WO2021000974A1 - Air filtration filter material - Google Patents
Air filtration filter material Download PDFInfo
- Publication number
- WO2021000974A1 WO2021000974A1 PCT/CZ2020/050048 CZ2020050048W WO2021000974A1 WO 2021000974 A1 WO2021000974 A1 WO 2021000974A1 CZ 2020050048 W CZ2020050048 W CZ 2020050048W WO 2021000974 A1 WO2021000974 A1 WO 2021000974A1
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- WO
- WIPO (PCT)
- Prior art keywords
- woven
- layer
- polypropylene
- filtration
- meltblown
- Prior art date
Links
- 238000001914 filtration Methods 0.000 title claims abstract description 68
- 239000000463 material Substances 0.000 title claims abstract description 52
- 239000004753 textile Substances 0.000 claims abstract description 51
- 239000011148 porous material Substances 0.000 claims abstract description 12
- 238000009826 distribution Methods 0.000 claims abstract description 11
- 238000004378 air conditioning Methods 0.000 claims abstract description 4
- 238000004140 cleaning Methods 0.000 claims abstract description 3
- 238000005192 partition Methods 0.000 claims abstract description 3
- 239000011882 ultra-fine particle Substances 0.000 claims abstract 2
- 239000004743 Polypropylene Substances 0.000 claims description 54
- 229920001155 polypropylene Polymers 0.000 claims description 54
- 239000002033 PVDF binder Substances 0.000 claims description 32
- 229920002981 polyvinylidene fluoride Polymers 0.000 claims description 31
- -1 polypropylene Polymers 0.000 claims description 20
- 229920000297 Rayon Polymers 0.000 claims description 11
- 239000004814 polyurethane Substances 0.000 claims description 11
- 229920002635 polyurethane Polymers 0.000 claims description 11
- 229920000139 polyethylene terephthalate Polymers 0.000 claims description 10
- 229920000642 polymer Polymers 0.000 claims description 10
- 239000000758 substrate Substances 0.000 claims description 10
- 239000000835 fiber Substances 0.000 claims description 9
- 239000005020 polyethylene terephthalate Substances 0.000 claims description 9
- 229920001410 Microfiber Polymers 0.000 claims description 7
- 239000003658 microfiber Substances 0.000 claims description 7
- 239000000203 mixture Substances 0.000 claims description 7
- 229920002292 Nylon 6 Polymers 0.000 claims description 6
- 229920002301 cellulose acetate Polymers 0.000 claims description 5
- 229920002037 poly(vinyl butyral) polymer Polymers 0.000 claims description 5
- 229920002239 polyacrylonitrile Polymers 0.000 claims description 5
- 239000004626 polylactic acid Substances 0.000 claims description 5
- 239000004793 Polystyrene Substances 0.000 claims description 3
- 239000004721 Polyphenylene oxide Substances 0.000 claims description 2
- 229920000570 polyether Polymers 0.000 claims description 2
- 125000001174 sulfone group Chemical group 0.000 claims description 2
- 239000002121 nanofiber Substances 0.000 abstract description 11
- 239000002245 particle Substances 0.000 description 11
- 239000002086 nanomaterial Substances 0.000 description 6
- 238000004519 manufacturing process Methods 0.000 description 5
- 239000000443 aerosol Substances 0.000 description 3
- 239000010419 fine particle Substances 0.000 description 3
- 230000008092 positive effect Effects 0.000 description 3
- 238000011156 evaluation Methods 0.000 description 2
- 239000002657 fibrous material Substances 0.000 description 2
- 238000005304 joining Methods 0.000 description 2
- 208000034530 PLAA-associated neurodevelopmental disease Diseases 0.000 description 1
- 239000005662 Paraffin oil Substances 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000001747 exhibiting effect Effects 0.000 description 1
- 239000004744 fabric Substances 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 239000002105 nanoparticle Substances 0.000 description 1
- 239000012188 paraffin wax Substances 0.000 description 1
- 230000000149 penetrating effect Effects 0.000 description 1
- 230000035515 penetration Effects 0.000 description 1
- 229920000747 poly(lactic acid) Polymers 0.000 description 1
- 239000012462 polypropylene substrate Substances 0.000 description 1
- 229920002223 polystyrene Polymers 0.000 description 1
- 238000011045 prefiltration Methods 0.000 description 1
- 238000009958 sewing Methods 0.000 description 1
- 238000003466 welding Methods 0.000 description 1
Classifications
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- B01D39/14—Other self-supporting filtering material ; Other filtering material
- B01D39/16—Other self-supporting filtering material ; Other filtering material of organic material, e.g. synthetic fibres
- B01D39/1607—Other self-supporting filtering material ; Other filtering material of organic material, e.g. synthetic fibres the material being fibrous
- B01D39/1623—Other self-supporting filtering material ; Other filtering material of organic material, e.g. synthetic fibres the material being fibrous of synthetic origin
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01D39/14—Other self-supporting filtering material ; Other filtering material
