Tag Archives: Electrospun Membranes

Electrospun Membranes for Distillation

Electrospun nanofiber membrane structure used in membrane distillation

Introduction: The Challenge of Thermal Separation Processes

Water desalination, wastewater treatment, and resource recovery all depend on efficient separation technologies capable of producing high-purity water while minimizing energy consumption. Among the emerging approaches being investigated, membrane distillation has attracted significant interest because it combines high salt rejection with relatively low operating temperatures. This makes it a promising technology for advanced water treatment applications.

The efficiency of membrane distillation depends strongly on membrane structure and surface chemistry. Parameters such as porosity, pore size distribution, pore tortuosity, thickness, and hydrophobicity directly influence vapor transport and heat transfer resistance.

In recent years, electrospun membranes for membrane distillation have been extensively investigated because electrospinning enables the fabrication of highly porous nanofiber structures with interconnected pore networks. These architectures can facilitate vapor diffusion while maintaining separation between the feed and permeate streams.

As a result, electrospun nanofiber membrane distillation systems are becoming an increasingly important research area in advanced water treatment and separation science.

What Is Membrane Distillation?

Membrane distillation is a thermally driven membrane separation process in which a hydrophobic semipermeable membrane separates a heated feed solution from a colder permeate side.

The process operates through a vapor pressure gradient generated by a temperature difference across the membrane. Water evaporates at the interface between the warm feed and the membrane, and the vapors diffuse through the membrane pores and condense at the colder permeate side.

Because the membrane is hydrophobic, liquid water is prevented from penetrating the pores, resulting in selective vapor transport.

The performance of membrane distillation membranes depends on several key parameters:

  • Membrane porosity
  • Pore size distribution
  • Membrane thickness
  • Thermal conductivity
  • Hydrophobicity
  • Pore tortuosity

These factors influence vapor flux, conductive heat loss, liquid entry pressure (LEP; the maximum working pressure for the membrane distillation process, above which liquid water would penetrate the membrane), and long-term operational stability.

Traditionally, membrane distillation membranes are designed with relatively high thicknesses to reduce conductive heat transfer between the feed and permeate streams. However, thicker membranes may also increase the resistance to vapor transport, thus reducing the vapor flux.

Consequently, membrane engineering for distillation requires balancing thermal insulation with efficient vapor transport.

Electrospun Membranes for Membrane Distillation

Electrospinning is a versatile fabrication technology capable of producing continuous nanofibers from polymer solutions using a strong electric field.

Electrospun nanofiber membranes typically exhibit:

  • High surface-area-to-volume ratio
  • High porosity
  • Interconnected pore structures
  • Tunable fiber diameters

These structural characteristics are advantageous for membrane distillation because they can facilitate vapor diffusion.

At the same time, electrospun membranes must maintain sufficient hydrophobicity to prevent membrane wetting during operation.

Research has demonstrated that fiber morphology significantly influences membrane wetting behavior and vapor transport performance.

However, smoother fibers may sometimes provide higher vapor flux because of differences in pore interconnectivity and membrane packing density.

These observations highlight the importance of carefully balancing:

  • Fiber morphology
  • Hydrophobicity
  • Porosity
  • Mechanical stability
  • Liquid entry pressure

when designing electrospun membranes for distillation applications.

Hydrophobic Nanofibers for Efficient Vapor Transport

Hydrophobicity is one of the most critical parameters in membrane distillation systems. If pore wetting occurs (i.e., if liquid water penetrates the membrane pores), the feed and permeate solutions come in direct contact with each-other, resulting in contamination of the permeate stream. This scenario is considered a critical failure of the membrane.

Electrospun poly (vinylidene fluoride) (PVDF) membranes have been widely investigated in the context of membrane distillation due to their intrinsic hydrophobicity, chemical resistance, and thermal stability.

