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JPH0832889B2 - Treatment method for polystyrene waste - Google Patents
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JPH0832889B2 - Treatment method for polystyrene waste - Google Patents

Treatment method for polystyrene waste

Info

Publication number
JPH0832889B2
JPH0832889B2 JP17801788A JP17801788A JPH0832889B2 JP H0832889 B2 JPH0832889 B2 JP H0832889B2 JP 17801788 A JP17801788 A JP 17801788A JP 17801788 A JP17801788 A JP 17801788A JP H0832889 B2 JPH0832889 B2 JP H0832889B2
Authority
JP
Japan
Prior art keywords
polystyrene waste
polystyrene
zeolite
zsm
waste
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.)
Expired - Lifetime
Application number
JP17801788A
Other languages
Japanese (ja)
Other versions
JPH0229492A (en
Inventor
喜代志 斉藤
隆至 福田
智 鈴木
政和 阿部
寿夫 弘田
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.)
National Institute of Advanced Industrial Science and Technology AIST
Original Assignee
Agency of Industrial Science and Technology
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 Agency of Industrial Science and Technology filed Critical Agency of Industrial Science and Technology
Priority to JP17801788A priority Critical patent/JPH0832889B2/en
Publication of JPH0229492A publication Critical patent/JPH0229492A/en
Publication of JPH0832889B2 publication Critical patent/JPH0832889B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Classifications

    • 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

Landscapes

  • Manufacture Of Porous Articles, And Recovery And Treatment Of Waste Products (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
  • Processing Of Solid Wastes (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • Catalysts (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
  • Low-Molecular Organic Synthesis Reactions Using Catalysts (AREA)

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明はポリスチレン廃棄物の処理方法に関し、特に
ポリスチレン廃棄物からハイオクタンガソリン基材及び
高付加価値化学品原料を高収率で取得する方法に関す
る。
Description: TECHNICAL FIELD The present invention relates to a method for treating polystyrene waste, and in particular, a method for obtaining a high-octane gasoline base material and a high-value-added chemical raw material from polystyrene waste in high yield. Regarding

(従来の技術) 近年プラスチックの生産量の増加に伴いその廃棄物の
処理が社会問題化していることは周知のとおりである。
プラスチックの種類によってはその再利用の技術開発が
実用段階に達しているものも少なくない。
(Prior Art) It is well known that the treatment of waste has become a social problem with the increase in the production amount of plastics in recent years.
Depending on the type of plastic, the technological development of its reuse has reached the stage of practical use.

しかし我国での熱可塑性プラスチックの生産量の約半
分ほどを占めているといわれるポリオレフィン系プラス
チックの再利用技術は成形材料としての再利用等小規模
なものを除き十分な実用効果を得るには至っていない。
However, the recycling technology of polyolefin plastics, which is said to occupy about half of the production of thermoplastics in Japan, has not achieved sufficient practical effects except for small-scale reuse such as molding material. Not in.

ポリスチレン、特に発泡ポリスチレンは安価にして保
温性等に優れるところから各種食品容器等として大量に
用いられているが、そのほとんどは廃棄処分されている
のが実情である。
Polystyrene, particularly expanded polystyrene, is used in large quantities as various food containers and the like because it is inexpensive and has excellent heat retention, but most of them are actually discarded.

(発明が解決すべき課題) 本発明の目的はポリスチレン廃棄物の有効利用法を提
供することにあり、特にポリスチレン廃棄物からハイオ
クタンガソリン基材及び高付加価値化学品原料として有
用な芳香族炭化水素油を高収率にて生成せしめる方法を
提供することにある。
(Problems to be Solved by the Invention) An object of the present invention is to provide an effective utilization method of polystyrene waste, and in particular, aromatic polystyrene which is useful as a raw material for high octane gasoline and high value-added chemicals from polystyrene waste. It is to provide a method for producing hydrogen oil in a high yield.

