JP3194792B2 - Decomposition method of aliphatic polyester using enzyme - Google Patents
Decomposition method of aliphatic polyester using enzymeInfo
- Publication number
- JP3194792B2 JP3194792B2 JP17903292A JP17903292A JP3194792B2 JP 3194792 B2 JP3194792 B2 JP 3194792B2 JP 17903292 A JP17903292 A JP 17903292A JP 17903292 A JP17903292 A JP 17903292A JP 3194792 B2 JP3194792 B2 JP 3194792B2
- Authority
- JP
- Japan
- Prior art keywords
- lipase
- enzyme
- amano
- aliphatic polyester
- pcl
- 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 - Fee Related
Links
- 229920003232 aliphatic polyester Polymers 0.000 title claims description 20
- 238000000034 method Methods 0.000 title claims description 20
- 108090000790 Enzymes Proteins 0.000 title description 30
- 102000004190 Enzymes Human genes 0.000 title description 30
- 238000000354 decomposition reaction Methods 0.000 title description 13
- 108090001060 Lipase Proteins 0.000 claims description 69
- 102000004882 Lipase Human genes 0.000 claims description 69
- 239000004367 Lipase Substances 0.000 claims description 69
- 235000019421 lipase Nutrition 0.000 claims description 69
- 229920001610 polycaprolactone Polymers 0.000 claims description 23
- 239000004632 polycaprolactone Substances 0.000 claims description 23
- 241000589513 Burkholderia cepacia Species 0.000 claims description 4
- 229940088598 enzyme Drugs 0.000 description 29
- 239000000835 fiber Substances 0.000 description 29
- 230000035484 reaction time Effects 0.000 description 17
- 230000004580 weight loss Effects 0.000 description 13
- 238000006243 chemical reaction Methods 0.000 description 11
- 229920003169 water-soluble polymer Polymers 0.000 description 10
- 241000589516 Pseudomonas Species 0.000 description 9
- 230000000694 effects Effects 0.000 description 7
- 244000005700 microbiome Species 0.000 description 7
- 241000235527 Rhizopus Species 0.000 description 6
- 239000013585 weight reducing agent Substances 0.000 description 6
- 229920002988 biodegradable polymer Polymers 0.000 description 5
- 239000004621 biodegradable polymer Substances 0.000 description 5
- 239000007853 buffer solution Substances 0.000 description 5
- 230000003100 immobilizing effect Effects 0.000 description 5
- 229920001223 polyethylene glycol Polymers 0.000 description 5
- 108010093096 Immobilized Enzymes Proteins 0.000 description 4
- 239000002202 Polyethylene glycol Substances 0.000 description 4
- 229920000728 polyester Polymers 0.000 description 4
- 239000000843 powder Substances 0.000 description 4
- 230000036962 time dependent Effects 0.000 description 4
- 241000894006 Bacteria Species 0.000 description 3
- 230000000593 degrading effect Effects 0.000 description 3
- 229920003023 plastic Polymers 0.000 description 3
- 239000004033 plastic Substances 0.000 description 3
- 229920000642 polymer Polymers 0.000 description 3
- 229920001059 synthetic polymer Polymers 0.000 description 3
- 238000011282 treatment Methods 0.000 description 3
- -1 In particular Polymers 0.000 description 2
- 239000004372 Polyvinyl alcohol Substances 0.000 description 2
- 240000005384 Rhizopus oryzae Species 0.000 description 2
- 235000013752 Rhizopus oryzae Nutrition 0.000 description 2
- 238000006065 biodegradation reaction Methods 0.000 description 2
- 239000000872 buffer Substances 0.000 description 2
- 229920001577 copolymer Polymers 0.000 description 2
- 229920006240 drawn fiber Polymers 0.000 description 2
- 230000002255 enzymatic effect Effects 0.000 description 2
- 238000007654 immersion Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 238000006116 polymerization reaction Methods 0.000 description 2
- 229920002451 polyvinyl alcohol Polymers 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 241000228212 Aspergillus Species 0.000 description 1
- 229920002134 Carboxymethyl cellulose Polymers 0.000 description 1
- 229920002307 Dextran Polymers 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- 241000159512 Geotrichum Species 0.000 description 1
- 229920001612 Hydroxyethyl starch Polymers 0.000 description 1
- 101710098556 Lipase A Proteins 0.000 description 1
- 102000004317 Lyases Human genes 0.000 description 1
- 108090000856 Lyases Proteins 0.000 description 1
- 101710099648 Lysosomal acid lipase/cholesteryl ester hydrolase Proteins 0.000 description 1
- 102100026001 Lysosomal acid lipase/cholesteryl ester hydrolase Human genes 0.000 description 1
- 241001465754 Metazoa Species 0.000 description 1
- 108010019160 Pancreatin Proteins 0.000 description 1
- 239000004698 Polyethylene Substances 0.000 description 1
- 108010020346 Polyglutamic Acid Proteins 0.000 description 1
- 229920000331 Polyhydroxybutyrate Polymers 0.000 description 1
- 108010039918 Polylysine Proteins 0.000 description 1
- 241000235545 Rhizopus niveus Species 0.000 description 1
- 239000002262 Schiff base Substances 0.000 description 1
- 229920002125 Sokalan® Polymers 0.000 description 1
- 241000209140 Triticum Species 0.000 description 1
- 235000021307 Triticum Nutrition 0.000 description 1
- 239000008351 acetate buffer Substances 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 125000001931 aliphatic group Chemical group 0.000 description 1
- 150000001540 azides Chemical class 0.000 description 1
- 150000001718 carbodiimides Chemical class 0.000 description 1
- 239000001768 carboxy methyl cellulose Substances 0.000 description 1
- 235000010948 carboxy methyl cellulose Nutrition 0.000 description 1
- 239000008112 carboxymethyl-cellulose Substances 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 238000009833 condensation Methods 0.000 description 1
- 230000005494 condensation Effects 0.000 description 1
- 230000008878 coupling Effects 0.000 description 1
- 238000010168 coupling process Methods 0.000 description 1
- 238000005859 coupling reaction Methods 0.000 description 1
- ATDGTVJJHBUTRL-UHFFFAOYSA-N cyanogen bromide Chemical compound BrC#N ATDGTVJJHBUTRL-UHFFFAOYSA-N 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 239000012954 diazonium Substances 0.000 description 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-O diazynium Chemical compound [NH+]#N IJGRMHOSHXDMSA-UHFFFAOYSA-O 0.000 description 1
