WO2018025500A1 - Method for recovering pulp fibers from used absorbent article - Google Patents
Method for recovering pulp fibers from used absorbent article Download PDFInfo
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- WO2018025500A1 WO2018025500A1 PCT/JP2017/021540 JP2017021540W WO2018025500A1 WO 2018025500 A1 WO2018025500 A1 WO 2018025500A1 JP 2017021540 W JP2017021540 W JP 2017021540W WO 2018025500 A1 WO2018025500 A1 WO 2018025500A1
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- superabsorbent polymer
- absorbent article
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/0075—Disposal of medical waste
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE
- B09B5/00—Operations not covered by a single other subclass or by a single other group in this subclass
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/02—Separating plastics from other materials
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- 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
- C08J11/18—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 organic material
- C08J11/22—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 organic material by treatment with organic oxygen-containing compounds
- C08J11/26—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 organic material by treatment with organic oxygen-containing compounds containing carboxylic acid groups, their anhydrides or esters
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- D—TEXTILES; PAPER
- D21—PAPER-MAKING; PRODUCTION OF CELLULOSE
- D21C—PRODUCTION OF CELLULOSE BY REMOVING NON-CELLULOSE SUBSTANCES FROM CELLULOSE-CONTAINING MATERIALS; REGENERATION OF PULPING LIQUORS; APPARATUS THEREFOR
- D21C5/00—Other processes for obtaining cellulose, e.g. cooking cotton linters ; Processes characterised by the choice of cellulose-containing starting materials
- D21C5/02—Working-up waste paper
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- A—HUMAN NECESSITIES
- A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
- A61L—METHODS OR APPARATUS FOR STERILISING MATERIALS OR OBJECTS IN GENERAL; DISINFECTION, STERILISATION OR DEODORISATION OF AIR; CHEMICAL ASPECTS OF BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES; MATERIALS FOR BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES
- A61L11/00—Methods specially adapted for refuse
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29B—PREPARATION OR PRETREATMENT OF THE MATERIAL TO BE SHAPED; MAKING GRANULES OR PREFORMS; RECOVERY OF PLASTICS OR OTHER CONSTITUENTS OF WASTE MATERIAL CONTAINING PLASTICS
- B29B17/00—Recovery of plastics or other constituents of waste material containing plastics
- B29B17/02—Separating plastics from other materials
- B29B2017/0213—Specific separating techniques
- B29B2017/0293—Dissolving the materials in gases or liquids
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B29—WORKING OF PLASTICS; WORKING OF SUBSTANCES IN A PLASTIC STATE IN GENERAL
- B29L—INDEXING SCHEME ASSOCIATED WITH SUBCLASS B29C, RELATING TO PARTICULAR ARTICLES
- B29L2031/00—Other particular articles
- B29L2031/48—Wearing apparel
- B29L2031/4871—Underwear
- B29L2031/4878—Diapers, napkins
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- 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
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- 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
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- Health & Medical Sciences (AREA)
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- Life Sciences & Earth Sciences (AREA)
- Medicinal Chemistry (AREA)
- Polymers & Plastics (AREA)
- Organic Chemistry (AREA)
- Mechanical Engineering (AREA)
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Description
[1]パルプ繊維および高吸水性ポリマーを含む使用済み吸収性物品からパルプ繊維を回収する方法であって、該方法が、使用済み吸収性物品を、テルペン炭化水素、テルペンアルデヒドおよびテルペンケトンからなる群から選ばれる少なくとも1種のテルペンを0.05質量%以上含みかつ高吸水性ポリマーを不活化可能な不活化剤を含む水溶液で処理し、高吸水性ポリマーを不活化する工程を含むことを特徴とする方法。
[2]前記水溶液で処理した後の使用済み吸収性物品から、パルプ繊維および不活化した高吸水性ポリマーを分離する工程をさらに含む[1]に記載の方法。
[3]分離したパルプ繊維および不活化した高吸水性ポリマーを含む混合物を酸化剤で処理し、不活化した高吸水性ポリマーを分解し、低分子量化し、可溶化する工程をさらに含む[2]に記載の方法。
[4]酸化剤で処理した混合物からパルプ繊維を分離する工程をさらに含む[3]に記載の方法。
[5]高吸水性ポリマーを不活化可能な不活化剤を含む水溶液がpH2.5以下の有機酸水溶液であることを特徴とする[1]~[4]のいずれかに記載の方法。
[6]有機酸がクエン酸であることを特徴とする[5]に記載の方法。
[7]有機酸水溶液のクエン酸濃度が2質量%以上であることを特徴とする[6]に記載の方法。
[8]テルペンがテルペン炭化水素であることを特徴とする[1]~[7]のいずれかに記載の方法。
[9]テルペン炭化水素がリモネンであることを特徴とする[8]に記載の方法。
[10]前記水溶液中のテルペンの濃度が0.05~1.0質量%であることを特徴とする[1]~[9]のいずれかに記載の方法。
[11]使用済み吸収性物品が熱可塑性樹脂からなる素材を含み、かつ前記方法が、使用済み吸収性物品からパルプ繊維および不活化した高吸水性ポリマーを分離した後の残渣を乾燥し、乾燥した残渣から熱可塑性樹脂からなる素材を分離する工程をさらに含むことを特徴とする[2]~[10]のいずれかに記載の方法。
[12]使用済み吸収性物品が熱可塑性樹脂フィルムを含み、かつ前記方法が、使用済み吸収性物品からパルプ繊維および不活化した高吸水性ポリマーを分離した後の残渣を乾燥し、乾燥した残渣から熱可塑性樹脂フィルムを分離する工程をさらに含むことを特徴とする[2]~[10]のいずれかに記載の方法。
[13]吸収性物品が、紙おむつ、尿取りパッド、ベッドシーツ、生理用ナプキンおよびペットシーツからなる群から選択される少なくとも1種であることを特徴とする[1]~[12]のいずれかに記載の方法。 The present invention includes the following aspects.
