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JPH0771502B2 - Decomposition method of polyamide polymer - Google Patents

Decomposition method of polyamide polymer

Info

Publication number
JPH0771502B2
JPH0771502B2 JP12317991A JP12317991A JPH0771502B2 JP H0771502 B2 JPH0771502 B2 JP H0771502B2 JP 12317991 A JP12317991 A JP 12317991A JP 12317991 A JP12317991 A JP 12317991A JP H0771502 B2 JPH0771502 B2 JP H0771502B2
Authority
JP
Japan
Prior art keywords
nylon
polyamide
wood
polymer compound
culture
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
JP12317991A
Other languages
Japanese (ja)
Other versions
JPH05304968A (en
Inventor
幸史 上園
哲也 出口
友昭 西田
義昌 高原
義博 片山
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Kobe Steel Ltd
Original Assignee
Kobe Steel Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Kobe Steel Ltd filed Critical Kobe Steel Ltd
Priority to CA002078859A priority Critical patent/CA2078859C/en
Priority to EP9292902879A priority patent/EP0596113A4/en
Priority to PCT/JP1992/000038 priority patent/WO1992013087A1/en
Publication of JPH05304968A publication Critical patent/JPH05304968A/en
Publication of JPH0771502B2 publication Critical patent/JPH0771502B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • Y02P20/143Feedstock the feedstock being recycled material, e.g. plastics
    • 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
    • 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
    • Y02W30/78Recycling of wood or furniture waste

Landscapes

  • Preparation Of Compounds By Using Micro-Organisms (AREA)
  • Processing Of Solid Wastes (AREA)
  • Processes Of Treating Macromolecular Substances (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • Manufacture Of Porous Articles, And Recovery And Treatment Of Waste Products (AREA)

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、ポリアミド系高分子化
合物の分解法に関するものであり、更に詳細には、水不
溶性の高分子ナイロン等も強力に分解することのできる
新しい工業的方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for decomposing a polyamide polymer compound, and more particularly to a new industrial method capable of decomposing water-insoluble polymer nylon etc. strongly. Is.

【0002】したがって本発明は、現在その処理が大き
な社会問題となっているプラスチック廃棄物の処理に大
きな貢献をなすのみでなく、その分解メカニズムを解明
することにより、生分解性高分子化合物のデザインにも
大きな期待をつなぐものである。
Therefore, the present invention not only makes a great contribution to the treatment of plastic waste, whose treatment is now a major social problem, but also elucidates the decomposition mechanism to design biodegradable polymer compounds. It is also a great expectation.

【0003】[0003]

【従来の技術】従来、ポリアミド系化合物の分解法とし
ては、細菌(Flavobacterium sp.K
I72)を用いる方法が知られている(Agr.Bio
l.Chem.,39(6),1219−1223(1
975);発酵工学,60(5),363−375(1
982))。
2. Description of the Related Art Conventionally, as a method of decomposing a polyamide compound, bacteria (Flavobacterium sp.
I72) is known (Agr. Bio).
l. Chem. , 39 (6), 1219-1223 (1
975); Fermentation Engineering, 60 (5), 363-375 (1
982)).

【0004】しかしながらこれらの従来法は、いずれ
も、水溶性低分子ナイロン6オリゴマー(分子量約20
00まで)を処理する方法であって、水不溶性の高分子
ナイロン(分子量約10,000以上)を分解すること
はできない。
However, all of these conventional methods are water-soluble low molecular weight nylon 6 oligomers (molecular weight of about 20).
00) and cannot decompose water-insoluble polymer nylon (molecular weight of about 10,000 or more).

【0005】[0005]

【発明が解決しようとする課題】プラスチック廃棄物の
処理で特に問題となるのは、水溶性プラスチックの処理
ではなく水に溶けない水不溶性高分子物質の処理であっ
て、ポリアミド系高分子化合物廃棄物においても同様で
ある。しかしながら、従来法では上記したことからも明
らかなように、水不溶性のナイロンを分解することはで
きず、これでは所期の目的を達成することはできない。
What is particularly problematic in the treatment of plastic waste is not the treatment of water-soluble plastics but the treatment of water-insoluble polymer substances that are insoluble in water. The same applies to things. However, as is clear from the above, the conventional method cannot decompose the water-insoluble nylon, and this cannot achieve the intended purpose.