(課題を解決するための手段) 本発明はポリスチレン廃棄物を溶融し、該溶融物を加
熱して液相で熱分解させ、発生した蒸気状生成物を1〜
12の範囲の拘束係数を持つゼオライト充填層中において
接触転化させ芳香族炭化水素油を生成取得することを特
徴とするポリスチレン廃棄物の処理方法にある。
(Means for Solving the Problems) The present invention melts polystyrene waste, heats the melt to thermally decompose it in a liquid phase, and
A method for treating polystyrene waste is characterized in that catalytic conversion is carried out in a packed bed of zeolite having a constraint coefficient of 12 to produce and obtain aromatic hydrocarbon oil.

本発明方法に供するポリスチレン廃棄物はフィルム、
シート、成形品等いかなる形態の廃棄物でもよいが、特
に発泡ポリスチレン製品の廃棄物が好ましく用いられ
る。これらは通常適宜の手段で粉砕した上、そのまま又
は押出機等を用いて加熱し軟化溶融させつつ連続的に熱
分解反応槽に供給されるが、発泡ポリスチレン製品の場
合は水蒸気処理等により脱泡後粉砕したものを軟化溶融
させることが望ましい。
The polystyrene waste used in the method of the present invention is a film,
Although wastes in any form such as sheets and molded products may be used, wastes of expanded polystyrene products are particularly preferably used. These are usually pulverized by an appropriate means and then continuously supplied to the pyrolysis reaction tank as they are or while being heated and softened and melted by using an extruder or the like. It is desirable to soften and melt what is crushed afterwards.

本発明方法では第1段の分解をポリスチレンの溶融液
相にて行うことを本質とする。この第1段の熱分解反応
槽の加熱温度は200〜450℃、特に250〜400℃が好まし
い。第1段の熱分解反応は溶融ポリスチレンを所定温度
条件に維持するだけでも進行するが、撹拌を併用したり
反応系に無機多孔質粒状物等を共存させることもでき
る。無機多孔質粒状物としては反応条件下に変形したり
変質したりしないものであれば、その種類、大きさ等は
特に制限されないが、大きさとしては通常1〜10mm程度
の粒径のものが好ましい。かかる多孔質粒状物の具体例
としては天然ゼオライト、ボーキサイト、赤泥等があ
る。
In the method of the present invention, the essence is that the first-stage decomposition is carried out in the molten liquid phase of polystyrene. The heating temperature of the first-stage thermal decomposition reaction tank is preferably 200 to 450 ° C, and particularly preferably 250 to 400 ° C. The first-stage thermal decomposition reaction proceeds only by maintaining the molten polystyrene at a predetermined temperature condition, but it is also possible to use stirring in combination or to allow inorganic porous particles and the like to coexist in the reaction system. As the inorganic porous granular material, if it does not deform or deteriorate under the reaction conditions, its type, size, etc. are not particularly limited, but the size is usually 1 to 10 mm or so. preferable. Specific examples of such porous granular material include natural zeolite, bauxite, red mud and the like.

かくして第1段の熱分解反応槽で生成した蒸気状生成
物は順次ゼオライト充填層に通され接触転化される。
Thus, the vaporous products produced in the first-stage pyrolysis reaction tank are successively passed through the packed bed of zeolite and catalytically converted.

本発明ではこの第2段の気相接触転化において触媒と
して1〜12の範囲の拘束係数を持つゼオライトを用いる
ことを本質とする。拘束係数(constraint index)はた
とえば米国特許第4,016,218に定義されている。
In the present invention, it is essential to use zeolite having a constraint coefficient in the range of 1 to 12 as a catalyst in the gas phase catalytic conversion in the second stage. The constraint index is defined, for example, in US Pat. No. 4,016,218.

かかる型のゼオライトの具体例としてはZSM−5,ZSM−
11,ZSM−12,ZSM−23,ZSM−35,ZSM−38,ZSM−48等があ
り、特にZSM−5が好ましく用いられる。ZSM−5はその
X線回折パターン中に、合成した状態において、次に示
す線を有する結晶性ゼオライトである。
Specific examples of such type of zeolite include ZSM-5, ZSM-
There are 11, ZSM-12, ZSM-23, ZSM-35, ZSM-38, ZSM-48 and the like, and ZSM-5 is particularly preferably used. ZSM-5 is a crystalline zeolite having the following lines in the synthesized state in its X-ray diffraction pattern.