- 125000005442 diisocyanate group Chemical group 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 230000007515 enzymatic degradation Effects 0.000 description 1
- 230000032050 esterification Effects 0.000 description 1
- 238000005886 esterification reaction Methods 0.000 description 1
- 239000010408 film Substances 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 238000005194 fractionation Methods 0.000 description 1
- 230000014509 gene expression Effects 0.000 description 1
- 230000007062 hydrolysis Effects 0.000 description 1
- 238000006460 hydrolysis reaction Methods 0.000 description 1
- 229940050526 hydroxyethylstarch Drugs 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- FPYJFEHAWHCUMM-UHFFFAOYSA-N maleic anhydride Chemical compound O=C1OC(=O)C=C1 FPYJFEHAWHCUMM-UHFFFAOYSA-N 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 229920005615 natural polymer Polymers 0.000 description 1
- FEMOMIGRRWSMCU-UHFFFAOYSA-N ninhydrin Chemical compound C1=CC=C2C(=O)C(O)(O)C(=O)C2=C1 FEMOMIGRRWSMCU-UHFFFAOYSA-N 0.000 description 1
- 210000000496 pancreas Anatomy 0.000 description 1
- 229940055695 pancreatin Drugs 0.000 description 1
- UQGPCEVQKLOLLM-UHFFFAOYSA-N pentaneperoxoic acid Chemical compound CCCCC(=O)OO UQGPCEVQKLOLLM-UHFFFAOYSA-N 0.000 description 1
- 239000000825 pharmaceutical preparation Substances 0.000 description 1
- 229940127557 pharmaceutical product Drugs 0.000 description 1
- 239000008363 phosphate buffer Substances 0.000 description 1
- 239000005015 poly(hydroxybutyrate) Substances 0.000 description 1
- 229920000747 poly(lactic acid) Polymers 0.000 description 1
- 239000004584 polyacrylic acid Substances 0.000 description 1
- 229920000768 polyamine Polymers 0.000 description 1
- 229920000573 polyethylene Polymers 0.000 description 1
- 229920002643 polyglutamic acid Polymers 0.000 description 1
- 239000004626 polylactic acid Substances 0.000 description 1
- 229920000656 polylysine Polymers 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 239000010409 thin film Substances 0.000 description 1
- 238000000108 ultra-filtration Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
- 229920003176 water-insoluble polymer Polymers 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
- C08J11/00—Recovery or working-up of waste materials
- C08J11/04—Recovery or working-up of waste materials of polymers
- C08J11/10—Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation
- C08J11/105—Recovery 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 enzymes
-
- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
- C08J2300/00—Characterised by the use of unspecified polymers
- C08J2300/14—Water soluble or water swellable polymers, e.g. aqueous gels
-
- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
- C08J2367/00—Characterised by the use of polyesters obtained by reactions forming a carboxylic ester link in the main chain; Derivatives of such polymers
- C08J2367/04—Polyesters derived from hydroxy carboxylic acids, e.g. lactones
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/62—Plastics recycling; Rubber recycling
Landscapes
- Chemical & Material Sciences (AREA)
- Polymers & Plastics (AREA)
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
- Sustainable Development (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Medicinal Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Organic Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Polyesters Or Polycarbonates (AREA)
- Biological Depolymerization Polymers (AREA)
- Chemical Or Physical Treatment Of Fibers (AREA)
- Preparation Of Compounds By Using Micro-Organisms (AREA)
- Treatments Of Macromolecular Shaped Articles (AREA)
- Manufacture Of Porous Articles, And Recovery And Treatment Of Waste Products (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は、生分解性高分子ポリマ
ーの分解法及び該高分子ポリマーの表面処理方法に関す
る。より詳細には、酵素を用いた脂肪族ポリエステルの
分解法及び固定化酵素を用いた脂肪族ポリエステル繊維
等の表面処理方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for decomposing a biodegradable polymer and a method for surface treating the polymer. More specifically, the present invention relates to a method for decomposing an aliphatic polyester using an enzyme and a method for treating a surface of an aliphatic polyester fiber or the like using an immobilized enzyme.
【0002】[0002]
【従来の技術】プラスチックを代表とする高分子化合物
は、金属やセラミックとともに現在では生活と緊密な関
係のある材料であり、プラスチック製品は衣食住にとど
まらず各種産業、医療等に幅広く使用されている。2. Description of the Related Art High molecular compounds represented by plastics, together with metals and ceramics, are materials that are closely related to daily life, and plastic products are widely used not only in clothes, food and living but also in various industries and medical treatments. .
【0003】しかしながら、長期安定性を重要視して開
発されてきた従来のプラスチックは自然環境の中で分解
されないため、不要となった大量の廃棄物が地球的規模
で環境を破壊し大きな問題となっている。However, conventional plastics, which have been developed with an emphasis on long-term stability, are not decomposed in the natural environment, and a large amount of unnecessary waste destroys the environment on a global scale. Has become.
【0004】近年、上記のような問題に人々の関心が高
まる中で、自然の中の微生物により分解される、いわゆ
る生分解性高分子の研究が盛んに行われ、実用化されつ
つある。[0004] In recent years, with increasing public interest in the above-mentioned problems, studies on so-called biodegradable polymers that are degraded by microorganisms in nature have been actively conducted and are being put to practical use.
【0005】現在研究の対象となっているのは、微生
物の生産する高分子、植物及び動物由来の天然高分
子、合成高分子等が挙げられる。やはその生産性
等の点で満足するものを得ることが困難であり、ポリビ
ニルアルコール、ポリエチレングリコール、ポリエステ
ルに代表されるが生分解性高分子として期待されてい
る。[0005] At present, the subject of research includes polymers produced by microorganisms, natural polymers and synthetic polymers derived from plants and animals. It is difficult to obtain a product that is satisfactory in terms of productivity and the like, and is typified by polyvinyl alcohol, polyethylene glycol, and polyester, but is expected as a biodegradable polymer.
