WO2021153626A1 - Adsorbent sheet, adsorbent element, and adsorption treatment device using same - Google Patents

Adsorbent sheet, adsorbent element, and adsorption treatment device using same Download PDF

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Publication number
WO2021153626A1
WO2021153626A1 PCT/JP2021/002874 JP2021002874W WO2021153626A1 WO 2021153626 A1 WO2021153626 A1 WO 2021153626A1 JP 2021002874 W JP2021002874 W JP 2021002874W WO 2021153626 A1 WO2021153626 A1 WO 2021153626A1
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Prior art keywords
adsorption
mass
metal complex
porous metal
sheet
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PCT/JP2021/002874
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French (fr)
Japanese (ja)
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有希 岡田
晶徳 水谷
哲 永井
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東洋紡株式会社
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Priority to KR1020227022185A priority Critical patent/KR20220128343A/en
Priority to CN202180011264.5A priority patent/CN115087499A/en
Priority to JP2021574080A priority patent/JPWO2021153626A1/ja
Publication of WO2021153626A1 publication Critical patent/WO2021153626A1/en

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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/223Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material containing metals, e.g. organo-metallic compounds, coordination complexes
    • B01J20/226Coordination polymers, e.g. metal-organic frameworks [MOF], zeolitic imidazolate frameworks [ZIF]
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/02Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
    • B01D53/04Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with stationary adsorbents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/02Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
    • B01D53/04Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with stationary adsorbents
    • B01D53/0407Constructional details of adsorbing systems
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/26Drying gases or vapours
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/26Drying gases or vapours
    • B01D53/261Drying gases or vapours by adsorption
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/26Drying gases or vapours
    • B01D53/28Selection of materials for use as drying agents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28014Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their form
    • B01J20/28033Membrane, sheet, cloth, pad, lamellar or mat
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/34Regenerating or reactivating
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/30Processes for preparing, regenerating, or reactivating
    • B01J20/34Regenerating or reactivating
    • B01J20/3483Regenerating or reactivating by thermal treatment not covered by groups B01J20/3441 - B01J20/3475, e.g. by heating or cooling
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2253/00Adsorbents used in seperation treatment of gases and vapours
    • B01D2253/20Organic adsorbents
    • B01D2253/204Metal organic frameworks (MOF's)

Definitions

  • the present invention relates to an adsorption sheet, an adsorption element, and an adsorption treatment apparatus using the adsorption sheet, which efficiently separates, recovers, or adsorbs and removes substances to be adsorbed such as moisture, organic solvent, and malodorous components.
  • Porous materials such as activated carbon, silica gel, and zeolite are used for various purposes such as deodorization, purification of air and water, and separation / purification of gas, and are indispensable materials for modern life.
  • a porous material in which a metal ion capable of taking various coordination forms and a bridging ligand having two or more coordinations are combined and self-assembled that is, a porous metal complex (MOF), or a porous metal complex (MOF), or A new porous material called Porous Coordination Polymer (PCP) has been discovered.
  • These porous metal complexes have features such as high specific surface area, sharp pore distribution, and high structural design, which are features not found in conventional porous materials such as activated carbon, silica gel, and zeolite. Attention has been paid.
  • Patent Document 1 discloses that a specific dicarboxylic acid metal complex is suitable as a gas occlusion material, particularly a gas occlusion material containing methane as a main component.
  • Patent Document 2 discloses a porous metal complex synthesized from copper ions and trimesic acids, and an adsorbent is disclosed as an example of its use.
  • Patent Document 3 discloses that a metal chromium or a chromium salt and a porous metal complex obtained from trimesic acids are particularly excellent as a water vapor adsorbent.
  • the porous metal complex has the potential as an adsorbent for various gases.
  • Patent Document 4 discloses an adsorption sheet containing a porous metal complex, a heat-resistant fiber, a self-consolidating clay mineral fiber, and an organic binder as a sheet containing the porous metal complex. ..
  • Japanese Patent Publication Japanese Patent Laid-Open No. 2001-348361
  • Japanese Patent Publication Japanese Patent Publication "Japanese Patent Laid-Open No. 2000-327628”
  • Japanese Patent Publication Japanese Patent Laid-Open No. 2007-51112
  • Japanese Patent Publication Japanese Patent Laid-Open No. 2013-154301
  • the adsorption sheet disclosed in Patent Document 4 requires clay mineral fibers, and the heat-resistant fiber content ratio is reduced by that amount. Therefore, the sheet itself is not stiff, and for example, a step is formed during honeycomb processing when making a filter. There are problems such as not sticking.
  • the present invention relates to an adsorption sheet, an adsorption element, and an adsorption / desorption treatment apparatus using the adsorption sheet, which is excellent in the supportability of the porous metal complex and the flexibility and processability of the sheet, and has sufficient adsorption performance. Is raised as an issue.
  • the present invention has the following configuration.
  • a porous metal complex having a metal and an organic ligand and having a water adsorption rate of 30% by mass or more at 25 ° C. and a relative pressure of 0.5, and non-fibrillated fibers and fibrillated fibers.
  • An adsorption sheet characterized by containing,.
  • An adsorption element comprising any one of the above 1 to 4 adsorption sheets.
  • the adsorption target substance is provided with the adsorption element of 5 above, an adsorption means for introducing and adsorbing the adsorption target substance into the adsorption element, and a desorption means for desorbing the adsorption target substance adsorbed by the adsorption element.
  • An adsorption / desorption processing device that continuously performs adsorption / desorption.
  • an adsorption sheet or the like which is excellent in the supportability of the porous metal complex and the flexibility and processability of the sheet and has sufficient adsorption performance.
  • the adsorption sheet of the present invention contains a porous metal complex having a metal and an organic ligand and having a water adsorption rate of 30% by mass or more at 25 ° C. and a relative pressure of 0.5, and non-fibrillated fibers and fibrils. Containing the carbonized fiber.
  • the ratio is called relative pressure.
  • the adsorption sheet of the present invention contains a porous metal complex, high adsorption performance can be obtained. Moreover, since this porous metal complex is characterized in that the water adsorption rate at 25 ° C. and a relative pressure of 0.5 is 30% by mass or more, a large amount of water can be retained by the sheet itself, and the sheet can be processed. High flexibility of time is obtained. Furthermore, since the porous metal complex can sufficiently develop flexibility, it is possible to reduce the amount of organic binder conventionally used for imparting flexibility, and as a result, it is possible to reduce the amount of organic binder in the pores of the adsorbent. The rate of adsorption (porosity) of the side chains of the binder and the like can be reduced, and further sufficient adsorption performance can be obtained. If the water adsorption rate is less than 30% by mass, the flexibility will be lacking.
  • the adsorption sheet of the present invention contains non-fibrillated fibers and fibrillated fibers.
  • the fibers that are not fibrillated for example, it is possible to maintain the step shape by itself even when step processing is performed, and the workability is excellent.
  • the fibrillated fiber the porous metal complex particles can be efficiently retained, and not only the supportability is excellent, but also the organic binder conventionally used for imparting the supportability can be reduced. Is possible. As a result, pore clogging can be reduced, and more sufficient adsorption performance can be obtained.
  • the adsorption sheet of the present invention may contain an organic binder having a melting point in water of 65 ° C. to 100 ° C. and a high melting point.
  • an organic binder having a high melting point of 65 ° C. to 100 ° C. in water it is possible to further reduce pore clogging and obtain excellent adsorption performance. If the dissolution temperature in water is less than 65 ° C., the adsorption performance will be insufficient due to pore clogging, and if the temperature is higher than 100 ° C., the adhesion will be insufficient and the supportability will be insufficient.
  • the porous metal complex according to the present invention is a porous material composed of a metal ion and a compound having an organic ligand.
  • the form of the porous metal complex that can be used is not particularly specified, and powder or granular ones can be used. It is preferably a porous metal complex having an average particle size of 0.1 ⁇ m to 200 ⁇ m, more preferably 1 to 100 ⁇ m, and most preferably 1 to 80 ⁇ m. If the average particle size is less than 0.1 ⁇ m, the yield during the adsorption sheet formation becomes low. On the other hand, if the average particle size exceeds 200 ⁇ m, it becomes difficult to sufficiently support the porous metal complex on the adsorption sheet, and the porous metal complex may come off more often.
  • the average particle size can be measured using, for example, a scanning electron microscope.
  • the BET specific surface area of the porous metal complex by the 77K nitrogen adsorption method is not particularly limited, but is preferably 500 m 2 / g or more, for example. If the BET specific surface area is smaller than 500 m 2 / g, it may be difficult to obtain sufficient adsorption performance.
  • the BET specific surface area is more preferably 1000 m 2 / g or more.
  • the upper limit of the BET specific surface area is not particularly limited, but is preferably 6000 m 2 / g or less. This is because if it exceeds this range, there is a disadvantage that the production of the porous metal complex becomes very difficult.
  • the BET specific surface area can be measured, for example, by the method described in the subsequent examples.
  • the metal ions constituting the porous metal complex are not particularly limited, and examples thereof include typical metal elements such as aluminum ions and transition metal elements such as titanium ions, zirconium ions, iron ions, and copper ions.
  • examples of the compound having a ligand include fumaric acid, 2-aminoterephthalic acid, 1,4-naphthalenedicarboxylic acid, terephthalic acid, trimesic acid and the like.
  • Specific examples of the porous metal complex include a porous metal complex composed of aluminum ions and terephthalic acid (Basolite A100 manufactured by BASF) and a porous metal complex composed of copper ions and trimesic acid (BASF).
  • Basolite C300 Basolite C300
  • a porous metal complex composed of iron ions and trimesic acid BASF, Basolite F300
  • a porous metal complex composed of titanium ions and terephthalic acid and composed of zirconium ions and terephthalic acid.
  • Porous metal complex, porous metal complex composed of zirconium ion and fumaric acid, porous metal complex composed of zirconium ion and 2-aminoterephthalic acid, porous metal complex composed of titanium ion and 2-aminoterephthalic acid Examples include a sex metal complex.
  • the BET specific surface area varies depending on the synthesis method and purity, but in order to impart the flexibility of the adsorption sheet, the relative pressure is 0.5 at 25 ° C.
  • the water adsorption rate in the above is preferably 30% by mass or more, more preferably 35% by mass or more, and further preferably 40% by mass or more. If it is less than 30% by mass, it is necessary to increase the content of the organic binder in order to impart sufficient flexibility to the adsorption sheet. If the content of the organic binder is high, the side chains and the like of the organic binder are often adsorbed in the pores of the adsorbent, and as a result, sufficient adsorption performance cannot be exhibited.
  • the content of the porous metal complex in the adsorption sheet of the present invention is preferably 60% by mass to 85% by mass, more preferably 65% by mass to 80% by mass. If the content is less than 60% by mass, it may be difficult to obtain sufficient adsorption performance. On the other hand, if the content exceeds 85% by mass, it becomes difficult to sufficiently support the porous metal complex on the adsorption sheet, and the amount of shedding increases. In addition, the sheet strength may be significantly reduced.
  • the fiber diameter of the non-fibrilized fiber is preferably 5 ⁇ m or more, and more preferably 5 ⁇ m to 30 ⁇ m.
  • the fiber length is preferably 1 mm to 10 mm, more preferably 2 mm to 8 mm. If the fiber diameter of the thick fiber is less than 5 ⁇ m and the fiber length is less than 1 mm, the strength of the sheet decreases, it is difficult to maintain the step shape by itself after the step processing, and it is processed into a honeycomb-shaped adsorption element in the post processing. This is because it becomes impossible. Further, if the fiber diameter of the non-fibrillated fiber exceeds 30 ⁇ m and the fiber length exceeds 10 mm, the fiber is inflexible and difficult to process. Further, fibers having different fiber diameters may be mixed.
  • non-fibrillated fibers include inorganic fibers such as glass fibers, ceramic fibers and rock wool fibers; synthetic fibers such as aramid fibers, meta-aramid fibers, polybenzimidazole fibers, polyether ketone fibers, polyethylene terephthalate fibers and nylon fibers; Examples include semi-synthetic fibers such as acetate fibers and triacetate fibers; rayon fibers; regenerated fibers such as cupra fibers; and plant fibers such as cotton, hemp, and wood-based fibers. One or more of these can be used.
  • the fibrillated fiber examples include pulp and the like in addition to the fibrillated fiber described above. One or more of these can be used.
  • the method of fibrillation is not particularly limited, and a normal beating method can be adopted. A typical example is a method of fibrilizing using a beating machine such as a beater or a refiner. Further, the fibrilized fiber is preferably 50 ml or more and less than 800 ml when the Canadian standard drainage degree (CSF) according to JIS P 811-2 is measured.
  • CSF Canadian standard drainage degree
  • the total content of the non-fibrillated fibers and the fibrillated fibers in the adsorption sheet of the present invention is preferably 5% by mass to 25% by mass, more preferably 10% by mass to 25% by mass. If the content is less than 5% by mass, it becomes difficult to sufficiently support the porous metal complex on the adsorption sheet, the amount of falling off may increase, and the strength of the sheet may be significantly reduced. On the other hand, if the content exceeds 25% by mass, it may be difficult to obtain sufficient adsorption performance.
  • the adsorption sheet in the present invention contains an organic binder. This is because the flexibility and strength of the adsorption sheet are improved.
  • the organic binder is not particularly limited as long as it can bond the porous metal complex and the fiber.
  • polyvinyl alcohol-based polymers, polyacrylonitrile-based polymers, polyethylene-based polymers, polyester-based polymers, polyphenylene ether-based polymers, and the like can be used. From the viewpoint of handleability, a polyvinyl alcohol-based polymer is preferable.
  • the mode of use of the organic binder is not particularly limited, but it is preferable to use a fibrous binder because an adsorption sheet can be easily produced.
  • the content of the organic binder in the adsorption sheet is preferably 3% by mass to 15% by mass, more preferably 4% by mass to 12% by mass. If it is less than 3% by mass, the supportability of the porous metal complex and the flexibility of the sheet are insufficient, and if it exceeds 15% by mass, the porous metal complex is coated with the organic binder, and it tends to be difficult to obtain sufficient adsorption performance. There is.
  • the dissolution temperature of the organic binder in water is preferably 65 ° C to 100 ° C, more preferably 70 ° C to 100 ° C. If the dissolution temperature in water is less than 65 ° C., the proportion of the binder side chain entering the pores of the porous metal complex increases, and as a result, the adsorption performance may be insufficient. Further, if the temperature is higher than 100 ° C., there is a problem that the supportability is lacking due to insufficient adhesion.
  • the dissolution temperature of the organic binder in water can be measured by a usual method. For example, 100 ml of pure water is placed in a beaker and stirred, heated in an oil bath until the water temperature reaches 50 ° C., 0.5 g of an organic binder is added thereto, and the water temperature is raised at a heating rate of 2 ° C./min. , There is a method of visually measuring the temperature when the binder begins to melt and becomes translucent.
  • the adsorption sheet of the present invention exhibits supportability due to the fibrillated fibers even if the content of the organic binder is small, and exhibits the flexibility of the adsorption sheet due to the high water adsorption rate of the porous metal complex. As a result, it is possible to exhibit sufficient adsorption performance due to the small amount of organic binder and the high adsorption performance of the porous metal complex itself.
  • the adsorption sheet of the present invention preferably has a specific tensile elongation of 5% ⁇ m / g or more as an index of flexibility. If it is less than 5% m / g, the sheet lacks flexibility and cracks occur during honeycomb processing (step processing).
  • the adsorption sheet of the present invention may contain one or more types of porous metal complexes, and may further contain a porous material other than the porous metal complex.
