invention. Although the recovered expanded polystyrene can be used as it is as a raw material for brominated polystyrene without crushing, reducing the volume, or pelletizing, it is bulky when considering transportation, storage, and industrial level production. Since it is large and difficult to handle, it is necessary to increase the specific gravity by crushing, reducing the volume, or pelletizing. The expanded polystyrene after the foreign matter is separated and sorted is roughly pulverized and then finely pulverized to obtain a pulverized product. Alternatively, after coarsely pulverizing, the resin may be melted and extruded by an extruder, and then cut into a resin pellet. Also, in the recovered expanded polystyrene, when the foreign matter as described above is not much mixed, without performing the separation and sorting work, melted in the extruder with the foreign matter mixed,
It is also possible to filter foreign matter with a wire net provided near the exit of the extruder, then extrude from a nozzle die or the like, cut and pelletize. Further, when the recovered expanded polystyrene contains less than a certain amount of foreign matter, it is mechanically coarsely pulverized as it is, and the coarsely pulverized product is finely pulverized again by mechanically applying a shearing force to the finely pulverized material. The heat raises the temperature above the softening temperature of polystyrene to soften it and degasses most of the bubbles to reduce the volume. Further, this degassed finely pulverized product can be pulverized into amorphous resin particles by an impact pulverizer at a softening temperature of polystyrene or lower. For example, 1
The recovered expanded polystyrene mixed with 0% by weight or less of foreign matter is mechanically coarsely pulverized, and the coarsely pulverized product is mechanically pulverized again by applying a shearing force to the coarsely pulverized product. The temperature of the foam is softened, and most of the bubbles are degassed to reduce the volume of the foam to about 1/5 or less.
Further, the deaerated finely pulverized product, which is pulverized into amorphous resin particles by an impact pulverizer at a softening temperature of polystyrene or lower, can be suitably used.

【0009】上記のように粉砕または減容、あるいはペ
レット化したポリスチレンはハロゲン化炭化水素系溶剤
に溶解後、そのまま臭素化することも可能であるが、難
燃剤として耐熱性に優れた臭素化ポリスチレンを得るた
めには、前記溶剤不溶物を濾過、遠心沈降などの方法に
より除去する必要がある。更に溶解後、珪藻土、シリカ
ゲル、活性白土、活性炭などの吸着剤を加えて不溶物を
吸着させた後、濾過除去することがより望ましい。ハロ
ゲン化炭化水素系溶剤としては、塩化メチレン、クロロ
ホルム、四塩化炭素、エチレンジクロライド、1,1,
1−トリクロロエタン、トリクロロエチレン、テトラク
ロロエチレン、モノクロルベンゼンなどの塩素化炭化水
素、臭化メチレン、エチレンジブロマイドなどの臭素化
炭化水素が用いられる。不溶物を除去しないで臭素化に
供した場合は、回収した発泡ポリスチレン中に含まれる
製造の予備発泡時の合着防止剤、成形時の融着促進剤お
よび帯電防止剤などの表面処理剤、気泡調整および気泡
安定剤、滑剤、発泡剤などの添加剤によって熱的に不安
定な化合物が生成し、得られる臭素化ポリスチレンは耐
熱性に劣るものとなり、難燃剤として樹脂に配合した際
に、分解、着色現象を引き起こし、成形品の商品価値を
低下させる。
The polystyrene crushed, reduced in volume, or pelletized as described above can be dissolved in a halogenated hydrocarbon solvent and then brominated as it is, but a brominated polystyrene excellent in heat resistance as a flame retardant. In order to obtain the above, it is necessary to remove the solvent insoluble matter by a method such as filtration or centrifugal sedimentation. After dissolution, it is more desirable to add an adsorbent such as diatomaceous earth, silica gel, activated clay, or activated carbon to adsorb the insoluble matter, and then remove by filtration. Halogenated hydrocarbon solvents include methylene chloride, chloroform, carbon tetrachloride, ethylene dichloride, 1,1,
Chlorinated hydrocarbons such as 1-trichloroethane, trichloroethylene, tetrachloroethylene and monochlorobenzene, and brominated hydrocarbons such as methylene bromide and ethylene dibromide are used. When subjected to bromination without removing insoluble matter, anti-adhesion agent at the time of pre-foaming production, which is contained in the recovered expanded polystyrene, a surface treatment agent such as a fusion accelerator and an antistatic agent at the time of molding, A thermally unstable compound is generated by an additive such as a bubble control agent, a bubble stabilizer, a lubricant, and a foaming agent, and the obtained brominated polystyrene becomes inferior in heat resistance, and when blended in a resin as a flame retardant, It causes decomposition and coloring phenomena and reduces the commercial value of molded products.