[1] A method for recovering pulp fibers from a used absorbent article containing pulp fibers and a superabsorbent polymer, wherein the method comprises a terpene hydrocarbon, a terpene aldehyde, and a terpene ketone. Including a step of inactivating the superabsorbent polymer by treating with 0.05% by mass or more of a terpene selected from the group and an aqueous solution containing an inactivating agent capable of inactivating the superabsorbent polymer. Feature method.
[2] The method according to [1], further comprising a step of separating pulp fibers and inactivated superabsorbent polymer from the used absorbent article after being treated with the aqueous solution.
[3] The method further includes a step of treating the mixture containing separated pulp fibers and inactivated superabsorbent polymer with an oxidizing agent, decomposing the inactivated superabsorbent polymer, reducing the molecular weight, and solubilizing [2]. The method described in 1.
[4] The method according to [3], further comprising separating pulp fibers from the mixture treated with the oxidizing agent.
[5] The method according to any one of [1] to [4], wherein the aqueous solution containing an inactivating agent capable of inactivating the superabsorbent polymer is an aqueous organic acid solution having a pH of 2.5 or lower.
[6] The method according to [5], wherein the organic acid is citric acid.
[7] The method according to [6], wherein the citric acid concentration of the organic acid aqueous solution is 2% by mass or more.
[8] The method according to any one of [1] to [7], wherein the terpene is a terpene hydrocarbon.
[9] The method according to [8], wherein the terpene hydrocarbon is limonene.
[10] The method according to any one of [1] to [9], wherein the concentration of the terpene in the aqueous solution is 0.05 to 1.0% by mass.
[11] The used absorbent article includes a material made of a thermoplastic resin, and the method dries the residue after separating the pulp fiber and the inactivated superabsorbent polymer from the used absorbent article, The method according to any one of [2] to [10], further comprising a step of separating a material comprising a thermoplastic resin from the residue.
[12] The used absorbent article includes a thermoplastic resin film, and the method is used to dry the residue after separating the pulp fibers and the inactivated superabsorbent polymer from the used absorbent article, and to obtain a dried residue. The method according to any one of [2] to [10], further comprising a step of separating the thermoplastic resin film from the film.
[13] Any one of [1] to [12], wherein the absorbent article is at least one selected from the group consisting of a disposable diaper, a urine absorbing pad, a bed sheet, a sanitary napkin, and a pet sheet. The method described in 1.
なお、pHは水温により変化するため、本発明におけるpHは、水溶液温度20℃で測定したpHをいうものとする。 The pH of the organic acid aqueous solution is 2.5 or less, preferably 1.3 to 2.4, and more preferably 1.5 to 2.1. If the pH is too high, the water absorption ability of the superabsorbent polymer cannot be sufficiently reduced. Moreover, there exists a possibility that the disinfection ability may fall and it cannot disinfect. If the pH is too low, there is a concern that the equipment will be corroded and the service life will be reduced, or a lot of alkaline chemicals may be required for the neutralization treatment during the wastewater treatment.
In addition, since pH changes with water temperature, pH in this invention shall mean pH measured by aqueous solution temperature 20 degreeC.
テルペン炭化水素としては、ミルセン、リモネン、ピネン、カンファー、サピネン、フェランドレン、パラシメン、オシメン、テルピネン、カレン、ジンギベレン、カリオフィレン、ビサボレン、セドレン等が挙げられるが、なかでも、リモネン、ピネン、テルピネン、カレンが好ましい。
テルペンアルデヒドとしては、シトロネラール、シトラル、シクロシトラール、サフラナール、フェランドラール、ペリルアルデヒド、ゲラニアール、ネラール等が挙げられるが、なかでもシトラルが好ましい。
テルペンケトンとしては、ショウノウ、ツヨシ等が挙げられる。
テルペンの中でもテルペン炭化水素が好ましく、特に好ましいテルペンはリモネンである。リモネンには、d-リモネン、l-リモネン、ジペンテン(dl-リモネン)の3種類があるが、いずれも好ましく用いることができる。
テルペンは1種単独で使用することもできるし、2種以上を組み合わせて使用することもできる。 The aqueous solution containing an inactivating agent capable of inactivating the superabsorbent polymer contains at least one terpene selected from the group consisting of terpene hydrocarbons, terpene aldehydes and terpene ketones.