  • the porous material contained in the adsorption sheet of the present invention is not particularly limited, but for example, organic highs such as activated carbon, zeolite, silica gel, activated alumina, aluminophosphate, silicoaluminolic acid, and styrene-divinylbenzene copolymer. Examples include molecular porous materials. Preferred are activated carbon, zeolite, silica gel, and activated alumina, which are inexpensively available.
  • the thickness of the adsorption sheet of the present invention is preferably 0.1 mm to 0.9 mm, more preferably 0.1 mm to 0.7 mm. If the thickness is less than 0.1 mm, the sheet strength is remarkably lowered, so that it may be difficult to process the adsorption element into a honeycomb shape or the like in the post-processing. Further, if the thickness is larger than 0.9 mm, the pressure loss of the suction element when the suction sheet is processed into a honeycomb shape or the like tends to be high.
  • the basis weight of the adsorption sheet of the present invention is preferably 25 g / m 2 to 200 g / m 2. More preferably, it is 40 g / m 2 to 150 g / m 2 . If the basis weight is less than 25 g / m 2 , the thickness of the sheet may become thin and the sheet strength may be significantly reduced, which may make it difficult to process the adsorption element such as a honeycomb shape in the post-processing. Further, if the basis weight exceeds 200 g / m 2 , the thickness of the sheet may become too large, and the pressure loss of the suction element when processed into a honeycomb shape or the like may increase.
  • the method for producing the adsorption sheet of the present invention is not particularly limited, and a conventionally known processing method can be used.
  • a wet sheeting method obtained by dispersing the porous metal complex, the fiber, and the organic binder in water, an organic solvent, or a mixture thereof, forming, dehydrating, and drying the mixture can be mentioned.
  • the porous metal complex is mixed with the above-mentioned sheet constituent material in a state of having solvent molecules in its pores and subjected to the sheet forming step. If the porous metal complex does not have solvent molecules in the pores, the organic binder constituting the adsorption sheet may be adsorbed in the pores. In this case, it is difficult to remove the organic binder trapped in the pores of the porous metal complex even if the solvent removal treatment described later is carried out after the sheet is formed, resulting in inferior adsorption performance of the adsorption sheet.
  • the solvent molecules in the pores of the porous metal complex by adsorbing the solvent molecules in the pores of the porous metal complex, the adsorption of the organic binder or the like in the pores in the sheeting step is prevented, and after the sheeting step, the solvent is removed, which will be described later.
  • the solvent molecules By removing the solvent molecules from the pores by the treatment, the adsorption performance of the adsorption sheet is ensured.
  • solvent molecules are adsorbed in the pores of the porous metal complex, but when the porous metal complex does not have solvent molecules in the pores or solvent molecules.
  • the organic solvent can be adsorbed in the pores by the method described in Examples described later.
  • the solvent molecule refers to water or a general organic solvent molecule.
  • a solvent removal treatment step of removing the solvent contained in the adsorption sheet is carried out after the sheet forming step.
  • the porous metal complex is preferably sheeted with solvent molecules in its pores, and in this case, sufficient adsorption performance can be obtained by the solvent molecules in the pores of the porous metal complex. It's hard to get rid of. Therefore, in order to develop the adsorption performance, the solvent removal treatment is carried out after the sheeting step.
  • the timing of the desolvation treatment is not particularly limited as long as it is after the sheeting step.
  • the conditions for the desolvation treatment are not particularly specified, but the temperature is preferably 50 ° C. to 300 ° C. If the temperature is lower than 50 ° C., the removal of the solvent may be incomplete, and it may be difficult to obtain sufficient adsorption performance. On the other hand, if the temperature exceeds 300 ° C., the pore structure of the porous metal complex may be broken, and in this case as well, it becomes difficult to obtain sufficient adsorption performance. More preferably, it is 80 ° C. to 200 ° C. Further, the solvent can be removed more efficiently by carrying out the desolvation treatment under reduced pressure. At this time, the pressure is not particularly limited and may be appropriately adjusted according to the physical properties and the blending amount of the porous metal complex.
  • the desolvation treatment time is also not particularly limited, but is preferably 1 hour to 100 hours, more preferably 3 hours to 48 hours, and further preferably 3 hours to 24 hours.
  • the most preferable desolvation treatment conditions are 80 ° C. to 200 ° C. for 3 hours to 24 hours under vacuum conditions.
  • the adsorption sheet of the present invention may be used in a flat plate shape, or may be appropriately subjected to pleating, honeycomb processing, corrugated processing, or the like to be used as a desired shape.
  • FIG. 1 shows a single-stage sheet obtained by processing the suction sheet 1 into a corrugated shape as an example of processing the suction sheet of the present invention.
  • pleating, honeycombing, and corrugating require a step of bending the sheet during processing, and at that time, the flexibility of the sheet is exhibited by sufficiently adsorbing water to the porous metal complex before processing. Will be done.
  • the method for adsorbing water to the porous metal complex is not particularly specified, but a method such as using a humidified room or processing while spraying steam is convenient and preferable.
  • the adsorption element of the present invention is characterized by including the above-mentioned adsorption sheet of the present invention.
  • the type of the adsorption element of the present invention is not particularly limited, and any conventionally known type can be adopted and may be appropriately selected depending on the intended use and purpose.
  • the shape of the suction sheet provided in the suction element of the present invention is not particularly limited, but for example, a suction sheet processed into a flat plate shape, a pleated shape, a honeycomb shape, or the like can be used.
  • the pleated adsorption sheet is used as a orthogonal flow type adsorption element
  • the honeycomb-shaped adsorption sheet is used as a parallel flow type adsorption element.
  • the adsorption sheet provided in the adsorption element is a honeycomb. It is preferably shaped.
  • FIG. 2 shows a diagram of a suction rotor 2 in which the suction sheet of the present invention is wound in a rotor shape as an example of the suction element of the present invention.
  • the suction sheet provided in the suction rotor 2 has a honeycomb shape.
  • the adsorption sheet of the present invention and the adsorption element provided with the adsorption sheet are discharged from factories, etc. for the purpose of reducing malodorous components, etc. in indoors, in vehicles, wallpaper, furniture, interior materials, resin molded products, electrical equipment, etc. It can be widely used for the purpose of separating / recovering organic solvents in the air, or controlling humidity / desiccant.
  • the present invention also relates to an adsorption / desorption processing apparatus including the adsorption element of the present invention, an adsorption means for introducing an adsorption target substance into the adsorption element and adsorbing the substance, and a desorption means for desorbing the adsorption target substance adsorbed by the adsorption element.
  • adsorption means a pipe or the like for introducing air or gas containing a malodorous substance such as an organic solvent or a substance to be adsorbed such as moisture can be considered.
  • a method for desorbing the substance to be adsorbed there are a method of heating and a method of lowering the pressure of the system, and as a desorption means, a tube for introducing a heating gas, a heater, a decompressor, or the like can be considered.
  • a means for introducing heated air is desirable from the viewpoint of desorption efficiency and economy.
  • FIG. 3 shows a desiccant air conditioning system 11 as an example of the suction / desorption processing device of the present invention.
  • the desiccant air conditioning system 11 includes a suction type rotor 2, a motor 3, a heat source 8 such as a heater, a fan 9, and a dehumidifying / humidifying area dividing member 10.
  • a suction type rotor 2 such as a suction type rotor 2
  • a heat source 8 such as a heater, a fan 9, and a dehumidifying / humidifying area dividing member 10.
  • the desiccant air conditioning system 11 when the high-humidity gas 4 containing water as the substance to be adsorbed is introduced, the water is adsorbed by the adsorption rotor 2 and discharged as the gas 5 after dehumidification.
  • the suction / desorption treatment device of the present invention can be applied to both a desiccant air conditioning system for factories and a desiccant air conditioning system for home use.
  • the water adsorption rate [%] is calculated by the following formula (i) from the water adsorption amount [g] per 1 g of the porous metal complex at a relative pressure of 0.5.
  • Moisture adsorption rate [%] Moisture adsorption amount per 1 g of adsorbent [g] ⁇ 100 ... (i)
  • the porosity is calculated by the following formula (iii) based on the BET specific surface area [m 2 / g] of the porous metal complex.
  • Porosity [%] ⁇ BET specific surface area of adsorption sheet [m 2 / g] x 100 / (porosity of porous metal complex in adsorption sheet) ⁇ / (BET specific surface area of porous metal complex sample [m] 2 / g]) ⁇ 100 ...
  • an amount of water vapor adsorption of 410 ml / g or more is evaluated as ⁇ (good), a value larger than 400 ml / g and less than 410 ml / g is evaluated as ⁇ (possible), and 400 ml / g or less is evaluated as ⁇ (defective).
  • the adsorption sheet sample is made to have a width of 30 cm and a length of 30 cm, and is theoretically passed through a corrugated processing machine capable of producing a corrugated paper having a width of 30 cm and a length of 21.4 cm. Then, after the corrugated adsorption sheet was allowed to stand for 24 hours at 22 ° C. in a 40% RH atmosphere, the recovery rate of the length was less than 20% (good) and 20% to less than 50% (good). Yes), 50% to 100% is evaluated as x (defective).
  • Example 1 And Fe (NO 3) 3 ⁇ 9H 2 O16.2g (40mmol) and trimesic acid 7.5 g (36 mmol) was dissolved in water 32 ml, was synthesized porous metal complex was heated for 15 hours at 95 ° C.. As a result of evaluating the physical properties of the obtained porous metal complex by nitrogen adsorption measurement and water vapor adsorption measurement, the BET specific surface area was 1575 m 2 / g and the water adsorption rate was 53%. Then, the synthesized porous metal complex was immersed in water for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores.
  • This porous metal complex sample is 80% by mass (excluding solvent molecules), aramid fiber is 8% by mass as non-fibrillated fiber, aramid fiber is 5% by mass as fibrillated fiber, and the dissolution temperature in water is 70 as an organic binder.
  • Polyvinyl alcohol (PVA) fibers at ° C (catalog value) are mixed at a ratio of 7% by mass, and adsorbed using a wet paper machine (manufactured by Toyo Boseki Engineering Co., Ltd., the same applies hereinafter) at a mass of 100 g / m 2 basis weight.
  • a sheet was prepared. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • Example 2 80% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 10% by mass of aramid fibers as unfibrillated fibers, and 3% by mass of aramid fibers as fibrillated fibers.
  • organic binder polyvinyl alcohol (PVA) fibers having a dissolution temperature of 70 ° C. (catalog value) in water are mixed at a ratio of 7% by mass, and an adsorption sheet is prepared using a wet paper machine at a mass of 100 g / m 2 basis weight. Made. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • PVA polyvinyl alcohol
  • Example 3 80% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 8% by mass of aramid fibers as unfibrillated fibers, and 7% by mass of aramid fibers as fibrillated fibers.
  • an organic binder polyvinyl alcohol (PVA) fibers having a dissolution temperature of 70 ° C. (catalog value) in water are mixed at a ratio of 5% by mass, and an adsorption sheet is prepared using a wet paper machine at a mass of 100 g / m 2 basis weight. Made. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • PVA polyvinyl alcohol
  • Example 4 80% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 8% by mass of aramid fibers as unfibrillated fibers, 9% by mass of aramid fibers as fibrillated fibers,
  • an organic binder polyvinyl alcohol (PVA) fibers having a dissolution temperature of 70 ° C. (catalog value) in water are mixed at a ratio of 3% by mass, and an adsorption sheet is prepared using a wet paper machine at a mass of 100 g / m 2 basis weight. Made. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • PVA polyvinyl alcohol
  • Example 5 75% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 10% by mass of aramid fiber as a non-fibrillated fiber, and 6.3% by mass of aramid fiber as a fibrillated fiber.
  • % Polyvinyl alcohol (PVA) fiber having a dissolution temperature in water of 70 ° C. (catalog value) as an organic binder is mixed at a ratio of 8.7% by mass, and a wet papermaking apparatus is used at a mass of 100 g / m 2 basis weight.
  • a suction sheet was prepared for use. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • Example 6 70% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 12% by mass of aramid fiber as a non-fibrillated fiber, and 7.5% by mass of aramid fiber as a fibrillated fiber.
  • % Polyvinyl alcohol (PVA) fiber having a dissolution temperature in water of 70 ° C. (catalog value) as an organic binder is mixed at a ratio of 10.5% by mass, and a wet papermaking apparatus is used at a mass of 100 g / m 2 basis weight.
  • a suction sheet was prepared for use. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • Example 7 65% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 14% by mass of aramid fiber as a non-fibrillated fiber, and 8.8% by mass of aramid fiber as a fibrillated fiber.
  • % Polyvinyl alcohol (PVA) fiber having a dissolution temperature in water of 70 ° C. (catalog value) as an organic binder is mixed at a ratio of 12.2% by mass, and a wet papermaking apparatus is used at a mass of 100 g / m 2 basis weight.
  • a suction sheet was prepared for use. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • Example 8 65% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 14% by mass of aramid fiber as a non-fibrillated fiber, and 8.8% by mass of aramid fiber as a fibrillated fiber.
  • % Polyvinyl alcohol (PVA) fiber having a dissolution temperature in water ⁇ 99 ° C. (catalog value indicating the case where it starts to dissolve before boiling of water) as an organic binder is mixed at a ratio of 12.2% by mass, and the basis weight is 100 g.
  • a suction sheet was prepared using a wet paper making device with a mass of / m 2. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • Example 9 80% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 8% by mass of rayon fiber as a non-fibrillated fiber, 5% by mass of rayon fiber as a fibrillated fiber,
  • an organic binder polyvinyl alcohol (PVA) fibers having a dissolution temperature of 70 ° C. (catalog value) in water are mixed at a ratio of 7% by mass, and an adsorption sheet is prepared using a wet papermaking device at a mass of 100 g / m 2 basis weight.
  • the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample.
  • the supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • Example 10 80% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 8% by mass of PET fiber as a non-fibrillated fiber, 5% by mass of aramid fiber as a fibrillated fiber,
  • organic binder polyvinyl alcohol (PVA) fibers having a dissolution temperature of 70 ° C. (catalog value) in water are mixed at a ratio of 7% by mass, and an adsorption sheet is prepared using a wet paper machine at a mass of 100 g / m 2 basis weight. Made. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • PVA polyvinyl alcohol
  • Basolite C300 manufactured by BASF was used as the porous metal complex.
  • the BET specific surface area was 1609 m 2 / g and the water adsorption rate was 43%.
  • the porous metal complex was immersed in N, N-dimethylformaldehyde for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores.
  • This porous metal complex sample is 80% by mass (excluding solvent molecules), aramid fiber is 8% by mass as non-fibrillated fiber, aramid fiber is 5% by mass as fibrillated fiber, and the dissolution temperature in water is 70 as an organic binder.
  • Polyvinyl alcohol (PVA) fibers at ° C. (catalog value) were mixed at a ratio of 7% by mass to prepare an adsorption sheet using a wet paper machine at a mass of 100 g / m 2 basis weight. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • Example 12 3 ml (10 mmol) of tetraisopropyl orthotitate and 2.5 g (15 mmol) of terephthalic acid were dissolved in 45 ml of N, N-dimethylformaldehyde and 5 ml of methanol, and heated at 150 ° C. for 15 hours to synthesize a porous metal complex.
  • the BET specific surface area was 1199 m 2 / g and the water adsorption rate was 38%.
  • the synthesized porous metal complex was immersed in N, N-dimethylformaldehyde for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores.
  • This porous metal complex sample is 80% by mass (excluding solvent molecules)
  • aramid fiber is 8% by mass as non-fibrillated fiber
  • aramid fiber is 5% by mass as fibrillated fiber
  • the dissolution temperature in water is 70 as an organic binder.
  • Polyvinyl alcohol (PVA) fibers at ° C. (catalog value) were mixed at a ratio of 7% by mass to prepare an adsorption sheet using a wet paper machine at a mass of 100 g / m 2 basis weight.