【0006】[0006]

【課題を解決するための手段】本発明は、このような技
術の現状に鑑み、プラスチック公害の防止を目的として
なされたものであって、従来法では分解することのでき
なかった水不溶性のポリアミド系高分子化合物も効率よ
く分解することのできる方法を開発する目的でなされた
ものである。
SUMMARY OF THE INVENTION The present invention has been made in view of the present state of the art in order to prevent plastic pollution, and is a water-insoluble polyamide that cannot be decomposed by conventional methods. The high-molecular compounds are also made for the purpose of developing a method capable of efficiently decomposing.

【0007】上記目的を達成するために検討を行い、二
次公害を防止するという観点から、従来法をひきつづき
生物処理に着目した。しかしながら、従来法にしたがっ
て細菌に注目し、各種細菌について検討したけれども目
的とする細菌を発見するには至らなかった。
[0007] In order to achieve the above object, studies were conducted, and from the viewpoint of preventing secondary pollution, attention was paid to biological treatment, continuing from the conventional method. However, although attention was paid to bacteria according to the conventional method and various bacteria were examined, the desired bacteria could not be found.

【0008】そこで広く他の微生物について検討するこ
ととし、ナイロン等プラスチックの分解とは全く関連性
のない木材腐朽菌にはじめて着目した。しかしながら、
所期の目的を達成するには至らなかったので、培養条
件、処理条件等について発想の大転換の必要性を認め
た。
Therefore, it was decided to widely study other microorganisms, and attention was first focused on wood-destroying fungi that have no relation to the decomposition of plastics such as nylon. However,
Since the intended purpose was not achieved, the necessity of a major change in the idea of culture conditions, treatment conditions, etc. was recognized.

【0009】そこで、微生物の生育やその処理に必要で
あって添加こそすれ減少させてはならない栄養成分であ
る窒素源及び/又は炭素源について、技術常識とは全く
逆にこれをカットし、また、ポリアミド系高分子化合物
を粉末状にして処理したところ、従来分解処理すること
のできなかった不溶性のポリマーを分解するのにはじめ
て成功し、本発明を完成するに至った。以下本発明を詳
述するが、本明細書において、ポリアミド系高分子化合
物をナイロンという場合もある。
Therefore, nitrogen sources and / or carbon sources, which are nutrient components necessary for the growth and treatment of microorganisms and which should not be reduced by addition, are cut out in a manner contrary to common general technical knowledge. As a result of treating the polyamide-based polymer compound into a powder form, it succeeded in decomposing an insoluble polymer that could not be conventionally decomposed, and completed the present invention. The present invention will be described in detail below, but in the present specification, the polyamide-based polymer compound may be referred to as nylon.

【0010】本発明を実施するには、分解処理しようと
するポリアミド系高分子化合物を、窒素含有量及び/又
は炭素含有量を低下せしめた培地上で木材腐朽性担子菌
により培養処理する必要がある。
In order to carry out the present invention, it is necessary to cultivate the polyamide polymer compound to be decomposed by a wood-destroying basidiomycete on a medium having a reduced nitrogen content and / or carbon content. is there.

【0011】本発明においては、Lentinus l
epideus等褐色腐朽性担子菌を含む木材腐朽性担
子菌が広く使用できるが、特に白色腐朽性担子菌つまり
リグニン分解菌が有利に使用できる。
In the present invention, Lentinus l
Wood-destroying basidiomycetes including brown-rotting basidiomycetes such as epideus can be widely used, and particularly white-rotting basidiomycetes, that is, lignin-degrading bacteria can be advantageously used.

