1. Introduction
Removing hazardous particles and aerosols from the air is in great demand in the world. Particulate matter such as mineral powder, carbon powder and bioaerosols, which may contain harmful micro-organisms such as bacteria and viruses, can cause acute and chronic diseases alike [
1]. Many techniques have been developed for air purification, such as ionizers, ozonizers, photocatalytic oxidation and adsorption. However, filtration has been preferred in many cases due to its high efficiency and excellent stability [
1,
2]. There are three major categories of filters, namely non-woven, woven and membrane filters. Non-woven filters have the advantages of higher permeability, higher specific surface area, smaller pore size and controllable pore size distribution over woven filters, leading to higher filtration efficiency and lower pressure drop [
3]. Methods such as spunbond and melt-blown have been commercialized to produce non-woven air filters. Nevertheless, they can only provide relatively thick fibers with low filtering efficiency for small airborne particles (0.1 to 0.5 µm) [
1]. One of the most promising methods for the fabrication of nano-size fibers is electrospinning. A polymer solution or molten polymer is charged up by a high voltage power supply in this method. When the accumulated charge is above a critical value, the surface charge offsets the liquid’s surface tension (polymer solution or molten polymer) and generates a liquid jet [
4]. The jet stretches and whips rapidly due to its high residual surface charge and perturbation effect, leading to a dramatic reduction of its diameter before it reaches the collector [
5]. A porous non-woven layer will be deposited on the collector by selecting proper electrospinning parameters, containing very thin fibers in the range of a few nanometers to 2µm. Therefore, it improves the fine airborne particles’ capturing efficiency to smaller than 0.3 µm [
6].
One of the advantages of electrospinning is controlling the morphology of fibers to improve the performance of the air filter and the pore diameters [
7] and generating beads mixed with fibers to decrease the packing density and reduce the pressure drop [
8]. Producing a wide range of fiber-size filters has also been suggested to increase filtering efficiency at low pressure drop [
9]. Wang et al. [
10] added silica nanoparticles to polyacrylonitrile (PAN) to fabricate a hybrid nanocomposite air filter with higher roughness of fibers. By increasing the fiber’s roughness, slow air mobility regions (stagnation) near the rough fibers were developed when the electrospun layer worked as the air filter. Therefore, the capturing efficiency was enhanced significantly (99.989%) while the pressure drop remained relatively low (117 Pa).
Polyvinylpyrrolidone (PVP) is a known biocompatible and biodegradable polymer with low toxicity [
11], widely used in the medical, food, and cosmetic industries [
12]. However, the water solubility of PVP is pointed out for air filter applications, especially in high humidity conditions [
13,
14]. There are reports that the water solubility of PVP has been used to trap micro-organisms by PVP air filter and extract them by dissolving the filter in the water [
14,
15]. However, for air filter applications, a crosslinking treatment is needed to limit the water solubility of PVP. Melike et al. have fabricated centrifugally spun PVP nanofibers for air filter application, which showed a high filtering efficiency and quality factor of 99.995% and 0.39 (mm H
2O)
−1, respectively. Furthermore, by thermal crosslinking treatment, the filter remained stable in high humidity conditions [
13].
Nanoclay is an inexpensive filler used in polymer processing due to its low price, flame retardation and thermo-mechanical properties [
16] and has attracted much attention in both industry and academic sectors. The electrospinning of clay polymer has been successfully examined for some polymers, such as poly(methyl methacrylate) (PMMA) [
17], cellulose acetate [
18], poly(vinylidene fluoride) [
19] and polyethylene oxide [
20]. Besides the properties mentioned above, the addition of nanoclay to electrospun polymers has also been reported to modify the crystallinity and alignment of the polymer chains [
19,
20]. However, studies on introducing nanoclay into electrospun nanofibers for enhancement of the fibers’ roughness for air filtration are lacking, to the authors’ knowledge.
In the present study, electrospinning is utilized to make non-woven PVP layers with the potential for air filter applications. The novelty of this work is not limited to the introduction of nanoclay to electrospun fibers for making PVP–nanoclay fiber composites. This strategy can enhance the fiber roughness, fiber size distribution and pore size to improve the required morphology of the air filter application by using inexpensive materials.
2. Materials and Methods
The nanoclay used in the experiments was from Sigma-Aldrich, which contained 25 wt% trimethyl stearyl ammonium. Polyvinylpyrrolidone (PVP), with an average molecular weight of 1,300,000 g/mol, was also from Sigma-Aldrich. The nanoclay was dried at 180 °C before use in each experiment. A 95% ethanol from Greenfield Global was used to make the solutions.
PVP–nanoclay solutions were prepared by making sonicated ethanol–nanoclay colloids, adding 10 wt% PVP to the colloids and stirring for 24 h. Ethanol–nanoclay colloids were made at 3, 10 and 25 weight percent of the PVP (nanoclay:PVP = 3:97, 10:90 and 25:75). Additionally, a plain 10% PVP solution was used as a reference.
