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TWI683840B - Treatment method of water-absorbent resin - Google Patents

Treatment method of water-absorbent resin Download PDF

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TWI683840B
TWI683840B TW103116481A TW103116481A TWI683840B TW I683840 B TWI683840 B TW I683840B TW 103116481 A TW103116481 A TW 103116481A TW 103116481 A TW103116481 A TW 103116481A TW I683840 B TWI683840 B TW I683840B
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water
absorbent resin
resin powder
acid
absorbent
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TW201500415A (en
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太田義久
西田素子
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日商利衛多股份有限公司
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    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J11/00Recovery or working-up of waste materials
    • C08J11/04Recovery or working-up of waste materials of polymers
    • C08J11/10Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation
    • C08J11/16Recovery 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
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/40Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/80Destroying solid waste or transforming solid waste into something useful or harmless involving an extraction step
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J11/00Recovery or working-up of waste materials
    • C08J11/04Recovery or working-up of waste materials of polymers
    • C08J11/10Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation
    • C08J11/18Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation by treatment with organic material
    • C08J11/22Recovery or working-up of waste materials of polymers by chemically breaking down the molecular chains of polymers or breaking of crosslinks, e.g. devulcanisation by treatment with organic material by treatment with organic oxygen-containing compounds
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    • C09K17/00Soil-conditioning materials or soil-stabilising materials
    • C09K17/14Soil-conditioning materials or soil-stabilising materials containing organic compounds only
    • C09K17/18Prepolymers; Macromolecular compounds
    • C09K17/20Vinyl polymers
    • C09K17/22Polyacrylates; Polymethacrylates
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L5/00Solid fuels
    • C10L5/40Solid fuels essentially based on materials of non-mineral origin
    • C10L5/406Solid fuels essentially based on materials of non-mineral origin on plastic
    • CCHEMISTRY; METALLURGY
    • C08ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
    • C08JWORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
    • C08J2333/00Characterised by the use of homopolymers or copolymers of compounds having one or more unsaturated aliphatic radicals, each having only one carbon-to-carbon double bond, and only one being terminated by only one carboxyl radical, or of salts, anhydrides, esters, amides, imides, or nitriles thereof; Derivatives of such polymers
    • C08J2333/02Homopolymers or copolymers of acids; Metal or ammonium salts thereof
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/141Feedstock
    • Y02P20/143Feedstock the feedstock being recycled material, e.g. plastics
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Polymers & Plastics (AREA)
  • Health & Medical Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
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  • Sustainable Development (AREA)
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  • Oil, Petroleum & Natural Gas (AREA)
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  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Absorbent Articles And Supports Therefor (AREA)

Abstract

提供用於對使用後的吸收性物品所含的吸水性樹脂粉末再利用之處理方法。 Provide a treatment method for reusing the water-absorbent resin powder contained in the absorbent article after use.

本發明之吸水性樹脂的處理方法,特徵在於:在吸水性樹脂粉末因吸水、凝聚而成的吸水性樹脂粉末的凝聚物,添加弱酸的鹼金屬鹽混合。 The method for processing a water-absorbent resin of the present invention is characterized in that an alkali metal salt of a weak acid is added to agglomerates of a water-absorbent resin powder formed by water absorption and aggregation of water-absorbent resin powder by adding weak acid.

Description

吸水性樹脂的處理方法 Treatment method of water-absorbent resin

本發明關於使用後之吸收性物品所含的吸水性樹脂的處理方法。 The present invention relates to a method of treating water-absorbent resin contained in an absorbent article after use.

由於高齡化,使用看護用的成人用拋棄式紙尿布的人増加。又,從全世界上來看,使用小孩用拋棄式紙尿布的人口亦増加。近年來,拋棄式紙尿布的使用量急速地增加。因為使用後的紙尿布受到污物污染,所以未再利用而被廢棄。被廢棄的紙尿布通常被焚燒處理。但是伴隨著紙尿布的廢棄量增加,從環境保護的觀點,已研討將構成紙尿布之材料再利用。 Due to aging, the number of people using disposable diapers for nursing care is increasing. Moreover, from a global perspective, the population of children using disposable diapers has also increased. In recent years, the use of disposable paper diapers has rapidly increased. Because the used paper diapers are contaminated with dirt, they are discarded without reuse. Discarded paper diapers are usually incinerated. However, with the increase in the amount of paper diapers discarded, from the viewpoint of environmental protection, it has been studied to reuse the materials constituting the paper diapers.

專利文獻1揭示將使用後的紙尿布分離為乙烯基塑料及其以外的成分之使用後的紙尿布之分離方法,其特徵在於具有以下的步驟:在裁斷或粉碎的使用後的紙尿布添加水及脫水劑混合,使使用後的紙尿布所含有的吸水聚合物與脫水劑反應而其脫水的反應步驟;將該脫水完畢的混合物投入轉鼓而溶解,使乙烯基塑料以外的溶解物沈澱而排出至轉鼓外,使乙烯基塑料殘留在轉鼓內的分離步驟;及將殘留的乙烯基塑料吸引至轉鼓外而回收的回收步驟。 Patent Document 1 discloses a separation method of a used paper diaper that separates the used paper diaper into vinyl plastic and other components, and is characterized by the following steps: adding water to the cut or crushed used paper diaper The reaction step of mixing the dehydrating agent to make the water-absorbent polymer contained in the used paper diaper react with the dehydrating agent to dehydrate it; put the dehydrated mixture into a drum to dissolve it, and precipitate the dissolved matter other than vinyl plastic. The separation step of discharging to the outside of the drum to make the vinyl plastic remain in the drum; and the recovery step of attracting the remaining vinyl plastic to the outside of the drum for recovery.

專利文獻2揭示使用後的紙尿布的處理裝置,具備:接收已被截斷的使用後的紙尿布及處理用液體而攪拌,將 含有前述紙尿布的母材成分及吸水性物質成分之再生用物質、與塑膠成分分離的攪拌分離槽;接收從前述攪拌分離槽被排出之含有前述再生用物質之前述處理用液體的第1回收槽;及接收從前述攪拌分離槽被排出之含有前述再生用物質之前述處理用液體的第2回收槽,不同於前述第1回收槽的第2回收槽。 Patent Document 2 discloses a treatment device for a used paper diaper, which includes: receiving the cut-off used paper diaper and the treatment liquid, stirring it, and Recycling substance containing the base material component of the paper diaper and the water-absorbing substance component, and a stirring separation tank separated from the plastic component; receiving the first recovery of the processing liquid containing the regeneration substance discharged from the stirring separation tank A tank; and a second recovery tank that receives the processing liquid containing the regeneration substance discharged from the agitating separation tank, and is different from the second recovery tank of the first recovery tank.

