JP2009018293A - Method for separation treatment of plastic wallpaper having paper as base material - Google Patents

Method for separation treatment of plastic wallpaper having paper as base material Download PDF

Info

Publication number
JP2009018293A
JP2009018293A JP2007196700A JP2007196700A JP2009018293A JP 2009018293 A JP2009018293 A JP 2009018293A JP 2007196700 A JP2007196700 A JP 2007196700A JP 2007196700 A JP2007196700 A JP 2007196700A JP 2009018293 A JP2009018293 A JP 2009018293A
Authority
JP
Japan
Prior art keywords
paper
plastic
wallpaper
base material
acid
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.)
Pending
Application number
JP2007196700A
Other languages
Japanese (ja)
Inventor
Yoichi Okada
陽一 岡田
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
DAIKYO KASEI KOGYO KK
Original Assignee
DAIKYO KASEI KOGYO KK
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 DAIKYO KASEI KOGYO KK filed Critical DAIKYO KASEI KOGYO KK
Priority to JP2007196700A priority Critical patent/JP2009018293A/en
Publication of JP2009018293A publication Critical patent/JP2009018293A/en
Pending legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling
    • 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
    • Y02W30/64Paper recycling

Abstract

<P>PROBLEM TO BE SOLVED: To provide a separation treatment method which eliminates following difficulties and enabling to recycle a wall paper, since recycling (reuse of resource) is extremely difficult since a bat generated in a manufacturing factory where it is mass-produced or at execution and further the plastic wallpaper discarded accompanying with reforming of a residence or the like are in the state that the paper, i.e., a base material and the plastic are completely closely adhered. <P>SOLUTION: The portion of paper, i.e., the base material of the plastic wallpaper is separated/decomposed using an enzyme commercially available as a fiber modifying enzyme or a cellulolytic enzyme. Recycling of the wallpaper is enabled by separating it from the plastic. <P>COPYRIGHT: (C)2009,JPO&INPIT

Description

本発明は、プラスチック壁紙のリサイクル(資源再利用)を容易にする分離処理法に関する。  The present invention relates to a separation processing method that facilitates recycling (resource reuse) of plastic wallpaper.

発明の背景Background of the Invention

本発明の背景は、内装材として大量に生産されている紙を基材とするプラスチック壁紙が、製造段階、施工時及び内装リホ−ム時大量に産業廃棄物として廃棄されている。  The background of the present invention is that a large amount of paper-based plastic wallpaper produced as an interior material is discarded as a large amount of industrial waste at the manufacturing stage, during construction, and during interior reform.

しかも、此等の製品は基材である紙とプラスチックが完全密着状態であるがために、簡単に分離分別することでリサイクル(資源再利用)を行なうことは不可能である。  Moreover, since these products are completely in close contact with the base paper and plastic, they cannot be recycled (resource reuse) by simply separating and separating them.

此等の壁紙に使用されるプラスチック類は軟質ポリ塩化ビニル(PVC)、エチレン酢酸ビニル共重合体(EVA)、エチレン・メチル・メタアクリレ−ト(EMMA)等で、其の90%程度はポリ塩化ビニルが使用されている。  Plastics used in these wallpapers are soft polyvinyl chloride (PVC), ethylene vinyl acetate copolymer (EVA), ethylene methyl methacrylate (EMMA), etc., about 90% of which are polychlorinated Vinyl is used.

又、更に其の壁紙にはにそれ自体の風合い、そして防音性を付与するため、アゾジカルボンアミド(ADCA)、4,4’−オキシビスベンゼンスルホニルヒドラジド(OBSH)、等の有機系熱分解型発泡剤を使用し、発泡製品として製造されている。  Furthermore, in order to give the wallpaper its own texture and soundproofing, organic pyrolysis type such as azodicarbonamide (ADCA), 4,4'-oxybisbenzenesulfonylhydrazide (OBSH), etc. It is manufactured as a foamed product using a foaming agent.

現在、此等の製品は殆どリサイクル(資源再利用)されることなく、その大部分は産業廃棄物として焼却処分もしくは埋め立て廃棄処分されている。  At present, these products are hardly recycled (resource reuse), and most of them are incinerated or disposed of as industrial waste.

