TWI726234B - Method and system for recovering pulp fibers from used absorbent articles - Google Patents
Method and system for recovering pulp fibers from used absorbent articles Download PDFInfo
- Publication number
- TWI726234B TWI726234B TW107128944A TW107128944A TWI726234B TW I726234 B TWI726234 B TW I726234B TW 107128944 A TW107128944 A TW 107128944A TW 107128944 A TW107128944 A TW 107128944A TW I726234 B TWI726234 B TW I726234B
- Authority
- TW
- Taiwan
- Prior art keywords
- aqueous solution
- super absorbent
- absorbent polymer
- pulp fiber
- aforementioned
- Prior art date
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- 239000000835 fiber Substances 0.000 title claims abstract description 311
- 238000000034 method Methods 0.000 title claims abstract description 201
- 239000002250 absorbent Substances 0.000 title claims abstract description 112
- 230000002745 absorbent Effects 0.000 title claims abstract description 106
- 229920000247 superabsorbent polymer Polymers 0.000 claims abstract description 349
- 239000007864 aqueous solution Substances 0.000 claims abstract description 272
- 239000007788 liquid Substances 0.000 claims abstract description 194
- 238000011282 treatment Methods 0.000 claims abstract description 161
- 238000000926 separation method Methods 0.000 claims abstract description 140
- 230000008569 process Effects 0.000 claims abstract description 95
- 239000007800 oxidant agent Substances 0.000 claims abstract description 82
- 239000007787 solid Substances 0.000 claims abstract description 28
- 239000004583 superabsorbent polymers (SAPs) Substances 0.000 claims abstract description 22
- 230000002378 acidificating effect Effects 0.000 claims description 141
- 239000000463 material Substances 0.000 claims description 60
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 claims description 57
- 230000018044 dehydration Effects 0.000 claims description 18
- 238000006297 dehydration reaction Methods 0.000 claims description 18
- 230000002779 inactivation Effects 0.000 claims description 18
- 229920000642 polymer Polymers 0.000 claims description 18
- 239000000126 substance Substances 0.000 claims description 7
- 150000001875 compounds Chemical class 0.000 claims description 2
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 101
- 239000000428 dust Substances 0.000 description 71
- 230000001590 oxidative effect Effects 0.000 description 49
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 32
- 239000000243 solution Substances 0.000 description 29
- 230000005484 gravity Effects 0.000 description 27
- 239000000203 mixture Substances 0.000 description 25
- 235000015165 citric acid Nutrition 0.000 description 17
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- 238000002156 mixing Methods 0.000 description 7
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- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 6
- 150000007524 organic acids Chemical class 0.000 description 6
- 238000006864 oxidative decomposition reaction Methods 0.000 description 6
- 238000010979 pH adjustment Methods 0.000 description 6
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- 230000001070 adhesive effect Effects 0.000 description 5
- 238000000354 decomposition reaction Methods 0.000 description 5
- 150000007522 mineralic acids Chemical class 0.000 description 5
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- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 4
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- OSVXSBDYLRYLIG-UHFFFAOYSA-N dioxidochlorine(.) Chemical compound O=Cl=O OSVXSBDYLRYLIG-UHFFFAOYSA-N 0.000 description 4
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- NLKNQRATVPKPDG-UHFFFAOYSA-M potassium iodide Chemical compound [K+].[I-] NLKNQRATVPKPDG-UHFFFAOYSA-M 0.000 description 3
- 238000011084 recovery Methods 0.000 description 3
- AKHNMLFCWUSKQB-UHFFFAOYSA-L sodium thiosulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=S AKHNMLFCWUSKQB-UHFFFAOYSA-L 0.000 description 3
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- CIWBSHSKHKDKBQ-JLAZNSOCSA-N Ascorbic acid Chemical compound OC[C@H](O)[C@H]1OC(=O)C(O)=C1O CIWBSHSKHKDKBQ-JLAZNSOCSA-N 0.000 description 2
- 229920003043 Cellulose fiber Polymers 0.000 description 2
- 239000004155 Chlorine dioxide Substances 0.000 description 2
- RGHNJXZEOKUKBD-SQOUGZDYSA-N D-gluconic acid Chemical compound OC[C@@H](O)[C@@H](O)[C@H](O)[C@@H](O)C(O)=O RGHNJXZEOKUKBD-SQOUGZDYSA-N 0.000 description 2
- FEWJPZIEWOKRBE-JCYAYHJZSA-N Dextrotartaric acid Chemical compound OC(=O)[C@H](O)[C@@H](O)C(O)=O FEWJPZIEWOKRBE-JCYAYHJZSA-N 0.000 description 2
- AEMRFAOFKBGASW-UHFFFAOYSA-N Glycolic acid Chemical compound OCC(O)=O AEMRFAOFKBGASW-UHFFFAOYSA-N 0.000 description 2
- 239000004831 Hot glue Substances 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 2
- 239000004677 Nylon Substances 0.000 description 2
- 239000004698 Polyethylene Substances 0.000 description 2
- 229920001131 Pulp (paper) Polymers 0.000 description 2
- 239000005708 Sodium hypochlorite Substances 0.000 description 2
- FEWJPZIEWOKRBE-UHFFFAOYSA-N Tartaric acid Natural products [H+].[H+].[O-]C(=O)C(O)C(O)C([O-])=O FEWJPZIEWOKRBE-UHFFFAOYSA-N 0.000 description 2
- 235000019398 chlorine dioxide Nutrition 0.000 description 2
- 239000002131 composite material Substances 0.000 description 2
- 238000011109 contamination Methods 0.000 description 2
- 230000009849 deactivation Effects 0.000 description 2
- 238000009792 diffusion process Methods 0.000 description 2
- 229940093915 gynecological organic acid Drugs 0.000 description 2
- 230000000415 inactivating effect Effects 0.000 description 2
- 229910052742 iron Inorganic materials 0.000 description 2
- 229920001778 nylon Polymers 0.000 description 2
- 235000005985 organic acids Nutrition 0.000 description 2
- 229920001707 polybutylene terephthalate Polymers 0.000 description 2
- 229920000573 polyethylene Polymers 0.000 description 2
- 229920000139 polyethylene terephthalate Polymers 0.000 description 2
- 239000005020 polyethylene terephthalate Substances 0.000 description 2
- 230000000630 rising effect Effects 0.000 description 2
- SUKJFIGYRHOWBL-UHFFFAOYSA-N sodium hypochlorite Chemical compound [Na+].Cl[O-] SUKJFIGYRHOWBL-UHFFFAOYSA-N 0.000 description 2
- 235000019345 sodium thiosulphate Nutrition 0.000 description 2
- 230000001954 sterilising effect Effects 0.000 description 2
- 238000004659 sterilization and disinfection Methods 0.000 description 2
- 230000001629 suppression Effects 0.000 description 2
- 235000002906 tartaric acid Nutrition 0.000 description 2
- 239000011975 tartaric acid Substances 0.000 description 2
- 238000004448 titration Methods 0.000 description 2
- BJEPYKJPYRNKOW-REOHCLBHSA-N (S)-malic acid Chemical compound OC(=O)[C@@H](O)CC(O)=O BJEPYKJPYRNKOW-REOHCLBHSA-N 0.000 description 1
- VSKJLJHPAFKHBX-UHFFFAOYSA-N 2-methylbuta-1,3-diene;styrene Chemical compound CC(=C)C=C.C=CC1=CC=CC=C1.C=CC1=CC=CC=C1 VSKJLJHPAFKHBX-UHFFFAOYSA-N 0.000 description 1
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- RGHNJXZEOKUKBD-UHFFFAOYSA-N D-gluconic acid Natural products OCC(O)C(O)C(O)C(O)C(O)=O RGHNJXZEOKUKBD-UHFFFAOYSA-N 0.000 description 1
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- 239000004743 Polypropylene Substances 0.000 description 1
- 239000004820 Pressure-sensitive adhesive Substances 0.000 description 1
- 229920002472 Starch Polymers 0.000 description 1
- KDYFGRWQOYBRFD-UHFFFAOYSA-N Succinic acid Natural products OC(=O)CCC(O)=O KDYFGRWQOYBRFD-UHFFFAOYSA-N 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 235000011054 acetic acid Nutrition 0.000 description 1
- 239000003929 acidic solution Substances 0.000 description 1
- 150000001336 alkenes Chemical class 0.000 description 1
- BJEPYKJPYRNKOW-UHFFFAOYSA-N alpha-hydroxysuccinic acid Natural products OC(=O)C(O)CC(O)=O BJEPYKJPYRNKOW-UHFFFAOYSA-N 0.000 description 1
- 239000011668 ascorbic acid Substances 0.000 description 1
- 229960005070 ascorbic acid Drugs 0.000 description 1
- 235000010323 ascorbic acid Nutrition 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 238000004061 bleaching Methods 0.000 description 1
- KDYFGRWQOYBRFD-NUQCWPJISA-N butanedioic acid Chemical compound O[14C](=O)CC[14C](O)=O KDYFGRWQOYBRFD-NUQCWPJISA-N 0.000 description 1
- 239000001110 calcium chloride Substances 0.000 description 1
- 229910001628 calcium chloride Inorganic materials 0.000 description 1
- 238000004364 calculation method Methods 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 238000004332 deodorization Methods 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
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- 210000003608 fece Anatomy 0.000 description 1
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- 239000004571 lime Substances 0.000 description 1
- FPYJFEHAWHCUMM-UHFFFAOYSA-N maleic anhydride Chemical class O=C1OC(=O)C=C1 FPYJFEHAWHCUMM-UHFFFAOYSA-N 0.000 description 1
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- 150000002739 metals Chemical class 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
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- 239000005416 organic matter Substances 0.000 description 1
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- 230000002265 prevention Effects 0.000 description 1
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- 229920001935 styrene-ethylene-butadiene-styrene Polymers 0.000 description 1
- 210000002700 urine Anatomy 0.000 description 1
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Images
Classifications
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/70—Chemical treatment, e.g. pH adjustment or oxidation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/30—Destroying solid waste or transforming solid waste into something useful or harmless involving mechanical treatment
- B09B3/35—Shredding, crushing or cutting
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/30—Destroying solid waste or transforming solid waste into something useful or harmless involving mechanical treatment
- B09B3/38—Stirring or kneading
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B5/00—Operations not covered by a single other subclass or by a single other group in this subclass
-
- 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
-
- 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
- B29B17/04—Disintegrating plastics, e.g. by milling
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B30—PRESSES
- B30B—PRESSES IN GENERAL
- B30B9/00—Presses specially adapted for particular purposes
- B30B9/02—Presses specially adapted for particular purposes for squeezing-out liquid from liquid-containing material, e.g. juice from fruits, oil from oil-containing material
- B30B9/12—Presses specially adapted for particular purposes for squeezing-out liquid from liquid-containing material, e.g. juice from fruits, oil from oil-containing material using pressing worms or screws co-operating with a permeable casing
-
- 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
- C08J11/06—Recovery or working-up of waste materials of polymers without chemical reactions
- C08J11/08—Recovery or working-up of waste materials of polymers without chemical reactions using selective solvents for polymer components
-
- 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
- C08J11/16—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 inorganic material
-
- 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
- B29B2017/0217—Mechanical separating techniques; devices therefor
-
- 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
-
- 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
- Y02W30/20—Waste processing or separation
-
- 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
- Y02W30/52—Mechanical processing of waste for the recovery of materials, e.g. crushing, shredding, separation or disassembly
-
- 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
-
- 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
- Y02W30/64—Paper recycling
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical & Material Sciences (AREA)
- Mechanical Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Health & Medical Sciences (AREA)
- Polymers & Plastics (AREA)
- Medicinal Chemistry (AREA)
- Sustainable Development (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- General Chemical & Material Sciences (AREA)
- General Health & Medical Sciences (AREA)
- Toxicology (AREA)
- Processing Of Solid Wastes (AREA)
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
- Paper (AREA)
Abstract
提供一種由從使用完畢的吸收性物品所分離出之殘留高吸水性聚合物的紙漿纖維,以高處理效率將高吸水性聚合物去除的方法。 本發明係一種從包含紙漿纖維及高吸水性聚合物之使用完畢的吸收性物品回收紙漿纖維的方法,本方法係具備有:固液分離工程(S18),其係一邊將包含由使用完畢的吸收性物品被分離出的紙漿纖維及高吸水性聚合物的不活性化水溶液,分離成包含紙漿纖維及高吸水性聚合物的固體、與包含高吸水性聚合物及不活性化水溶液的液體,一邊將高吸水性聚合物壓碎;及氧化劑處理工程(S19),其係將經分離的固體所包含的紙漿纖維及被壓碎的高吸水性聚合物,以含有氧化劑的水溶液進行處理。Provided is a method for removing the superabsorbent polymer with high processing efficiency from the pulp fiber of the residual superabsorbent polymer separated from the used absorbent article. The present invention is a method for recovering pulp fibers from used absorbent articles containing pulp fibers and superabsorbent polymers. The method is equipped with: a solid-liquid separation process (S18). The pulp fiber and the inactivated aqueous solution of the super absorbent polymer separated from the absorbent article are separated into a solid containing the pulp fiber and the super absorbent polymer, and a liquid containing the super absorbent polymer and the inactivated aqueous solution, While crushing the super absorbent polymer; and the oxidizing agent treatment process (S19), which is to treat the pulp fiber contained in the separated solid and the crushed super absorbent polymer with an aqueous solution containing an oxidizing agent.
Description
本發明係關於從使用完畢的吸收性物品回收紙漿纖維的方法及系統。The present invention relates to a method and system for recovering pulp fibers from used absorbent articles.
已知一種從使用完畢的用後即棄紙尿褲等吸收性物品回收紙漿纖維的方法。例如,在專利文獻1中已揭示一種由使用完畢的衛生用品,製造再回收紙漿的方法。該方法係具備有:在酸性水溶液等之中,使物理上的力作用於使用完畢的衛生用品,將使用完畢的衛生用品分解成紙漿纖維與其他素材的工程;由紙漿纖維與其他素材的混合物中將紙漿纖維分離的工程;及以含臭氧水溶液處理經分離的紙漿纖維的工程。藉由以含臭氧水溶液處理紙漿纖維,將在分離出的紙漿纖維殘留不少的高吸水性聚合物氧化分解、低分子量化而可溶化,而可由紙漿纖維去除。
[先前技術文獻]
[專利文獻]A method for recovering pulp fibers from absorbent articles such as disposable diapers after use is known. For example,
[專利文獻1]日本特開2016-881號公報[Patent Document 1] Japanese Patent Application Laid-Open No. 2016-881
(發明所欲解決之課題)(The problem to be solved by the invention)
為使從使用完畢的吸收性物品被回收的紙漿纖維更為有用,紙漿纖維中的高吸水性聚合物的濃度的減低、或減低高吸水性聚合物的濃度的處理效率的提升極為重要。在專利文獻1的方法中,係藉由以含臭氧水溶液處理紙漿纖維,將殘留在紙漿纖維的高吸水性聚合物氧化分解,而可由紙漿纖維去除。但是,以含臭氧水溶液處理的時間相對耗費較長,在其處理效率的提升的觀點上,有改良餘地。期望一種由從使用完畢的吸收性物品所分離出之殘留高吸水性聚合物的紙漿纖維,以高處理效率去除高吸水性聚合物的技術。In order to make the pulp fibers recovered from the used absorbent articles more useful, it is extremely important to reduce the concentration of the superabsorbent polymer in the pulp fibers, or to improve the treatment efficiency of reducing the concentration of the superabsorbent polymer. In the method of
本發明之目的在提供可由從使用完畢的吸收性物品所分離出之殘留高吸水性聚合物的紙漿纖維,以高處理效率去除高吸水性聚合物的方法及系統。 (解決課題之手段)The object of the present invention is to provide a method and system for removing the superabsorbent polymer from the pulp fiber of the residual superabsorbent polymer separated from the used absorbent article with high processing efficiency. (Means to solve the problem)
本發明中之從包含紙漿纖維及高吸水性聚合物的使用完畢的吸收性物品回收紙漿纖維的方法係如下所示。(1)一種從使用完畢的吸收性物品回收紙漿纖維的方法,其係從包含紙漿纖維及高吸水性聚合物之使用完畢的吸收性物品回收紙漿纖維的方法,該方法係具備有:固液分離工程,其係一邊將包含由使用完畢的吸收性物品被分離出的紙漿纖維及高吸水性聚合物的不活性化水溶液,分離成包含前述紙漿纖維及前述高吸水性聚合物的固體、與包含前述高吸水性聚合物及前述不活性化水溶液的液體,一邊將前述固體所包含的前述高吸水性聚合物壓碎;及氧化劑處理工程,其係將經分離的前述固體所包含的前述紙漿纖維及被壓碎的前述高吸水性聚合物,以含有氧化劑的水溶液進行處理。 本方法係藉由將殘留在紙漿纖維之經吸水的凝膠狀(塊狀或大致球狀)的高吸水性聚合物壓碎(例示:藉由以凝膠強度以上的壓力壓碎),使高吸水性聚合物的厚度變薄,形成為平坦的形狀或微細分裂的形狀。亦即,本方法係藉由塊狀或大致球狀的高吸水性聚合物的壓碎,可將高吸水性聚合物的表面積擴展較大,可增加使原為高吸水性聚合物的內側的部分露出於表側等露出的部分。因此,在氧化劑處理工程中,若為塊狀或大致球狀的高吸水性聚合物,可使原難以與氧化劑相接觸的高吸水性聚合物的內側的部分接觸氧化劑等,可加大高吸水性聚合物中與氧化劑的接觸面積。藉此,可更有效率地進展高吸水性聚合物的氧化分解,可縮短氧化劑處理的時間。因此,可提高從紙漿纖維去除高吸水性聚合物的處理效率。在此,以氧化劑而言,列舉:臭氧、二氧化氯、過氧乙酸、次氯酸鈉、過氧化氫等。The method of recovering the pulp fiber from the used absorbent article containing pulp fiber and superabsorbent polymer in this invention is as follows. (1) A method for recovering pulp fibers from used absorbent articles, which is a method for recovering pulp fibers from used absorbent articles containing pulp fibers and superabsorbent polymers, and the method includes: solid-liquid The separation process involves separating the inactivated aqueous solution containing the pulp fiber and super absorbent polymer separated from the used absorbent article into a solid containing the pulp fiber and the super absorbent polymer, and A liquid containing the aforementioned super absorbent polymer and the aforementioned inactivated aqueous solution, while crushing the aforementioned super absorbent polymer contained in the aforementioned solid; and an oxidizing agent treatment process, which is the aforementioned pulp contained in the separated solid The fiber and the crushed super absorbent polymer are treated with an aqueous solution containing an oxidizing agent. This method crushes the water-absorbed gel-like (block or roughly spherical) superabsorbent polymer remaining in the pulp fiber (for example: crushed by pressure higher than the gel strength) to make The thickness of the superabsorbent polymer becomes thinner, and it is formed into a flat shape or a finely divided shape. That is, this method can expand the surface area of the superabsorbent polymer by crushing the block or roughly spherical superabsorbent polymer, and increase the inner surface of the superabsorbent polymer. Partially exposed on exposed parts such as the front side. Therefore, in the oxidizing agent treatment process, if it is a block or roughly spherical superabsorbent polymer, the inner part of the superabsorbent polymer that is difficult to contact with the oxidizing agent can be contacted with the oxidizing agent, etc., and the superabsorbent can be increased. The area of contact with the oxidant in the polymer. Thereby, the oxidative decomposition of the super absorbent polymer can be progressed more efficiently, and the time for the oxidizing agent treatment can be shortened. Therefore, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved. Here, as an oxidant, ozone, chlorine dioxide, peroxyacetic acid, sodium hypochlorite, hydrogen peroxide, etc. are listed.