Terpene hydrocarbons include myrcene, limonene, pinene, camphor, sapinene, ferrandlene, paracymene, osymene, terpinene, karen, gingivalene, caryophyllene, bisabolene, cedrene, among others, limonene, pinene, terpinene, caren. Is preferred.
Examples of the terpene aldehyde include citronellal, citral, cyclocitral, safranal, ferrandral, perillaldehyde, geranial, and neral, among which citral is preferable.
Examples of terpene ketones include camphor and tsuyoshi.
Among the terpenes, terpene hydrocarbons are preferable, and a particularly preferable terpene is limonene. There are three types of limonene: d-limonene, l-limonene, and dipentene (dl-limonene), and any of them can be preferably used.
Terpenes can be used singly or in combination of two or more.
オゾン濃度(ppm)と処理時間(分)の積(以下「CT値」ともいう。)は、好ましくは100~6000ppm・分であり、より好ましくは200~4800ppm・分であり、さらに好ましくは300~3600ppm・分である。CT値が小さすぎると、高吸水性ポリマーを完全に可溶化することができず、回収したパルプ繊維に高吸水性ポリマーが残存する虞がある。逆に、CT値が大きすぎると、パルプ繊維の損傷、安全性の低下、製造原価の増加につながる虞がある。
処理時間は、オゾン濃度に依存することは、上述のとおりであるが、好ましくは20~120分であり、より好ましくは30~100分であり、さらに好ましくは40~80分である。 The time for the ozone treatment is not particularly limited as long as it is a time during which the superabsorbent polymer can be decomposed. The treatment time may be short if the ozone concentration is high, and a long time is required if the ozone concentration is low.
The product of ozone concentration (ppm) and treatment time (min) (hereinafter also referred to as “CT value”) is preferably 100 to 6000 ppm · min, more preferably 200 to 4800 ppm · min, and even more preferably 300. ~ 3600 ppm · min. If the CT value is too small, the superabsorbent polymer cannot be completely solubilized and the superabsorbent polymer may remain in the recovered pulp fiber. On the other hand, if the CT value is too large, it may lead to damage of pulp fibers, a decrease in safety, and an increase in manufacturing costs.
As described above, the treatment time depends on the ozone concentration, but is preferably 20 to 120 minutes, more preferably 30 to 100 minutes, and further preferably 40 to 80 minutes.
処理時間は、オゾン処理の場合と同様である。 When chlorine dioxide is blown into wastewater containing pulp fibers and inactivated superabsorbent polymer, the concentration of chlorine dioxide in the wastewater is not particularly limited as long as it is a concentration capable of decomposing the superabsorbent polymer, but preferably Is from 150 to 1100 ppm by mass, more preferably from 200 to 1000 ppm by mass, and even more preferably from 300 to 900 ppm by mass. If the concentration is too low, the superabsorbent polymer cannot be completely solubilized and the superabsorbent polymer may remain in the recovered pulp fiber. On the other hand, if the concentration is too high, the oxidizing power is also increased, which may damage the pulp fiber and may cause a problem in safety.
The treatment time is the same as in the case of ozone treatment.
処理時間は、オゾン処理の場合と同様である。 When adding sodium hypochlorite to wastewater containing pulp fiber and deactivated superabsorbent polymer, or when immersing pulp fiber and deactivated superabsorbent polymer in aqueous sodium hypochlorite solution, The concentration of sodium hypochlorite in the aqueous sodium hypochlorite solution is not particularly limited as long as it is a concentration capable of decomposing the superabsorbent polymer, but is preferably 0.5 to 2% by mass, more Preferably, it is 0.75 to 1.5% by mass. If the concentration is too low, the superabsorbent polymer cannot be completely solubilized and the superabsorbent polymer may remain in the recovered pulp fiber. Further, Bacillus subtilis forming spores cannot be completely sterilized. On the other hand, if the concentration is too high, the oxidizing power is also increased, which may damage the pulp fiber and may cause a problem in safety.
The treatment time is the same as in the case of ozone treatment.
乾燥する場合、乾燥温度は、好ましくは105~210℃であり、より好ましくは110~190℃であり、さらに好ましくは120~180℃である。乾燥時間は、乾燥温度にもよるが、好ましくは10~120分であり、より好ましくは15~100分であり、さらに好ましくは20~90分である。 The separated pulp fibers can be dehydrated, dried and recovered as necessary.
In the case of drying, the drying temperature is preferably 105 to 210 ° C, more preferably 110 to 190 ° C, and further preferably 120 to 180 ° C. Although depending on the drying temperature, the drying time is preferably 10 to 120 minutes, more preferably 15 to 100 minutes, and further preferably 20 to 90 minutes.