專利文獻3揭示紙尿布處理裝置,具備:接收使用後的紙尿布的轉鼓;收存該轉鼓的至少下端部、內部積存水的水槽部;供給水至該水槽部內的水供給裝置;旋轉驅動轉鼓,將在水中所浸漬的紙尿布分離解體成為水溶物與不溶物的驅動裝置;及將被分離解體後的水溶物與污水同時排出至污水處理設備側的排出裝置。 Patent Document 3 discloses a paper diaper processing device, including: a drum for receiving used paper diapers; a water tank portion that stores at least the lower end portion of the drum and water inside; a water supply device that supplies water into the water tank portion; rotation Drive the drum to separate and disintegrate the paper diapers immersed in water into water-soluble and insoluble materials; and a discharge device that simultaneously discharges the water-soluble and water-dissolved materials separated and disintegrated to the sewage treatment equipment side.

專利文獻4揭示從含有吸水性樹脂之污染後的衛生用品,回收其素材的方法,其係將含有吸水而成凝膠狀的吸水性樹脂之污染後的衛生用品進行粉碎,使該粉碎後的衛生用品分散在含有消毒劑的水中,從前述衛生用品的粉碎物分離附著在衛生用品之污染的一部分。 Patent Document 4 discloses a method of recovering materials from a contaminated sanitary product containing water-absorbent resin, which is to pulverize the contaminated sanitary product containing water-absorbent resin that has absorbed water into a gel form, and to make the pulverized sanitary product The sanitary products are dispersed in the water containing the disinfectant, and the contaminated part of the sanitary products is separated from the crushed product of the foregoing sanitary products.

專利文獻5揭示粒狀的排泄物處理材料,其特徵在於:含有從粉狀塑膠材料乾燥物及吸水後的吸水性樹脂回收的吸水性樹脂,形成1毫米以上的粒度之粒狀物。 Patent Document 5 discloses a granular excrement disposal material, which is characterized by containing a water-absorbent resin recovered from a dried powdered plastic material and a water-absorbent resin after water absorption to form a granular material having a particle size of 1 mm or more.

【先前技術文獻】 【Prior Technical Literature】 【專利文獻】 【Patent Literature】

[專利文獻1]日本特開2012-81433號公報 [Patent Document 1] Japanese Unexamined Patent Publication No. 2012-81433

[專利文獻2]日本特開2012-170918號公報 [Patent Document 2] Japanese Unexamined Patent Publication No. 2012-170918

[專利文獻3]日本特開2004-104929號公報 [Patent Document 3] Japanese Patent Laid-Open No. 2004-104929

[專利文獻3]日本特開2009-73198號公報 [Patent Document 3] Japanese Patent Laid-Open No. 2009-73198

[專利文獻4]日本特開2005-304506號公報 [Patent Document 4] Japanese Patent Laid-Open No. 2005-304506

吸水性樹脂粉末因吸水且凝聚而成之吸水性樹脂的凝聚物,因吸收大量的水分且表面積小而有難以乾燥之問題。特別是在吸水而膨潤的吸水性樹脂添加脫水劑(例如,氯化鈣)而進行脫水處理後之情形,雖然含水率少許降低,但是含水率尚高而難以將吸水性樹脂的凝聚物進行乾燥。因此,再利用拋棄式紙尿布的情形,被要求吸水、凝聚後的吸水性樹脂之有效率的處理方法。 The water-absorbent resin powder has a problem that it is difficult to dry because the aggregate of the water-absorbent resin formed by absorbing water and coagulating absorbs a large amount of water and has a small surface area. In particular, when a water-absorbent resin that absorbs water and swells is added with a dehydrating agent (for example, calcium chloride) and is subjected to dehydration treatment, although the water content is slightly reduced, the water content is still high and it is difficult to dry the aggregate of the water-absorbent resin . Therefore, in the case of reusing disposable paper diapers, an efficient treatment method for water-absorbing and coagulated water-absorbing resin is required.

本發明係鑒於前述情形而進行,係以提供用於對使用後的吸收性物品所含的吸水性樹脂粉末再利用的處理方法為課題。 The present invention has been made in view of the foregoing circumstances, and it is a problem to provide a treatment method for reusing the water-absorbent resin powder contained in the absorbent article after use.

解決前述課題之本發明之吸水性樹脂的處理方法,其特徵在於:在吸水性樹脂粉末因吸水、凝聚而成的吸水性樹脂粉末的凝聚物,添加弱酸的鹼金屬鹽混合。 The method for treating a water-absorbent resin of the present invention that solves the aforementioned problems is characterized in that a weak acid alkali metal salt is added to agglomerates of a water-absorbent resin powder obtained by water absorption and aggregation of water-absorbent resin powder.

本發明者專心研討的結果,發現使用脫水劑(例如,氯化鈣)脫水處理後的吸水性樹脂,構成吸水性樹脂之丙烯酸的羧基,因為脫水劑的2價金屬離子形成交聯結構,因強凝聚力而凝聚著。因此,藉由在因2價金屬離子形成交聯的吸水性樹脂粉末的凝聚物中,添加弱酸的鹼金屬鹽混合,脫水劑 的2價金屬離子與鹼金屬離子進行離子交換。其結果,由2價金屬離子所形成的交聯被切斷。因為金屬交聯被切斷時凝聚力下降,所以吸水性樹脂粉末的凝聚物變化成為原來的粒狀。粒狀的吸水性樹脂表面積面積大而容易乾燥。 As a result of intensive research, the inventors found that the water-absorbent resin after dehydration treatment using a dehydrating agent (for example, calcium chloride) constitutes the carboxyl group of acrylic acid of the water-absorbing resin because the divalent metal ion of the dehydrating agent forms a cross-linked structure. Strong cohesion and cohesion. Therefore, by adding a weak acid alkali metal salt to the aggregate of the water-absorbent resin powder formed by the crosslinking of the divalent metal ion, the dehydrating agent Ion exchange of divalent metal ions with alkali metal ions. As a result, the crosslink formed by the divalent metal ion is cut. Since the cohesive force decreases when the metal crosslink is cut, the aggregate of the water-absorbent resin powder changes to the original granular form. The particulate water-absorbing resin has a large surface area and is easy to dry.

