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JP5457625B2 - Recycling method of polylactic acid resin - Google Patents
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JP5457625B2 - Recycling method of polylactic acid resin - Google Patents

Recycling method of polylactic acid resin Download PDF

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JP5457625B2
JP5457625B2 JP2007014951A JP2007014951A JP5457625B2 JP 5457625 B2 JP5457625 B2 JP 5457625B2 JP 2007014951 A JP2007014951 A JP 2007014951A JP 2007014951 A JP2007014951 A JP 2007014951A JP 5457625 B2 JP5457625 B2 JP 5457625B2
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polylactic acid
acid resin
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JP2008179713A (en
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晃一 中村
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Nitto Denko Corp
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Priority to EP20070737841 priority patent/EP2022818B1/en
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    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J11/00Recovery or working-up of waste materials
    • C08J11/04Recovery or working-up of waste materials of polymers
    • C08J11/10Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation
    • C08J11/14Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation by treatment with steam or water
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J2367/00Characterised by the use of polyesters obtained by reactions forming a carboxylic ester link in the main chain; Derivatives of such polymers
    • C08J2367/04Polyesters derived from hydroxy carboxylic acids, e.g. lactones
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling

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Description

本発明は、ポリ乳酸樹脂を加水分解処理して乳酸に再生させる方法において、加水分解処理時間を大幅に短縮する方法に関する。 The present invention relates to a method for significantly shortening the hydrolysis treatment time in a method for regenerating lactic acid by hydrolyzing a polylactic acid resin.

自然界で微生物に与えられた、驚くべき能力の一つは、高分子有機化合物の加水分解能力である。微生物はこの反応を常温・常圧という全く自然の環境の中で、いとも簡単にやってのけ、有機物連鎖を分断して分子量を小さくしていく。この方法は何億年という長い時間をかけて微生物が獲得・改良してきた方法であり、この方法は通常「酵素による加水分解法」と言われている。   One of the surprising abilities given to microorganisms in nature is the ability to hydrolyze macromolecular organic compounds. Microorganisms can carry out this reaction in a completely natural environment at normal temperature and pressure, breaking down the organic chain and reducing the molecular weight. This method has been acquired and improved by microorganisms over a long time of hundreds of millions of years, and this method is usually referred to as an “enzymatic hydrolysis method”.

この酵素による加水分解法は、現在のところ我々人間が知能の総力を結集してもその真似をすることは難しい。この「酵素による加水分解法」による分解物、すなわち、微生物によって分解された結果物は、他の全ての生物にとって有用な成分となり、そのまま吸収・組織化されていく基本要素となっている。   At present, it is difficult to imitate the hydrolysis method using this enzyme even if we gather all the power of intelligence. A degradation product by this “enzymatic hydrolysis method”, that is, a result of degradation by microorganisms, becomes a useful component for all other organisms, and is a basic element that is absorbed and organized as it is.

酵素による加水分解法は、現段階では人間が真似をすることが難しいが、酵素による加水分解法以外の方法を用いて同じ結果を得る方法が1つある。その方法は「物理エネルギーを用いた加水分解法」である。この方法は、元々何千メートルもの深海の底に地球内部より吹き出して来る熱水による分解の現象と類似した方法である。この方法によれば、温度・圧力がともに遙かに水の臨界(375℃,220気圧)を超えた状態で反応が進行し、反応の結果、有機化合物の加水分解をはじめ、金属を含めた多くの物質(化合物)を分解し、物質の構成成分を溶出させることができる。   Although it is difficult for humans to imitate the enzymatic hydrolysis method at this stage, there is one method for obtaining the same result by using a method other than the enzymatic hydrolysis method. The method is a “hydrolysis method using physical energy”. This method is similar to the phenomenon of decomposition by hot water that originally blows from the inside of the earth to the bottom of thousands of meters deep sea. According to this method, the reaction proceeds with both the temperature and pressure far exceeding the criticality of water (375 ° C., 220 atm). As a result of the reaction, hydrolysis of organic compounds and metals were included. Many substances (compounds) can be decomposed and the constituents of the substances can be eluted.

このような高圧と高温の状態を、より現実的な状態(より常温に近い状態)にもって来たときにも加水分解は可能である。とりわけ有機物は100℃、1気圧を越えると、時間の積で徐々に加水分解していく。そして、このような「物理エネルギーを用いた加水分解法」の結果は、微生物が行った「酵素による加水分解法」の結果と同等になる。この原理を利用して生分解性プラスチックを分解する方法として、例えば特許文献1には、超臨界熱水処理を利用する方法、特許文献2には、亜臨界状態の熱水を利用する方法が紹介されている。   Hydrolysis is possible even when such a high pressure and high temperature state is brought to a more realistic state (a state closer to room temperature). In particular, organic matter gradually hydrolyzes over time when it exceeds 100 ° C. and 1 atmosphere. The result of such “hydrolysis using physical energy” is equivalent to the result of “enzymatic hydrolysis” performed by microorganisms. As a method for decomposing a biodegradable plastic using this principle, for example, Patent Document 1 discloses a method using supercritical hydrothermal treatment, and Patent Document 2 discloses a method using subcritical hot water. It has been introduced.

超臨界や亜臨界状態での反応の例に限らず、一般に、高圧下では、比較的低温であっても物質は分圧比の影響で相転移する。しかし、有機物の場合、温度が飽和水蒸気圧より高いと炭化し、温度が飽和水蒸気圧より低いと溶剤等の液化混入などの危険が生じることもあって、実際に「物理エネルギーを用いた加水分解法」を有効に活用するには、温度・圧力などを含めた処理条件の設定が難しい。
即ち、超臨界および亜臨界流体を処理に利用する場合には、その極めて高い温度・圧力条件を発生・維持できる処理装置が必要となる。一般的に、高温・高圧状態を維持するための装置は、容積が大きくなるほどその製作が難しく、製作コストが飛躍的に高くなるため、大規模な工業設備に応用するのが難しい。さらに、超臨界および亜臨界熱水の持つ極めて高い分解能力は、処理対象有機物に留まらず処理容器そのものにも及ぶために、分解を防ぐために高価な材料を装置に使用する必要がある。
Not limited to examples of reactions in supercritical and subcritical states, generally, substances undergo phase transition under the influence of partial pressure ratio under high pressure even at relatively low temperatures. However, in the case of organic substances, if the temperature is higher than the saturated water vapor pressure, carbonization occurs, and if the temperature is lower than the saturated water vapor pressure, there may be dangers such as liquefaction mixing of solvents, etc. In order to effectively use the “method”, it is difficult to set processing conditions including temperature and pressure.
That is, when supercritical and subcritical fluids are used for processing, a processing apparatus capable of generating and maintaining the extremely high temperature and pressure conditions is required. In general, an apparatus for maintaining a high temperature and high pressure state is difficult to manufacture as the volume increases, and the manufacturing cost increases dramatically. Therefore, it is difficult to apply the apparatus to a large-scale industrial facility. Furthermore, since the extremely high decomposition ability of supercritical and subcritical hot water extends not only to the organic substance to be treated but also to the treatment vessel itself, it is necessary to use an expensive material for the apparatus in order to prevent decomposition.

そこで上記問題点を解決する方法として飽和水蒸気圧のもとでの加水分解処理雰囲気の温度・圧力を制御することによって乳酸系生分解性プラスチックを再生させる方法(特許文献3参照)を実現した。この方法は、要するに、加熱モードと冷却モードとによって、乳酸系生分解性プラスチックを含む廃棄物の加水分解処理を行うという方法である。ここに、加熱モードは、被処理物の総重量の約20%の水分を加え、約140℃の飽和水蒸気圧の下で、乳酸を原料とする生分解性プラスチックを含む被処理物と水とを反応させ、生分解性プラスチックを加水分解して乳酸水溶液を生成させる処理であり、冷却モードは、温度と圧力をコンピュータで制御しつつ降温させ、被処理物の加水分解の進行に伴って発生した乳酸などを抽出する処理である。   Therefore, as a method for solving the above problems, a method of regenerating lactic acid biodegradable plastic by controlling the temperature and pressure of the hydrolysis treatment atmosphere under saturated water vapor pressure (see Patent Document 3) was realized. In short, this method is a method of hydrolyzing waste containing a lactic acid-based biodegradable plastic in a heating mode and a cooling mode. Here, in the heating mode, water of about 20% of the total weight of the object to be processed is added, and the object to be processed and water containing a biodegradable plastic made from lactic acid under a saturated water vapor pressure of about 140 ° C. Is a process in which biodegradable plastics are hydrolyzed to form a lactic acid aqueous solution, and the cooling mode is generated while the temperature and pressure are controlled by a computer and the hydrolysis of the workpiece is progressed. This is a process for extracting lactic acid and the like.

