JPH09263772A - Apparatus and method for treating waste plastic - Google Patents

Apparatus and method for treating waste plastic

Info

Publication number
JPH09263772A
JPH09263772A JP8075610A JP7561096A JPH09263772A JP H09263772 A JPH09263772 A JP H09263772A JP 8075610 A JP8075610 A JP 8075610A JP 7561096 A JP7561096 A JP 7561096A JP H09263772 A JPH09263772 A JP H09263772A
Authority
JP
Japan
Prior art keywords
water
waste plastic
reaction
solvent
heating
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.)
Granted
Application number
JP8075610A
Other languages
Japanese (ja)
Other versions
JP3419624B2 (en
Inventor
Yukishige Maezawa
幸繁 前沢
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.)
Toshiba Corp
Original Assignee
Toshiba Corp
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 Toshiba Corp filed Critical Toshiba Corp
Priority to JP07561096A priority Critical patent/JP3419624B2/en
Publication of JPH09263772A publication Critical patent/JPH09263772A/en
Application granted granted Critical
Publication of JP3419624B2 publication Critical patent/JP3419624B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To recover fuel oils or chemical raw materials from plastics not easily convertible into oils and wastes containing foreign matter, etc., at good efficiency by using an apparatus consisting of a specified pressure vessel, a specified heating means and a specified extracting means. SOLUTION: This apparatus for treating waste plastic comprizing of a pressure vessel 1 for mixing waste plastics containing at least C, H and other elements with water, a heating means 3 for heating the vessel 1 until the water is converted into supercritical water which can function as a solvent for the heat decomposition reaction of the waste plastics, and means 6 and 7 for extracting oils and solid chemical substances from the solvent. Desirably, an oxygen source such as oxygen, air or H2 O2 is mixed with waste plastics and water, Namely, the number of hydrogen bonds and the orientation force which determine the properties of water depend on the temperature. When the temperature is high, the effect of thermal movement preponderates. It can therefore dissolve nonpolar compounds at the critical point or higher and can further dissolve various gases. Therefore, water can function as a reaction solvent which accelerates the oxidation reaction of organic compounds.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は廃棄されたプラスチ
ック(明細書中では廃プラスチックと称する)を熱分解
して油として回収する方法に関し、さらに詳しくは、超
臨界水を用いて油化不適物を効率良く除去し、高品質な
油を回収する方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for thermally decomposing discarded plastic (referred to as waste plastic in the specification) and recovering it as oil. More specifically, it is an unsuitable material for oilization using supercritical water. The present invention relates to a method for efficiently removing oil and recovering high-quality oil.

【0002】[0002]

【従来の技術】廃プラスチックを乾留熱分解して燃料油
として再資源化する技術は、再生品の価値が比較的高い
ことなどから注目されている。しかしながら、塩化ビニ
ル樹脂、ホ゜リエチレンテレフタレートなどのC、H以
外の元素を含む油化不適物や紙などの異物を含む混合廃
プラスチックを熱分解すると、分解効率が低下する、ハ
ロゲン(塩素)を含む油が生成する、凝縮管が固形物に
より閉塞する、などの様々な問題点があった。
2. Description of the Related Art A technique for pyrolyzing waste plastics by pyrolysis to recycle them as fuel oil has attracted attention because the value of recycled products is relatively high. However, if pyrolysis of mixed waste plastics containing foreign substances such as vinyl chloride resin, polyethylene terephthalate and other elements other than C and H, and foreign substances such as paper, the decomposition efficiency decreases, and the oil containing halogen (chlorine) However, there are various problems, such as the formation of solids, the condensing tube is blocked by solid matter, and the like.

【0003】そこでアルカリと水を加えて加熱分解を行
うことによりハロゲンが生成油に混入することを防ぎ、
かつ凝縮管に無水フタル酸等の固形物が析出するのを防
ぐ試み(特開昭4-35334 号公報)を行ってきたが、この
方法では紙などによる分解効率の低下を防ぎきれず、ま
た熱分解残渣が多量に残るため減容化効率が悪いなどの
問題点があった。
Therefore, by adding alkali and water to carry out thermal decomposition, halogen is prevented from being mixed in the produced oil,
Attempts have also been made to prevent the precipitation of solid substances such as phthalic anhydride on the condensing tube (Japanese Patent Laid-Open No. 4-35334), but this method cannot prevent the degradation of decomposition efficiency due to paper, etc. Since a large amount of thermal decomposition residue remains, there is a problem that volume reduction efficiency is poor.

【0004】[0004]

【発明が解決しようとする課題】本発明は、油化困難な
プラスチックおよび異物等を含む混合プラスチック廃棄
物から良質な燃料油を回収すると共に固体の化学原料を
回収する方法を提供することを目的とする。
SUMMARY OF THE INVENTION It is an object of the present invention to provide a method for recovering a good quality fuel oil and a solid chemical raw material from a mixed plastic waste containing a difficult-to-oil plastic and a foreign substance. And

【0005】[0005]

【課題を解決するための手段】上記課題を解決するため
に、請求項1の発明は、少なくともC、H以外の元素を
含む廃プラスチックと水を混合する耐圧容器と、前記水
が超臨界水になるまで前記耐圧容器を加熱し前記廃プラ
スチックの熱分解反応溶媒にせしめる加熱手段と、前記
溶媒から油及び固体の化学物質を抽出する手段とを備え
ることを特徴とする廃プラスチックの処理装置を提供す
るものである。
In order to solve the above-mentioned problems, the invention of claim 1 provides a pressure vessel for mixing waste plastic containing at least an element other than C and H with water, and the water is supercritical water. A treatment device for waste plastic, comprising: heating means for heating the pressure resistant container until it becomes a solvent for thermal decomposition reaction of the waste plastic; and means for extracting oil and solid chemical substances from the solvent. It is provided.