  • the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample.
  • the supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • Example 13 5.3 g (22.7 mmol) of zirconium chloride and 3.78 g (22.8 mmol) of terephthalic acid were dissolved in 500 ml of N, N-dimethylformaldehyde and heated at 120 ° C. for 24 hours to synthesize a porous metal complex.
  • the BET specific surface area was 1283 m 2 / g and the water adsorption rate was 42%.
  • the synthesized porous metal complex was immersed in water for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores.
  • This porous metal complex sample is 80% by mass (excluding solvent molecules), aramid fiber is 8% by mass as non-fibrillated fiber, aramid fiber is 5% by mass as fibrillated fiber, and the dissolution temperature in water is 70 as an organic binder.
  • Polyvinyl alcohol (PVA) fibers at ° C. (catalog value) were mixed at a ratio of 7% by mass to prepare an adsorption sheet using a wet paper machine at a mass of 100 g / m 2 basis weight. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • Example 14 The porous metal complex sample obtained in the same manner as in Example 14 was 80% by mass (excluding solvent molecules), 9.2% by mass of aramid fiber as a non-fibrillated fiber, and aramid fiber as a fibrillated fiber.
  • a wet paper making device in which polyvinyl alcohol (PVA) fibers having a dissolution temperature of 70 ° C. (catalog value) in water are mixed at a ratio of 5% by mass as an organic binder at a ratio of 8% by mass to a basis weight of 100 g / m 2.
  • a suction sheet was prepared using. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • Example 15 ZrOCl 2 ⁇ 8H 2 O200g and (0.62 mol) of fumaric acid 72 g (0.62 mol) N, was dissolved in N- dimethylformamide 2L and 700mL formic acid, was synthesized porous metal complex was heated for 6 hours at 130 ° C. ..
  • the BET specific surface area was 884 m 2 / g and the water adsorption rate was 33%. Then, the synthesized porous metal complex was immersed in water for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores.
  • This porous metal complex sample is 80% by mass (excluding solvent molecules), aramid fiber is 8% by mass as non-fibrillated fiber, aramid fiber is 5% by mass as fibrillated fiber, and the dissolution temperature in water is 70 as an organic binder.
  • Polyvinyl alcohol (PVA) fibers at ° C. (catalog value) were mixed at a ratio of 7% by mass to prepare an adsorption sheet using a wet paper machine at a mass of 100 g / m 2 basis weight. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • Example 16 12.87 g (55.2 mmol) of zirconium chloride and 9.45 g (52.5 mmol) of 2-aminoterephthalic acid are dissolved in 600 mL of N, N-dimethylformaldehyde and heated at 120 ° C. for 24 hours to synthesize a porous metal complex. did.
  • the BET specific surface area was 949 m 2 / g and the water adsorption rate was 32%.
  • the synthesized porous metal complex was immersed in water for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores.
  • This porous metal complex sample is 80% by mass (excluding solvent molecules)
  • aramid fiber is 8% by mass as non-fibrillated fiber
  • aramid fiber is 5% by mass as fibrillated fiber
  • the dissolution temperature in water is 70 as an organic binder.
  • Polyvinyl alcohol (PVA) fibers at ° C. (catalog value) were mixed at a ratio of 7% by mass to prepare an adsorption sheet using a wet paper machine at a mass of 100 g / m 2 basis weight.
  • the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample.
  • the supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • Example 17 3.6 ml (12.3 mmol) of tetraisopropyl orthotitanium and 3.6 g (19.9 mmol) of 2-aminoterephthalic acid were dissolved in 48 ml of N, N-dimethylformamide and 12 ml of methanol, and heated at 150 ° C. for 18 hours. A porous metal complex was synthesized. As a result of evaluating the physical properties of the obtained porous metal complex by nitrogen adsorption measurement and water vapor adsorption measurement, the BET specific surface area was 1248 m 2 / g and the water adsorption rate was 43%.
  • the synthesized porous metal complex was immersed in water for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores.
  • This porous metal complex sample is 80% by mass (excluding solvent molecules)
  • aramid fiber is 8% by mass as non-fibrillated fiber
  • aramid fiber is 5% by mass as fibrillated fiber
  • the dissolution temperature in water is 70 as an organic binder.
  • Polyvinyl alcohol (PVA) fibers at ° C. (catalog value) were mixed at a ratio of 7% by mass to prepare an adsorption sheet using a wet paper machine at a mass of 100 g / m 2 basis weight.
  • the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample.
  • the supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • the BET specific surface area was 639 m 2 / g and the water adsorption rate was 17%.
  • the synthesized porous metal complex was immersed in water for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores.
  • As an organic binder polyvinyl alcohol (PVA) fibers having a dissolution temperature in water of 60 ° C. (catalog value) are mixed at a ratio of 7% by mass, and an adsorption sheet is prepared using a wet paper machine at a mass of 100 g / m 2 basis weight. Made. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • PVA polyvinyl alcohol
  • the (PVA) fiber was mixed at a ratio of 7% by mass, and a suction sheet was prepared using a wet paper machine at a mass of 100 g / m 2 basis weight. In this comparative example, non-fibrillated fibers were not used.
  • the adsorption sheet prepared above was further desolvated for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • Polyvinyl alcohol (PVA) fibers were mixed at a ratio of 7% by mass to prepare an adsorption sheet using a wet paper machine at a mass of 100 g / m 2 basis weight. In this comparative example, fibrillated fibers were not used.
  • the adsorption sheet prepared above was further desolvated for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
  • A-type silica gel (manufactured by Toyota Kako Co., Ltd.) was used as an adsorbent.
  • the BET specific surface area was 820 m 2 / g and the water adsorption rate was 25%. Then, the adsorbent was immersed in water for 24 hours and then filtered to obtain an adsorbent sample in which solvent molecules were adsorbed in the pores.
  • Tables 1 to 5 show the measurement results of the adsorption sheet samples obtained in Examples 1 to 17 and Comparative Examples 1 to 6.
  • the adsorption sheets of Examples 1 to 17 are excellent in the supportability of the porous metal complex, the flexibility and processability of the sheet, and have sufficient adsorption performance. Understand.
  • the adsorption sheet, adsorption element, and adsorption / desorption treatment device of the present invention it becomes possible to efficiently separate, recover, or adsorb and remove water, organic solvent, and substances to be adsorbed such as malodorous components. Therefore, it can be expected to greatly contribute to the industrial world.
  • Adsorption sheet 2 Adsorption rotor
  • 3 Motor
  • 4 High humidity gas
  • 5 Gas after dehumidification
  • 6 Low humidity gas
  • 7 Gas after humidification
  • 8 Heat source
  • Fan 10 Dehumidifying / humidifying area dividing member
  • 11 Desiccant air conditioning system

Abstract

An adsorbent sheet of the present invention comprises: a porous metal complex comprising a metal and an organic ligand and having a water adsorption ratio of 30% by mass or more at 25°C under a relative pressure of 0.5; and a non-fibrillated fiber and a fibrillated fiber. The adsorbent sheet is excellent in the property of supporting the porous metal complex and the flexibility/processability of the sheet, and can exert sufficient adsorption performance.

Description

吸着シート、吸着エレメント、およびそれを用いた吸着処理装置Adsorption sheet, adsorption element, and adsorption processing device using it
 本発明は、水分、有機溶剤、悪臭成分等の吸着対象物質を効率的に分離回収または吸着除去する吸着シート、吸着エレメント、およびそれを用いた吸着処理装置に関するものである。 The present invention relates to an adsorption sheet, an adsorption element, and an adsorption treatment apparatus using the adsorption sheet, which efficiently separates, recovers, or adsorbs and removes substances to be adsorbed such as moisture, organic solvent, and malodorous components.
 活性炭やシリカゲル、ゼオライト等といった多孔質材料は、脱臭、空気や水の浄化、ガスの分離・精製といった種々な用途に利用されており、現代の生活に必要不可欠な材料となっている。近年、種々の配位形態を取り得る金属イオンと2座以上の配位座を有する架橋配位子とを組み合わせて自己集合させた多孔質材料、すなわち、多孔性金属錯体(MOF)、または、多孔性配位高分子(PCP)と呼ばれる新しい多孔質材料が見出された。これら多孔性金属錯体は、活性炭やシリカゲル、ゼオライト等の従来の多孔質材料にはない特徴である、高比表面積、シャープな細孔分布、および、高い構造設計性という特徴を有しており、注目されている。 Porous materials such as activated carbon, silica gel, and zeolite are used for various purposes such as deodorization, purification of air and water, and separation / purification of gas, and are indispensable materials for modern life. In recent years, a porous material in which a metal ion capable of taking various coordination forms and a bridging ligand having two or more coordinations are combined and self-assembled, that is, a porous metal complex (MOF), or a porous metal complex (MOF), or A new porous material called Porous Coordination Polymer (PCP) has been discovered. These porous metal complexes have features such as high specific surface area, sharp pore distribution, and high structural design, which are features not found in conventional porous materials such as activated carbon, silica gel, and zeolite. Attention has been paid.
 このような多孔性金属錯体として、例えば、特許文献1には、特定のジカルボン酸金属錯体がガス吸蔵材、特にメタンを主成分とするガスの吸蔵材として好適であることが開示されている。また、特許文献2には、銅イオンとトリメシン酸類から合成された多孔性金属錯体が開示されており、吸着材がその用途の一例として開示されている。さらに、特許文献3には、金属クロムまたはクロム塩と、トリメシン酸類から得られる多孔性金属錯体が、特に水蒸気吸着材として優れていることが開示されている。 As such a porous metal complex, for example, Patent Document 1 discloses that a specific dicarboxylic acid metal complex is suitable as a gas occlusion material, particularly a gas occlusion material containing methane as a main component. Further, Patent Document 2 discloses a porous metal complex synthesized from copper ions and trimesic acids, and an adsorbent is disclosed as an example of its use. Further, Patent Document 3 discloses that a metal chromium or a chromium salt and a porous metal complex obtained from trimesic acids are particularly excellent as a water vapor adsorbent.
 このように多孔性金属錯体は、様々なガスに対応する吸着材としての可能性を秘めている。吸着材として利用する場合には、粉体として存在する多孔性金属錯体を動作流体と圧力損失が少なく接触できるよう、利用に適した吸着エレメントに成形することが好ましく、そのためにはシート化する技術を確立することが重要となってくる。 In this way, the porous metal complex has the potential as an adsorbent for various gases. When used as an adsorbent, it is preferable to mold the porous metal complex existing as powder into an adsorbent element suitable for use so that it can come into contact with the operating fluid with little pressure loss. It becomes important to establish.
 そこで、特許文献4では、多孔性金属錯体を含有したシートとして、多孔性金属錯体と耐熱性繊維、および自己固結性を有する粘土鉱物繊維、並びに有機バインダーを含有する吸着シートが開示されている。 Therefore, Patent Document 4 discloses an adsorption sheet containing a porous metal complex, a heat-resistant fiber, a self-consolidating clay mineral fiber, and an organic binder as a sheet containing the porous metal complex. ..
日本国特許公開公報「特開2001-348361号」Japanese Patent Publication "Japanese Patent Laid-Open No. 2001-348361" 日本国特許公開公報「特開2000-327628号」Japanese Patent Publication "Japanese Patent Laid-Open No. 2000-327628" 日本国特許公開公報「特開2007-51112号」Japanese Patent Publication "Japanese Patent Laid-Open No. 2007-51112" 日本国特許公開公報「特開2013-154301号」Japanese Patent Publication "Japanese Patent Laid-Open No. 2013-154301"
 ところが、特許文献4に開示の吸着シートは、粘土鉱物繊維を必須とし、その分、耐熱性繊維含有比率を減らしていので、シート自体のコシがなく、例えばフィルターにする際のハニカム加工時に段が付かない等の問題がある。 However, the adsorption sheet disclosed in Patent Document 4 requires clay mineral fibers, and the heat-resistant fiber content ratio is reduced by that amount. Therefore, the sheet itself is not stiff, and for example, a step is formed during honeycomb processing when making a filter. There are problems such as not sticking.
 そこで、本発明は、多孔性金属錯体の担持性、および、シートの柔軟性・加工性に優れており、かつ十分な吸着性能を有する吸着シート、吸着エレメント、およびそれを用いた吸脱着処理装置の提供を課題として掲げる。 Therefore, the present invention relates to an adsorption sheet, an adsorption element, and an adsorption / desorption treatment apparatus using the adsorption sheet, which is excellent in the supportability of the porous metal complex and the flexibility and processability of the sheet, and has sufficient adsorption performance. Is raised as an issue.
 本発明者らは上記の課題を解決するために、鋭意研究した結果、遂に本発明を完成するに到った。すなわち本発明は、以下の構成である。
[1]金属および有機配位子を有し、25℃、相対圧0.5での水分吸着率が30質量%以上である多孔性金属錯体と、フィブリル化していない繊維およびフィブリル化した繊維と、を含有することを特徴とする吸着シート。
[2]水中溶解温度が65℃~100℃の有機バインダーを含有することを特徴とする上記1の吸着シート。
[3]前記比引張伸度が5%・m/g以上であることを特徴とする、上記1または2の吸着シート。
[4]前記多孔性金属錯体を60~85質量%含有することを特徴とする、上記1から3のいずれか1つの吸着シート。
[5]上記1から4のいずれか1つの吸着シートを備えることを特徴とする吸着エレメント。
[6]上記5の吸着エレメントと、前記吸着エレメントに吸着対象物質を導入して吸着させる吸着手段と、前記吸着エレメントが吸着した吸着対象物質を脱着させる脱着手段と、を備え、吸着対象物質の吸脱着を連続的に行う吸脱着処理装置。
As a result of diligent research in order to solve the above problems, the present inventors have finally completed the present invention. That is, the present invention has the following configuration.
[1] A porous metal complex having a metal and an organic ligand and having a water adsorption rate of 30% by mass or more at 25 ° C. and a relative pressure of 0.5, and non-fibrillated fibers and fibrillated fibers. An adsorption sheet characterized by containing,.
[2] The adsorption sheet according to 1 above, which contains an organic binder having a dissolution temperature in water of 65 ° C. to 100 ° C.
[3] The adsorption sheet of 1 or 2 above, wherein the specific tensile elongation is 5% · m / g or more.
[4] The adsorption sheet according to any one of 1 to 3 above, which contains 60 to 85% by mass of the porous metal complex.
[5] An adsorption element comprising any one of the above 1 to 4 adsorption sheets.
[6] The adsorption target substance is provided with the adsorption element of 5 above, an adsorption means for introducing and adsorbing the adsorption target substance into the adsorption element, and a desorption means for desorbing the adsorption target substance adsorbed by the adsorption element. An adsorption / desorption processing device that continuously performs adsorption / desorption.
 上記構成によると、多孔性金属錯体の担持性、および、シートの柔軟性・加工性に優れており、かつ十分な吸着性能を有する吸着シート等提供できる。 According to the above configuration, it is possible to provide an adsorption sheet or the like which is excellent in the supportability of the porous metal complex and the flexibility and processability of the sheet and has sufficient adsorption performance.
本発明の吸着シートをコルゲート状に加工した片段シートの一例を示す図である。It is a figure which shows an example of the single-stage sheet which processed the adsorption sheet of this invention into a corrugated shape. 本発明の吸着エレメントの一例を示す図である。It is a figure which shows an example of the adsorption element of this invention. 本発明の吸脱着処理装置の一例を示す図である。It is a figure which shows an example of the adsorption / desorption processing apparatus of this invention.