The electrical conductivity of the PVP–nanoclay solutions and ethanol–nanoclay colloids was measured using a conductivity meter with a precision of 0.1 µS/cm at room temperature. Each solution was measured three times, and the average value was reported.
Electrospinning tests were conducted using a 21-gauge blunt stainless-steel needle at a flow rate of 6 μL/min, a voltage of 15 kV and 30 ± 1% humidity in a closed chamber. A grounded aluminum rotating drum with a 10 cm diameter covered by aluminum foil was used as the current collector. The distance between the needle’s tip and the drum (working distance) ranged from 10 to 20 cm, and the drum speed was 100 rpm during the electrospinning process.
The produced electrospun fibers were examined using a scanning electron microscope (SEM) equipped with energy dispersive spectroscopy (EDS). An image analyzer (ImageJ software) was used to measure the fabricated fibers’ pore size and fiber size distribution. SEM images from five locations of the samples at 10,000 X were used for the fiber size measurements for each image analysis. The diameters of the fibers and pores were measured manually using ImageJ software. If a fiber contained beads, the diameter of the uniform section of the fiber was measured.
3. Results
Figure 1a shows the SEM image of the as-received nanoclay particles. The nanoclay flakes are agglomerated due to their van der Waals forces.
Figure 1b is the SEM image of the dried slurry of 3.5 wt% nanoclay in ethanol after 10 min of sonication. The sonication process has separated the flakes, but they are reattached after the slurry is dried. It is reported that the ultrasonic treatment can reduce the particle size of the nanoclay suspensions [
21].
Figure 2a is an SEM micrograph of the electrospun plain PVP (without nanoclay), which shows fibers with smooth surfaces. The effect of nanoclay addition on the electrospun fibers’ surface morphology is shown in
Figure 2b–d. As
Figure 2b shows, the addition of 3 wt% nanoclay has a small effect on the fibers’ roughness. However, a new set of ultra-fine fibers are formed in the microstructure. At a 10 wt% nanoclay concentration (
Figure 2c), the surface roughness has increased by forming clay-contained beads, and the highest surface roughness is achieved at 25 wt% concentration (
Figure 2d), containing the highest number of clay-contained beads and fibers.
EDS maps of silicon (representing the silicon in the nanoclay) from the SEM images in
Figure 3a,c are shown in
Figure 3b,d, indicating a nonuniform distribution of nanoclay particles in fibers, increasing the fibers’ surface roughness. As
Figure 3b shows, at 25 wt% nanoclay, larger sections of the electrospun fibers contain nanoclay, compared to 3 wt% nanoclay (
Figure 3d) forming the clay-contained beads. Therefore, the overall roughness of the electrospun fibers at 25 wt% nanoclay has increased.
Figure 4b–d shows that by adding nanoclay to PVP solution, a new range of ultra-fine fibers in the range of 40–200 nm formed, the range of the fibers’ size distribution increased up to 100% and the occurrence of the highest frequency distribution of fiber size shifted from 58.1 ± 3.1% for 400–500 nm fibers to 75.1 ± 4.3% for 40–100 nm fibers. Concurrently, as the nanoclay concentration increased from 3 wt% to 25 wt%, the frequency distribution decreased dramatically for the larger fiber sizes while increasing sharply for smaller fiber sizes.
The addition of nanoclay affected the average pore size of the electrospun fiber, too. The effect of the nanoclay addition on the average pore size of the electrospun fibers in
Figure 5 shows that adding 3 wt% nanoclay decreased the average pore size from 1.78 ± 0.13 μm to 0.91 ± 0.12 μm; however, a higher nanoclay concentration had less effect on the average pore size, so that at 25 wt% concentration, the average pore size decreased to 0.65 ± 0.05 μm. The effect of nanoclay concentration on the total frequency distribution of the fibers in the range of 40–200 nm, which are formed after nanoclay addition, is shown in
Figure 5b. It shows that at 3 wt% nanoclay, the total frequency distribution of 40–200 nm fibers is 71.5 ± 3.6% and increases to a maximum of 94.1 ± 5.8% at 25 wt% nanoclay.
Figure 6 shows the effect of nanoclay concentration on the electrical conductivity of the PVP–nanoclay solution and nanoclay colloid. As the nanoclay concentration increases, the conductivity of both solutions increases, but the conductivity of the nanoclay colloid increases at a higher rate.
4. Discussion
The main reason for introducing nanoclay to the PVP solutions was to increase the electrospun fibers’ surface roughness. It has been reported that the addition of silica nanoparticles to PAN can improve the filtering performance of the electrospun fibers significantly. It was suggested that silica nanoparticles could increase the surface roughness of the fibers. Therefore, stagnated regions (slow air mobility regions) close to the rough sections of fibers can be generated, improving the filtering efficiency while the pressure drop remains low [
10]. It was also reported that bead formation could promote the filtering performance because it can optimize the packing density of the fibers, which assists in reducing the pressure drop remarkably, while the filtering efficiency is not deteriorated significantly [
8,
22].