【0012】これら木材腐朽性担子菌としては、次のよ
うな各属に属する微生物が広く例示される:コリオラス
属(Coriolus versicolor IFO
7043等)、ファネロケーテ属(Phaneroc
haete chrysosporium ATCC
34541等)、トラメテス属(Trametesdi
ckinsii IFO 6488等)、ポリポラス属
(Polyporus mikadoi IFO 65
17等)、ステレウム属(Stereumfrustu
losum IFO 4932等)、ガノデルマ属(G
anoderma applanatum IFO 6
499等)、レンチテス属(Lenzites bet
ulina IFO 8714等)、ホーメス属(Fo
mes fomentarius IFO 30371
等)、ポロディスキュラス属(Porodisculu
s pendulus IFO 4967等)、レンチ
ヌス属(Lentinus edodes IFO 3
1336、L.lepideus IFO 7043
等)、セルプラ属(Serpula lacryman
s IFO 8697等)その他。
As these wood-destroying basidiomycetes, microorganisms belonging to the following genera are widely exemplified: Coriolus versicolor IFO.
7043 etc.), genus Phanelocete (Phaneroc)
haete chrysosporium ATCC
34541), Trametesdi (Trametesdi)
ckinsii IFO 6488 etc., Polyporus genus (Polyporus mikadoi IFO 65
17, etc., genus Stereumfrustu
losum IFO 4932 etc.), Ganoderma (G
anoderoma applanatum IFO 6
499), Lentites bet
ulina IFO 8714 etc.), genus (Fo)
mes fomentarius IFO 30371
Etc.), Porodisculus (Porodisculus)
s pendulus IFO 4967, etc., Lentinus edodes IFO 3
1336, L.S. lepideus IFO 7043
Etc.), genus of Serpula (Serpula lacryman)
s IFO 8697 etc.) Others.

【0013】本発明において使用可能な木材腐朽性担子
菌としては、上記した微生物のほか、NK−1148株
(FERM BP−1859)も使用することができ、
本菌株はポリアミド系高分子化合物を高度に分解するこ
とがる。このNK−1148株の菌学的性質の詳細につ
いては、特開平2−259180号に開示されている。
As the wood-destroying basidiomycetes usable in the present invention, in addition to the above-mentioned microorganisms, NK-1148 strain (FERM BP-1859) can be used.
This strain can highly decompose polyamide polymer compounds. Details of the mycological properties of the NK-1148 strain are disclosed in JP-A-2-259180.

【0014】本発明においては、ポリアミド系高分子化
合物を上記した1種又はそれ以上の木材腐朽性担子菌で
処理して分解するのであるが、この場合、培地中の窒素
濃度及び/又は炭素濃度制限下において処理することを
特徴とする。
In the present invention, the polyamide polymer compound is treated with one or more of the above wood-destroying basidiomycetes and decomposed. In this case, the nitrogen concentration and / or carbon concentration in the medium are It is characterized by processing under restrictions.

【0015】具体的にはポリアミド系高分子化合物を窒
素濃度及び/又は炭素濃度を制限した培地上に置き及び
/又は培地中に混合し、これに木材腐朽性担子菌を接種
し、至適温度例えば15〜35℃で静置培養すれば、5
〜30日間程度で高分子化合物を分解することができる
のである。また、上記した培養条件のもとで(通気及び
/又は攪拌しながら)液体培養することによっても、ポ
リアミド系高分子化合物を分解することが可能である。
Specifically, the polyamide polymer compound is placed on and / or mixed with a medium in which the nitrogen concentration and / or carbon concentration is limited, and this is inoculated with a wood-destroying basidiomycete at an optimum temperature. For example, if static culture is performed at 15 to 35 ° C, 5
The polymer compound can be decomposed in about 30 days. The polyamide-based polymer compound can also be decomposed by liquid culture under the above-mentioned culture conditions (aeration and / or stirring).