【0006】また、請求項2の発明は、少なくともC、
H以外の元素を含む廃プラスチックと水を混合する第1
の工程と、前記水が超臨界水になるまで前記混合物を加
熱して前記廃プラスチックの反応溶媒にせしめる第2の
工程と、前記溶媒から油及び固体の化学物質を抽出する
第3の工程とを備えることを特徴とする廃プラスチック
の処理方法を提供するものである。
The invention according to claim 2 is at least C,
First, mixing waste plastic containing elements other than H with water
A second step of heating the mixture until the water becomes supercritical water to make it a reaction solvent of the waste plastic, and a third step of extracting oil and solid chemicals from the solvent. The present invention provides a method for treating waste plastic, which comprises:

【0007】また、請求項3の発明は、請求項2の発明
における第1の工程において、酸素、空気、過酸化水素
等の酸素源を前記廃プラスチックと水と共に混合するこ
とを特徴とする廃プラスチックの処理方法を提供するも
のである。
Further, the invention of claim 3 is characterized in that in the first step of the invention of claim 2, an oxygen source such as oxygen, air or hydrogen peroxide is mixed with the waste plastic and water. A method of processing plastics is provided.

【0008】また、請求項4の発明は、請求項2の発明
における第3の工程の後、抽出した前記固体の化学物質
をさらに加熱分解することを特徴とする廃プラスチック
の処理方法を提供するものである。
Further, the invention of claim 4 provides a method for treating waste plastic, characterized in that after the third step in the invention of claim 2, the extracted solid chemical substance is further decomposed by heating. It is a thing.

【0009】[0009]

【発明の実施の形態】本発明者らは、塩化ビニル樹脂や
テフロン等の少なくともC、H以外の元素であるCl等
のハロゲンを含む廃プラスチック、ポリエチレンテレフ
タレート等のO元素を含む廃プラスチック、紙(炭水化
物)などの異物を含む混合廃プラスチックの加熱分解油
化方法について鋭意検討した。その結果、水とともに加
熱して水の臨界点近傍の温度、圧力状態に保つことによ
って、第1に塩化ビニル樹脂等の脱ハロゲン分解を促進
できる事を見いだし、第2にホ゜リエチレンテレフタレ
ート等の縮重合(脱水重合)プラスチックを加水分解で
きることを見いだし、本発明を完成するに至った。
BEST MODE FOR CARRYING OUT THE INVENTION The present inventors have made a waste plastic containing halogen such as vinyl chloride resin and Teflon, such as Cl, which is an element other than C and H, waste plastic containing O element such as polyethylene terephthalate, and paper. We conducted a thorough study on the method of thermal decomposition and oilification of mixed waste plastic containing foreign substances such as (carbohydrate). As a result, it was found that by heating with water and maintaining the temperature and pressure in the vicinity of the critical point of water, the dehalogenation decomposition of vinyl chloride resin etc. can be promoted first, and secondly the polycondensation of polyethylene terephthalate etc. (Dehydration polymerization) It was found that the plastic can be hydrolyzed, and the present invention was completed.

【0010】さらに、場合によっては、水の他に酸素源
を加えて加熱すれば廃プラスチックの表面に付着してい
る紙などの異物を容易に酸化して除去できることも見い
だした。
Further, it has been found that, in some cases, by adding an oxygen source in addition to water and heating, foreign matter such as paper adhering to the surface of the waste plastic can be easily oxidized and removed.

【0011】本発明の上述した廃プラスチックの分解原
理は以下通りである。水は、分子量が小さい割に高い沸
点や臨界点を有し、比熱や潜熱も大きい。また誘電率も
大きいので多くの元素をイオンの形で溶解し、多くの極
性化合物も選択的に溶解するが、常温などの比較的低温
では、油を溶融することはない。ところが、水の性質を
規定する水素結合の数と配向力(分子内での電子の偏在
に基づく永久双極子間に働く力)は温度に依存し、高温
になると熱運動の影響が支配的となるので、臨界点(温
度374.2 ℃、圧力22.1MPa )以上の温度領域では一般に
「油」と言われているような非極性化合物が水に溶解可
能になる。さらに各種のガスとも相互溶解するので、例
えば酸素ガスと水と有機化合物とを適量混合して水の臨
界点付近の温度、圧力、密度条件を満たすように操作す
ると、水はその有機化合物の酸化反応を促進する反応溶
媒の働きをする。本発明では、この臨界水の性質を応用
した。
The decomposition principle of the above-mentioned waste plastic of the present invention is as follows. Water has a high boiling point and a critical point despite its small molecular weight, and has a large specific heat and latent heat. Further, since it has a large dielectric constant, it dissolves many elements in the form of ions and selectively dissolves many polar compounds, but it does not melt oil at relatively low temperatures such as room temperature. However, the number of hydrogen bonds and the orientation force (the force that acts between permanent dipoles due to the uneven distribution of electrons in the molecule) that determine the properties of water depend on temperature, and the effect of thermal motion is dominant at high temperatures. Therefore, in the temperature range above the critical point (temperature 374.2 ° C, pressure 22.1MPa), non-polar compounds generally called "oils" can be dissolved in water. Furthermore, since it also dissolves with various gases, if, for example, oxygen gas, water and an organic compound are mixed in appropriate amounts and operated so as to satisfy the temperature, pressure and density conditions near the critical point of water, water will oxidize the organic compound. It acts as a reaction solvent that accelerates the reaction. In the present invention, this property of critical water is applied.