Experimental studies have shown that electrospun PVDF membranes can achieve relatively high vapor permeation fluxes. However, electrospun structures often exhibit lower liquid entry pressure than commercial PTFE membranes, meaning the risk of pore wetting is higher.

For example, reported studies observed that electrospun PVDF membranes exhibited liquid entry pressure (LEP) values below 0.64 bar, whereas commercial PTFE membranes demonstrated substantially higher LEP values of approximately 9 bar. The relatively low LEP of the electrospun PVDF membranes indicated a greater susceptibility to pore wetting under pressure-driven conditions, although these membranes often exhibited higher vapor flux due to their highly porous nanofibrous structure.

Despite this limitation, electrospun PVDF membranes have demonstrated higher vapor flux in certain membrane distillation configurations due to their highly porous nanofibrous architecture.

These findings indicate that electrospun nanofiber membranes may offer important mass transport advantages, although long-term wetting resistance remains an active area of research.

Materials and Design Strategies for High-Performance Membranes

Polymer Selection for Membrane Distillation

The polymer used during electrospinning strongly influences membrane performance in membrane distillation applications.

Materials commonly investigated include:

  • Polyvinylidene fluoride (PVDF)
  • Polyurethane (PU)
  • Polystyrene (PS)
  • Polysulfone (PSU)
  • PVDF-HFP copolymers

These polymers differ in:

  • Hydrophobicity
  • Thermal stability
  • Mechanical resistance
  • Solvent compatibility
  • Processability

Experimental studies with electrospun polyurethane (PU) membranes demonstrated that membrane thickness and feed salinity significantly influence permeation flux. In the work reported by Feng, Khayet, and Matsuura in their study on electrospun nanofibrous membranes for membrane distillation, thin electrospun membranes (approximately 6–10 g m⁻²) achieved fluxes above 10 kg m⁻² h⁻¹ under the experimental conditions reported by the authors and at feed salinities below 20 wt. % NaCl.

As feed salinity increased, flux progressively decreased to approximately 8 kg m⁻² h⁻¹, highlighting the impact of concentration polarization and membrane wetting phenomena on membrane distillation performance. In contrast, thicker electrospun membranes exhibited lower but more stable flux values, typically between 6 and 8 kg m⁻² h⁻¹ across the tested salinity range.

The lower stability of thinner membranes was associated with larger pore sizes and lower bubble-point pressures, increasing susceptibility to membrane wetting.

Surface Engineering and Hydrophobic Modification

Several surface engineering strategies have been investigated to improve hydrophobicity and wetting resistance in electrospun membranes.

One reported approach involved electroless silver plating followed by 1-dodecanethiol surface modification of electrospun PVDF nanofibers. The resulting membrane achieved:

  • Water contact angle ≈153°
  • Sliding angle <10°

Under the reported experimental conditions, the modified membrane maintained a relatively stable vapor flux during eight hours of membrane distillation testing.

Other studies (Zhou et al. (2014) have reported PTFE nanofibrous membranes fabricated by electrospinning PTFE/PVA precursor suspensions followed by high-temperature sintering. In this approach, PVA acts as a carrier polymer during electrospinning, while the PTFE particles are subsequently fused during thermal treatment to generate a nanofibrous PTFE structure.

These membranes demonstrated:

  • Water contact angle ≈156.7°
  • Salt rejection >98 %

during vacuum membrane distillation experiments.

Such approaches illustrate how membrane surface engineering can improve wetting resistance and operational stability in membrane distillation systems.

 

Desalination plant in Germany.

Desalination plant in Germany.

Performance and Efficiency Advantages

Nanofiber Membranes for Desalination and Water Treatment

Several experimental studies have evaluated electrospun membranes in desalination and water purification applications.

One investigation involving electrospun polysulfone nanofibers modified with beeswax reported:

  • Water contact angle ≈162°
  • Salt rejection >99.8 %
  • Permeate flux ≈6.4 L m⁻² h⁻¹

during direct contact membrane distillation testing with sodium chloride feed solution.