本方法亦可為(2)如上述(1)所記載之方法,其中,前述固液分離工程係包含:壓碎工程,其係將包含前述紙漿纖維與前述高吸水性聚合物的前述不活性化水溶液,以加壓式脫水法進行處理,將殘留在前述紙漿纖維的前述高吸水性聚合物壓碎。 本方法係藉由加壓式脫水法,將殘留在紙漿纖維的高吸水性聚合物壓碎,因此可同時有效率且確實地執行固液分離、及紙漿纖維上的高吸水性聚合物的壓碎。亦即,本方法係可有效率而且確實地將紙漿纖維上的高吸水性聚合物的表面積擴展較大。藉此,可提高從紙漿纖維去除高吸水性聚合物的處理效率。其中,殘留在紙漿纖維的高吸水性聚合物係例示為附著在紙漿纖維的表面的高吸水性聚合物。This method may also be (2) the method described in (1) above, wherein the solid-liquid separation process includes: a crushing process, which combines the inactive pulp fibers and the superabsorbent polymer. The aqueous solution is treated by a pressurized dehydration method to crush the superabsorbent polymer remaining in the pulp fiber. This method crushes the superabsorbent polymer remaining on the pulp fiber by the pressurized dehydration method, so that the solid-liquid separation and the pressure of the superabsorbent polymer on the pulp fiber can be efficiently and reliably performed at the same time. broken. That is, this method can efficiently and surely expand the surface area of the superabsorbent polymer on the pulp fiber to a larger extent. Thereby, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved. Among them, the super absorbent polymer system remaining on the pulp fiber is exemplified as the super absorbent polymer attached to the surface of the pulp fiber.
本方法亦可為(3)如上述(2)所記載之方法,其中,前述壓碎工程中的前述加壓式脫水法的加壓時的壓力係0.02MPa以上、0.5MPa以下。 本方法係將加壓式脫水法的加壓時的壓力形成為0.02MPa以上、0.5MPa以下。因此,本方法係不會損傷紙漿纖維,而可將殘留在紙漿纖維的高吸水性聚合物充分壓碎,因此可將高吸水性聚合物的表面積充分擴展較大。藉此,可提高從紙漿纖維去除高吸水性聚合物的處理效率。但是,若將壓力形成為未達0.02MPa,無法將高吸水性聚合物充分壓碎,因此,不太能縮短氧化劑處理的時間,若使壓力大於0.5MPa,雖然可將高吸水性聚合物充分壓碎,但是有損傷紙漿纖維之虞。This method may also be (3) the method described in (2) above, wherein the pressure during the pressurization of the pressurized dehydration method in the crushing process is 0.02 MPa or more and 0.5 MPa or less. In this method, the pressure during the pressurization of the pressurized dehydration method is set to 0.02 MPa or more and 0.5 MPa or less. Therefore, this method does not damage the pulp fibers, but can sufficiently crush the superabsorbent polymer remaining in the pulp fibers, and therefore can sufficiently expand the surface area of the superabsorbent polymer. Thereby, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved. However, if the pressure is less than 0.02 MPa, the super absorbent polymer cannot be crushed sufficiently. Therefore, the oxidant treatment time cannot be shortened. If the pressure is greater than 0.5 MPa, the super absorbent polymer can be sufficiently reduced. Crushing, but there is a risk of damaging the pulp fibers.
本方法亦可為(4)如上述(1)至(3)中任一者之方法,其中,在前述固液分離工程之前,另外具備有:由包含前述紙漿纖維與前述高吸水性聚合物的前述不活性化水溶液,將前述高吸水性聚合物及前述不活性化水溶液的一部分進行分離的工程。 本方法係在固液分離工程之前,由包含紙漿纖維與高吸水性聚合物的不活性化水溶液,將一定量的高吸水性聚合物及不活性化水溶液進行分離。因此,本方法係可將固液分離工程中被供給的材料(紙漿纖維、高吸水性聚合物及不活性化水溶液)中的高吸水性聚合物的比例抑制為較低。藉此,可在固液分離工程中,將附著在紙漿纖維的高吸水性聚合物更有效率地壓碎,且可提高從紙漿纖維去除高吸水性聚合物的處理效率。This method may also be (4) the method of any one of (1) to (3) above, wherein, prior to the solid-liquid separation process, the method is additionally provided with: comprising the pulp fiber and the super absorbent polymer The said inactivation aqueous solution is a process of separating a part of the said super absorbent polymer and the said inactivation aqueous solution. In this method, before the solid-liquid separation process, a certain amount of super absorbent polymer and the inactivated aqueous solution are separated from the inactivated aqueous solution containing the pulp fiber and the super absorbent polymer. Therefore, this method can suppress the ratio of the super absorbent polymer in the materials (pulp fiber, super absorbent polymer, and inactivated aqueous solution) supplied in the solid-liquid separation process to a low level. Thereby, in the solid-liquid separation process, the super absorbent polymer adhering to the pulp fiber can be crushed more efficiently, and the processing efficiency of removing the super absorbent polymer from the pulp fiber can be improved.
本方法亦可為(5)如上述(1)至(4)中任一者之方法,其中,前述固液分離工程中被供給的前述不活性化水溶液中的前述高吸水性聚合物的比例係50%以下。 在本方法中,在固液分離工程中,將成為分離對象的不活性化水溶液中的高吸水性聚合物的比例設為50%以下。藉此,由於不需要將過剩的量的高吸水性聚合物壓碎,因此可將高吸水性聚合物更確實且更有效率地壓碎。藉此,可提高從紙漿纖維去除高吸水性聚合物的處理效率。This method may also be (5) the method of any one of (1) to (4) above, wherein the ratio of the super absorbent polymer in the inactivated aqueous solution supplied in the solid-liquid separation process Department below 50%. In this method, in the solid-liquid separation process, the ratio of the superabsorbent polymer in the inactivated aqueous solution to be separated is 50% or less. Thereby, since there is no need to crush an excessive amount of super absorbent polymer, the super absorbent polymer can be crushed more reliably and efficiently. Thereby, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved.
本方法亦可為(6)如上述(1)至(5)中任一者之方法,其中,在前述固液分離工程之前,另外具備有:將前述使用完畢的吸收性物品在不活性化水溶液中進行破碎的工程;及由包含在前述進行破碎的工程中所得的破碎物的不活性化水溶液,將包含紙漿纖維及高吸水性聚合物的不活性化水溶液進行分離的工程。 在本方法中,藉由進行破碎的工程及進行分離的工程,生成在固液分離工程中被供給之包含從使用完畢的吸收性物品被分離出的紙漿纖維與高吸水性聚合物的不活性化水溶液。藉此,可抑制在不活性化水溶液中混入異物(用後即棄吸收性物品的紙漿纖維及高吸水性聚合物以外的資材(例示:薄膜(背面薄片等)、不織布(表面薄片等)、彈性體(防漏壁用橡膠等))。藉此,不會有被異物阻礙的情形而可更加正確地將高吸水性聚合物壓碎。結果,可提高從紙漿纖維去除高吸水性聚合物的處理效率。This method may also be (6) the method of any one of (1) to (5) above, wherein, before the solid-liquid separation process, the method is additionally provided with: inactivating the used absorbent article A process of crushing in an aqueous solution; and a process of separating an inactivated aqueous solution containing pulp fibers and a super absorbent polymer from the inactivated aqueous solution containing the crushed material obtained in the foregoing crushing process. In this method, through the process of crushing and the process of separating, the inactive material containing the pulp fiber separated from the used absorbent article and the super absorbent polymer supplied in the solid-liquid separation process is generated.化液。 Water solution. This can prevent foreign matter (pulp fibers of disposable absorbent articles and materials other than superabsorbent polymers (examples: films (back sheets, etc.)), non-woven fabrics (surface sheets, etc.) from being mixed in the inactivated aqueous solution. Elastomers (rubbers for leak-proof walls, etc.). With this, the super absorbent polymer can be crushed more accurately without being hindered by foreign matter. As a result, the removal of the super absorbent polymer from the pulp fiber can be improved The processing efficiency.
本方法亦可為(7)如上述(1)至(6)中任一者之方法,其中,前述不活性化水溶液係酸性水溶液。 在本方法中,由於不活性化水溶液為酸性水溶液,因此可將使用完畢的吸收性物品中的高吸水性聚合物確實地脫水,且形成為預定的大小(例示:粒徑)以下。藉此,可在固液分離工程中,輕易地一邊進行固液分離,一邊將高吸水性聚合物壓碎。結果,可提高從紙漿纖維去除高吸水性聚合物的處理效率。This method may also be (7) the method of any one of (1) to (6) above, wherein the inactivation aqueous solution is an acidic aqueous solution. In this method, since the inactivation aqueous solution is an acidic aqueous solution, the superabsorbent polymer in the used absorbent article can be surely dehydrated and formed into a predetermined size (example: particle size) or less. Thereby, it is possible to easily crush the super absorbent polymer while performing solid-liquid separation in the solid-liquid separation process. As a result, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved.
本方法亦可為(8)如上述(7)之方法,其中,前述酸性水溶液係pH2.5以下。 在本方法中,由於酸性水溶液為pH2.5以下,因此可將使用完畢的吸收性物品中的高吸水性聚合物更確實地脫水,且形成為預定的大小(例示:粒徑)以下。藉此,可在固液分離工程中,更加輕易地一邊進行固液分離,一邊將高吸水性聚合物壓碎。結果,可提高從紙漿纖維去除高吸水性聚合物的處理效率。此外,由於將高吸水性聚合物在凝膠的狀態下形成為預定的大小以下,因此可將高吸水性聚合物輕易壓碎。This method may also be (8) the method as described in (7) above, wherein the acidic aqueous solution has a pH of 2.5 or less. In this method, since the acidic aqueous solution has a pH of 2.5 or less, the superabsorbent polymer in the used absorbent article can be dehydrated more reliably and be formed to a predetermined size (example: particle size) or less. Thereby, in the solid-liquid separation process, the super absorbent polymer can be crushed more easily while performing solid-liquid separation. As a result, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved. In addition, since the super absorbent polymer is formed into a predetermined size or less in the state of a gel, the super absorbent polymer can be easily crushed.
本方法亦可為(9)如上述(7)或(8)之方法,其中,前述酸性水溶液係含有檸檬酸。 在本方法中,由於酸性水溶液含有檸檬酸(例示:濃度0.5~2.0質量%),因此可將使用完畢的吸收性物品中的高吸水性聚合物確實地脫水,且形成為預定的粒徑以下。藉此,可在固液分離工程中,輕易地一邊進行固液分離,一邊將高吸水性聚合物壓碎。結果,可提高從紙漿纖維去除高吸水性聚合物的處理效率。This method may also be (9) the method of (7) or (8) above, wherein the acidic aqueous solution contains citric acid. In this method, since the acidic aqueous solution contains citric acid (example: concentration 0.5 to 2.0% by mass), the super absorbent polymer in the used absorbent article can be reliably dehydrated and formed into a predetermined particle size or less . Thereby, it is possible to easily crush the super absorbent polymer while performing solid-liquid separation in the solid-liquid separation process. As a result, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved.
本發明中之被使用在用以從包含紙漿纖維及高吸水性聚合物的使用完畢的吸收性物品回收紙漿纖維的系統係如下所示。(10)一種從使用完畢的吸收性物品回收紙漿纖維的系統,其係從包含紙漿纖維及高吸水性聚合物的使用完畢的吸收性物品回收紙漿纖維的系統,該系統係具備有:固液分離裝置,其係一邊將包含由使用完畢的吸收性物品被分離出的紙漿纖維及高吸水性聚合物的不活性化水溶液,分離成包含前述紙漿纖維及前述高吸水性聚合物的固體、與包含前述高吸水性聚合物及前述不活性化水溶液的液體,一邊將前述固體所包含的前述高吸水性聚合物壓碎;及氧化劑處理裝置,其係將經分離的前述固體所包含的前述紙漿纖維及被壓碎的前述高吸水性聚合物,以含有氧化劑的水溶液進行處理。 本系統係藉由將殘留在紙漿纖維之經吸水的凝膠狀(塊狀或大致球狀)的高吸水性聚合物壓碎(例示:藉由以凝膠強度以上的壓力壓碎),使高吸水性聚合物的厚度變薄,而形成為平坦的形狀或微細分裂的形狀。亦即,本系統係藉由高吸水性聚合物的壓碎,可將塊狀或大致球狀的高吸水性聚合物的表面積擴展較大,且可增加使原為高吸水性聚合物的內側的部分露出於表側等露出的部分增加。因此,在氧化劑處理裝置中,若為塊狀或大致球狀的高吸水性聚合物,可使原難以與氧化劑相接觸的高吸水性聚合物的內側的部分接觸氧化劑等,可加大高吸水性聚合物中與氧化劑的接觸面積。藉此,可更有效率地進展高吸水性聚合物的氧化分解,可縮短氧化劑處理的時間。因此,可提高從紙漿纖維去除高吸水性聚合物的處理效率。The system used in the present invention for recovering pulp fibers from used absorbent articles containing pulp fibers and superabsorbent polymers is as follows. (10) A system for recovering pulp fibers from used absorbent articles, which is a system for recovering pulp fibers from used absorbent articles containing pulp fibers and superabsorbent polymers, and the system is equipped with: solid-liquid Separating device, which separates the inactivated aqueous solution containing the pulp fiber and super absorbent polymer separated from the used absorbent article into a solid containing the pulp fiber and the super absorbent polymer, and A liquid containing the aforementioned super absorbent polymer and the aforementioned inactivated aqueous solution, while crushing the aforementioned super absorbent polymer contained in the aforementioned solid; and an oxidizing agent treatment device which treats the aforementioned pulp contained in the aforementioned solid after separation The fiber and the crushed super absorbent polymer are treated with an aqueous solution containing an oxidizing agent. This system crushes the water-absorbed gel-like (block or roughly spherical) superabsorbent polymer remaining in the pulp fiber (example: crushed by pressure higher than the gel strength) to make The thickness of the superabsorbent polymer becomes thin, and it is formed into a flat shape or a finely divided shape. In other words, this system can expand the surface area of the block or roughly spherical superabsorbent polymer by crushing the superabsorbent polymer, and increase the inner side of the superabsorbent polymer. The part exposed on the front side and the exposed part increase. Therefore, in the oxidizing agent treatment device, if it is a block or roughly spherical superabsorbent polymer, the inner part of the superabsorbent polymer that is difficult to contact with the oxidizing agent can be contacted with the oxidizing agent, etc., and the superabsorbent can be increased. The area of contact with the oxidant in the polymer. Thereby, the oxidative decomposition of the super absorbent polymer can be progressed more efficiently, and the time for the oxidizing agent treatment can be shortened. Therefore, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved.
本系統亦可為(11)如上述(10)之系統,其中,前述固液分離裝置係包含:螺旋壓榨式脫水機,其係將包含前述紙漿纖維及前述高吸水性聚合物的前述不活性化水溶液,以加壓式脫水法進行處理,將殘留在前述紙漿纖維的前述高吸水性聚合物壓碎。 本系統係藉由利用螺旋壓榨式脫水機所為之加壓式脫水法,將殘留在紙漿纖維的高吸水性聚合物壓碎,因此可同時有效率且確實地執行固液分離、及紙漿纖維上的高吸水性聚合物的壓碎。亦即,本系統係可有效率且確實地將紙漿纖維上的高吸水性聚合物的表面積擴展較大。藉此,可提高從紙漿纖維去除高吸水性聚合物的處理效率。其中,殘留在紙漿纖維的高吸水性聚合物係例示為附著在紙漿纖維的表面的高吸水性聚合物。This system may also be (11) the system as described in (10) above, wherein the solid-liquid separation device includes: a screw press dehydrator, which combines the aforementioned inactive pulp fibers and the aforementioned superabsorbent polymer The aqueous solution is treated by a pressurized dehydration method to crush the superabsorbent polymer remaining in the pulp fiber. This system crushes the superabsorbent polymer remaining in the pulp fiber by using the pressurized dewatering method of the screw press dehydrator, so it can efficiently and reliably perform the solid-liquid separation and the pulp fiber at the same time. The crushing of the super absorbent polymer. That is, this system can efficiently and surely expand the surface area of the superabsorbent polymer on the pulp fiber. Thereby, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved. Among them, the super absorbent polymer system remaining on the pulp fiber is exemplified as the super absorbent polymer attached to the surface of the pulp fiber.
