Materials Today Communications
3D structure design and simulation for efficient particles capture: The influence of nanofiber diameter and distribution
Graphical abstract
Introduction
Particulate matter 2.5 (PM 2.5) refers to tiny particles with an equivalent diameter of less than or equal to 2.5 μm in the atmosphere, which have large specific surface area, strong activity, and easy to attach toxic and harmful substances. Fig. 1 shows the distribution of the global median PM2.5 simulated concentration from World Health Organization [1]. Particles of 10 μm in diameter are usually deposited in the upper respiratory tract, and they can penetrate deep into the bronchioles and alveoli once the size are less than 2 μm, posing a great threat to human health [2]. PM 2.5 mainly come from human activities such as industrial pollution, secondary inorganic aerosol, coal combustion, biomass burning, traffic and waste incineration emission as well as the natural soil dust [3]. The composition changes with different seasons. Except for controlling air pollution from various original sources, the demand for air purified with filters is increasing with booming industrial development.
High filtration efficiency, low pressure drops and large dust holding capacity are the ideal properties for effective air filtration. Reducing the fiber diameter in filter is an efficient way to increase filtration efficiency [4]. Electrospun nanofiber filters offer a promising method for PM 2.5 capture due to their large specific surface area, small fiber diameter and tortuous pore architecture. They have fibers with diameters ranging from 50-2000 nm and mean pore sizes of around several hundred nanometers to several microns [5]. Whereas the increase of filtration efficiency with thinner fibers is desirable, the increase of pressure drop that goes hand in hand with it is unwanted. Accordingly, quality factor (QF) is applied to optimally balance the effect of filtration efficiency () and pressure drop () [1,4].
Plenty of researches have been done focusing on filtration efficiency and QF. Gao et al. [6] developed a ternary structure built from scaffold nanofibers, microspheres and thin nanofibers. The filtration efficiency could go up to 99.99 % with 126.7 Pa pressure drop. The inclusion of microspheres enlarged the inter-fiber voids while the thin nanofibers increased the filter surface area for efficient particle capture. For high efficiency particulate air (HEPA) filters with a minimum removal efficiency of 99.97 % for particles greater or equal to 0.3 μm, a reduction of fiber diameter is an efficient way to increase the filtration efficiency [7]. The decrease of fiber diameter to around 60-100 nm was found to be most effective for slip-effect of air molecules on the periphery of nanofibers for low air resistance [8]. As an alternative method, the introduction of carbon nanotubes (CNTs) [9,10] or cellulose nanocrystals (CNCs) [11] in electrospun nanofiber membranes not only enhanced their mechanical properties, but also greatly reduced the pressure drop. The diameter of CNTs or CNCs (from several nanometers to dozens of nanometers) is less than the mean free path of the air molecules (66 nm) which alters the Brownian diffusion of aerosol particles [12]. The incorporation of zein nanoparticles on cellulose nanofibers could also efficiently remove particles with hierarchical structure from nano to micron scale [13].
Except for structure optimization, surface modification such as electret electrospun nanofiber air filter through the implementation of corona charging, tribo-charging or low-energy-electron-beam bombardment are also regarded as promising materials for efficient particulate matter (PM) capture [[14], [15], [16]]. However, further improvement on the long-term effectiveness with high filtration efficiency is needed [17]. Besides, surface modification with sputtering copper or carbon on electrospun nanofiber with higher dipole moment would have better removal efficiencies to particulate matter [18]. A movable air filter system generating a high electric field would even reduce pressure drop to only several Pascal with removal efficiency over 99 % [19].