格子面間隔 相対強度 11.2±0.2 S 10.1±0.2 S 3.86±0.08 VS 3.72±0.08 S 3.66±0.05 M かかるゼオライトは通常酸型(当初のアルカリ金属を
Hで置きかえた型)で用いられるが、必要に応じ、白金
その他の金属を有するものも用いられる。かかるゼオラ
イトは通常それ自体で又はアルミナ等の担体と共に粒径
0.1〜10mm程度の任意の形に成型して用いられる。
Lattice plane spacing Relative strength 11.2 ± 0.2 S 10.1 ± 0.2 S 3.86 ± 0.08 VS 3.72 ± 0.08 S 3.66 ± 0.05 M Such zeolites are usually used in acid form (the original alkali metal is replaced with H), but it is necessary. Correspondingly, one having platinum or other metal is also used. Such zeolites usually have a particle size on their own or with a carrier such as alumina.
It is used after being molded into an arbitrary shape of about 0.1 to 10 mm.

この第2段の接触転化反応は通常の操作では200〜400
℃、好ましくは250〜350℃の温度で行われる。このよう
な低温操作は従来の知見からは予想外のことである。か
かる低温の使用は経済性だけでなく、望ましくない副反
応の抑制等の効果ももたらす。
This second-stage catalytic conversion reaction is 200-400 in normal operation.
C., preferably at a temperature of 250 to 350.degree. Such low temperature operation is unexpected from the conventional knowledge. The use of such a low temperature brings not only economical efficiency but also effects such as suppression of undesirable side reactions.

上記ゼオライトの使用は単に温度条件の低下や安定し
た連続操作を可能にするだけでなく、生成物の品質と収
率向上に顕著な効果をもたらす。またこの触媒は再生再
使用してもその効果が維持される。この再生に伴う効果
の維持は本発明方法において特に顕著である。他の反応
に用いた再生触媒であっても本発明方法で効果的に用い
ることができる。
The use of the above-mentioned zeolite not only allows reduction of temperature conditions and stable continuous operation, but also has a remarkable effect on improvement of product quality and yield. Moreover, the effect is maintained even if this catalyst is regenerated and reused. The maintenance of the effect associated with this regeneration is particularly remarkable in the method of the present invention. Even a regenerated catalyst used in another reaction can be effectively used in the method of the present invention.

本発明方法により高収率で芳香族炭化水素油が得られ
る。その成分はベンゼン、トルエン及びキシレン異性体
(o−,m−及びp−キシレン並びにエチルベンゼン)が
大半である。これらはBTXと称されいずれも石油化学工
業で高い利用価値をもっている。従って必要に応じ各成
分に分離して化学品原料として利用できると共に、その
成分特性からハイオクタンガソリン基材としても有効に
利用される。
By the method of the present invention, aromatic hydrocarbon oil can be obtained in high yield. The components are mostly benzene, toluene and xylene isomers (o-, m- and p-xylene and ethylbenzene). These are called BTX and all have high utility value in the petrochemical industry. Therefore, it can be used as a raw material for chemicals after being separated into each component as necessary, and can be effectively used as a high-octane gasoline base material because of its component characteristics.

(実施例) 次に実施例に基づいて本発明を説明する。第1図は実
施例で用いた装置の断面図である。
(Example) Next, this invention is demonstrated based on an Example. FIG. 1 is a sectional view of the apparatus used in the examples.