The membrane exhibited relatively stable operation over extended testing periods, with only moderate flux decline reported after prolonged operation.

These results demonstrate the potential of electrospun membranes for advanced water treatment applications where high salt rejection and controlled vapor transport are required.

Multi-Layer Membrane Architectures

To improve wetting resistance and liquid entry pressure, researchers have explored multilayer membrane designs.

One reported configuration included:

  • Hydrophilic nanofiber support layer
  • Cast membrane intermediate layer
  • Superhydrophobic electrospun PVDF top layer

In this structure:

  • The superhydrophobic layer reduces pore wetting
  • The intermediate layer increases liquid entry pressure
  • The hydrophilic support assists vapor transport

Under reported experimental conditions, the membrane maintained stable permeation performance over extended operating periods while preserving high salt rejection.

Influence of Fiber Architecture

Recent studies have also investigated electrospun membranes containing bimodal fiber diameter distributions.

These structures combine fibers of different diameters within the same membrane, modifying pore architecture and vapor transport pathways.

Research involving PS, PVDF-HFP, and blended systems reported permeation fluxes up to approximately 43.41 L m⁻² h⁻¹ while maintaining salt rejection near 99.74%.

These findings suggest that fiber diameter distribution and structural organization may significantly influence membrane distillation performance.

Fluidnatek’s Role in Electrospun Membrane Development and Scale-Up

Advanced electrospinning equipment plays an important role in the development of nanofiber membranes for membrane distillation and thermal separation technologies.

Fluidnatek electrospinning platforms support controlled fabrication of nanofiber membranes by enabling adjustment of:

  • Fiber diameter
  • Membrane thickness
  • Porosity
  • Polymer solution formulation
  • Multi-layer architecture

Such process control capabilities are relevant for researchers investigating membrane distillation, desalination membranes, hydrophobic nanofiber systems, and advanced filtration materials.

Fluidnatek platforms also support process scalability from laboratory development toward pilot-scale and even full-scale manufacturing configurations, which is an important consideration for membrane technology translation.

Conclusion

Membrane distillation is an important emerging technology for desalination and water treatment.

Electrospun membranes for membrane distillation offer several potential advantages, including:

  • High porosity
  • Tunable nanofiber structures
  • Enhanced vapor transport
  • Flexible membrane architecture design

At the same time, challenges related to pore wetting and long-term hydrophobic stability remain active areas of scientific research.

Ongoing developments in polymer engineering, multilayer membrane architecture, and surface modifications continue to improve the performance of electrospun nanofiber membranes for distillation applications.

Although many of these technologies are still at the research and pilot scale, electrospinning is expected to play an increasingly important role in next-generation membrane distillation systems.

Accelerate Membrane Distillation Research with Fluidnatek

Looking to develop high-performance membranes for distillation and advanced separation technologies?

Fluidnatek’s electrospinning platforms support the development of customizable nanofiber membranes for membrane distillation, desalination research, filtration, and other water treatment applications.

Contact Fluidnatek’s technical team to explore scalable electrospinning solutions for membrane engineering and thermal separation research.

 

References

ElectrospinTech. Electrospun membrane for distillation.
http://electrospintech.com/memdistillation.html

Essalhi, M., & Khayet, M. (2014). Surface modification of electrospun PVDF membranes for membrane distillation. Desalination.

Liao, Y., et al. (2013). Superhydrophobic modification of electrospun PVDF nanofibers for membrane distillation.

Zhou, X., et al. (2014). Electrospun PTFE nanofiber membranes for vacuum membrane distillation.

Prince, J. A., et al. (2014). Triple-layer membranes for improved membrane distillation performance.

Zhao, S., et al. (2023). Bimodal fiber diameter electrospun membranes for membrane distillation.

Khayet, M., & Matsuura, T. (2011). Membrane Distillation: Principles and Applications. Elsevier.