【0010】次に前記溶媒に溶解したポリスチレンを一
般的な方法で臭素化する。例えば臭素化剤としては、臭
素、塩化臭素などを用いることができる。臭素化の触媒
としては、無水塩化アルミニウム、無水塩化第二鉄、三
塩化アンチモンなどのルイス酸、またはアルミニウム、
鉄、アンチモンなどの金属を使用することができる。反
応温度は−20〜100℃が好ましい。臭素化反応後の
臭素化ポリスチレン溶液は、水洗中和して酸分および無
機塩を除去した後、溶媒を留去あるいはメタノール、エ
タノールなどの貧溶剤中へ滴下することにより、粉体ま
たは固体の臭素化ポリスチレンを得ることができる。
Next, polystyrene dissolved in the solvent is brominated by a general method. For example, as the brominating agent, bromine, bromine chloride or the like can be used. As the bromination catalyst, anhydrous aluminum chloride, anhydrous ferric chloride, Lewis acid such as antimony trichloride, or aluminum,
Metals such as iron and antimony can be used. The reaction temperature is preferably -20 to 100 ° C. The brominated polystyrene solution after the bromination reaction is neutralized by washing with water to remove the acid component and the inorganic salt, and then the solvent is distilled off or dropped into a poor solvent such as methanol or ethanol to obtain a powder or a solid. Brominated polystyrene can be obtained.

【0011】本発明の方法で得られる臭素化ポリスチレ
ンの臭素含有率は、20〜70重量%であることが可燃
性樹脂の難燃剤としての使用を考慮した場合好ましい。
The bromine content of the brominated polystyrene obtained by the method of the present invention is preferably 20 to 70% by weight in consideration of the use of the flammable resin as a flame retardant.

【0012】可燃性樹脂としては、ポリスチレンやAB
Sのようなスチレン系樹脂、ポリエチレンやポリプロピ
レンのようなポリオレフィン、ポリエチレンテレフタレ
ートやポリブチレンテレフタレートのような熱可塑性ポ
リエステル、ナイロン66やナイロン46のようなポリ
アミドなどが挙げられる。
Examples of combustible resins include polystyrene and AB
Examples thereof include styrene resins such as S, polyolefins such as polyethylene and polypropylene, thermoplastic polyesters such as polyethylene terephthalate and polybutylene terephthalate, and polyamides such as nylon 66 and nylon 46.

【0013】[0013]

【実施例】以下に実施例を挙げて本発明を更に詳細に説
明するが、本発明はこれらの実施例によって限定される
ものではない。
The present invention will be described in more detail with reference to the following examples, but the present invention is not limited to these examples.