約50倍の発泡倍率をもつ使用済発泡ポリスチレン容器
を小片に切断後約130℃の水蒸気で処理して脱泡し得ら
れた縮小片を約5mmに粉砕した。この粉砕物8kgを原料投
入口1から高さ約65cmの第1次熱分解槽2に入れ加熱溶
融した。10℃/分で昇温を続けると約310℃で熱分解に
伴うガス状生成物が発生しはじめこれが第2次熱分解槽
3に移動した。第1次熱分解槽の液温を350℃付近に保
持しLHSV0.9〜1.3で反応を継続した。尚加熱は下部に設
けたガスバーナーで行った。第2次熱分解槽3には粒径
約3mmのH型ZSM−5を約500g充填しておいた。第2次熱
分解槽3の上部から生成ガスを冷却器へ導き液状生成物
を取得した。
A used expanded polystyrene container having an expansion ratio of about 50 times was cut into small pieces, treated with steam at about 130 ° C. to remove air, and the resulting reduced pieces were crushed to about 5 mm. 8 kg of this pulverized product was put into the primary pyrolysis tank 2 having a height of about 65 cm from the raw material inlet 1 and heated and melted. When the temperature was raised at 10 ° C./minute, a gaseous product due to thermal decomposition started to be generated at about 310 ° C. and moved to the secondary thermal decomposition tank 3. The liquid temperature in the primary pyrolysis tank was maintained near 350 ° C and the reaction was continued at LHSV 0.9-1.3. The heating was performed with a gas burner provided at the bottom. The secondary pyrolysis tank 3 was filled with about 500 g of H type ZSM-5 having a particle size of about 3 mm. The produced gas was introduced into the cooler from the upper portion of the secondary thermal decomposition tank 3 to obtain a liquid product.

第1次熱分解槽2の液温が370℃になった時点で加熱
をやめた。第1次熱分解槽中に1部残渣が残っている状
態で上記と同様の操作を更に2回繰り返した。
The heating was stopped when the liquid temperature in the first thermal decomposition tank 2 reached 370 ° C. The same operation as above was repeated twice more in the state where a part of the residue remained in the primary thermal decomposition tank.

3回の操作の結果液状生成物の収率は91%であり、他
はガス分(約5%)と残渣(約4%)であった。
As a result of three operations, the yield of the liquid product was 91%, and the others were gas (about 5%) and residue (about 4%).

液状生成物を分析した結果、ベンゼン3%、トルエン
13%、主にエチルベンゼンからなるC8分50%、残りはそ
の他の芳香族炭化水素が主で一部パラフィン系炭化水素
であった。
As a result of analyzing the liquid product, benzene 3%, toluene
13%, 50% C8 consisting mainly of ethylbenzene, and the balance was mainly other aromatic hydrocarbons and partly paraffinic hydrocarbons.

【図面の簡単な説明】[Brief description of drawings]

第1図は本発明方法の実施に用いる装置の一例を示す断
面図である。
FIG. 1 is a sectional view showing an example of an apparatus used for carrying out the method of the present invention.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C07C 5/22 15/02 C08J 11/10 CET // C07B 61/00 300 (72)発明者 斉藤 喜代志 北海道札幌市豊平区月寒東二条17丁目2番 1号 工業技術院北海道工業開発試験所内 (72)発明者 福田 隆至 北海道札幌市豊平区月寒東二条17丁目2番 1号 工業技術院北海道工業開発試験所内 (72)発明者 鈴木 智 北海道札幌市豊平区月寒東二条17丁目2番 1号 工業技術院北海道工業開発試験所内 (72)発明者 阿部 政和 兵庫県宍粟郡安富町植木野88番地 株式会 社フジテック内 (72)発明者 弘田 寿夫 神奈川県横浜市旭区金が谷791―51 審査官 岩瀬 眞紀子 (56)参考文献 特開 昭51−89504(JP,A) 特開 昭60−49086(JP,A) 特開 昭49−41322(JP,A) 特開 昭50−5335(JP,A)─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location C07C 5/22 15/02 C08J 11/10 CET // C07B 61/00 300 (72) Inventor Saito Kiyoshi, 17-21, Nijokanto Nijo 17-2, Toyohira-ku, Sapporo, Hokkaido (72) Inventor, Takashi Fukuda 2-17-1, Tsukikanto Nijo 17-2, Toyohira-ku, Sapporo, Hokkaido In the laboratory (72) Satoshi Suzuki Satoshi Nijo 17-2-1, Tsukikanto, Toyohira-ku, Sapporo, Hokkaido Inside the Hokkaido Industrial Development Laboratory (72) Inventor Masakazu Abe 88 Uekino Ueno, Antomi-cho, Shishiwa-gun, Hyogo Inside Fujitec Co., Ltd. (72) Inventor Toshio Hirota 791-51 Kanagaya, Asahi-ku, Yokohama-shi, Kanagawa Examiner Makiko Iwase (56) References 51-89504 (JP, A) JP Akira 60-49086 (JP, A) JP Akira 49-41322 (JP, A) JP Akira 50-5335 (JP, A)