【0012】しかしながらこれは有機化合物が流体の形
で水に溶けていることが条件であるので、それ以外の場
合には、プラスチックなどの固体の場合には表面でのみ
反応が進行する。従って、表面に紙などの異物が付着し
ている廃プラスチック原料については、加える酸素量を
調整し、かつ反応時間を調整することにより表面の異物
除去のみを行い、プラスチックの分解は抑制するといっ
た応用が可能になる。
However, this is a condition that the organic compound is dissolved in water in the form of fluid, and in other cases, in the case of solid such as plastic, the reaction proceeds only on the surface. Therefore, for waste plastic raw materials that have foreign matter such as paper adhered to the surface, only the foreign matter on the surface is removed by adjusting the amount of oxygen added and the reaction time, and the decomposition of plastic is suppressed. Will be possible.

【0013】廃プラスチック中の各樹脂は以下のように
反応が進む。まず、塩化ビニル樹脂は通常300 ℃以下で
分解して塩化水素を脱離し、残りの分子鎖は隣接分子同
士で架橋結合する。従って加熱処理を行っても油状物質
はほとんど回収されない。そればかりか、実用に供され
る塩化ビニル樹脂には用途によって数十%も可塑剤が添
加されている場合があって、この可塑剤の熱分解により
無水フタル 酸などの固形物が生成するので回収が難しいと
いう問題がある。さらに可塑剤の熱分解によりアルコー
ル系およびオレフィン系の油状物質が得られるが、この
オレフィンは塩化水素と付加反応が起こり易いので塩素
化有機物が生成し油に混合するので、生成油を燃料とし
て使用する場合に燃焼排ガスの処理が必要になり、良質
の燃料油が生成できないという弊害がある。そこで超臨
界水中で加熱処理を行うと、塩化水素とフタル 酸とアルコ
ール系に分解され、塩化水素と有機化合物との付加反応
の問題は解決する。さらに処理後に温度を室温付近まで
下げると、塩化水素は水溶液として、フタル酸は沈澱固
体として、アルコール系は油状物として分離するので、
それぞれを容易に回収できる。
The reaction of each resin in the waste plastic proceeds as follows. First, vinyl chloride resin is usually decomposed at 300 ° C or lower to desorb hydrogen chloride, and the remaining molecular chains cross-link with adjacent molecules. Therefore, the oily substance is hardly recovered even if the heat treatment is performed. Not only that, but some vinyl chloride resins used for practical purposes may contain tens of percent of plasticizer depending on the application, and solid substances such as phthalic anhydride are generated by the thermal decomposition of this plasticizer. There is a problem that collection is difficult. Further, alcohol-based and olefin-based oily substances are obtained by the thermal decomposition of the plasticizer.Since this olefin easily undergoes an addition reaction with hydrogen chloride, chlorinated organic substances are produced and mixed with the oil, so the produced oil is used as a fuel. In this case, it is necessary to treat the combustion exhaust gas, which causes a problem that high quality fuel oil cannot be produced. When heat treatment is performed in supercritical water, hydrogen chloride, phthalic acid, and alcohols are decomposed, and the problem of addition reaction between hydrogen chloride and organic compounds is solved. When the temperature is further lowered to around room temperature after the treatment, hydrogen chloride separates as an aqueous solution, phthalic acid separates as a precipitated solid, and an alcohol system separates as an oil.
Each can be easily recovered.

【0014】また、ホ゜リエチレンテレフタレートはテ
レフタル酸とエチレンク゛リコールとを交互に縮重合
(脱水)して製造される。これを熱分解しても油状物質
は得られず、フタル酸系あるいはエステル系の固形物が
得られるのみである。そこで、超臨界水中で処理した場
合にはテレフタル酸とエチレンク゛リコールとに完全に
分解される。処理後に室温に戻すとテレフタル酸は沈澱
固体として、エチレンク゛リコールは水溶液としてそれ
ぞれ回収可能である。
Polyethylene terephthalate is produced by alternately polycondensing (dehydrating) terephthalic acid and ethylene glycol. Even if this is thermally decomposed, an oily substance is not obtained, but only a phthalic acid-based or ester-based solid substance is obtained. Therefore, when treated in supercritical water, it is completely decomposed into terephthalic acid and ethylene glycol. When the temperature is returned to room temperature after the treatment, terephthalic acid can be recovered as a precipitated solid, and ethylene glycol can be recovered as an aqueous solution.