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01D39/16—Other self-supporting filtering material ; Other filtering material of organic material, e.g. synthetic fibres
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- B01D39/18—Other self-supporting filtering material ; Other filtering material of organic material, e.g. synthetic fibres the material being cellulose or derivatives thereof
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- B32B5/26—Layered products characterised by the non- homogeneity or physical structure, i.e. comprising a fibrous, filamentary, particulate or foam layer; Layered products characterised by having a layer differing constitutionally or physically in different parts characterised by the presence of two or more layers which are next to each other and are fibrous, filamentary, formed of particles or foamed one layer being a fibrous or filamentary layer another layer next to it also being fibrous or filamentary
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- B01D2239/02—Types of fibres, filaments or particles, self-supporting or supported materials
- B01D2239/025—Types of fibres, filaments or particles, self-supporting or supported materials comprising nanofibres
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- B01D2239/06—Filter cloth, e.g. knitted, woven non-woven; self-supported material
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- B01D2239/0627—Spun-bonded
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Definitions
- the technical solution relates to a filtration material intended for air filtering, the filtration material being based on a combination of spun bond (SB) and/or meltblown (MB) and electrospun (ES) non-woven textiles (NT).
- This material can be easily processed by welding or sewing to make filtering facepieces - face masks, respirators, half-masks, pocket filters, filters for automobile interiors and simple or folded partitions for mask filters, air-conditioning devices and similar protection applications for cleaning particle-contaminated air.
- filtration materials made from non-woven textiles (NT) or fabrics are used, which, however, do not optimally meet the properties required by manufacturers of filtration products, i.e. maximum filtration efficiency at the minimum possible pressure drop.
- the filtration materials are assessed according to EN 143, EN 149, EN 779 - 2011 European standards, which specify requirements for filtration efficiency (FE) and pressure drop (Ap) for filtered particles 400 nm in size, and according to EN 1822 - 2009 standard defining requirements for filtration efficiency (FE) at a place where the nanoparticles penetration is maximum one (maximum penetrating particle size - MPPS) - consequently, an extreme in the dependence of filtration efficiency on particle size (a V-shaped curve).
- the most significant mechanism of eliminating fine particles from air with ES filters is that of particle capture (see Fig. 1).
- a disadvantage of the currently used filtration materials based on meltblown (MB) non- woven textiles is a lower capture of very fine particles (10 - 400 nm in size).
- MB meltblown
- an increase in the content of the meltblown (MB) fibrous material results in an excessive increase of the filter pressure drop.
- At least one layer of spun bond (SB) and/or meltblown (MB) non-woven textile having a mass per unit surface area of 15 to 100 g/ m 2 , a distribution of fibre diameters of 200 nm to 8000 nm and a mean pore size greater than 1200 nm and
- ES non-woven nanotextile having a mass per unit surface area of 0.05 to 4 g/ m 2 , a distribution of fibre diameters in the range of 40 nm to 400 nm and a mean pore size of 200 to 1800 nm.
- the spun bond (SB) and/or meltblown (MB) non-woven textile is made advantageously from fibres based on a polymer selected from a group of polymers including polypropylene (PP), polyethylene terephthalate (PET), polyurethanes (PU), polylactic acid (PLA) and polyamide 6 (PA6).
- PP polypropylene
- PET polyethylene terephthalate
- PU polyurethanes
- PLA polylactic acid
- PA6 polyamide 6
- the layer of the electrospun (ES) non-woven nanotextile is made advantageously from nanofibres based on a polymer from a group of polymers comprising polyvinylidene fluoride (PVDF), polyurethanes (PU), polylactic acid (PLA), polyamide 6 (PA6), polyacrylonitrile (PAN), cellulose acetate (CA), polystyrene (PS), polyether sulphone (PESU) and polyvinyl butyral (PVB).
- PVDF polyvinylidene fluoride
- PU polyurethanes
- PLA polylactic acid
- PA6 polyamide 6
- PAN polyacrylonitrile
- CA cellulose acetate
- PS polystyrene
- PESU polyether sulphone
- PVB polyvinyl butyral
- MB meltblown
- SB spun-bond
- ES electrospun
- MB meltblown
- SB spun bond
- PP polypropylene
- ES electrospun
- PVDF polyvinylidene fluoride
- MB meltblown
- PET polyethylene terephthalate
- ES electrospun
- the layer composition being a spunbond (SB) polypropylene (PP) layer - meltblown (MB) polypropylene (PP) layer - non-woven nanotextile made from polyvinylidene fluoride (PVDF) nanofibers - meltblown (MB) polypropylene (PP) layer - spunbond (SB) polypropylene (PP) layer.