Feng, C., Khayet, M., & Matsuura, T. Preparation and Characterization of Electrospun Nanofibrous Membranes for Membrane Distillation. In: Membrane Distillation: Principles and Applications. Elsevier.

 

 

Electrospun Membrane for Textile Wastewater Treatment

Electrospun Membranes for Textile Wastewater

Introduction – The Challenge of Textile Wastewater

The textile industry is widely recognised as one of the most water-intensive manufacturing sectors. Dyeing and finishing operations generate substantial quantities of effluents containing complex mixtures of synthetic dyes, salts, surfactants, heavy metals, and auxiliary chemicals. These waste streams are particularly persistent due to their high chemical oxygen demand (COD), colour intensity, and the presence of recalcitrant organic molecules such as azo dyes.International organisations, including the World Bank, have identified textile dyeing and finishing processes as major contributors to industrial water pollution, especially in regions with concentrated manufacturing activity. The persistence and toxicity of certain dyes raise environmental and public health concerns, particularly when wastewater treatment infrastructure is insufficient.

Conventional treatment technologies — coagulation–flocculation, biological oxidation, activated carbon adsorption, advanced oxidation processes (AOPs), and membrane filtration — can reduce pollutant loads but often present trade-offs. These include high operational costs, secondary sludge generation, limited removal efficiency for low-molecular-weight dyes, and membrane fouling challenges.

As regulatory standards become more stringent and water reuse strategies gain importance within circular economy frameworks, there is increasing interest in advanced materials capable of enhancing separation efficiency while maintaining scalability. In this context, the electrospun membrane for textile wastewater treatment has emerged as a promising platform within nanofiber membrane technology.

Electrospun Nanofiber Membranes – A New Frontier in Filtration

Electrospinning is a fibre fabrication technique that employs a high-voltage electric field to draw ultrafine fibres from polymer solutions or melts. The resulting nanofiber membranes consist of nonwoven mats with fibre diameters typically ranging from tens of nanometres to several micrometres.

These membranes are characterised by:

  • High porosity (often exceeding 80%)
  • Interconnected pore structures
  • Large specific surface area
  • Tunable fibre diameter and thickness

Key structural advantages

High surface-area-to-volume ratio
The nanoscale diameter of electrospun fibres significantly increases the available surface area, enhancing adsorption interactions with dissolved pollutants such as dyes and metal ions.

Interconnected porous structure
The open, porous morphology enables high permeability compared to dense phase-inversion membranes, facilitating improved water flux under comparable pressure conditions.

Tailorable surface chemistry
Electrospun membranes can be functionalised either during spinning (by polymer blending or nanoparticle incorporation) or post-treatment (plasma, grafting, coating), allowing optimisation for specific wastewater compositions.

In contrast to conventional membranes governed predominantly by size exclusion, electrospun nanofiber membranes offer a versatile platform for integrating adsorptive, sieving, and catalytic functionalities, dictated by their specific material composition and functionalization strategies

Materials Used for Electrospun Membranes in Water Treatment

Material selection plays a decisive role in mechanical stability, chemical resistance, hydrophilicity/hydrophobicity balance, and pollutant interaction.

Polyvinylidene fluoride (PVDF) nanofiber membranes

PVDF is widely used in membrane engineering due to its:

  • Chemical resistance
  • Thermal stability
  • Mechanical robustness

Despite its robust mechanical properties, PVDF exhibits intrinsic hydrophobicity. For aqueous textile wastewater treatment, surface modification or blending with hydrophilic additives is often necessary to improve wettability and reduce fouling.

Studies published in journals such as Separation and Purification Technology and Journal of Membrane Science report effective dye rejection when PVDF electrospun membranes are modified or combined with functional nanoparticles.

Incorporation of photocatalytic fillers such as TiO₂ can enable additional degradation mechanisms under UV irradiation, contributing to colour removal beyond simple filtration.