標準コンポスト(八幡物産株式会社製YK-8)100gを1Lのイオン交換水に浸漬し、5分間攪拌後、30分間静置し、その上澄み溶液を240mL採水して、人工汚水を調製した。調製した人工汚水について、測定機器としてキッコーマン株式会社製ルミテスターPD-30を用いて、ATP検査を実施したところ、ATP値は13126であった。
市販紙おむつ(ユニ・チャーム株式会社製「ムーニー」(登録商標)Mサイズ)に、先に調製した人工汚水240mLを吸水させた後、紙おむつを2槽式小型洗濯機(アルミス社製「晴晴」AST-01)の洗濯槽に1個投入し、続けて水温20℃の水にクエン酸(扶桑化学工業株式会社製)を濃度2.0質量%になるように溶解し、さらにd-リモネン(ナカライテスク株式会社製試薬1級)を濃度0.05質量%になるように溶解した水溶液(pH2.1)を10L投入し、15分間洗濯した。洗濯終了後、おむつは表面シートと裏面シートが剥がれ、中身の吸収体が紙おむつの外に出て、パルプ繊維は洗濯槽内の液中に分散していた。洗濯槽内の液中に浮遊する不織布、フィルム等の大型固形物をφ10mmの孔の開いたザルですくい取り分離後、排水し、槽内に残ったパルプ繊維と不活化した高吸水性ポリマー、および排水と一緒に槽外に排出されたパルプ繊維と不活化した高吸水性ポリマーを回収し、ATP検査を実施した。ATP検査の結果、ATP値は0であった。
なお、ザルですくい取った大型固形物のなかには、フィルムが付着したままの不織布もあったが、そのフィルムは不織布から簡単かつ綺麗に剥がすことができた。
その後、パルプ繊維と不活化した高吸水性ポリマーをナイロンネット(株式会社NBCメッシュテック製250メッシュナイロンネット)の袋(250mm×250mm)に入れ、脱水槽で5分間脱水した。脱水したパルプ繊維と不活化した高吸水性ポリマーをナイロンネットの袋ごと濃度1.0質量%の次亜塩素酸ナトリウム水溶液中に浸漬し、5分間攪拌洗浄を行い、再び脱水槽で5分間脱水し、その後105℃の熱風乾燥機で24時間乾燥後、パルプ繊維を回収した。回収されたパルプ繊維の灰分を分析したところ、灰分は0.28質量%であった。 Example 1
100 g of standard compost (YK-8 manufactured by Yawata Bussan Co., Ltd.) was immersed in 1 L of ion-exchanged water, stirred for 5 minutes, allowed to stand for 30 minutes, and 240 mL of the supernatant solution was sampled to prepare artificial sewage. The prepared artificial sewage was subjected to an ATP inspection using a Lumitester PD-30 manufactured by Kikkoman Corporation as a measuring instrument. The ATP value was 13126.
A commercial paper diaper (Moonie (registered trademark) M size manufactured by Unicharm Co., Ltd.) was allowed to absorb 240 mL of the artificial sewage prepared above, and then the paper diaper was placed in a two-tank small washing machine (Aseis “Sunny” AST -01) was added to the washing tub, and citric acid (manufactured by Fuso Chemical Co., Ltd.) was dissolved in water at a water temperature of 20 ° C. to a concentration of 2.0% by mass. 10 L of an aqueous solution (pH 2.1) in which a reagent grade 1 manufactured by Tesque Co., Ltd. was dissolved so as to have a concentration of 0.05% by mass was charged and washed for 15 minutes. After completion of washing, the top sheet and the back sheet of the diaper were peeled off, and the absorbent body inside was out of the paper diaper, and the pulp fibers were dispersed in the liquid in the washing tub. Large solids such as non-woven fabric and film floating in the liquid in the washing tub are scooped and separated with a colander with a hole of φ10 mm, drained, and the pulp fibers remaining in the tub and the inactivated superabsorbent polymer, In addition, the pulp fibers discharged out of the tank together with the waste water and the inactivated superabsorbent polymer were collected, and ATP inspection was performed. As a result of the ATP test, the ATP value was 0.
Some of the large solids scooped with colander also had a nonwoven fabric with the film still attached, but the film could be easily and cleanly removed from the nonwoven fabric.
Thereafter, the pulp fibers and the inactivated superabsorbent polymer were placed in a nylon net (250 mesh nylon net manufactured by NBC Meshtec Co., Ltd.) bag (250 mm × 250 mm) and dehydrated in a dehydration tank for 5 minutes. The dehydrated pulp fiber and the deactivated superabsorbent polymer are immersed in a 1.0% by weight sodium hypochlorite aqueous solution together with the nylon net bag, washed with stirring for 5 minutes, and dehydrated again for 5 minutes in the dehydration tank. Then, after drying with a hot air dryer at 105 ° C. for 24 hours, the pulp fiber was recovered. When the ash content of the recovered pulp fibers was analyzed, the ash content was 0.28% by mass.
d-リモネンの濃度を0.1質量%に変更した以外は、実施例1と同様に実施した。15分間洗濯した後、洗濯槽内の紙おむつは表面シートと裏面シートが剥がれ、中身の吸収体が紙おむつの外に出て、パルプ繊維は洗濯槽内の液中に分散していた。 Example 2
The same operation as in Example 1 was carried out except that the concentration of d-limonene was changed to 0.1% by mass. After washing for 15 minutes, the top sheet and the back sheet of the paper diaper in the washing tub were peeled off, the contents of the absorbent body came out of the paper diaper, and the pulp fibers were dispersed in the liquid in the washing tub.