- SB spunbond
- PP polypropylene
- MB meltblown
- PP polypropylene
- PP non-woven nanotextile made from polyvinylidene fluoride
- PVDF polyvinylidene fluoride
- Fig. 1 An image of electrospun (ES) nanostructure containing captured particles 20 - 400 nm in size; magnification: lOOOOx;
- Fig. 2 A scanning electron microscope (SEM) image of the meltblown (MB) structure, magnification: 4000x;
- Fig. 3 An image of an electrospun (ES) nanostructure, magnification: 40000x;
- Fig. 4 - 3D models (a) meltblown (MB) structure (b), electrospun (ES) nanostructure, (c) combination of meltblown (MB) structure and electrospun (ES) nanostructure;
- Fig. 5 Experimental data for filtration materials based on meltblown (MB) structure, electrospun (ES) nanostructure and a combination of meltblown (MB) structure and electrospun (ES) nanostructure.
- the multilayer structure of the filtration material in the exemplary embodiment contains a combination of a non-woven textile comprising an MB layer from PP (see Figs 2 and 4a) deposited onto a SB substrate made from PP with an ES non-woven nanotextile (see Figs. 3 and 4b) made from PVDF nanofibers.
- the MB PP layer has a mass per unit surface area of 25 g / m 2 , a fibre diameter distribution of 500 nm to 5000 nm and a mean pore size of 1900 nm.
- the MB PP layer was deposited onto the SB PP substrate having a mass per unit surface area of 17 g/m 2 .
- ES non-woven nanotextile made from PVDF nanofibers has a mass per unit surface area of 0.2 g / m 2 , a fibre diameter distribution ranging from 40 to 400 nm and a mean pore size of 1100 nm.
- a filtration material intended for making half-masks features a multilayer structure comprising a combination of MB and SB non-woven textiles made from PP microfibers and an ES non-woven nanotextile made from PVDF nanofibers, the multilayer structure lying on a viscose (VS) substrate.
- the microfibre material made from PP microfibres is produced by joining SB and MB non-woven textiles having a mass per unit surface areas of 17 and 25 g/m 2 , consequently, a total mass per unit surface area of 42 g/m 2 , an MB fibre diameter distribution ranging from 500 to 1500 nm and a mean pore size of 1900 nm.
- ES non- woven nanotextile made from PVDF nanofibres having a mass per unit surface area of 0.5 g/m 2 , a fibre diameter distribution ranging from 40 to 400 nm and a mean pore size of 800 nm is deposited onto a non-woven VS substrate having a mass per unit surface area of 55 g/m 2 .
- the example documents an improvement of filtration properties of the materials for half-masks evaluated in compliance with EN 149 standard, which makes use of aerosol having an average particle size of 400 nm for evaluation of the filtration capacity.
- the composition of the multilayer material is identical with that given in Example 2, the difference consisting in the fact that the ES non-woven textile has a mass per unit surface area of 2.3 g/m 2 , a fibre diameter distribution ranging from 40 to 400 nm and a mean pore size of 255 nm.
- This material was used for production of folded filters for HEPA filtration in air- conditioning units.
- a positive effect of the combination of MB and ES non-woven textile was demonstrated in two tests where the material described was subjected to identical flow of contaminated air from the side of the VS SB material as well as from the opposite side of PP MB non-woven textile. In case of filtration from the side of the MB non-woven textile the filter capacity increased by 32% due to a more efficient prefiltration.
- the filtration material is analogical to that described in Example 2 but instead of a layer of nanofibres on VS a non-woven textile made from a blend of PP and PET staple fibres having a mass per unit surface area of 30 g/m 2 was used as an underlying substrate.
- filtration material intended for production of filtering facepieces features a multilayer structure created as a sandwich having the layer composition as follows: SB PP layer - MB PP layer - non-woven textile from PVDF nanofibres -MB PP layer - SB PP layer.
- the sandwich material has a total mass per unit surface area of 84.5 g/m 2
- the non-woven nanotextile made from PVDF nanofibres has a mass per unit surface area of 0.48 g/m 2 .
- This example documents an improvement of filtration properties of the material for production of filters for particle filtering according to EN 143 standard, i. e. face masks, respirators, etc.