本系統亦可為(12)如上述(11)之系統,其中,前述螺旋壓榨式脫水機中的前述加壓式脫水法的加壓時的壓力係0.02MPa以上、0.5MPa以下。 本系統係將加壓式脫水法的加壓時的壓力形成為0.02MPa以上、0.5MPa以下。因此,本系統並不會損傷紙漿纖維,而可將殘留在紙漿纖維的高吸水性聚合物充分壓碎,因此可將高吸水性聚合物的表面積充分擴展較大。藉此,可提高從紙漿纖維去除高吸水性聚合物的處理效率。但是,若使壓力為未達0.02MPa,無法將高吸水性聚合物充分壓碎,因此,不太能縮短氧化劑處理的時間,若使壓力大於0.5MPa,雖然可將高吸水性聚合物充分壓碎,但是有損傷紙漿纖維之虞。This system may also be (12) the system of the above-mentioned (11), wherein the pressure during the pressurization of the pressurized dehydration method in the screw press dehydrator is 0.02 MPa or more and 0.5 MPa or less. In this system, the pressure during the pressurization of the pressurized dehydration method is 0.02 MPa or more and 0.5 MPa or less. Therefore, the system does not damage the pulp fibers, but can fully crush the super absorbent polymer remaining in the pulp fibers, so the surface area of the super absorbent polymer can be fully expanded. Thereby, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved. However, if the pressure is less than 0.02 MPa, the super absorbent polymer cannot be crushed sufficiently. Therefore, the oxidizing agent treatment time cannot be shortened. If the pressure is greater than 0.5 MPa, the super absorbent polymer can be fully compressed. Broken, but there is a risk of damaging the pulp fibers.
本系統亦可為(13)如上述(10)至(12)中任一者之系統,其中,另外具備有:圓筒篩式脫水機,其係在前述固液分離工程之前,由包含前述紙漿纖維與前述高吸水性聚合物的前述不活性化水溶液,將前述高吸水性聚合物及前述不活性化水溶液的一部分進行分離。 本系統係在固液分離裝置之前,以圓筒篩式脫水機,由包含紙漿纖維與高吸水性聚合物的不活性化水溶液,將一定量的高吸水性聚合物及不活性化水溶液進行分離。因此,本系統係可將固液分離工程中被供給的材料(紙漿纖維、高吸水性聚合物及不活性化水溶液)中的高吸水性聚合物的比例抑制為較低。藉此,可以螺旋壓榨式脫水機,將附著在紙漿纖維的高吸水性聚合物更有效率地壓碎,可提高從紙漿纖維去除高吸水性聚合物的處理效率。This system can also be (13) the system of any one of (10) to (12) above, in which it is additionally equipped with: a cylindrical screen type dehydrator, which is set before the solid-liquid separation process and includes the aforementioned The pulp fiber and the inactivated aqueous solution of the super absorbent polymer are separated from a part of the super absorbent polymer and the inactivated aqueous solution. This system is in front of the solid-liquid separation device, using a cylindrical screen dehydrator to separate a certain amount of super absorbent polymer and inactivated aqueous solution from an inactivated aqueous solution containing pulp fiber and super absorbent polymer . Therefore, this system can suppress the ratio of the super absorbent polymer in the materials (pulp fiber, super absorbent polymer, and inactivated aqueous solution) supplied in the solid-liquid separation process to a low level. Thereby, the screw press type dehydrator can more efficiently crush the super absorbent polymer adhering to the pulp fiber, and the processing efficiency of removing the super absorbent polymer from the pulp fiber can be improved.
本系統亦可為(14)如上述(10)至(13)中任一者之系統,其中,前述固液分離裝置被供給的前述不活性化水溶液中的前述高吸水性聚合物的比例係50%以下。 在本系統中,在固液分離裝置中,將成為分離對象的不活性化水溶液中的高吸水性聚合物的比例設為50%以下。藉此,由於不需要將過剩的量的高吸水性聚合物壓碎,因此可將高吸水性聚合物更確實且更有效率地壓碎。藉此,可提高從紙漿纖維去除高吸水性聚合物的處理效率。This system may also be (14) the system of any one of (10) to (13) above, wherein the ratio of the super absorbent polymer in the inactivated aqueous solution supplied to the solid-liquid separation device is based on Less than 50%. In this system, in the solid-liquid separator, the ratio of the superabsorbent polymer in the inactivated aqueous solution to be separated is 50% or less. Thereby, since there is no need to crush an excessive amount of super absorbent polymer, the super absorbent polymer can be crushed more reliably and efficiently. Thereby, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved.
本系統亦可為(15)如上述(10)至(14)中任一者之系統,其中,前述不活性化水溶液係酸性水溶液。 在本系統中,由於不活性化水溶液為酸性水溶液,因此可將使用完畢的吸收性物品中的高吸水性聚合物確實地脫水,且形成為預定的粒徑以下。藉此,可在固液分離裝置中,輕易地一邊進行固液分離,一邊將高吸水性聚合物壓碎。結果,可提高從紙漿纖維去除高吸水性聚合物的處理效率。This system may also be (15) the system of any one of (10) to (14) above, wherein the aforementioned inactivated aqueous solution is an acidic aqueous solution. In this system, since the inactivation aqueous solution is an acidic aqueous solution, the superabsorbent polymer in the used absorbent article can be surely dehydrated and formed into a predetermined particle size or less. Thereby, the super absorbent polymer can be crushed easily while performing solid-liquid separation in the solid-liquid separation device. As a result, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved.
本系統亦可為(16)如上述(15)之系統,其中,前述酸性水溶液係pH2.5以下。 在本系統中,由於酸性水溶液為pH2.5以下,因此可將使用完畢的吸收性物品中的高吸水性聚合物更確實地脫水,且形成為預定粒徑以下。藉此,可在螺旋壓榨式脫水機中,更加輕易地一邊進行固液分離,一邊將高吸水性聚合物壓碎。結果,可提高從紙漿纖維去除高吸水性聚合物的處理效率。此外,由於將高吸水性聚合物在凝膠的狀態下形成為預定的粒徑以下,因此可將高吸水性聚合物輕易壓碎。This system may also be (16) the system as described in (15) above, wherein the aforementioned acidic aqueous solution has a pH of 2.5 or less. In this system, since the acidic aqueous solution has a pH of 2.5 or less, the superabsorbent polymer in the used absorbent article can be dehydrated more reliably and be formed to a predetermined particle size or less. Thereby, in the screw press type dehydrator, the super absorbent polymer can be crushed more easily while the solid-liquid separation is performed. As a result, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved. In addition, since the super absorbent polymer is formed into a predetermined particle size or less in a gel state, the super absorbent polymer can be easily crushed.
本系統亦可為(17)如上述(15)或(16)之系統,其中,前述酸性水溶液係含有檸檬酸。 在本系統中,由於酸性水溶液含有檸檬酸(例示:濃度0.5~2.0質量%),因此可將使用完畢的吸收性物品中的高吸水性聚合物確實地脫水,且形成為預定粒徑以下。藉此,可在螺旋壓榨式脫水機中,輕易地一邊進行固液分離,一邊將高吸水性聚合物壓碎。結果,可提高從紙漿纖維去除高吸水性聚合物的處理效率。 (發明之效果)This system may also be (17) the system as described in (15) or (16) above, wherein the aforementioned acidic aqueous solution contains citric acid. In this system, since the acidic aqueous solution contains citric acid (example: concentration 0.5 to 2.0% by mass), the superabsorbent polymer in the used absorbent article can be surely dehydrated and formed into a predetermined particle size or less. Thereby, it is possible to easily crush the super absorbent polymer while performing solid-liquid separation in the screw press type dehydrator. As a result, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved. (Effects of the invention)
藉由本發明之方法及系統,可由從使用完畢的吸收性物品所分離出之殘留高吸水性聚合物的紙漿纖維,以高處理效率去除高吸水性聚合物。With the method and system of the present invention, the pulp fiber of the residual super absorbent polymer separated from the used absorbent article can be removed with high treatment efficiency.
以下說明實施形態之從包含紙漿纖維及高吸水性聚合物的使用完畢的吸收性物品回收紙漿纖維的方法。其中,使用完畢的吸收性物品係指被使用者所使用的吸收性物品,包含吸收/保持使用者的排泄物的狀態的吸收性物品,亦包含雖經使用但未吸收/保持排泄物者、或雖未使用卻被廢棄者。以吸收性物品而言,列舉例如紙尿褲、尿墊、生理期用衛生棉、床舖薄片、寵物薄片。其中,本實施形態之從使用完畢的吸收性物品回收紙漿纖維的方法係生成再回收紙漿纖維,因此亦可謂為從使用完畢的吸收性物品生成再回收紙漿纖維的方法。此外,本實施形態之從使用完畢的吸收性物品回收紙漿纖維的方法係在途中連同紙漿纖維一起回收高吸水性聚合物,且藉由分離,生成再回收高吸水性聚合物,因此亦可謂為從使用完畢的吸收性物品回收高吸水性聚合物的方法、或生成再回收高吸水性聚合物的方法。在此係作為從使用完畢的吸收性物品回收紙漿纖維的方法來說明。Hereinafter, a method of recovering pulp fibers from a used absorbent article containing pulp fibers and a super absorbent polymer according to the embodiment will be described. Among them, the used absorbent article refers to the absorbent article used by the user, including the absorbent article that absorbs/maintains the excrement of the user, and also includes those that have not absorbed/maintained the excrement after use, Or those who have not been used but have been discarded. Examples of absorbent articles include diapers, urine pads, sanitary napkins for menstrual periods, bed sheets, and pet sheets. Among them, the method of recovering pulp fibers from used absorbent articles in the present embodiment is to generate recycled pulp fibers, so it can also be referred to as a method of generating recycled pulp fibers from used absorbent articles. In addition, the method of recovering pulp fibers from used absorbent articles in this embodiment is to recover the super absorbent polymer along with the pulp fibers on the way, and by separating, produce and recycle the super absorbent polymer, so it can also be described as A method of recovering a super absorbent polymer from a used absorbent article, or a method of producing and recovering a super absorbent polymer. This is explained as a method of recovering pulp fibers from used absorbent articles.
首先,說明吸收性物品的構成例。吸收性物品具備有:表面薄片、背面薄片、及配置在表面薄片與背面薄片之間的吸收體。以吸收性物品的大小之一例而言,列舉:長度約15~100cm、寬度5~100cm。其中,吸收性物品亦可包含一般的吸收性物品所具備的另外其他構件,例如擴散薄片或防漏壁等。First, an example of the configuration of an absorbent article will be described. The absorbent article includes a top sheet, a back sheet, and an absorber arranged between the top sheet and the back sheet. As an example of the size of an absorbent article, the length is about 15 to 100 cm, and the width is 5 to 100 cm. Among them, the absorbent article may also include other other members provided in general absorbent articles, such as a diffusion sheet or a leak-proof wall.
以表面薄片的構成構件而言,列舉例如:液透過性的不織布、具有液透過孔的合成樹脂薄膜、該等的複合薄片等。以背面薄片的構成構件而言,列舉例如:液不透過性的不織布、液不透過性的合成樹脂薄膜、該等的複合薄片。以擴散薄片的構成構件而言,列舉例如:液透過性的不織布。以防漏壁的構成構件而言,列舉例如:液不透過性的不織布,亦可包含如橡膠的彈性構件。在此,以不織布或合成樹脂薄膜的材料而言,若可作為吸收性物品來使用,並無特別限制,列舉例如:聚乙烯、聚丙烯等烯烴系樹脂、6-尼龍、6,6-尼龍等聚醯胺系樹脂、聚對苯二甲酸乙二酯(PET)、聚對苯二甲酸丁二酯(PBT)等聚酯系樹脂等。在本實施形態中,以將背面薄片的構成構件作為薄膜,將表面薄片的構成構件作為不織布的吸收性物品為例來進行說明。As the structural member of the surface sheet, for example, a liquid-permeable nonwoven fabric, a synthetic resin film having liquid-permeable holes, and such composite sheets are listed. The constituent members of the back sheet include, for example, liquid-impermeable non-woven fabrics, liquid-impermeable synthetic resin films, and composite sheets of these. As the constituent member of the diffusion sheet, for example, a liquid-permeable non-woven fabric is cited. As a constituent member of the leakage prevention wall, for example, a liquid-impermeable non-woven fabric may be mentioned, and an elastic member such as rubber may be included. Here, the non-woven fabric or synthetic resin film material is not particularly limited if it can be used as an absorbent article. Examples include olefin resins such as polyethylene and polypropylene, 6-nylon, and 6,6-nylon. Polyamide resins, polyester resins such as polyethylene terephthalate (PET) and polybutylene terephthalate (PBT). In this embodiment, an absorbent article in which the constituent member of the back sheet is used as a film and the constituent member of the front sheet is used as a non-woven fabric will be described as an example.
以吸收體的構成構件而言,係列舉:吸收體材料,亦即紙漿纖維及高吸水性聚合物。以紙漿纖維而言,若可作為吸收性物品來使用,並無特別限制,列舉例如:纖維素系纖維。以纖維素系纖維而言,列舉例如:木材紙漿、架橋紙漿、非木材紙漿、再生纖維素、半合成纖維素等。以紙漿纖維的大小而言,列舉:纖維長徑的平均值為例如數十μm,以20~40μm為佳,列舉纖維長的平均值例如數mm,以2~5mm為佳。以高吸水性聚合物(SuperAbsorbent Polymer:SAP)而言,若可作為吸收性物品來使用,並無特別限制,列舉例如:聚丙烯酸酯系、聚磺酸鹽系、馬來酸酐鹽系的吸水性聚合物。以高吸水性聚合物的大小(乾燥時)而言,列舉粒徑的平均值為例如數百μm,以200~500μm為佳。In terms of the constituent members of the absorber, a series of examples include: absorber materials, namely pulp fibers and super absorbent polymers. The pulp fiber is not particularly limited as long as it can be used as an absorbent article, and examples include cellulose fibers. For cellulose fibers, for example, wood pulp, cross-linked pulp, non-wood pulp, regenerated cellulose, semi-synthetic cellulose, and the like are listed. In terms of the size of the pulp fiber, the average value of the fiber long diameter is, for example, several tens of μm, preferably 20 to 40 μm, and the average value of the fiber length is, for example, several mm, preferably 2 to 5 mm. In terms of superabsorbent polymer (SuperAbsorbent Polymer: SAP), if it can be used as an absorbent article, there is no particular limitation, for example: polyacrylate series, polysulfonate series, maleic anhydride salt series.性polymer. In terms of the size of the super absorbent polymer (when dried), the average particle size is, for example, several hundreds of μm, preferably 200 to 500 μm.
吸收體的其中一面及另一面係分別透過接著劑而被接合在表面薄片及背面薄片。在平面視下,表面薄片之中以包圍吸收體的方式朝吸收體的外側延伸的部分(周緣部分)係透過接著劑而與背面薄片之中以包圍吸收體的方式朝吸收體的外側延伸的部分(周緣部分)相接合。因此,吸收體係被包入在表面薄片與背面薄片的接合體的內部。以接著劑而言,若可作為吸收性物品來使用,且後述之藉由溫水而軟化等而接合力降低者,並無特別限制,列舉例如熱熔型接著劑。以熱熔型接著劑而言,列舉例如:苯乙烯-乙烯-丁二烯-苯乙烯、苯乙烯-乙烯-苯乙烯、苯乙烯-異戊二烯-苯乙烯等橡膠系主體、或聚乙烯等烯烴系主體的感壓型接著劑或感熱型接著劑。One surface and the other surface of the absorber are respectively bonded to the top sheet and the back sheet through the adhesive. In a plan view, the part (peripheral part) of the surface sheet that extends to the outside of the absorber so as to surround the absorber is through the adhesive and extends to the outside of the absorber so as to surround the absorber in the back sheet. The parts (peripheral parts) are joined. Therefore, the absorbent system is enclosed in the bonded body of the top sheet and the back sheet. There are no particular restrictions on the adhesive as long as it can be used as an absorbent article, and the adhesive strength is reduced by softening with warm water as described later, and examples include hot-melt adhesives. For hot-melt adhesives, for example, rubber-based bodies such as styrene-ethylene-butadiene-styrene, styrene-ethylene-styrene, styrene-isoprene-styrene, etc., or polyethylene Pressure sensitive adhesives or heat sensitive adhesives based on olefins.
接著,說明實施形態之從包含紙漿纖維及高吸水性聚合物的使用完畢的吸收性物品回收紙漿纖維的方法。在本實施形態中,係將使用完畢的吸收性物品由外部回收/取得來使用,俾供再利用(再回收)之用。此時,使用完畢的吸收性物品係以髒污(排泄物等)或菌類或臭氣不會逸逃至外部的方式被封入在複數個收集用袋(以下亦稱為「收集袋」)。收集袋內的各個的使用完畢的吸收性物品係以排泄物不會露出於表側的方式,而且,以臭氣不會擴散至周圍的方式,以被排泄排泄物的表面薄片為內側,主要在被弄成一團的狀態或被折疊的狀態下被回收等。Next, a method of recovering pulp fibers from a used absorbent article containing pulp fibers and a super absorbent polymer according to the embodiment will be described. In this embodiment, the used absorbent article is recycled/obtained from the outside for use for reuse (recycling). At this time, the used absorbent article is enclosed in a plurality of collection bags (hereinafter also referred to as "collection bags") so that dirt (excretion, etc.), fungi or odors will not escape to the outside. Each used absorbent article in the collection bag is designed so that the excrement will not be exposed on the surface and the odor will not spread to the surroundings. The surface sheet of the excreted excrement is used as the inner side, mainly in It is collected in a balled state or folded state.