特に此等の製品の中で、軟質ポリ塩化ビニルをプラスチック部分に使用されている物を焼却処分する場合、ポリ塩化ビニルが起因するとされるダイオキシンの問題は、最近の焼却炉技術の改善で問題視されなくなっているが、焼却処分で生ずる塩化水素が起因する酸性成分である塩酸の焼却炉への影響が懸念されている。  In particular, when disposing of products that use soft polyvinyl chloride in plastic parts among these products, the problem of dioxins caused by polyvinyl chloride is a problem with recent improvements in incinerator technology. Although it has not been seen, there is concern about the influence of hydrochloric acid, which is an acidic component caused by hydrogen chloride generated by incineration, on the incinerator.

又、此等の製品を埋め立て廃棄する場合、発泡製品で有るが為かさ比重が小さく埋め立効率が極めてよくない。埋め立て処分された此等製品の紙の部分は土壌に含まれる酵素で分解されるがプラスチック部分は長年月に亙って土壌中に温存される。  In addition, when these products are disposed of in landfills, the bulk density is small and the landfill efficiency is not very good because they are foamed products. The paper portion of these products, which are disposed of in landfills, is decomposed by enzymes contained in the soil, but the plastic portion is preserved in the soil for many years.

特開2006−75007  JP 2006-75007 A 特開2006−149343  JP 2006-149343 A

以上に述べた壁紙の廃棄処分は、地球環境の面からも適切なる処分方法ではなく、更に今後廃棄される不要な壁紙は増加の方向にある。  The above-mentioned disposal of wallpaper is not an appropriate disposal method from the viewpoint of the global environment, and unnecessary wallpaper to be discarded in the future is increasing.

産業廃棄物として廃棄される此等の壁紙は、例えば其れを機械的な手段で微粉末化し、プラスチック部分と基材である紙を比重の差で分離する方法が試みられているが、完全な分離は不可能である。
或いは、プラスチックを溶剤で溶解分離する方法も試みられているが処理コスト、環境の面で問題が残されている。
These wallpaper, which are discarded as industrial waste, have been tried, for example, by pulverizing them by mechanical means and separating the plastic part and the paper that is the base material by the difference in specific gravity. Separation is impossible.
Alternatively, attempts have been made to dissolve and separate plastics with a solvent, but problems remain in terms of processing cost and environment.

又、資源有効利用促進法に基づき塩ビ壁紙リサイクルブロック(商品名、パイン・ブロック)としての利用も進められている。  In addition, based on the Law for Promotion of Effective Utilization of Resources, use as a PVC wallpaper recycling block (trade name, pine block) is also being promoted.

本発明は、此等の処理方法と異なり、壁紙の基材の紙の主成分がセルロ−ズ繊維で有ることに着眼し、セルロ−ズ分解酵素(繊維素分解酵素剤)によりそれらを分離分解し、プラスチック部分と基材である紙を完全に分離することでプラスチック部分はリサイクル(資源再利用)可能な物として再生し、更にセルロ−ズ分解酵素(繊維素分解酵素剤)でプラスチックと分離分解された紙の部分は再生紙への転用も可能とする。  The present invention, unlike these treatment methods, focuses on the fact that the main component of the paper substrate of the wallpaper is cellulose fiber, and separates and decomposes them with cellulose-degrading enzyme (fibrinolytic enzyme agent). Then, by completely separating the plastic part and the paper that is the base material, the plastic part is recycled as a recyclable (resource reusable) product, and further separated from the plastic by a cellulose-degrading enzyme (fibrinolytic enzyme). The disassembled paper portion can be converted into recycled paper.