- This standard similarly like EN 149, employs for evaluation of filtration capacities aerosol having a particle size of 400 nm.
- a similar material without any layer of non-woven textile, produced from SB/MB materials only and having identical pressure resistance, was able to capture particles 400 nm in size to about 90% only and the material meeting requirements for filtration efficiency of 99.95 % made from layers of SB/MB non-woven textile only and having a mass per unit surface area of 120 g/m 2 , exhibited a pressure resistance of Dr 184 Pa, as measured at a flow rate of 30 1/min.; therefore, it complied only with class 2 specified in EN 143 standard.
- the sixth example of the technical embodiment assesses a situation when the same non- woven nanotextile combined with either SB non-woven textile or MB non-woven textile is used in all cases.
- a comparison is made of sandwiches of VS SB non-woven textile - 0.2 g/m 2 PVDF non-woven nanotextile - PP SB and VS SB non-woven textile - 0.2 g/m 2 PVDF non-woven nanotextile - PP MB non-woven textile.
- the filtration class F9 decreased to class F8, as determined according to EN 779-2011 standard, which shows a positive effect of the MB non-woven textile and ES non-woven nano textile combination.
- MB non-woven textile in combination with ES nanofibres showed very desirable features also when employed for manufacture of filtration bags used in the food industry.
- Three- layer sandwiches comprising SB non-woven textile - non-woven nanotextile - SB non-woven textile + MB non-woven textile - non-woven nanotextile - SB non-woven textile contained an identical ES non-woven nanotextile made from polyurethane nanofibres having a mass per unit surface area of 1.4 g/m 2 , a mean pore size of 320 nm and an identical filtration performance.
- the filtration material containing the MB layer had a 41% longer lifetime than the material produced from SB non- woven textile only.
- Comparable results with the materials according to Examples 1 to 8 are obtained also with the materials containing a layer of SB and/or MB non-woven textile from the group of polymers including PET, PU, PLA and PA6 instead of the presented PP.
- a similar case is that of a layer of ES non-woven nanotextile, which can alternatively be also produced from nanofibres based on a polymer from a group comprising PU, PLA, PA6, PAN, CA, PS, PESU and PVB while achieving results comparable with those attained when PVDF was used.
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- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Engineering & Computer Science (AREA)
- Textile Engineering (AREA)
- Filtering Materials (AREA)
- Nonwoven Fabrics (AREA)
- Laminated Bodies (AREA)
Abstract
A filtration material for air filtering intended particularly for use in filtration products for cleaning particle-contaminated air, including that contaminated with ultrafine particles 1 to 1000 nm in size, such as - face masks, respirators, half-masks, textile filtration bags, pocket filters, filters for automobile interiors and simple or folded partitions for mask filters and air- conditioning devices, featuring a multilayer structure. The multilayer structure comprises at least one layer of spun bond (SB) and/or meltblown (MB) non- woven textile having a mass per unit surface area of 15 to 100 g/m2, a distribution of nanofibre diameters ranging from 200 to 8000 nm and a mean pore size exceeding 1200 nm, and at least one layer of electro spun (ES) non-woven nanotextile having a mass per unit surface area of 0.05 to 4 g/m2, a distribution of nanofibre diameters ranging from 40 to 400 nm and a mean pore size of 200 to 1800 nm.
Description
AIR FILTRATION FILTER MATERIAL
Field of invention
The technical solution relates to a filtration material intended for air filtering, the filtration material being based on a combination of spun bond (SB) and/or meltblown (MB) and electrospun (ES) non-woven textiles (NT). This material can be easily processed by welding or sewing to make filtering facepieces - face masks, respirators, half-masks, pocket filters, filters for automobile interiors and simple or folded partitions for mask filters, air-conditioning devices and similar protection applications for cleaning particle-contaminated air.
Description of the prior art
At present, for the above applications filtration materials made from non-woven textiles (NT) or fabrics are used, which, however, do not optimally meet the properties required by manufacturers of filtration products, i.e. maximum filtration efficiency at the minimum possible pressure drop.
The filtration materials are assessed according to EN 143, EN 149, EN 779 - 2011 European standards, which specify requirements for filtration efficiency (FE) and pressure drop (Ap) for filtered particles 400 nm in size, and according to EN 1822 - 2009 standard defining requirements for filtration efficiency (FE) at a place where the nanoparticles penetration is maximum one (maximum penetrating particle size - MPPS) - consequently, an extreme in the dependence of filtration efficiency on particle size (a V-shaped curve). The most significant mechanism of eliminating fine particles from air with ES filters is that of particle capture (see Fig. 1).