依照本發明,能夠將使用後的吸收性物品所含的吸水性樹脂粉末再資源化。所得到的吸水性樹脂粉末,能夠適合地作為土壤改良劑、固體燃料等利用。 According to the present invention, the water-absorbent resin powder contained in the absorbent article after use can be recycled. The obtained water-absorbent resin powder can be suitably used as a soil improver, solid fuel, or the like.

1‧‧‧吸水性樹脂粉末 1‧‧‧Water-absorbent resin powder

第1圖係顯示吸收性物品的處理步驟之流程圖。 Figure 1 is a flow chart showing the processing steps of an absorbent article.

第2圖係顯示吸水性樹脂粉末的凝聚狀態的變化之圖。 Fig. 2 is a graph showing changes in the aggregation state of the water-absorbent resin powder.

第3圖係顯示吸水性樹脂粉末的凝聚狀態之圖式代替照片。 Fig. 3 is a diagram instead of a photograph showing the aggregation state of the water-absorbent resin powder.

第4圖係顯示吸水性樹脂粉末的凝聚狀態之圖式代替照片。 Fig. 4 is a diagram instead of a photograph showing the aggregation state of the water-absorbent resin powder.

第5圖係顯示吸水性樹脂粉末的凝聚狀態之圖式代替照片。 Fig. 5 is a diagram instead of a photograph showing the aggregation state of the water-absorbent resin powder.

【用以實施發明之形態】 [Forms for carrying out the invention]

本發明之吸水性樹脂的處理方法,其特徵在於:在吸水性樹脂粉末因吸水、凝聚而成的吸水性樹脂粉末的凝聚物,添加弱酸的鹼金屬鹽混合。 The method for processing a water-absorbent resin of the present invention is characterized in that a weak acid alkali metal salt is added to agglomerates of a water-absorbent resin powder obtained by absorbing and coagulating water-absorbent resin powder.

首先,吸收性物品的處理步驟參照圖式說明,但 是本發明不受圖式所顯示的處理步驟限定。第1圖係顯示吸收性物品的處理步驟的一例。第1步驟係附著有污物的吸收性物品之洗淨步驟。首先,將截斷後之使用後的吸收性物品投入處理液體。作為處理液體,適合使用水。藉由在處理液體中進行攪拌處理,能夠將在吸收性物品所附著的污物洗淨。又,能夠藉由構成吸收性物品的材料的比重而分離。 First, the processing procedure of the absorbent article is explained with reference to the drawings, but The present invention is not limited by the processing steps shown in the drawings. Fig. 1 shows an example of the processing procedure of the absorbent article. The first step is a washing step of the absorbent article to which dirt is attached. First, put the absorbent article after use after the cut into the treatment liquid. As a processing liquid, water is suitable. By performing the stirring treatment in the treatment liquid, the dirt adhering to the absorbent article can be washed. In addition, it can be separated by the specific gravity of the materials constituting the absorbent article.

第2步驟係吸水性樹脂的脫水處理。藉由該脫水處理,吸水性樹脂的吸水性喪失。作為脫水劑,適合使用2價金屬鹽,氯化鈣可更適合使用。藉由以2價金屬鹽進行處理,構成吸水性樹脂粉末的丙烯酸的羧基被交聯。其結果,吸水性樹脂粉末的凝聚物體積縮小。藉由凝聚物的體積變化,水從凝聚物被排出。藉由該脫水處理,吸水性樹脂粉末的含水率從約98質量%降低至約70質量%。 The second step is the dehydration treatment of the water-absorbing resin. By this dehydration treatment, the water absorption of the water-absorbent resin is lost. As a dehydrating agent, a divalent metal salt is suitably used, and calcium chloride can be more suitably used. By treatment with a divalent metal salt, the carboxyl group of acrylic acid constituting the water-absorbent resin powder is cross-linked. As a result, the volume of the aggregate of the water-absorbent resin powder is reduced. As the volume of the condensate changes, water is discharged from the condensate. By this dehydration treatment, the water content of the water-absorbent resin powder is reduced from about 98% by mass to about 70% by mass.

第3步驟係塑膠成分回收步驟。將吸收性物品所使用的不織布、薄膜等的塑膠成分進行回收。被回收之塑膠成分進一步被洗淨,以再利用作為油化.碳化原料等為佳。第4步驟係紙漿回收步驟。在第4步驟,將構成吸收體之紙漿回收。被回收之紙漿進一步被洗淨而再利用為佳。 The third step is the plastic component recovery step. Recycle plastic components such as nonwoven fabrics and films used in absorbent articles. The recycled plastic components are further washed and reused as oil. Carbonized raw materials are preferred. The fourth step is the pulp recovery step. In the fourth step, the pulp constituting the absorber is recovered. The recovered pulp is further washed and reused.

第5步驟係紙漿回收後的污水處理步驟。該污水大量地含有被使用作為吸收性物品的吸水性樹脂粉末且含有紙漿的殘渣、糞尿等。污水的沈降物和污水的濃縮物,係以污泥的方式被處理。吸水性樹脂粉末在污泥中係以凝聚物的方式存在。但是,因為污泥中大量地含有吸水性樹脂粉末的凝聚物,所以有不容易將污泥乾燥之問題。特別是即便直接進行乾 燥,亦有只有表面乾燥而凝聚物的內部未乾燥之問題。在本發明之處理方法,對該污泥添加弱酸的鹼金屬鹽。弱酸的鹼金屬鹽對污泥中所含的吸水性樹脂粉末的凝聚物產生作用。藉由使用弱酸的鹼金屬鹽進行處理,2價金屬離子與鹼金屬離子之間產生離子交換反應。其結果,由於金屬交聯被切斷而能夠容易地將吸水性樹脂粉末的凝聚物粒狀化。粒狀化後的吸水性樹脂,因為表面積増加,可輕易地使其乾燥。 The fifth step is the wastewater treatment step after pulp recovery. This sewage contains a large amount of water-absorbent resin powder used as an absorbent article, and contains pulp residues, feces, and the like. Sediment and sewage concentrates are treated as sludge. The water-absorbent resin powder exists in the form of agglomerates in the sludge. However, since the sludge contains a large amount of aggregates of water-absorbent resin powder, there is a problem that it is not easy to dry the sludge. Especially if you do it directly Dryness also has the problem that only the surface is dry and the interior of the aggregate is not dry. In the treatment method of the present invention, a weak acid alkali metal salt is added to the sludge. The weakly acidic alkali metal salt acts on the aggregates of the water-absorbent resin powder contained in the sludge. By processing with alkali metal salt of weak acid, ion exchange reaction occurs between divalent metal ion and alkali metal ion. As a result, since the metal crosslink is cut, the aggregate of the water-absorbent resin powder can be easily granulated. The granulated water-absorbent resin can be easily dried because of the increased surface area.