【0015】さらに、紙はセルロースなどの天然高分子
化合物から製造される。加熱処理を行った場合には分解
して水を生成し、炭素質の残渣が残る。プラスチックと
共に加熱をした場合、紙自身の分解にエネルギーが必要
となるので処理時間が長くなり、経済性が低下する。さ
らにアルカリを加えて塩化ビニル樹脂からの有機塩素化
合物の生成を防止しようとする場合において、紙が混在
していると効率が悪くなるという実験データが得られて
いる。そこで、超臨界水中で酸素と共に加熱した場合に
は完全に分解して水と二酸化炭素とを生成する。
Further, the paper is manufactured from natural polymer compounds such as cellulose. When heat-treated, it decomposes to produce water, leaving a carbonaceous residue. When heated together with plastic, energy is required to decompose the paper itself, resulting in a long processing time and reduced economic efficiency. Further, when trying to prevent the formation of an organic chlorine compound from a vinyl chloride resin by adding an alkali, it has been obtained experimental data that the efficiency is deteriorated when paper is mixed. Therefore, when heated together with oxygen in supercritical water, it is completely decomposed to generate water and carbon dioxide.

【0016】またさらに、ホ゜リオレフィン系プラスチ
ック、すなわちポリエチレン、ポリプロピレン、ポリス
チレンは炭素と水素のみで構成される高分子化合物であ
り、熱分解により高い割合で油状物質を生成する。超臨
界水中で酸素を加えないで処理した場合には、ポリスチ
レンは分解温度が低いので分解して油状物質を生成し、
他の2種類はほとんど反応しない。処理後に室温まで冷
やすとポリエチレンおよびポリプロピレンは比重が小さ
いので水に浮遊した状態で回収される。
Furthermore, polyolefin plastics, that is, polyethylene, polypropylene, and polystyrene are polymer compounds composed of only carbon and hydrogen, and produce a high proportion of oily substance by thermal decomposition. When treated in supercritical water without adding oxygen, polystyrene has a low decomposition temperature and thus decomposes to produce an oily substance.
The other two types hardly react. When cooled to room temperature after the treatment, polyethylene and polypropylene have a small specific gravity and are recovered in a state of being suspended in water.

【0017】実際に、本発明を実施するには図1示した
廃プラスチックの処理装置を使用する。1は、廃プラス
チック原料を仕込む耐圧容器のオートクレーブ、2はオ
ートクレーブ内の圧力を低減するための真空ポンプ、3
は溶融塩浴であり、その外周には前記水が超臨界水にな
るまでオートクレーブ1を加熱し廃プラスチックの熱分
解反応溶媒にせしめるための加熱手段としてのヒーター
10が取り付けられている。このヒーター10は抵抗加
熱であるが、誘導加熱によるもの等でも良い。4はオー
トクレーブ1を冷却するための水槽、5はオートクレー
ブに酸素を供給するための酸素ボンベ、6はオートクレ
ーブから蒸発させたガスを液体に戻すための凝縮器、7
は凝縮器6で得られた油などの液状物質及び場合によっ
ては固体の化学物質を回収するための回収容器である。
また、凝縮器6及び回収容器7は、油及び固体の化学物
質を抽出する手段、8は凝縮器の内部に通す冷媒であ
る。また、オートクレーブ1、真空ポンプ2、凝縮器6
等を結ぶ線は、ガス通路のラインを示している。
In practice, the waste plastic processing apparatus shown in FIG. 1 is used to carry out the present invention. 1 is a pressure-resistant autoclave for charging waste plastic raw materials, 2 is a vacuum pump for reducing the pressure in the autoclave, 3
Is a molten salt bath, and a heater 10 as a heating means for heating the autoclave 1 until the water becomes supercritical water and causing it to become a solvent for thermal decomposition reaction of waste plastic is attached to the outer periphery thereof. The heater 10 is resistance heating, but may be induction heating or the like. 4 is a water tank for cooling the autoclave 1, 5 is an oxygen cylinder for supplying oxygen to the autoclave, 6 is a condenser for returning the gas evaporated from the autoclave to a liquid, 7
Is a recovery container for recovering a liquid substance such as oil obtained in the condenser 6 and a solid chemical substance in some cases.
Further, the condenser 6 and the recovery container 7 are means for extracting oil and solid chemical substances, and 8 is a refrigerant passed through the inside of the condenser. Also, autoclave 1, vacuum pump 2, condenser 6
The line connecting the lines and the like indicates the line of the gas passage.

【0018】[0018]

【実施例】【Example】

(実施例1)以下の実施例では、図1に示した廃プラス
チック処理装置を使用して廃プラスチックを燃料或いは
化学原料として使用できる油等の有機物、化学原料とし
て使用できる化学製品等を得る。
(Embodiment 1) In the following embodiment, the waste plastic processing apparatus shown in FIG. 1 is used to obtain an organic substance such as oil which can use waste plastic as a fuel or a chemical raw material, a chemical product which can be used as a chemical raw material, and the like.