【0006】これらの合成高分子は微生物や酵素によっ
て分解されるものがあることが知られている。例えば水
溶性高分子であるポリビニルアルコールは土壌中の細菌
によって分解される〔(Agric. Biol. Chem., 37巻, 74
7頁(1973)〕。同じく水溶性高分子であるポリエチレ
ングリコールを分解する微生物は知られているが、その
重合度の増大に伴って細菌による分解は困難となり、特
に分子量6,000以上のポリエチレングリコールは単独の
菌では分解することが困難である〔J. ferment. Techno
l., 53巻, 757頁(1977)〕。[0006] It is known that some of these synthetic polymers are decomposed by microorganisms or enzymes. For example, polyvinyl alcohol, which is a water-soluble polymer, is decomposed by bacteria in the soil [(Agric. Biol. Chem., 37, 74).
7 (1973)]. Microorganisms that degrade polyethylene glycol, which is also a water-soluble polymer, are known, but as the degree of polymerization increases, it becomes difficult for bacteria to degrade, especially polyethylene glycol with a molecular weight of 6,000 or more can be degraded by a single bacterium. Is difficult [J. ferment. Techno
l., 53, 757 (1977)].
【0007】また、最近では水に不溶な高分子であるポ
リエステルはその加工のし易さより、生分解性合成高分
子としては最も期待されている。特に脂肪族ポリエステ
ルであるポリカプロラクトン(以下、PCLという)は
土壌中で加水分解を受けることが報告〔Polym. Preprin
ts, 13巻, 629頁(1972)〕され、さらに数々のリパー
ゼによるPCLの分解も詳細に検討されてきた〔Agric.
Biol. Chem., 52巻 ,265頁(1977)〕。このようにそ
の生分解が微生物のみならず酵素を用いる事によっても
行うことができる点で脂肪族ポリエステルはより好まし
い性質を有した生分解性高分子と考えられる。[0007] Recently, polyester, which is a water-insoluble polymer, is most expected as a biodegradable synthetic polymer because of its ease of processing. In particular, it has been reported that polycaprolactone (PCL), which is an aliphatic polyester, undergoes hydrolysis in soil [Polym. Preprin].
ts, 13, 629 (1972)], and the degradation of PCL by various lipases has been studied in detail [Agric.
Biol. Chem., 52, 265 (1977)]. As described above, the aliphatic polyester is considered to be a biodegradable polymer having more preferable properties in that biodegradation can be performed not only by using a microorganism but also by using an enzyme.
【0008】[0008]
【発明が解決しようとする課題】ポリエステルをリパー
ゼを用いて分解する方法は知られている(特開昭52-827
74)。上記の方法においては、PCLに対しては例えば
アスペルギルス(Aspergillus)・ニガー、ジオトリカ
ム(Geotrichum)・カンジダム、リゾプス(Rhizopus)
・デレマー、リゾプス・アリズス、カンジダ(Candid
a)・シリンドラッセ、小麦胚芽、豚膵臓の各由来リパ
ーゼが作用することが知られ、特にリゾプス属由来のリ
パーゼが強い分解力を有している事が明らかにされてい
る。A method for decomposing polyester using lipase is known (Japanese Patent Laid-Open No. 52-827).
74). In the above method, for PCL, for example, Aspergillus, Niger, Geotrichum, Candidum, Rhizopus
・ Delemar, Rhizopus Arizus, Candid
a). It is known that lipases derived from syrindrasse, wheat germ, and pig pancreas act, and it has been revealed that lipases derived from the genus Rhizopus have a particularly strong decomposing ability.
【0009】しかしながら、その分解力は満足できるも
のではなく、より強い分解力を示す酵素の開発が強く望
まれていた。However, its decomposing power is not satisfactory, and there has been a strong demand for the development of an enzyme having a stronger decomposing power.
【0010】このような状況に鑑み、本発明者らは、シ
ュードモナス(Pseudomonas)属に属する微生物の産生
するリパーゼが、従来のリゾプス属由来のリパーゼと比
較して非常に強力な脂肪族ポリエステル分解能を有する
ことを始めて見いだして本発明を完成した。[0010] In view of such a situation, the present inventors have found that a lipase produced by a microorganism belonging to the genus Pseudomonas has a very strong ability to degrade an aliphatic polyester as compared with a conventional lipase derived from the genus Rhizopus. The present invention has been completed for the first time by finding out.
【0011】更に本発明は脂肪族ポリエステル分解能を
有するリパーゼを固定化して用いることによって、脂肪
族ポリエステルを材料とした繊維等の表面を処理し、繊
維等の強度は保持したまま、その風合いを改善すること
ができる方法をも発明完成した。[0011] Further, the present invention improves the texture while maintaining the strength of fibers and the like by treating the surface of fibers and the like made of aliphatic polyester by immobilizing and using lipase having the ability to degrade aliphatic polyester. A method that can be done has also been invented.
【0012】[0012]
【課題を解決するための手段】本発明の分解対象として
の脂肪族ポリエステルとは、ポリグリコシド、ポリ乳
酸、ポリヒドロキシブチレート、PCL、ヒドロキシバ
リレートおよびそれらの共重合体などが挙げられる。そ
の中でも、PCL等は酵素分解性に優れた素材である。The aliphatic polyester to be decomposed in the present invention includes polyglycoside, polylactic acid, polyhydroxybutyrate, PCL, hydroxyvalerate and copolymers thereof. Among them, PCL and the like are materials excellent in enzymatic degradation.
【0013】本発明の第1の発明はシュードモナス属に
属する微生物の産生するリパーゼを用いた脂肪族ポリエ
ステルの分解法に関する。The first invention of the present invention relates to a method for decomposing an aliphatic polyester using a lipase produced by a microorganism belonging to the genus Pseudomonas.