 以下、本発明を詳細に説明する。
 本発明の吸着シートは、金属および有機配位子を有し、25℃、相対圧0.5での水分吸着率が30質量%以上である多孔性金属錯体と、フィブリル化していない繊維およびフィブリル化した繊維と、を含有する。
 ここで、一定圧力下で吸着の進行が止まったように見える状態(吸着分子数=脱着分子数)のときの圧力を吸着平衡圧と言い、相対圧とは、吸着平衡圧と飽和蒸気圧の比を相対圧と言う。
Hereinafter, the present invention will be described in detail.
The adsorption sheet of the present invention contains a porous metal complex having a metal and an organic ligand and having a water adsorption rate of 30% by mass or more at 25 ° C. and a relative pressure of 0.5, and non-fibrillated fibers and fibrils. Containing the carbonized fiber.
Here, the pressure in a state where the progress of adsorption seems to have stopped under a constant pressure (the number of adsorbed molecules = the number of desorbed molecules) is called the adsorption equilibrium pressure, and the relative pressure is the adsorption equilibrium pressure and the saturated vapor pressure. The ratio is called relative pressure.
 本発明の吸着シートは、多孔性金属錯体を含有しているため高い吸着性能を得ることができる。かつ、この多孔性金属錯体は、25℃、相対圧0.5での水分吸着率が30質量%以上であることを特徴とするため、シート自体で水分を多く保持することができ、シート加工時の高い柔軟性が得られる。さらに、多孔性金属錯体により柔軟性を十分に発現できることから、従来、柔軟性の付与のために用いられてきた有機バインダーを削減することが可能であり、結果、吸着材の細孔内に有機バインダーの側鎖等が吸着する(細孔閉塞)割合を減らすことができ、さらに十分な吸着性能を得ることができる。水分吸着率が30質量%未満であれば、柔軟性に欠けることになる。 Since the adsorption sheet of the present invention contains a porous metal complex, high adsorption performance can be obtained. Moreover, since this porous metal complex is characterized in that the water adsorption rate at 25 ° C. and a relative pressure of 0.5 is 30% by mass or more, a large amount of water can be retained by the sheet itself, and the sheet can be processed. High flexibility of time is obtained. Furthermore, since the porous metal complex can sufficiently develop flexibility, it is possible to reduce the amount of organic binder conventionally used for imparting flexibility, and as a result, it is possible to reduce the amount of organic binder in the pores of the adsorbent. The rate of adsorption (porosity) of the side chains of the binder and the like can be reduced, and further sufficient adsorption performance can be obtained. If the water adsorption rate is less than 30% by mass, the flexibility will be lacking.
 さらに、本発明の吸着シートは、フィブリル化してない繊維およびフィブリル化した繊維を含む。フィブリル化していない繊維を含有することにより、例えば、段加工した場合でも自力で段形状を保持することが可能であり、加工性に優れる。また、フィブリル化した繊維を含有することにより、多孔性金属錯体粒子を効率よく保持でき、担持性に優れるだけではなく、従来、担持性の付与のために用いられてきた有機バインダーを削減することが可能である。その結果、細孔閉塞を減らすことができ、さらに十分な吸着性能を得ることができる。 Further, the adsorption sheet of the present invention contains non-fibrillated fibers and fibrillated fibers. By containing the fibers that are not fibrillated, for example, it is possible to maintain the step shape by itself even when step processing is performed, and the workability is excellent. Further, by containing the fibrillated fiber, the porous metal complex particles can be efficiently retained, and not only the supportability is excellent, but also the organic binder conventionally used for imparting the supportability can be reduced. Is possible. As a result, pore clogging can be reduced, and more sufficient adsorption performance can be obtained.
 さらに、本発明の吸着シートは、水中溶解温度が65℃~100℃と高融点の有機バインダーを含有していてもよい。水中溶解温度が65℃~100℃と高融点の有機バインダーを用いることで、より細孔閉塞を減らし、優れた吸着性能を得ることが可能である。水中溶解温度が65℃未満では細孔閉塞による吸着性能不十分となり、100℃より高温では接着不十分により担持性に欠けることになる。 Further, the adsorption sheet of the present invention may contain an organic binder having a melting point in water of 65 ° C. to 100 ° C. and a high melting point. By using an organic binder having a high melting point of 65 ° C. to 100 ° C. in water, it is possible to further reduce pore clogging and obtain excellent adsorption performance. If the dissolution temperature in water is less than 65 ° C., the adsorption performance will be insufficient due to pore clogging, and if the temperature is higher than 100 ° C., the adhesion will be insufficient and the supportability will be insufficient.
 本発明に係る多孔性金属錯体は、金属イオンと有機配位子を有する化合物とからなる多孔質材料である。使用可能な多孔性金属錯体の形態には特に定めがなく、粉末状、もしくは、粒状のものを用いることができる。好ましくは平均粒子径が0.1μm~200μmの多孔性金属錯体であり、より好ましくは1~100μmであり、もっとも好ましくは1~80μmである。平均粒子径が0.1μm未満では、吸着シート化中の歩留まりが低くなる原因となる。また、平均粒子径が200μmを超えると、吸着シートに、多孔性金属錯体を十分に担持させ難くなり、多孔性金属錯体の脱落が多くなる場合がある。平均粒子径は、例えば、走査型電子顕微鏡を用いて測定することができる。 The porous metal complex according to the present invention is a porous material composed of a metal ion and a compound having an organic ligand. The form of the porous metal complex that can be used is not particularly specified, and powder or granular ones can be used. It is preferably a porous metal complex having an average particle size of 0.1 μm to 200 μm, more preferably 1 to 100 μm, and most preferably 1 to 80 μm. If the average particle size is less than 0.1 μm, the yield during the adsorption sheet formation becomes low. On the other hand, if the average particle size exceeds 200 μm, it becomes difficult to sufficiently support the porous metal complex on the adsorption sheet, and the porous metal complex may come off more often. The average particle size can be measured using, for example, a scanning electron microscope.
 多孔性金属錯体の77K窒素吸着法によるBET比表面積は、特に限定されないが、例えば500m/g以上であることが好ましい。BET比表面積が500m/gより小さいと、十分な吸着性能を得難い場合がある。BET比表面積は1000m/g以上であるのがより好ましい。BET比表面積の上限は特に限定されないが、6000m/g以下であることが好ましい。この範囲を超えると、多孔性金属錯体の製造が非常に困難になるという不都合が生じるからである。なお、BET比表面積は、例えば、後段の実施例に記載の方法により測定することができる。 The BET specific surface area of the porous metal complex by the 77K nitrogen adsorption method is not particularly limited, but is preferably 500 m 2 / g or more, for example. If the BET specific surface area is smaller than 500 m 2 / g, it may be difficult to obtain sufficient adsorption performance. The BET specific surface area is more preferably 1000 m 2 / g or more. The upper limit of the BET specific surface area is not particularly limited, but is preferably 6000 m 2 / g or less. This is because if it exceeds this range, there is a disadvantage that the production of the porous metal complex becomes very difficult. The BET specific surface area can be measured, for example, by the method described in the subsequent examples.
 多孔性金属錯体を構成する金属イオンとしては、特に限定されないが、例えば、アルミニウムイオン等の典型金属元素、チタンイオン、ジルコニウムイオン、鉄イオン、銅イオン等の遷移金属元素が挙げられる。一方、配位子を有する化合物としては、例えば、フマル酸、2-アミノテレフタル酸、1,4-ナフタレンジカルボン酸、テレフタル酸及びトリメシン酸等が挙げられる。具体的な多孔性金属錯体としては、例えば、アルミニウムイオンとテレフタル酸から構成される多孔性金属錯体(BASF社製、Basolite A100)、銅イオンとトリメシン酸から構成される多孔性金属錯体(BASF社製、Basolite C300)、鉄イオンとトリメシン酸から構成される多孔性金属錯体(BASF社製、Basolite F300)、チタンイオンとテレフタル酸から構成される多孔性金属錯体、ジルコニウムイオンとテレフタル酸から構成される多孔性金属錯体、ジルコニウムイオンとフマル酸から構成される多孔性金属錯体、ジルコニウムイオンと2-アミノテレフタル酸から構成される多孔性金属錯体、チタンイオンと2-アミノテレフタル酸から構成される多孔性金属錯体、等が挙げられる。これらの多孔性金属錯体は同じ多孔性金属錯体であっても合成法や純度によりBET比表面積は様々であるが、吸着シートの柔軟性を付与させるためには、25℃、相対圧0.5での水分吸着率が30質量%以上であることが好ましく、35質量%以上であることがより好ましく、40質量%以上であることがさらに好ましい。30質量%未満の場合は、吸着シートに十分な柔軟性を付与するために、有機バインダーの含有量を多くする必要がある。有機バインダーの含有量が多いと、吸着材の細孔内に有機バインダーの側鎖等が吸着する割合が多く、結果、十分な吸着性能が発揮できない。 The metal ions constituting the porous metal complex are not particularly limited, and examples thereof include typical metal elements such as aluminum ions and transition metal elements such as titanium ions, zirconium ions, iron ions, and copper ions. On the other hand, examples of the compound having a ligand include fumaric acid, 2-aminoterephthalic acid, 1,4-naphthalenedicarboxylic acid, terephthalic acid, trimesic acid and the like. Specific examples of the porous metal complex include a porous metal complex composed of aluminum ions and terephthalic acid (Basolite A100 manufactured by BASF) and a porous metal complex composed of copper ions and trimesic acid (BASF). , Basolite C300), a porous metal complex composed of iron ions and trimesic acid (BASF, Basolite F300), a porous metal complex composed of titanium ions and terephthalic acid, and composed of zirconium ions and terephthalic acid. Porous metal complex, porous metal complex composed of zirconium ion and fumaric acid, porous metal complex composed of zirconium ion and 2-aminoterephthalic acid, porous metal complex composed of titanium ion and 2-aminoterephthalic acid Examples include a sex metal complex. Even if these porous metal complexes are the same porous metal complex, the BET specific surface area varies depending on the synthesis method and purity, but in order to impart the flexibility of the adsorption sheet, the relative pressure is 0.5 at 25 ° C. The water adsorption rate in the above is preferably 30% by mass or more, more preferably 35% by mass or more, and further preferably 40% by mass or more. If it is less than 30% by mass, it is necessary to increase the content of the organic binder in order to impart sufficient flexibility to the adsorption sheet. If the content of the organic binder is high, the side chains and the like of the organic binder are often adsorbed in the pores of the adsorbent, and as a result, sufficient adsorption performance cannot be exhibited.
 本発明の吸着シートにおける多孔性金属錯体の含有量は、60質量%~85質量%であるのが好ましく、より好ましくは65重量%~80質量%である。含有量が60質量%未満では十分な吸着性能を得ることが難しい場合がある。一方、含有量が85質量%を超えると、吸着シートに多孔性金属錯体を十分に担持することが困難になり、脱落量が多くなる。また、シート強度も著しく低下する恐れがある。 The content of the porous metal complex in the adsorption sheet of the present invention is preferably 60% by mass to 85% by mass, more preferably 65% by mass to 80% by mass. If the content is less than 60% by mass, it may be difficult to obtain sufficient adsorption performance. On the other hand, if the content exceeds 85% by mass, it becomes difficult to sufficiently support the porous metal complex on the adsorption sheet, and the amount of shedding increases. In addition, the sheet strength may be significantly reduced.
 フィブリル化していない繊維の繊維径は5μm以上であることが好ましく、5μm~30μmであることがより好ましい。また、繊維長は1mm~10mmであるのが好ましく、2mm~8mmであるのがより好ましい。太繊維の繊維径が5μm未満、繊維長が1mm未満ではシートの強度が低下し、段加工後に自力で段形状を保持することが難しく、また後加工においてハニカム状等の吸着エレメントに加工することができなくなるためである。また、フィブリル化していない繊維の繊維径が30μmを超え、かつ繊維長10mmを超えると、柔軟性がなく、加工しにくくなる。さらに繊維径が異なる繊維を混合してもよい。 The fiber diameter of the non-fibrilized fiber is preferably 5 μm or more, and more preferably 5 μm to 30 μm. The fiber length is preferably 1 mm to 10 mm, more preferably 2 mm to 8 mm. If the fiber diameter of the thick fiber is less than 5 μm and the fiber length is less than 1 mm, the strength of the sheet decreases, it is difficult to maintain the step shape by itself after the step processing, and it is processed into a honeycomb-shaped adsorption element in the post processing. This is because it becomes impossible. Further, if the fiber diameter of the non-fibrillated fiber exceeds 30 μm and the fiber length exceeds 10 mm, the fiber is inflexible and difficult to process. Further, fibers having different fiber diameters may be mixed.
 フィブリル化していない繊維としては、ガラス繊維、セラミック繊維、ロックウール繊維等の無機繊維;アラミド繊維、メタアラミド繊維、ポリベンズイミダゾール繊維、ポリエーテルケトン繊維、ポリエチレンテレフタレート繊維、ナイロン繊維等の合成繊維;、
アセテート繊維、トリアセテート繊維等の半合成繊維;、レーヨン繊維;キュプラ繊維等の再生繊維;、綿、麻、および木材を主成分とした繊維などの植物繊維が挙げられる。これらの中の1種又は2種以上を用いることができる。
Examples of non-fibrillated fibers include inorganic fibers such as glass fibers, ceramic fibers and rock wool fibers; synthetic fibers such as aramid fibers, meta-aramid fibers, polybenzimidazole fibers, polyether ketone fibers, polyethylene terephthalate fibers and nylon fibers;
Examples include semi-synthetic fibers such as acetate fibers and triacetate fibers; rayon fibers; regenerated fibers such as cupra fibers; and plant fibers such as cotton, hemp, and wood-based fibers. One or more of these can be used.
 フィブリル化した繊維としては、上述した繊維をフィブリル化した繊維に加え、パルプ等も挙げられる。これらの中の1種又は2種以上を用いることができる。フィブリル化の方法としては特に制限はなく、通常の叩解方法を採用することができる。代表的な例としては、ビーターやリファイナーなどの叩解機を用いてフィブリル化する方法が挙げられれる。また、フィブリル化した繊維は、JIS P 8121-2に準ずるカナダ標準濾水度(CSF)を測定した場合、50ml以上800ml未満であることが好ましい。 Examples of the fibrillated fiber include pulp and the like in addition to the fibrillated fiber described above. One or more of these can be used. The method of fibrillation is not particularly limited, and a normal beating method can be adopted. A typical example is a method of fibrilizing using a beating machine such as a beater or a refiner. Further, the fibrilized fiber is preferably 50 ml or more and less than 800 ml when the Canadian standard drainage degree (CSF) according to JIS P 811-2 is measured.
 本発明の吸着シートにおける、フィブリル化していない繊維およびフィブリル化した繊維の合計の含有量は、5質量%~25質量%であるのが好ましく、より好ましくは10重量%~25質量%である。含有量が5質量%未満では吸着シートに多孔性金属錯体を十分に担持することが困難となり、脱落量が多くなる、かつ、シートの強度が著しく低下する恐れがある。一方、含有量が25質量%を超えると、十分な吸着性能を得ることが難しい場合がある。 The total content of the non-fibrillated fibers and the fibrillated fibers in the adsorption sheet of the present invention is preferably 5% by mass to 25% by mass, more preferably 10% by mass to 25% by mass. If the content is less than 5% by mass, it becomes difficult to sufficiently support the porous metal complex on the adsorption sheet, the amount of falling off may increase, and the strength of the sheet may be significantly reduced. On the other hand, if the content exceeds 25% by mass, it may be difficult to obtain sufficient adsorption performance.