【0019】先ず、混合廃プラスチック100 重量部(軟
質塩化ビニル樹脂製電線被覆材:40、ホ゜リエチレンテ
レフタレート製飲料ホ゛トル:20 、発泡スチロールの食
品トレイ:20、ホ゜リエチレン製買い物袋:20 重量部)
と水200 重量部とを常温においてオートクレーブ1に封
入し、真空ポンプ2を用いて空気を除去した。ここで
は、常温における水の蒸気圧:3.5kPa まで真空排気し
た。この目的は酸素の影響を排除することにあるが、酸
素の存在は反応促進の面でプラスであるので実際には真
空排気はしなくても良い。3.5kPa以下にすると投入した
水が蒸発してしまう。従って3.5kPa~101kPa の範囲であ
ることが好ましい。
First, 100 parts by weight of mixed waste plastic (soft vinyl chloride resin wire coating material: 40, polyethylene terephthalate beverage bottle: 20, foam polystyrene food tray: 20, polyethylene shopping bag: 20 parts by weight)
Then, 200 parts by weight of water and 200 parts by weight of water were sealed in the autoclave 1 at room temperature, and the air was removed using the vacuum pump 2. Here, the evacuation was performed to the vapor pressure of water at room temperature: 3.5 kPa. The purpose of this is to eliminate the influence of oxygen, but the presence of oxygen is positive in terms of accelerating the reaction, so that evacuation is not actually required. If the pressure is less than 3.5kPa, the added water will evaporate. Therefore, it is preferably in the range of 3.5 kPa to 101 kPa.

【0020】次にその容器を溶融塩浴3に浸して375 ℃
まで加熱した。この際の溶融塩浴3の熱媒体にはSuper-
Saltと呼ばれる3 元系溶融塩を用いたが、375 ℃で液体
であり開放系で使用できるもの例えば、亜硝酸カリウム
塩や亜硝酸ナトリウム塩等の混合塩あるいは金属ナトリ
ウム等であっても良い。また、加熱する温度は、超臨界
水の反応溶媒特性をできる限り発揮させる観点から370
℃~400℃の範囲であることが望ましい。
Next, the container is immersed in a molten salt bath 3 and 375 ° C.
Heated up. At this time, the heat medium of the molten salt bath 3 is Super-
A ternary molten salt called Salt was used, but it is liquid at 375 ° C. and can be used in an open system, for example, a mixed salt of potassium nitrite salt, sodium nitrite salt or the like, or metallic sodium may be used. The heating temperature is 370 from the viewpoint of exerting the reaction solvent characteristics of supercritical water as much as possible.
It is desirable to be in the range of ℃ to 400 ℃.

【0021】ついで、375 ℃の設定温度到達後、30分間
反応させてから容器を取り出し、水槽4に入れて急冷し
た。この際の、反応時間は、塩化ビニル樹脂の脱塩素反
応、可塑剤の分解反応、ホ゜リエチレンテレフタレート
の加水分解反応ができれば良く、5分から1時間の間で
あれば充分な反応が得られる。この結果、オートクレー
ブ1内部の圧力は温度上昇と共に上昇し、最終的に20MP
a 以上となった。反応生成物はスチレンを主体とする黄
色透明の油状液体、水(塩酸)に浮遊する固体、約6%濃
度の塩酸、そして塩酸に沈澱する固体物質であった。分
析の結果、浮遊固体はホ゜リエチレン、沈澱固体はフタ
ル酸、テレフタル酸、炭素質残渣の混合物であることが
わかった。ガスはほとんど生成しなかった。物質収支を
まとめると以下の通りである。
Then, after reaching the set temperature of 375 ° C., the reaction was carried out for 30 minutes, the container was taken out, placed in a water tank 4 and rapidly cooled. At this time, the reaction time is sufficient if the dechlorination reaction of the vinyl chloride resin, the decomposition reaction of the plasticizer and the hydrolysis reaction of polyethylene terephthalate can be carried out, and a sufficient reaction can be obtained if it is between 5 minutes and 1 hour. As a result, the pressure inside the autoclave 1 rises as the temperature rises and finally reaches 20MP.
It was over a. The reaction product was a yellow transparent oily liquid mainly composed of styrene, a solid suspended in water (hydrochloric acid), hydrochloric acid having a concentration of about 6%, and a solid substance precipitated in hydrochloric acid. As a result of the analysis, it was found that the suspended solids were polyethylene and the precipitated solids were a mixture of phthalic acid, terephthalic acid and carbonaceous residue. Little gas was produced. The material balance is summarized as follows.

【0022】(1) 反応前:廃プラスチック100 、水200 (2) 反応後:油状物33、浮遊固体20、水溶液213 、沈澱
固体34 これらの反応生成物は容易に分離回収できるので無駄の
無いリサイクルが可能となる。すなわち、油状物は燃料
油として利用でき、浮遊固体はさらに高温で熱分解すれ
ば燃料油化でき、水溶液は再度プラスチックを処理する
ための添加用として再利用でき、さらに沈澱固体は加熱
してフタル酸類を溶融し、炭素質残渣と分離することに
より化学原料として回収できる。
(1) Before reaction: waste plastic 100, water 200 (2) After reaction: oily substance 33, floating solid 20, aqueous solution 213, precipitated solid 34 Since these reaction products can be easily separated and collected, there is no waste. It can be recycled. That is, oil can be used as fuel oil, suspended solids can be fuel oil if pyrolyzed at higher temperature, aqueous solution can be reused for addition to process plastics again, and precipitated solids can be heated to phthalate. It can be recovered as a chemical raw material by melting the acid and separating it from the carbonaceous residue.