この方法によるときには、特許文献1や2に記載されたような超臨界流体を利用する方法や亜臨界状態での処理に比べて処理時間には、多少長い時間を必要とするものの、規制の厳しい高価な超臨界状態や亜臨界状態を形成するための特別の設備や装置を要することなく、超臨界処理や亜臨界処理に比べて処理が格段に簡単であり、さらに処理中の保守性に優れ、何処でも、誰にでも、大規模な処理装置が安全に運転できるという、実用性の面で格段に優れたシステムの実現が可能となる。   When this method is used, the treatment time is somewhat longer than the method using a supercritical fluid as described in Patent Documents 1 and 2 and the treatment in a subcritical state, but the regulation is severe. Compared to supercritical processing and subcritical processing, it is much easier to maintain and has better maintainability during processing without requiring special equipment and equipment to form expensive supercritical and subcritical states. This makes it possible to realize a system that is extremely practical in terms of practicality, enabling anyone and anyone to safely operate a large-scale processing device.

加水分解処理を可能な限り低い温度,低い圧力の条件の下で行うことは望ましいことではあるが、そのために処理時間には、長い時間を必要とするというのは必ずしも好ましいものではない。加水分解時間を短縮することは、望ましいことである。
特許公開平11−292777 特開2003−313283 特願2006−60529
Although it is desirable to perform the hydrolysis treatment under conditions of as low temperature and low pressure as possible, it is not always preferable to require a long treatment time. It is desirable to shorten the hydrolysis time.
Patent Publication 11-292777 JP2003-313283A Japanese Patent Application No. 2006-60529

解決しようとする問題点は、特許文献3に記載された方法では、加熱モードと冷却モードとによって、乳酸系生分解性プラスチックを含む廃棄物の加水分解処理を行い、工業的に実用可能な温度・圧力条件で乳酸系生分解性プラスチックを再生させる方法を実現できたが、その加水分解の処理時間に、超臨界処理や亜臨界処理に比べて多少長い時間を必要とするという問題が残されていたという点である。   The problem to be solved is that in the method described in Patent Document 3, the waste containing the lactic acid biodegradable plastic is hydrolyzed by the heating mode and the cooling mode, and the temperature is industrially practical.・ Although a method for regenerating lactic acid-based biodegradable plastics under pressure conditions has been realized, there remains a problem that the hydrolysis process requires a slightly longer time than supercritical processing or subcritical processing. It is that it was.

本発明は、常温に近い温度で、しかも加水分解時間を短縮するという目的を、加水分解処理に先立つ前処理として、加熱によってポリ乳酸樹脂を一旦アモルファス状態から結晶の状態に変化させてから加水分解処理を行うことによって実現した。   The present invention has a purpose of shortening the hydrolysis time at a temperature close to normal temperature, and as a pretreatment prior to the hydrolysis treatment, the polylactic acid resin is once changed from an amorphous state to a crystalline state by heating, and then hydrolyzed. Realized by processing.

以下に本発明の実施例を示す。本発明は、ポリ乳酸樹脂を含む被処理物の加水分解処理に先立ち、前処理をした後、飽和水蒸気圧のもとで、加熱によってアモルファス状態から結晶の状態に変化したポリ乳酸樹脂の加水分解処理を行うものである。前処理の結果、加水分解反応が促進され、前処理温度100℃近傍の比較的低い飽和水蒸気圧のもとでも、ポリ乳酸樹脂を乳酸に分解することが可能となる。また、同一の温度条件における、ポリ乳酸樹脂の完全分解に要する時間も大幅に短縮される。 Examples of the present invention are shown below. The present invention hydrolyzes a polylactic acid resin that has been pretreated and then changed from an amorphous state to a crystalline state by heating under a saturated water vapor pressure prior to the hydrolysis treatment of an object to be treated containing the polylactic acid resin. The processing is performed. As a result of the pretreatment, the hydrolysis reaction is promoted, and the polylactic acid resin can be decomposed into lactic acid even under a relatively low saturated water vapor pressure near a pretreatment temperature of 100 ° C. In addition, the time required for complete decomposition of the polylactic acid resin under the same temperature condition is greatly reduced.

本発明において、前処理は、水分を加えない環境の下でポリ乳酸樹脂を、ポリ乳酸の結晶化温度を目安に加熱してポリ乳酸を結晶化する処理であり、加水分解処理は、ポリ乳酸樹脂を被処理物として加水分解する処理である。 In the present invention, the pretreatment, the polylactic acid resin in an environment without added water, a process of crystallizing the polylactic acid by heating the crystallization temperature of the polylactic acid as a guide, hydrolysis treatment, the polylactic acid In this process, the resin is hydrolyzed as an object to be processed.

図1に、本発明による加水分解処理に用いる装置の一実施例を示す。図1において、加水分解処理を行う装置は、処理チャンバー1と、抽出管2と、冷却塔3と、循環ポンプ4との組み合わせからなっている。処理チャンバー1は、内部に投入された被処理物を加熱して加水分解処理を行う釜であり、その外壁にはヒータ5が装備され、処理チャンバー1と、冷却塔3間は、前記抽出管2で接続されている。   FIG. 1 shows an embodiment of an apparatus used for the hydrolysis treatment according to the present invention. In FIG. 1, the apparatus for performing the hydrolysis treatment is composed of a combination of a processing chamber 1, an extraction pipe 2, a cooling tower 3, and a circulation pump 4. The processing chamber 1 is a kettle that heats a workpiece to be processed and performs a hydrolysis treatment. The outer wall of the processing chamber 1 is equipped with a heater 5, and the extraction pipe is disposed between the processing chamber 1 and the cooling tower 3. 2 are connected.

抽出管2は、処理チャンバー1の下部の蒸気戻り口6と、上部の蒸気送出口7間をつなぐ循環管路であり、冷却塔3は、その管路内に接続され、循環ポンプ4は、冷却塔3の上流側の管路内に接続されたものである。また、処理チャンバー1は、被処理物の投入口8と排出口9とを有し、その内部には、垂直軸を中心に回転しながら処理チャンバー1内に投入された被処理物を攪拌する攪拌羽根10を装備する。   The extraction pipe 2 is a circulation pipe that connects between the lower steam return port 6 of the processing chamber 1 and the upper steam outlet 7, and the cooling tower 3 is connected in the pipe, and the circulation pump 4 is It is connected in the pipe line on the upstream side of the cooling tower 3. Further, the processing chamber 1 has an input port 8 and a discharge port 9 for the object to be processed, in which the object to be processed input into the processing chamber 1 is agitated while rotating about the vertical axis. Equipped with a stirring blade 10.