【0014】使用できるリパーゼとしてはシュードモナ
ス属由来で脂肪族ポリエステル分解能を有するリパーゼ
であれば何れでも使用できる。例えばリパーゼPS(天
野製薬製:シュードモナス・セパシア由来)、リパーゼ
AK(天野製薬製:シュードモナス・フローレッセンス
由来)が挙げられる。より好ましくはリパーゼPSが使
用できる。これらのリパーゼは粗製品であっても高度に
精製されていてもかまわない。As the lipase that can be used, any lipase derived from the genus Pseudomonas and having the ability to degrade aliphatic polyesters can be used. Examples thereof include lipase PS (manufactured by Amano Pharmaceutical: derived from Pseudomonas cepacia) and lipase AK (manufactured by Amano Pharmaceutical: derived from Pseudomonas florescens). More preferably, lipase PS can be used. These lipases can be crude or highly purified.
【0015】分解対象の脂肪族ポリエステルは酵素との
接触面積を大きくするためにできるだけ細かく分散させ
ることが望ましく、例えば細い繊維状、薄い膜状、粉末
状とすることが望ましい。It is desirable to disperse the aliphatic polyester to be decomposed as finely as possible in order to increase the contact area with the enzyme. For example, it is desirable to disperse the aliphatic polyester in the form of a fine fiber, a thin film, or a powder.
【0016】リパーゼを用いて脂肪族ポリエステルを分
解する反応条件は、使用するリパーゼが酵素活性を示す
範囲であればいずれの条件でも使用できるが、好ましく
は温度は10〜60℃で、pH4〜9の緩衝液中である。もち
ろん、反応系に適当な溶媒系、例えば適当な水分が存在
すれば固体系で作用させることもできる。The reaction conditions for decomposing the aliphatic polyester using lipase may be any conditions as long as the lipase used exhibits enzymatic activity, but preferably the temperature is 10 to 60 ° C. and the pH is 4 to 9 Buffer. Of course, the reaction can be carried out in a suitable solvent system, for example, a solid system if suitable water is present.
【0017】第2の発明は脂肪族ポリエステル分解能を
有するリパーゼを適当な担体に固定化し、当該固定化酵
素を用いてポリエステルの表面を処理する方法に関す
る。The second invention relates to a method for immobilizing a lipase having the ability to degrade an aliphatic polyester on a suitable carrier and treating the surface of the polyester with the immobilized enzyme.
【0018】本発明に使用できるリパーゼは脂肪族ポリ
エステルを分解できる酵素であれば何れでも使用でき
る。例えばシュードモナス属由来、リゾプス属由来の酵
素が好適に利用できる。より具体的に示すと例えばリパ
ーゼPS(天野製薬製:シュードモナス・セパシア由
来)、リパーゼAK(天野製薬製:シュードモナス・フ
ローレッセンス由来)、リパーゼF−AP(天野製薬
製:リゾプス・オリゼ由来)が挙げられる。より好まし
くはリパーゼPS、リパーゼF−APが使用できる。こ
れらのリパーゼは粗製品であっても高度に精製されてい
てもかまわない。As the lipase usable in the present invention, any enzyme capable of decomposing an aliphatic polyester can be used. For example, enzymes derived from Pseudomonas and Rhizopus can be suitably used. More specifically, for example, lipase PS (manufactured by Amano Pharmaceutical: derived from Pseudomonas cepacia), lipase AK (manufactured by Amano Pharmaceutical: derived from Pseudomonas florescens), and lipase F-AP (manufactured by Amano Pharmaceutical: derived from Rhizopus oryzae). Can be More preferably, lipase PS and lipase F-AP can be used. These lipases can be crude or highly purified.
【0019】用いる担体としては繊維などを浸漬処理す
るために水溶性の高分子担体が好ましく、例えばコポリ
(メチルビニルエーテル/無水マレイン酸)〔Copoly(m
ethylvinylester-co-maleic anhydride)〕(MAMEC)の他
に、ポリエチレングリコール、ポリアクリル酸、ポリア
ミン、ポリグルタミン酸、ポリリジン、デキストラン、
ヒドロキシエチルスターチ、カルボキシメチルセルロー
ス等が挙げられる。より好ましくはMAMECが使用でき
る。As the carrier to be used, a water-soluble polymer carrier is preferable for immersion treatment of fibers and the like. For example, copoly (methyl vinyl ether / maleic anhydride) [Copoly (m
ethylvinylester-co-maleic anhydride)) (MAMEC), polyethylene glycol, polyacrylic acid, polyamine, polyglutamic acid, polylysine, dextran,
Hydroxyethyl starch, carboxymethyl cellulose and the like can be mentioned. More preferably, MAMEC can be used.
【0020】当該担体にリパーゼを固定化する方法とし
ては、例えばイオン結合法および共有結合法があるが、
酵素を安定的に固定化するためには共有結合法が望まし
い。共有結合法として良く用いられる反応としては、活
性エステル化法をはじめ、シッフ塩基結合法、ジアゾニ
ウムカップリング法、臭化シアン活性化結合法、ジイソ
シアネート法、縮合試薬(カルボジイミド法)、トリア
ジニル誘導体結合法、ハロゲノアセチル誘導体結合法、
酸アジド誘導体結合法、ハロゲノアセチル誘導体結合法
等があるが、酵素固定化反応に際しては酵素の活性を低
下させない様に注意する必要がある。As a method for immobilizing lipase on the carrier, there are, for example, an ionic bonding method and a covalent bonding method.
In order to stably immobilize the enzyme, a covalent bonding method is desirable. Reactions often used as covalent bonding methods include active esterification, Schiff base bonding, diazonium coupling, cyanogen bromide activated bonding, diisocyanate, condensation reagent (carbodiimide), and triazinyl derivative bonding. , Halogenoacetyl derivative binding method,
There are an acid azide derivative binding method, a halogenoacetyl derivative binding method, and the like. However, in the enzyme immobilization reaction, care must be taken so as not to reduce the activity of the enzyme.
【0021】上記のようにして固定化したリパーゼを用
いて脂肪族ポリエステルを材料とした繊維又はフィルム
等を処理する条件としては使用するリパーゼが酵素活性
を示す範囲であればいずれの条件でも使用できるが、好
ましくは温度は10〜60℃で、pH4〜9の緩衝液中であ
る。The conditions for treating fibers or films made of aliphatic polyester using the lipase immobilized as described above can be used under any conditions as long as the lipase to be used exhibits enzymatic activity. Preferably, however, the temperature is between 10 and 60 ° C. in a buffer of pH 4-9.