d-リモネンの濃度を0.01質量%に変更した以外は、実施例1と同様に実施した。15分間洗濯した後、洗濯槽内の紙おむつは表面シートと裏面シートが張り付いたままであり、吸収体は紙おむつの中に保持されたままであった。 Comparative Example 1
The same operation as in Example 1 was carried out except that the concentration of d-limonene was changed to 0.01% by mass. After washing for 15 minutes, the paper diaper in the washing tub had the top sheet and the back sheet stuck, and the absorbent body was held in the paper diaper.
d-リモネンの濃度を0.03質量%に変更した以外は、実施例1と同様に実施した。15分間洗濯した後、洗濯槽内の紙おむつは表面シートと裏面シートが張り付いたままであり、吸収体は紙おむつの中に保持されたままであった。 Comparative Example 2
The same operation as in Example 1 was carried out except that the concentration of d-limonene was changed to 0.03% by mass. After washing for 15 minutes, the paper diaper in the washing tub had the top sheet and the back sheet stuck, and the absorbent body was held in the paper diaper.
特開2010-84031号公報に記載の方法を追試した。具体的には、市販紙おむつ(ユニ・チャーム株式会社製「ムーニー」(登録商標)Mサイズ)に、先に調製した人工汚水240mLを吸水させた後、紙おむつを2槽式小型洗濯機(アルミス社製「晴晴」AST-01)の洗濯槽に1個投入し、洗濯槽内にCaO(和光純薬工業株式会社製)80gを投入し、続けて濃度250質量ppmの次亜塩素酸ナトリウム水溶液(和光純薬工業株式会社で購入したものを希釈して調製)6.5Lを投入した。15分間洗濯後、洗濯層内の液中に浮遊する紙おむつを回収し、おむつが形態を保持したまま分離していなかったため、手で物理的に表面材を破りおむつ内部の不活化した高吸水性ポリマーを含むパルプ繊維を回収した。回収したパルプ繊維の灰分を分析したところ、灰分は15.9質量%であった。 Comparative Example 3
The method described in JP 2010-84031 A was additionally tested. Specifically, after a commercial paper diaper (Moonie (registered trademark) M size manufactured by Unicharm Co., Ltd.) was allowed to absorb 240 mL of the artificial sewage prepared previously, the paper diaper was placed in a 2-tank small washing machine (Aluminus) One of them was put into a washing tub of “Harasei” AST-01), and 80 g of CaO (manufactured by Wako Pure Chemical Industries, Ltd.) was put into the washing tub, followed by a sodium hypochlorite aqueous solution having a concentration of 250 mass ppm ( 6.5 L was charged by diluting a product purchased from Wako Pure Chemical Industries, Ltd. After washing for 15 minutes, the paper diapers floating in the liquid in the washing layer were collected, and the diapers were not separated while retaining their form, so the surface material was physically broken by hand, and the inactivated high water absorption inside the diapers The pulp fiber containing the polymer was recovered. When the ash content of the recovered pulp fibers was analyzed, the ash content was 15.9% by mass.
市販紙おむつ(ユニ・チャーム株式会社製「ムーニー」(登録商標)Mサイズ)を2槽式小型洗濯機(アルミス社製「晴晴」AST-01)の洗濯槽に1個投入した。次いで、クエン酸200gとd-リモネン100gを10Lの水に溶かして、洗濯槽に投入した。洗濯機を稼働させ、9分間攪拌した。攪拌終了後、紙おむつは表面シートと裏面シートが剥がれ、中身の吸収体が紙おむつの外に出て、パルプ繊維は洗濯槽内の液中に分散していた。洗濯槽内の液中に浮遊する不織布、フィルム等の大型固形物を目開き10mmの金網ですくい取り、回収した。その後、排水し、洗濯槽内に残ったパルプ繊維と不活化した高吸水性ポリマー、および排水と一緒に槽外に排出されたパルプ繊維と不活化した高吸水性ポリマーを回収した。
図1に処理前の紙おむつの写真を、図2(a)に処理後の洗濯槽内の写真を、図2(b)に処理後に回収した不織布、フィルム等の写真を、図2(c)に処理後に回収したパルプ繊維と不活化した高吸水性ポリマーの写真を示す。
紙おむつはきれいに分解され、不織布、フィルム等の大型固形物と、パルプ繊維と不活化した高吸水性ポリマーとを容易に分離することができた。 Example 3
One commercially available disposable diaper (“Mooney” (registered trademark) M size manufactured by Unicharm Co., Ltd.) was put into a washing tub of a two-tank type small washing machine (“Haruharu” AST-01 manufactured by Arumis). Next, 200 g of citric acid and 100 g of d-limonene were dissolved in 10 L of water and put into a washing tub. The washing machine was turned on and stirred for 9 minutes. After completion of the stirring, the top sheet and the back sheet of the paper diaper were peeled off, the contents of the absorbent body came out of the paper diaper, and the pulp fibers were dispersed in the liquid in the washing tub. Large solids such as non-woven fabric and film floating in the liquid in the washing tub were scooped with a wire mesh having an opening of 10 mm and collected. Thereafter, drained and recovered the pulp fibers remaining in the washing tub and the inactivated superabsorbent polymer, and the pulp fibers discharged out of the tub together with the drainage and the inactivated superabsorbent polymer.