 

Polyacrylonitrile (PAN) and polyamide membranes

Polyacrylonitrile (PAN) is frequently used in electrospinning due to:

  • Good spinnability
  • Mechanical strength
  • Reactive nitrile groups

The nitrile functionality can be chemically modified to introduce amine or carboxyl groups, improving affinity for heavy metal ions such as Cu²⁺ or Pb²⁺ through coordination mechanisms.

Functionalised PAN nanofiber membranes have demonstrated promising adsorption capacities for heavy metals and certain dye classes in laboratory-scale studies.

 

Composite and hybrid membrane architectures

Recent research trends focus on multifunctional composite membranes, where electrospun fibres act as a support or active layer integrating nanomaterials.

Examples include:

  • PVDF/TiO₂ nanofibers for photocatalytic dye degradation
  • PAN/graphene oxide composites enhancing adsorption performance
  • Chitosan-based nanofibers offering inherent affinity for anionic dyes
  • Cellulose acetate electrospun membranes for more sustainable polymer options

These hybrid strategies enable the design of multifunctional membranes that synergistically combine physical sieving with chemical adsorption or catalytic degradation.

 

Case Example – Poly-CD Nanofibrous Membranes

A study by Celebioglu et al. (2017) investigated poly-cyclodextrin (poly-CD) electrospun nanofibrous membranes for dye removal applications.

Using a dead-end filtration system (HP4750), methylene blue (MB) solutions at concentrations of 40 and 80 mg/L were filtered under controlled nitrogen pressure. The study reported:

  • Significant colour reduction in permeate solutions
  • Preservation of nanofibre morphology after filtration
  • Mechanical stability under applied pressure

SEM analysis confirmed that the fibrous structure remained intact, demonstrating that properly engineered nanofibrous membranes can withstand operational stress conditions while maintaining adsorption functionality.

This example highlights the importance of polymer chemistry and structural stability in practical filtration environments.

 

Advantages in Textile Wastewater Remediation

Electrospun membranes offer several potential advantages over conventional polymeric membranes and adsorption media.

Enhanced Pollutant Interaction

The nanoscale fibre diameter increases the likelihood of contact between pollutants and active sites, supporting improved adsorption-driven removal mechanisms.

High Permeability

Due to their high porosity and interconnected structure, electrospun membranes often exhibit elevated permeability compared to dense membranes fabricated via phase inversion. Several comparative studies report substantially higher water flux values, although performance depends on membrane thickness and operational pressure.

Functionalisation Flexibility

Electrospinning enables the incorporation of nanoparticles, adsorptive fillers, and catalytic agents directly into the fibre matrix. This flexibility supports the development of application-specific membranes tailored to particular textile effluent compositions.

Potential Integration into Multistage Systems

Electrospun membranes can function as:

  • Standalone filtration layers
  • Support structures in composite membrane assemblies
  • Pretreatment stages before reverse osmosis
  • Adsorptive polishing units

Such versatility makes them attractive for modular wastewater treatment strategies.

Filtration performance of poly-CD nanofibrous membrane

Filtration performance of poly-CD nanofibrous membrane. (A) The photographs of membrane cell part of HP4750 dead-end system and the cropped poly-CD nanofibrous membrane with a definite active filtration area (14.6 cm2). The schematic view of HP4750 filtration system. For each test, 50 mL solution is passed through the poly-CD nanofibrous membranes with a definite N2 pressure. Then, the permeated solution is collected in a clear beaker. (B) The visual illustration of the MB solutions prepared at two different MB concentrations (40 and 80 mg/L) before and after filtration test. The photographs and SEM images (scale bar-10 µm) of the poly-CD nanowebs exposed to these two concentrated MB solutions during the experiments. As clearly seen, both the macroscopic visual appearance and the fibrous morphology of poly-CD nanofibers were protected under such applied pressure [Celebioglu et al 2017].