【0016】この場合、微生物を培養するにもかかわら
ず、窒素濃度及び/又は炭素濃度を制限することが重要
である。窒素濃度は及び/又は炭素濃度は、可及的少
量、好ましくは含有しないのが良いが、工業上の面から
は0.1g/l以下であれば良く、0.05g/l以下
とすれば更に好結果が得られ、炭素濃度は、0.2g/
l以下とすれば良い。窒素および炭素以外の培地組成に
ついては格別の制限はなく、木材腐朽菌の生育に常用さ
れる各成分が適宜使用される。本発明においては、上記
の窒素及び/又は炭素に関する条件が満たされれば、固
体培養及び液体培養を問わずいづれも所期の目的が達成
されるので、窒素源や炭素源を完全にカットした培地、
例えば水のみに(必要あれば寒天及び/又はpH調整剤
等は添加する)ポリアミド系高分子化合物と木材腐朽菌
を加えてインキューベートすることによっても、高分子
化合物を分解することができる。
In this case, it is important to limit the nitrogen concentration and / or the carbon concentration despite culturing the microorganism. The nitrogen concentration and / or the carbon concentration is preferably as small as possible, preferably not contained, but from an industrial viewpoint, it may be 0.1 g / l or less, and if it is 0.05 g / l or less. Even better results were obtained, and the carbon concentration was 0.2 g /
It may be set to 1 or less. There is no particular limitation on the medium composition other than nitrogen and carbon, and each component commonly used for growing wood-destroying fungi is appropriately used. In the present invention, if the above-mentioned conditions for nitrogen and / or carbon are satisfied, the intended purpose can be achieved regardless of whether it is solid culture or liquid culture. ,
For example, the polymer compound can also be decomposed by adding a polyamide polymer compound and a wood-destroying fungus to water alone (adding agar and / or a pH adjuster or the like if necessary) and incubating.

【0017】また、本発明においては、木材腐朽性担子
菌を使用するのであるが、菌自体のほか、その培養物及
び/又はその処理物も使用することができる。該培養物
とは、菌を培養して得た菌体及び培養液の混合物を広く
指すが、本発明においては、菌体培養物から分離したウ
ェットケーキ等の菌体、その残渣、及び、固体物をすべ
て除去した後の培養液を利用することもできる。また、
その処理物とは、上記したものを濃縮、乾燥、または希
釈したものをすベて指すものである。
In the present invention, wood-destroying basidiomycetes are used, but in addition to the fungi themselves, cultures and / or processed products thereof can also be used. The culture broadly refers to a mixture of cells and a culture solution obtained by culturing a bacterium, but in the present invention, cells such as wet cake separated from the cell culture, its residue, and solids. It is also possible to use the culture medium after removing all the substances. Also,
The processed product is a product obtained by concentrating, drying, or diluting the above-mentioned products.

【0018】本発明にしたがってポリアミド系高分子化
合物を分解処理するに際して、これらの高分子はそのま
まで用いても良いが、微生物やそれから生産される酵素
等との接触面積を増加させるため、細砕したり、粉末化
したり、あるいは細孔膜化するのが好適である。
When the polyamide polymer compound is decomposed according to the present invention, these polymers may be used as they are, but they are pulverized to increase the contact area with the microorganism and the enzyme produced therefrom. It is preferable that it is made into a powder, a powder, or a porous film.

【0019】本発明によれば、ポリアミドのうち線状の
合成ポリアミドであるナイロンmm、ナイロンmn及び
ナイロンnのほか、ポリアミド系の高分子化合物であれ
ば水不溶性の高分子(例えば分子量約80,000〜1
60,000)もすべて分解することができる。したが
って本発明によれば、ナイロン6、ナイロン66、ナイ
ロン610、ナイロン7、ナイロン9、ナイロン11、
ナイロン12等も自由に分解することができる。もちろ
んこれらの混合物も生分解可能である。以下、本発明の
実施例について述べる。
According to the present invention, in addition to nylon mm, nylon mn, and nylon n, which are linear synthetic polyamides among polyamides, a water-insoluble polymer (for example, a molecular weight of about 80 000-1
60,000) can also be decomposed. Therefore, according to the present invention, nylon 6, nylon 66, nylon 610, nylon 7, nylon 9, nylon 11,
Nylon 12 etc. can also be decomposed freely. Of course, these mixtures are also biodegradable. Examples of the present invention will be described below.