第2圖係顯示吸水性樹脂粉末的凝聚狀態的變化之圖。第2圖(a)係顯示吸水性樹脂粉末1的凝聚物。吸水性樹脂粉末1係由脫水劑的2價金屬離子產生金屬交聯(-COO-.M2+-OOC-)而凝聚著。2價金屬離子M2+與鹼金屬離子M+藉由離子交換而切斷金屬交聯(-COO-M+ M+-OOC-)。其結果,吸收性樹脂粉末的凝聚物變化成粒狀(第2圖(b))。 Fig. 2 is a graph showing the change of the aggregation state of the water-absorbent resin powder. Fig. 2(a) shows the aggregate of the water-absorbent resin powder 1. (- .M 2+ -. -COO OOC- ) water absorbent resin powder 1 based metal produced by crosslinking divalent metal ion of a dehydrating agent and cohesion. The divalent metal ion M 2+ and the alkali metal ion M + cut off the metal crosslink (-COO - M + M +- OOC-) by ion exchange. As a result, the aggregate of the absorbent resin powder changes into a granular shape (Figure 2 (b)).

前述弱酸的鹼金屬鹽的添加量,相對於使用脫水劑處理後的含水狀態之吸水性樹脂100質量份,以1質量份以上為佳,以3質量份以上為較佳,以100質量份以下為佳,以30質量份以下為較佳。 The addition amount of the alkali metal salt of the weak acid is preferably 1 part by mass or more, preferably 3 parts by mass or more, and 100 parts by mass or less with respect to 100 parts by mass of the water-absorbent resin in the water-containing state treated with the dehydrating agent. Preferably, 30 parts by mass or less is preferable.

吸水後的吸水性樹脂粉末的凝聚物、與弱酸的鹼金屬鹽之混合,沒有特別限定,例如可使用愛知電機股份公司製ROCKING MIXER BHR型等進行。前述混合沒有特別限定,以在5℃以上且130℃以下的溫度範圍進行5分鐘~6小時為佳。亦可在混合之同時,進行脫水。混合脫水沒有特別限定,以在80℃以上且130℃以下的溫度範圍進行5分鐘~6小時為佳。亦可在常壓、減壓、加壓的任一條件下進行。 The mixture of the water-absorbent resin powder after water absorption and the alkali metal salt of the weak acid are not particularly limited. For example, ROCKING MIXER BHR type manufactured by Aichi Electric Co., Ltd. can be used. The aforementioned mixing is not particularly limited, and it is preferably performed in a temperature range of 5°C or more and 130°C or less for 5 minutes to 6 hours. It can also be dehydrated while mixing. The mixed dehydration is not particularly limited, and it is preferably performed in a temperature range of 80°C or more and 130°C or less for 5 minutes to 6 hours. It can also be carried out under any conditions of normal pressure, reduced pressure, and increased pressure.

藉由前述混合,吸收樹脂粉末的凝聚物變化成為粒狀或粉末狀的吸收性樹脂。因為粒狀或粉末狀的吸收性樹脂粉末之表面積大,所以能夠容易地使其乾燥。 By the aforementioned mixing, the aggregate of the absorbent resin powder changes into a granular or powdery absorbent resin. Because the surface area of the particulate or powdery absorbent resin powder is large, it can be easily dried.

作為前述弱酸的鹼金屬鹽的弱酸成分,以與吸水性樹脂粉末的構成成分之丙烯酸同程度或是較弱的酸為佳。亦即,作為弱酸成分,係以使用具有丙烯酸的酸解離常數以上的酸解離常數之酸為佳。藉由使用與丙烯酸相同或較弱的酸之金屬鹽,容易與作為脫水劑使用的2價金屬鹽產生離子交換反應。丙烯酸在水25℃下的酸解離常數為4.26。亦即,在本發明,作為弱酸成分,以使用在水25℃下的酸解離常數為4.26以上的酸為佳。以使用4.30以上的酸為較佳,以使用4.50以上的酸為更佳。弱酸的酸解離常數之上限沒有特別限定,以12為佳,以10為較佳。例如,酸解離常數為9.95的苯酚被認為有效果,但是酸解離常數為16之乙醇則不認為有效果。 The weak acid component of the alkali metal salt of the weak acid is preferably an acid of the same level as the acrylic acid constituting the water-absorbent resin powder or a weaker acid. That is, it is preferable to use an acid having an acid dissociation constant equal to or higher than that of acrylic acid as the weak acid component. By using the metal salt of the same or weaker acid as acrylic acid, it is easy to produce ion exchange reaction with the divalent metal salt used as a dehydrating agent. The acid dissociation constant of acrylic acid at 25°C in water is 4.26. That is, in the present invention, it is preferable to use an acid having an acid dissociation constant of 4.26 or more at 25°C in water as the weak acid component. It is more preferable to use an acid of 4.30 or more, and it is more preferable to use an acid of 4.50 or more. The upper limit of the acid dissociation constant of the weak acid is not particularly limited, but 12 is preferred, and 10 is preferred. For example, phenol with an acid dissociation constant of 9.95 is considered effective, but ethanol with an acid dissociation constant of 16 is not considered effective.