冷却塔3は、抽出管2内の気体(蒸気)を冷却する熱交換器であり、循環ポンプ4は、被処理物の加水分解処理後、処理チャンバー1内の水蒸気を冷却塔3に強制送風するものである。冷却塔3には、ドレイン11を備え、冷却塔3内に蒸気中の加水分解成分である抽出された粗乳酸水溶液が貯められ、冷却塔3内にためられた粗乳酸水溶液は、抽出液として容器V1内に回収される。また、チャンバー1内で加水分解後一旦気化して水に溶入した粗乳酸水溶液はドレイン11’を開くことによって、容器V2に回収される。   The cooling tower 3 is a heat exchanger that cools the gas (steam) in the extraction pipe 2, and the circulation pump 4 forcibly blows the water vapor in the processing chamber 1 to the cooling tower 3 after hydrolysis of the object to be processed. To do. The cooling tower 3 includes a drain 11, in which the extracted crude lactic acid aqueous solution that is a hydrolysis component in steam is stored, and the crude lactic acid aqueous solution stored in the cooling tower 3 is used as an extract. It is collected in the container V1. Further, the crude lactic acid aqueous solution once evaporated after being hydrolyzed in the chamber 1 and dissolved in water is recovered in the container V2 by opening the drain 11 '.

本発明は、上記装置を用い、ポリ乳酸樹脂を含む被処理物、例えば乳酸系生分解性プラスチックを含む廃棄物を被処理物としてその加水分解処理を行うものである。廃棄物の再生処理において最も大切なことは、再生に必要なエネルギー(コスト)を最小にするということである。本発明による乳酸系生分解性プラスチックの再生処理においては、処理温度、処理圧力、そして処理時間をどのように最小化するかということが、重要な課題となる。   The present invention uses the above-mentioned apparatus to perform a hydrolysis treatment using a treatment object containing a polylactic acid resin, for example, a waste material containing a lactic acid biodegradable plastic as a treatment object. The most important thing in waste recycling is to minimize the energy (cost) required for recycling. In the regeneration treatment of lactic acid-based biodegradable plastics according to the present invention, how to minimize the treatment temperature, treatment pressure, and treatment time is an important issue.

本発明においては、前処理としてポリ乳酸を結晶化させた後、加水分解処理を行うことで、処理時間の減少を達成する。アモルファス状態のポリ乳酸を結晶化させることによって、同一の温度条件(例えば、140℃)において、結晶化させていないものよりも短時間で加水分解処理できることが明らかになった。図2は、加水分解による有機物の分解メカニズムを示す図である。図2において、加水分解とは、結合している有機物の酸素と他の原子(例えば炭素C)との間に水イオン(HとOH)を作用させて結合を切ることである。 In the present invention, the polylactic acid is crystallized as a pretreatment and then subjected to a hydrolysis treatment to achieve a reduction in treatment time. It has been clarified that by crystallization of polylactic acid in an amorphous state, hydrolysis treatment can be performed in a shorter time than those not crystallized under the same temperature condition (for example, 140 ° C.). FIG. 2 is a diagram showing a decomposition mechanism of organic substances by hydrolysis. In FIG. 2, hydrolysis refers to breaking a bond by allowing water ions (H + and OH ) to act between oxygen and other atoms (for example, carbon C) of the organic substance bonded thereto.

すなわち、「C」と「O」との間で電子の移動が起こり偏在する、いわゆる分極が起こり、そこに水イオン「H」と「OH」が引き寄せられて電気的に結合する現象であるが、そこに電子と原子とのそれぞれが持つエネルギーが深く関係しており、温度・圧力はこの電子と原子の励起エネルギーとして直接作用している。従って、この時に反応に作用させる温度・圧力によって加水分解反応の反応速度は変化する。 That is, a phenomenon in which electrons move between “C” and “O” and are unevenly distributed, so-called polarization occurs, and water ions “H + ” and “OH ” are attracted and electrically coupled therewith. However, the energy of each electron and atom is closely related, and temperature and pressure directly act as excitation energy for this electron and atom. Accordingly, the reaction rate of the hydrolysis reaction varies depending on the temperature and pressure applied to the reaction at this time.

例えばポリ乳酸の原料である乳酸は、ある温度範囲で昇華して気体となったり、融解して液体となったり、また蒸発して気体となったりする。しかしながら、融解自体は分解を伴う反応であり、乳酸が分解すると、純粋な乳酸ではなくなり、ポリ乳酸の原料とはなりにくい。ここで、雰囲気の温度・圧力を制御することによって、この微妙な反応領域を通過させることが可能である。   For example, lactic acid, which is a raw material for polylactic acid, is sublimated into a gas within a certain temperature range, melted into a liquid, or evaporated into a gas. However, melting itself is a reaction accompanied by decomposition. When lactic acid decomposes, it is not pure lactic acid and is difficult to be a raw material for polylactic acid. Here, it is possible to pass through this delicate reaction region by controlling the temperature and pressure of the atmosphere.

ここで、温度・圧力を制御することによってポリ乳酸樹脂を加水分解させ、乳酸オリゴマーにする。この乳酸オリゴマーは高圧下であれば比較的低温でも昇華し、一旦気体となった後、この気体は水溶性であるため高圧力下で熱水に多量に溶解する。これによって多量の乳酸を溶液で回収することが可能となる。本発明においては、加水分解処理において、処理チャンバー1内の温度と圧力を制御するに際し、図3に示す水蒸気圧を飽和水蒸気圧曲線に沿って、温度・圧力域で水蒸気圧を上げるとともに反応終了時には、降温させる。   Here, by controlling the temperature and pressure, the polylactic acid resin is hydrolyzed into a lactic acid oligomer. This lactic acid oligomer sublimes even at a relatively low temperature under high pressure, and once it becomes a gas, this gas is water-soluble, so it dissolves in a large amount in hot water under high pressure. This makes it possible to recover a large amount of lactic acid as a solution. In the present invention, in controlling the temperature and pressure in the processing chamber 1 in the hydrolysis treatment, the water vapor pressure shown in FIG. 3 is increased along the saturated water vapor pressure curve in the temperature / pressure range and the reaction is completed. Sometimes the temperature is lowered.

ちなみに、ある温度・圧力下で1成分系の気液両相が共存するとき、その気相をなす蒸気が飽和に達している状態を飽和蒸気といい、そのときの圧力が飽和蒸気圧である。ある物質の液体の周囲で、その物質の分圧が液体の蒸気圧に等しいとき、その液体は気液平衡の状態にある。温度を下げると蒸気は凝結して液体になる。逆に温度を上げると液体は気化する(蒸気になる)。また、固相と気相の間でも同様の平衡状態が保たれ、この転移を昇華という。   By the way, when one-component gas-liquid phases coexist at a certain temperature and pressure, the state in which the vapor forming the gas phase reaches saturation is called saturated vapor, and the pressure at that time is the saturated vapor pressure. . Around the liquid of a substance, when the partial pressure of the substance is equal to the vapor pressure of the liquid, the liquid is in a vapor-liquid equilibrium state. When the temperature is lowered, the vapor condenses into a liquid. Conversely, when the temperature is raised, the liquid is vaporized (turns to vapor). Also, the same equilibrium is maintained between the solid phase and the gas phase, and this transition is called sublimation.

本発明は、この理論に基づき、前処理後の加水分解処理においては、処理チャンバー1内の分圧としての水蒸気圧を飽和水蒸気圧曲線に沿って制御する。この時、乳酸の分圧比はごく低いため、水蒸気圧が支配的である。乳酸系生分解性プラスチックを含む蒸気の温度・圧力域では、飽和水蒸気圧より少しでも温度が高いと炭化し、低いと溶剤の液化混入の危険が生ずる。本発明は、処理チャンバー内の雰囲気の温度と、圧力とをコンピュータ制御によって、微妙な反応領域を通過させるものである。   Based on this theory, the present invention controls the water vapor pressure as the partial pressure in the processing chamber 1 along the saturated water vapor pressure curve in the hydrolysis treatment after the pretreatment. At this time, since the partial pressure ratio of lactic acid is very low, the water vapor pressure is dominant. In the temperature / pressure range of steam containing lactic acid-based biodegradable plastics, carbonization occurs if the temperature is slightly higher than the saturated water vapor pressure, and if it is low, there is a risk of liquefaction of the solvent. In the present invention, the temperature and pressure of the atmosphere in the processing chamber are passed through a delicate reaction region by computer control.