【0020】[0020]

【実施例1】細孔を有するナイロン膜(ザルトリウス社
製ナイロン66メンブレンフィルター)を窒素源を含ま
ない固体培地(KHPO 1.0g、NaHPO
0.2g、MgSO・7HO 0.1g、ZnS
・7HO 0.01mg、CuSO・5H
0.02mg、コハク酸ジメチル 1.46g、gl
ucose 20g、Agar 30g、水 1l)上
に置き各種微生物(白色腐朽性担子菌;Phanero
chaete chysosporiumATCC 3
4541、Coriolus versicoler
IFO 7043、NK−1148FERM BP−1
859、褐色腐朽性担子菌;Lentinus lep
ideus IFO 7043、Serpula la
crymans EPRI 6352、不完全菌;As
pergillus niger IFO 6341、
Penicillium citrinum IFO6
352、細菌;Bacillus subtillis
IFO 3134、Pseudomonas pau
cimobillis SYK−6)を接種し20〜2
8℃で20日間静置培養した。培養後、細孔膜をHFI
P(ヘキサフルオロイソプロパノール)で試料濃度0.
2%になるよう溶解しGPCで分析して(昭和電工製カ
ラムHFIP−80M;溶離液HFIP;流速1ml/
min;温度40℃;検出器RI)平均分子量の変化で
分解性を評価した。菌処理された試料の平均分子量を下
記の表1に示す。
Example 1 A nylon membrane having pores (nylon 66 membrane filter manufactured by Sartorius) was used as a solid medium (KH 2 PO 4 1.0 g, NaH 2 PO) containing no nitrogen source.
4 0.2g, MgSO 4 · 7H 2 O 0.1g, ZnS
O 4 · 7H 2 O 0.01mg, CuSO 4 · 5H 2 O
0.02 mg, dimethyl succinate 1.46 g, gl
ucose 20g, Agar 30g, water 1l) and put on various microorganisms (white-rotting basidiomycetes; Phanero
chaete chysosporium ATCC 3
4541, Coriolus versicolor
IFO 7043, NK-1148 FERM BP-1
859, brown-rot basidiomycete; Lentinus lep
ideaus IFO 7043, Serpula la
crymans EPRI 6352, imperfect bacteria; As
pergillus niger IFO 6341,
Penicillium citrinum IFO6
352, bacteria; Bacillus subtillis
IFO 3134, Pseudomonas pau
20 to 2 inoculated with C. mobilis SYK-6)
Static culture was carried out at 8 ° C for 20 days. After culturing, the porous membrane was HFI
P (hexafluoroisopropanol) with a sample concentration of 0.
Dissolved to 2% and analyzed by GPC (Showa Denko column HFIP-80M; eluent HFIP; flow rate 1 ml /
min; temperature 40 ° C .; detector RI) Degradability was evaluated by the change in average molecular weight. The average molecular weight of the sample treated with the bacteria is shown in Table 1 below.

【0021】[0021]

【表1】 [Table 1]

【0022】[0022]

【実施例2】実施例1において分解が認められた3種の
白色腐朽性担子菌(Phanerochaete ch
ysosporium,Coriolus versi
coler,NK−1148)を用いて実施例1の培養
条件に準じ、窒素濃度の異なる固体培地(窒素濃度を酒
石酸アンモニウムを用いて0g/l、0.05g/l、
0.10g/l、0.15g/lとし、他は実施例1と
同様の培地組成である)で静置培養を行い分解性をGP
Cで調べた。その結果を下記の表2に示す。
[Example 2] Three types of white-rotting basidiomycetes (Phanerochaete ch.) Which were found to be decomposed in Example 1
ysosporium, Coriolus versi
colorer, NK-1148) according to the culturing conditions of Example 1, and a solid medium having a different nitrogen concentration (nitrogen concentration was 0 g / l, 0.05 g / l using ammonium tartrate,
0.10 g / l, 0.15 g / l, the other medium having the same medium composition as in Example 1) was subjected to static culture and the degradability was GP.
Checked in C. The results are shown in Table 2 below.