首先,說明從使用完畢的吸收性物品回收紙漿纖維的方法所使用的系統1。系統1係從使用完畢的吸收性物品回收紙漿纖維(較佳為甚至高吸水性聚合物),因此生成再回收紙漿纖維(較佳為甚至再回收高吸水性聚合物)的系統。圖1係顯示本實施形態之系統1之一例的區塊圖。系統1係具備有:第3分離裝置18、及氧化劑處理裝置19,較佳為具備有:破袋裝置11、破碎裝置12、第1分離裝置13、第1除塵裝置14、第2除塵裝置15、第3除塵裝置16、第2分離裝置17、及第4分離裝置20。以下詳細說明之。First, the
首先,說明破袋裝置11及破碎裝置12。破袋裝置11係在包含使用完畢的吸收性物品的收集袋,在不活性化水溶液中開孔。破碎裝置12係連同收集袋一起將沈在不活性化水溶液的水面下的不活性化水溶液中的使用完畢的吸收性物品進行破碎。其中,不活性化水溶液係指將高吸水性聚合物不活性化的水溶液,因不活性化,高吸水性聚合物的吸水性能降低。藉此,高吸水性聚合物係若比已降低的吸水性能吸收更多的水時,將水放出,亦即脫水至以吸水性能可容許的量。以下係以使用酸性水溶液作為不活性化水溶液的情形為例進行說明。First, the
圖2係顯示圖1的破袋裝置11及破碎裝置12的構成例的模式圖。
破袋裝置11係蓄積例如透過具備閥的配管而被供給的酸性水溶液B,在被放入在該酸性水溶液B中的收集袋A開孔。破袋裝置11係包含:溶液槽V、及開孔部50。溶液槽V係蓄積酸性水溶液B。開孔部50係設在溶液槽V內,當收集袋A被放入在溶液槽V時,在收集袋A中與酸性水溶液B相接的表面開孔。
開孔部50係包含:送入部30、及破袋部40。送入部30係將收集袋A(物理性強制性地)送入(引入)至溶液槽V內的酸性水溶液B中。送入部30係列舉例如攪拌機,具備有:攪拌葉片33、支持攪拌葉片33的支持軸(旋轉軸)32、及將支持軸32沿著軸旋轉的驅動裝置31。攪拌葉片33藉由驅動裝置31而繞著旋轉軸(支持軸32)旋轉,藉此在酸性水溶液B發生旋流。送入部30係藉由旋流,將收集袋A引入至酸性水溶液B(溶液槽V)的底部方向。
破袋部40係被配置在溶液槽V的下部(較佳為底部),具備有:破袋刃41、支持破袋刃41的支持軸(旋轉軸)42、及將支持軸42沿著軸旋轉的驅動裝置43。破袋刃41係藉由驅動裝置43而繞著旋轉軸(支持軸42)旋轉,藉此在移動至酸性水溶液B(溶液槽V)的下部的收集袋A開孔。其中,溶液槽V的下部係表示比溶液槽V的高度方向的一半位置更為下側的部分。
其中,破袋裝置11的開孔部50的破袋刃41亦可一邊繞著旋轉軸(支持軸42)旋轉,一邊在溶液槽V中以上下方向移動。此時,因破袋刃41朝向上方移動,收集袋A即使未朝酸性水溶液B(溶液槽V)的下部移動,亦可在收集袋A開孔。Fig. 2 is a schematic diagram showing a configuration example of the
破碎裝置12係連同收集袋A一起將沈入至酸性水溶液B的水面下的收集袋A內的使用完畢的吸收性物品破碎。破碎裝置12係包含:破碎部60、及泵63。破碎部60係以配管61而與溶液槽V相連接,將由溶液槽V連同酸性水溶液B一起被送出的收集袋A內的使用完畢的吸收性物品(混合液91),連同收集袋A一起在酸性水溶液B中進行破碎。以破碎部60而言,列舉:雙軸破碎機(例示:雙軸旋轉式破碎機、雙軸差動式破碎機、雙軸切變式破碎機),列舉例如:SUMICUTTER(住友重機械環境股份有限公司製)。泵63係以配管62而與破碎部60相連接,將在破碎部60所得的破碎物連同酸性水溶液B一起由破碎部60引出(混合液92),且送出至下一工程。其中,破碎物係包含有:紙漿纖維及高吸水性聚合物、與其他資材(收集袋A的素材、薄膜、不織布、彈性體等)。破袋裝置11與破碎裝置12較佳為彼此不同的裝置。The crushing
參照圖1,第1分離裝置13係攪拌包含在破碎裝置12所得的破碎物與酸性水溶液的混合液92,一邊進行由破碎物去除髒污(排泄物等)的洗淨,一邊由混合液92分離紙漿纖維、高吸水性聚合物及酸性水溶液(混合液93),且送出至第1除塵裝置14。
以第1分離裝置13而言,係列舉例如具備洗衣槽兼脫水槽及包圍其之水槽的洗衣機。其中,洗衣槽兼脫水槽(旋轉筒)被使用作為洗淨槽兼篩槽(分離槽)。設在洗衣槽周面的複數貫穿孔的大小係形成為破碎物之中的紙漿纖維及高吸水性聚合物容易通過而其他資材難以通過的大小。以洗衣機而言,列舉例如橫型洗衣機ECO-22B(稻本製作所股份有限公司製)。1, the
其中,亦可不在不活性化水溶液(例示:酸性水溶液)中連同收集袋一起將使用完畢的吸收性物品進行破碎,而在氣體中(例示:空氣中)連同收集袋一起將使用完畢的吸收性物品進行破碎。此時並不需要破袋裝置11,在無不活性化水溶液的狀態的空氣中,破碎裝置12進行破碎。之後,破碎裝置12的破碎物與不活性化水溶液被供給至第1分離裝置13。Among them, it is not necessary to break the used absorbent article together with the collection bag in the inactivated aqueous solution (example: acidic aqueous solution), and to break the used absorbent article together with the collection bag in the gas (example: air) The item is broken. At this time, the
其中,若在破袋裝置11~第1分離裝置13之間,未使用酸性水溶液作為不活性化水溶液時,亦可由第1除塵裝置14對不活性化水溶液添加酸性水溶液,且將被供給至第1除塵裝置14之包含紙漿纖維及高吸水性聚合物的不活性化水溶液實質上形成為酸性水溶液。此時,可以pH來輕易調整高吸水性聚合物的比重及大小。Among them, if the acidic aqueous solution is not used as the inactivated aqueous solution between the
第1除塵裝置14係一邊在預定的範圍內維持pH,一邊將由第1分離裝置13被送出之包含紙漿纖維及高吸水性聚合物的酸性水溶液(混合液93),藉由具有複數開口的篩,分離成酸性水溶液中的紙漿纖維及高吸水性聚合物(混合液94)與其他資材(異物)。為了在預定的範圍內維持pH,係例如不添加在途中使pH變動的液體(例示:水),或若添加液體時,則大概形成為相同pH的液體(例示:酸性水溶液)。預定的範圍係指pH的變動為±1.0以內的範圍。
第1除塵裝置14係列舉例如篩式分離機(粗篩分離機)。但是,在篩(screen)的開口並無特別限制,列舉例如:開縫、圓孔、四角孔、網孔,在此係使用圓孔。開口的大小,亦即圓孔的大小(直徑)係形成為紙漿纖維及高吸水性聚合物可通過的大小,且以原以第1分離裝置13無法去除的其他資材(異物)難以通過的大小,而且大於第2除塵裝置15的篩的開縫的寬幅的大小。圓孔的大小係例如直徑2~5mmφ,藉此可去除至少10mm見方左右以上的其他資材(異物)。若為開縫,開縫的大小(寬幅)為例如2~5mm。
其中,由異物去除的效率提升的觀點來看,亦可一邊將由第1分離裝置13被送出的混合液93加壓(例示:0.5~1kgf/cm2
),一邊供給至第1除塵裝置14。第1除塵裝置14係列舉例如Pack Pulper(SATOMI製作所股份有限公司製)。The first
第2除塵裝置15係一邊在預定的範圍內維持pH,一邊將由第1除塵裝置14被送出之包含紙漿纖維及高吸水性聚合物的酸性水溶液(混合液94),藉由具有複數開口的篩,分離成酸性水溶液中的紙漿纖維及高吸水性聚合物(混合液95)與其他資材(異物)。
第2除塵裝置15係列舉例如篩分離機。其中,篩(screen)的開口並無特別限制,列舉例如:開縫、圓孔、四角孔、網孔,在此係使用開縫。開縫的大小(寬幅)係設為紙漿纖維及高吸水性聚合物可通過的大小,且原以第1除塵裝置14無法去除的其他資材(異物)難以通過的大小。開縫的大小係例如寬幅0.2~0.5mm,藉此可去除至少3mm見方左右以上的其他資材(異物)。若為圓孔,圓孔的大小(直徑)係例如直徑0.2~0.5mmφ。
其中,由異物去除的效率提升的觀點來看,亦可一邊將由第1除塵裝置14被送出的混合液94加壓(例示:0.5~2kgf/cm2
),一邊供給至第2除塵裝置15。由去除相對較小的異物的觀點來看,其壓力係以高於第1除塵裝置14的壓力為佳。以第2除塵裝置15而言,列舉例如RAMOLT SCREEN(相川鐵工股份有限公司製)。The second
第3除塵裝置16係一邊在預定的範圍內維持pH,一邊將由第2除塵裝置15被送出之包含紙漿纖維及高吸水性聚合物的酸性水溶液(混合液95)進行離心分離,將酸性水溶液中的紙漿纖維及高吸水性聚合物(混合液96)與其他資材(重量大的異物)分離。
第3除塵裝置16係列舉例如旋風分離機。以相對比重較輕的酸性水溶液中的紙漿纖維及高吸水性聚合物上升,比該等為比重較重的異物(金屬等)下降的方式,以預定的流速,將包含紙漿纖維及高吸水性聚合物的酸性水溶液(混合液95),供給至第3除塵裝置16之相反方向的圓錐框體(未圖示)內。以第3除塵裝置16而言,例示為ACT低濃度清潔器(相川鐵工股份有限公司製)。The third
第2分離裝置17係將由第3除塵裝置16被送出之包含紙漿纖維及高吸水性聚合物的酸性水溶液(混合液96),藉由具有複數開口的篩,分離成酸性水溶液中的紙漿纖維(混合液97)、及酸性水溶液中的高吸水性聚合物。因此,可看作由混合液96連同高吸水性聚合物一起去除酸性水溶液的脫水機。
第2分離裝置17係列舉例如圓筒篩式分離機。其中,圓筒篩(screen)的開口並無特別限制,列舉例如開縫、圓孔、四角、網孔,在此係使用開縫。開縫的大小(寬幅)係設為高吸水性聚合物可通過的大小,而且紙漿纖維難以通過的大小。若為開縫,開縫的大小係例如寬幅0.2~0.8mm,藉此可至少去除較多的高吸水性聚合物。若為圓孔,圓孔的大小係例如直徑0.2~0.8mmφ。以第2分離裝置17而言,列舉圓筒篩式脫水機(Toyo Screen股份有限公司製)。The
第3分離裝置18係將由第2分離裝置17被送出的紙漿纖維、無法分離而殘留下來的高吸水性聚合物及酸性水溶液(混合液97),一邊藉由具有複數開口的篩,分離成包含紙漿纖維及高吸水性聚合物的固體(混合物98)、及包含高吸水性聚合物及酸性水溶液的液體,一邊對固體施加壓力,而將固體中的高吸水性聚合物壓碎。因此,第3分離裝置18亦可看作由混合液97連同高吸水性聚合物一起去除酸性水溶液的加壓脫水方式的脫水機。其中,固體(混合物98)係含有些微酸性水溶性。
圖3係顯示圖1的第3分離裝置18的構成例的模式圖。第3分離裝置18係列舉例如螺旋壓榨式脫水機。第3分離裝置18係例如具備有:圓筒篩81、螺旋軸82、螺旋葉片83、驅動裝置86、蓋體84、及調壓裝置85。圓筒篩81係設在框體80內的圓筒狀的篩(screen)。螺旋軸82係沿著圓筒篩81的圓筒的軸延伸,其直徑隨著朝向圓筒篩81的前端部而逐漸變大。螺旋葉片83係以螺旋狀設在螺旋軸82的外側,沿著圓筒篩81的內周面旋轉。螺旋葉片83的間距亦可隨著朝向圓筒篩81的前端部而逐漸變窄。驅動裝置86係將螺旋軸82旋轉。蓋體84係設成閉塞圓筒篩81的前端部。調壓裝置85係調整將蓋體84按壓在圓筒篩81的前端部的按壓的壓力。
其中,圓筒篩(screen)81的開口並無特別限制,列舉例如:開縫、圓孔、四角、網孔,在此係使用開縫。開縫的大小(寬幅)係形成為高吸水性聚合物可通過的大小,而且紙漿纖維難以通過的大小。若為開縫,開縫的大小係例如寬幅0.1~0.5mm,至少可將剩餘的高吸水性聚合物去除。第3分離裝置18係一邊由圓筒篩81側面的開縫送出包含高吸水性聚合物與酸性水溶液的液體E,一邊由圓筒篩81前端部與蓋體84的間隙G,送出包含紙漿纖維與高吸水性聚合物的固體(混合物98)。固體(混合物98)送出時,高吸水性聚合物被壓碎。被施加在蓋體的按壓的壓力係列舉例如0.01MPa以上、1MPa以下。以第3分離裝置18而言,列舉螺旋壓榨式脫水機(川口精機股份有限公司製)。The
氧化劑處理裝置19係將由第3分離裝置18被送出之包含固體中被壓碎的高吸水性聚合物的紙漿纖維(混合物98),以含有氧化劑的水溶液(處理液)進行處理。藉此,將高吸水性聚合物進行氧化分解而由紙漿纖維去除,將未含有吸水性聚合物的紙漿纖維連同處理液一起送出(混合液99)。The oxidizing
圖4係顯示氧化劑處理裝置19的構成例的模式圖。氧化劑處理裝置19係若使用臭氧作為氧化劑,包含:泵121、處理槽123、泵125、臭氧發生裝置126、臭氧混合裝置127、及臭氧分解裝置129。處理槽123係具有酸性水溶液作為處理液P,由被設在上部的供給口122b被供給混合物98。酸性水溶液若使用臭氧作為氧化劑,以提高臭氧的安定性方面為佳。泵121係透過配管132,由處理槽123的底部的送出口124a抽出處理液P,由處理槽123的上部的供給口122a供給至處理槽123中。泵125係透過配管136,由處理槽123的底部的送出口124b抽出處理液P,由處理槽123的下部的供給口122c供給至處理槽123中。臭氧發生裝置126係生成屬於氣體狀物質的含臭氧氣體Z,且供給至臭氧混合裝置127。臭氧混合裝置127係位於配管136的途中,將透過配管135被供給的含臭氧氣體Z,混合在朝向處理槽123的下部的供給口122c而在配管136內流通的處理液P。臭氧混合裝置127係將含臭氧氣體Z形成為複數微細氣泡而供給至處理液P中。含臭氧氣體Z係含有臭氧的其他種類氣體,列舉例如含有臭氧的氧氣或空氣。以臭氧發生裝置126而言,列舉例如:EcoDesign股份有限公司製臭氧水曝露試驗機ED-OWX-2、三菱電機股份有限公司製臭氧發生裝置OS-25V等。臭氧分解裝置129係經由配管134收取蓄積在處理槽123的上部的含臭氧氣體Z,將臭氧分解且無害化而放出至外部。其中,處理槽123內的處理液P係初期僅有處理液P,開始後係形成為混合有處理液P與混合物98的液體,但是在本實施形態中,係亦包含混合有處理液P與混合物98的液體,將處理槽123內的液體作為處理液P。FIG. 4 is a schematic diagram showing a configuration example of the
圖5係顯示氧化劑處理裝置19的其他構成例的模式圖。氧化劑處理裝置19係具備有:連同處理液Pa一起貯藏包含紙漿纖維的混合物98的混合液貯藏部110;及將處理液Pa中的紙漿纖維所包含的被壓碎的高吸水性聚合物,藉由處理液P進行氧化分解而由紙漿纖維去除的氧化劑處理部120。混合液貯藏部110係包含:混合液槽112、及攪拌機113。混合液槽112係在處理液Pa中貯藏透過配管131而被供給之包含紙漿纖維的混合物98。攪拌機113係在混合液槽112中的處理液Pa中攪拌,俾使混合物98不會下沈至處理液Pa中的下方。另一方面,氧化劑處理部120係包含:泵121a、處理槽123、臭氧供給裝置128、泵125a、及臭氧分解裝置129。處理槽123係具有酸性水溶液作為處理液P。泵121a係透過配管132a而將包含混合液槽112的混合物98的處理液Pa,以第1流量連續供給至處理槽123之中。臭氧供給裝置128係在臭氧發生裝置126發生屬於氣體狀物質的含臭氧氣體Z,且透過配管135而供給至處理槽123。送出含臭氧氣體Z的噴嘴127a係配置在處理槽123的下部(較佳為底部),具有例如管狀或平板狀的形狀。噴嘴127a係將含臭氧氣體Z形成為複數微細氣泡而在處理液P中,由處理槽123的下部朝向上部連續供給。泵125a係透過配管133,將處理槽123內的處理液P,以第2流量連續排出至處理槽123之外。臭氧分解裝置129係經由配管134而收取蓄積在處理槽123的上部的含臭氧氣體Z,將臭氧分解且無害化而放出至外部。FIG. 5 is a schematic diagram showing another configuration example of the
其中,上述之氧化劑處理裝置19係使用臭氧作為氧化劑,但是亦可使用其他氧化劑,亦可為即使非為氣體狀的氧化劑,亦可使液體的氧化劑或固體的氧化劑熔融在液中者。以氧化劑而言,列舉例如:二氧化氯、過氧乙酸、次氯酸鈉、過氧化氫。Among them, the above-mentioned
第4分離裝置20係由在氧化劑處理裝置19被處理之包含紙漿纖維的處理液(混合液99),藉由具有複數開口的篩,將紙漿纖維分離,藉此回收紙漿纖維,且生成再回收紙漿纖維。
以第4分離裝置20而言,列舉例如篩分離機。其中,篩(screen)的開口並無特別限制,列舉例如開縫、圓孔、四角孔、網孔,在此係使用開縫。開縫的大小(寬幅)係紙漿纖維難以通過的大小。開縫的大小係例如寬幅0.2~0.8mm。若為圓孔,圓孔的大小係例如直徑0.2~0.8mmφ。The
其中,系統1較佳為具備有:臭氧處理裝置22、pH調整裝置23、及貯水槽24。該等裝置係用以將在系統1中所使用的酸性水溶液再生且再利用的裝置。藉由酸性水溶液的再利用,可削減酸性水溶液的成本。臭氧處理裝置22係將由在第2分離裝置17被分離出的高吸水性聚合物及酸性水溶液另外使高吸水性聚合物被分離出之後的酸性水溶液101,以含臭氧水溶液進行殺菌處理。pH調整裝置23係調整以含臭氧水溶液予以殺菌處理後的酸性水溶液102的pH,生成所再生的酸性水溶液103。貯水槽24係貯留所再生的酸性水溶液103之中的剩餘份。Among them, the
接著,說明從使用完畢的吸收性物品回收紙漿纖維的方法。該方法係從使用完畢的吸收性物品回收紙漿纖維(較佳為甚至高吸水性聚合物),因此生成再回收紙漿纖維(較佳為甚至回收高吸水性聚合物)的方法。圖6係顯示本實施形態之方法之一例的流程圖。該方法係具備有:第3分離工程S18、及氧化劑處理工程S19,較佳為具備有:開孔工程S11、破碎工程S12、第1分離工程S13、第1除塵工程S14、第2除塵工程S15、第3除塵工程S16、第2分離工程S17、及第4分離工程S20。以下詳細說明之。Next, a method of recovering pulp fibers from the used absorbent article will be described. This method is a method of recovering pulp fibers (preferably even super absorbent polymers) from used absorbent articles, so that recycled pulp fibers (preferably even super absorbent polymers) are generated. Fig. 6 is a flowchart showing an example of the method of this embodiment. The method system includes: the third separation process S18, and the oxidant treatment process S19, preferably: the hole-opening process S11, the crushing process S12, the first separation process S13, the first dust removal process S14, and the second dust removal process S15 , The third dust removal process S16, the second separation process S17, and the fourth separation process S20. The following is a detailed description.