Research Trends and Industrial Considerations

While numerous studies demonstrate laboratory-scale feasibility, challenges remain in translating electrospun nanofiber membranes to full industrial deployment.

Key considerations include:

  • Long-term fouling resistance
  • Mechanical durability under continuous flow
  • Chemical stability in highly saline or alkaline effluents
  • Reusability and regeneration cycles
  • Production scalability

Recent publications in Journal of Membrane Science, Desalination, and Water Research emphasise the need for robust scale-up strategies and standardised testing protocols to enable commercial adoption.

Role of Fluidnatek in Scalable Membrane Development

Scaling electrospun membranes from laboratory prototypes to industrial production requires advanced electrospinning platforms capable of maintaining fibre uniformity and reproducibility.

Fluidnatek provides electrospinning equipment designed for:

  • Controlled fibre diameter distribution
  • Multi-nozzle and free-surface electrospinning
  • Integration of functional fillers
  • Pilot and industrial-scale membrane manufacturing

By supporting both research and scale-up stages, Fluidnatek’s platforms enable development of nanofiber membranes for water treatment applications, including textile wastewater remediation.

More information on electrospinning technologies for separation applications can be found at: https://www.fluidnatek.com

Conclusion – Towards Sustainable Textile Wastewater Treatment

Textile wastewater represents a recalcitrant effluent stream, characterized by significant chemical complexity and inherent variability. While traditional treatment technologies facilitate partial remediation, they frequently exhibit insufficient removal efficiencies for persistent synthetic dyes and dissolved contaminants.

Electrospun nanofiber membranes represent a promising material platform capable of enhancing separation efficiency through high porosity, tunable surface chemistry, and multifunctional design. Laboratory studies demonstrate effective dye adsorption, heavy metal capture, and potential photocatalytic degradation when appropriate materials are employed.

Despite successful laboratory demonstrations, transitioning to industrial-scale application remains contingent upon the development of scalable fabrication techniques and more stringent performance validation

Looking to develop next-generation membranes for advanced wastewater treatment?
👉 Fluidnatek’s electrospinning platforms enable the engineering and scale-up of high-performance nanofiber membranes tailored to industrial filtration challenges. Contact our technical team to explore scalable solutions for textile wastewater treatment.

References

  1. Rocha, J.M., Sousa, R.P.C.L., Fangueiro, R. & Ferreira, D.P. (2024). The Potential of Electrospun Membranes in the Treatment of Textile Wastewater: A Review. Polymers, 16(6), 801. https://doi.org/10.3390/polym16060801
  2. Li, L., Guo, W., Zhang, S., Guo, R. & Zhang, L. (2023). Electrospun Nanofiber Membrane: An Efficient and Environmentally Friendly Material for the Removal of Metals and Dyes. Molecules, 28(8), 3288. https://doi.org/10.3390/molecules28083288
  3. Chen, H., Huang, M., Liu, Y., Meng, L. & Ma, M. (2020). Functionalized Electrospun Nanofiber Membranes for Water Treatment: A Review. Science of The Total Environment, 739, 139944. https://doi.org/10.1016/j.scitotenv.2020.139944
  4. Zhu, Y., et al. (2023). Multifunctional Electrospun Nanofibrous Membrane: An Effective Method for Water Purification. Separation and Purification Technology, 327, 124952. https://doi.org/10.1016/j.seppur.2023.124952
  5. Li, J., Gao, M., Lin, T., Dai, Q., Ao, T. & Chen, W. (2022). Adsorption Treatment of Wastewater by Electrospun Nanofiber Membranes: A Review. Acta Materiae Compositae Sinica, 39(4), 1378–1394. https://doi.org/10.13801/j.cnki.fhclxb.20211008.001
  6. Chitosan‑coated Electrospun PVDF‑ZnO Nanofibrous Membranes for Dye Wastewater Separation. Dye and Pigment, 100281. https://doi.org/10.1016/j.dwt.2024.100281
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