【0023】(比較例1)実施例1と同じ装置、サンプ
ルを用い、水を加えないということを除いて処理条件な
ど全く同様の方法で廃プラスチック原料を処理した。
(Comparative Example 1) Using the same apparatus and sample as in Example 1, the waste plastic raw material was treated in exactly the same manner as in the treatment conditions except that water was not added.

【0024】その結果、水槽4に入れて急冷した後のオ
ートクレーブ内部の圧力は10MPa を越えなかった。反応
生成物は塩化水素を主体とするガス、粘着性のあるガム
状物質および固体であった。ガム状物質はスチレンの2
量体が主成分であり、単量体や3量体も含まれていた。
固形物はホ゜リエチレン、エステル類、フタル酸類、炭
素質残渣の混合物であった。物質収支は (1) 反応前:廃プラスチック原料100 (2) 反応後:ガス12、ガム状物+固形物88 である。この反応ではポリ塩化ビニルの脱塩素分解、可
塑剤の分解、ホ゜リスチレンの分解、ホ゜リエチレンテ
レフタレートの分解が確認されたものの、生成物の分離
回収は困難であり、従ってリサイクルが困難であるばか
りでなく、その固形物をさらに高温で熱分解させた場合
にはフタル酸等による配管閉塞が問題となった。
As a result, the pressure inside the autoclave after being placed in the water tank 4 and rapidly cooled did not exceed 10 MPa. The reaction products were hydrogen chloride-based gas, viscous gums and solids. Gum-like substance is styrene 2
The main component was the monomer, and the monomer and trimer were also included.
The solid was a mixture of polyethylene, esters, phthalic acids, and carbonaceous residue. The material balance is (1) before the reaction: waste plastic raw material 100 (2) after the reaction: gas 12, gum-like substance + solid substance 88. Although dechlorination decomposition of polyvinyl chloride, decomposition of plasticizer, decomposition of polystyrene, and decomposition of poly (ethylene terephthalate) were confirmed in this reaction, it is difficult to separate and recover the product, and therefore it is not only difficult to recycle the product. When the solid matter was pyrolyzed at a higher temperature, there was a problem of pipe clogging due to phthalic acid or the like.

【0025】(実施例2)実施例1と同じ装置、サンプ
ルを用い、ただし真空排気後に酸素ガスをボンベ5から
1MPa加えてから加熱を行った。ここであえて記載し
ない条件などは実施例1と同様である。
(Example 2) The same apparatus and sample as in Example 1 were used, but after evacuation, heating was performed after adding 1 MPa of oxygen gas from the cylinder 5 to the gas. Conditions and the like not described here are the same as those in the first embodiment.

【0026】設定温度到達後、1分程度で取り出し、急
冷した。その結果、反応生成物の性状は実施例1とほぼ
同じであるが、二酸化炭素を主とするガスがあった。物
質収支は、 (1) 反応前:プラスチック100 、水200 、酸素ガス14 (2) 反応後:ガス10、油状物30、浮遊固体20、水溶液22
1 、沈澱固体33 であった。この反応では部分的に酸化反応が起こったた
め短い反応時間でも十分に分解が進み、実施例1と同じ
くリサイクル可能な生成物が得られた。但し、反応時間
は、脱塩素反応と加水分解反応および部分酸化反応が行
われれば良く、高分子の熱分解まで行われる必要はない
ので、30秒~10 分の範囲が望ましい。この結果得られた
生成物の内、油状物、浮遊固体、水溶液、沈澱固体の内
容は以下の通りである。
After reaching the set temperature, it was taken out in about 1 minute and rapidly cooled. As a result, the properties of the reaction product were almost the same as in Example 1, but there was a gas containing mainly carbon dioxide. Mass balance is (1) before reaction: plastic 100, water 200, oxygen gas 14 (2) after reaction: gas 10, oil 30, floating solids 20, aqueous solution 22
1 and the precipitated solid was 33. Since a partial oxidation reaction occurred in this reaction, decomposition proceeded sufficiently even in a short reaction time, and a recyclable product was obtained as in Example 1. However, the reaction time is preferably in the range of 30 seconds to 10 minutes, as long as the dechlorination reaction, the hydrolysis reaction and the partial oxidation reaction are performed, and it is not necessary to perform the thermal decomposition of the polymer. Among the products obtained as a result, the contents of oil, suspended solids, aqueous solution, and precipitated solids are as follows.

【0027】(1) ガスは、二酸化炭素であり、(2) 油状
物は、スチレンモノマーを主成分とする炭化水素油、
(3) 浮遊固体は、ホ゜リエチレン、(4) 水溶液は、約6%
濃度の塩酸、(5) 固形物は、フタル酸類および炭素質残
渣の混合物であった。
(1) The gas is carbon dioxide, (2) the oil is a hydrocarbon oil containing styrene monomer as a main component,
(3) Floating solids are polyethylene, (4) Aqueous solution is about 6%
The concentration of hydrochloric acid, (5) solids, was a mixture of phthalic acids and carbonaceous residues.