Figure 2a shows that the plain electrospun PVP fibers had a smooth surface. However, by adding nanoclay to the PVP, the clay-contained beads were formed with a rough appearance in the microstructure. The number of clay-containing beads and their surface roughness increased significantly by increasing the nanoclay concentration from 3 wt% to 25 wt% (
Figure 2b–d). It is noteworthy that the nanoclay particles were not very stable in ethanol. However, when PVP was added, it formed a colloidal solution and acted as a dispersant to form metastable suspensions. Although there are many reports on the dispersing effect of PVP on metal oxide nanoparticles [
23], very little work has been done on the interaction of clay and PVP [
24]. Colloidal solutions containing more than 25 wt% nanoclay were not used in this work since they needed more than 10 wt% PVP to be stabilized; however, this concentration of the polymer would be beyond the optimum concentration for electrospinning.
The non-homogeneous distribution of nanoclay particles in the fibers has caused the formation of the silicon-rich beads shown in
Figure 3b,d. Comparing the silicon maps in
Figure 3b,d with the corresponding SEM images in
Figure 3a,c reveals that the clay-containing beads and rough fibers are rich in silicon, indicating nanoclay particle accumulation in those areas.
As
Figure 4 shows, adding nanoclay to PVP solutions increased the range of the fiber size distribution and changed the frequency distribution of the fiber size. The histogram in
Figure 4a shows that the size of the pure PVP fibers was in the range of 300–700 nm, and most of the fibers had a diameter between 400 and 500 nm. By adding 3 wt% nanoclay to the PVP solution, ultrafine fibers formed in the microstructure with a broader range of fiber size distribution (40–700 nm), while the ultrafine fibers (40–100 nm) showed the highest frequency distribution, as shown in
Figure 4b. Increasing the nanoclay concentration to 10 wt% and 25 wt% shifted the highest frequency distribution of fiber size to the ultrafine fibers, as
Figure 4c,d shows.
These phenomena can be related to the higher conductivity of the solution at higher nanoclay contents. The conductivity of the PVP–nanoclay solution and nanoclay colloid versus nanoclay concentration in
Figure 6 shows that the conductivity increases from 1.70 ± 0.05 µS/cm for the PVP solution (0.0% nanoclay) to 62.70 ± 0.19 µS/cm for the PVP–nanoclay solution containing 25 wt% nanoclay. The PVP–nanoclay solutions show lower conductivity than the nanoclay colloids (without PVP) due to the higher viscosity of PVP–nanoclay solutions, decreasing the diffusion rate of the ions. The PVP–nanoclay solutions show lower conductivity than the nanoclay colloids (without PVP) due to their higher viscosity, decreasing the diffusion rate of the ions. The higher conductivity of the solution makes the electrospinning jet unstable under a strong electrical field. Therefore, a wider range of fiber size distribution can be produced [
25].
The effect of the nanoclay addition on the average pore size of the electrospun fibers shown in
Figure 5a is mainly due to the formation of finer nanofibers in the presence of the nanoclay. As
Figure 2a–d and
Figure 4a–d show, the addition of nanoclay to the PVP solution forms new finer nanofibers in the range of 40–200 nm, which provide a finer nanofiber net and reduce the average pore size. Based on
Figure 5b, the total frequency distribution of the fibers in the range of 40–200 nm increases from zero at zero nanoclay to 71.51% at 3 wt% nanoclay. However, the rate of increase of the total frequency distribution of 40–200 nm fibers decreases considerably as nanoclay concentration increases to 10 wt% and 25 wt%. Therefore, this phenomenon reduces the reduction rate of average pore size at nanoclay concentrations higher than 3 wt%, as shown in
Figure 5a.
A wide range of fiber sizes is beneficial for air filter applications. A combination of thick and narrow fibers enhances the capturing of particles while preventing a highly compact filter structure [
9]. Furthermore, the higher surface roughness of the fibers containing nanoclay also improves the filtering efficiency. Therefore, the electrospun fibers containing up to 25 wt% nanoclay are good candidates for air filter applications.
It should be noted that the hydrophilic nature of PVP had previously restricted its wide application as an air filter. However, crosslinking has proven to increase the stability of PVP at high humidity conditions [
13]. Crosslinking forms an integrated network in the polymer by connecting its chains by either intra- or intermolecular covalent or non-covalent links, decreasing the rate of solubility of the PVP fibers. Further research is being performed to investigate the influence of several crosslinking methods and coaxial electrospinning strategies on improving the water resistance of electrospun PVP–nanoclay composites as well as the aerosol filtering performance of the PVP–nanoclay.