此等の繊維状物質はセルロ−ズ分解酵素で分解を進め更に糖化酵素で糖(C12)にまで分解した後、醗酵酵母による醗酵でエチルアルコ−ル、グリセリン、アセトン、ブタノ−ル、イソブタノ−ル、更にはイソブチレン、ジイソブチレン、イソオクタン等高付加価値のある有機化合物の原料に転化することが出来る。These fibrous substances are decomposed with cellulose-degrading enzymes and further decomposed into sugars (C 6 H 12 O 6 ) with saccharifying enzymes, and then fermented with fermenting yeast to produce ethyl alcohol, glycerin, acetone, butanol. It can be converted into a raw material for organic compounds having high added value such as isobutylene, isobutanol, and isobutylene, diisobutylene and isooctane.

本発明者は、極めて困難な壁紙のリサイクル(資源再利用)に着眼し、誠意検討を進めた結果、対象とする壁紙を適当なサイズに裁断し、通常の水に分散した状態にセロ−ズ分解酵素(繊維素分解酵素剤)を加え、適切な条件下でプラスチック部分と紙を完全に分離することが可能であることを発見した。  The present inventor focused on extremely difficult wallpaper recycling (resource reuse), and as a result of proceeding with sincerity studies, the subject wallpaper was cut into an appropriate size and dispersed in normal water. It was discovered that it was possible to add a degrading enzyme (fibrinolytic enzyme agent) to completely separate the plastic part and the paper under appropriate conditions.

分離されたプラスチック部分は簡単な洗浄と乾燥を行うことで再利用可能なプラスチックとしての物性を有する物で有ることを確認した。  It was confirmed that the separated plastic part had a physical property as a reusable plastic by performing simple cleaning and drying.

本発明の具体的な手段は、リサイクルを対象とする此等製品を適当なサイズに裁断し、繊維改質剤或いは繊維処理剤の名目で比較的安価に市販されている繊維改質酵例えばGODO TCL(合同酒精株式会社製)、セルラ−ゼ”オノズカ”3S(ヤクルト薬品工業株式会社製)、エンチロンCM−40L(洛東化成工業株式会社製)、ドリラ−ゼ20(協和醗酵株式会社製)、セルラ−ゼA「アマノ」3(天野エンザイム株式会社)等々を此等の製品の製造会社の仕様にもとずく処理温度並びに水素イオン濃度の適切な管理処理を行うことでプラスチック部分と紙とを完全に分離することが出来る。  The specific means of the present invention is to cut these products to be recycled into appropriate sizes, and for fiber modification fermentations, such as GODO, which are commercially available at a relatively low price in the name of fiber modifiers or fiber treatment agents. TCL (manufactured by Godo Shusei Co., Ltd.), Cellulase “Onozuka” 3S (manufactured by Yakult Yakuhin Kogyo Co., Ltd.), Enchiron CM-40L (manufactured by Tohto Kasei Kogyo Co., Ltd.), Dorrase 20 (manufactured by Kyowa Hakko Kogyo Co., Ltd.) Cellulase A “Amano” 3 (Amano Enzyme Co., Ltd.), etc. are treated according to the specifications of the manufacturer of these products, and the processing temperature and the hydrogen ion concentration are appropriately managed, so that the plastic part and paper Can be completely separated.

本発明は、此等通常に市販されている繊維改質酵素剤を0.1〜20重量%、好ましくは1〜5重量%の水溶液で、水溶液の水素イオン濃度pHはクエン酸、酒石酸、りんご酸、酢酸、しゅう酸、琥珀酸、グルコン酸等の水溶性有機弱酸の0.005〜0.02重量%の使用でpH4〜5の範囲に調整することで、本発明の目的を確認することができた。  The present invention is an aqueous solution of 0.1 to 20% by weight, preferably 1 to 5% by weight, of these normally commercially available fiber-modifying enzyme agents, and the hydrogen ion concentration pH of the aqueous solution is citric acid, tartaric acid, apple. To confirm the purpose of the present invention by adjusting the pH to 4 to 5 by using 0.005 to 0.02% by weight of a water-soluble organic weak acid such as acid, acetic acid, oxalic acid, succinic acid and gluconic acid. I was able to.