A disadvantage of the currently used filtration materials based on meltblown (MB) non- woven textiles is a lower capture of very fine particles (10 - 400 nm in size). In order to improve the fine particle capture capacity it is necessary to increase the content of the meltblown (MB) fibrous material in the filter. However, an increase in the content of the meltblown (MB) fibrous material results in an excessive increase of the filter pressure drop.
Nature of the technical solution
The shortcomings described above can be eliminated to a great extent with the filtration material for air filtering in compliance with the technical solution submitted here. The nature of the solution consists in the fact that the multilayer structure of this material comprises
- at least one layer of spun bond (SB) and/or meltblown (MB) non-woven textile having a mass per unit surface area of 15 to 100 g/ m2, a distribution of fibre diameters of 200 nm to 8000 nm and a mean pore size greater than 1200 nm and
- at least one layer of electrospun (ES) non-woven nanotextile having a mass per unit surface area of 0.05 to 4 g/ m2, a distribution of fibre diameters in the range of 40 nm to 400 nm and a mean pore size of 200 to 1800 nm.
The spun bond (SB) and/or meltblown (MB) non-woven textile is made advantageously from fibres based on a polymer selected from a group of polymers including polypropylene (PP), polyethylene terephthalate (PET), polyurethanes (PU), polylactic acid (PLA) and polyamide 6 (PA6).
The layer of the electrospun (ES) non-woven nanotextile is made advantageously from nanofibres based on a polymer from a group of polymers comprising polyvinylidene fluoride (PVDF), polyurethanes (PU), polylactic acid (PLA), polyamide 6 (PA6), polyacrylonitrile (PAN), cellulose acetate (CA), polystyrene (PS), polyether sulphone (PESU) and polyvinyl butyral (PVB).
Several preferred multilayer structures of the filtration material have been produced with respect to the specific composition of the layers, namely:
a) a multilayer structure containing a non-woven textile based on a combination of a meltblown (MB) polypropylene (PP) layer deposited onto a spun-bond (SB) polypropylene substrate and an electrospun (ES) non-woven nanotextile made from polyvinylidene fluoride (PVDF) nanofibers;
b) a multilayer structure containing a double-layer of meltblown (MB) and spun bond (SB) non-woven textiles from polypropylene (PP) microfibers joined with an electrospun (ES) non-woven nano textile made from polyvinylidene fluoride (PVDF) nanofibers, the multilayer structure lying on a viscose substrate;
c) a multilayer structure containing a combination of meltblown (MB) non-woven textile made from a blend of polypropylene (PP) and polyethylene terephthalate (PET) staple fibres, and
electrospun (ES) non-woven nanotextile made from polyvinylidene fluoride (PVDF) nanofibers;
d) the multilayer structure created as a sandwich, the layer composition being a spunbond (SB) polypropylene (PP) layer - meltblown (MB) polypropylene (PP) layer - non-woven nanotextile made from polyvinylidene fluoride (PVDF) nanofibers - meltblown (MB) polypropylene (PP) layer - spunbond (SB) polypropylene (PP) layer.
Drawings
Fig. 1 - An image of electrospun (ES) nanostructure containing captured particles 20 - 400 nm in size; magnification: lOOOOx;
Fig. 2 - A scanning electron microscope (SEM) image of the meltblown (MB) structure, magnification: 4000x;
Fig. 3 - An image of an electrospun (ES) nanostructure, magnification: 40000x;
Fig. 4 - 3D models: (a) meltblown (MB) structure (b), electrospun (ES) nanostructure, (c) combination of meltblown (MB) structure and electrospun (ES) nanostructure;
Fig. 5 - Experimental data for filtration materials based on meltblown (MB) structure, electrospun (ES) nanostructure and a combination of meltblown (MB) structure and electrospun (ES) nanostructure.
Examples of implemented technical solution (embodiments)
Example 1
The multilayer structure of the filtration material in the exemplary embodiment (see Fig. 4c) contains a combination of a non-woven textile comprising an MB layer from PP (see Figs 2 and 4a) deposited onto a SB substrate made from PP with an ES non-woven nanotextile (see Figs. 3 and 4b) made from PVDF nanofibers. The MB PP layer has a mass per unit surface area of 25 g / m2, a fibre diameter distribution of 500 nm to 5000 nm and a mean pore size of 1900 nm. The MB PP layer was deposited onto the SB PP substrate having a mass per unit surface area of 17 g/m2. ES non-woven nanotextile made from PVDF nanofibers has a mass per unit surface area of 0.2 g / m2, a fibre diameter distribution ranging from 40 to 400 nm and a mean pore size of 1100 nm.