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】ポリスチレン廃棄物を溶融し、該溶融物を
加熱して液相で熱分解させ、発生した蒸気状生成物を1
〜12の範囲の拘束係数を持つゼオライト充填層中におい
て200〜400℃の範囲の温度で接触転化させ芳香族炭化水
素油を生成取得することを特徴とするポリスチレン廃棄
物の処理方法。
1. A polystyrene waste is melted, and the melt is heated to be thermally decomposed in a liquid phase.
A process for treating polystyrene waste, which comprises subjecting a zeolite packed bed having a constraint coefficient in the range of ~ 12 to catalytic conversion at a temperature in the range of 200 to 400 ° C to produce and obtain an aromatic hydrocarbon oil.
【請求項2】溶融液相熱分解温度が200〜450℃の範囲の
温度である請求項1記載の方法。
2. A process according to claim 1, wherein the melt liquid phase pyrolysis temperature is in the range of 200 to 450 ° C.
【請求項3】ゼオライトがZSM−5である請求項1記載
の方法。
3. The method according to claim 1, wherein the zeolite is ZSM-5.
【請求項4】ゼオライトの粒径が0.1〜10mmである請求
項1記載の方法。
4. The method according to claim 1, wherein the particle size of the zeolite is 0.1 to 10 mm.
【請求項5】ポリスチレン廃棄物が発泡ポリスチレンで
ある請求項1記載の方法。
5. The method according to claim 1, wherein the polystyrene waste is expanded polystyrene.
【請求項6】発泡ポリスチレン廃棄物を脱泡、粉砕の後
溶融する請求項5記載の方法。
6. The method according to claim 5, wherein the expanded polystyrene waste is defoamed, ground and then melted.
JP17801788A 1988-07-19 1988-07-19 Treatment method for polystyrene waste Expired - Lifetime JPH0832889B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP17801788A JPH0832889B2 (en) 1988-07-19 1988-07-19 Treatment method for polystyrene waste

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP17801788A JPH0832889B2 (en) 1988-07-19 1988-07-19 Treatment method for polystyrene waste

Publications (2)

Publication Number Publication Date
JPH0229492A JPH0229492A (en) 1990-01-31
JPH0832889B2 true JPH0832889B2 (en) 1996-03-29

Family

ID=16041114

Family Applications (1)

Application Number Title Priority Date Filing Date
JP17801788A Expired - Lifetime JPH0832889B2 (en) 1988-07-19 1988-07-19 Treatment method for polystyrene waste

Country Status (1)

Country Link
JP (1) JPH0832889B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH07100795B2 (en) * 1990-11-14 1995-11-01 フジリサイクル株式会社 Method for producing aromatic hydrocarbon oil from pyrolytic polyolefin plastic
DE4243063C2 (en) * 1991-12-20 1996-01-11 Toshiba Kawasaki Kk Method and device for the pyrolytic decomposition of plastic, in particular plastic waste
JP7725862B2 (en) * 2021-05-13 2025-08-20 東ソー株式会社 Catalyst for converting pyrolysis products of hydrocarbon-based plastics and method for producing lower hydrocarbons using the same

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3756942A (en) * 1972-05-17 1973-09-04 Mobil Oil Corp Process for the production of aromatic compounds
US3926782A (en) * 1973-02-09 1975-12-16 Mobil Oil Corp Hydrocarbon conversion
JPS5189504A (en) * 1975-02-05 1976-08-05
JPS6049086A (en) * 1983-08-26 1985-03-18 Sanesu:Kk Method for converting polyethylene based resin into oil and apparatus therefor

Also Published As

Publication number Publication date
JPH0229492A (en) 1990-01-31

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