酸(HnXn-)的酸解離常數pKa,可使用以下的式表示。 The acid dissociation constant pKa of the acid (H n X n- ) can be expressed by the following formula.

pKa=-log(1/Ka),Ka=[H+]n.[Xn-]/[HnXn-] pKa=-log(1/Ka),Ka=[H + ] n . [X n- ]/[H n X n- ]

以多階段解離酸時,以至少1階段的酸解離常數為4.26~12的範圍為佳,以4.3~11的範圍為較佳,以4.5~10的範圍為更佳。又,以全部階段的解離常數為4.26~12的範圍為佳,以4.3~11的範圍為較佳,以4.5~10的範圍為更佳。 When dissociating acid in multiple stages, the acid dissociation constant of at least one stage is preferably in the range of 4.26-12, preferably in the range of 4.3-11, and more preferably in the range of 4.5-10. In addition, the dissociation constant in all stages is preferably in the range of 4.26 to 12, preferably in the range of 4.3 to 11, and more preferably in the range of 4.5 to 10.

作為在水25℃下的酸解離常數為4.26以上的酸之具體例,例如,能夠舉出己二酸(4.26)、壬二酸(4.39)、對茴香酸(4.48)、鄰胺基苯甲酸(第2階段:4.95)、對胺基苯甲酸(4.85)、異戊酸(4.58)、異菸鹼酸(第2階段:4.87)、異酪酸 (4.63)、辛酸(4.89)、戊酸(4.64)、2-喹啉甲酸(quinaldic acid)(第2階段:4.75)、檸檬酸(第2階段:4.35)、巴豆酸(4.69)、桂皮酸(反式)(4.44)、乙酸(4.56)、環己烷羧酸(4.70)、(R,R)-酒石酸(第2階段:4.44)、對羥基苯甲酸(4.58)、庚二酸(4.31)、2,6-吡啶二羧酸(第3階段:4.68)、丙酸(4.67)、己酸(4.63)、庚酸(4.66)、鄰苯二羧酸(第2階段:4.93)、丙二酸(第2階段:5.28)、酪酸(4.63)、蘋果酸(3.24)、乙醯丙酸(levulinic acid)(4.44)、碳酸(6.35)等。 Specific examples of acids having an acid dissociation constant of 4.26 or more at 25°C in water include adipic acid (4.26), azelaic acid (4.39), p-anisic acid (4.48), and o-aminobenzoic acid. (2nd stage: 4.95), p-aminobenzoic acid (4.85), isovaleric acid (4.58), isonicotinic acid (2nd stage: 4.87), isobutyric acid (4.63), caprylic acid (4.89), valeric acid (4.64), 2-quinodic acid (stage 2: 4.75), citric acid (stage 2: 4.35), crotonic acid (4.69), cinnamic acid (Trans) (4.44), acetic acid (4.56), cyclohexane carboxylic acid (4.70), (R,R)-tartaric acid (stage 2: 4.44), p-hydroxybenzoic acid (4.58), pimelic acid (4.31 ), 2,6-pyridinedicarboxylic acid (stage 3: 4.68), propionic acid (4.67), hexanoic acid (4.63), heptanoic acid (4.66), phthalic acid (stage 2: 4.93), propylene Diacid (stage 2: 5.28), butyric acid (4.63), malic acid (3.24), levulinic acid (4.44), carbonic acid (6.35), etc.

作為前述鹼金屬,可舉出鋰、鈉、鉀等。作為前述弱酸的鹼金屬鹽的具體例,例如,可舉出碳酸鈉、碳酸氫鈉、碳酸鉀、碳酸氫鉀、檸檬酸乙酸鈉、及琥珀酸乙酸鈉等。又,前述弱酸的鹼金屬鹽,以固體狀為佳。因為添加固體狀的弱酸鹼金屬鹽混合,因為滲透壓水從吸水性樹脂粉末的凝聚物排出變為容易。 Examples of the alkali metal include lithium, sodium, and potassium. Specific examples of the alkali metal salt of the weak acid include, for example, sodium carbonate, sodium bicarbonate, potassium carbonate, potassium bicarbonate, sodium citrate acetate, and sodium succinate acetate. In addition, the alkali metal salt of the weak acid is preferably solid. The addition of a solid weak acid alkali metal salt mix makes it easy to discharge osmotic pressure water from the aggregates of the water-absorbent resin powder.

藉由將使用前述處理方法所得到之粒狀的吸水性樹脂進行乾燥,能夠將粒狀的吸水性樹脂粉末再生。再生後的吸水性樹脂粉末之吸收性能亦優,例如,再生吸水性樹脂粉末的吸收倍率為15g/g以上。 By drying the particulate water-absorbent resin obtained using the aforementioned processing method, the particulate water-absorbent resin powder can be regenerated. The regenerated water-absorbent resin powder also has excellent absorption performance. For example, the regenerated water-absorbent resin powder has an absorption ratio of 15 g/g or more.

再生後的吸水性樹脂粉末,例如可作為土壤改良劑使用,或可作為固體燃料使用。因此,本發明包含乾燥以前述處理方法所得到的粒狀的吸收性樹脂粉末為特徵之再生吸水性樹脂粉末的製造方法、土壤改良劑的製造方法、及固體燃料的製造方法。 The regenerated water-absorbent resin powder can be used, for example, as a soil amendment or as a solid fuel. Therefore, the present invention includes a method for drying a regenerated water-absorbent resin powder characterized by the particulate absorbent resin powder obtained by the aforementioned processing method, a method for producing a soil improver, and a method for producing solid fuel.

本發明之處理對象的吸水性樹脂粉末,沒有特別 限定,為以丙烯酸作為構成成分之交聯聚合物,其羧基的至少一部分被中和者為佳。構成交聯聚合物之丙烯酸成分的含量,以90質量%以上為佳,以95質量%以上較佳,以99質量%以下為佳,以97質量%以下為更佳。 The water-absorbent resin powder to be treated by the present invention is not particularly As a limitation, a cross-linked polymer having acrylic acid as a constituent component, it is preferable that at least a part of its carboxyl group is neutralized. The content of the acrylic component constituting the crosslinked polymer is preferably 90% by mass or more, preferably 95% by mass or more, preferably 99% by mass or less, and more preferably 97% by mass or less.

將作為交聯聚合物的羧基之至少一部分中和的陽離子,沒有特別限定,例如,能夠舉出鋰、鈉、鉀等的鹼金屬離子、鎂、鈣等的鹼土金屬離子等。這些之中,以交聯聚合物的羧基之至少一部分被鈉離子中和為佳。又,交聯聚合物的羧基之中和,可將聚合而得到的交聯聚合物之羧基進行中和,亦可預先使用中和後的單體而形成交聯聚合物。 The cation that neutralizes at least a part of the carboxyl group of the crosslinked polymer is not particularly limited, and examples thereof include alkali metal ions such as lithium, sodium, and potassium, and alkaline earth metal ions such as magnesium and calcium. Among these, it is preferable that at least a part of the carboxyl group of the cross-linked polymer is neutralized by sodium ions. In addition, the carboxyl group of the cross-linked polymer is neutralized, and the carboxyl group of the cross-linked polymer obtained by polymerization may be neutralized, or the monomer after neutralization may be used in advance to form a cross-linked polymer.