With regard to structure optimization, the hierarchical structure of nanofibers would increase the removal efficiency with tortuous pore channels to separate different sized PM [20]. A layer by layer structure with alternate different average fiber diameters was also designed to increase the filtration efficiency and QF [21]. High quality factor was also derived from the heterogeneous structure during the capture of various sizes of sodium hydroxide aerosols. In addition, due to a more regular pore size distribution, aligned nanofiber filter showed higher probability for particle capture than randomly oriented nanofiber membrane [22]. In this work, the influence of nanofiber diameter and its distribution on filtration properties were studied by simulation. Different 3D filter structures were designed and simulated subsequently in COMSOL Multiphysics 5.4 to check the corresponding filtration properties. The filter thickness, fiber diameter, diameter variation coefficient (CV) and membrane rotating angle θ were adjusted to study their relationships with filtration efficiency, pressure drop and QF. Finally, cellulose acetate (CA) nanofiber filters with different diameter and distribution were prepared by needleless electrospinning to verify the simulation results.
Section snippets
Methodology and simulation details
Different 3D geometric filter structures were designed in COMSOL Multiphysics 5.4. The whole process included physics selection, global parameters definition, 3D structure construction, materials attribution, boundary condition settings, meshing, study settings and results analysis. The design of the 3D geometry is shown in Fig. 2. Randomly oriented nanofibers were constructed layer by layer in a cylindrical computational region to mimic the aerosol filtration test. The filter thickness and
Material and methods
Cellulose diacetate (acetyl content 39.8 wt%) was purchased from Aladdin Reagent; acetone and N, N-Dimethylacetamide (DMAC) and dimethyl sulfoxide (DMSO) were purchased from Shanghai Lingfeng Chemical Reagent Co., Ltd.
CA (16 wt%) was fully dissolved in acetone/ N, N-Dimethylacetamide = 2/1 v/v for double needle electrospinning and acetone/ DMSO = 2/1 v/v for plate needleless electrospinning with magnetic stirring. The filter prepared by needleless electrospinning, denoted as “Filter_A”, was
The relationship between nanofiber diameter and filtration effect
The prevailing air fluid of Stokes flow had low Reynolds number Re here, which was given by
Herein, ρ is the fluid density (1.204 kg/m3 at 293.15 K), is the fluid velocity, μ is the dynamic viscosity of air (1.825*10−5 Pa*s) and df is the fiber diameter. Re, ranging from 0.00035 to 0.00315, was far less than 1 with various fiber diameters, which could be inferred that the inertia force was far lower than viscous force [23]. The airflow field velocity distribution on the periphery of
Conclusions
In this work, we have designed and simulated the different 3D structured filters of different diameters ranging from 100 to 900 nm. The influence of nanofiber diameter and their CV on filtration efficiency, pressure drop and QF were studied based on same filter thickness and porosity. The rotation of nanofiber-based filters within the computational domain, steadily raised their filtration efficiency and QF. The simulation results were partially verified by electrospun cellulose acetate
CRediT authorship contribution statement
Jiajun Wu: Writing - original draft, Formal analysis, Investigation, Data curation, Validation. Obed Akampumuza: Methodology, Conceptualization. Penghong Liu: Visualization. Zhenzhen Quan: Writing - review & editing. Hongnan Zhang: Funding acquisition. Xiaohong Qin: Supervision. Rongwu Wang: Software. Jianyong Yu: Project administration.
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
This work was supported by the Chang Jiang Youth Scholars Program of China and grants [51773037] and the general program [51973027] from the National Natural Science Foundation of China to Prof. Xiaohong Qin as well as the “Innovation Program of Shanghai Municipal Education Commission”, “Fundamental Research Funds for the Central Universities” and “DHU Distinguished Young Professor Program” to her. This work has also been supported by grant [51803023, 61771123] from the National Natural Science
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2021, Building and EnvironmentCitation Excerpt :There are many studies on performance improvement through parameter optimization of the filter medium. The key lies in optimizing the fiber diameter [6], solid volume fraction (SVF) [7], fiber diameter distribution [8], material thickness [9], and other parameters of the material [10] in such a way that the filter medium can intercept more particulate matter with a lower airflow resistance. Different filter structure designs, including the pleat structure and filter structure, also have an impact on the performance of filters, especially in the process of dust holding.