【0022】このような固定化したリパーゼを用いて脂
肪族ポリエステル繊維などを処理するとリパーゼを固定
化しないで処理した時と比較して、その繊維の延伸強度
を損なうことなく表面のみを均一に分解することができ
る。つまり、浸漬時間を処理する繊維径や重合度などを
考慮して変化させることによって風合いの異なった脂肪
族ポリエステル繊維を得ることができる。もちろんリパ
ーゼは高分子担体に固定化されているため再利用が可能
であり、かつ安定性も向上する。When aliphatic polyester fibers or the like are treated with such an immobilized lipase, only the surface is uniformly decomposed without impairing the stretching strength of the fibers, as compared with the case where the treatment is performed without immobilizing the lipase. can do. That is, aliphatic polyester fibers having different textures can be obtained by changing the immersion time in consideration of the fiber diameter to be treated, the degree of polymerization, and the like. Of course, since lipase is immobilized on a polymer carrier, it can be reused and the stability is improved.
【0023】以下、本発明について実施例を示して詳細
に説明する。尚、本発明はこれらに限定されるものでは
ない。Hereinafter, the present invention will be described in detail with reference to examples. Note that the present invention is not limited to these.
【0024】[0024]
【実施例】実施例1 各種リパーゼのPCL繊維の分解 各種リパーゼを用いて、PCL繊維を試料として以下の
条件に従って処理した。処理後の繊維について乾燥時の
重量減少、単純抗張力測定により抗張力保持率を求め
た。さらに繊維試料の表面性状を走査型電子顕微鏡で観
察した。EXAMPLES Example 1 Decomposition of PCL fibers of various lipases PCL fibers were treated as samples using various lipases under the following conditions. The tensile strength retention of the treated fiber was determined by weight loss during drying and simple tensile strength measurement. Further, the surface properties of the fiber sample were observed with a scanning electron microscope.
【0025】0.1Mのリン酸緩衝液(pH7.0)に0.5W/V%と
なるように酵素を溶解し、該酵素液(10ml)にPCL末
延伸繊維試料(繊維径 275μm)約75mgを入れ、25℃で
緩やかにかき混ぜながら処理する。その反応条件及び結
果を表1に示す。The enzyme is dissolved in a 0.1 M phosphate buffer (pH 7.0) at a concentration of 0.5 W / V%, and about 75 mg of a PCL-end drawn fiber sample (fiber diameter 275 μm) is added to the enzyme solution (10 ml). Add and treat at 25 ° C with gentle stirring. The reaction conditions and results are shown in Table 1.
【0026】[0026]
【表1】 [Table 1]
【0027】尚、表1中でL-PSはリパーゼPS「アマ
ノ」、L-AKはリパーゼAK「アマノ」、L-F-APはリパー
ゼF-AP-15、L-A-6はリパーゼA「アマノ」6、L-M-10は
リパーゼM「アマノ」10、L-AY30はリパーゼAY「アマ
ノ」30、L-PEGはリパーゼPGE「アマノ」、N-Fはニュ
ーラーゼF、P-FはパンクレアチンF(以上、いずれも
天野製薬製 商品名)を示す。In Table 1, L-PS is lipase PS "Amano", L-AK is lipase AK "Amano", LF-AP is lipase F-AP-15, and LA-6 is lipase A "Amano" 6. , LM-10 is lipase M "Amano" 10, L-AY30 is lipase AY "Amano" 30, L-PEG is lipase PGE "Amano", NF is neurolase F, PF is pancreatin F (all of these are Amano Pharmaceutical product name).
【0028】表1からも明らかなようにシュードモナス
・セパシア由来のリパーゼ、即ちリパーゼPS「アマ
ノ」が非常に強い分解活性を示し、同じくシュードモナ
ス属であるシュードモナス・フローレッセンス由来のリ
パーゼ、即ちリパーゼAK「アマノ」もPCLを良く分
解する活性を有している。また、リゾプス・オリゼ由来
のリパーゼ、即ちリパーゼF-AP-15もPCLを良く分解
するが、同じリゾプス属であるリゾプス・ニベウス由来
のリパーゼ、即ちニューラーゼFはほとんど分解活性を
示さず、その他のリパーゼも分解活性を示さないことが
判る。As is clear from Table 1, the lipase derived from Pseudomonas cepacia, ie, the lipase PS "Amano", has a very strong degrading activity, and the lipase derived from Pseudomonas florescens, also belonging to the genus Pseudomonas, namely lipase AK " Amano also has the activity of degrading PCL well. In addition, lipase derived from Rhizopus oryzae, ie, lipase F-AP-15, also degrades PCL well, but lipase derived from Rhizopus niveus, which is the same genus of Rhizopus, ie, Neulase F, shows almost no degrading activity, It can be seen that the lipase does not show any decomposition activity.
【0029】実施例2 リパーゼPS「アマノ」による
PCL末延伸繊維の生分解 リパーゼPS「アマノ」を用い、酵素濃度を0.1W/V%で
実施例1と同様にして反応し、反応時間と分解度合いを
測定し、重量減少率(Wr/Wo)および抗張力残存比
(σB,r/σB,o)の経時的変化を求めた。その結果を表
2及び図1に示す。 Example 2 By lipase PS "Amano"
Using a biodegradable lipase PS “Amano” of drawn PCL powder at an enzyme concentration of 0.1 W / V%, the reaction was carried out in the same manner as in Example 1, the reaction time and the degree of decomposition were measured, and the weight loss rate (W r / W o ) and the residual strength ratio (σ B , r / σ B , o ) over time were determined. The results are shown in Table 2 and FIG.
【0030】[0030]
【表2】 [Table 2]
【0031】反応時間が0時間は酵素無添加の緩衝液中
で1時間浸漬した結果を示した。When the reaction time was 0 hour, the results were immersed in a buffer solution containing no enzyme for 1 hour.
【0032】また、処理したPCL繊維を走査型電子顕
微鏡で観察した結果、30時間処理した繊維は酵素によっ
て大きく侵食されて分解している事が観察された。Further, as a result of observing the treated PCL fiber with a scanning electron microscope, it was observed that the fiber treated for 30 hours was greatly eroded by enzymes and decomposed.