図4に、処理チャンバー内で進行する加水分解反応の進行を監視するシステムの構成を示す。中央監視室12には、加水分解制御装置13としてコンピュータが設置され、コンピュータからは、ヒータ5の電源投入,攪拌羽根10の駆動制御,処理時間の設定,配管のバルブの開閉制御,循環ポンプ4の駆動制御などを含めて、処理チャンバー1内で進行させる前処理及び加水分解処理に必要な一切の制御並びに設定情報の管理を行う機能を有している。加水分解反応の進行状況の監視並びに生成された粗乳酸の状態及び冷却塔3から得られた抽出液の状態は、モニター14によって監視するほか、コンピュータは、更にこれらのサンプリングを行う機能を有している。   FIG. 4 shows the configuration of a system that monitors the progress of the hydrolysis reaction that proceeds in the processing chamber. In the central monitoring room 12, a computer is installed as a hydrolysis control device 13. From the computer, the heater 5 is turned on, the stirring blade 10 is driven, the processing time is set, the valve opening / closing control of the piping, the circulation pump 4 is turned on. Including the drive control and the like, and the control of all the control and setting information necessary for the pretreatment and hydrolysis treatment to proceed in the treatment chamber 1. In addition to monitoring the progress of the hydrolysis reaction and the state of the produced crude lactic acid and the state of the extract obtained from the cooling tower 3, the monitor 14 has a function of sampling them. ing.

本発明においては、上記装置を用い、ポリ乳酸樹脂を含む被処理物として、加水分解処理に先立って前処理を行い、ついで加水分解処理の加熱モードと、冷却モードとを順に行う。上記装置を用いて乳酸系生分解性プラスチックを含む廃棄物を被処理物として乳酸系生分解性プラスチックの原料を再生させる要領を図5のフローチャートを用い、図1を参照して説明する。   In the present invention, pretreatment is performed prior to the hydrolysis treatment as an object to be treated containing the polylactic acid resin using the above apparatus, and then the heating mode and the cooling mode of the hydrolysis treatment are sequentially performed. A procedure for regenerating the raw material of the lactic acid-based biodegradable plastic with the waste containing the lactic acid-based biodegradable plastic as an object to be processed using the above apparatus will be described with reference to FIG. 1 using the flowchart of FIG.

まず、乳酸系生分解性プラスチックを含む廃棄物からなる被処理物を、処理チャンバー1内に投入し(ステップS1)、投入口8を閉じ、前処理として、約30分以上の時間をかけてポリ乳酸樹脂の結晶化点近くの温度に加熱する(ステップS2)。その後、加水分解処理に移行し、被処理物総重量の20%の水を処理チャンバー1内に投入する(ステップS3)。投入口8を閉じ、タイマーをセットしてヒータ5に通電し、(ステップS4)処理チャンバー1内を約100℃〜150℃に加熱しつつ加熱モードを開始する。加熱モードでは処理チャンバー1内の圧力を、100℃〜150℃の範囲内で設定した加水分解処理の加熱温度での飽和水蒸気圧に保つ。また、一定間隔(例えば2秒)ごとに1回程度攪拌羽根10を回転駆動して処理チャンバー1内の原料を攪拌する。   First, an object to be processed made of waste containing lactic acid-based biodegradable plastic is put into the processing chamber 1 (Step S1), the inlet 8 is closed, and the pretreatment takes about 30 minutes or more. Heat to a temperature near the crystallization point of the polylactic acid resin (step S2). Then, it transfers to a hydrolysis process and 20% of water of the to-be-processed object total weight is thrown in in the processing chamber 1 (step S3). The inlet 8 is closed, a timer is set and the heater 5 is energized (step S4), and the heating mode is started while heating the inside of the processing chamber 1 to about 100 ° C. to 150 ° C. In the heating mode, the pressure in the processing chamber 1 is maintained at the saturated water vapor pressure at the heating temperature of the hydrolysis treatment set within the range of 100 ° C to 150 ° C. Further, the stirring blade 10 is rotationally driven about once every fixed interval (for example, 2 seconds) to stir the raw material in the processing chamber 1.

この状態で一定時間をかけて加熱しながら処理チャンバー1内に発生する飽和水蒸気の雰囲気中に被処理物を曝して加水分解反応を進行させる。加熱モードによって、乳酸系生分解性プラスチックの加水分解反応が進行して、水蒸気と共に粗乳酸およびその蒸気が生成され、その蒸気が処理チャンバー1に充満する。予め定められた時間経過後、ヒータ5の電源を遮断して加熱モードを完了する(ステップS5)。   In this state, the object to be processed is exposed to an atmosphere of saturated water vapor generated in the processing chamber 1 while heating for a certain time, and the hydrolysis reaction proceeds. Depending on the heating mode, the hydrolysis reaction of the lactic acid-based biodegradable plastic proceeds to produce crude lactic acid and its vapor together with water vapor, and the vapor fills the processing chamber 1. After elapse of a predetermined time, the heater 5 is turned off to complete the heating mode (step S5).

被処理物の加水分解処理に要する時間は、被処理物および処理チャンバー1の容量にもよるが、通常は5〜8時間である。つまり密閉された処理チャンバー1内で、約100℃〜150℃の範囲内の温度で加熱したときには、その設定温度での飽和水蒸気圧のもとで数時間のうちに被処理物中の生分解性プラスチックを加水分解することができる。   The time required for the hydrolysis treatment of the workpiece is usually 5 to 8 hours, although it depends on the volume of the workpiece and the processing chamber 1. That is, when heated in a sealed processing chamber 1 at a temperature in the range of about 100 ° C. to 150 ° C., biodegradation in the object to be processed within a few hours under the saturated water vapor pressure at the set temperature. The functional plastic can be hydrolyzed.

加水分解処理は、処理チャンバー1内を密閉した状態で、投入された水と共に処理温度まで昇温し、その温度における飽和水蒸気圧のもとで被処理物の加水分解を進行させる。設定時間が経過するとブザーで報知する。また設定時間前であっても、処理条件の異常(温度異常,圧力異常)が発生したときには、ブザーで報知することもできる。   In the hydrolysis treatment, with the inside of the treatment chamber 1 sealed, the temperature is raised to the treatment temperature together with the charged water, and the hydrolysis of the object to be treated proceeds under the saturated water vapor pressure at that temperature. When the set time has elapsed, a buzzer will notify you. In addition, even before the set time, when a processing condition abnormality (temperature abnormality, pressure abnormality) occurs, a buzzer can also notify.

タイマーで設定した加水分解処理の時間が経過したときには、加熱を終了し、そのままチャンバーを冷却する(ステップS6)。冷却が完了したら、処理チャンバー1下部に滴下、滞留している飽和乳酸水溶液を回収する。   When the hydrolysis processing time set by the timer has elapsed, the heating is terminated and the chamber is cooled as it is (step S6). When the cooling is completed, the saturated lactic acid aqueous solution dropped and staying in the lower part of the processing chamber 1 is recovered.

処理終了時点においては、処理チャンバー1内には、粗乳酸の水溶液とその他の固形物(ポリ乳酸に混合した骨材等)等が完全に分離した形で回収される。   At the end of the treatment, an aqueous solution of crude lactic acid and other solids (such as aggregate mixed with polylactic acid) are collected in the treatment chamber 1 in a completely separated form.