開孔工程S11係藉由破袋裝置11來執行。已封入使用完畢的吸收性物品的收集袋A被投入至貯留有酸性水溶液B的溶液槽V,在收集袋A中與酸性水溶液B相接的表面開孔。酸性水溶液B係當在收集袋A開孔時,以收集袋A內的使用完畢的吸收性物品的髒污或菌類或臭氣不會被放出至外部的方式,包圍收集袋A的周圍來進行密封。若酸性水溶液由孔浸入至收集袋A內,收集袋A內的氣體逸逃至收集袋A的外部,收集袋A的比重比酸性水溶液B重,收集袋A沈積在酸性水溶液B內。此外,酸性水溶液B係將收集袋A內的使用完畢的吸收性物品內的高吸水性聚合物不活性化。The hole-opening process S11 is performed by the
使用完畢的吸收性物品內的高吸水性聚合物不活性化,其吸水能力降低,由此高吸水性聚合物脫水,粒徑變小,因此容易在後續的各工程中處理,處理效率提升。之所以使用酸性水溶液,亦即無機酸及有機酸的水溶液作為不活性化水溶液,係基於與石灰或氯化鈣等水溶液相比較,灰分不會殘留在紙漿纖維之故,此外,容易以pH來調整不活性化的程度(粒徑或比重的大小)之故。以酸性水溶液的pH而言,以1.0以上、4.0以下為佳,以1.2以上、2.5以下為較佳。若pH過高,無法使高吸水性聚合物的吸水能力充分降低。此外,亦有殺菌能力降低之虞。若pH過低,有設備腐蝕之虞,在排水處理時的中和處理中必須要有較多的鹼性藥品。尤其,為了分離成紙漿纖維及高吸水性聚合物、及其他資材,以紙漿纖維的大小或比重與高吸水性聚合物的大小或比重相對較近為佳。因此,以酸性水溶液的pH而言,藉由形成為1.0以上、4.0以下,可藉由不活性化而使高吸水性聚合物更小,藉此,可使紙漿纖維的大小或比重與高吸水性聚合物的大小或比重彼此相對較近。以有機酸而言,列舉例如:檸檬酸、酒石酸、乙醇酸、蘋果酸、琥珀酸、乙酸、抗壞血酸等,以檸檬酸、酒石酸、葡萄糖酸等羥基碳酸酯系有機酸尤佳。藉由檸檬酸的螯合效應,排泄物中的金屬離子等被捕捉且可去除,而且因檸檬酸的洗淨效果,可期待較高的髒污成分去除效果。另一方面,以無機酸而言,列舉例如:硫酸、鹽酸、硝酸,惟由不含氯或成本等觀點來看,以硫酸為佳。pH係依水溫而改變,因此本發明中的pH係指以水溶液溫度20℃所測定到的pH者。有機酸水溶液的有機酸濃度並未特別限定,若有機酸為檸檬酸,以0.5質量%以上、4質量%以下為佳。無機酸水溶液的無機酸濃度並未特別限定,若無機酸為硫酸,以0.1質量%以上、0.5質量%以下為佳。The superabsorbent polymer in the used absorbent article is inactivated and its water absorption capacity is reduced. As a result, the superabsorbent polymer is dehydrated and the particle size becomes smaller. Therefore, it is easy to handle in subsequent processes and the processing efficiency is improved. The reason for using an acidic aqueous solution, that is, an aqueous solution of an inorganic acid and an organic acid, as the inactivation aqueous solution, is based on the fact that ash does not remain on the pulp fibers compared with aqueous solutions such as lime or calcium chloride. In addition, it is easy to change the pH Adjust the degree of inactivation (the size of the particle size or specific gravity). With regard to the pH of the acidic aqueous solution, it is preferably 1.0 or more and 4.0 or less, and more preferably 1.2 or more and 2.5 or less. If the pH is too high, the water absorption capacity of the super absorbent polymer cannot be sufficiently reduced. In addition, there is a risk that the sterilization ability will decrease. If the pH is too low, there is a risk of equipment corrosion, and more alkaline chemicals must be used in the neutralization treatment of the wastewater treatment. In particular, in order to separate into pulp fibers, super absorbent polymers, and other materials, it is better that the size or specific gravity of the pulp fibers is relatively close to the size or specific gravity of the super absorbent polymer. Therefore, in terms of the pH of the acidic aqueous solution, by setting it to be 1.0 or more and 4.0 or less, the super absorbent polymer can be made smaller by inactivation, thereby making the size or specific gravity of the pulp fiber more and more water absorbent. The size or specific gravity of the sex polymers are relatively close to each other. Examples of organic acids include citric acid, tartaric acid, glycolic acid, malic acid, succinic acid, acetic acid, ascorbic acid, and the like. Hydroxycarbonate organic acids such as citric acid, tartaric acid, and gluconic acid are particularly preferred. Due to the chelating effect of citric acid, metal ions in the excrement are captured and can be removed, and due to the cleaning effect of citric acid, a higher effect of removing contaminants can be expected. On the other hand, in terms of inorganic acids, for example, sulfuric acid, hydrochloric acid, and nitric acid are listed, but from the viewpoint of not containing chlorine or cost, sulfuric acid is preferred. The pH changes according to the water temperature. Therefore, the pH in the present invention refers to the pH measured at the temperature of the aqueous solution at 20°C. The organic acid concentration of the organic acid aqueous solution is not particularly limited. If the organic acid is citric acid, it is preferably 0.5% by mass or more and 4% by mass or less. The inorganic acid concentration of the inorganic acid aqueous solution is not particularly limited, and if the inorganic acid is sulfuric acid, it is preferably 0.1% by mass or more and 0.5% by mass or less.
例如在圖2的破袋裝置11中,首先,藉由攪拌葉片33繞著旋轉軸(支持軸32)旋轉,在酸性水溶液B產生旋流,收集袋A物理性且強制性地朝向酸性水溶液B(溶液槽V)的底部方向被引入。接著,移動至底部的收集袋A藉由破袋刃41繞著旋轉軸(支持軸42)旋轉,接觸破袋刃41而開孔。其中,若破袋刃41可在溶液槽V中以上下方向移動,即使收集袋A未以旋流而朝向酸性水溶液B(溶液槽V)的底部方向被引入,破袋刃41亦朝向上方移動而在收集袋A開孔。For example, in the
破碎工程S12係藉由破碎裝置12來執行。一邊包含開孔而沈入至酸性水溶液B的水面下的收集袋A的酸性水溶液B,亦即混合液91由溶液槽V被排出,一邊收集袋A內的使用完畢的吸收性物品連同收集袋A一起在酸性水溶液B中被破碎。
例如,在圖2的破碎裝置12中,首先,藉由破碎部60,由溶液槽V連同酸性水溶液B一起被送出的收集袋A內的使用完畢的吸收性物品連同收集袋A一起在酸性水溶液B中被破碎(液中破碎工程)。此時,在破碎部60中,對雙軸破碎機中彼此相咬合而朝內旋轉的旋轉刃及間隔件被供給混合液91,且收集袋A連同袋子一起被破碎。接著,藉由泵63,包含在破碎部60(液中破碎工程)所得的破碎物的酸性水溶液B(混合液92)由破碎部60被引出(引出工程),且被送至下一工程。The crushing process S12 is executed by the crushing
在此,在破碎工程S12中,較佳為具有以破碎物的大小的平均值成為50mm以上、100mm以下的方式,使用完畢的吸收性物品連同收集袋A一起被破碎的工程。以吸收性物品而言,假想長度約150~1000mm、寬度100mm~1000mm。藉由將破碎物的大小的平均值成為50mm以上、100mm以下的方式進行破碎,可在各使用完畢的吸收性物品的背面薄片及/或表面薄片確實地放入切斷處。藉此,在各使用完畢的吸收性物品,可由切斷處大概不會殘留而取出紙漿纖維,因此可提高紙漿纖維的回收率(所再生的紙漿纖維的總量/所被供給的使用完畢的吸收性物品的紙漿纖維的總量)。若將大小的平均值形成為未達50mm,紙漿纖維以外的其他資材(例示:薄膜(收集袋A的素材、背面薄片等)、不織布(表面薄片等)、彈性體(防漏壁用橡膠等))被切斷太小,在後續的工程中,難以將該等資材與紙漿纖維分離。結果,混入至所再生的紙漿纖維的異物(其他資材)增加,紙漿纖維的回收率降低。另一方面,若將大小的平均值形成為大於100mm,在使用完畢的吸收性物品難以放入切斷處。結果,產生無法使紙漿纖維取出的使用完畢的吸收性物品,紙漿纖維的回收率降低。Here, in the crushing process S12, it is preferable to have a process in which the used absorbent article is crushed together with the collection bag A so that the average value of the size of the crushed material becomes 50 mm or more and 100 mm or less. In the case of absorbent articles, the imaginary length is approximately 150-1000 mm and the width is 100-1000 mm. By crushing so that the average size of the crushed material becomes 50 mm or more and 100 mm or less, the back sheet and/or surface sheet of each used absorbent article can be reliably inserted into the cut portion. In this way, in each used absorbent article, the pulp fiber can be taken out from the cut portion without remaining, so the recovery rate of the pulp fiber can be improved (the total amount of recycled pulp fiber/used used The total amount of pulp fibers of the absorbent article). If the average size is less than 50mm, materials other than pulp fiber (example: film (material of collection bag A, back sheet, etc.), non-woven fabric (surface sheet, etc.), elastomer (rubber for leak-proof wall, etc.) )) The cut is too small, and it is difficult to separate these materials from the pulp fibers in subsequent projects. As a result, foreign matter (other materials) mixed into the recycled pulp fiber increases, and the recovery rate of the pulp fiber decreases. On the other hand, if the average value of the size is greater than 100 mm, it is difficult to put the used absorbent article into the cut portion. As a result, a used absorbent article in which the pulp fiber cannot be taken out is produced, and the recovery rate of the pulp fiber is reduced.
第1分離工程S13係藉由第1分離裝置13來執行。一邊攪拌包含在破碎裝置12所得的破碎物與酸性水溶液的混合液92而進行由破碎物去除髒污的洗淨,一邊混合液92被分離成紙漿纖維、高吸水性聚合物及酸性水溶液與其他資材。此時,為提高洗淨效果,及/或為調整pH,亦可另外添加酸性水溶液。結果,混合液92之中的紙漿纖維、高吸水性聚合物及酸性水溶液(一部分包含其他資材等)通過貫穿孔而被分離,由第1分離裝置13被送出(混合液93)。另一方面,除了混合液92之中的紙漿纖維、高吸水性聚合物及酸性水溶液之外的其他資材無法通過貫穿孔而殘留在第1分離裝置13內、或以其他路徑被送出。其中,其他資材的一部分未完全分離,而連同混合液93一起被送出。在此,使用洗衣機作為第1分離裝置13時,以作為篩來發揮功能的洗衣槽的貫穿孔大小而言,若為圓孔,列舉5mm~20mmφ,若為除此之外的形狀的孔,列舉與圓孔為大致相同面積的大小。The first separation process S13 is executed by the
本方法(系統)係在如上所述將使用完畢的吸收性物品進行破碎的破碎處理(開孔工程S11(破袋裝置11)~第1分離工程S13(第1分離裝置13))中,至少具備有:開孔工程S11(破袋裝置11)、破碎工程S12(破碎裝置12)。因此,由於將已放入收集袋的狀態的使用完畢的吸收性物品連同收集袋一起在不活性化水溶液中破碎,因此至少至開始破碎為止,幾乎不會有在不活性化水溶液混入髒污或菌類、或產生臭氣的情形。接著,使用完畢的吸收性物品被破碎時,即使在不活性化水溶液混入髒污或菌類、或產生臭氣,亦與破碎大致同時,已混入髒污或菌類的不活性化水溶液連同破碎物一起由溶液槽被送出,因此髒污或菌類幾乎不會殘留在溶液槽而可沖走。此外,可以不活性化水溶液密封臭氣,因此臭氣的發生亦被抑制為較低。藉此,使用完畢的吸收性物品破碎時,可抑制髒污或菌類飛散、或臭氣被放出的情形。This method (system) is used in the crushing process (opening process S11 (bag breaking device 11) to the first separation process S13 (first separation device 13)) for crushing the used absorbent article as described above, at least Equipped with: hole-opening process S11 (bag breaking device 11), crushing process S12 (crushing device 12). Therefore, since the used absorbent article in the state of being put into the collection bag is broken in the inactivation aqueous solution together with the collection bag, at least until the beginning of the breakage, there is almost no contamination or contamination in the inactivation aqueous solution. Fungus, or a situation that produces odor. Next, when the used absorbent article is broken, even if the inactivated aqueous solution is mixed with dirt or fungus, or produces odor, it is roughly at the same time as the broken, and the inactivated aqueous solution that has mixed with dirt or fungus is together with the broken material. It is sent out from the solution tank, so dirt or fungi hardly remain in the solution tank and can be washed away. In addition, the aqueous solution may not be activated to seal off odors, so the occurrence of odors is also suppressed to a low level. Thereby, when the used absorbent article is broken, it is possible to prevent dirt, fungus flying, or odor from being released.
其中,亦可在不活性化水溶液(例示:酸性水溶液)中,不連同收集袋一起將使用完畢的吸收性物品破碎,而在氣體中(例示:空氣中),連同收集袋一起將使用完畢的吸收性物品破碎。在該情形下,並不需要開孔工程S11,在無不活性化水溶液的狀態的空氣中,破碎工程S12係進行破碎。之後,連同破碎工程S12的破碎物一起將不活性化水溶液供給至第1分離工程S13。Among them, it is also possible to break the used absorbent article in an inactivated aqueous solution (example: acidic aqueous solution) without the collection bag, and in the gas (example: air), the used absorbent article together with the collection bag The absorbent article shattered. In this case, the hole-opening process S11 is not required, and the crushing process S12 performs crushing in the air without the inactivated aqueous solution. After that, the inactivated aqueous solution is supplied to the first separation step S13 together with the crushed material in the crushing step S12.
其中,在開孔工程S11~第1分離工程S13之間,若不使用酸性水溶液作為不活性化水溶液,較佳為由第1除塵工程S14添加酸性水溶液,將第1除塵工程S14所供給之包含紙漿纖維及高吸水性聚合物的不活性化水溶液實質上形成為酸性水溶液。此時,可以pH來輕易調整高吸水性聚合物的比重及大小。Among them, between the hole opening process S11 to the first separation process S13, if an acidic aqueous solution is not used as the inactivation aqueous solution, it is preferable to add the acidic aqueous solution from the first dust removal process S14, and include the supply of the first dust removal process S14 The inactivated aqueous solution of pulp fiber and super absorbent polymer is substantially formed as an acidic aqueous solution. At this time, the specific gravity and size of the super absorbent polymer can be easily adjusted by pH.
第1除塵工程S14係藉由第1除塵裝置14來執行。由第1分離裝置13被送出之包含紙漿纖維及高吸水性聚合物的酸性水溶液,亦即混合液93係一邊在預定的範圍內維持pH,一邊藉由篩,被分離成包含紙漿纖維及高吸水性聚合物的酸性水溶液、與其他資材(異物)。結果,混合液93之中的紙漿纖維、高吸水性聚合物及酸性水溶液(一部分包含其他資材等)通過篩而被分離,且由第1除塵裝置14被送出(混合液94)。另一方面,除了混合液93之中的紙漿纖維、高吸水性聚合物及酸性水溶液之外的其他資材無法通過篩而殘留在第1除塵裝置14內、或以其他路徑被送出。其中,其他資材的一部分未完全分離而連同混合液94一起被送出。The first dust removal process S14 is executed by the first
其中,酸性水溶液係以至少至第1除塵工程S14為止,以高吸水性聚合物的比重及大小與各個紙漿纖維的比重及大小的相異在預定的範圍內的方式調整pH為佳。預定的範圍內係指例如其中一方為另一方的0.2~5倍的範圍內。此時,第1除塵工程S14之前的工程係可看作將紙漿纖維及高吸水性聚合物、及以高吸水性聚合物的比重及大小與各個紙漿纖維的比重及大小的相異在預定的範圍內的方式調整pH後的酸性水溶液相混合,而將高吸水性聚合物不活性化的不活性化工程。Among them, the acidic aqueous solution is preferably adjusted to pH at least until the first dust removal process S14, so that the specific gravity and size of the superabsorbent polymer and the specific gravity and size of each pulp fiber are different within a predetermined range. The predetermined range means, for example, a range where one of them is 0.2 to 5 times the other. At this time, the engineering department before the first dust removal process S14 can be regarded as the difference between the specific gravity and size of the pulp fiber, super absorbent polymer, and the specific gravity and size of each pulp fiber in a predetermined An inactivation process in which the acidic aqueous solution after adjusting the pH in a manner within the range is mixed to inactivate the super absorbent polymer.