【0033】実施例3 リパーゼAK「アマノ」による
PCL末延伸繊維の生分解 リパーゼAK「アマノ」を用い、酵素濃度を0.5W/V%で
実施例1と同様にして反応し、反応時間と分解度合いを
測定し、重量減少率(Wr/Wo)および抗張力残存比
(σB,r/σB,o)の経時的変化を求めた。その結果を表
3及び図2に示す。 Example 3 By lipase AK "Amano"
Using a biodegradable lipase AK “Amano” of drawn PCL powder at an enzyme concentration of 0.5 W / V%, the reaction was carried out in the same manner as in Example 1, the reaction time and the degree of decomposition were measured, and the weight loss rate (W r / W o ) and the residual strength ratio (σ B , r / σ B , o ) over time were determined. The results are shown in Table 3 and FIG.
【0034】[0034]
【表3】 [Table 3]
【0035】反応時間が0時間は酵素無添加の緩衝液中
で1時間浸漬した結果を示した。When the reaction time was 0 hour, the results were immersed in a buffer solution containing no enzyme for 1 hour.
【0036】実施例4 リパーゼF-AP-15によるPCL
末延伸繊維の生分解 リパーゼF-AP-15を用い、酵素濃度を0.2W/V%で実施例1
と同様にして反応し、反応時間と分解度合いを測定し、
重量減少率(Wr/Wo)および抗張力残存比(σB,r/
σB,o)の経時的変化を求めた。その結果を表4及び図
3に示す。 Example 4 PCL using lipase F-AP-15
Example 1 using biodegradable lipase F-AP-15 of undrawn fiber at an enzyme concentration of 0.2 W / V%
React in the same manner as above, measure the reaction time and the degree of decomposition,
Weight loss rate (W r / W o ) and residual tensile strength ratio (σ B , r /
σ B , o ) was determined over time. The results are shown in Table 4 and FIG.
【0037】[0037]
【表4】 [Table 4]
【0038】反応時間が0時間は酵素無添加の緩衝液中
で1時間浸漬した結果を示した。When the reaction time was 0 hour, the result was immersed for 1 hour in a buffer solution containing no enzyme.
【0039】実施例5 リパーゼPS「アマノ」による
PCL末延伸繊維の生分解に及ぼす酵素濃度の影響 リパーゼPS「アマノ」を用い、酵素濃度を0.065〜0.2
W/V%と変化させて実施例2と同様にして反応し、反応時
間と分解度合いを測定し、重量減少率(Wr/Wo)の経
時的変化を求めて反応時間依存度及び(Wr/Wo)1/2
を求めて酵素濃度依存度を検討した。その結果を表5、
図4及び図5に示す。 Example 5 By lipase PS "Amano"
Effect of enzyme concentration on biodegradation of PCL powder drawn fiber Using lipase PS "Amano", the enzyme concentration was adjusted to 0.065 to 0.2.
The reaction was carried out in the same manner as in Example 2 except that the reaction time was changed to W / V%, the reaction time and the degree of decomposition were measured, and the time-dependent change in the weight loss rate ( Wr / Wo ) was obtained to determine the reaction time dependency and ( Wr / Wo ) 1/2
Was determined, and the enzyme concentration dependence was examined. Table 5 shows the results.
4 and 5.
【0040】[0040]
【表5】 [Table 5]
【0041】いずれの場合も分解の初期では良好な直線
性が示され、分解速度が繊維の表面積に対して一次反応
で進むと考えられる。In each case, good linearity is exhibited at the beginning of the decomposition, and it is considered that the decomposition rate proceeds by a first-order reaction with respect to the surface area of the fiber.
【0042】実施例6 水溶性高分子に固定化したリパ
ーゼPS「アマノ」を用いたPCL繊維の分解 平均分子量約20,000のMAMEC 5.0gを0.1M−酢酸緩衝液
(pH5.4)90mlに溶解させる。リパーゼPS「アマノ」
酵素1.0gを同上緩衝液10mlに溶解させ、両者を20℃で混
合し、24時間攪拌反応させる。反応後、100,000分子量
分画様限外ろ過膜を用いて分画精製することにより未反
応の酵素を除去し、濃縮後凍結乾燥してMAMEC−固
定化酵素を得る。ニンヒドリン法により固定化酵素濃度
を定量した結果、4.5wt%が得られた。 Example 6 Lipa immobilized on a water-soluble polymer
Decomposition of PCL fiber using ASE PS "Amano" 5.0 g of MAMEC having an average molecular weight of about 20,000 is dissolved in 90 ml of 0.1 M acetate buffer (pH 5.4). Lipase PS "Amano"
1.0 g of the enzyme is dissolved in 10 ml of the same buffer solution, and the two are mixed at 20 ° C. and reacted with stirring for 24 hours. After the reaction, unreacted enzyme is removed by fractionation and purification using a 100,000 molecular weight fractionation-like ultrafiltration membrane, and concentrated and freeze-dried to obtain a MAMEC-immobilized enzyme. As a result of quantifying the concentration of the immobilized enzyme by the ninhydrin method, 4.5 wt% was obtained.
【0043】上記で得られた水溶性高分子に固定化した
リパーゼPS「アマノ」を用い、酵素濃度を0.1W/V%で
実施例4と同様にして反応し、反応時間と分解度合いを
測定し、重量減少率(Wr/Wo)および抗張力残存比
(σB,r/σB,o)の経時的変化を求めた。その結果を表
6及び図6に示す。Using the lipase PS "Amano" immobilized on the water-soluble polymer obtained above, the reaction was carried out at an enzyme concentration of 0.1 W / V% in the same manner as in Example 4, and the reaction time and the degree of decomposition were measured. Then, the time-dependent changes in the weight loss rate ( Wr / Wo ) and the residual tensile strength ratio (? B , r /? B , o ) were determined. The results are shown in Table 6 and FIG.
【0044】[0044]
【表6】 [Table 6]
【0045】反応時間が0時間は酵素無添加の緩衝液中
で1時間浸漬した結果を示した。When the reaction time was 0 hour, the results were immersed in a buffer solution containing no enzyme for 1 hour.