処理チャンバー1内の温度・圧力が十分に下がった(少なくとも100℃・1気圧以下)ことを確認したら、処理チャンバー1内の乳酸水溶液をドレイン11’を開いて容器V2に回収する。また固形生成物は排出口9から回収する(ステップS9)。容器V1及びV2内に回収した粗乳酸水溶液は、再び生分解性プラスチック製品の原料になり、処理チャンバー1から回収された固形生成物は、その素材に応じて再びリサイクルされるか、もしくは廃棄される。
この実施例ではヒータを使用して処理チャンバーを水と一緒に直接加熱する例を示したが、大型のシステムになれば、別途用意したボイラー等を使用して加熱水蒸気を生成し、それを処理チャンバー内に投入する方が効率的である。また、処理施設の設置場所に応じて、電気ではなくガス・石油などを燃焼させた熱を利用することもできる。将来的には、燃料電池を利用したシステムを構築することによって、燃料電池から作り出される電気エネルギーと廃熱の両方を利用した高エネルギー効率の処理装置を構築することが可能となる。
When it is confirmed that the temperature and pressure in the processing chamber 1 have sufficiently decreased (at least 100 ° C. and 1 atmosphere or less), the lactic acid aqueous solution in the processing chamber 1 is recovered in the container V2 by opening the drain 11 ′. The solid product is recovered from the discharge port 9 (step S9). The crude lactic acid aqueous solution recovered in the containers V1 and V2 becomes the raw material of the biodegradable plastic product again, and the solid product recovered from the processing chamber 1 is recycled again or discarded depending on the material. The
In this example, the heater is used to directly heat the processing chamber together with water. However, if the system becomes large, heated steam is generated using a separately prepared boiler or the like and processed. It is more efficient to put it in the chamber. Further, depending on the installation location of the treatment facility, heat obtained by burning gas, oil, or the like instead of electricity can be used. In the future, by constructing a system that uses a fuel cell, it will be possible to construct a high-energy-efficient treatment device that uses both electrical energy and waste heat produced from the fuel cell.

以上、実施例においては、加水分解処理用の処理チャンバー1内でポリ乳酸樹脂を含む被処理物の前処理を行う例を説明したが、前処理は必ずしも加水分解処理用の処理チャンバー内で行う必要はない。前処理用の処理チャンバーを特別に用意し、図6に示すように前処理用の処理チャンバー15内で被処理物の前処理を行った後、前処理用の処理チャンバー15内から取り出した結晶化ポリ乳酸樹脂を、加水分解処理用の処理チャンバー1内に投入し、加水分解処理用の処理チャンバー1内で加水分解処理を行うこともできる。   As described above, in the embodiment, the example in which the pretreatment of the object to be processed including the polylactic acid resin is performed in the treatment chamber 1 for the hydrolysis treatment is described. However, the pretreatment is not necessarily performed in the treatment chamber for the hydrolysis treatment. There is no need. A special processing chamber for pretreatment is prepared. As shown in FIG. 6, after pretreatment of an object to be processed in the processing chamber 15 for pretreatment, the crystal taken out from the processing chamber 15 for pretreatment is taken out. Alternatively, the hydrolyzed polylactic acid resin can be introduced into the treatment chamber 1 for hydrolysis treatment, and the hydrolysis treatment can be performed in the treatment chamber 1 for hydrolysis treatment.

前処理用の処理チャンバー15を特別に用意することの実益は、例えば前処理用の処理チャンバー15を例えばコンビニエンスストア、レストランなどのポリ乳酸樹脂廃棄物の発生地に据え付け、ポリ乳酸樹脂廃棄物の発生地において、前処理を行って処理物を減容し、各地に散在したポリ乳酸樹脂廃棄物の発生地に据え付けられたそれぞれの処理チャンバー15、15、・・・から前処理された結晶化ポリ乳酸樹脂を中央処理施設に回収し、中央処理施設に据え付けられた大型の加水分解処理用の処理チャンバー1内で一挙に加水分解処理を行うことでその処理効率を高めることができる。   The benefit of specially preparing the pretreatment chamber 15 is that, for example, the pretreatment chamber 15 is installed in a place where polylactic acid resin waste is generated, for example, at a convenience store, a restaurant, etc. Pretreatment from the treatment chambers 15, 15,... Installed in the places where the polylactic acid resin waste scattered in various places is reduced by pretreatment at the place of occurrence. The polylactic acid resin is recovered in the central processing facility, and the processing efficiency can be increased by performing the hydrolysis treatment at once in the large-scale hydrolysis processing chamber 1 installed in the central processing facility.

(実験例)
本発明による加水分解効果を確認するため、以下の実験を行った。実験には、試料としてポリ乳酸成形品(ユニチカ製ポリ乳酸成形品(テラマック(登録商標))を用いた。実験に先立ち、熱水中に8時間浸漬し、また、200℃の空気中に2時間放置し、また130℃、2.6気圧の空気中に放置して分解するかどうかの試験を行ったが、いずれの条件のもとでも、試料が分解することはなかった。
(Experimental example)
In order to confirm the hydrolysis effect according to the present invention, the following experiment was conducted. In the experiment, a polylactic acid molded product (unitika polylactic acid molded product (Teramac (registered trademark)) was used as a sample. Prior to the experiment, the sample was immersed in hot water for 8 hours, and the sample was immersed in 200 ° C. air. A test was conducted as to whether or not the sample was allowed to stand for 130 hours at a temperature of 2.6 ° C. and decomposed, but the sample was not decomposed under any conditions.

図7に、試料として用いたポリ乳酸樹脂成形品(ユニチカ製の商品名テラマック(登録商標)))の温度とDSC(エネルギー吸収量)との関係を示す。図7によれば、試料のガラス転移点は、67.64℃であり、100.36℃で結晶化が起こり、167.54℃で溶融することが分かった。この事実から、前処理の温度として溶融点を多少越える温度であっても差支えがなく、このような事実を踏まえて実質的に170℃以下で、少なくとも結晶化点である100℃以上が必要であると判断した。前処理を行うに際してその処理温度は高いほど、結晶化速度が速いと考えられ、後の加水分解反応が促進されるであろうことは容易に推測されたが、現実問題として実際の実験において100℃でも30分程度の処理で十分前処理の効果が確認できることから、高温で処理することが有利であると考える理由はない。   FIG. 7 shows a relationship between the temperature of a polylactic acid resin molded product (trade name Terramac (registered trademark) manufactured by Unitika) used as a sample and DSC (energy absorption amount). According to FIG. 7, it was found that the glass transition point of the sample was 67.64 ° C., crystallization occurred at 100.36 ° C., and it melted at 167.54 ° C. From this fact, there is no problem even if the temperature of the pretreatment is slightly higher than the melting point. Based on such fact, it is substantially 170 ° C. or lower, and at least a crystallization point of 100 ° C. or higher is required. Judged that there was. It was easily estimated that the higher the treatment temperature when performing the pretreatment, the faster the crystallization rate, and the subsequent hydrolysis reaction would be accelerated. There is no reason to think that it is advantageous to perform the treatment at a high temperature since the effect of the pretreatment can be confirmed sufficiently by the treatment for about 30 minutes even at ° C.

また、試料の融点である167℃を越えると、ポリ乳酸樹脂が液状化するため、図6に示したように前処理用の処理チャンバー15内で被処理物を回収し、中央処理装置の加水分解処理用の処理チャンバー1内で加水分解処理を行うようなときに、処理物の取り扱いが厄介になることから、実用的な前処理温度の範囲を、結晶化点(この例では約100℃)から融点(この例では167.54℃)以下で被処理物が結晶状態を保つ温度(約150℃)を上限として設定することが実用に即しているものと考えられる。なお、前処理温度範囲100℃〜150℃の設定は、この試料(テラマック)の場合の例であり、すべてのポリ乳酸製品に共通のものではない。ただし、試料は特殊な構造のものではないので、他のポリ乳酸樹脂成形品であっても、この試料と大幅な違いはないものと推測され、したがって、100℃〜150℃の前処理温度は、一般的なポリ乳酸樹脂成形品前処理温度としてもそのまま適用できるものと考えられる。   When the melting point of the sample exceeds 167 ° C., the polylactic acid resin becomes liquefied, so that the object to be treated is collected in the pretreatment chamber 15 as shown in FIG. When the hydrolysis treatment is performed in the treatment chamber 1 for the decomposition treatment, the handling of the processed material becomes troublesome, and therefore the practical pretreatment temperature range is set to a crystallization point (in this example, about 100 ° C.). ) To a melting point (167.54 ° C. in this example) or lower and the temperature at which the object to be processed maintains a crystalline state (about 150 ° C.) as an upper limit is considered to be practical. The setting of the pretreatment temperature range of 100 ° C. to 150 ° C. is an example in the case of this sample (Teramac) and is not common to all polylactic acid products. However, since the sample is not of a special structure, it is presumed that there is no significant difference from this sample even with other polylactic acid resin molded products. Therefore, the pretreatment temperature of 100 ° C. to 150 ° C. is It is considered that this can be applied as it is as a pretreatment temperature for general polylactic acid resin molded products.