此の様に調整された水溶液に対する分離対象の壁紙の仕込量は、壁紙の発泡倍率により異なる。
低発泡製品(2〜4倍)の場合、水溶液100重量部に対して15乃至25重量部の仕込みが可能である。
高発泡製品(5〜8倍)の場合は、水溶液100重量部に対して8乃至15重量部程度の仕込量となる。
The amount of the wallpaper to be separated with respect to the aqueous solution adjusted in this way varies depending on the expansion ratio of the wallpaper.
In the case of a low foamed product (2 to 4 times), 15 to 25 parts by weight can be charged with respect to 100 parts by weight of the aqueous solution.
In the case of a highly foamed product (5 to 8 times), the charging amount is about 8 to 15 parts by weight with respect to 100 parts by weight of the aqueous solution.

本発明に関わる分離を対象とする壁紙は、其れを粉砕機により粉砕供与することは、処理後分離分解された紙の部分との分離が不可能となるため好ましくない。  It is not preferable that the wallpaper intended for separation according to the present invention is supplied by pulverization with a pulverizer because separation from the separated and decomposed paper portion after processing becomes impossible.

本発明に関わる対象とする壁紙は、処理設備の規模にもよるが、処理後のプラスチック部分の分離を容易にするため2cm〜50cm角、好ましくは4cm〜15cm角程度に裁断されることが望ましいが、必ずしも正四角形の必要はない。Wallpaper of interest according to the invention will depend on the processing equipment scale, 2 cm 2 to 50 cm 2 square to facilitate the separation of the plastic part after treatment, preferably cut into 2 square about 4 cm 2 ~15Cm However, it is not always necessary to use a regular square.

適切なる繊維改質酵素剤並びに適切な水素イオン濃度に調整された水溶液を使用することでプラスチック部分と基剤である紙は、ほぼ完全に分離されプラスチック部分は1メッシュ程度の網で分別する。  By using an appropriate fiber-modifying enzyme agent and an aqueous solution adjusted to an appropriate hydrogen ion concentration, the plastic part and the base paper are almost completely separated, and the plastic part is separated by a mesh of about 1 mesh.

プラスチック部分を分別し繊維改質酵素剤で分離、一部は分解された繊維状の紙の部分は合成繊維製不織布或いはガラス繊維製の濾過布を使用し、掻き出し可能な遠心分離機等を使用して濾別する。  The plastic part is separated and separated with a fiber-modifying enzyme, and the partially broken fiber paper part uses a synthetic fiber nonwoven fabric or glass fiber filter cloth, and a scraper that can be scraped off. And filter.

プラスチック並びに紙の部分を分別した残水溶液は、水素イオン濃度pHを調整することで繰り返し使用することが可能である。  The remaining aqueous solution obtained by separating the plastic and paper portions can be used repeatedly by adjusting the hydrogen ion concentration pH.

本発明に関わる紙の分離作業中の水素イオン濃度pH及び反応温度は使用する分解酵素の酵素失活を避けるため、製造会社の仕様に従う。  The hydrogen ion concentration pH and reaction temperature during the paper separation work according to the present invention are in accordance with the manufacturer's specifications in order to avoid enzyme deactivation of the degrading enzyme used.

上述したように、本発明は排出される不要壁紙のリサイクル(資源再利用)処理方法として、現在主として行われている埋め立て処理、或いは焼却処理に伴う問題を解決し、容易にしかも環境にも優しく、経済的にも有利な処理方法である。  As described above, the present invention solves the problems associated with landfill processing or incineration processing that are currently mainly performed as a method for recycling (reusing resources) unnecessary wallpaper that is discharged, and is easy and environmentally friendly. This is an economically advantageous treatment method.

本発明に関わるプラスチック壁紙の分離操作に必要とする反応時間は、反応温度を50℃に設定して、壁紙製造に使用されのプラスチックの種類、重合度、可塑剤の種類及び使用量、発泡倍率、エンボッシングの程度並びに分解酵素の違い或いは使用量等で幾分違いは有るが、大略2時間30分乃至5時間程度で、本発明の目的を達成することが出来る。  The reaction time required for the separation operation of the plastic wallpaper according to the present invention is as follows: the reaction temperature is set to 50 ° C., the type of plastic used for wallpaper production, the degree of polymerization, the type and amount of plasticizer used, and the expansion ratio Although there are some differences in the degree of embossing and the difference or amount of degradation enzyme, the object of the present invention can be achieved in about 2 hours 30 minutes to 5 hours.