Fig. 1 shows a photograph of a disposable diaper before treatment, Fig. 2 (a) shows a photograph of a laundry tub after treatment, Fig. 2 (b) shows a photograph of a nonwoven fabric, a film, etc. collected after treatment, Fig. 2 (c). Shows photographs of the pulp fibers recovered after the treatment and the inactivated superabsorbent polymer.
The disposable diaper was decomposed cleanly, and large solids such as nonwoven fabrics and films could be easily separated from the pulp fibers and the inactivated superabsorbent polymer.
d-リモネンを3-カレンに変更し、実施例3と同様に実施した。
図3(a)に処理後の洗濯槽内の写真を、図3(b)に処理後に回収した不織布、フィルム等の写真を、図3(c)に処理後に回収したパルプ繊維と不活化した高吸水性ポリマーの写真を示す。
紙おむつはきれいに分解され、不織布、フィルム等の大型固形物と、パルプ繊維と不活化した高吸水性ポリマーとを容易に分離することができた。 Example 4
d-Limonene was changed to 3-carene, and the same procedure as in Example 3 was performed.
The photograph in the washing tub after processing is in FIG. 3 (a), the photograph of the nonwoven fabric, film, etc. recovered after processing in FIG. 3 (b) is inactivated with the pulp fiber recovered after processing in FIG. 3 (c). A photograph of a superabsorbent polymer is shown.
The disposable diaper was decomposed cleanly, and large solids such as nonwoven fabrics and films could be easily separated from the pulp fibers and the inactivated superabsorbent polymer.
d-リモネンをα-ピネンに変更し、実施例3と同様に実施した。
図4(a)に処理後の洗濯槽内の写真を、図4(b)に処理後に回収した不織布、フィルム等の写真を、図4(c)に処理後に回収したパルプ繊維と不活化した高吸水性ポリマーの写真を示す。
紙おむつはきれいに分解され、不織布、フィルム等の大型固形物と、パルプ繊維と不活化した高吸水性ポリマーとを容易に分離することができた。 Example 5
d-Limonene was changed to α-pinene and the same procedure as in Example 3 was performed.
The photograph in the washing tub after processing is in FIG. 4 (a), the photograph of the nonwoven fabric, film, etc. recovered after processing in FIG. 4 (b) is inactivated with the pulp fiber recovered after processing in FIG. 4 (c). A photograph of a superabsorbent polymer is shown.
The disposable diaper was decomposed cleanly, and large solids such as nonwoven fabrics and films could be easily separated from the pulp fibers and the inactivated superabsorbent polymer.
d-リモネン100gをシトラル89.4g(100mL)に変更し、実施例3と同様に実施した。
図5(a)に処理後の洗濯槽内の写真を、図5(b)に処理後に回収した不織布、フィルム等の写真を、図5(c)に処理後に回収したパルプ繊維と不活化した高吸水性ポリマーの写真を示す。
紙おむつはきれいに分解され、不織布、フィルム等の大型固形物と、パルプ繊維と不活化した高吸水性ポリマーとを容易に分離することができた。 Example 6
The same procedure as in Example 3 was performed, except that 100 g of d-limonene was changed to 89.4 g (100 mL) of citral.
Fig. 5 (a) shows the photograph in the washing tub after processing, Fig. 5 (b) shows the photograph of the nonwoven fabric, film, etc. recovered after the processing, and Fig. 5 (c) shows the pulp fibers recovered after the processing. A photograph of a superabsorbent polymer is shown.
The disposable diaper was decomposed cleanly, and large solids such as nonwoven fabrics and films could be easily separated from the pulp fibers and the inactivated superabsorbent polymer.
d-リモネン100gをγ-テルピネン91.3g(100mL)に変更し、実施例3と同様に実施した。
図6(a)に処理後の洗濯槽内の写真を、図6(b)に処理後に回収した不織布、フィルム等の写真を、図6(c)に処理後に回収したパルプ繊維と不活化した高吸水性ポリマーの写真を示す。
紙おむつはきれいに分解され、不織布、フィルム等の大型固形物と、パルプ繊維と不活化した高吸水性ポリマーとを容易に分離することができた。 Example 7
The same procedure as in Example 3 was carried out except that 100 g of d-limonene was changed to 91.3 g (100 mL) of γ-terpinene.
The photograph in the washing tub after processing is in FIG. 6 (a), the photograph of the non-woven fabric, film, etc. recovered after processing in FIG. 6 (b) is inactivated with the pulp fiber recovered after processing in FIG. 6 (c). A photograph of a superabsorbent polymer is shown.
The disposable diaper was decomposed cleanly, and large solids such as nonwoven fabrics and films could be easily separated from the pulp fibers and the inactivated superabsorbent polymer.