図8は、試料の加水分解前の赤外線分光分析(IR)のグラフ、図9は、加熱処理後の加水分解前の赤外線分光分析(IR)のグラフである。いずれも縦軸目盛りは赤外線透過率(%)、横軸目盛りは波数(cm−1)である。図8の波形から、試料はポリ乳酸樹脂であると判断され、この試料を加水分解したものは、図9の波形から乳酸であると判断される。 FIG. 8 is a graph of infrared spectroscopic analysis (IR) before hydrolysis of a sample, and FIG. 9 is a graph of infrared spectroscopic analysis (IR) before hydrolysis after heat treatment. In either case, the vertical scale is infrared transmittance (%), and the horizontal scale is wave number (cm −1 ). From the waveform of FIG. 8, it is determined that the sample is polylactic acid resin, and the hydrolyzed sample is determined to be lactic acid from the waveform of FIG.

上記試料を気中暴露状態でビーカーに入れ、圧力容器(アルプ株式会社製高圧蒸気滅菌器 IT−2322)中で前処理なしで加水分解処理を行った。その結果を図10に示す。図10の実験例1〜6は、加水分解処理の加熱温度100℃〜130℃、圧力1atm〜2.7atmの条件のもとで加水分解処理を行った結果である。ポリ乳酸樹脂は乳酸に分解されることにより強酸性度pHを示すことから、加水分解反応進行の程度の検知には、pH判定リトマス紙を用い、目視によって色を識別することによって行った。   The said sample was put into the beaker in the air exposure state, and it hydrolyzed in the pressure vessel (The high pressure steam sterilizer IT-2322 by Alp Co., Ltd.) without pretreatment. The result is shown in FIG. Experimental examples 1 to 6 in FIG. 10 are results of the hydrolysis treatment performed under the conditions of the heating temperature of the hydrolysis treatment of 100 ° C. to 130 ° C. and the pressure of 1 atm to 2.7 atm. Since the polylactic acid resin exhibits a strong acidity pH by being decomposed into lactic acid, the progress of the hydrolysis reaction was detected by using a pH judgment litmus paper and visually identifying the color.

実験の結果によれば、温度が高いほど、また圧力が高いほど加水分解処理の進行速度が速いことが分かった。なお、加水分解処理の加熱温度の上限が130℃であるのは、実験に用いた圧力容器の加熱温度の上限が130℃であったためである。   According to the results of the experiment, it was found that the higher the temperature and the higher the pressure, the faster the progress of the hydrolysis treatment. The upper limit of the heating temperature of the hydrolysis treatment is 130 ° C. because the upper limit of the heating temperature of the pressure vessel used in the experiment was 130 ° C.

図11の実験例7〜12は、前処理の加熱温度130℃、圧力2.6atm、前処理時間8時間の条件の下で前処理を行った後、加水分解処理の加熱温度100℃〜130℃、圧力1atm〜2.7atmの条件の下で加水分解処理を行った実験の結果を示している。この実験結果によれば、いずれも加水分解処理の開始直後に試料の加水分解が開始していることが分かる。このことから、試料の加水分解処理に先立つ前処理として高温、高圧は必要ではなく、実質的にこの実験での前処理温度は130℃で十分であるということができる。   In Experimental Examples 7 to 12 in FIG. 11, the pretreatment was performed under conditions of a pretreatment heating temperature of 130 ° C., a pressure of 2.6 atm, and a pretreatment time of 8 hours, and then a hydrolysis treatment heating temperature of 100 ° C. to 130 ° C. The result of the experiment which hydrolyzed under the conditions of ° C. and pressure of 1 atm to 2.7 atm is shown. According to these experimental results, it can be seen that hydrolysis of the sample started immediately after the start of the hydrolysis treatment. From this, it can be said that high temperature and high pressure are not necessary as pretreatment prior to the hydrolysis treatment of the sample, and that the pretreatment temperature in this experiment is substantially 130 ° C.

図12は、ポリ乳酸樹脂のペレットを試料とし、その試料について前処理を行わずに加水分解処理を行った比較例1と、前処理の加熱温度120℃で、30分〜4時間前処理の後、加水分解処理を行った実験例13〜16との比較を示す図である。なお、加水分解処理は、比較例1、実験例13〜16のいずれについても、加水分解処理の加熱温度130℃、圧力2.7atmの水蒸気圧のもとで行った。実験の結果によれば、比較例1では、ポリ乳酸ペレットの加水分解開始に約4時間を必要としたのに対し、前処理を施した実験例13〜16のものでは前処理時間の長短に関わらず、遅くとも3時間でポリ乳酸ペレットの加水分解が開始することが分かった。したがって、前処理としては、図12の結果を見る限り、前処理の加熱温度が120℃以上、前処理時間は30分で十分であることが分かった。   FIG. 12 shows a comparative example 1 in which a pellet of polylactic acid resin was used as a sample, and the sample was hydrolyzed without pretreatment, and the pretreatment was performed at a heating temperature of 120 ° C. for 30 minutes to 4 hours. It is a figure which shows the comparison with Experimental Examples 13-16 which performed the hydrolysis process afterwards. The hydrolysis treatment was carried out under the heating temperature of the hydrolysis treatment at 130 ° C. and the water vapor pressure of 2.7 atm for both Comparative Example 1 and Experimental Examples 13-16. According to the results of the experiment, in Comparative Example 1, it took about 4 hours to start hydrolysis of the polylactic acid pellets, whereas in Examples 13 to 16 in which the pretreatment was performed, the pretreatment time was long and short. Regardless, it was found that hydrolysis of the polylactic acid pellets started in 3 hours at the latest. Therefore, as the pretreatment, as can be seen from the results of FIG. 12, it was found that the pretreatment heating temperature was 120 ° C. or more and the pretreatment time was 30 minutes.

次に、前処理温度を120℃,130℃にそれぞれ設定し、前処理時間を30分、1時間、2時間、4時間に変化させて試料の前処理を行った後、処理温度130℃、水蒸気圧2.7atmの条件で加水分解処理を行った実験例17〜20と、前処理なしで同じ条件で加水分解処理を行った比較例2とについて、分解融解までに要した時間を測定した。その実験結果を図13に示す。実験結果は、図13に明らかなとおり、前処理を行わない比較例2では、分解融解終了までに12時間を必要としたのに対し、実験例17〜20では、ほぼ7時間〜9時間で試料の分解融解が終了した。前処理温度が120℃であっても、130℃であっても大差がなく、また、前処理時間に長時間をかけることが必ずしも必要ではないことが判断でき、この結果を見る限り、前処理は120℃、30分で十分であることが分かる。   Next, the pretreatment temperature was set to 120 ° C. and 130 ° C. respectively, the pretreatment time was changed to 30 minutes, 1 hour, 2 hours, and 4 hours. About Experimental Examples 17-20 which performed the hydrolysis process on the conditions of water vapor pressure 2.7 atm, and the comparative example 2 which performed the hydrolysis process on the same conditions without pre-processing, the time required by decomposition | disassembly melting was measured. . The experimental results are shown in FIG. As is apparent from FIG. 13, the experimental result required 12 hours to complete the decomposition and melting in Comparative Example 2 where no pretreatment was performed, whereas in Experimental Examples 17 to 20, the experimental result was approximately 7 to 9 hours. Decomposition and melting of the sample was completed. Even if the pretreatment temperature is 120 ° C. or 130 ° C., it can be judged that there is no great difference and it is not always necessary to spend a long time for the pretreatment time. It can be seen that 120 ° C. and 30 minutes are sufficient.