【0046】また、処理したPCL繊維を走査型電子顕
微鏡で観察した結果、50時間処理した繊維の表面は実施
例2の時と比較して非常に均一に分解されていることが
観察された。また、図6よりも明らかなように、重量減
少率は実施例2の固定化されていないリパーゼPS「ア
マノ」を用いた時と大差無く変化しているにもかかわら
ず、抗張力残存比の急激な低下はみられない。つまり、
PCL繊維の表面が非常に均一に分解され、繊維の表面
を処理することができた。Further, as a result of observing the treated PCL fiber with a scanning electron microscope, it was observed that the surface of the fiber treated for 50 hours was more uniformly decomposed than in Example 2. Further, as is clear from FIG. 6, although the weight reduction rate has not changed much from the time when the non-immobilized lipase PS “Amano” of Example 2 was used, the rapid decrease in the tensile strength residual ratio was observed. No significant decrease is seen. That is,
The surface of the PCL fiber was decomposed very uniformly, and the surface of the fiber could be treated.
【0047】実施例7 水溶性高分子に固定化したリパ
ーゼAK「アマノ」を用いたPCL繊維の分解 水溶性高分子と結合したリパーゼAK「アマノ」を用い
て、実施例6と同様にして操作した。その結果実施例6
と同様に重量減少率は実施例3の固定化されていないリ
パーゼAK「アマノ」を用いた時と大差はなかったが、
抗張力残存比に急激な低下はみられず、繊維の強度は比
較的保持していた。 Example 7 Lipa immobilized on a water-soluble polymer
Decomposition of PCL fiber using AK AK “Amano” The same operation as in Example 6 was carried out using lipase AK “Amano” bound to a water-soluble polymer. As a result, Example 6
Similarly, the weight loss rate was not much different from that when the non-immobilized lipase AK “Amano” of Example 3 was used,
There was no sharp drop in the tensile strength residual ratio, and the fiber strength was relatively maintained.
【0048】実施例8 水溶性高分子に固定化したリパ
ーゼF-AP-15を用いたPCL繊維の分解 水溶性高分子と結合したリパーゼF-AP-15を用いて、実
施例6と同様にして操作した。その結果実施例6と同様
に重量減少率は実施例4の固定化されていないリパーゼ
F-AP-15を用いた時と大差はなかったが、抗張力残存比
に急激な変化はみられなかった。 Example 8 Lipa immobilized on a water-soluble polymer
Decomposition of PCL fiber using lyase F-AP-15 The same operation as in Example 6 was performed using lipase F-AP-15 bound to a water-soluble polymer. As a result, as in Example 6, the weight loss rate was the same as that of Example 4
Although there was not much difference from when F-AP-15 was used, there was no sharp change in the tensile strength residual ratio.
【0049】[0049]
【発明の効果】本発明により生分解性高分子ポリマー、
とりわけ脂肪族ポリエチレンであるポリカプロラクトン
をシュードモナス属由来のリパーゼを用いて効率よく分
解することができる。さらにリパーゼを水溶性高分子担
体に固定化することによって得られた固定化酵素を用い
るとPCL繊維などの表明を分解して繊維などの風合い
を改良することができ、この際には当該繊維などの強度
を比較的損なわないという効果がある。According to the present invention, a biodegradable polymer,
In particular, polycaprolactone, which is an aliphatic polyethylene, can be efficiently decomposed using a lipase derived from Pseudomonas. Further, by using an immobilized enzyme obtained by immobilizing lipase on a water-soluble polymer carrier, expressions such as PCL fibers can be decomposed and the texture of the fibers can be improved. This has the effect of relatively not impairing the strength.
【図1】実施例2のリパーゼPS「アマノ」を用いた時
の反応時間と重量減少率(Wr/Wo)および抗張力残存
比(σB,r/σB,o)の経時的変化を示す。図中で●は重
量減少率を示し、○は抗張力残存比を示す。FIG. 1 Changes over time in reaction time, weight loss rate (W r / W o ) and residual tensile strength ratio (σ B , r / σ B , o ) when using lipase PS “Amano” of Example 2 Is shown. In the figure, ● indicates the weight reduction rate, and ○ indicates the residual tensile strength ratio.
【図2】実施例3のリパーゼAK「アマノ」を用いた時
の反応時間と重量減少率(Wr/Wo)および抗張力残存
比(σB,r/σB,o)の経時的変化を示す。図中で●は重
量減少率を示し、○は抗張力残存比を示す。[FIG. 2] Time-dependent changes in reaction time, weight loss rate (W r / W o ) and residual tensile strength ratio (σ B , r / σ B , o ) when using lipase AK “Amano” of Example 3 Is shown. In the figure, ● indicates the weight reduction rate, and ○ indicates the residual tensile strength ratio.
【図3】実施例4のリパーゼF-AP-15を用いた時の反応
時間と重量減少率(Wr/Wo)および抗張力残存比(σ
B,r/σB,o)の経時的変化を示す。図中で●は重量減少
率を示し、○は抗張力残存比を示す。FIG. 3 shows the reaction time, weight loss rate (W r / W o ) and residual tensile strength ratio (σ) when lipase F-AP-15 of Example 4 was used.
B, submitted changes over time r / σ B, o). In the figure, ● indicates the weight reduction rate, and ○ indicates the residual tensile strength ratio.
【図4】実施例4のリパーゼPS「アマノ」を用いたと
きの反応時間と重量減少率の関係を示す。図中で、
、及びは各々酵素濃度が0.065、0.10、0.15及び
0.20W/V%の時の結果を示す。FIG. 4 shows the relationship between the reaction time and the weight loss rate when the lipase PS “Amano” of Example 4 was used. In the figure,
, And have enzyme concentrations of 0.065, 0.10, 0.15 and
The result at the time of 0.20 W / V% is shown.
【図5】実施例4のリパーゼPS「アマノ」を用いたと
きの反応時間と重量減少率の平方根の関係を示す。図中
で、、及びは各々酵素濃度が0.065、0.10、0.1
5及び0.20W/V%の時の結果を示す。FIG. 5 shows the relationship between the reaction time and the square root of the weight loss rate when the lipase PS “Amano” of Example 4 was used. In the figure, and indicate that the enzyme concentrations are 0.065, 0.10, 0.1, respectively.
The results at 5 and 0.20 W / V% are shown.