発明を実施するための最良の手段BEST MODE FOR CARRYING OUT THE INVENTION

以下実施例によって本発明を説明するが、本発明はこれらによつて限定されるものではない。
尚、以下に説明する実施例は、製造される壁紙の90%を占めるポリ塩化ビニル製壁紙に限定する。
EXAMPLES The present invention will be described below with reference to examples, but the present invention is not limited thereto.
In addition, the Example demonstrated below is limited to the wallpaper made from polyvinyl chloride which occupies 90% of the wallpaper manufactured.

ポリ塩化ビニル製壁紙(竹野株式会社より入手した製品)を約2cm角に裁断した物100gを、水1Lに洛東化成工業株式会社製エンチロンCM−40Lを50g、更にpH調整としてクエン酸0.01gを溶解した水溶液(pH4.3)に分散し、50℃に保たれた状態で3時間攪拌を続けた後、プラスチック部分を繊維状に分解された水溶液部分から分別する。The 100g thing was cut polyvinyl chloride wallpaper (product obtained from Takeno, Ltd.) to about 2 cm 2 square, citrate Rakuto Kasei Kogyo Co., Ltd. Enchiron CM-40L water 1L 50 g, as a further pH adjustment 0 After 0.01 g is dispersed in an aqueous solution (pH 4.3) dissolved and stirred at a temperature of 50 ° C. for 3 hours, the plastic portion is separated from the aqueous solution portion decomposed into fibers.

分別したプラスチックを簡単に水で洗浄後、充分に乾燥し80.5gの軟質ポリ塩化ビニルを得た。  The separated plastic was simply washed with water and then sufficiently dried to obtain 80.5 g of soft polyvinyl chloride.

プラスチック部分を分離した残水溶液を、合成繊維製の濾布で繊維状の紙を濾別取出し、充分に乾燥し18.5gの繊維状の物を得た。  The remaining aqueous solution from which the plastic part was separated was separated by filtering out fibrous paper with a synthetic fiber filter cloth and dried sufficiently to obtain 18.5 g of fibrous material.

塩化ビニル樹脂(重合度1100)100部、DINP(ジ・イソノニルフタレ−ト)50部、Ba−Zn系液状安定剤2部を混合した物に分別して得た軟質ポリ塩化ビニル30部を混合し、表面温度170℃に保たれた6インチ2本テスト・ロ−ルで5分間混練し、厚み0.5mmの繊維状物質を全く認めない、均一な軟質ポリ塩化ビニルシ−トを得ることが出来た。  Mixing 100 parts of vinyl chloride resin (degree of polymerization 1100), 50 parts of DINP (di-isononyl phthalate), 2 parts of Ba-Zn liquid stabilizer, 30 parts of soft polyvinyl chloride obtained by fractionation, Kneading was carried out for 5 minutes in two 6-inch test rolls maintained at a surface temperature of 170 ° C., and a uniform soft polyvinyl chloride sheet with no fibrous material having a thickness of 0.5 mm could be obtained. .

プラスチック部分並びに繊維状の紙の部分を濾過分離した水素イオン濃度pHが5.0を示す水溶液を、クエン酸0.002gを加えて水素イオン濃度pHを4.3とし、同様の分離処理を行うことで、上記と同様の結果を得た。  The same separation treatment is performed by adding 0.002 g of citric acid to an aqueous solution having a pH of 5.0 obtained by filtering and separating the plastic portion and the fibrous paper portion to obtain a hydrogen ion concentration pH of 4.3. Thus, the same result as above was obtained.

上記と同様に、僅かに失われた水と、其れに必要とする分解酵素と水素イオン濃度pHの調整で、3回の分離操作を行い、全く同様の結果を得ることが出来た。  In the same manner as described above, the separation operation was performed three times by adjusting the slightly lost water, the necessary decomposing enzyme and the hydrogen ion concentration pH, and the same results could be obtained.