此外,以將在第1除塵工程S14的酸性溶液中的紙漿纖維與高吸水性聚合物合併後的濃度而言,列舉例如0.1質量%以上、10質量%以下,以0.1質量%以上、5質量%以下為佳。此外,酸性溶液中的紙漿纖維與高吸水性聚合物的比係列舉例如50~90質量%:50~10質量%。In addition, in terms of the concentration after combining the pulp fiber and the super absorbent polymer in the acidic solution of the first dust removal process S14, for example, 0.1% by mass or more and 10% by mass or less, and 0.1% by mass or more and 5% by mass are listed. % Or less is better. In addition, examples of the ratio series of the pulp fiber to the super absorbent polymer in the acid solution are 50 to 90% by mass: 50 to 10% by mass.
第2除塵工程S15係藉由第2除塵裝置15來執行。由第1除塵裝置14被送出之包含紙漿纖維及高吸水性聚合物的酸性水溶液,亦即混合液94一邊在預定的範圍內維持pH,一邊藉由篩,被分離成包含紙漿纖維及高吸水性聚合物的酸性水溶液、與其他資材(異物)。結果,混合液94之中的紙漿纖維、高吸水性聚合物及酸性水溶液(一部分包含其他資材等)通過篩而被分離,且由第2除塵裝置15被送出(混合液95)。另一方面,除了混合液94之中的紙漿纖維、高吸水性聚合物及酸性水溶液之外的其他資材無法通過篩而殘留在第2除塵裝置15內、或以其他路徑被送出。其中,其他資材的一部分未完全分離而連同混合液95一起被送出。其中,酸性水溶液係以高吸水性聚合物的比重及大小與各個紙漿纖維的比重及大小的相異在預定的範圍內的方式調整pH。The second dust removal process S15 is executed by the second
第3除塵工程S16係藉由第3除塵裝置16來執行。由第2除塵裝置15被送出之包含紙漿纖維及高吸水性聚合物的酸性水溶液,亦即混合液95一邊在預定的範圍內維持pH,一邊在相反方向的圓錐框體內被離心分離,被分離成酸性水溶液中的紙漿纖維及高吸水性聚合物與其他資材(重量較大的異物)。結果,混合液95之中的紙漿纖維、高吸水性聚合物及酸性水溶液由第3除塵裝置16(旋風分離機)的上部被送出(混合液96)。另一方面,除了混合液95之中的紙漿纖維、高吸水性聚合物及酸性水溶液之外之如金屬般之較重的其他資材由第3除塵裝置16(旋風分離機)的下部被送出。其中,酸性水溶液係以高吸水性聚合物的比重及大小與各個紙漿纖維的比重及大小的相異在預定的範圍內的方式調整pH。The third dust removal process S16 is executed by the third
本方法(系統)係在如上所述去除異物(其他資材)的除塵處理(第1除塵工程S14(第1除塵裝置14)~第3除塵工程S16(第3除塵裝置16)中,至少具備有:第2除塵工程S15(第2除塵裝置15)、第3除塵工程S16(第3除塵裝置16))。因此,可將紙漿纖維及高吸水性聚合物,由除了紙漿纖維及高吸水性聚合物之外的使用完畢的吸收性物品的其他資材之中主要為樹脂材料,容易以大小分離(第2除塵工程S15(第2除塵裝置15)),由其他資材之中比重大的材料,例如金屬材料,容易以比重分離(第3除塵工程S16(第3除塵裝置16))。接著,之後,將紙漿纖維與高吸水性聚合物彼此分離(第2、3分離工程S17、S18(第2、3分離裝置17、18),藉此可從使用完畢的吸收性物品回收紙漿纖維及高吸水性聚合物。此時,可減低將紙漿纖維及高吸水性聚合物與其他資材分離的處理次數。亦即,可提高將高吸水性聚合物及紙漿纖維分離的處理效率。This method (system) is used in the dust removal process (the first dust removal process S14 (first dust removal device 14) to the third dust removal process S16 (third dust removal device 16) to remove foreign materials (other materials) as described above, and at least : The second dust removal process S15 (the second dust removal device 15), the third dust removal process S16 (the third dust removal device 16)). Therefore, the pulp fiber and super absorbent polymer can be separated from the pulp fiber and super absorbent polymer, and the other materials of the used absorbent article are mainly resin materials, which can be easily separated by size (Second Dust Removal). Process S15 (the second dust removal device 15)), among other materials, materials with a high specific gravity, such as metal materials, are easily separated by specific gravity (the third dust removal process S16 (third dust removal device 16)). Then, after that, the pulp fiber and super absorbent polymer are separated from each other (Second and Third Separation Process S17, S18 (Second and
第2分離工程S17係藉由第2分離裝置17來執行。由第3除塵裝置16被送出之包含紙漿纖維及高吸水性聚合物的前述酸性水溶液,亦即混合液96,藉由圓筒篩,被分離成酸性水溶液中的紙漿纖維與酸性水溶液中的高吸水性聚合物。結果,包含高吸水性聚合物的酸性水溶液通過圓筒篩而由混合液96被分離,且由第2分離裝置17被送出。另一方面,混合液96之中包含紙漿纖維的酸性水溶液無法通過圓筒篩而由第2分離裝置17以其他路徑被送出(混合液97)。其中,之後,可由經分離的高吸水性聚合物及酸性水溶液,將高吸水性聚合物以篩分離機等分離。因此,以上工程係將高吸水性聚合物進行分離/回收的工程,因此可稱為生成再回收高吸水性聚合物的工程。The second separation process S17 is executed by the
第3分離工程S18係藉由第3分離裝置18來執行。由第2分離裝置17被送出之紙漿纖維、無法分離而殘留下來的高吸水性聚合物及酸性水溶液,亦即混合液97,藉由圓筒篩,被分離成包含紙漿纖維及高吸水性聚合物的固體,亦即混合物98、及包含高吸水性聚合物及酸性水溶液的液體E。接著,連同分離,固體中的高吸水性聚合物被加壓而被壓碎。結果,包含高吸水性聚合物的酸性水溶液通過圓筒篩而由混合液97被分離,且由第3分離裝置18被送出。另一方面,混合液97之中的高吸水性聚合物被壓碎的紙漿纖維無法追加圓筒篩,而由圓筒篩前端部的蓋體的間隙被送出至第3分離裝置18的外側(混合物98)。The third separation process S18 is executed by the
例如,在圖3所示之第3分離裝置18中,首先,由第2分離裝置17被送出之包含紙漿纖維、高吸水性聚合物及酸性水溶液的混合液97被投入至圓筒篩81內,而到達螺旋軸82的周圍。藉由驅動裝置86,螺旋軸82進行旋轉,螺旋軸82的周圍的混合液97一邊藉由螺旋軸82及螺旋葉片83被按壓在圓筒篩81的側面而被加壓,一邊朝向圓筒篩81的前端部被搬送。此時,高吸水性聚合物及酸性水溶液通過圓筒篩81的側面的篩,藉此由混合液97被分離,紙漿纖維及一部分高吸水性聚合物殘留在圓筒篩81內。亦即,由混合液97被分離:包含紙漿纖維及高吸水性聚合物的固體亦即混合物98、及包含高吸水性聚合物及酸性水溶液的液體E。接著,混合物98係一邊被加壓,一邊從圓筒篩81的前端部、與以與混合物98的搬送方向為相反方向被加壓的蓋體84的間隙G被強制送出。在一邊被加壓一邊被搬送且送出的過程中,混合物98中的高吸水性聚合物被壓碎。另一方面,液體E係由框體80被送出。被施加於蓋體84的按壓的壓力係列舉例如0.01MPa以上、1MPa以下,以0.02MPa以上、0.5MPa以下為佳。若將壓力形成為未達0.02MPa,難以壓碎高吸水性聚合物,不太能縮短氧化劑處理的時間,若使壓力大於0.5MPa,雖然使高吸水性聚合物充分壓碎,但有損傷紙漿纖維之虞。For example, in the
氧化劑處理工程S19係藉由氧化劑處理裝置19來執行。由第3分離裝置18被送出的固體中的紙漿纖維及被壓碎的高吸水性聚合物以含有氧化劑的水溶液予以處理。藉此,高吸水性聚合物進行氧化分解而由紙漿纖維被去除。結果,原附著在混合物98的紙漿纖維(例示:殘留在紙漿纖維的表面)的高吸水性聚合物藉由含有氧化劑(例示:臭氧)的水溶液(處理液)進行氧化分解,而變化成可溶於水溶液的低分子量的有機物,藉此由紙漿纖維被去除。在此,高吸水性聚合物進行氧化分解,且變化成可溶於水溶液的低分子量的有機物的狀態係指高吸水性聚合物通過2mm的篩的狀態。藉此,可將紙漿纖維所包含的高吸水性聚合物等雜質去除,生成純度高的紙漿纖維,且可進行藉由氧化劑處理所為之紙漿纖維的殺菌、漂白及消臭。The oxidant treatment process S19 is executed by the
例如,在圖4所示之氧化劑處理裝置19中,包含在第3分離工程S18被分離出的紙漿纖維(殘留高吸水性聚合物)的混合物98係由設在處理槽123的上部的供給口122b被供給至處理液P中。處理液P係酸性水溶液(為了臭氧的失活抑制及高吸水性聚合物的不活性化),以比重而言,大概為1。因此,紙漿纖維係由處理液P的上部朝向下部沈積。另一方面,在臭氧發生裝置126所生成的含臭氧氣體Z係以臭氧混合裝置127而被混合在處理液P,透過配管136,由供給口122c被供給至處理槽123。含臭氧氣體Z係由處理槽123的下部的供給口122c附近,以微細氣泡的狀態(例示:微米氣泡或奈米氣泡)被連續放出至處理液P內。亦即,含臭氧氣體Z係由處理液P的下部朝向上部上升。接著,在處理液P內,由上部朝向下部沈積的紙漿纖維、及由下部朝向上部上升的含臭氧氣體Z一邊相對向前進一邊互相衝撞。接著,含臭氧氣體Z係以包入紙漿纖維的方式附著在紙漿纖維的表面。此時,含臭氧氣體Z中的臭氧與紙漿纖維中的高吸水性聚合物起反應,使高吸水性聚合物氧化分解而溶解於處理液P。藉此,紙漿纖維上的高吸水性聚合物由紙漿纖維被去除。由於為對向流,因此可提高紙漿纖維所包含的高吸水性聚合物與含臭氧氣體Z的接觸機率。
接著,紙漿纖維係沈積至處理槽123的底部,含臭氧氣體Z係逸逃至處理槽123的上部的空間。蓄積在處理槽123的上部的含臭氧氣體Z的臭氧係在臭氧分解裝置129被分解且被無害化而被放出至外部。之後,處理槽123的底部的處理液P(包含紙漿纖維)係藉由泵121,透過配管132,由被設在處理槽123的上部的供給口122a被供給至處理槽123中。藉此,處理液P的紙漿纖維係再次由處理液P的上部朝向下部沈積,且可與再次由下部朝向上部上升的含臭氧氣體Z起反應。如上所示包含以含臭氧氣體Z予以處理的紙漿纖維的處理液P由處理槽123的下部(底部)再次被供給至處理槽123的上部,藉此可使處理槽123內強制性產生由上部朝向下部的連續且安定的流體(包含紙漿纖維)的流動。可更加提高紙漿纖維所包含的高吸水性聚合物與含臭氧氣體Z的接觸機率。此外,紙漿纖維反覆以含臭氧氣體Z予以處理,因此可將紙漿纖維所包含的高吸水性聚合物幾乎去除,可使紙漿纖維的純度極高。若使用圖4的氧化劑處理裝置19,氧化劑處理工程S19較佳為以批次處理進行。For example, in the
若對處理液P供給含臭氧氣體Z,處理液P中的臭氧濃度係列舉例如1~50質量ppm。含臭氧氣體Z中的臭氧濃度係列舉例如40~200g/m3
。處理液P中的紙漿纖維(包含高吸水性聚合物)的濃度係列舉例如0.1~20質量%。紙漿纖維存在於處理槽123內的時間係列舉例如2分鐘~60分鐘。含臭氧氣體Z係在微米氣泡(直徑為1~1000μm左右的氣泡)或奈米氣泡(直徑為100~1000nm左右的氣泡)的狀態下送出。亦即,微米氣泡或奈米氣泡係微細氣泡,平均單位體積的表面積大,而液中的上升速度慢,因此提高氣泡接觸到紙漿纖維的機率。此外,微細氣泡係可更多接觸紙漿纖維的表面。藉此,可沒有遺漏地以微細氣泡包入紙漿纖維,而使紙漿纖維與含臭氧氣體Z的接觸面積更加增加。此外,因更多氣泡接觸紙漿表面,由此因氣泡的浮力,可使包含高吸水性聚合物的紙漿纖維的沈積速度降低,且使紙漿纖維與含臭氧氣體Z的接觸時間更為增加。藉由該等,可使紙漿纖維所包含的高吸水性聚合物更加確實地氧化分解,而由紙漿纖維去除。If the ozone-containing gas Z is supplied to the treatment liquid P, the ozone concentration series in the treatment liquid P is, for example, 1 to 50 mass ppm. Examples of the ozone concentration series in the ozone-containing gas Z are 40 to 200 g/m 3 . The concentration series of the pulp fibers (including the super absorbent polymer) in the treatment liquid P is, for example, 0.1 to 20% by mass. The time series during which the pulp fiber exists in the
在圖5所示之氧化劑處理裝置19中,在第3分離工程S18被分離出的紙漿纖維(殘留高吸水性聚合物)係與酸性水溶液混合而成為處理液Pa。處理液Pa係透過配管131而被供給至混合液槽112且貯藏。接著,混合液槽112內的處理液Pa係藉由泵121a的流量控制,透過配管132a,以第1流量被連續供給至處理槽123。藉此,紙漿纖維係由被設在處理槽123的上部的供給口122,被供給至處理液P中。處理液P係酸性水溶液,以比重而言,大概為1。因此,紙漿纖維係由處理液P的上部朝向下部沈積。另一方面,在臭氧發生裝置126所生成的含臭氧氣體Z係透過配管135而被供給至處理槽123,由處理槽123的噴嘴127a,在微細氣泡的狀態(例示:微米氣泡或奈米氣泡)下被連續放出至處理液P內。亦即,含臭氧氣體Z係由處理液P的下部朝向上部上升。接著,在處理液P內,由上部朝向下部沈積的紙漿纖維、與由下部朝向上部上升的含臭氧氣體Z一邊相對向前進一邊互相衝撞。接著,含臭氧氣體Z係以包入紙漿纖維的方式附著在紙漿纖維的表面。此時,含臭氧氣體Z中的臭氧與紙漿纖維中的高吸水性聚合物起反應,使高吸水性聚合物氧化分解而溶解於處理液P。藉此,紙漿纖維上的高吸水性聚合物由紙漿纖維被去除。由於為對向流,因此可提高紙漿纖維所包含的高吸水性聚合物與含臭氧氣體Z的接觸機率。接著,紙漿纖維係沈積至處理槽123的底部,含臭氧氣體Z係朝向處理槽123的上部的空間逸逃。之後,處理槽123的底部的處理液P(包含紙漿纖維)係藉由泵125a的流量控制,透過配管133,由處理槽123的排出口124以第2流量被連續排出至處理槽123之外。蓄積在處理槽123的上部的含臭氧氣體Z的臭氧係在臭氧分解裝置129被分解且無害化而被放出至外部。如上所示,處理液Pa由處理槽123的上部以第1流量被連續供給至處理槽123之中,處理液P由處理槽123的下部(底部)以第2流量被連續排出至處理槽123之外。藉此,可使處理槽123內強制性地發生由上部朝向下部的連續且安定的流體(包含紙漿纖維)的流動。可提高紙漿纖維所包含的高吸水性聚合物與含臭氧氣體Z的接觸機率。若使用圖5的氧化劑處理裝置19,氧化劑處理工程S19較佳為以連續處理來進行。In the
但是,若氧化劑為臭氧,藉由將處理液形成為酸性水溶液,可抑制臭氧的失活,且可提高臭氧的效果(高吸水性聚合物的氧化分解、殺菌、漂白、消臭)。此外,除了可將高吸水性聚合物不活性化之外,若在破碎處理或除塵處理中使用酸性水溶液,由於在各處理間具有連續性,因此不會有在各處理間因水溶液不同而產生任何不良情形之虞,可安定且確實地進行處理。此外,由減低因酸所致之對作業者或裝置的影響的觀點來看,以酸性水溶液之中的有機酸為佳,其中由金屬去除的觀點來看,亦以檸檬酸為佳。However, if the oxidizing agent is ozone, by forming the treatment liquid into an acidic aqueous solution, the deactivation of ozone can be suppressed, and the effect of ozone can be improved (oxidative decomposition of super absorbent polymer, sterilization, bleaching, and deodorization). In addition, in addition to inactivating the super absorbent polymer, if an acidic aqueous solution is used in the crushing treatment or dust removal treatment, due to the continuity between the treatments, there will be no difference in the aqueous solution between the treatments. Any unfavorable situation can be dealt with in a stable and reliable manner. In addition, from the viewpoint of reducing the impact on the operator or equipment caused by the acid, the organic acid in the acidic aqueous solution is preferred, and the citric acid is also preferred from the viewpoint of metal removal.