【図6】実施例6の固定化したリパーゼSP「アマノ」
を用いた時の反応時間と重量減少率(Wr/Wo)および
抗張力残存比(σB,r/σB,o)の経時的変化を示す。図
中で●は重量減少率を示し、○は抗張力残存比を示す。FIG. 6: Immobilized lipase SP “Amano” of Example 6.
The time-dependent changes in the reaction time, weight reduction rate (W r / W o ) and residual tensile strength ratio (σ B , r / σ B , o ) when using are shown. In the figure, ● indicates the weight reduction rate, and ○ indicates the residual tensile strength ratio.
フロントページの続き (51)Int.Cl.7 識別記号 FI // C08J 11/10 C08J 11/10 C08L 67:02 C08L 67:02 (58)調査した分野(Int.Cl.7,DB名) C12P 7/64 C08G 63/78 C08J 7/00 - 11/10 D06M 16/00 C08L 67:02 BIOSIS(DIALOG) CA(STN) JICSTファイル(JOIS) REGISTRY(STN) WPI(DIALOG)Continuation of the front page (51) Int.Cl. 7 identification code FI // C08J 11/10 C08J 11/10 C08L 67:02 C08L 67:02 (58) Investigated field (Int.Cl. 7 , DB name) C12P 7/64 C08G 63/78 C08J 7/00-11/10 D06M 16/00 C08L 67:02 BIOSIS (DIALOG) CA (STN) JICST file (JOIS) REGISTRY (STN) WPI (DIALOG)
Claims (1)
るポリカプロラクトンを分解する方法において、シュー
ドモナス・セパシア由来のリパーゼを用いることを特徴
とする脂肪族ポリエステルの分解法。1. A method for decomposing polycaprolactone, which is an aliphatic polyester, using a lipase, wherein a lipase derived from Pseudomonas cepacia is used.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP17903292A JP3194792B2 (en) | 1992-06-12 | 1992-06-12 | Decomposition method of aliphatic polyester using enzyme |
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP17903292A JP3194792B2 (en) | 1992-06-12 | 1992-06-12 | Decomposition method of aliphatic polyester using enzyme |
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| Application Number | Title | Priority Date | Filing Date |
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| JP2001110407A Division JP3470109B2 (en) | 2001-04-09 | 2001-04-09 | Surface treatment method of aliphatic polyester fiber using enzyme |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH05344897A JPH05344897A (en) | 1993-12-27 |
| JP3194792B2 true JP3194792B2 (en) | 2001-08-06 |
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ID=16058924
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| Application Number | Title | Priority Date | Filing Date |
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| JP17903292A Expired - Fee Related JP3194792B2 (en) | 1992-06-12 | 1992-06-12 | Decomposition method of aliphatic polyester using enzyme |
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Families Citing this family (18)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE4415127A1 (en) * | 1994-04-29 | 1995-11-02 | Boehringer Mannheim Gmbh | Degradable polymers |
| KR100188446B1 (en) | 1995-02-28 | 1999-06-01 | 미쯔이카가쿠 가부시키가이샤 | Method of degrading polymer |
| TR199701705T1 (en) * | 1995-06-27 | 1998-04-21 | Unilever N.V. | Immobile enzyme and its use in the processing of triglyceride oils. |
| BR9707840A (en) * | 1996-03-06 | 2000-01-04 | Univ California | Processes to alter the wettability and water absorbency of textile fibers, to increase the wettability and water absorbency in cotton fibers and to alter the physical properties of polyester fibers, and aromatic polyester fiber. |
| JP2889953B2 (en) * | 1996-03-27 | 1999-05-10 | 工業技術院長 | Degradation method of microorganism-produced aliphatic polyester using anaerobic bacteria |
| GB9613758D0 (en) * | 1996-07-01 | 1996-09-04 | Unilever Plc | Detergent composition |
| TR199901337T2 (en) * | 1996-12-19 | 1999-10-21 | Unilever N.V. | Immobilized enzyme and its use in the treatment of triglyceride oils. |
| DE19706024A1 (en) * | 1997-02-17 | 1998-08-20 | Wolff Walsrode Ag | Process for modifying products or semi-finished products from molding compounds consisting of mixtures of thermoplastics |
| DE19706023A1 (en) * | 1997-02-17 | 1998-08-20 | Bayer Ag | Degradation of biodegradable polymers with enzymes |
| DE19754063A1 (en) * | 1997-12-05 | 1999-06-10 | Bayer Ag | Degradation of biodegradable polymers |
| US6254645B1 (en) | 1999-08-20 | 2001-07-03 | Genencor International, Inc. | Enzymatic modification of the surface of a polyester fiber or article |
| US6933140B1 (en) | 1999-11-05 | 2005-08-23 | Genencor International, Inc. | Enzymes useful for changing the properties of polyester |
| JP4765273B2 (en) * | 2004-06-23 | 2011-09-07 | 三菱化学株式会社 | Decomposition method of polyester resin |
| JP5630597B2 (en) * | 2008-12-04 | 2014-11-26 | 東洋製罐株式会社 | Method for treating organic waste containing biodegradable resin moldings |
| JP2013023643A (en) * | 2011-07-25 | 2013-02-04 | National Institute For Agro-Environmental Science | Method for accelerating decomposition of biodegradable plastic material |
| FR2984354A1 (en) * | 2011-12-20 | 2013-06-21 | Centre Nat Rech Scient | PROCESS FOR PREPARING POLYMER ALLOY / ENZYMES |
| KR102268532B1 (en) | 2013-12-11 | 2021-06-24 | 노보자임스 에이/에스 | Cutinase variants and polynucleotides encoding same |
| BR112022022626A2 (en) * | 2020-05-29 | 2023-01-10 | Rhodia Poliamida E Espec Sa | METHODS FOR DEGRADING AN EPOXY RESIN AND FOR RECYCLING A COMPOSITE MATERIAL, AND, USE OF A GLUTHATHIONE S-TRANSFERASE |
-
1992
- 1992-06-12 JP JP17903292A patent/JP3194792B2/en not_active Expired - Fee Related
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| Publication number | Publication date |
|---|---|
| JPH05344897A (en) | 1993-12-27 |
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