尚、3回目に使用した水溶液の分析結果は、Ba,14ppm、Zn,50ppm、Ca,634ppm、その他Cd、Pb等の重金属並びに有機錫も検出しない。
Ba、Zn金属は、壁紙製造時に使用された塩化ビニル樹脂用安定剤からである。Ca金属は壁紙プラスチック部分に使用された充填材(炭酸カルシュウム)からの物である。
The analysis result of the aqueous solution used for the third time does not detect Ba, 14 ppm, Zn, 50 ppm, Ca, 634 ppm, other heavy metals such as Cd and Pb, and organic tin.
Ba and Zn metal are from the stabilizer for vinyl chloride resin used at the time of wallpaper manufacture. Ca metal is from the filler (calcium carbonate) used for wallpaper plastic parts.

ヤクルト薬品工業株式会社製の繊維素分解酵素剤、セルラ−ゼ“オノズカ”3S、50gとpH調整剤として0.01gの酒石酸を1Lの水に溶解し、pH5に調整した水溶液に約2cm角に裁断した軟質ポリ塩化ビニル製高発泡壁紙(裏糊処理の無い市販品)80gを分散し、温度を50℃に保持した状態で5時間攪拌を継続したのちプラスチック部分と繊維の状態で分散している水溶液部分を分離する。Yakult Pharmaceutical Co., Ltd., fibrinolytic enzyme agent Cellulase “Onozuka” 3S, 50 g and 0.01 g of tartaric acid as a pH adjuster dissolved in 1 L of water and adjusted to pH 5 in an aqueous solution of about 2 cm 2 Disperse 80 g of soft polyvinyl chloride highly foamed wallpaper (commercially available product without back paste treatment) cut into pieces, and continue stirring for 5 hours while maintaining the temperature at 50 ° C. The aqueous solution portion is separated.

プラスチック部分を洗浄し、充分に乾燥することで密着しているプラスチックと紙が完全に分離していることを確認した。  The plastic part was washed and thoroughly dried to confirm that the adhered plastic and paper were completely separated.

Claims (4)

基材に紙が使用される<プラスチック壁紙の紙質基材の主成分であるセルロ−ズ(繊維素)をセルロ−ズ分解酵素(繊維素分解酵素剤)により紙質を分離分解し、プラスチック部分を分別することで、基材に紙を使用し生産されるプラスチック壁紙のリサイクルを可能とする分離処理法。  Paper is used as the base material <Cellulose (fibrin), which is the main component of the paper base material for plastic wallpaper, is separated and decomposed by cellulose-degrading enzyme (fibrinolytic enzyme agent), and the plastic part is Separation method that enables recycling of plastic wallpaper produced using paper as a base material by sorting. 前記セルロ−ズ分解酵素の酵素種類は、セルラ−ゼ、グルカナ−ゼ、キシラナ−ゼ、ヘミセルラ−ゼ、マンナナ−ゼ、ペクチナ−ゼ等で、其々単独もしくは混合した0.1乃至20重量%の水溶液を使用する分離処理法。  The enzyme type of the cellulose-degrading enzyme is cellulase, glucanase, xylanase, hemicellulase, mannanase, pectinase, etc., each of which is 0.1 to 20% by weight, either alone or in combination. Separation treatment method using an aqueous solution. 前記セルラ−ゼ酵素等の活性と安定性を保持するため要求される水素イオン濃度pHを保持するために、クエン酸、酒石酸、りんご酸、酢酸、しゅう酸、琥珀酸、グルコン酸等の水溶性有機弱酸0.01乃至0.5重量%を使用する分離処理法。  Water solubility such as citric acid, tartaric acid, malic acid, acetic acid, oxalic acid, oxalic acid, gluconic acid, etc. in order to maintain the required hydrogen ion concentration pH in order to maintain the activity and stability of the above-mentioned cellulase enzymes, etc. Separation process using 0.01 to 0.5% by weight of organic weak acid. 基剤に紙が使用されるプラスチック壁紙を請求項1,2で調整された水溶液でプラスチックと紙を分別分離した後の水溶液は、追加する水と其れに必要とするセルロ−ズ分解酵素を追加し、更に水素イオン濃度を調整することで、繰り返し使用を可能とする分離処理法。  A plastic wallpaper in which paper is used as the base material, the aqueous solution after the separation of the plastic and paper with the aqueous solution prepared in claims 1 and 2 contains the additional water and the cellulose-degrading enzyme required for it. Separation treatment method that enables repeated use by adding and adjusting the hydrogen ion concentration.
JP2007196700A 2007-06-15 2007-07-02 Method for separation treatment of plastic wallpaper having paper as base material Pending JP2009018293A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2007196700A JP2009018293A (en) 2007-06-15 2007-07-02 Method for separation treatment of plastic wallpaper having paper as base material