【0014】臭素化ポリスチレンの合成 (実施例1)1L のガラス製反応器(撹拌装置、コンデ
ンサー、温度計、滴下ロート及びガス吸収装置を備え
る)内で、発泡ポリスチレンの回収減容品75g をエチ
レンジクロライド(以下EDCと称する)750g に溶
解し、さらに珪藻土20g を加え、撹拌しながら不溶物
を吸着させた後、ヌッチェ濾過により不溶物と珪藻土を
除去した。濾液に三塩化アンチモン6g を加え撹拌溶解
した後、撹拌しつつ内温を15〜25℃に保ちながら、
予め調整した70重量%の塩化臭素のEDC溶液370
g を2時間かけて滴下し、さらに15〜25℃で1時間
熟成させた。熟成終了後、過剰の塩化臭素を還元し、臭
素化ポリスチレンのEDC溶液を中和、水洗した後、メ
タノール中に滴下し、晶析させた。濾過乾燥後、粉体の
臭素化ポリスチレン205g を得た。得られた臭素化ポ
リスチレンの臭素含有量は68.5%であった。臭素含
有量、熱重量分析(5%、10%重量減少温度)、外観
色相および加熱発生HBr量を分析した結果を表1に示
す。また分析は以下の方法で行った。
Synthesis of Brominated Polystyrene (Example 1) In a 1 L glass reactor equipped with a stirrer, a condenser, a thermometer, a dropping funnel and a gas absorbing device, 75 g of a volume-reduced polystyrene foam product was recovered. It was dissolved in 750 g of dichloride (hereinafter referred to as EDC), 20 g of diatomaceous earth was further added, the insoluble matter was adsorbed with stirring, and the insoluble matter and diatomaceous earth were removed by Nutsche filtration. After adding 6 g of antimony trichloride to the filtrate and stirring to dissolve it, while maintaining the internal temperature at 15 to 25 ° C. with stirring,
Preconditioned 70% by weight EDC solution of bromine chloride 370
g was added dropwise over 2 hours and further aged at 15 to 25 ° C for 1 hour. After completion of aging, excess bromine chloride was reduced, the EDC solution of brominated polystyrene was neutralized, washed with water, and then dropped into methanol for crystallization. After filtration and drying, 205 g of powdered brominated polystyrene was obtained. The bromine content of the obtained brominated polystyrene was 68.5%. Table 1 shows the results of analysis of the bromine content, thermogravimetric analysis (5%, 10% weight loss temperature), appearance hue, and amount of HBr generated by heating. The analysis was conducted by the following method.

【0015】・臭素含有量はフラスコ燃焼法(JIS
K−7299)に準ずる方法で測定した。 ・熱重量分析は、測定装置としてサーモフレックス81
00(リガク製)を使用した。また雰囲気は空気(約5
0ml/min)、昇温速度は10℃/min. として測定した。 ・外観色相は、色彩色差計(ミノルタカメラ製、CR−
100型)によって測定し、L、a、b表示系の値とし
て求めた。 ・加熱発生HBr量は電気炉に加熱管をセットし、さら
に吹き込み管を備えたガス吸収瓶(蒸留水100ml)に
接続し、電気炉に窒素ガス(約50ml/min)を通し、試
料3g を加熱管に入れ、200℃で1時間加熱した後、
ガス吸収水の臭素量をボルハード法により定量分析し
た。
The bromine content is determined by the flask combustion method (JIS
K-7299).・ Thermogravimetric analysis uses Thermoflex 81 as a measuring device.
00 (manufactured by Rigaku) was used. The atmosphere is air (about 5
0 ml / min), and the heating rate was 10 ° C./min.・ Appearance hue is a color difference meter (Minolta camera, CR-
100 type) and determined as values for L, a, and b display systems.・ For the amount of HBr generated by heating, set a heating tube in the electric furnace, connect it to a gas absorption bottle (distilled water 100 ml) equipped with a blowing tube, and pass nitrogen gas (about 50 ml / min) through the electric furnace to sample 3 g. Put in a heating tube and heat at 200 ℃ for 1 hour,
The amount of bromine in the gas absorption water was quantitatively analyzed by the Volhard method.

【0016】(実施例2)実施例1において、溶剤のE
DC750g を臭化メチレン1,500g に、触媒の三
酸化アンチモンを無水塩化アルミニウムに、臭素化剤の
塩化臭素のEDC溶液370g を臭素359g に変更し
た以外は、実施例1と同様の方法で臭素化ポリスチレン
の粉体208g を得た。分析結果は表1に示す。
(Example 2) In Example 1, the solvent E
Bromination in the same manner as in Example 1 except that 750 g of DC was changed to 1,500 g of methylene bromide, antimony trioxide as a catalyst was changed to anhydrous aluminum chloride, and 370 g of an EDC solution of bromine chloride as a brominating agent was changed to 359 g of bromine. 208 g of polystyrene powder was obtained. The analysis results are shown in Table 1.