灰分とは、有機質が灰化されてあとに残った無機質または不燃性残留物の量をいう。灰分は、生理処理用品材料規格の「2.一般試験法」の「5.灰分試験法」に従って測定する。すなわち、灰分は、次のようにして測定する。
あらかじめ白金製、石英製または磁製のるつぼを500~550℃で1時間強熱し、放冷後、その質量を精密に量る。試料2~4gを採取し、るつぼに入れ、その質量を精密に量り、必要ならばるつぼのふたをとるか、またはずらし、初めは弱く加熱し、徐々に温度を上げて500~550℃で4時間以上強熱して、炭化物が残らなくなるまで灰化する。放冷後、その質量を精密に量る。再び残留物を恒量になるまで灰化し、放冷後、その質量を精密に量り、灰分の量(質量%)とする。 [Analytical analysis method]
Ash refers to the amount of inorganic or incombustible residue left after organic matter has been ashed. Ash content is measured in accordance with “5. Ash test method” in “2. That is, the ash content is measured as follows.
A platinum, quartz, or magnetic crucible is ignited in advance at 500 to 550 ° C. for 1 hour, allowed to cool, and then its mass is accurately measured. Take 2 to 4 g of sample, place in crucible, weigh accurately, remove or shift crucible if necessary, heat gently at first, gradually increase temperature to 500-550 ° C. Ignite for over an hour until no carbides remain. After standing to cool, weigh its mass precisely. The residue is incinerated until it reaches a constant weight, and after standing to cool, its mass is precisely measured to obtain the amount of ash (mass%).
Claims (13)
- パルプ繊維および高吸水性ポリマーを含む使用済み吸収性物品からパルプ繊維を回収する方法であって、該方法が、使用済み吸収性物品を、テルペン炭化水素、テルペンアルデヒドおよびテルペンケトンからなる群から選ばれる少なくとも1種のテルペンを0.05質量%以上含みかつ高吸水性ポリマーを不活化可能な不活化剤を含む水溶液で処理し、高吸水性ポリマーを不活化する工程を含むことを特徴とする方法。 A method for recovering pulp fibers from a used absorbent article comprising pulp fibers and a superabsorbent polymer, wherein the method is selected from the group consisting of terpene hydrocarbons, terpene aldehydes and terpene ketones. And a step of inactivating the superabsorbent polymer by treating with an aqueous solution containing at least one terpene that is 0.05% by mass or more and containing a deactivator capable of inactivating the superabsorbent polymer. Method.
- 前記水溶液で処理した後の使用済み吸収性物品から、パルプ繊維および不活化した高吸水性ポリマーを分離する工程をさらに含む請求項1に記載の方法。 The method according to claim 1, further comprising a step of separating pulp fibers and inactivated superabsorbent polymer from the used absorbent article after being treated with the aqueous solution.
- 分離したパルプ繊維および不活化した高吸水性ポリマーを含む混合物を酸化剤で処理し、不活化した高吸水性ポリマーを分解し、低分子量化し、可溶化する工程をさらに含む請求項2に記載の方法。 The method according to claim 2, further comprising a step of treating the mixture containing the separated pulp fibers and the inactivated superabsorbent polymer with an oxidizing agent, decomposing the inactivated superabsorbent polymer, reducing the molecular weight, and solubilizing. Method.
- 酸化剤で処理した混合物からパルプ繊維を分離する工程をさらに含む請求項3に記載の方法。 The method according to claim 3, further comprising separating pulp fibers from the mixture treated with the oxidizing agent.
- 高吸水性ポリマーを不活化可能な不活化剤を含む水溶液がpH2.5以下の有機酸水溶液であることを特徴とする請求項1~4のいずれか1項に記載の方法。 The method according to any one of claims 1 to 4, wherein the aqueous solution containing an inactivating agent capable of inactivating the superabsorbent polymer is an organic acid aqueous solution having a pH of 2.5 or lower.
- 有機酸がクエン酸であることを特徴とする請求項5に記載の方法。 The method according to claim 5, wherein the organic acid is citric acid.
- 有機酸水溶液のクエン酸濃度が2質量%以上であることを特徴とする請求項6に記載の方法。 The method according to claim 6, wherein the citric acid concentration of the organic acid aqueous solution is 2% by mass or more.
- テルペンがテルペン炭化水素であることを特徴とする請求項1~7のいずれか1項に記載の方法。 The method according to any one of claims 1 to 7, wherein the terpene is a terpene hydrocarbon.
- テルペンがリモネン、カレン、ピネン、テルピネンおよびシトラルからなる群から選ばれる少なくとも1種であることを特徴とする請求項8に記載の方法。 The method according to claim 8, wherein the terpene is at least one selected from the group consisting of limonene, karen, pinene, terpinene and citral.
- 前記水溶液中のテルペンの濃度が0.05~1.0質量%であることを特徴とする請求項1~9のいずれか1項に記載の方法。 The method according to any one of claims 1 to 9, wherein the concentration of the terpene in the aqueous solution is 0.05 to 1.0 mass%.
- 使用済み吸収性物品が熱可塑性樹脂からなる素材を含み、かつ前記方法が、使用済み吸収性物品からパルプ繊維および不活化した高吸水性ポリマーを分離した後の残渣を乾燥し、乾燥した残渣から熱可塑性樹脂からなる素材を分離する工程をさらに含むことを特徴とする請求項2~10のいずれか1項に記載の方法。 The used absorbent article includes a material made of a thermoplastic resin, and the method is to dry the residue after separating the pulp fiber and the inactivated superabsorbent polymer from the used absorbent article, and from the dried residue The method according to any one of claims 2 to 10, further comprising a step of separating a material made of a thermoplastic resin.