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
JP2007182636 2007-06-15
JP2007196700A JP2009018293A (en) 2007-06-15 2007-07-02 Method for separation treatment of plastic wallpaper having paper as base material

Publications (1)

Publication Number Publication Date
JP2009018293A true JP2009018293A (en) 2009-01-29

Family

ID=40358401

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2007196700A Pending JP2009018293A (en) 2007-06-15 2007-07-02 Method for separation treatment of plastic wallpaper having paper as base material

Country Status (1)

Country Link
JP (1) JP2009018293A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010241074A (en) * 2009-04-09 2010-10-28 Tokuyama Corp Method for recovering resin sheet
CN108058310A (en) * 2017-12-14 2018-05-22 成都新柯力化工科技有限公司 A kind of method that waste and old paper substrate compound package material recycling prepares lightweight packaging material

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010241074A (en) * 2009-04-09 2010-10-28 Tokuyama Corp Method for recovering resin sheet
CN108058310A (en) * 2017-12-14 2018-05-22 成都新柯力化工科技有限公司 A kind of method that waste and old paper substrate compound package material recycling prepares lightweight packaging material

Similar Documents

Publication Publication Date Title
JP4357585B2 (en) Separating and collecting plastic and paper from plastic wallpaper
Jadaun et al. Biodegradation of plastics for sustainable environment
Krueger et al. Prospects for microbiological solutions to environmental pollution with plastics
Shen et al. Enzymatic saccharification coupling with polyester recovery from cotton-based waste textiles by phosphoric acid pretreatment
EP0968300B1 (en) Degradation of biologically degradable polymers using enzymes
JP6698506B2 (en) How to recycle used absorbent articles
WO2013182801A1 (en) Method for separating polyester and cotton in order to recycle textile waste
TW201605939A (en) A process for recovering polyester from polyester blend
JP2009018293A (en) Method for separation treatment of plastic wallpaper having paper as base material
Sahu et al. A review on cutinases enzyme in degradation of microplastics
Singhal et al. Chemical recycling of waste clothes: a smarter approach to sustainable development
JP2009062662A (en) Method for carrying out separation treatment of plastic wall paper using paper as substrate
JP2010241074A (en) Method for recovering resin sheet
JP2020124711A (en) Recycling method for used absorbent article
KR101297978B1 (en) Preparation method of porous hydrophilic media containing gelatin which is extracted from waste of leather processing for wastewater biological treatment
WO2010016536A1 (en) Method for treating lignocellulose material
Elgharbawy et al. Ionic liquids as a green solvent for lipase-catalyzed reactions
Gomes et al. Lessons from biomass valorization for improving plastic-recycling enzymes
Mahal Enhanced hydrolysis of polyethylene terephthalate (PET) plastics by ozone and ultrasound pretreatment
JP2008280493A (en) Method for separation treatment of plastic leathercloth and plastic wallpaper
CN107649493B (en) Preparation method of biological matrix loaded with strains and garbage treatment method
Lu et al. Directed Evolution of Material Binding Peptide for Polylactic Acid-specific Degradation in Mixed Plastic Wastes
Mamun et al. Biotechno-logical Solutions for Recycling Syn-thetic Fibers. 2023, 5, x
CN107813439A (en) A kind of plastics recovery method
EP3357593B1 (en) Bio-purification of used domestic packaging