 本発明における吸着シートは、有機バインダーを含む。吸着シートの柔軟性や強度を向上させるからである。有機バインダーとしては、多孔性金属錯体と繊維とを接合できるものであれば特に限定されない。例えば、ポリビニルアルコール系ポリマー、ポリアクリロニトリル系ポリマー、ポリエチレン系ポリマー、ポリエステル系ポリマー、ポリフェニレンエーテル系ポリマー等を用いることができる。取り扱い性の面からは、ポリビニルアルコール系ポリマーが好ましい。有機バインダーの使用態様は特に限定されないが、繊維状のものを使用すると、吸着シートが簡便に作製できるため好ましい。吸着シートにおける有機バインダーの含有率は、3質量%~15質量%が好ましく、4質量%~12質量%がより好ましい。3質量%未満では多孔性金属錯体の担持性やシートの柔軟性が不足し、15質量%を超えると多孔性金属錯体が有機バインダーにより被覆されてしまい、十分な吸着性能が得られ難くなる傾向がある。 The adsorption sheet in the present invention contains an organic binder. This is because the flexibility and strength of the adsorption sheet are improved. The organic binder is not particularly limited as long as it can bond the porous metal complex and the fiber. For example, polyvinyl alcohol-based polymers, polyacrylonitrile-based polymers, polyethylene-based polymers, polyester-based polymers, polyphenylene ether-based polymers, and the like can be used. From the viewpoint of handleability, a polyvinyl alcohol-based polymer is preferable. The mode of use of the organic binder is not particularly limited, but it is preferable to use a fibrous binder because an adsorption sheet can be easily produced. The content of the organic binder in the adsorption sheet is preferably 3% by mass to 15% by mass, more preferably 4% by mass to 12% by mass. If it is less than 3% by mass, the supportability of the porous metal complex and the flexibility of the sheet are insufficient, and if it exceeds 15% by mass, the porous metal complex is coated with the organic binder, and it tends to be difficult to obtain sufficient adsorption performance. There is.
 有機バインダーの水中溶解温度は、65℃~100℃であることが好ましく、より好ましくは70℃~100℃である。水中溶解温度が65℃未満では、バインダー側鎖が多孔性金属錯体の細孔内に入る割合が多くなり、結果、吸着性能が不十分となる可能性がある。また、100℃より高温では接着不十分により担持性に欠けるといった問題がある。 The dissolution temperature of the organic binder in water is preferably 65 ° C to 100 ° C, more preferably 70 ° C to 100 ° C. If the dissolution temperature in water is less than 65 ° C., the proportion of the binder side chain entering the pores of the porous metal complex increases, and as a result, the adsorption performance may be insufficient. Further, if the temperature is higher than 100 ° C., there is a problem that the supportability is lacking due to insufficient adhesion.
 有機バインダーの水中溶解温度は、通常の方法で測定できる。例えば、純水100mlをビーカーにいれ撹拌し、水温が50℃になるまでオイルバスにて加熱し、そこに有機バインダー0.5gを添加し、昇温速度2℃/minにて水温を上昇させ、目視でバインダーが溶解始め半透明な状態になった時の温度を測定する、といった方法がある。 The dissolution temperature of the organic binder in water can be measured by a usual method. For example, 100 ml of pure water is placed in a beaker and stirred, heated in an oil bath until the water temperature reaches 50 ° C., 0.5 g of an organic binder is added thereto, and the water temperature is raised at a heating rate of 2 ° C./min. , There is a method of visually measuring the temperature when the binder begins to melt and becomes translucent.
 本発明の吸着シートは、有機バインダーの含有量が少なくても、フィブリル化した繊維により担持性を発現し、多孔性金属錯体の高い水分吸着率により吸着シートの柔軟性を発現するものである。結果、有機バインダーが少なくて済むこと、および多孔性金属錯体自身が持つ高い吸着性能により、十分な吸着性能を発現することを可能とする。 The adsorption sheet of the present invention exhibits supportability due to the fibrillated fibers even if the content of the organic binder is small, and exhibits the flexibility of the adsorption sheet due to the high water adsorption rate of the porous metal complex. As a result, it is possible to exhibit sufficient adsorption performance due to the small amount of organic binder and the high adsorption performance of the porous metal complex itself.
 本発明の吸着シートは、柔軟性の指標として、比引張伸度が5%・m/g以上であることが好ましい。5%・m/g未満では、シートの柔軟性に欠け、ハニカム加工(段加工)時に割れが生じてしまう。 The adsorption sheet of the present invention preferably has a specific tensile elongation of 5% · m / g or more as an index of flexibility. If it is less than 5% m / g, the sheet lacks flexibility and cracks occur during honeycomb processing (step processing).
 本発明の吸着シートは、多孔性金属錯体を1種または2種以上含んでいてもよく、さらに多孔性金属錯体以外の多孔質材料を含んでいてもよい。本発明の吸着シートに含有される多孔質材料については特に限定されないが、例えば、活性炭、ゼオライト、シリカゲル、活性アルミナ、アルミノリン酸塩、シリコアルミノリン酸、スチレン-ジビニルベンゼン共重合体等の有機高分子多孔質体、等が挙げられる。好ましくは、安価に入手できる活性炭、ゼオライト、シリカゲル、活性アルミナである。 The adsorption sheet of the present invention may contain one or more types of porous metal complexes, and may further contain a porous material other than the porous metal complex. The porous material contained in the adsorption sheet of the present invention is not particularly limited, but for example, organic highs such as activated carbon, zeolite, silica gel, activated alumina, aluminophosphate, silicoaluminolic acid, and styrene-divinylbenzene copolymer. Examples include molecular porous materials. Preferred are activated carbon, zeolite, silica gel, and activated alumina, which are inexpensively available.
 本発明の吸着シートの厚みは、0.1mm~0.9mmであることが好ましく、より好ましくは0.1mm~0.7mmである。厚みが0.1mm未満であればシート強度が著しく低下するため、後加工においてハニカム状等の吸着エレメントに加工することが困難になる場合がある。また、厚みが0.9mmより大きければ、吸着シートをハニカム状等に加工した時の吸着エレメントの圧損が高くなる傾向がある。 The thickness of the adsorption sheet of the present invention is preferably 0.1 mm to 0.9 mm, more preferably 0.1 mm to 0.7 mm. If the thickness is less than 0.1 mm, the sheet strength is remarkably lowered, so that it may be difficult to process the adsorption element into a honeycomb shape or the like in the post-processing. Further, if the thickness is larger than 0.9 mm, the pressure loss of the suction element when the suction sheet is processed into a honeycomb shape or the like tends to be high.
 本発明の吸着シートの坪量は、25g/m2~200g/m2が好ましい。より好ましくは40g/m2~150g/m2である。坪量が25g/m2未満であれば、シートの厚みが薄くなり、シート強度が著しく低下する虞があり、後加工においてハニカム状等の吸着エレメントへの加工が困難になる場合がある。また、坪量が200g/m2を超えると、シートの厚みが大きくなり過ぎ、ハニカム状等に加工した時の吸着エレメントの圧損が高くなる場合がある。 The basis weight of the adsorption sheet of the present invention is preferably 25 g / m 2 to 200 g / m 2. More preferably, it is 40 g / m 2 to 150 g / m 2 . If the basis weight is less than 25 g / m 2 , the thickness of the sheet may become thin and the sheet strength may be significantly reduced, which may make it difficult to process the adsorption element such as a honeycomb shape in the post-processing. Further, if the basis weight exceeds 200 g / m 2 , the thickness of the sheet may become too large, and the pressure loss of the suction element when processed into a honeycomb shape or the like may increase.
 本発明の吸着シートを製造する方法としては、特に制限されず、従来公知の加工方法を用いることができる。好ましくは、多孔性金属錯体と、繊維と、有機バインダーとを、水、有機溶媒又はこれらの混合物中に分散させ、成形、脱水、乾燥することにより得られる湿式シート化法が挙げられる。 The method for producing the adsorption sheet of the present invention is not particularly limited, and a conventionally known processing method can be used. Preferably, a wet sheeting method obtained by dispersing the porous metal complex, the fiber, and the organic binder in water, an organic solvent, or a mixture thereof, forming, dehydrating, and drying the mixture can be mentioned.
 ここで、多孔性金属錯体は、その細孔内に溶媒分子を有する状態で、上記シート構成材料と混合し、シート化工程に供するのが好ましい。多孔性金属錯体が細孔内に溶媒分子を有していない場合、吸着シートを構成する有機バインダーが、当該細孔内に吸着されてしまう虞がある。この場合、シート化後、後述する脱溶媒処理を実施しても多孔性金属錯体細孔内に捕捉された有機バインダーを除去することは難しく、吸着シートの吸着性能が劣る結果となる。すなわち、本発明では、多孔性金属錯体の細孔に溶媒分子を吸着させておくことにより、シート化工程における有機バインダー等の細孔への吸着を防止し、シート化工程後、後述する脱溶媒処理により細孔内から溶媒分子を除去することにより、吸着シートの吸着性能を確保している。通常は、多孔性金属錯体を合成する段階で、当該多孔性金属錯体の細孔内に溶媒分子が吸着するが、多孔性金属錯体が細孔内に溶媒分子を有していない場合又は溶媒分子の吸着量が不十分である場合は、後述する実施例に記載の方法により細孔内に有機溶媒を吸着させることができる。ここで、溶媒分子とは、水や一般的な有機溶媒分子を指す。 Here, it is preferable that the porous metal complex is mixed with the above-mentioned sheet constituent material in a state of having solvent molecules in its pores and subjected to the sheet forming step. If the porous metal complex does not have solvent molecules in the pores, the organic binder constituting the adsorption sheet may be adsorbed in the pores. In this case, it is difficult to remove the organic binder trapped in the pores of the porous metal complex even if the solvent removal treatment described later is carried out after the sheet is formed, resulting in inferior adsorption performance of the adsorption sheet. That is, in the present invention, by adsorbing the solvent molecules in the pores of the porous metal complex, the adsorption of the organic binder or the like in the pores in the sheeting step is prevented, and after the sheeting step, the solvent is removed, which will be described later. By removing the solvent molecules from the pores by the treatment, the adsorption performance of the adsorption sheet is ensured. Normally, at the stage of synthesizing a porous metal complex, solvent molecules are adsorbed in the pores of the porous metal complex, but when the porous metal complex does not have solvent molecules in the pores or solvent molecules. When the amount of adsorbed is insufficient, the organic solvent can be adsorbed in the pores by the method described in Examples described later. Here, the solvent molecule refers to water or a general organic solvent molecule.
 本発明の吸着シートを製造する場合、シート化工程後に、吸着シート内に含まれる溶媒を除去する脱溶媒処理工程を実施する。上述の様に多孔性金属錯体は、その細孔内に溶媒分子を有する状態でシート化するのが好ましく、この場合、多孔性金属錯体の細孔内の溶媒分子により、十分な吸着性能が得られ難い。よって、吸着性能を発現させるため、シート化工程後に脱溶媒処理を実施する。なお、脱溶媒処理の実施時期はシート化工程以降であれば特に限定されない。 When producing the adsorption sheet of the present invention, a solvent removal treatment step of removing the solvent contained in the adsorption sheet is carried out after the sheet forming step. As described above, the porous metal complex is preferably sheeted with solvent molecules in its pores, and in this case, sufficient adsorption performance can be obtained by the solvent molecules in the pores of the porous metal complex. It's hard to get rid of. Therefore, in order to develop the adsorption performance, the solvent removal treatment is carried out after the sheeting step. The timing of the desolvation treatment is not particularly limited as long as it is after the sheeting step.
 脱溶媒処理の条件は特に定めないが、温度は50℃~300℃であることが好ましい。50℃未満では、溶媒の除去が不完全となる虞があり、十分な吸着性能が得られ難い場合がある。一方、300℃を超えると、多孔性金属錯体の細孔構造が壊れてしまう虞があり、この場合も十分な吸着性能が得られ難くなる。より好ましくは80℃~200℃である。また、脱溶媒処理は、減圧下で実施することで一層効率よく溶媒を除去できる。この際、圧力は特に限定されず、多孔性金属錯体の物性や配合量に応じて適宜調整すればよいが、例えば、103Pa~10-5Paが好ましく、10-1Pa~10-5Paであるのがより好ましい。脱溶媒処理時間も特に限定されないが、例えば1時間~100時間とするのが好ましく、より好ましくは3時間~48時間であり、さらに好ましくは3時間~24時間である。尚、最も好ましい脱溶媒処理の条件は、真空条件下で80℃~200℃、3時間~24時間である。 The conditions for the desolvation treatment are not particularly specified, but the temperature is preferably 50 ° C. to 300 ° C. If the temperature is lower than 50 ° C., the removal of the solvent may be incomplete, and it may be difficult to obtain sufficient adsorption performance. On the other hand, if the temperature exceeds 300 ° C., the pore structure of the porous metal complex may be broken, and in this case as well, it becomes difficult to obtain sufficient adsorption performance. More preferably, it is 80 ° C. to 200 ° C. Further, the solvent can be removed more efficiently by carrying out the desolvation treatment under reduced pressure. At this time, the pressure is not particularly limited and may be appropriately adjusted according to the physical properties and the blending amount of the porous metal complex. For example, 10 3 Pa to 10 -5 Pa is preferable, and 10 -1 Pa to 10 -5 is preferable. Pa is more preferable. The desolvation treatment time is also not particularly limited, but is preferably 1 hour to 100 hours, more preferably 3 hours to 48 hours, and further preferably 3 hours to 24 hours. The most preferable desolvation treatment conditions are 80 ° C. to 200 ° C. for 3 hours to 24 hours under vacuum conditions.
 本発明の吸着シートは、平板状で使用してもよく、また、適宜、プリーツ加工、ハニカム加工、又は、コルゲート加工等を施して、所望の形状として用いてもよい。図1に本発明の吸着シートの加工の一例として、吸着シート1をコルゲート状に加工した片段シートを示す。特に、プリーツ加工、ハニカム加工、コルゲート加工は、加工時にシートを折り曲げる工程が必要であるが、その際、多孔性金属錯体に水分を十分に吸着させてから加工することによりシートの柔軟性が発現される。多孔性金属錯体に水分を吸着させる方法は特に定めないが、加湿された部屋の使用、または、蒸気を吹きかけながら加工するといった方法が簡便で好ましい。 The adsorption sheet of the present invention may be used in a flat plate shape, or may be appropriately subjected to pleating, honeycomb processing, corrugated processing, or the like to be used as a desired shape. FIG. 1 shows a single-stage sheet obtained by processing the suction sheet 1 into a corrugated shape as an example of processing the suction sheet of the present invention. In particular, pleating, honeycombing, and corrugating require a step of bending the sheet during processing, and at that time, the flexibility of the sheet is exhibited by sufficiently adsorbing water to the porous metal complex before processing. Will be done. The method for adsorbing water to the porous metal complex is not particularly specified, but a method such as using a humidified room or processing while spraying steam is convenient and preferable.
 本発明の吸着エレメントは、上記本発明の吸着シートを備えていることに特徴を有する。本発明の吸着エレメントの型式は特に限定されず、従来公知の型式はいずれも採用でき、用途や目的に応じて適宜選択すればよい。また、本発明の吸着エレメントに備えられる吸着シートの形状には特に定めはないが、例えば、吸着シートを平板状、プリーツ状、ハニカム状等に加工したものを用いることができる。例えば、プリーツ状に加工された吸着シートは直交流型吸着エレメントとしての使用において、また、ハニカム状に加工された吸着シートは平行流型吸着エレメントとしての使用において、それぞれ、処理する気体との接触面積を大きくして吸着対象物質の除去効率の向上と、吸着エレメントの低圧損化とを同時に図ることができる。平行流型吸着エレメントは、直交流型吸着エレメントと比較して、ミストやゴミによる目詰まりの防止、低圧損化、軽量化の点で優れているため、当該吸着エレメントに備えられる吸着シートはハニカム状であることが好ましい。 The adsorption element of the present invention is characterized by including the above-mentioned adsorption sheet of the present invention. The type of the adsorption element of the present invention is not particularly limited, and any conventionally known type can be adopted and may be appropriately selected depending on the intended use and purpose. The shape of the suction sheet provided in the suction element of the present invention is not particularly limited, but for example, a suction sheet processed into a flat plate shape, a pleated shape, a honeycomb shape, or the like can be used. For example, the pleated adsorption sheet is used as a orthogonal flow type adsorption element, and the honeycomb-shaped adsorption sheet is used as a parallel flow type adsorption element. It is possible to increase the area to improve the removal efficiency of the substance to be adsorbed and to reduce the low pressure of the adsorption element at the same time. Compared to the orthogonal flow type adsorption element, the parallel flow type adsorption element is superior in terms of prevention of clogging due to mist and dust, low pressure loss, and weight reduction. Therefore, the adsorption sheet provided in the adsorption element is a honeycomb. It is preferably shaped.