【0017】(比較例1)実施例1において、臭素化前
のポリスチレンのEDC溶液から不溶物の吸着・濾過を
行わずに、そのまま臭素化に供した以外は、実施例1と
同様の方法で臭素化ポリスチレンの粉体213g を得
た。分析結果は表1に示す。
(Comparative Example 1) In the same manner as in Example 1, except that the EDC solution of polystyrene before bromination was used for bromination without adsorbing and filtering insoluble matter. 213 g of brominated polystyrene powder was obtained. The analysis results are shown in Table 1.

【0018】[0018]

【表1】 [Table 1]

【0019】樹脂成形品の難燃性と機械特性の評価 (実施例3、4及び比較例2)ポリエチレンテレフタレ
ート(帝人製TR−4550BH)に、実施例1、2及
び比較例1で得られた臭素化ポリスチレン、三酸化アン
チモン(日本精鉱製ATOX−S)、ガラス繊維(旭フ
ァイバーグラス製3MA429−A)を表2に示す配合
割合で混合後、二軸押出機(陸亜製RY−30−30−
VS3.7)により設定温度280℃で混練し、押出機
先端に付設されたノズル金型から押出した直後に、押出
されたストランドを水中で冷却し、ペレタイザーでペレ
ット化した。このペレットを120℃で24時間乾燥し
た後、射出成形機(クロックナー製F85)を用い、シ
リンダー温度240〜265℃、金型温度140〜15
0℃で成形して試験片を得た。得られた試験片について
下記の方法で物性試験を行った。表2にその試験結果を
示す。 ・熱変形温度はJIS K 7207に準ずる方法で測
定した。 ・曲げ強度はJIS K 7203に準ずる方法で測定
した。 ・引張強度はJIS K 7113に準ずる方法で測定
した。 ・燃焼試験はUL94(1/16インチ)に準ずる方法
で測定した。 ・酸素指数はJIS K 7201に準ずる方法で測定
した。
Evaluation of Flame Retardancy and Mechanical Properties of Resin Molded Articles (Examples 3, 4 and Comparative Example 2) Polyethylene terephthalate (TR-4550BH manufactured by Teijin) was obtained in Examples 1, 2 and Comparative Example 1. After mixing brominated polystyrene, antimony trioxide (ATOX-S manufactured by Nippon Mining Co., Ltd.), and glass fiber (3MA429-A manufactured by Asahi Fiber Glass) at the compounding ratio shown in Table 2, a twin-screw extruder (RY-30 manufactured by Rikua). -30-
Immediately after extruding from a nozzle die attached to the tip of the extruder, the extruded strand was cooled in water and pelletized by a pelletizer. After drying the pellets at 120 ° C. for 24 hours, a cylinder temperature of 240 to 265 ° C. and a mold temperature of 140 to 15 are used by using an injection molding machine (F85 made by Crokner).
A test piece was obtained by molding at 0 ° C. The physical properties of the obtained test piece were tested by the following methods. Table 2 shows the test results. -The heat distortion temperature was measured by a method according to JIS K7207. Bending strength was measured by a method according to JIS K7203. -Tensile strength was measured by a method according to JIS K7113. -The combustion test was measured by a method according to UL94 (1/16 inch). The oxygen index was measured by a method according to JIS K7201.

【0020】[0020]

【表2】 [Table 2]