【0023】[0023]

【表2】 [Table 2]

【0024】[0024]

【実施例3】実施例1において分解が認められた白色腐
朽菌(NK−1148)を用いて、実施例1の培養条件
に準じ、炭素濃度の異なる固体培地(炭素濃度が0g/
l、0.2g/l、0.4g/l、8.0g/lとなる
ようにグルコースをそれぞれ添加し、コハク酸ジメチル
及び(NHSOをそれぞれ0g、0.58gと
した以外は実施例1と同様の培地組成である)で静置培
養を行い分解性をGPCで調べた。その結果を下記の表
3に示す。
[Example 3] Using the white-rot fungus (NK-1148), which was found to be decomposed in Example 1, solid medium having different carbon concentrations (carbon concentration 0 g /
Glucose was added so as to be 1, 0.2 g / l, 0.4 g / l, and 8.0 g / l, and dimethyl succinate and (NH 4 ) 2 SO 4 were changed to 0 g and 0.58 g, respectively. Is the same medium composition as in Example 1) and the degradability was examined by GPC. The results are shown in Table 3 below.

【0025】[0025]

【表3】 [Table 3]

【0026】[0026]

【実施例4】実施例1において分解が認められた白色腐
朽菌(NK−1148)を用いて、実施例3の培養条件
に準じ、窒素源および炭素源を含まない固体培地(グル
コース及び(NHSO添加量を0gとし、他は
実施例3と同様の培地組成である)で静置培養を行い分
解性をGPCで調べた。また、実施例3の培地から栄養
源を全て除いた固体培地(Agar 30g、水1l)
でも静置培養を行い同様に分解性をGPCで調べた。そ
の結果を表4に示す。
Example 4 Using the white-rot fungus (NK-1148), which was found to be decomposed in Example 1, a solid medium (glucose and (NH 4 ) 2 SO 4 was added in an amount of 0 g, and the other medium had the same medium composition as in Example 3), and static culture was carried out to examine the degradability by GPC. Moreover, a solid medium (Agar 30 g, water 1 l) obtained by removing all nutrients from the medium of Example 3.
However, static culture was performed and the degradability was examined by GPC in the same manner. The results are shown in Table 4.

【0027】[0027]

【表4】 [Table 4]

【0028】[0028]

【実施例5】実施例2において最大の分解能力を示した
窒素濃度条件(酒石酸アンモニウム0g/l、他の条件
は実施例1に準ずる)で、Phanerochaete
chysosporiumを用い、ナイロンの形態が分
解性に及ぼす影響を調べた。その形態として細孔膜(ザ
ルトリウス社製ナイロン66メンブレンフィルター)、
ナイロンフィルム(旭化成社製、厚さ50μm)、ナイ
ロン66繊維(NBC工業社製 径60μm)、粉末の
4種を用いた。なお粉末はサンプルミル(HEIKO社
製 TI−100)で5分間粉砕する操作を4〜5回繰
り返し獲られた粉末を分級し、80メッシュ以上の画分
を分解試料として用いた。なお分解性は実施例1に準じ
て評価した。その結果を下記表5に示す。
[Example 5] Phanerochaete under the nitrogen concentration conditions (ammonium tartrate 0 g / l, other conditions are the same as in Example 1) that showed the maximum decomposition ability in Example 2.
The effect of nylon morphology on degradability was investigated using chysosporium. As its form, a pore membrane (nylon 66 membrane filter manufactured by Sartorius),
Nylon film (Asahi Kasei Co., Ltd., thickness 50 μm), nylon 66 fiber (NBC Kogyo Co., Ltd. diameter 60 μm), and powder were used. The powder was classified by crushing the powder for 5 minutes with a sample mill (TI-100 manufactured by HEIKO) 4 to 5 times, and the 80 or more mesh fraction was used as a decomposition sample. The degradability was evaluated according to Example 1. The results are shown in Table 5 below.

【0029】[0029]

【表5】 [Table 5]

【0030】[0030]

【発明の効果】本発明によれば、水不溶性の高分子ナイ
ロン等のポリアミド系高分子化合物を効率的に分解処理
することができ、しかもその際二次公害をひき起すこと
もないので、本発明は、現在その処理が世界的にも大き
な社会問題となっているプラスチック廃棄物の処理に大
きな貢献をなすものである。
According to the present invention, a polyamide polymer compound such as a water-insoluble polymer nylon can be efficiently decomposed, and at the same time, it does not cause secondary pollution. The invention makes a great contribution to the treatment of plastic waste, the treatment of which is now a major social problem in the world.