 図2に、本発明の吸着エレメントの一例として、本発明の吸着シートをローター形状に巻回した吸着ローター2の図を示す。吸着ローター2に備えられる吸着シートはハニカム状となっている。 FIG. 2 shows a diagram of a suction rotor 2 in which the suction sheet of the present invention is wound in a rotor shape as an example of the suction element of the present invention. The suction sheet provided in the suction rotor 2 has a honeycomb shape.
 本発明の吸着シート、および、それを備えた吸着エレメントは、屋内、乗り物内、壁紙、家具、内装材、樹脂成形体、電気機器等で、悪臭成分等を低減する目的や、工場等から排出される空気中の有機溶剤の分離・回収、もしくは、調湿・デシカントの目的で広く用いることができる。 The adsorption sheet of the present invention and the adsorption element provided with the adsorption sheet are discharged from factories, etc. for the purpose of reducing malodorous components, etc. in indoors, in vehicles, wallpaper, furniture, interior materials, resin molded products, electrical equipment, etc. It can be widely used for the purpose of separating / recovering organic solvents in the air, or controlling humidity / desiccant.
 また、本発明の吸着エレメントと、吸着エレメントに吸着対象物質を導入して吸着させる吸着手段と、吸着エレメントが吸着した吸着対象物質を脱着させる脱着手段と、を備えた吸脱着処理装置も本発明の範囲内に含まれる。吸着手段は、有機溶剤等の悪臭物質や水分等の吸着対象物質を含む空気やガスを導入する管等が考えられる。吸着対象物質を脱着させる方法として、加熱する方法や系の圧力を下げる方法などあり、脱着手段としては、加熱ガスを導入する菅や加熱器や減圧器等が考えられる。脱着効率や経済性から加熱空気を導入する手段が望ましい。 The present invention also relates to an adsorption / desorption processing apparatus including the adsorption element of the present invention, an adsorption means for introducing an adsorption target substance into the adsorption element and adsorbing the substance, and a desorption means for desorbing the adsorption target substance adsorbed by the adsorption element. Is included in the range of. As the adsorption means, a pipe or the like for introducing air or gas containing a malodorous substance such as an organic solvent or a substance to be adsorbed such as moisture can be considered. As a method for desorbing the substance to be adsorbed, there are a method of heating and a method of lowering the pressure of the system, and as a desorption means, a tube for introducing a heating gas, a heater, a decompressor, or the like can be considered. A means for introducing heated air is desirable from the viewpoint of desorption efficiency and economy.
 図3に、本発明の吸脱着処理装置の一例として、デシカント空調システム11を示す。デシカント空調システム11は、吸着式ローター2、モーター3、ヒーター等の熱源8、ファン9、除湿・加湿領域区切部材10を備えている。デシカント空調システム11では、吸着対象物質としての水分を含む高湿度気体4が導入されると、吸着式ローター2にて水分が吸着され、除湿後気体5として排出される。熱源8で加熱された低湿度気体6が導入されると、吸着ローター2に吸着された水分が脱着され、加湿後気体7として排出される。本発明の吸脱着処理装置は、工場用のデシカント空調システムにも家庭用のデシカント空調システムにも適用できる。 FIG. 3 shows a desiccant air conditioning system 11 as an example of the suction / desorption processing device of the present invention. The desiccant air conditioning system 11 includes a suction type rotor 2, a motor 3, a heat source 8 such as a heater, a fan 9, and a dehumidifying / humidifying area dividing member 10. In the desiccant air conditioning system 11, when the high-humidity gas 4 containing water as the substance to be adsorbed is introduced, the water is adsorbed by the adsorption rotor 2 and discharged as the gas 5 after dehumidification. When the low-humidity gas 6 heated by the heat source 8 is introduced, the water adsorbed on the adsorption rotor 2 is desorbed and discharged as the gas 7 after humidification. The suction / desorption treatment device of the present invention can be applied to both a desiccant air conditioning system for factories and a desiccant air conditioning system for home use.
 以下、実施例によって本発明についてより具体的に示す。なお、下記実施例は本発明を限定する性質のものではなく、前・後記の趣旨に沿って設計変更することはいずれも本発明の技術的範囲に含まれるものである。
 初めに、実施例及び比較例において求めた特性値の測定方法および評価方法を以下に示す。
Hereinafter, the present invention will be described more specifically by way of examples. It should be noted that the following examples do not have the property of limiting the present invention, and any design change according to the gist of the above and the following is included in the technical scope of the present invention.
First, the measurement method and the evaluation method of the characteristic values obtained in Examples and Comparative Examples are shown below.
 [水分吸着率]
 多孔性金属錯体(水または有機溶媒処理前)約100mgを採取し、120℃で12時間真空乾燥した後、秤量する。高精度ガス・蒸気吸着量測定装置(BELSORP-max、日本ベル社製)を使用し、25℃における水蒸気の吸着量を、相対圧を0.02~0.95の範囲で徐々に高めながら40点測定し、吸着等温線を作成する。このとき、目標相対圧を0.001,0.01,0.05,0.1,0.2,0.3,0.4,0.5,0.6,0.7,0.8,0.9に設定し、さらに吸着量増減許容量を相対圧0~0.3では30cm/g、相対圧0.3~0.5では50cm/g、相対圧0.5~では30cm/gに設定し、吸着等温線を作成する。そして、相対圧0.5における多孔性金属錯体1gあたりの水分吸着量[g]から水分吸着率[%]を下記式(i)にて算出する。
 水分吸着率[%]=吸着材1gあたりの水分吸着量[g]×100・・・(i)
[Moisture adsorption rate]
Approximately 100 mg of the porous metal complex (before treatment with water or organic solvent) is collected, vacuum dried at 120 ° C. for 12 hours, and then weighed. Using a high-precision gas / vapor adsorption amount measuring device (BELSORP-max, manufactured by Nippon Bell Co., Ltd.), increase the adsorption amount of water vapor at 25 ° C in the range of 0.02 to 0.95 while gradually increasing 40. Measure points and create an adsorption isotherm. At this time, the target relative pressure is 0.001, 0.01, 0.05, 0.1, 0.2, 0.3, 0.4, 0.5, 0.6, 0.7, 0.8. , is set to 0.9, further relative pressure adsorption amount decrease allowable amount 0-0.3 in 30 cm 2 / g, relative pressure 0.3-0.5 in 50 cm 2 / g, a relative pressure of 0.5 at ~ Set to 30 cm 2 / g and create an adsorption isotherm. Then, the water adsorption rate [%] is calculated by the following formula (i) from the water adsorption amount [g] per 1 g of the porous metal complex at a relative pressure of 0.5.
Moisture adsorption rate [%] = Moisture adsorption amount per 1 g of adsorbent [g] × 100 ... (i)
[BET比表面積]
 多孔性金属錯体(水または有機溶媒処理前)約100mgを採取し、120℃で12時間真空乾燥した後、秤量する。自動比表面積測定装置(ジェミニ2375、マイクロメリティックス社製)を使用し、液体窒素の沸点(-195.8℃)における窒素ガスの吸着量を、相対圧を0.02~0.95の範囲で徐々に高めながら40点測定し、吸着等温線を作成する。自動比表面積測定装置に付属の解析ソフト(GEMINI-PCW version1.01)にて、BET条件で、表面積解析範囲を0.01~0.15に設定して、BET比表面積[m2/g]を求める。
[BET specific surface area]
Approximately 100 mg of the porous metal complex (before treatment with water or organic solvent) is collected, vacuum dried at 120 ° C. for 12 hours, and then weighed. Using an automatic specific surface area measuring device (Gemini 2375, manufactured by Micromeritix), the adsorption amount of nitrogen gas at the boiling point (-195.8 ° C.) of liquid nitrogen was adjusted to a relative pressure of 0.02 to 0.95. Measure 40 points while gradually increasing in the range to create an adsorption isotherm. Using the analysis software (GEMINI-PCW version 1.01) attached to the automatic specific surface area measuring device, set the surface area analysis range to 0.01 to 0.15 under BET conditions, and set the BET specific surface area [m 2 / g]. Ask for.
[担持性]
 吸着シートサンプルから切り出した10cm×10cmの試験片を10cm×10cmの平面部分が実験台に垂直になるように固定し、そこに直径2.4cm、質量20gの球体(素材:アルミニウム)を、試験片10cm×10cmの平面部分に対し垂直に10回衝突させる。球体は10cm/sの速度で転がす。結果、脱落した多孔性金属錯体の量が、0.1mgより少ない場合を○(良好)、10mgより多い場合を×(不良)、0.1mg~10mgの場合を△(可)とする。
[Supportability]
A 10 cm × 10 cm test piece cut out from the adsorption sheet sample was fixed so that the flat portion of 10 cm × 10 cm was perpendicular to the laboratory table, and a sphere (material: aluminum) having a diameter of 2.4 cm and a mass of 20 g was tested therein. It is made to collide vertically with a flat portion of 10 cm × 10 cm 10 times. The sphere rolls at a speed of 10 cm / s. As a result, when the amount of the dropped porous metal complex is less than 0.1 mg, it is evaluated as ◯ (good), when it is more than 10 mg, it is evaluated as × (poor), and when it is 0.1 mg to 10 mg, it is evaluated as Δ (possible).
[柔軟性]
 実施例および比較例では、柔軟性に関して、吸着シートをハニカム加工(段加工)時に割れが生じないかを観測する。
 吸着シートサンプルから切り出した10cm×10cmの試験片を120℃、1時間乾燥した後、22℃、40%RH雰囲気下で1時間静置する。このように調湿した試験片の両端を持ち、90度に折り曲げる。この時、シートが割れないものを○(良好)、亀裂が生じるものを△(難あり)、割れるものを×(不良)として評価する。
[Flexibility]
In the examples and the comparative examples, regarding the flexibility, it is observed whether or not the adsorption sheet is cracked during the honeycomb processing (step processing).
A 10 cm × 10 cm test piece cut out from the adsorption sheet sample is dried at 120 ° C. for 1 hour, and then allowed to stand at 22 ° C. for 1 hour in a 40% RH atmosphere. Hold both ends of the test piece whose humidity has been adjusted in this way, and bend it at 90 degrees. At this time, the sheet that does not crack is evaluated as ◯ (good), the sheet that cracks is evaluated as Δ (difficult), and the sheet that cracks is evaluated as × (defective).
[比引張伸度]
 吸着シートサンプルから切り出した15mm×100mmの試験片を120℃、1時間乾燥し、その重量を測定する。そして、乾燥したサンプルを22℃、40%RH雰囲気下で1時間静置し、引張・圧縮試験機(TENSILON RTG-1310、A&D社製)にて最大点伸度[%]を測定する。なお、チャック間距離は50mm、引張速度は15mm/minとする。得られたデータより、比引張伸度を下記式(ii)にて算出する。
 比引張伸度[%・m/g]=最大点伸度[%]/サンプル幅[m]/吸着シートの坪量[g/m]・・・(ii)
[Specific tensile elongation]
A 15 mm × 100 mm test piece cut out from the adsorption sheet sample is dried at 120 ° C. for 1 hour, and the weight thereof is measured. Then, the dried sample is allowed to stand at 22 ° C. in a 40% RH atmosphere for 1 hour, and the maximum point elongation [%] is measured with a tensile / compression tester (TENSILON RTG-1310, manufactured by A & D Co., Ltd.). The distance between the chucks is 50 mm, and the tensile speed is 15 mm / min. From the obtained data, the specific tensile elongation is calculated by the following formula (ii).
Specific tensile elongation [% · m / g] = maximum point elongation [%] / sample width [m] / adsorption sheet basis weight [g / m 2 ] ... (ii)
[細孔維持率]
 吸着シートサンプル約100mgを採取し、120℃で12時間真空乾燥した後、秤量する。自動比表面積測定装置(ジェミニ2375、マイクロメリティックス社製)を使用し、液体窒素の沸点(-195.8℃)における窒素ガスの吸着量を、相対圧を0.02~0.95の範囲で徐々に高めながら40点測定し、前記サンプルの吸着等温線を作成する。自動比表面積測定装置に付属の解析ソフト(GEMINI-PCW version1.01)にて、BET条件で、表面積解析範囲を0.01~0.15に設定して、BET比表面積[m2/g]を求める。そして、多孔性金属錯体のBET比表面積[m/g]をもとに細孔維持率を下記式(iii)にて算出する。
 細孔維持率[%]={吸着シートのBET比表面積[m/g]×100/(吸着シート内の多孔性金属錯体含有率)}/(多孔性金属錯体サンプルのBET比表面積[m/g])×100・・・(iii)
 細孔維持率が高いほど、多孔性金属錯体の細孔がバインダー等により埋まっていない(細孔閉塞されていない)ことを示し、吸着性能が高くなる。
[Pore retention rate]
Approximately 100 mg of an adsorption sheet sample is collected, vacuum dried at 120 ° C. for 12 hours, and then weighed. Using an automatic specific surface area measuring device (Gemini 2375, manufactured by Micromeritix), the amount of nitrogen gas adsorbed at the boiling point (-195.8 ° C) of liquid nitrogen was adjusted to a relative pressure of 0.02 to 0.95. Measure 40 points while gradually increasing the temperature in the range to create an adsorption isotherm of the sample. Using the analysis software (GEMINI-PCW version 1.01) attached to the automatic specific surface area measuring device, set the surface area analysis range to 0.01 to 0.15 under BET conditions, and set the BET specific surface area [m 2 / g]. Ask for. Then, the porosity is calculated by the following formula (iii) based on the BET specific surface area [m 2 / g] of the porous metal complex.
Porosity [%] = {BET specific surface area of adsorption sheet [m 2 / g] x 100 / (porosity of porous metal complex in adsorption sheet)} / (BET specific surface area of porous metal complex sample [m] 2 / g]) × 100 ... (iii)
The higher the porosity, the higher the adsorption performance, indicating that the pores of the porous metal complex are not filled with a binder or the like (the pores are not closed).
[シート性能(水蒸気吸着量)]
 多孔性金属錯体(水または有機溶媒処理前)約100mgを採取し、120℃で12時間真空乾燥した後、秤量する。高精度ガス・蒸気吸着量測定装置(BELSORP-max、日本ベル社製)を使用し、25℃における水蒸気の吸着量を、相対圧を0.02~0.95の範囲で徐々に高めながら40点測定し、吸着等温線を作成する。そして、相対圧0.95における多孔性金属錯体1gあたりの水蒸気吸着量[ml]を求める。シート性能の評価として、水蒸気吸着量が410ml/g以上を〇(良好)、400ml/gよりも大きく410ml/g未満を△(可)、400ml/g以下を×(不良)として評価する。
[Sheet performance (water vapor adsorption amount)]
Approximately 100 mg of the porous metal complex (before treatment with water or organic solvent) is collected, vacuum dried at 120 ° C. for 12 hours, and then weighed. Using a high-precision gas / vapor adsorption amount measuring device (BELSORP-max, manufactured by Nippon Bell Co., Ltd.), increase the adsorption amount of water vapor at 25 ° C in the range of 0.02 to 0.95 while gradually increasing 40. Measure points and create an adsorption isotherm. Then, the amount of water vapor adsorbed [ml] per 1 g of the porous metal complex at a relative pressure of 0.95 is determined. As an evaluation of the sheet performance, an amount of water vapor adsorption of 410 ml / g or more is evaluated as 〇 (good), a value larger than 400 ml / g and less than 410 ml / g is evaluated as Δ (possible), and 400 ml / g or less is evaluated as × (defective).