【0021】(実施例5、6及び比較例3)ナイロン6
6樹脂(東レ製アラミンCM3001N)に、実施例
1、2及び比較例1で得られた臭素化ポリスチレン、三
酸化アンチモン(日本精鉱製ATOX−S)、ガラス繊
維(旭ファイバーグラス製03MAFT−2A)を表3
に示す配合割合で混合後、二軸押出機により設定温度2
40〜260℃で混練し、押出機先端に付設されたノズ
ル金型から押出した直後に、押出されたストランドを水
中で冷却し、ペレタイザーでペレット化した。得られた
ペレットを80℃で5時間真空乾燥した後、射出成形機
を用い、シリンダー温度255〜265℃、金型温度1
00℃で成形して試験片を得た。得られた試験片につい
て、実施例3、4及び比較例2と同様の試験方法で物性
試験を行った。その結果を表3に示す。
(Examples 5 and 6 and Comparative Example 3) Nylon 6
6 resin (Aramin CM3001N manufactured by Toray), brominated polystyrene obtained in Examples 1 and 2 and Comparative Example 1, antimony trioxide (ATOX-S manufactured by Nihon Seiko Co., Ltd.), glass fiber (03MAFT-2A manufactured by Asahi Fiber Glass) ) To Table 3
After mixing with the compounding ratio shown in, set temperature 2 with a twin-screw extruder.
Immediately after being kneaded at 40 to 260 ° C. and extruded from a nozzle die attached to the tip of the extruder, the extruded strand was cooled in water and pelletized by a pelletizer. After vacuum-drying the obtained pellets at 80 ° C. for 5 hours, using an injection molding machine, the cylinder temperature is 255 to 265 ° C. and the mold temperature is 1
A test piece was obtained by molding at 00 ° C. The obtained test pieces were subjected to a physical property test by the same test method as in Examples 3 and 4 and Comparative Example 2. The results are shown in Table 3.

【0022】[0022]

【表3】 [Table 3]

【0023】[0023]

【発明の効果】本発明によれば得られる臭素化ポリスチ
レンは、回収した発泡ポリスチレンを原料とするもので
あり、これら廃棄物の有効な活用方法として、社会に貢
献するものである。また、得られた臭素ポリスチレン
は、外観色相及び耐熱性に優れ、特に、臭素化ポリスチ
レンを可燃性樹脂に配合した樹脂組成物から得られる成
形品は、難燃性、耐熱性、機械特性に優れたものとする
ことができる。すなわち、回収した発泡ポリスチレン中
に含まれる種々の添加剤が臭素化前に除去されるため、
臭素化によって熱的に不安定な化合物が生成しないの
で、難燃剤として使用した場合にも、優れて成形品を得
ることができ、商品価値を向上させることができる。
The brominated polystyrene obtained according to the present invention uses recovered expanded polystyrene as a raw material and contributes to society as an effective method of utilizing these wastes. Further, the obtained bromine polystyrene is excellent in appearance hue and heat resistance, and in particular, molded articles obtained from a resin composition in which brominated polystyrene is mixed with a flammable resin have excellent flame retardancy, heat resistance, and mechanical properties. It can be That is, since various additives contained in the recovered expanded polystyrene are removed before bromination,
Since a thermally unstable compound is not generated by bromination, a molded product can be obtained excellently even when it is used as a flame retardant, and the commercial value can be improved.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 門野 晋一 広島県福山市箕沖町92番地 マナック株式 会社箕沖工場内 (72)発明者 三島 清志 広島県福山市箕沖町92番地 マナック株式 会社箕沖工場内 (72)発明者 酒林 淳 広島県福山市箕沖町92番地 マナック株式 会社箕沖工場内 (72)発明者 高橋 明久 広島県福山市箕沖町92番地 マナック株式 会社箕沖工場内 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Shinichi Kadono Shinichi Kadano 92 Minohoki-cho, Fukuyama-shi, Hiroshima Manac Co., Ltd.Minooki Plant (72) Inventor Kiyoshi Mishima 92 Minohoki-cho, Fukuyama-shi, Hiroshima Manac Co., Ltd. Minokioki Plant ( 72) Inventor Atsushi Sakabayashi 92 Minooki-cho, Fukuyama-shi, Hiroshima Manac Co., Ltd.Minooki Plant (72) Inventor Akihisa Takahashi 92 Minohoki-cho, Fukuyama-shi, Hiroshima Manac Co., Ltd.