Filtration effects of the material according to Example 1 are illustrated in a clear manner in Fig. 5. As it is obvious here, in case of particles approximately 103 nm in size, the MB PP
structure alone (according to Fig. 4a) deposited onto the SB PP substrate exhibits a filtration efficiency of 55% and a pressure drop of Dr = 42 Pa. The ES non- woven nanotextile (according to Fig. 4b) made from PVDF nano fibers has a filtration efficiency FE = 65% and a pressure drop Dr of 20 Pa only. A combination of the MB and ES structures described (according to Fig. 4c) results in a filtration material having a filtration efficiency FE = 82% for particles 40 nm in size and a pressure drop Dr of 61 Pa only. Hence it results in a material corresponding already to almost E 10 filtration class (according to EN 1822 standard) while exhibiting a lower pressure drop, as measured at the front speed of 5.7 cm/s, which corresponds to an air flow rate of 30 1/min.
Example 2
Another example of a filtration material intended for making half-masks features a multilayer structure comprising a combination of MB and SB non-woven textiles made from PP microfibers and an ES non-woven nanotextile made from PVDF nanofibers, the multilayer structure lying on a viscose (VS) substrate. The microfibre material made from PP microfibres is produced by joining SB and MB non-woven textiles having a mass per unit surface areas of 17 and 25 g/m2, consequently, a total mass per unit surface area of 42 g/m2, an MB fibre diameter distribution ranging from 500 to 1500 nm and a mean pore size of 1900 nm. ES non- woven nanotextile made from PVDF nanofibres having a mass per unit surface area of 0.5 g/m2, a fibre diameter distribution ranging from 40 to 400 nm and a mean pore size of 800 nm is deposited onto a non-woven VS substrate having a mass per unit surface area of 55 g/m2.
The example documents an improvement of filtration properties of the materials for half-masks evaluated in compliance with EN 149 standard, which makes use of aerosol having an average particle size of 400 nm for evaluation of the filtration capacity. The material from PP microfibres produced by joining two SB/MB non-woven textiles features an inhalation resistance of Dr = 229 Pa and a filtration efficiency FE = 94 %, as measured with paraffin oil at an air flow rate of 95 1/min. and corresponds to FFP2 class. Corresponding minimum requirements specified in EN 149 standard for class 2 under the above given conditions of the test using the paraffin aerosol are Dr = 240 Pa and filtration efficiency FE = 94%. A material having approximately the same pressure resistance of Dr = 213 Pa can be produced by combining SB/MB non-woven textiles having mass per unit surface areas of 17/25 g/m2 with a material produced by applying 0.5 g/m2 PVDF nanofibres onto a VS substrate having a mass per unit surface area of 55 g/m2. The filtration efficiency of such a combination, in comparison
with the original SB/MB material containing no nanofibers, increases markedly up to FE = 99.6%. Consequently, the material features a FFP3 filtration class, the minimum requirements at a flow rate of 95 1/min being Dr < 300 Pa and filtration efficiency FE > 99,0 %.
Example 3
The composition of the multilayer material is identical with that given in Example 2, the difference consisting in the fact that the ES non-woven textile has a mass per unit surface area of 2.3 g/m2, a fibre diameter distribution ranging from 40 to 400 nm and a mean pore size of 255 nm. This material was used for production of folded filters for HEPA filtration in air- conditioning units. A positive effect of the combination of MB and ES non-woven textile was demonstrated in two tests where the material described was subjected to identical flow of contaminated air from the side of the VS SB material as well as from the opposite side of PP MB non-woven textile. In case of filtration from the side of the MB non-woven textile the filter capacity increased by 32% due to a more efficient prefiltration.
Example 4
The filtration material is analogical to that described in Example 2 but instead of a layer of nanofibres on VS a non-woven textile made from a blend of PP and PET staple fibres having a mass per unit surface area of 30 g/m2 was used as an underlying substrate. Filtration performance achieved under identical conditions was as follows: filtration efficiency FE > 99.5 % and pressure resistance Ap = 87 up to 98 Pa at an air flow rate of 30 1/min., or 257 up to 289 Pa at an air flow rate of 95 1/min. (as measured with the Lorenz 143 apparatus). Consequently, by combining MB non-woven textiles and ES non-woven nanotextile the filtration class of FFP3 was attained again.
Example 5
Another example of the filtration material intended for production of filtering facepieces features a multilayer structure created as a sandwich having the layer composition as follows: SB PP layer - MB PP layer - non-woven textile from PVDF nanofibres -MB PP layer - SB PP layer. The sandwich material has a total mass per unit surface area of 84.5 g/m2, the non-woven nanotextile made from PVDF nanofibres has a mass per unit surface area of 0.48 g/m2.