[加工性]
 実施例及び比較例では、加工性として、段加工後に自力で段形状を保持できるかについて観測する。
 吸着シートサンプルを巾30cm×長さ30cmにし、理論上は巾30cm×長さ21.4cmのコルゲート紙を作製できるコルゲート加工機に通過させる。そして、コルゲート加工された吸着シートを22℃、40%RH雰囲気下で24時間静置させた後、長さの回復率が20%未満を○(良好)、20%から50%未満を△(可)、50%~100%を×(不良)として評価する。
[Workability]
In the examples and comparative examples, as workability, it is observed whether the step shape can be maintained by itself after the step processing.
The adsorption sheet sample is made to have a width of 30 cm and a length of 30 cm, and is theoretically passed through a corrugated processing machine capable of producing a corrugated paper having a width of 30 cm and a length of 21.4 cm. Then, after the corrugated adsorption sheet was allowed to stand for 24 hours at 22 ° C. in a 40% RH atmosphere, the recovery rate of the length was less than 20% (good) and 20% to less than 50% (good). Yes), 50% to 100% is evaluated as x (defective).
[水中溶解温度]
 実施例、比較例で用いた有機バインダーについて、以下の測定方法で、水中溶解温度を実測したところ、実施例8の有機バインダーを除き、カタログ値と同じであった。実施例8の有機バインダーのカタログ値は<99℃であるが、実測値は95℃であった。
 純水4mL、有機バインダー0.02gを6mlガラス瓶にいれた。50℃から5℃刻みで加熱したウォーターバスに前記ガラス瓶を10分入れた。瓶内の有機バインダーは2分毎にスパチュラを用いて撹拌した。目視でバインダーが溶解初め半透明な状態になった時の温度を測定した。
[Dissolution temperature in water]
When the dissolution temperature in water was actually measured with respect to the organic binder used in Examples and Comparative Examples by the following measuring method, it was the same as the catalog value except for the organic binder of Example 8. The catalog value of the organic binder of Example 8 was <99 ° C, but the measured value was 95 ° C.
4 mL of pure water and 0.02 g of an organic binder were placed in a 6 ml glass bottle. The glass bottle was placed in a water bath heated at intervals of 50 ° C. to 5 ° C. for 10 minutes. The organic binder in the bottle was stirred with a spatula every 2 minutes. The temperature at which the binder began to melt and became translucent was visually measured.
<実施例1>
 Fe(NO・9HO16.2g(40mmol)とトリメシン酸7.5g(36mmol)とを水32mlに溶解させ、95℃で15時間加熱し多孔性金属錯体を合成した。得られた多孔性金属錯体について、窒素吸着測定および水蒸気吸着測定により物性評価を行った結果、BET比表面積は1575m/g、水分吸着率は53%であった。
 その後、上記合成した多孔性金属錯体を水中に24時間浸漬させた後に、ろ過し、細孔内に溶媒分子が吸着された多孔性金属錯体サンプルを得た。この多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を8質量%、フィブリル化した繊維としてアラミド繊維を5質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置(東洋紡エンジニアリング株式会社製、以下同様)を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 1>
And Fe (NO 3) 3 · 9H 2 O16.2g (40mmol) and trimesic acid 7.5 g (36 mmol) was dissolved in water 32 ml, was synthesized porous metal complex was heated for 15 hours at 95 ° C.. As a result of evaluating the physical properties of the obtained porous metal complex by nitrogen adsorption measurement and water vapor adsorption measurement, the BET specific surface area was 1575 m 2 / g and the water adsorption rate was 53%.
Then, the synthesized porous metal complex was immersed in water for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores. This porous metal complex sample is 80% by mass (excluding solvent molecules), aramid fiber is 8% by mass as non-fibrillated fiber, aramid fiber is 5% by mass as fibrillated fiber, and the dissolution temperature in water is 70 as an organic binder. Polyvinyl alcohol (PVA) fibers at ° C (catalog value) are mixed at a ratio of 7% by mass, and adsorbed using a wet paper machine (manufactured by Toyo Boseki Engineering Co., Ltd., the same applies hereinafter) at a mass of 100 g / m 2 basis weight. A sheet was prepared. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例2>
 実施例1と同様に得られた多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を10質量%、フィブリル化した繊維としてアラミド繊維を3質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 2>
80% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 10% by mass of aramid fibers as unfibrillated fibers, and 3% by mass of aramid fibers as fibrillated fibers. As an organic binder, polyvinyl alcohol (PVA) fibers having a dissolution temperature of 70 ° C. (catalog value) in water are mixed at a ratio of 7% by mass, and an adsorption sheet is prepared using a wet paper machine at a mass of 100 g / m 2 basis weight. Made. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例3>
 実施例1と同様に得られた多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を8質量%、フィブリル化した繊維としてアラミド繊維を7質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を5質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 3>
80% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 8% by mass of aramid fibers as unfibrillated fibers, and 7% by mass of aramid fibers as fibrillated fibers. As an organic binder, polyvinyl alcohol (PVA) fibers having a dissolution temperature of 70 ° C. (catalog value) in water are mixed at a ratio of 5% by mass, and an adsorption sheet is prepared using a wet paper machine at a mass of 100 g / m 2 basis weight. Made. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例4>
 実施例1と同様に得られた多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を8質量%、フィブリル化した繊維としてアラミド繊維を9質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を3質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 4>
80% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 8% by mass of aramid fibers as unfibrillated fibers, 9% by mass of aramid fibers as fibrillated fibers, As an organic binder, polyvinyl alcohol (PVA) fibers having a dissolution temperature of 70 ° C. (catalog value) in water are mixed at a ratio of 3% by mass, and an adsorption sheet is prepared using a wet paper machine at a mass of 100 g / m 2 basis weight. Made. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例5>
 実施例1と同様に得られた多孔性金属錯体サンプルを75質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を10質量%、フィブリル化した繊維としてアラミド繊維を6.3質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を8.7質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 5>
75% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 10% by mass of aramid fiber as a non-fibrillated fiber, and 6.3% by mass of aramid fiber as a fibrillated fiber. %, Polyvinyl alcohol (PVA) fiber having a dissolution temperature in water of 70 ° C. (catalog value) as an organic binder is mixed at a ratio of 8.7% by mass, and a wet papermaking apparatus is used at a mass of 100 g / m 2 basis weight. A suction sheet was prepared for use. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例6>
 実施例1と同様に得られた多孔性金属錯体サンプルを70質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を12質量%、フィブリル化した繊維としてアラミド繊維を7.5質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を10.5質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 6>
70% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 12% by mass of aramid fiber as a non-fibrillated fiber, and 7.5% by mass of aramid fiber as a fibrillated fiber. %, Polyvinyl alcohol (PVA) fiber having a dissolution temperature in water of 70 ° C. (catalog value) as an organic binder is mixed at a ratio of 10.5% by mass, and a wet papermaking apparatus is used at a mass of 100 g / m 2 basis weight. A suction sheet was prepared for use. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例7>
 実施例1と同様に得られた多孔性金属錯体サンプルを65質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を14質量%、フィブリル化した繊維としてアラミド繊維を8.8質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を12.2質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 7>
65% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 14% by mass of aramid fiber as a non-fibrillated fiber, and 8.8% by mass of aramid fiber as a fibrillated fiber. %, Polyvinyl alcohol (PVA) fiber having a dissolution temperature in water of 70 ° C. (catalog value) as an organic binder is mixed at a ratio of 12.2% by mass, and a wet papermaking apparatus is used at a mass of 100 g / m 2 basis weight. A suction sheet was prepared for use. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例8>
 実施例1と同様に得られた多孔性金属錯体サンプルを65質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を14質量%、フィブリル化した繊維としてアラミド繊維を8.8質量%、有機バインダーとして水中溶解温度が<99℃(水の沸騰手前で溶け始める場合を示す、カタログ値)のポリビニルアルコール(PVA)繊維を12.2質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 8>
65% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 14% by mass of aramid fiber as a non-fibrillated fiber, and 8.8% by mass of aramid fiber as a fibrillated fiber. %, Polyvinyl alcohol (PVA) fiber having a dissolution temperature in water <99 ° C. (catalog value indicating the case where it starts to dissolve before boiling of water) as an organic binder is mixed at a ratio of 12.2% by mass, and the basis weight is 100 g. A suction sheet was prepared using a wet paper making device with a mass of / m 2. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例9>
 実施例1と同様に得られた多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてレーヨン繊維を8質量%、フィブリル化した繊維としてレーヨン繊維を5質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 9>
80% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 8% by mass of rayon fiber as a non-fibrillated fiber, 5% by mass of rayon fiber as a fibrillated fiber, As an organic binder, polyvinyl alcohol (PVA) fibers having a dissolution temperature of 70 ° C. (catalog value) in water are mixed at a ratio of 7% by mass, and an adsorption sheet is prepared using a wet papermaking device at a mass of 100 g / m 2 basis weight. Made. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例10>
 実施例1と同様に得られた多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてPET繊維を8質量%、フィブリル化した繊維としてアラミド繊維を5質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 10>
80% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 8% by mass of PET fiber as a non-fibrillated fiber, 5% by mass of aramid fiber as a fibrillated fiber, As an organic binder, polyvinyl alcohol (PVA) fibers having a dissolution temperature of 70 ° C. (catalog value) in water are mixed at a ratio of 7% by mass, and an adsorption sheet is prepared using a wet paper machine at a mass of 100 g / m 2 basis weight. Made. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例11>
 多孔性金属錯体としてBasolite C300(BASF社製)を使用した。窒素吸着測定および水蒸気吸着測定により物性評価を行った結果、BET比表面積は1609m/g、水分吸着率は43%であった。
 その後、上記多孔性金属錯体をN,N-ジメチルホルムアルデヒド中に24時間浸漬させた後に、ろ過し、細孔内に溶媒分子が吸着された多孔性金属錯体サンプルを得た。この多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を8質量%、フィブリル化した繊維としてアラミド繊維を5質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/m2となる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 11>
Basolite C300 (manufactured by BASF) was used as the porous metal complex. As a result of physical property evaluation by nitrogen adsorption measurement and water vapor adsorption measurement, the BET specific surface area was 1609 m 2 / g and the water adsorption rate was 43%.
Then, the porous metal complex was immersed in N, N-dimethylformaldehyde for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores. This porous metal complex sample is 80% by mass (excluding solvent molecules), aramid fiber is 8% by mass as non-fibrillated fiber, aramid fiber is 5% by mass as fibrillated fiber, and the dissolution temperature in water is 70 as an organic binder. Polyvinyl alcohol (PVA) fibers at ° C. (catalog value) were mixed at a ratio of 7% by mass to prepare an adsorption sheet using a wet paper machine at a mass of 100 g / m 2 basis weight. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例12>
 オルトチタン酸テトライソプロピル3ml(10mmol)とテレフタル酸2.5g(15mmol)とをN,N-ジメチルホルムアルデヒド45ml及びメタノール5mlに溶解させ、150℃で15時間加熱し多孔性金属錯体を合成した。得られた多孔性金属錯体について、窒素吸着測定および水蒸気吸着測定により物性評価を行った結果、BET比表面積は1199m/g、水分吸着率は38%であった。
 その後、上記合成した多孔性金属錯体をN,N-ジメチルホルムアルデヒド中に24時間浸漬させた後に、ろ過し、細孔内に溶媒分子が吸着された多孔性金属錯体サンプルを得た。この多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を8質量%、フィブリル化した繊維としてアラミド繊維を5質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/m2となる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 12>
3 ml (10 mmol) of tetraisopropyl orthotitate and 2.5 g (15 mmol) of terephthalic acid were dissolved in 45 ml of N, N-dimethylformaldehyde and 5 ml of methanol, and heated at 150 ° C. for 15 hours to synthesize a porous metal complex. As a result of evaluating the physical properties of the obtained porous metal complex by nitrogen adsorption measurement and water vapor adsorption measurement, the BET specific surface area was 1199 m 2 / g and the water adsorption rate was 38%.
Then, the synthesized porous metal complex was immersed in N, N-dimethylformaldehyde for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores. This porous metal complex sample is 80% by mass (excluding solvent molecules), aramid fiber is 8% by mass as non-fibrillated fiber, aramid fiber is 5% by mass as fibrillated fiber, and the dissolution temperature in water is 70 as an organic binder. Polyvinyl alcohol (PVA) fibers at ° C. (catalog value) were mixed at a ratio of 7% by mass to prepare an adsorption sheet using a wet paper machine at a mass of 100 g / m 2 basis weight. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例13>
 塩化ジルコニウム5.3g(22.7mmol)とテレフタル酸3.78g(22.8mmol)とをN,N-ジメチルホルムアルデヒド500mlに溶解させ、120℃で24時間加熱し多孔性金属錯体を合成した。得られた多孔性金属錯体について、窒素吸着測定および水蒸気吸着測定により物性評価を行った結果、BET比表面積は1283m/g、水分吸着率は42%であった。
 その後、上記合成した多孔性金属錯体を水中に24時間浸漬させた後に、ろ過し、細孔内に溶媒分子が吸着された多孔性金属錯体サンプルを得た。この多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を8質量%、フィブリル化した繊維としてアラミド繊維を5質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 13>
5.3 g (22.7 mmol) of zirconium chloride and 3.78 g (22.8 mmol) of terephthalic acid were dissolved in 500 ml of N, N-dimethylformaldehyde and heated at 120 ° C. for 24 hours to synthesize a porous metal complex. As a result of evaluating the physical properties of the obtained porous metal complex by nitrogen adsorption measurement and water vapor adsorption measurement, the BET specific surface area was 1283 m 2 / g and the water adsorption rate was 42%.
Then, the synthesized porous metal complex was immersed in water for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores. This porous metal complex sample is 80% by mass (excluding solvent molecules), aramid fiber is 8% by mass as non-fibrillated fiber, aramid fiber is 5% by mass as fibrillated fiber, and the dissolution temperature in water is 70 as an organic binder. Polyvinyl alcohol (PVA) fibers at ° C. (catalog value) were mixed at a ratio of 7% by mass to prepare an adsorption sheet using a wet paper machine at a mass of 100 g / m 2 basis weight. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例14>
 実施例14と同様に得られた多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を9.2質量%、フィブリル化した繊維としてアラミド繊維を5.8質量%、有機バインダーとして、水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を5質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 14>
The porous metal complex sample obtained in the same manner as in Example 14 was 80% by mass (excluding solvent molecules), 9.2% by mass of aramid fiber as a non-fibrillated fiber, and aramid fiber as a fibrillated fiber. A wet paper making device in which polyvinyl alcohol (PVA) fibers having a dissolution temperature of 70 ° C. (catalog value) in water are mixed at a ratio of 5% by mass as an organic binder at a ratio of 8% by mass to a basis weight of 100 g / m 2. A suction sheet was prepared using. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例15>
 ZrOCl・8HO200g(0.62mol)とフマル酸72g(0.62mol)とをN,N-ジメチルホルムアルデヒド2Lおよびギ酸700mLに溶解させ、130℃で6時間加熱し多孔性金属錯体を合成した。得られた多孔性金属錯体について、窒素吸着測定および水蒸気吸着測定により物性評価を行った結果、BET比表面積は884m/g、水分吸着率は33%であった。
 その後、上記合成した多孔性金属錯体を水中に24時間浸漬させた後に、ろ過し、細孔内に溶媒分子が吸着された多孔性金属錯体サンプルを得た。この多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を8質量%、フィブリル化した繊維としてアラミド繊維を5質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 15>
ZrOCl 2 · 8H 2 O200g and (0.62 mol) of fumaric acid 72 g (0.62 mol) N, was dissolved in N- dimethylformamide 2L and 700mL formic acid, was synthesized porous metal complex was heated for 6 hours at 130 ° C. .. As a result of evaluating the physical properties of the obtained porous metal complex by nitrogen adsorption measurement and water vapor adsorption measurement, the BET specific surface area was 884 m 2 / g and the water adsorption rate was 33%.