さらに、処理温度130℃で前処理した後、130℃以上の処理温度で加水分解処理を行った。その実験結果を以下に示す。実験には試料1(前処理を行ったポリ乳酸成形品(テラマック(登録商標))、試料2(前処理を行わないポリ乳酸成形品(テラマック(登録商標))、試料3(ポリ乳酸成形品の成形材料であるポリ乳酸ペレット)を用い、それぞれの試料(約1gのサンプル)を個別に圧力容器(耐圧硝子株式会社製、ハイパーグラスターTEM−V1000N)内に入れ、実験例21〜25として加水分解温度(そのときの水蒸気圧)をそれぞれ130℃(2.7atm)、135℃(3.1atm)、140℃(3.6atm)、145℃(4.1atm)、150℃(4.7atm)に設定し、それぞれの実験例についてポリ乳酸樹脂の加水分解開始時間を測定した。実験結果を図14に示す。図14の結果から、前処理を行った試料1の加水分解開始時間は著しく早まり、とくに加水分解温度150℃では瞬時に加水分解反応が開始することが分かったが、135℃〜140℃においても加水分解処理を1時間で終了されることができることから、実用レベルでは、加水分解温度は、135℃〜140℃の範囲に設定することで十分であると判断される。なお、いずれの実験例においても、加水分解開始後ほぼ20〜30分後には、加水分解反応は終了した。   Further, after pretreatment at a treatment temperature of 130 ° C., hydrolysis treatment was performed at a treatment temperature of 130 ° C. or higher. The experimental results are shown below. In the experiment, sample 1 (polylactic acid molded product with pretreatment (Teramac (registered trademark)), sample 2 (polylactic acid molded product with no pretreatment (terramac (registered trademark)), sample 3 (polylactic acid molded product) Each sample (about 1 g sample) was individually placed in a pressure vessel (Hyperglaster TEM-V1000N, manufactured by Pressure Glass Co., Ltd.) and used as Experimental Examples 21-25. The decomposition temperature (water vapor pressure at that time) is 130 ° C. (2.7 atm), 135 ° C. (3.1 atm), 140 ° C. (3.6 atm), 145 ° C. (4.1 atm), 150 ° C. (4.7 atm), respectively. The hydrolysis start time of the polylactic acid resin was measured for each of the experimental examples, and the experimental results are shown in Fig. 14. From the results of Fig. 14, hydrolysis of sample 1 that had been pretreated was performed. The start time was remarkably advanced, and it was found that the hydrolysis reaction started instantly at a hydrolysis temperature of 150 ° C., but the hydrolysis treatment can be completed in 1 hour at 135 ° C. to 140 ° C. In terms of level, it is judged that it is sufficient to set the hydrolysis temperature in the range of 135 ° C. to 140 ° C. In any of the experimental examples, the hydrolysis is performed after about 20 to 30 minutes after the start of hydrolysis. The decomposition reaction was finished.

(結果の考察)
以上の結果から前処理は、ポリ乳酸樹脂をポリ乳酸樹脂の融点以下の温度を上限として少なくともポリ乳酸樹脂の結晶化温度の前後、あるいは結晶化温度以上の温度で加熱して、アモルファス状態から結晶の状態に変化させる処理であり、通常の場合に、100℃〜167℃の範囲内の温度で加熱する処理であるということができる。また、前処理に続く、加水分解処理の加熱モードとしては、処理チャンバー内を飽和水蒸気圧で満たすために十分な水分量を加え、約100℃〜150℃範囲内の温度での飽和水蒸気圧の下で、ポリ乳酸樹脂と水分とを反応させて乳酸水溶液を生成させることができる。
(Consideration of results)
Based on the above results, the pretreatment is carried out by heating the polylactic acid resin from the amorphous state by heating the polylactic acid resin at a temperature at or below the crystallization temperature of the polylactic acid resin up to a temperature below the melting point of the polylactic acid resin, or at a temperature above the crystallization temperature. a process for changing the state, to the normal case, it is possible that a process of heating at a temperature in the range of 100 ℃ ~167 ℃. In addition, as a heating mode of the hydrolysis treatment following the pretreatment, a sufficient amount of water is added to fill the inside of the treatment chamber with the saturated water vapor pressure, and the saturated water vapor pressure at a temperature in the range of about 100 ° C. to 150 ° C. Under the condition, a polylactic acid resin and moisture can be reacted to generate an aqueous lactic acid solution.

さらに、ポリ乳酸樹脂を前処理するということは、後工程における加水分解処理の反応の促進だけにとどまらず、プラスチックの分別に大きな意味がある。すなわち、前処理されたポリ乳酸樹脂は、著しく脆性が高まるために、対のローラー間で粉砕が可能である。他のほとんどの合成樹脂は、ローラー間で圧潰しても、変形するだけで粉砕することはできない。したがって、合成樹脂廃棄物を一旦100℃〜130℃レベルの温度で加熱した後、その処理物をローラー間に通せば、ポリ乳酸樹脂は粉末となって他の合成樹脂から粒径分離され、粉末となったポリ乳酸樹脂のみを取り出して加水分解処理を行うことができることを示唆している。   Furthermore, pretreatment of the polylactic acid resin has a great significance not only in promoting the hydrolysis treatment reaction in the post-process but also in plastic separation. That is, since the pretreated polylactic acid resin is significantly brittle, it can be pulverized between a pair of rollers. Most other synthetic resins can only be deformed and cannot be crushed even if they are crushed between rollers. Therefore, once the synthetic resin waste is heated at a temperature of 100 ° C. to 130 ° C. and then the treated product is passed between rollers, the polylactic acid resin becomes powder and is separated from other synthetic resins in particle size. This suggests that only the polylactic acid resin thus obtained can be taken out and hydrolyzed.

本発明によれば、加水分解処理に先立って、単に100℃を越える温度に加熱するのみの前処理を行うことによって、その後の加水分解処理時間を大幅に短縮してポリ乳酸樹脂の原料である乳酸および乳酸水溶液を回収でき、したがって本発明によれば、ポリ乳酸樹脂の完全ケミカルリサイクルを実現することによって、廃棄物処理の問題,資源の有効活用の問題を解決してまことに好ましい資源のクローズドサイクルシステムを実現できる。   According to the present invention, prior to the hydrolysis treatment, by performing a pretreatment simply by heating to a temperature exceeding 100 ° C., the subsequent hydrolysis treatment time is greatly shortened, and this is a raw material for polylactic acid resin. Lactic acid and lactic acid aqueous solution can be recovered. Therefore, according to the present invention, by realizing the complete chemical recycling of polylactic acid resin, the problem of waste disposal and the problem of effective use of resources are solved, which is a particularly preferable closed cycle of resources. A system can be realized.

加水分解装置の構成図である。It is a block diagram of a hydrolysis apparatus. 有機物の加水分解メカニズムを説明する図である。It is a figure explaining the hydrolysis mechanism of organic substance. 飽和水蒸気圧曲線を示すグラフである。It is a graph which shows a saturated water vapor pressure curve. 本発明方法を実施するシステムの構成図である。It is a block diagram of the system which implements the method of this invention. 本発明方法のフローを示す図である。It is a figure which shows the flow of this invention method. 処理チャンバーを前処理用と、加熱処理用とに使い分ける例を示す図である。It is a figure which shows the example which uses a process chamber properly for pre-processing and for heat processing. ポリ乳酸樹脂の温度とエネルギー吸収量との関係を示すグラフである。It is a graph which shows the relationship between the temperature of polylactic acid resin, and energy absorption. 試料の加水分解前の赤外線分光分析(IR)のグラフである。It is a graph of infrared spectroscopy (IR) before hydrolysis of a sample. 試料の加熱処理後の加水分解後の赤外線分光分析(IR)のグラフである。It is a graph of infrared spectroscopy (IR) after hydrolysis after heat treatment of a sample. ポリ乳酸樹脂成形品を、前処理なしで加水分解処理を行った実験の結果を示す図である。It is a figure which shows the result of the experiment which hydrolyzed the polylactic acid resin molded product without the pretreatment. ポリ乳酸樹脂成形品に、前処理を行った後、加水分解処理を行った実験の結果を示す図である。It is a figure which shows the result of the experiment which hydrolyzed the polylactic acid resin molded article after performing the pretreatment. ポリ乳酸樹脂成形品について、前処理を行わずに加水分解処理を行った比較例と、前処理の後、加水分解処理を行った実験例との比較を示す図である。It is a figure which shows the comparison with the comparative example which performed the hydrolysis process, without performing pre-processing about the polylactic acid resin molded article, and the experiment example which performed the hydrolysis process after pre-processing. 前処理条件を種々変えて加水分解処理を行ったときの加水分解終了時間の違いを示す図である。It is a figure which shows the difference of the hydrolysis completion time when changing a pre-processing condition variously and performing a hydrolysis process. ポリ乳酸樹脂成形品と、その材料であるペレットについて、130℃〜150℃で加水分解処理を行ったときの加水分解開始時間の比較を示す図である。It is a figure which shows the comparison of the hydrolysis start time when a polylactic acid resin molded product and the pellet which is the material perform a hydrolysis process at 130 to 150 degreeC.