【0028】(実施例3)実施例1と同じ装置、サンプ
ルを用い、加熱分解を30分間行った後、溶融塩浴からオ
ートクレーブを取り出さずに内部流体を凝縮器6を通し
て回収容器7に導くことによりオートクレーブの内圧を
大気圧まで落とし、さらに溶融塩浴で500℃まで加熱し
た。
(Embodiment 3) Using the same apparatus and sample as in Embodiment 1, after carrying out thermal decomposition for 30 minutes, the internal fluid is introduced into the recovery container 7 through the condenser 6 without taking out the autoclave from the molten salt bath. The internal pressure of the autoclave was lowered to atmospheric pressure by, and further heated to 500 ° C. in a molten salt bath.

【0029】この結果、回収容器には黄色透明の油状液
体と塩酸が、凝縮器にはフタル 酸類が、オートクレーブに
は炭素質残渣がそれぞれ回収された。物質収支をまとめ
ると次の通りである。
As a result, a yellow transparent oily liquid and hydrochloric acid were recovered in the recovery container, phthalic acids were recovered in the condenser, and carbonaceous residue was recovered in the autoclave. The material balance is summarized as follows.

【0030】(1) 反応前:廃プラスチック100 、水200 (2) 反応後:ガス2 、油状物50、水溶液213 、付着物2
6、残渣9 であった。このうち各生成物の内容は以下の通りであっ
た。
(1) Before reaction: waste plastic 100, water 200 (2) After reaction: gas 2, oil 50, aqueous solution 213, deposit 2
6 and residue 9. The contents of each product were as follows.

【0031】(1) ガスは、低級炭化水素であり、(2) 油
状物は、オレフィンを主体とする炭化水素油、(3) 水溶
液は、約6%濃度の塩酸、(4) 付着物は、フタル酸類、
(5) 残渣は、炭素質の残渣であった。
(1) The gas is a lower hydrocarbon, (2) the oil is a hydrocarbon oil mainly containing olefins, (3) the aqueous solution is hydrochloric acid having a concentration of about 6%, and (4) the deposit is , Phthalates,
(5) The residue was a carbonaceous residue.

【0032】この結果、分解反応は完全に終了し、多量
の燃料油が得られた。水溶液は再度プラスチックを分解
するときの添加剤として利用可能であり、塩化水素濃度
が高くなれば濃塩酸としての利用も可能である。付着物
(フタル酸類)は化学原料に利用可能である。
As a result, the decomposition reaction was completed, and a large amount of fuel oil was obtained. The aqueous solution can be used as an additive when decomposing the plastic again, and can also be used as concentrated hydrochloric acid if the concentration of hydrogen chloride increases. The deposits (phthalic acids) can be used as chemical raw materials.

【0033】[0033]

【発明の効果】以上説明したように、本発明によれば油
化不適プラスチックや異物を含む混合廃プラスチックか
ら燃料油或いは化学原料として高品質な油、有機化合物
を得ることができ、さらにフタル酸類などの化学原料も
容易に分別回収できるので効率的なリサイクルが可能と
なる。
As described above, according to the present invention, it is possible to obtain high-quality oils and organic compounds as fuel oils or chemical raw materials from plastics unsuitable for oiling and mixed waste plastics containing foreign substances. Since chemical raw materials such as can be easily separated and collected, efficient recycling becomes possible.

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

【図1】 本発明を実施するのに好適な油化処理装置の
構成を示す模式図である
FIG. 1 is a schematic diagram showing a configuration of an oil treatment device suitable for carrying out the present invention.

【符号の説明】[Explanation of symbols]

1:オートクレーブ 2:真空ポンプ 3:溶融塩浴 4:水槽 5:酸素ガスボンベ 6:凝縮器 7:回収容器 8:冷媒 10:ヒーター 1: Autoclave 2: Vacuum pump 3: Molten salt bath 4: Water tank 5: Oxygen gas cylinder 6: Condenser 7: Recovery container 8: Refrigerant 10: Heater

Claims (4)