Then, the synthesized porous metal complex was immersed in water for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores. This porous metal complex sample is 80% by mass (excluding solvent molecules), aramid fiber is 8% by mass as non-fibrillated fiber, aramid fiber is 5% by mass as fibrillated fiber, and the dissolution temperature in water is 70 as an organic binder. Polyvinyl alcohol (PVA) fibers at ° C. (catalog value) were mixed at a ratio of 7% by mass to prepare an adsorption sheet using a wet paper machine at a mass of 100 g / m 2 basis weight. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例16>
 塩化ジルコニウム 12.87g(55.2mmol)と2-アミノテレフタル酸9.45g(52.5mmol)とをN,N-ジメチルホルムアルデヒド600mLに溶解させ、120℃で24時間加熱し多孔性金属錯体を合成した。得られた多孔性金属錯体について、窒素吸着測定および水蒸気吸着測定により物性評価を行った結果、BET比表面積は949m/g、水分吸着率は32%であった。
 その後、上記合成した多孔性金属錯体を水中に24時間浸漬させた後に、ろ過し、細孔内に溶媒分子が吸着された多孔性金属錯体サンプルを得た。この多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を8質量%、フィブリル化した繊維としてアラミド繊維を5質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 16>
12.87 g (55.2 mmol) of zirconium chloride and 9.45 g (52.5 mmol) of 2-aminoterephthalic acid are dissolved in 600 mL of N, N-dimethylformaldehyde and heated at 120 ° C. for 24 hours to synthesize a porous metal complex. did. As a result of evaluating the physical properties of the obtained porous metal complex by nitrogen adsorption measurement and water vapor adsorption measurement, the BET specific surface area was 949 m 2 / g and the water adsorption rate was 32%.
Then, the synthesized porous metal complex was immersed in water for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores. This porous metal complex sample is 80% by mass (excluding solvent molecules), aramid fiber is 8% by mass as non-fibrillated fiber, aramid fiber is 5% by mass as fibrillated fiber, and the dissolution temperature in water is 70 as an organic binder. Polyvinyl alcohol (PVA) fibers at ° C. (catalog value) were mixed at a ratio of 7% by mass to prepare an adsorption sheet using a wet paper machine at a mass of 100 g / m 2 basis weight. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<実施例17>
 オルトチタン酸テトライソプロピル3.6ml(12.3mmol)と2-アミノテレフタル酸3.6g(19.9mmol)とをN,N-ジメチルホルムアミド48mlおよびメタノール12mlに溶解し、150℃で18時間加熱し多孔性金属錯体を合成した。得られた多孔性金属錯体について、窒素吸着測定および水蒸気吸着測定により物性評価を行った結果、BET比表面積は1248m/g、水分吸着率は43%であった。
 その後、上記合成した多孔性金属錯体を水中に24時間浸漬させた後に、ろ過し、細孔内に溶媒分子が吸着された多孔性金属錯体サンプルを得た。この多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を8質量%、フィブリル化した繊維としてアラミド繊維を5質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Example 17>
3.6 ml (12.3 mmol) of tetraisopropyl orthotitanium and 3.6 g (19.9 mmol) of 2-aminoterephthalic acid were dissolved in 48 ml of N, N-dimethylformamide and 12 ml of methanol, and heated at 150 ° C. for 18 hours. A porous metal complex was synthesized. As a result of evaluating the physical properties of the obtained porous metal complex by nitrogen adsorption measurement and water vapor adsorption measurement, the BET specific surface area was 1248 m 2 / g and the water adsorption rate was 43%.
Then, the synthesized porous metal complex was immersed in water for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores. This porous metal complex sample is 80% by mass (excluding solvent molecules), aramid fiber is 8% by mass as non-fibrillated fiber, aramid fiber is 5% by mass as fibrillated fiber, and the dissolution temperature in water is 70 as an organic binder. Polyvinyl alcohol (PVA) fibers at ° C. (catalog value) were mixed at a ratio of 7% by mass to prepare an adsorption sheet using a wet paper machine at a mass of 100 g / m 2 basis weight. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<比較例1>
 硝酸アルムニウム15g(40mmol)と1,4-ナフタレンジカルボン酸4.32g(20mmol)とを水400mlに溶解し、180℃で24時間加熱し多孔性金属錯体を合成した。得られた多孔性金属錯体について、窒素吸着測定および水蒸気吸着測定により物性評価を行った結果、BET比表面積は639m/g、水分吸着率は17%であった。
 その後、上記合成した多孔性金属錯体を水中に24時間浸漬させた後に、ろ過し、細孔内に溶媒分子が吸着された多孔性金属錯体サンプルを得た。この多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化した繊維としてアラミド繊維を8質量%、フィブリル化した繊維としてアラミド繊維を5質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/m2となる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Comparative example 1>
15 g (40 mmol) of alumnium nitrate and 4.32 g (20 mmol) of 1,4-naphthalenedicarboxylic acid were dissolved in 400 ml of water and heated at 180 ° C. for 24 hours to synthesize a porous metal complex. As a result of evaluating the physical properties of the obtained porous metal complex by nitrogen adsorption measurement and water vapor adsorption measurement, the BET specific surface area was 639 m 2 / g and the water adsorption rate was 17%.
Then, the synthesized porous metal complex was immersed in water for 24 hours and then filtered to obtain a porous metal complex sample in which solvent molecules were adsorbed in the pores. 80% by mass of this porous metal complex sample (excluding solvent molecules), 8% by mass of aramid fiber as fibrillated fiber, 5% by mass of aramid fiber as fibrillated fiber, and 70 ° C. in water as an organic binder. Polyvinyl alcohol (PVA) fibers (catalog value) were mixed at a ratio of 7% by mass, and an adsorption sheet was prepared using a wet paper machine at a mass having a basis weight of 100 g / m 2. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<比較例2>
 実施例1と同様に得られた多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を8質量%、フィブリル化した繊維としてアラミド繊維を5質量%、有機バインダーとして水中溶解温度が60℃(カタログ値)のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Comparative example 2>
80% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 8% by mass of aramid fibers as unfibrillated fibers, and 5% by mass of aramid fibers as fibrillated fibers. As an organic binder, polyvinyl alcohol (PVA) fibers having a dissolution temperature in water of 60 ° C. (catalog value) are mixed at a ratio of 7% by mass, and an adsorption sheet is prepared using a wet paper machine at a mass of 100 g / m 2 basis weight. Made. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<比較例3>
 実施例1と同様に得られた多孔性金属錯体サンプルを65質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を14質量%、フィブリル化した繊維としてアラミド繊維を8.8質量%、有機バインダーとして、水中溶解温度が>100℃(水の沸騰後溶けない場合を示す、カタログ値)のポリビニルアルコール(PVA)繊維を12.2質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Comparative example 3>
65% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 14% by mass of aramid fiber as a non-fibrillated fiber, and 8.8% by mass of aramid fiber as a fibrillated fiber. %, As an organic binder, polyvinyl alcohol (PVA) fibers having a dissolution temperature in water of> 100 ° C. (catalog value indicating the case where the water does not dissolve after boiling) are mixed at a ratio of 12.2% by mass, and the basis weight is 100 g. A suction sheet was prepared using a wet paper making device with a mass of / m 2. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<比較例4>
 実施例1と同様に得られた多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化した繊維としてアラミド繊維を13質量%、有機バインダーとして、水中溶解温度が70℃のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。なお、本比較例では、フィブリル化していない繊維は用いなかった。上記作製した吸着シートをさらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Comparative example 4>
80% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 13% by mass of aramid fiber as a fibrillated fiber, and polyvinyl alcohol having a dissolution temperature in water of 70 ° C. as an organic binder. The (PVA) fiber was mixed at a ratio of 7% by mass, and a suction sheet was prepared using a wet paper machine at a mass of 100 g / m 2 basis weight. In this comparative example, non-fibrillated fibers were not used. The adsorption sheet prepared above was further desolvated for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<比較例5>
 実施例1と同様に得られた多孔性金属錯体サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を13質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。なお、本比較例では、フィブリル化した繊維は用いなかった。上記作製した吸着シートをさらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Comparative example 5>
80% by mass (excluding solvent molecules) of the porous metal complex sample obtained in the same manner as in Example 1, 13% by mass of aramid fiber as a non-fibrillated fiber, and 70 ° C. in water as an organic binder (catalog value). ) Polyvinyl alcohol (PVA) fibers were mixed at a ratio of 7% by mass to prepare an adsorption sheet using a wet paper machine at a mass of 100 g / m 2 basis weight. In this comparative example, fibrillated fibers were not used. The adsorption sheet prepared above was further desolvated for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
<比較例6>
 吸着材としてA形シリカゲル(豊田化工社製)を使用した。窒素吸着測定および水蒸気吸着測定により物性評価を行った結果、BET比表面積は820m/g、水分吸着率は25%であった。
 その後、上記吸着材を水中に24時間浸漬させた後に、ろ過し、細孔内に溶媒分子が吸着された吸着材サンプルを得た。この吸着材サンプルを80質量%(溶媒分子を除く)、フィブリル化していない繊維としてアラミド繊維を8質量%、フィブリル化した繊維としてアラミド繊維を5質量%、有機バインダーとして水中溶解温度が70℃(カタログ値)のポリビニルアルコール(PVA)繊維を7質量%、の比率で混合し、坪量100g/mとなる質量にて湿式抄紙装置を使い吸着シートを作製した。さらに、130℃、真空条件下、24時間で脱溶媒処理を行い、吸着シートサンプルを得た。得られたサンプルについて、担持性、柔軟性、細孔維持率、水蒸気吸着性能、加工性を測定した。
<Comparative Example 6>
A-type silica gel (manufactured by Toyota Kako Co., Ltd.) was used as an adsorbent. As a result of physical property evaluation by nitrogen adsorption measurement and water vapor adsorption measurement, the BET specific surface area was 820 m 2 / g and the water adsorption rate was 25%.
Then, the adsorbent was immersed in water for 24 hours and then filtered to obtain an adsorbent sample in which solvent molecules were adsorbed in the pores. 80% by mass of this adsorbent sample (excluding solvent molecules), 8% by mass of aramid fiber as non-fibrillated fiber, 5% by mass of aramid fiber as fibrillated fiber, and 70 ° C. in water as an organic binder ( Polyvinyl alcohol (PVA) fibers of (catalog value) were mixed at a ratio of 7% by mass, and an adsorption sheet was prepared using a wet papermaking apparatus at a mass of 100 g / m 2 basis weight. Further, the solvent was removed for 24 hours under vacuum conditions at 130 ° C. to obtain an adsorption sheet sample. The supported sample, flexibility, pore retention rate, water vapor adsorption performance, and processability were measured.
 実施例1~17および比較例1~6にて得られた吸着シートサンプルについての測定結果を表1~5に示す。 Tables 1 to 5 show the measurement results of the adsorption sheet samples obtained in Examples 1 to 17 and Comparative Examples 1 to 6.
Figure JPOXMLDOC01-appb-T000001
Figure JPOXMLDOC01-appb-T000001
Figure JPOXMLDOC01-appb-T000002
Figure JPOXMLDOC01-appb-T000002
Figure JPOXMLDOC01-appb-T000003
Figure JPOXMLDOC01-appb-T000003
Figure JPOXMLDOC01-appb-T000004
Figure JPOXMLDOC01-appb-T000004
Figure JPOXMLDOC01-appb-T000005
Figure JPOXMLDOC01-appb-T000005
 表1~5から、実施例1~17の吸着シートは、多孔性金属錯体の担持性、および、シートの柔軟性・加工性に優れており、かつ十分な吸着性能を有していることがわかる。 From Tables 1 to 5, the adsorption sheets of Examples 1 to 17 are excellent in the supportability of the porous metal complex, the flexibility and processability of the sheet, and have sufficient adsorption performance. Understand.
 本発明の吸着シート、吸着エレメント、吸脱着処理装置によれば、水分、有機溶剤、および、悪臭成分等の吸着対象物質を効率的に分離回収または吸着除去することができるようになる。よって、産業界に大きく寄与することが期待できる。 According to the adsorption sheet, adsorption element, and adsorption / desorption treatment device of the present invention, it becomes possible to efficiently separate, recover, or adsorb and remove water, organic solvent, and substances to be adsorbed such as malodorous components. Therefore, it can be expected to greatly contribute to the industrial world.
1:吸着シート、2:吸着式ローター、3:モーター、4:高湿度気体、
5:除湿後気体、6:低湿度気体、7:加湿後気体、8:熱源、9:ファン
10:除湿・加湿領域区切部材、11:デシカント空調システム
 
1: Adsorption sheet 2: Adsorption rotor, 3: Motor, 4: High humidity gas,
5: Gas after dehumidification, 6: Low humidity gas, 7: Gas after humidification, 8: Heat source, 9: Fan 10: Dehumidifying / humidifying area dividing member, 11: Desiccant air conditioning system

Claims (6)

  1.  金属および有機配位子を有し、25℃、相対圧0.5での水分吸着率が30質量%以上である多孔性金属錯体と、
     フィブリル化していない繊維およびフィブリル化した繊維と、を含有することを特徴とする吸着シート。
    A porous metal complex having a metal and an organic ligand and having a water adsorption rate of 30% by mass or more at 25 ° C. and a relative pressure of 0.5.
    An adsorption sheet containing non-fibrillated fibers and fibrillated fibers.
  2.  水中溶解温度が65℃~100℃の有機バインダーを含有する、ことを特徴とする請求項1に記載の吸着シート。 The adsorption sheet according to claim 1, wherein the adsorption sheet contains an organic binder having a dissolution temperature in water of 65 ° C. to 100 ° C.
  3.  比引張伸度が5%m/g以上である、ことを特徴とする請求項1または2に記載の吸着シート。 The adsorption sheet according to claim 1 or 2, wherein the specific tensile elongation is 5% m / g or more.
  4.  前記多孔性金属錯体を60~85質量%含有する、ことを特徴とする請求項1から3のいずれか1項に記載の吸着シート。 The adsorption sheet according to any one of claims 1 to 3, wherein the porous metal complex is contained in an amount of 60 to 85% by mass.
  5.  請求項1から4のいずれか1項に記載の吸着シートを備える、ことを特徴とする吸着エレメント。 A suction element comprising the suction sheet according to any one of claims 1 to 4.
  6.  請求項5に記載の吸着エレメントと、
     前記吸着エレメントに吸着対象物質を導入して吸着させる吸着手段と、
     前記吸着エレメントが吸着した吸着対象物質を脱着させる脱着手段と、を備え、吸着対象物質の吸脱着を連続的に行う、ことを特徴とする吸脱着処理装置。
     
    The adsorption element according to claim 5 and
    An adsorption means for introducing a substance to be adsorbed into the adsorption element and adsorbing the substance,
    A suction / desorption processing apparatus comprising: a desorption means for desorbing a substance to be adsorbed by the adsorption element, and continuously adsorbing / desorbing the substance to be adsorbed.
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