This example documents an improvement of filtration properties of the material for production of filters for particle filtering according to EN 143 standard, i. e. face masks,
respirators, etc. This standard, similarly like EN 149, employs for evaluation of filtration capacities aerosol having a particle size of 400 nm. The sandwich material exhibited a pressure resistance Dr = 93 up to 109 Pa at a flow rate of 30 1/min. (requirement of the standard: < 120 Pa) and filtration efficiency FE = 99.96 - 99.99 % (requirement of the standard: > 99.95 %). Consequently, this material meets the requirements for materials of P3 class according to EN 143 standard. A similar material without any layer of non-woven textile, produced from SB/MB materials only and having identical pressure resistance, was able to capture particles 400 nm in size to about 90% only and the material meeting requirements for filtration efficiency of 99.95 % made from layers of SB/MB non-woven textile only and having a mass per unit surface area of 120 g/m2, exhibited a pressure resistance of Dr = 184 Pa, as measured at a flow rate of 30 1/min.; therefore, it complied only with class 2 specified in EN 143 standard.
Example 6
The sixth example of the technical embodiment assesses a situation when the same non- woven nanotextile combined with either SB non-woven textile or MB non-woven textile is used in all cases. A comparison is made of sandwiches of VS SB non-woven textile - 0.2 g/m2PVDF non-woven nanotextile - PP SB and VS SB non-woven textile - 0.2 g/m2 PVDF non-woven nanotextile - PP MB non-woven textile. In case of the material having no MB non-woven textile, the filtration class F9 decreased to class F8, as determined according to EN 779-2011 standard, which shows a positive effect of the MB non-woven textile and ES non-woven nano textile combination.
Example 7
A positive effect of combining a MB non-woven textile with a non-woven nanotextile became apparent also in manufacture of HEPA 15 filtration materials, when assessed in compliance with EN 1822-2009 standard. The sandwich of VS SB non-woven textile - 2.7 g/m2 PVDF non-woven nanotextile - PP MB non-woven textile exhibited a filtration efficiency FE = 99.9994 % at a pressure resistance of Dr = 234 Pa, while HEPA 15 filters made from glass microfibres exhibited a pressure resistance Dr up to 413 Pa at the corresponding filtration efficiency.
Example 8
MB non-woven textile in combination with ES nanofibres showed very desirable features also when employed for manufacture of filtration bags used in the food industry. Three-
layer sandwiches comprising SB non-woven textile - non-woven nanotextile - SB non-woven textile + MB non-woven textile - non-woven nanotextile - SB non-woven textile contained an identical ES non-woven nanotextile made from polyurethane nanofibres having a mass per unit surface area of 1.4 g/m2, a mean pore size of 320 nm and an identical filtration performance. When polluted air passed from the side of an MB non-woven textile, the filtration material containing the MB layer had a 41% longer lifetime than the material produced from SB non- woven textile only.
Example 9
Comparable results with the materials according to Examples 1 to 8 are obtained also with the materials containing a layer of SB and/or MB non-woven textile from the group of polymers including PET, PU, PLA and PA6 instead of the presented PP.
A similar case is that of a layer of ES non-woven nanotextile, which can alternatively be also produced from nanofibres based on a polymer from a group comprising PU, PLA, PA6, PAN, CA, PS, PESU and PVB while achieving results comparable with those attained when PVDF was used.
Claims
1. A filtration material for air filtering intended particularly for use in filtration products for cleaning particle-contaminated air, including that contaminated with ultrafine particles 1 to 1000 nm in size, such as filtering facepieces - face masks, respirators, , half-masks, textile filtration bags, pocket filters, filters for automobile interiors and simple or folded partitions for mask filters and air-conditioning devices characterized in that its multilayer structure contains at least one layer of spun bond (SB) and/or meltblown (MB) non-woven textile having a mass per unit surface area of 15 to 100 g/m2, a distribution of fibre diameters ranging from 200 nm to 8000 nm and a mean pore size exceeding 1200 nm, and at least one layer of electrospun (ES) non-woven nanotextile having a mass per unit surface area of 0.05 to 4 g/m2, a distribution of fibre diameters ranging from 40 up to 400 nm and a mean pore size of 200 to 1800 nm.
2. A filtration material according to Claim 1, characterized in that the layer of spun bond (SB) and/or meltblown (MB) non-woven textile is made from fibres based on a polymer from a group of polymers including polypropylene (PP), polyethylene terephthalate (PET), polyurethanes (PU), polylactic acid (PLA) and polyamide 6 (PA6).