交聯聚合物的羧基之中和度,以60莫耳%以上為佳,以65莫耳%以上較佳。因為中和度太低時,所得到的吸水性樹脂粉末之吸收性能有降低的情形。又,中和度之上限沒有特別限定,亦可將羧基的全部中和。又,中和度可以下述式求取。 The degree of neutralization of the carboxyl group of the cross-linked polymer is preferably 60 mol% or more, and preferably 65 mol% or more. When the degree of neutralization is too low, the absorption performance of the resulting water-absorbent resin powder may be reduced. In addition, the upper limit of the degree of neutralization is not particularly limited, and all of the carboxyl groups may be neutralized. In addition, the degree of neutralization can be obtained by the following formula.

中和度(莫耳%)=100×「交聯聚合物被中和的羧基之莫耳數」/「交聯聚合物所具有的羧基之總莫耳數(包含中和及未中和)」 Neutralization degree (mol %) = 100 × "number of carboxyl groups of the cross-linked polymer neutralized" / "total number of carboxyl groups of the cross-linked polymer (including neutralized and unneutralized) "

本發明之處理對象的吸收性物品,只要是使用吸水性樹脂粉末者,沒有特別限定,例如,可舉出拋棄式紙尿布、失禁墊片、輕失禁墊片、生理用衛生棉、母乳墊等。這些之中,以吸水性樹脂粉末的使用量多的拋棄式紙尿布為適合。 The absorbent article to be treated in the present invention is not particularly limited as long as it uses water-absorbent resin powder, and examples thereof include disposable diapers, incontinence pads, light incontinence pads, sanitary napkins, and breast milk pads. . Among these, disposable paper diapers with a large amount of water-absorbent resin powder used are suitable.

[實施例] [Example]

以下,藉由實施例而詳細地說明本發明,但是本 發明不被下述的實施例限定,在未脫離本發明宗旨的範圍之變更、實施態樣,任一者均被包含在本發明之範圍內。 Hereinafter, the present invention will be described in detail by examples, but the present The invention is not limited by the following examples, and any change or embodiment that does not deviate from the scope of the invention is included in the scope of the invention.

[處理例1~10] [Processing examples 1 to 10]

將使用後的市售拋棄式紙尿布粉碎後的物,投入含有以氯化鈣作為脫水劑之處理水,進行吸水性樹脂的脫水處理。從處理水中分離回收吸收性物品所使用的不織布、薄膜等的塑膠成分,隨後,將紙漿進行分離回收。以脫水機將分離回收後的污水進行脫水而將污泥(吸水性樹脂的凝聚物)回收。 The pulverized product of the commercially available disposable paper diaper was put into treated water containing calcium chloride as a dehydrating agent, and dehydrated by a water-absorbent resin. The non-woven fabrics, films and other plastic components used in absorbent articles are separated and recovered from the treated water, and then the pulp is separated and recovered. The separated and recovered sewage is dehydrated by a dehydrator to recover sludge (agglomerates of water-absorbent resin).

[處理例11~13] [Processing Examples 11 to 13]

將短纖漿(fluff pulp)100質量份及吸水性樹脂粉末(SUNDIA POLYMER公司製AQUAPEARL DS560:以丙烯酸為構成成分之交聯聚合物)60質量份以氣流型混合裝置(AUTECH股份公司製PAD FORMER)進行混合,將所得到的混合物以單位面積重量為約500g/m2之方式均勻地層積在壓克力板(acrylic plate)(厚度4mm)上,而且在5kg/cm2的壓力下加壓30秒鐘,得到吸收體。將該吸收體截斷成為14cm×36cm的長方形,在各自的上下配置與吸收體相同大小的吸水紙(單位面積重量15.5g/m2、ADVANTEC公司製、FILTER PAPER 2號),再將聚乙烯薄片(Tamapoly公司製Polyethylene film UB-1)配置在背面,而且將不織布(單位面積重量20g/m2、旭化成公司製ELTAS GUARD)配置在表面,來製造吸收性物品。 100 parts by mass of fluff pulp and 60 parts by mass of water-absorbent resin powder (AQUAPEARL DS560 manufactured by Sundia Polymer Co., Ltd.: a cross-linked polymer composed of acrylic acid) as an air-flow mixing device (PAD FORMER manufactured by AUTECH Co., Ltd.) ) Mixing, the resulting mixture is evenly laminated on an acrylic plate (thickness 4mm) with a weight per unit area of about 500g/m 2 and pressurized under a pressure of 5kg/cm 2 After 30 seconds, the absorber was obtained. The absorbent body was cut into a rectangular shape of 14 cm×36 cm, and water absorbing paper of the same size as the absorbent body (weight per unit area 15.5 g/m 2 , manufactured by ADVANTEC, FILTER PAPER No. 2) was placed above and below the polyethylene sheet. (Polyethylene film UB-1 manufactured by Tamapoly) is arranged on the back, and a non-woven fabric (weight 20g/m 2 per unit area, ELTAS GUARD manufactured by Asahi Kasei Corporation) is arranged on the surface to manufacture absorbent articles.

將前述吸收性物品浸漬於生理食鹽水60分鐘,之後,使其載置在金屬絲網之上60分鐘而進行去水。使用高速粉碎機RSC-500(R-ing股份公司)將去水後的吸收性物品進行 粉碎。將前述粉碎物浸漬於5質量%的氯化鈣液而進行脫水處理。脫水處理後,將沈降物(吸水性樹脂的凝聚物)回收。脫水處理前之吸水性樹脂的含水率係98質量%,沈降物(吸水性樹脂的凝聚物)的含水率為72質量%。 The absorbent article was immersed in physiological saline for 60 minutes, and then placed on a wire mesh for 60 minutes to remove water. Use the high-speed shredder RSC-500 (R-ing Co., Ltd.) to carry out the dehydrated absorbent articles Smash. The pulverized product was immersed in a 5% by mass calcium chloride solution and dehydrated. After the dehydration treatment, the sediment (agglomerate of water-absorbent resin) is recovered. The water content of the water-absorbent resin before the dehydration treatment was 98% by mass, and the water content of the sediment (agglomerate of the water-absorbent resin) was 72% by mass.