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 回収した発泡ポリスチレンを粉砕または
減容、あるいはペレット化した後、ハロゲン化炭化水素
系溶剤に溶解して不溶物を除去し、次いでこの溶液を臭
素化して、臭素化ポリスチレンを製造する方法。
1. The recovered expanded polystyrene is crushed, reduced in volume, or pelletized, and then dissolved in a halogenated hydrocarbon solvent to remove insolubles, and then this solution is brominated to produce brominated polystyrene. how to.
JP11312193A 1993-05-14 1993-05-14 Production of brominated polystyrene from recovered polystyrene foam Pending JPH06322023A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP11312193A JPH06322023A (en) 1993-05-14 1993-05-14 Production of brominated polystyrene from recovered polystyrene foam

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP11312193A JPH06322023A (en) 1993-05-14 1993-05-14 Production of brominated polystyrene from recovered polystyrene foam

Publications (1)

Publication Number Publication Date
JPH06322023A true JPH06322023A (en) 1994-11-22

Family

ID=14604060

Family Applications (1)

Application Number Title Priority Date Filing Date
JP11312193A Pending JPH06322023A (en) 1993-05-14 1993-05-14 Production of brominated polystyrene from recovered polystyrene foam

Country Status (1)

Country Link
JP (1) JPH06322023A (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002513060A (en) * 1998-04-24 2002-05-08 アルベマール・コーポレーシヨン Brominated polystyrene flame retardant
US7202296B2 (en) 2003-12-19 2007-04-10 Albemarle Corporation Flame retardant compositions and their use
JP2009516019A (en) * 2005-11-12 2009-04-16 ダウ グローバル テクノロジーズ インコーポレイティド Brominated butadiene-vinyl aromatic hydrocarbon copolymer, blend of the copolymer and vinyl aromatic hydrocarbon polymer, and polymer foam formed from the blend
US7632893B2 (en) 2005-06-30 2009-12-15 Albemarle Corporation Brominated styrenic polymers and their preparation
US7666943B2 (en) 2004-01-21 2010-02-23 Albemarle Corporation Flame retarded fibers and filaments and process of production therefor
US7666944B2 (en) 2004-01-21 2010-02-23 Albemarle Corporation Flame retarded fibers and filaments and process of production therefor
CN106565876A (en) * 2016-11-01 2017-04-19 珠海澳圣聚合物材料有限公司 Continuous preparation method of controlled-molecular-weight brominated polystyrene
CN106565875A (en) * 2016-11-01 2017-04-19 珠海澳圣聚合物材料有限公司 Method for continuous preparation of controlled-molecular-weight brominated polystyrene master batch

Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002513060A (en) * 1998-04-24 2002-05-08 アルベマール・コーポレーシヨン Brominated polystyrene flame retardant
JP4791633B2 (en) * 1998-04-24 2011-10-12 アルベマール・コーポレーシヨン Bromine substituted polystyrene flame retardant
US7202296B2 (en) 2003-12-19 2007-04-10 Albemarle Corporation Flame retardant compositions and their use
US7405254B2 (en) 2003-12-19 2008-07-29 Albemarle Corporation Flame retardant compositions and their use
US7666943B2 (en) 2004-01-21 2010-02-23 Albemarle Corporation Flame retarded fibers and filaments and process of production therefor
US7666944B2 (en) 2004-01-21 2010-02-23 Albemarle Corporation Flame retarded fibers and filaments and process of production therefor
US7632893B2 (en) 2005-06-30 2009-12-15 Albemarle Corporation Brominated styrenic polymers and their preparation
US8168723B2 (en) 2005-06-30 2012-05-01 Albemarle Corporation Brominated styrenic polymers and their preparation
JP2009516019A (en) * 2005-11-12 2009-04-16 ダウ グローバル テクノロジーズ インコーポレイティド Brominated butadiene-vinyl aromatic hydrocarbon copolymer, blend of the copolymer and vinyl aromatic hydrocarbon polymer, and polymer foam formed from the blend
CN106565876A (en) * 2016-11-01 2017-04-19 珠海澳圣聚合物材料有限公司 Continuous preparation method of controlled-molecular-weight brominated polystyrene
CN106565875A (en) * 2016-11-01 2017-04-19 珠海澳圣聚合物材料有限公司 Method for continuous preparation of controlled-molecular-weight brominated polystyrene master batch
CN106565876B (en) * 2016-11-01 2019-03-12 珠海澳圣聚合物材料有限公司 A method of continuously preparing molecular weight-controllable brominated polystyrene

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