3. A filtration material according to Claim 1, characterized in that the layer of electrospun (ES) non-woven textile is made from nano fibres on the basis of a polymer from a group of polymers including polyvinylidene fluoride (PVDF), polyurethanes (PU), polylactic acid (PLA), polyamide 6 (PA6), polyacrylonitrile (PAN), cellulose acetate (CA), polystyrene (PS), polyether sulphone (PESU) and polyvinyl butyral (PVB).
4. A filtration material according to Claims 1 to 3, characterized in that its multilayer structure contains a non-woven textile based on a combination of meltblown (MB) polypropylene (PP) layer deposited onto a spun bond (SB) polypropylene (PP) substrate provided with a layer of electrospun (ES) non-woven nanotextile made from polyvinylidene fluoride (PVDF) nanofibres.
5. A filtration material according to Claims 1 to 3, characterized in that its multilayer structure contains a combination of a double layer comprising meltblown (MB) and spun bond (SB) non-
woven textiles made from polypropylene (PP) microfibres with electrospun (ES) non-woven nanotextile made from polyvinylidene fluoride (PVDF) nanofibres lying on a viscose substrate.
6. A filtration material according to Claims 1 to 3, characterized in that its multilayer structure contains a combination of meltblown (MB) non-woven textile made from a blend of polypropylene (PP) and polyethylene terephtalate (PET) staple fibres and electrospun (ES) non- woven nanotextile made from polyvinylidene fluoride (PVDF) nanofibres.
7. A filtration material according to Claims 1 to 3, characterized in that its multilayer structure is created as a sandwich comprising layers as follows: spunbond (SB) polypropylene (PP) layer meltblown (MB) polypropylene (PP) layer - non- woven nanotextile made from polyvinylidene fluoride (PVDF) nano fibres - meltblown (MB) polypropylene (PP) layer - spunbond (SB) polypropylene (PP) layer.
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FR3106135A1 (en) * | 2020-06-19 | 2021-07-16 | Arkema France | PROCESS FOR RECYCLING RESPIRATORY PROTECTIVE MASKS |
WO2021255401A1 (en) * | 2020-06-19 | 2021-12-23 | Arkema France | Pvdf filtering face-piece respirator and recycling method |
CN114801393A (en) * | 2022-03-31 | 2022-07-29 | 金发科技股份有限公司 | Multi-scale fiber filter layer and preparation method and application thereof |
FR3126341A1 (en) * | 2021-08-30 | 2023-03-03 | Mdb Texinov | PROTECTIVE MASK, HALF-MASK AND FILTERING OBJECT |
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CZ202070A3 (en) * | 2020-02-13 | 2020-12-16 | Univerzita Tomáše Bati ve Zlíně | Method of manufacturing a filter membrane |
US20230144786A1 (en) * | 2020-04-03 | 2023-05-11 | King's Flair Innovative Marketing Limited | Novel filter material, face mask comprising the same and method of making the same |
WO2021224115A1 (en) * | 2020-05-08 | 2021-11-11 | Basf Se | Filter on the basis of a nonwoven composite material |
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Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
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FR3106135A1 (en) * | 2020-06-19 | 2021-07-16 | Arkema France | PROCESS FOR RECYCLING RESPIRATORY PROTECTIVE MASKS |
WO2021255402A1 (en) * | 2020-06-19 | 2021-12-23 | Arkema France | Method for recycling filtering facepiece respirators |
WO2021255401A1 (en) * | 2020-06-19 | 2021-12-23 | Arkema France | Pvdf filtering face-piece respirator and recycling method |
FR3111566A1 (en) * | 2020-06-19 | 2021-12-24 | Arkema France | PVDF RESPIRATORY PROTECTION MASKS AND RECYCLING PROCESS |
US20230219262A1 (en) * | 2020-06-19 | 2023-07-13 | Arkema France | Method for recycling filtering facepiece respirators |
US12377582B2 (en) * | 2020-06-19 | 2025-08-05 | Arkema France | Method for recycling filtering facepiece respirators |
FR3126341A1 (en) * | 2021-08-30 | 2023-03-03 | Mdb Texinov | PROTECTIVE MASK, HALF-MASK AND FILTERING OBJECT |
WO2023031526A1 (en) * | 2021-08-30 | 2023-03-09 | Mdb Texinov | Protective mask, protective half-mask and filtering object |
CN114801393A (en) * | 2022-03-31 | 2022-07-29 | 金发科技股份有限公司 | Multi-scale fiber filter layer and preparation method and application thereof |
CN114801393B (en) * | 2022-03-31 | 2024-03-15 | 金发科技股份有限公司 | Multi-scale fiber filter layer and preparation method and application thereof |
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