【特許請求の範囲】[Claims] 【請求項1】少なくともC、H以外の元素を含む廃プラ
スチックと水を混合する耐圧容器と、前記水が超臨界水
になるまで前記耐圧容器を加熱し前記廃プラスチックの
熱分解反応溶媒にせしめる加熱手段と、前記溶媒から油
及び固体の化学物質を抽出する手段とを備えることを特
徴とする廃プラスチックの処理装置。
1. A pressure-resistant container for mixing waste plastic containing at least an element other than C and H with water, and heating the pressure-resistant container until the water becomes supercritical water so as to be used as a solvent for the thermal decomposition reaction of the waste plastic. An apparatus for treating waste plastic, comprising: heating means; and means for extracting oil and solid chemical substances from the solvent.
【請求項2】少なくともC、H以外の元素を含む廃プラ
スチックと水を混合する第1の工程と、前記水が超臨界
水になるまで前記混合物を加熱して前記廃プラスチック
の反応溶媒にせしめる第2 の工程と、前記溶媒から油及
び固体の化学物質を抽出する第3の工程とを備えること
を特徴とする廃プラスチックの処理方法。
2. A first step of mixing waste plastic containing at least an element other than C and H with water, and heating the mixture until the water becomes supercritical water to become a reaction solvent for the waste plastic. A method for treating waste plastic, comprising a second step and a third step of extracting oil and solid chemical substances from the solvent.
【請求項3】前記第1の工程において、酸素、空気、過
酸化水素等の酸素源を前記廃プラスチックと水と共に混
合することを特徴とする請求項2に記載の廃プラスチッ
クの処理方法。
3. The method for treating waste plastic according to claim 2, wherein an oxygen source such as oxygen, air, or hydrogen peroxide is mixed with the waste plastic together with water in the first step.
【請求項4】前記第3の工程の後、抽出した前記固体の
化学物質をさらに加熱分解することを特徴とする請求項
2に記載の廃プラスチックの処理方法。
4. The method for treating waste plastic according to claim 2, wherein after the third step, the extracted solid chemical substance is further decomposed by heating.
JP07561096A 1996-03-29 1996-03-29 Waste plastic treatment equipment and treatment method Expired - Fee Related JP3419624B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP07561096A JP3419624B2 (en) 1996-03-29 1996-03-29 Waste plastic treatment equipment and treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP07561096A JP3419624B2 (en) 1996-03-29 1996-03-29 Waste plastic treatment equipment and treatment method

Publications (2)

Publication Number Publication Date
JPH09263772A true JPH09263772A (en) 1997-10-07
JP3419624B2 JP3419624B2 (en) 2003-06-23

Family

ID=13581161

Family Applications (1)

Application Number Title Priority Date Filing Date
JP07561096A Expired - Fee Related JP3419624B2 (en) 1996-03-29 1996-03-29 Waste plastic treatment equipment and treatment method

Country Status (1)

Country Link
JP (1) JP3419624B2 (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0872536A3 (en) * 1997-04-16 1999-05-06 Tohoku Electric Power Co., Inc. Process and system for converting plastics waste into oil
JPH11315162A (en) * 1998-03-02 1999-11-16 Toshiba Corp Heat treatment and heat treating system
JP2007316903A (en) * 2006-05-25 2007-12-06 Blest:Kk Recycle system for plastic product
JP2008030040A (en) * 2007-08-20 2008-02-14 Toshiba Corp Waste treatment method
CN103602816A (en) * 2013-11-12 2014-02-26 福建工程学院 Method for recycling waste printed circuit board

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0872536A3 (en) * 1997-04-16 1999-05-06 Tohoku Electric Power Co., Inc. Process and system for converting plastics waste into oil
US6107532A (en) * 1997-04-16 2000-08-22 Tohoku Electric Power Co., Inc. Process and system for converting plastics waste into oil
JPH11315162A (en) * 1998-03-02 1999-11-16 Toshiba Corp Heat treatment and heat treating system
JP2007316903A (en) * 2006-05-25 2007-12-06 Blest:Kk Recycle system for plastic product
JP2008030040A (en) * 2007-08-20 2008-02-14 Toshiba Corp Waste treatment method
CN103602816A (en) * 2013-11-12 2014-02-26 福建工程学院 Method for recycling waste printed circuit board
CN103602816B (en) * 2013-11-12 2015-12-09 福建工程学院 A kind of recovery and treatment method of discarded printed circuit board

Also Published As

Publication number Publication date
JP3419624B2 (en) 2003-06-23

Similar Documents

Publication Publication Date Title
US5413681A (en) Process for the recovery of terephthalic acid and ethylene glycol from poly(ethylene terephthalate)
JP6050834B2 (en) Separating and collecting plastic composite waste
JP5883585B2 (en) Separation and recovery method for composite plastic waste and universal type separation and recovery device used therefor
JP5069231B2 (en) How to recycle expanded polystyrene
US10472486B2 (en) Process for the treatment of a composition comprising thermoplastics
US5064487A (en) Method of cleaning of components to which polymers are bonded
WO2004041917A1 (en) Depolymerization process
JP3419624B2 (en) Waste plastic treatment equipment and treatment method
JPH09324181A (en) Liquefaction of plastic waste material and apparatus therefor
WO1994016032A1 (en) Improved method of cracking polymeric materials catalyzed by copper
JP4848506B2 (en) Plastic disassembly method
KR100635622B1 (en) Method for cleaning and decontaminating polyesters
JP4768920B2 (en) Thermal decomposition of waste plastic
US20100305223A1 (en) Process for recovering a polymer from a solution
JP2005154525A (en) Method and apparatus for treating polystyrene-based resin composition
US10479875B2 (en) Process for the treatment of a composition comprising thermoplastics
JP2001192495A (en) Method for reprocessing cross-linked polyolefin
JP2009084543A (en) Waste plastic liquefying apparatus
JPH1149889A (en) Treatment of waste ion-exchange resin
JP2000302707A (en) Thermal decomposition of polyethylene terephthalate
JP2001520684A (en) Partial oxidation of waste plastic material
JP4067477B2 (en) Method for decomposing resin components
JPH11323006A (en) Decomposition of plastic multilayer molded product and oiling of polyaddition polymer solid product
JPH11323002A (en) Treatment of plastic waste material
JP4648213B2 (en) Plasticizer recovery method

Legal Events

Date Code Title Description
LAPS Cancellation because of no payment of annual fees