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C12R 1:645) (C12P 13/02 C12R 1:685) (C12P 13/02 C12R 1:80) (C12P 13/02 C12R 1:125) (C12P 13/02 C12R 1:38) C08L 77:00 ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical indication C12R 1: 645) (C12P 13/02 C12R 1: 685) (C12P 13/02 C12R 1:80) (C12P 13/02 C12R 1: 125) (C12P 13/02 C12R 1:38) C08L 77:00

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 ポリアミド系高分子化合物を、添加窒素
濃度を0.1g/l及び/又は添加炭素濃度を0.2g
/l以下の組成とする培養条件下において、木材腐朽性
担子菌で処理することを特徴とするポリアミド系高分子
化合物の分解法。
1. A polyamide-based polymer compound having an added nitrogen concentration of 0.1 g / l and / or an added carbon concentration of 0.2 g.
A method for decomposing a polyamide polymer compound, which comprises treating with a wood-destroying basidiomycete under a culture condition having a composition of 1 / l or less.
【請求項2】 固体培養及び/又は液体培養条件下で処
理することを特徴とする請求項1の分解法。
2. The decomposition method according to claim 1, which is carried out under solid culture and / or liquid culture conditions.
【請求項3】 木材腐朽性担子菌が白色腐朽性担子菌で
あることを特徴とする請求項1〜請求項3のいずれか1
項の分解法。
3. The wood-rotting basidiomycete is a white-rotting basidiomycete, according to any one of claims 1 to 3.
Term decomposition method.
【請求項4】 木材腐朽性担子菌が、微生物それ自体、
微生物の培養物、及び/又はその処理物であることを特
徴とする請求項1〜請求項4のいずれか1項の分解法。
4. The wood-destroying basidiomycete is the microorganism itself,
The method for decomposing according to any one of claims 1 to 4, which is a culture of a microorganism and / or a treated product thereof.
【請求項5】 ポリアミド系高分子化合物として、粉
砕、粉末化、及び/又は細孔膜化したものを使用するこ
とを特徴とする請求項1〜請求項5のいずれか1項の分
解法。
5. The decomposition method according to any one of claims 1 to 5, wherein a polyamide-based polymer compound is used which is pulverized, powdered, and / or formed into a pore film.
JP12317991A 1991-01-23 1991-03-05 Decomposition method of polyamide polymer Expired - Lifetime JPH0771502B2 (en)

Priority Applications (3)

Application Number Priority Date Filing Date Title
CA002078859A CA2078859C (en) 1991-01-23 1992-01-20 Method of decomposing polyamide type high polymer compounds
EP9292902879A EP0596113A4 (en) 1991-01-23 1992-01-20 Method of decomposing polyamide.
PCT/JP1992/000038 WO1992013087A1 (en) 1991-01-23 1992-01-20 Method of decomposing polyamide

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
JP3-82076 1991-01-23
JP8207691A JPH05230273A (en) 1991-01-23 1991-01-23 Method for decomposing polyamide

Publications (2)

Publication Number Publication Date
JPH05304968A JPH05304968A (en) 1993-11-19
JPH0771502B2 true JPH0771502B2 (en) 1995-08-02

Family

ID=13764381

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JP8207691A Pending JPH05230273A (en) 1991-01-23 1991-01-23 Method for decomposing polyamide
JP12317991A Expired - Lifetime JPH0771502B2 (en) 1991-01-23 1991-03-05 Decomposition method of polyamide polymer

Family Applications Before (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (2) JPH05230273A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0738752A4 (en) * 1994-10-13 1999-03-10 Kobe Steel Ltd Method of enzymatically degrading synthetic polymer

Also Published As

Publication number Publication date
JPH05304968A (en) 1993-11-19
JPH05230273A (en) 1993-09-07

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