符号の説明Explanation of symbols

1 処理チャンバー
2 抽出管
3 冷却塔
4 循環ポンプ
5 ヒータ
6 蒸気戻り口
7 蒸気送出口
8 投入口
9 排出口
10 攪拌羽根
11,11’ ドレイン
12 中央監視室
13 加水分解制御装置
14 モニター
15 前処理用の処理チャンバー
V1,V2 容器
DESCRIPTION OF SYMBOLS 1 Processing chamber 2 Extraction pipe 3 Cooling tower 4 Circulating pump 5 Heater 6 Steam return port 7 Steam delivery port 8 Input port 9 Outlet port 10 Stirring blade 11, 11 'Drain 12 Central monitoring room 13 Hydrolysis control device 14 Monitor 15 Pretreatment Processing chamber for
V1, V2 container

Claims (4)

加水分解処理に先立って前処理を行った後、ポリ乳酸樹脂を加水分解して乳酸に再生させるポリ乳酸樹脂の再生方法であって、
前処理は、ポリ乳酸樹脂を処理チャンバー内に投入し、ポリ乳酸樹脂を100℃〜170℃の範囲内の温度で加熱し、ポリ乳酸樹脂をアモルファス状態から結晶の状態に変化させる処理であり、
加水分解処理は、加熱モードと、冷却モードとからなり、前処理後、加熱モードで処理チャンバー内を飽和水蒸気圧で満たすために十分な水分量を加え、100℃〜150℃範囲内の温度での飽和水蒸気圧の下で、ポリ乳酸樹脂と水分とを反応させて乳酸水溶液を生成させる処理であり、冷却モードは、予め定められた飽和水蒸気圧曲線に沿って蒸気圧を下降させ、ポリ乳酸樹脂の加水分解進行に伴って発生した乳酸を抽出する処理であることを特徴とするポリ乳酸樹脂の再生方法。
A method for regenerating a polylactic acid resin, comprising pretreating prior to the hydrolysis treatment and then hydrolyzing the polylactic acid resin to regenerate it into lactic acid,
The pretreatment is a treatment in which the polylactic acid resin is put into a processing chamber, the polylactic acid resin is heated at a temperature in the range of 100 ° C. to 170 ° C., and the polylactic acid resin is changed from an amorphous state to a crystalline state.
The hydrolysis treatment consists of a heating mode and a cooling mode. After the pretreatment, a sufficient amount of water is added to fill the inside of the treatment chamber with saturated water vapor pressure in the heating mode, and the temperature is in the range of 100 ° C to 150 ° C. This is a process of producing a lactic acid aqueous solution by reacting a polylactic acid resin and moisture under the saturated water vapor pressure of the water, and the cooling mode reduces the vapor pressure along a predetermined saturated water vapor pressure curve to produce polylactic acid. A method for regenerating a polylactic acid resin, which is a process for extracting lactic acid generated with the progress of hydrolysis of the resin .
ポリ乳酸樹脂を含む被処理物を処理チャンバー内に投入し、前処理として、処理対象のポリ乳酸樹脂を100℃〜170℃の温度範囲の中で少なくとも30分間以上加熱してポリ乳酸樹脂をアモルファス状態から結晶の状態に変化させるステップと、処理チャンバー内を飽和水蒸気圧で満たすために十分な水分量を投入して処理チャンバーを密閉するステップと、処理チャンバー内を100℃〜150℃の範囲内の温度に加熱し、処理チャンバー内の圧力を、100℃〜150℃の加水分解処理の加熱温度での飽和水蒸気圧に保ち、100℃〜150℃範囲内の温度での飽和水蒸気圧の下で、ポリ乳酸樹脂と水分とを反応させて乳酸水溶液を生成させるステップと、被処理物の加熱モード終了後、冷却モードで予め定められた飽和水蒸気圧曲線に沿って温度と圧力を制御し、蒸気圧を下降させることにより処理チャンバー内の蒸気を凝結して乳酸水溶液を抽出するステップと、抽出され乳酸水溶液を回収するステップと、処理チャンバー内に残存するポリ乳酸以外の被処理物等の固形物を回収するステップとを有することを特徴とする請求項1に記載のポリ乳酸樹脂の再生方法。 An object to be treated containing a polylactic acid resin is put into a processing chamber, and as a pretreatment, the polylactic acid resin to be treated is heated in a temperature range of 100 ° C. to 170 ° C. for at least 30 minutes to make the polylactic acid resin amorphous. A step of changing from a state to a crystalline state, a step of sealing a processing chamber by supplying a sufficient amount of water to fill the processing chamber with a saturated water vapor pressure, and a processing chamber within a range of 100 ° C. to 150 ° C. The pressure in the processing chamber is kept at the saturated water vapor pressure at the heating temperature of the hydrolysis treatment of 100 ° C. to 150 ° C., and under the saturated water vapor pressure at a temperature in the range of 100 ° C. to 150 ° C. A step of reacting a polylactic acid resin with water to form a lactic acid aqueous solution, and a saturated water vapor pressure curve predetermined in a cooling mode after completion of the heating mode of the workpiece. Controlling the temperature and pressure along the line, and recovering the steps of condensed vapor in the processing chamber by lowering the vapor pressure to extract the aqueous lactic acid solution, the extracted lactic acid aqueous solution, into the processing chamber 2. A method of reclaiming polylactic acid resin according to claim 1, further comprising a step of recovering a solid such as a treatment object other than the remaining polylactic acid. ポリ乳酸樹脂を含む被処理物を前処理した後、被処理物を圧潰し、圧潰によって変形するだけで粉砕できない他の合成樹脂と粒径分離し、圧潰によって粉末となったポリ乳酸樹脂のみを取り出して加水分解処理を行うことを特徴とする請求項1に記載のポリ乳酸樹脂の再生方法。 After pre-processing the object to be treated containing polylactic acid resin, the object to be treated is crushed, separated from other synthetic resins that cannot be crushed simply by being deformed by crushing, and only the polylactic acid resin powdered by crushing is removed. The method for regenerating a polylactic acid resin according to claim 1, wherein the polylactic acid resin is taken out and hydrolyzed. 前処理は、前処理用の処理チャンバー内にポリ乳酸樹脂を投入して加熱する処理であり、
加水分解処理は、前処理用の処理チャンバー内から取り出した結晶化ポリ乳酸樹脂を、加水分解処理用チャンバー内に投入して加水分解処理を行うことを特徴とする請求項に記載のポリ乳酸樹脂の再生方法。
The pretreatment is a treatment in which polylactic acid resin is put into a treatment chamber for pretreatment and heated,
2. The polylactic acid according to claim 1 , wherein the hydrolysis treatment is performed by introducing the crystallized polylactic acid resin taken out from the pretreatment chamber into the hydrolysis treatment chamber and performing the hydrolysis treatment. 3. Resin regeneration method.
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