在此,第1流量與第2流量較佳為相同。藉由將第1流量與第2流量形成為相同,可將處理槽123內的處理液P的量保持為一定,可進行安定且連續的處理。其中,第1流量與第2流量並非必須常時完全相同,若經時性平均而為大致相同(誤差5%以內)即可。Here, the first flow rate and the second flow rate are preferably the same. By making the first flow rate and the second flow rate the same, the amount of the treatment liquid P in the
第4分離工程S20係藉由第4分離裝置20來執行,在氧化劑處理裝置19所被處理之包含紙漿纖維的處理液,亦即混合液99通過具有複數開口的篩,而由混合液99被分離紙漿纖維與處理液。結果,處理液104通過篩而由混合液99被分離,且由第4分離裝置20被送出。所被分離出的處理液104,亦即氧化劑處理液亦可送回至氧化劑處理裝置19而再利用。可削減氧化劑處理液的成本。另一方面,混合液99之中的紙漿纖維無法通過篩而殘留在第4分離裝置20、或以其他路徑被送出。以上工程係將紙漿纖維進行分離/回收的工程,因此可稱為生成再回收紙漿纖維的工程。The fourth separation process S20 is performed by the
其中,高吸水性聚合物的比重係以JIS K 0061的化學製品的密度及比重測定方法的比重瓶法進行測定。結果,吸水前的吸水性聚合物的比重為1.32g/ml。以檸檬酸水溶液(pH2)不活性化時的比重為1.04g/ml,檸檬酸水溶液(pH4)不活性化時的比重為1.01g/ml。 另一方面,高吸水性聚合物(吸水後)的大小難以實測,因此假定高吸水性聚合物為球,如以下所示算出其大小(直徑)。亦即,將高吸水性聚合物的吸水前的平均直徑設為200μm,由高吸水性聚合物所吸水的水溶液中的水的量,藉由體積膨脹計算,推定出高吸水性聚合物的吸水後的大小(直徑)。在此,體積膨脹計算係進行如下。首先,計測出高吸水性聚合物所吸水的水的量(平均每粒)。接著,將相當於該水的量的水的體積假定為吸水後的高吸水性聚合物的體積V,根據V=4/3πr3 ,求出吸水後的高吸水性聚合物的半徑r。接著,將半徑r的2倍的直徑設為高吸水性聚合物(吸水後)的大小。結果,以檸檬酸水溶液(pH2)不活性化時的凝膠直徑係約420μm,以檸檬酸水溶液(pH4)不活性化時的凝膠直徑係約540μm。Among them, the specific gravity of the super absorbent polymer is measured by the pycnometer method of JIS K 0061 for the density and specific gravity of chemical products. As a result, the specific gravity of the water-absorbing polymer before water absorption was 1.32 g/ml. The specific gravity when the citric acid aqueous solution (pH 2) is inactivated is 1.04 g/ml, and the specific gravity when the citric acid aqueous solution (pH 4) is inactivated is 1.01 g/ml. On the other hand, it is difficult to measure the size of the super absorbent polymer (after water absorption). Therefore, assuming that the super absorbent polymer is a ball, the size (diameter) is calculated as shown below. That is, the average diameter of the super absorbent polymer before water absorption is set to 200 μm, and the amount of water in the aqueous solution absorbed by the super absorbent polymer is calculated by volume expansion to estimate the water absorption of the super absorbent polymer The size (diameter) of the back. Here, the volume expansion calculation system is performed as follows. First, the amount of water absorbed by the super absorbent polymer (average per grain) is measured. Next, the volume of water corresponding to this amount of water is assumed to be the volume V of the super absorbent polymer after water absorption, and the radius r of the super absorbent polymer after water absorption is obtained from V=4/3πr 3. Next, the diameter twice the radius r is set to the size of the super absorbent polymer (after water absorption). As a result, the gel diameter when inactivated with a citric acid aqueous solution (pH 2) was about 420 μm, and the gel diameter when inactivated with a citric acid aqueous solution (pH 4) was about 540 μm.
其中,酸性水溶液中的紙漿纖維及高吸水性聚合物的比例係如下進行測定。首先,採取酸性水溶液的一部分作為試料,將該試料放入至200網孔的過濾器來測定試料重量W0。接著,懸吊過濾器上的試料5分鐘來去除水份,以預定的絕對乾燥方法(以120℃加熱10分鐘,且使其乾燥的方法)進行絕對乾燥,測定出所得的絕對乾燥物的絕對乾燥重量W1。接著,將絕對乾燥物浸漬在含有臭氧的水溶液中,將所得者以上述之絕對乾燥方法進行絕對乾燥,形成為紙漿纖維而測定出絕對乾燥重量W2。接著,將由絕對乾燥重量W1減掉絕對乾燥重量W2後的重量作為高吸水性聚合物的重量,以下式計算出酸性水溶液中的紙漿纖維及高吸水性聚合物的比例。亦即,形成為(紙漿纖維的比例)=(絕對乾燥重量W2)/(試料重量W0),且形成為(高吸水性聚合物的比例)=(絕對乾燥重量W1-絕對乾燥重量W2)/(試料重量W0)。在重量比例上,污物的固形重量極小,故可忽略。Here, the ratio of the pulp fiber and the super absorbent polymer in the acidic aqueous solution is measured as follows. First, a part of the acidic aqueous solution was taken as a sample, and the sample was put in a 200-mesh filter to measure the sample weight W0. Next, the sample on the filter was suspended for 5 minutes to remove water, and the absolute drying was performed by a predetermined absolute drying method (heating at 120°C for 10 minutes and drying), and the absolute of the obtained absolute dried product was measured. Dry weight W1. Next, the absolutely dried product is immersed in an ozone-containing aqueous solution, and the resultant is absolutely dried by the above-mentioned absolute drying method to form a pulp fiber, and the absolute dry weight W2 is measured. Next, the weight obtained by subtracting the absolute dry weight W2 from the absolute dry weight W1 is taken as the weight of the super absorbent polymer, and the ratio of the pulp fiber and the super absorbent polymer in the acidic aqueous solution is calculated by the following formula. That is, it is formed as (proportion of pulp fiber)=(absolute dry weight W2)/(sample weight W0), and is formed as (proportion of super absorbent polymer)=(absolute dry weight W1-absolute dry weight W2)/ (Sample weight W0). In terms of weight ratio, the solid weight of the dirt is extremely small, so it can be ignored.
但是,水溶液中的臭氧濃度係如下進行測定。首先,在已放入碘化鉀約0.15g與10%的檸檬酸溶液5mL的100mL量筒,放入臭氧經溶解的水溶液85mL。反應後,移至200mL的三角燒瓶。在該處添加澱粉溶液,使其著上紫色後,一邊以0.01mol/L硫代硫酸鈉攪拌至形成為無色為止一邊進行滴定。由滴定值,使用下式,算出水溶液中的臭氧的濃度。水溶液中的臭氧的濃度(質量ppm)=滴定所需0.01mol/L硫代硫酸鈉(mL)×0.24×0.85(mL)However, the ozone concentration in the aqueous solution is measured as follows. First, in a 100 mL graduated cylinder into which about 0.15 g of potassium iodide and 5 mL of a 10% citric acid solution have been placed, 85 mL of an ozone-dissolved aqueous solution is placed. After the reaction, it was transferred to a 200 mL Erlenmeyer flask. After adding the starch solution to this place to make it purple, it was titrated while stirring with 0.01 mol/L sodium thiosulfate until it became colorless. From the titration value, the following formula is used to calculate the concentration of ozone in the aqueous solution. The concentration of ozone in the aqueous solution (mass ppm) = 0.01mol/L sodium thiosulfate (mL) × 0.24 × 0.85 (mL) required for titration
其中,該方法較佳為具備有:臭氧處理工程S22、及pH調整工程S23。該等工程係用以將在該方法中所使用的酸性水溶液再生且再利用的工程。藉由酸性水溶液的再利用,可削減酸性水溶液的成本。臭氧處理工程S22係將在第2分離工程S17中被分離出的高吸水性聚合物及由酸性水溶液另外分離出高吸水性聚合物之後的酸性水溶液101,以含臭氧水溶液進行殺菌處理。pH調整工程S23係調整以含臭氧水溶液經殺菌處理的酸性水溶液的pH,生成所再生的酸性水溶液103。酸性水溶液103係例如被供給至破碎裝置11。或者,若無開孔工程S11,而在破碎工程S12中未使用不活性化水溶液來進行破碎時,係被供給至第1分離工程S13。或者,亦可視需要,酸性水溶液被供給至所需的其他工程(裝置)。酸性水溶液103的剩餘份係被貯留在貯水槽24。Among them, the method preferably includes ozone treatment process S22 and pH adjustment process S23. These processes are processes for regenerating and reusing the acidic aqueous solution used in the method. By reusing the acidic aqueous solution, the cost of the acidic aqueous solution can be reduced. In the ozone treatment process S22, the super absorbent polymer separated in the second separation process S17 and the acid
從上述之包含紙漿纖維及高吸水性聚合物的使用完畢的吸收性物品回收紙漿纖維的方法係在回收紙漿纖維等的回收處理(第2分離工程S17(第2分離裝置17)~第4分離工程S20(第4分離裝置20))中,至少具備有:固液分離工程(固液分離裝置),亦即第3分離工程S18(第3分離裝置18);及氧化劑處理工程S19(氧化劑處理裝置19)。接著,在第3分離工程S18(第3分離裝置18)中,藉由將殘留在紙漿纖維之經吸水的凝膠狀(塊狀或大致球狀)的高吸水性聚合物壓碎,使高吸水性聚合物的厚度變薄,而形成為平坦的形狀或微細分裂的形狀。壓碎係例示以凝膠強度以上的壓力弄碎凝膠狀的高吸水性聚合物。亦即,本方法或系統係藉由大致球狀或塊狀的高吸水性聚合物的壓碎,可將高吸水性聚合物的表面積擴展較大,可增加使高吸水性聚合物的內側的部分露出於表側等露出的部分。因此,在氧化劑處理工程S19(氧化劑處理裝置19)中,若為塊狀或大致球狀的高吸水性聚合物,可使原難以與氧化劑相接觸的高吸水性聚合物的內側的部分接觸氧化劑等,可加大高吸水性聚合物中與氧化劑的接觸面積。藉此,可更有效率地進展高吸水性聚合物的氧化分解,且可縮短氧化劑處理的時間。因此,可提高從紙漿纖維去除高吸水性聚合物的處理效率。The method of recovering pulp fibers from the used absorbent articles containing pulp fibers and superabsorbent polymers mentioned above is in the recycling process of recycled pulp fibers (Second Separation Process S17 (Second Separation Device 17) to Fourth Separation Process S20 (fourth separation device 20)) includes at least: solid-liquid separation process (solid-liquid separation device), that is, the third separation process S18 (third separation device 18); and oxidant treatment process S19 (oxidant treatment) Device 19). Next, in the third separation process S18 (third separation device 18), the water-absorbent gel-like (lumpy or roughly spherical) superabsorbent polymer remaining in the pulp fibers is crushed to make high The thickness of the water-absorbing polymer becomes thin, and it is formed into a flat shape or a finely divided shape. The crushing system exemplifies the crushing of a gel-like super absorbent polymer under a pressure higher than the gel strength. That is, this method or system can expand the surface area of the superabsorbent polymer by crushing the roughly spherical or massive superabsorbent polymer, and can increase the inner surface of the superabsorbent polymer. Partially exposed on exposed parts such as the front side. Therefore, in the oxidant treatment process S19 (oxidant treatment device 19), if it is a block or roughly spherical super absorbent polymer, the inner part of the super absorbent polymer that is difficult to come into contact with the oxidant can be brought into contact with the oxidant. And so on, can increase the contact area of the super absorbent polymer with the oxidant. Thereby, the oxidative decomposition of the super absorbent polymer can be progressed more efficiently, and the time for the oxidizing agent treatment can be shortened. Therefore, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved.
以實施形態中之較佳態樣而言,第3分離工程S18(第3分離裝置18)亦可包含有:將包含紙漿纖維及高吸水性聚合物的不活性化水溶液(例示:酸性水溶液),以加壓式脫水法進行處理,且將殘留在前述紙漿纖維的前述高吸水性聚合物進行壓碎的壓碎工程(螺旋壓榨式脫水機)。 本方法或系統係藉由加壓式脫水法,將殘留在紙漿纖維的高吸水性聚合物壓碎,因此可同時有效率且確實地執行固液分離、及紙漿纖維上的高吸水性聚合物的壓碎。亦即,可有效率且確實地將紙漿纖維上的高吸水性聚合物的表面積擴展較大。藉此,可提高從紙漿纖維去除高吸水性聚合物的處理效率。In the preferred aspect of the embodiment, the third separation process S18 (third separation device 18) may also include: an inactivated aqueous solution containing pulp fibers and super absorbent polymers (example: acidic aqueous solution) A crushing process (screw press dehydrator) in which the superabsorbent polymer remaining in the pulp fiber is crushed by the pressurized dehydration method. This method or system crushes the superabsorbent polymer remaining in the pulp fiber by the pressurized dehydration method, so that the solid-liquid separation and the superabsorbent polymer on the pulp fiber can be efficiently and reliably performed at the same time Crushed. That is, the surface area of the super absorbent polymer on the pulp fiber can be expanded efficiently and surely. Thereby, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved.
以實施形態中之較佳態樣而言,第3分離工程S18的壓碎工程(螺旋壓榨式脫水機)中的加壓式脫水法的加壓時的壓力亦可為0.02MPa以上、0.5Pa以下。 在本方法或系統中,將加壓式脫水法的加壓時的壓力設為0.02MPa以上、0.5Pa以下。因此,不會損傷紙漿纖維,而可將殘留在紙漿纖維的高吸水性聚合物充分壓碎,因此可將高吸水性聚合物的表面積充分擴展較大。藉此,可提高從紙漿纖維去除高吸水性聚合物的處理效率。但是,若將壓力設為未達0.02MPa,無法將高吸水性聚合物充分壓碎,不太能縮短氧化劑處理的時間,若使壓力大於0.5MPa,雖然可將高吸水性聚合物充分壓碎,但是有損傷紙漿纖維之虞。In the preferred aspect of the embodiment, the pressure during the pressurization of the pressurized dehydration method in the crushing process (screw press dehydrator) of the third separation process S18 may be 0.02 MPa or more and 0.5 Pa. the following. In this method or system, the pressure during pressurization of the pressurized dehydration method is set to 0.02 MPa or more and 0.5 Pa or less. Therefore, the pulp fiber is not damaged, and the super absorbent polymer remaining in the pulp fiber can be sufficiently crushed, so the surface area of the super absorbent polymer can be sufficiently expanded. Thereby, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved. However, if the pressure is set to less than 0.02MPa, the super absorbent polymer cannot be crushed sufficiently, and the oxidant treatment time cannot be shortened. If the pressure is greater than 0.5 MPa, the super absorbent polymer can be crushed sufficiently. , But there is a risk of damaging the pulp fibers.
以實施形態中之較佳態樣而言,亦可在第3分離工程S18(第3分離裝置18)之前,另外具備有:由包含紙漿纖維與高吸水性聚合物的不活性化水溶液,將高吸水性聚合物及不活性化水溶液的一部分分離的工程,亦即第2分離工程S17(第2分離裝置17的圓筒篩式脫水機)。 本方法或系統係在第3分離工程S18(第3分離裝置18)之前,具備有第2分離工程S17(第2分離裝置17)的圓筒篩式脫水機。因此,本方法/系統係可將被供給至第3分離工程S18(第3分離裝置18)的材料(紙漿纖維、高吸水性聚合物及不活性化水溶液)中的高吸水性聚合物的比例抑制為較低。藉此,在第3分離工程S18(第3分離裝置18)中,可將附著在紙漿纖維的高吸水性聚合物更有效率地壓碎,且可提高從紙漿纖維去除高吸水性聚合物的處理效率。In the preferred aspect of the embodiment, before the third separation process S18 (third separation device 18), it is additionally equipped with: an inactivated aqueous solution containing pulp fibers and superabsorbent polymer The process of separating a part of the superabsorbent polymer and the inactivated aqueous solution, that is, the second separation process S17 (the cylindrical sieve dehydrator of the second separator 17). This method or system is a cylindrical screen dehydrator equipped with a second separation step S17 (second separation device 17) before the third separation step S18 (third separation device 18). Therefore, this method/system can reduce the proportion of super absorbent polymer in the materials (pulp fiber, super absorbent polymer, and inactivated aqueous solution) supplied to the third separation process S18 (third separation device 18) The suppression is low. Thereby, in the third separation process S18 (third separation device 18), the super absorbent polymer adhering to the pulp fiber can be crushed more efficiently, and the removal of the super absorbent polymer from the pulp fiber can be improved. Processing efficiency.
以實施形態中之較佳態樣而言,第3分離工程S18(第3分離裝置18)被供給的不活性化水溶液中的前述高吸水性聚合物的比例亦可為50%以下。 本方法或系統係在第3分離工程S18(第3分離裝置18)中,將成為分離對象的不活性化水溶液中的高吸水性聚合物的比例設為50%以下。藉此,由於不需要將過剩的量的高吸水性聚合物壓碎,因此可將高吸水性聚合物更確實且更有效率地壓碎。藉此,可提高從紙漿纖維去除高吸水性聚合物的處理效率。In a preferred aspect of the embodiment, the ratio of the super absorbent polymer in the inactivated aqueous solution supplied to the third separation step S18 (third separation device 18) may be 50% or less. In this method or system, in the third separation process S18 (third separation device 18), the ratio of the superabsorbent polymer in the inactivated aqueous solution to be separated is 50% or less. Thereby, since there is no need to crush an excessive amount of super absorbent polymer, the super absorbent polymer can be crushed more reliably and efficiently. Thereby, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved.