<吸水後的吸水性樹脂的凝聚物之處理> <Treatment of aggregates of water-absorbent resin after water absorption>

在200mL燒杯放入所得到的污泥或沈降物(吸水性樹脂粉末的凝聚物)10g及預定量的處理劑,使用藥匙混合60分鐘。所得到的混合物均勻地舖滿在鋁標準容器(寬度:276mm、深度:211mm、高度:35mm)。將鋁標準容器放入送風恆溫器(YAMATO科學股份公司DKM600)、100℃×3分鐘,使混合物乾燥。將所得到的結果整理在表1。在表中的乾燥性,「○」表示可容易地乾燥,「×」表示只有表面乾燥而內部未乾燥。吸收倍率係將乾燥後的吸收性樹脂粉末取出,調整成為250μm~500μm的粒度所測定的吸收倍率。吸收倍率係使用以下的方法進行測定。 Into a 200 mL beaker, 10 g of the obtained sludge or sediment (agglomerate of water-absorbent resin powder) and a predetermined amount of treatment agent were placed, and mixed with a medicine spoon for 60 minutes. The resulting mixture was evenly spread in an aluminum standard container (width: 276 mm, depth: 211 mm, height: 35 mm). Put an aluminum standard container into a blower thermostat (YAMATO Scientific Co., Ltd. DKM600) at 100°C for 3 minutes to dry the mixture. Table 1 summarizes the obtained results. In the dryness in the table, "○" indicates that it can be easily dried, and "×" indicates that only the surface is dry and the inside is not dry. The absorption ratio is the absorption ratio measured by taking out the dried absorbent resin powder and adjusting it to a particle size of 250 μm to 500 μm. The absorption ratio is measured using the following method.

(吸收倍率的測定方法) (Measurement method of absorption rate)

吸收倍率的測定係依據JIS K 7223(1996)而進行。將網目63μm的耐綸網(JIS Z8801-1:2000)切斷成為寬度10cm、長度40cm的長方形且在長度方向中央進行二折疊,將兩端熱封而製造寬度10cm(內尺寸9cm)、長度20cm的耐綸袋。精稱測定試料1.00g且均勻地裝入所製造的耐綸袋之底部。使將裝有試料的耐綸袋浸漬於生理食鹽水。從浸漬開始起算60分鐘後,將耐綸袋從生理食鹽水取出且在垂直狀態下懸吊1小時而去水之後,測定試料的質量(F1)。又,不使用試料而進行同樣的操 作且測定此時的質量F0(g)。然後,從質量F1、F0及試料的質量,依照下式而算出目的之吸收倍率。 The measurement of the absorption rate is performed in accordance with JIS K 7223 (1996). A nylon mesh (JIS Z8801-1: 2000) with a mesh size of 63 μm was cut into a rectangle with a width of 10 cm and a length of 40 cm, and folded in the center in the longitudinal direction, and both ends were heat-sealed to produce a width of 10 cm (internal size: 9 cm) and length. 20cm nylon bag. Measure exactly 1.00 g of the test sample and fill it evenly into the bottom of the manufactured nylon bag. The nylon bag containing the sample was immersed in physiological saline. After 60 minutes from the start of immersion, the nylon bag was taken out of physiological saline and hung vertically for 1 hour to remove water, and then the mass of the sample was measured (F1). Also, do the same without using samples Make and measure the mass F0(g) at this time. Then, from the masses F1, F0 and the mass of the sample, the target absorption rate is calculated according to the following formula.

吸收倍率(g/g)=(F1-F0)/試料的質量 Absorption rate (g/g)=(F1-F0)/quality of sample

Figure 103116481-A0202-12-0012-1
Figure 103116481-A0202-12-0012-1

從表1的結果能夠清楚明白得知,吸水性樹脂粉末在因吸水且凝聚而成之吸水性樹脂粉末的凝聚物添加弱酸的鹼金屬鹽而混合時,吸水性樹脂粉末的凝聚物成為粒狀。而且,可知粒狀的吸水性樹脂粉末能夠乾燥至使含水率為約3質量%以下。另一方面,凝膠狀的吸水性樹脂只有表面乾燥,但是內部未乾燥的原來狀態。 It is clear from the results in Table 1 that when the water-absorbent resin powder is mixed by adding the weak acid alkali metal salt to the aggregate of the water-absorbent resin powder formed by absorbing water and agglomeration, the aggregate of the water-absorbent resin powder becomes granular. . In addition, it can be seen that the particulate water-absorbent resin powder can be dried to a moisture content of about 3% by mass or less. On the other hand, the gel-like water-absorbent resin is in the original state where the surface is dry but the inside is not dried.

第3圖係表示脫水處理後的沈降物(吸水性樹脂的凝聚物)之圖式代替照片。第4圖係顯示將脫水處理後的沈降 物(吸水性樹脂的凝聚物),使用碳酸氫鈉作為弱酸的鹼金屬鹽之處理後的例子。第5圖係顯示將脫水處理後的沈降物(吸水性樹脂的凝聚物),使用氯化鉀之處理後的例子。從第4圖能夠清楚明白得知,使用弱酸的鹼金屬鹽時,吸水性樹脂的凝聚物成為粒狀。另一方面,如第5圖使用氯化鉀時,雖然利用滲透壓將水從吸水性樹脂排出,但是仍為凝聚物原來狀態且乾燥困難。 FIG. 3 is a diagram instead of a photograph showing a sediment (agglomerate of water-absorbent resin) after dehydration treatment. Figure 4 shows the settlement after dehydration The substance (agglomerate of water-absorbent resin) is an example after treatment using sodium bicarbonate as the alkali metal salt of weak acid. Fig. 5 shows an example in which the sediment after dehydration treatment (agglomerate of water-absorbent resin) is treated with potassium chloride. It can be clearly seen from FIG. 4 that when a weak acid alkali metal salt is used, the aggregate of the water-absorbent resin becomes granular. On the other hand, when potassium chloride is used as shown in Fig. 5, although water is discharged from the water-absorbent resin by osmotic pressure, it is still in the original state of the aggregate and drying is difficult.