- 使用済み吸収性物品が熱可塑性樹脂フィルムを含み、かつ前記方法が、使用済み吸収性物品からパルプ繊維および不活化した高吸水性ポリマーを分離した後の残渣を乾燥し、乾燥した残渣から熱可塑性樹脂フィルムを分離する工程をさらに含むことを特徴とする請求項2~10のいずれか1項に記載の方法。 The used absorbent article comprises a thermoplastic resin film, and the method dries the residue after separating the pulp fibers and the inactivated superabsorbent polymer from the used absorbent article, and the thermoplastic from the dried residue. The method according to any one of claims 2 to 10, further comprising a step of separating the resin film.
- 吸収性物品が、紙おむつ、尿取りパッド、ベッドシーツ、生理用ナプキンおよびペットシーツからなる群から選択される少なくとも1種であることを特徴とする請求項1~12のいずれか1項に記載の方法。 The absorbent article according to any one of claims 1 to 12, wherein the absorbent article is at least one selected from the group consisting of disposable diapers, urine pads, bed sheets, sanitary napkins and pet sheets. Method.
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US16/322,111 US10533282B2 (en) | 2016-08-05 | 2017-06-09 | Method for recovering pulp fibers from used absorbent article |
AU2017305754A AU2017305754B2 (en) | 2016-08-05 | 2017-06-09 | Method for recovering pulp fibers from used absorbent article |
CN201780045801.1A CN109477298B (en) | 2016-08-05 | 2017-06-09 | Method for recovering pulp fiber from used absorbent article |
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---|---|---|---|---|
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Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH04317785A (en) * | 1991-04-15 | 1992-11-09 | Nippon Shokubai Co Ltd | Recovery of pulp from water absorbable product |
JP2003039023A (en) * | 2001-07-31 | 2003-02-12 | Daiki:Kk | Method for recovering raw material from soiled sanitary goods |
JP2003225645A (en) * | 2002-02-05 | 2003-08-12 | Tomio Wada | Method for separating and recovering pulp component and water absorbing polymer from used absorptive article |
JP2007159604A (en) * | 2005-12-09 | 2007-06-28 | Three M Innovative Properties Co | Remover composition for skin adhesive agent |
JP2010084031A (en) | 2008-09-30 | 2010-04-15 | Samuzu:Kk | Method for treating used paper diaper |
JP2012066156A (en) * | 2008-12-22 | 2012-04-05 | Kazutoshi Noguchi | Method for treating/incinerating used article for disposal of excreta |
JP2014217835A (en) * | 2013-04-10 | 2014-11-20 | ユニ・チャーム株式会社 | Method for recovering pulp fiber from used sanitary article and regenerated pulp obtained by the method |
WO2015190140A1 (en) * | 2014-06-12 | 2015-12-17 | ユニ・チャーム株式会社 | Method for manufacturing recycled pulp from used sanitary products |
JP2016123973A (en) * | 2014-12-26 | 2016-07-11 | ユニ・チャーム株式会社 | Recycling method of used absorbent article |
-
2017
- 2017-06-09 WO PCT/JP2017/021540 patent/WO2018025500A1/en unknown
Patent Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH04317785A (en) * | 1991-04-15 | 1992-11-09 | Nippon Shokubai Co Ltd | Recovery of pulp from water absorbable product |
JP2003039023A (en) * | 2001-07-31 | 2003-02-12 | Daiki:Kk | Method for recovering raw material from soiled sanitary goods |
JP2003225645A (en) * | 2002-02-05 | 2003-08-12 | Tomio Wada | Method for separating and recovering pulp component and water absorbing polymer from used absorptive article |
JP2007159604A (en) * | 2005-12-09 | 2007-06-28 | Three M Innovative Properties Co | Remover composition for skin adhesive agent |
JP2010084031A (en) | 2008-09-30 | 2010-04-15 | Samuzu:Kk | Method for treating used paper diaper |
JP2012066156A (en) * | 2008-12-22 | 2012-04-05 | Kazutoshi Noguchi | Method for treating/incinerating used article for disposal of excreta |
JP2014217835A (en) * | 2013-04-10 | 2014-11-20 | ユニ・チャーム株式会社 | Method for recovering pulp fiber from used sanitary article and regenerated pulp obtained by the method |
WO2015190140A1 (en) * | 2014-06-12 | 2015-12-17 | ユニ・チャーム株式会社 | Method for manufacturing recycled pulp from used sanitary products |
JP2016123973A (en) * | 2014-12-26 | 2016-07-11 | ユニ・チャーム株式会社 | Recycling method of used absorbent article |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113767196A (en) * | 2019-04-26 | 2021-12-07 | 尤妮佳股份有限公司 | Method for producing recycled pulp fibers from used absorbent articles containing superabsorbent polymers, pulp fibers and waste |
EP3940141A4 (en) * | 2019-04-26 | 2022-05-04 | Unicharm Corporation | Method for producing recycled pulp fiber from used absorbent article containing highly water-absorbent polymer, pulp fiber, and excrement |
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