以實施形態中之較佳態樣而言,亦可在第3分離工程S18(第3分離裝置18)之前,另外具備有:將使用完畢的吸收性物品在不活性化水溶液中進行破碎的工程(包含S12);及由包含在進行破碎的工程(包含S12)中所得的破碎物的不活性化水溶液,將包含紙漿纖維與高吸水性聚合物的不活性化水溶液分離的工程(包含S13,較佳為包含S14~S16)。 本方法或系統係藉由進行破碎的工程及進行洗淨的分離工程,生成在第3分離工程S18(第3分離裝置18)中被供給之包含由使用完畢的吸收性物品被分離出的紙漿纖維與高吸水性聚合物的不活性化水溶液。藉由使用進行破碎的工程及進行分離的工程,可抑制在不活性化水溶液中混入異物(用後即棄吸收性物品的紙漿纖維及高吸水性聚合物以外的資材(例示:薄膜、不織布)、彈性體等)的情形。藉此,不會受到異物阻礙而可更加正確地壓碎高吸水性聚合物。結果,可提高從紙漿纖維去除高吸水性聚合物的處理效率。In the preferred aspect of the embodiment, before the third separation process S18 (third separation device 18), it is also possible to additionally include a process for crushing the used absorbent article in an inactivated aqueous solution. (Including S12); and the process of separating the inactivated aqueous solution containing pulp fibers and superabsorbent polymer from the inactivated aqueous solution containing the crushed product obtained in the process for crushing (including S12) (including S13, It preferably contains S14 to S16). This method or system generates pulp which is supplied in the third separation process S18 (third separation device 18) and contains the used absorbent articles separated by the crushing process and the cleaning separation process. An inactivated aqueous solution of fiber and super absorbent polymer. By using the process of crushing and the process of separating, it is possible to prevent foreign matter from being mixed in the inactivated aqueous solution (materials other than pulp fibers and super absorbent polymers of disposable absorbent articles (example: film, non-woven fabric) , Elastomers, etc.). Thereby, the super absorbent polymer can be crushed more accurately without being hindered by foreign matter. As a result, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved.
以實施形態中之較佳態樣而言,不活性化水溶液亦可為酸性水溶液。 在本方法或系統中,由於不活性化水溶液為酸性水溶液,因此可將使用完畢的吸收性物品中的高吸水性聚合物確實脫水,且形成為預定的大小(例示:粒徑)以下。藉此,可在第3分離工程S18(第3分離裝置18)中,輕易地一邊進行固液分離,一邊將高吸水性聚合物壓碎。結果,可提高從紙漿纖維去除高吸水性聚合物的處理效率。In the preferred aspect of the embodiment, the inactivated aqueous solution may also be an acidic aqueous solution. In this method or system, since the inactivation aqueous solution is an acidic aqueous solution, the superabsorbent polymer in the used absorbent article can be surely dehydrated and formed into a predetermined size (example: particle size) or less. Thereby, in the third separation process S18 (third separation device 18), the super absorbent polymer can be crushed easily while performing solid-liquid separation. As a result, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved.
以實施形態中之較佳態樣而言,酸性水溶液亦可為pH2.5以下。 在本方法或系統中,酸性水溶液為pH2.5以下,因此可將使用完畢的吸收性物品中的高吸水性聚合物更確實地脫水,且形成為預定的大小(例示:粒徑)以下。藉此,可在第3分離工程S18(第3分離裝置18)中,更輕易地一邊進行固液分離,一邊將高吸水性聚合物壓碎。結果,可提高從紙漿纖維去除高吸水性聚合物的處理效率。此外,由於將高吸水性聚合物在凝膠的狀態下形成為預定的大小以下,因此可將高吸水性聚合物輕易壓碎。In a preferred aspect of the embodiment, the acidic aqueous solution may also have a pH of 2.5 or less. In this method or system, the acidic aqueous solution has a pH of 2.5 or less, so that the superabsorbent polymer in the used absorbent article can be dehydrated more reliably and be formed to a predetermined size (example: particle size) or less. Thereby, in the third separation process S18 (third separation device 18), the super absorbent polymer can be crushed more easily while performing solid-liquid separation. As a result, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved. In addition, since the super absorbent polymer is formed into a predetermined size or less in the state of a gel, the super absorbent polymer can be easily crushed.
以實施形態中之較佳態樣而言,酸性水溶液亦可含有檸檬酸。 在本方法或系統中,酸性水溶液由於含有檸檬酸(例示:濃度0.5~2.0質量%),可將使用完畢的吸收性物品中的高吸水性聚合物確實脫水,而形成為預定粒徑以下。藉此,可在第3分離工程S18(第3分離裝置18)中,輕易地一邊進行固液分離,一邊將高吸水性聚合物壓碎。結果,可提高從紙漿纖維去除高吸水性聚合物的處理效率。 [實施例]In the preferred aspect of the embodiment, the acidic aqueous solution may also contain citric acid. In the present method or system, since the acidic aqueous solution contains citric acid (example: concentration 0.5-2.0% by mass), the superabsorbent polymer in the used absorbent article can be surely dehydrated and formed into a predetermined particle size or less. Thereby, in the third separation process S18 (third separation device 18), the super absorbent polymer can be crushed easily while performing solid-liquid separation. As a result, the treatment efficiency of removing the super absorbent polymer from the pulp fiber can be improved. [Example]
以下說明從上述之使用完畢的吸收性物品回收紙漿纖維的方法之實施例。Hereinafter, an example of a method of recovering pulp fibers from the above-mentioned used absorbent article will be described.
在本實施例中,對經粉碎且紙漿纖維及高吸水性聚合物以外的其他資材被去除後的吸收性物品,實施上述方法的第3分離工程S18與氧化劑處理工程S19。接著,調查在第3分離工程S18之加壓時所施加的壓力、與在氧化劑處理工程S19之氧化劑處理的處理時間的關係。具體而言,以吸收性物品而言,係使用以破碎工程S12~第2分離工程S17處理複數成人用的用後即棄紙尿褲(未使用)後的混合液97。在第3分離工程S18中,使以加壓脫水法之加壓時所施加的壓力(被施加於蓋體的壓力)變化為0~3.3kgf/cm2
(0~0.32MPa)。此時,計測在氧化劑處理工程S19中由紙漿纖維變得未檢測到高吸水性聚合物的時間作為處理時間。處理時間係在氧化劑處理工程S19中,每隔一定時間即取出預定量的紙漿纖維,檢測在紙漿纖維是否附著有高吸水性聚合物,將原變得未檢測到高吸水性聚合物的時間設為處理時間。In this embodiment, the third separation step S18 and the oxidizing agent treatment step S19 of the above-mentioned method are performed on the absorbent article after pulverization and removal of materials other than pulp fibers and superabsorbent polymers. Next, the relationship between the pressure applied during the pressurization of the third separation step S18 and the treatment time of the oxidant treatment in the oxidant treatment step S19 was investigated. Specifically, as an absorbent article, a
此外,高吸水性聚合物是否附著在紙漿纖維,係如下進行測定。 將紙漿纖維取出10g且除去水份後,一邊照射光一邊解開纖維,以倍率20倍的放大鏡,以目視進行確認是否有殘留聚合物的附著。若有殘留聚合物,光作反射而發光,因此可簡單發現。In addition, whether or not the super absorbent polymer adheres to the pulp fibers is measured as follows. After taking out 10 g of the pulp fiber and removing the moisture, the fiber was unwound while irradiating with light, and the adhesion of the residual polymer was visually confirmed with a magnifying glass with a magnification of 20 times. If there is residual polymer, the light is reflected and emits light, so it can be easily found.
將調查加壓時被施加的壓力與氧化劑處理的處理時間的關係後的結果顯示於圖7。圖7係顯示加壓時被施加的壓力與氧化劑處理的處理時間的關係的圖表。橫軸係被施加的壓力(kgf/cm2 )、縱軸係處理時間(分鐘)。 如圖所示,判明出以被施加的壓力為0kgf/cm2 時的處理時間40分鐘為基準,若被施加的壓力小,處理時間的減低效果小,但是被施加的壓力愈大,處理時間的減低效果愈大。此外,亦判明出在某壓力以上,處理時間的減低效果呈飽和。 因此,由處理時間降低的觀點來看,壓力以0.2kgf/cm2 (0.02MPa)以上為佳。此外,以減低效果的飽和或減低效果的確實性等觀點來看,壓力係以5kgf/cm2 (0.5MPa)以下為佳。壓力更佳為0.5kgf/cm2 (0.05MPa)以上、3kgf/cm2 (0.3MPa)。The result of investigating the relationship between the pressure applied during pressurization and the treatment time of the oxidant treatment is shown in FIG. 7. Fig. 7 is a graph showing the relationship between the pressure applied during pressurization and the treatment time of the oxidant treatment. The horizontal axis indicates the applied pressure (kgf/cm 2 ), and the vertical axis indicates the processing time (minutes). As shown in the figure, it is found that the treatment time is 40 minutes when the applied pressure is 0kgf/cm 2 as the standard. If the applied pressure is small, the reduction effect of the treatment time is small, but the greater the applied pressure, the treatment time The greater the reduction effect. In addition, it was also found that above a certain pressure, the treatment time reduction effect was saturated. Therefore, from the viewpoint of reducing the processing time, the pressure is preferably 0.2 kgf/cm 2 (0.02 MPa) or more. In addition, from the viewpoint of saturation of the reduction effect or the reliability of the reduction effect, the pressure is preferably 5 kgf/cm 2 (0.5 MPa) or less. The pressure is more preferably 0.5kgf/cm 2 (0.05MPa) or more and 3kgf/cm 2 (0.3MPa).
上述之實施形態係說明將背面薄片的構成構件形成為薄膜,將表面薄片的構成構件形成為不織布的情形。但是,關於將背面薄片的構成構件形成為不織布、且將表面薄片的構成構件形成為薄膜時、或將背面薄片及表面薄片之雙方的構成構件形成為薄膜時的實施形態,亦可以與上述實施形態相同的方法實現,且可達成相同的作用效果。The above-mentioned embodiment describes the case where the constituent member of the back sheet is formed as a film, and the constituent member of the front sheet is formed as a non-woven fabric. However, the embodiment in which the constituent members of the back sheet are formed as a non-woven fabric and the constituent members of the front sheet are formed as a film, or when the constituent members of both the back sheet and the front sheet are formed as films, can also be implemented as described above. The same method can achieve the same effect.
本發明之吸收性物品並非受限於上述各實施形態,可在未脫離本發明之目的、主旨之範圍內適當組合或變更等。The absorbent article of the present invention is not limited to the above-mentioned respective embodiments, and can be combined or changed appropriately without departing from the purpose and spirit of the present invention.
1‧‧‧系統 11‧‧‧破袋裝置 12‧‧‧破碎裝置 13‧‧‧第1分離裝置 14‧‧‧第1除塵裝置 15‧‧‧第2除塵裝置 16‧‧‧第3除塵裝置 17‧‧‧第2分離裝置 18‧‧‧第3分離裝置 19‧‧‧氧化劑處理裝置 20‧‧‧第4分離裝置 22‧‧‧臭氧處理裝置 23‧‧‧pH調整裝置 24‧‧‧貯水槽 30‧‧‧送入部 31‧‧‧驅動裝置 32‧‧‧支持軸(旋轉軸) 33‧‧‧攪拌葉片 40‧‧‧破袋部 41‧‧‧破袋刃 42‧‧‧支持軸(旋轉軸) 43‧‧‧驅動裝置 50‧‧‧開孔部 60‧‧‧破碎部 61‧‧‧配管 62‧‧‧配管 63‧‧‧泵 80‧‧‧框體 81‧‧‧圓筒篩 82‧‧‧螺旋軸 83‧‧‧螺旋葉片 84‧‧‧蓋體 85‧‧‧調壓裝置 86‧‧‧驅動裝置 91‧‧‧混合液 92‧‧‧混合液 93‧‧‧混合液 94‧‧‧混合液 95‧‧‧混合液 96‧‧‧混合液 97‧‧‧混合液 98‧‧‧混合物 99‧‧‧混合液 101‧‧‧酸性水溶液 102‧‧‧酸性水溶液 103‧‧‧酸性水溶液 104‧‧‧處理液 110‧‧‧混合液貯藏部 112‧‧‧混合液槽 113‧‧‧攪拌機 120‧‧‧氧化劑處理部 121‧‧‧泵 121a‧‧‧泵 122‧‧‧供給口 122a‧‧‧供給口 122b‧‧‧供給口 122c‧‧‧供給口 123‧‧‧處理槽 124a‧‧‧送出口 124b‧‧‧送出口 125‧‧‧泵 125a‧‧‧泵 126‧‧‧臭氧發生裝置 127‧‧‧臭氧混合裝置 127a‧‧‧噴嘴 128‧‧‧臭氧供給裝置 129‧‧‧臭氧分解裝置 131‧‧‧配管 132‧‧‧配管 132a‧‧‧配管 133‧‧‧配管 134‧‧‧配管 135‧‧‧配管 136‧‧‧配管 A‧‧‧收集袋 B‧‧‧酸性水溶液 E‧‧‧液體 G‧‧‧間隙 P‧‧‧處理液 Pa‧‧‧處理液 V‧‧‧溶液槽 Z‧‧‧含臭氧氣體 S11‧‧‧開孔工程 S12‧‧‧破碎工程 S13‧‧‧第1分離工程 S14‧‧‧第1除塵工程 S15‧‧‧第2除塵工程 S16‧‧‧第3除塵工程 S17‧‧‧第2分離工程 S18‧‧‧第3分離工程 S19‧‧‧氧化劑處理工程 S20‧‧‧第4分離工程 S22‧‧‧臭氧處理工程 S23‧‧‧pH調整工程1‧‧‧System 11‧‧‧Bag breaking device 12‧‧‧Crushing device 13‧‧‧The first separation device 14‧‧‧The first dust removal device 15‧‧‧The second dust removal device 16‧‧‧The third dust removal device 17‧‧‧Second separation device 18‧‧‧Separation device No. 3 19‧‧‧Oxidant treatment device 20‧‧‧Separation device No. 4 22‧‧‧Ozone treatment device 23‧‧‧pH adjustment device 24‧‧‧Water storage tank 30‧‧‧Delivery Department 31‧‧‧Drive device 32‧‧‧Support axis (rotation axis) 33‧‧‧Mixing blade 40‧‧‧Broken Bag Department 41‧‧‧Bag-Break Blade 42‧‧‧Support axis (rotation axis) 43‧‧‧Drive device 50‧‧‧Opening part 60‧‧‧Crushing Department 61‧‧‧Piping 62‧‧‧Piping 63‧‧‧Pump 80‧‧‧Frame 81‧‧‧Cylinder screen 82‧‧‧Spiral shaft 83‧‧‧Spiral blade 84‧‧‧Cover body 85‧‧‧Pressure regulator 86‧‧‧Drive 91‧‧‧Mixed liquid 92‧‧‧Mixed liquid 93‧‧‧Mixed liquid 94‧‧‧Mixed liquid 95‧‧‧Mixed liquid 96‧‧‧Mixed liquid 97‧‧‧Mixed liquid 98‧‧‧Mixture 99‧‧‧Mixed liquid 101‧‧‧Acid aqueous solution 102‧‧‧Acid aqueous solution 103‧‧‧Acid aqueous solution 104‧‧‧Treatment liquid 110‧‧‧Mixed liquid storage department 112‧‧‧Mixed liquid tank 113‧‧‧Mixer 120‧‧‧Oxidant Treatment Department 121‧‧‧Pump 121a‧‧‧Pump 122‧‧‧Supply Port 122a‧‧‧Supply Port 122b‧‧‧Supply Port 122c‧‧‧Supply Port 123‧‧‧Processing tank 124a‧‧‧Exit 124b‧‧‧Exit 125‧‧‧Pump 125a‧‧‧Pump 126‧‧‧Ozone generator 127‧‧‧Ozone mixing device 127a‧‧‧Nozzle 128‧‧‧Ozone supply device 129‧‧‧Ozone Decomposition Device 131‧‧‧Piping 132‧‧‧Piping 132a‧‧‧Piping 133‧‧‧Piping 134‧‧‧Piping 135‧‧‧Piping 136‧‧‧Piping A‧‧‧Collection bag B‧‧‧Acid aqueous solution E‧‧‧Liquid G‧‧‧Gap P‧‧‧Treatment fluid Pa‧‧‧treatment liquid V‧‧‧Solution tank Z‧‧‧Ozone-containing gas S11‧‧‧Hole-opening project S12‧‧‧Crushing Project S13‧‧‧Separation Project No. 1 S14‧‧‧The first dust removal project S15‧‧‧Second Dust Removal Project S16‧‧‧The third dust removal project S17‧‧‧Secondary Separation Project S18‧‧‧Separation Project No. 3 S19‧‧‧Oxidant treatment project S20‧‧‧Separation Project No. 4 S22‧‧‧Ozone Treatment Project S23‧‧‧pH adjustment project
圖1係顯示實施形態之系統之一例的區塊圖。 圖2係顯示圖1的破袋裝置及破碎裝置的構成例的模式圖。 圖3係顯示圖1的第3分離裝置的構成例的模式圖。 圖4係顯示圖1的氧化劑處理裝置的構成例的模式圖。 圖5係顯示圖1的氧化劑處理裝置的其他構成例的部分放大圖。 圖6係顯示實施形態之方法之一例的流程圖。 圖7係顯示在第3分離工程的壓力的大小與處理時間的關係的圖表。Fig. 1 is a block diagram showing an example of the system of the embodiment. Fig. 2 is a schematic diagram showing a configuration example of the bag breaking device and the crushing device of Fig. 1. Fig. 3 is a schematic diagram showing a configuration example of the third separation device of Fig. 1. Fig. 4 is a schematic diagram showing a configuration example of the oxidant treatment device of Fig. 1. Fig. 5 is a partially enlarged view showing another configuration example of the oxidant treatment device of Fig. 1. Fig. 6 is a flowchart showing an example of the method of the embodiment. Fig. 7 is a graph showing the relationship between the pressure in the third separation process and the processing time.
S11‧‧‧開孔工程 S11‧‧‧Hole-opening project
S12‧‧‧破碎工程 S12‧‧‧Crushing Project
S13‧‧‧第1分離工程 S13‧‧‧Separation Project No. 1
S14‧‧‧第1除塵工程 S14‧‧‧The first dust removal project
S15‧‧‧第2除塵工程 S15‧‧‧Second Dust Removal Project
S16‧‧‧第3除塵工程 S16‧‧‧The third dust removal project
S17‧‧‧第2分離工程 S17‧‧‧Secondary Separation Project
S18‧‧‧第3分離工程 S18‧‧‧Separation Project No. 3
S19‧‧‧氧化劑處理工程 S19‧‧‧Oxidant treatment project
S20‧‧‧第4分離工程 S20‧‧‧Separation Project No. 4
S22‧‧‧臭氧處理工程 S22‧‧‧Ozone Treatment Project
S23‧‧‧pH調整工程 S23‧‧‧pH adjustment project
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