【產業上之利用可能性】 【Industrial utilization possibilities】

本發明的吸收體,例如能夠適合使用在用以將從人體所排出的體液吸收所使用的吸收性物品,特別是能夠適合使用在失禁墊片.拋棄式尿布、生理用衛生棉、母乳墊等的吸收性物品。 The absorbent body of the present invention can be suitably used in absorbent articles used for absorbing body fluids discharged from the human body, and particularly can be suitably used in incontinence pads. Absorbent articles such as disposable diapers, sanitary napkins, breast pads, etc.

Claims (11)

一種吸水性樹脂的處理方法,其特徵在於:在作為吸收性物品而使用的吸水性樹脂粉末因吸水凝聚而成的吸水性樹脂粉末的凝聚物,於使用作為脫水劑之2價金屬鹽進行脫水處理之吸水性樹脂粉末的凝聚物中,添加並混合弱酸的鹼金屬鹽,使吸水性樹脂粉末的凝聚物變化成粒狀,並將所得之粒狀的吸水性樹脂進行乾燥。 A method for treating water-absorbent resin, characterized in that the water-absorbent resin powder used as an absorbent article is agglomerated by water-absorbent resin powder aggregated by water absorption, and is dehydrated by using a divalent metal salt as a dehydrating agent The agglomerate of the treated water-absorbent resin powder is added and mixed with an alkali metal salt of a weak acid to change the agglomerate of the water-absorbent resin powder into a granular form, and the resulting granular water-absorbent resin is dried. 如申請專利範圍第1項所述之吸水性樹脂的處理方法,其中前述吸水性樹脂粉末係以丙烯酸作為主要構成成分的吸水性樹脂粉末。 The method for processing a water-absorbent resin as described in item 1 of the patent application range, wherein the water-absorbent resin powder is a water-absorbent resin powder having acrylic acid as a main component. 如申請專利範圍第1項所述之吸水性樹脂的處理方法,其中對作為吸收性物品而使用的吸水性樹脂粉末吸水所成之物,使用2價金屬鹽作為脫水劑進行脫水處理,得到含有吸水性樹脂粉末的凝聚物的污水,對此污水沉降處理或濃縮處理,得到含有吸水性樹脂粉末的凝聚物的污水沉降物或污水濃縮物之污泥,將上述弱酸的鹼金屬鹽加入此污泥混合,使包含在污泥中的吸水性樹脂粉末的凝聚物變成粒狀,將所得到的粒狀的吸水性樹脂乾燥。 The method for processing a water-absorbent resin as described in item 1 of the patent application scope, wherein the water-absorbent resin powder used as an absorbent article is dehydrated by using a divalent metal salt as a dehydrating agent to obtain a product containing Sewage of aggregates of water-absorbent resin powder is treated by sedimentation or concentration of this sewage to obtain sludge of sewage sediments or sewage concentrates containing aggregates of water-absorbent resin powder, and the alkali metal salt of the above-mentioned weak acid is added to this sewage The sludge is mixed to make the aggregate of the water-absorbent resin powder contained in the sludge granular, and the obtained particulate water-absorbent resin is dried. 如申請專利範圍第1項所述之吸水性樹脂的處理方法,其中前述2價金屬鹽係氯化鈣。 The method for processing a water-absorbent resin as described in item 1 of the patent application, wherein the aforementioned divalent metal salt is calcium chloride. 如申請專利範圍第1項所述之吸水性樹脂的處理方法,其中前述弱酸係在水25℃下的酸解離常數為4.26以上的酸。 The method for processing a water-absorbent resin as described in item 1 of the patent application range, wherein the weak acid is an acid having an acid dissociation constant of 4.26 or more at 25°C in water. 如申請專利範圍第1項所述之吸水性樹脂的處理方法,其中前述弱酸的鹼金屬鹽係選自由碳酸鈉、碳酸氫鈉、碳酸 鉀、碳酸氫鉀、檸檬酸乙酸鈉、及琥珀酸乙酸鈉所組成之群組之至少1種。 The treatment method of water-absorbent resin as described in item 1 of the patent application scope, wherein the alkali metal salt of the weak acid is selected from sodium carbonate, sodium bicarbonate, carbonic acid At least one of the group consisting of potassium, potassium bicarbonate, sodium citrate acetate, and sodium succinate acetate. 如申請專利範圍第1項所述之吸水性樹脂的處理方法,其中前述吸收性物品係用以吸收從人體所排出的體液之吸收性物品。 The method for processing a water-absorbent resin as described in item 1 of the patent application scope, wherein the absorbent article is an absorbent article for absorbing body fluids discharged from the human body. 如申請專利範圍第3項所述之吸水性樹脂的處理方法,更包括:於脫水處理步驟之前,將附著於前述吸收性物品之污染物洗淨之步驟;及在前述沉降處理或濃縮處理之步驟之前,從前述污水將前述吸收性物品所使用之塑膠成分及紙漿成分分別回收之步驟。 The treatment method of the water-absorbent resin as described in item 3 of the patent application scope further includes: before the dehydration treatment step, the step of washing the contaminants attached to the aforementioned absorbent article; and in the aforementioned sedimentation treatment or concentration treatment Before the step, the plastic component and the pulp component used in the absorbent article are separately recovered from the sewage. 一種再生吸水性樹脂粉末的製造方法,其特徵在於:藉由申請專利範圍第1至8項中任一項所述之處理方法以得到再生吸水性樹脂粉末。 A method for manufacturing a regenerated water-absorbent resin powder, characterized in that the regenerated water-absorbent resin powder is obtained by the processing method described in any one of patent application items 1 to 8. 一種土壤改良材料的製造方法,其特徵在於:使用根據申請專利範圍第1至8項中任一項所述之處理方法所得到之粒狀的吸水性樹脂以製造土壤改良材料。 A method for producing a soil improvement material, characterized by using a particulate water-absorbent resin obtained by the treatment method described in any one of claims 1 to 8 to produce a soil improvement material. 一種固體燃料的製造方法,其特徵在於:使用根據申請專利範圍第1至8項中任一項所述之處理方法所得到之粒狀的吸水性樹脂以製造固體燃料。 A method for manufacturing a solid fuel, characterized in that a particulate water-absorbent resin obtained by the processing method described in any one of claims 1 to 8 is used to manufacture a solid fuel.
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