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Novel composite membrane based on recycled low-density polyethylene-alumina used for vacuum membrane distillation



Plastic materials have a significant impact on the entire environment. Very relevant ideas in different areas with the aim of enhancing these materials and making them effective in our daily lives. In this context, our work in this article by using plastic materials in the manufacture of hydrophobic membranes realized in our Laboratory LEEP Enig Gabes Tunisia, followed by various analyses. These membranes are made of a Recycled Low-Density Polyethylene polymer by means of the Thermal Induced Phase Separation (TIPS) method by using solvents such as Butyl Acetate, non-solvent Hexane with the addition of Alumina at different concentrations to increase porosity.


Hydrophobic membranes are coupled to the vacuum still to test their performance. An analytical study by FTIR was done. Contact angle, pore size, porosity, mechanical test, bubble point pressure, AFM and SEM analysis. The results revealed that the addition of alumina had an important role in improving the structure, properties and therefore the performance of the membrane.


The membrane already prepared admits according to the analyzes tested a good porosity, hydrophobicity.


Since antiquity, water has had a primordial value in our land. Their importance grows more and more given the population growth. Making wastewater safe to drink is a worldwide challenge. In addition, even drinking water becomes polluted due to the enormous use, mainly of plastic materials. Faced with this serious problem, several research works are working continuously to solve these water problems. According to studies conducted by the UN, one in four people or two billion people in the world—lack of drinking water and 1.4 million people die (Hamad et al. 2013), thus, desalination becomes a necessity for this important issue (Wang and Chung 2015). What drives all of the research to focus on the filtration and desalination of water to produce large amounts of purified water in a short time with less investment. Many technologies have been produced in this context: thermal processes such as the known one, such as (MSF, MED, MED-TC), processes with the use of membranes such as reverse osmosis (RO), and the hybrid process such as membrane distillation (MD) (Chang et al 2019). The choice of one of these techniques is the basis of several processes: fresh, water suitability, impactful of the environment. Currently, DM is a widely used technology; this technique is used more nowadays (Aljumaily et al. 2022; Khaled et al. 2020; Asma et al. 2020), with very significant rejection yields manifests itself as a promising alternative (Asma et al. 2022) due to its advantages such as low salt rejection. For this, it is necessary to couple membrane process with renewable energies such as solar energy (Fatma et al. 2017). In this work, membrane distillation under solar vacuum was studied for water desalination. The study is based on everything on the motor organ which is the membrane in the MD processes. Several have their work on the manufacture of membranes in various materials, to prepare hydrophobic porous membranes (Aljumaily et al. 2019) such as PVDF, PTFE, PP and PE. All these studies showed promising results, but despite everything, the cost of the polymer is very high and the cost of MD membranes (Abedini et al. 2014). Therefore, in this work, recycled low-density polyethylene was used to prepare a flat sheet membrane for VMD application to increase the production of potable water and at the same time get rid of solid waste. This material is used for several reasons like being very cheap, hydrophobic in nature, low surface energy similar to PVDF and PP, good chemical stability and very low thermal conductivity (Malinalli et al. 2023; Ajari et al. 2019). Nowadays, composite membranes have gotten a lot of attention due to their flexibility of having more than one layer and using a variety of materials to form the membrane. In this article, a composite membrane was prepared using recycled low-density polyethylene (RLDPE), thus helping to lighten the burden of plastics on the environment, while alumina powder was used to reinforce these membranes and improve its properties for better MD efficiency. Several studies are based on the manufacture of PE membranes for MD using melting/cold stretching extrusion methods (El-Bourawi et al. 2006). In addition, the use of thermally induced phase separation (TIPS) methods in the preparation of PE membranes is very suitable, especially for semi-crystalline polymers that cannot be easily dissolved by solvents like LDPE (Tobo-Niño et al. 2017). In this study, flat sheet membranes were fabricated by the TIPS method and tested in solar vacuum membrane distillation (SVMD) for the desalination of seawater and brackish water.



Recycled polymers (RLDPE) were supplied from plastic manufacturing company located in Gabes (Tunisia). Butyl acetate and hexane were purchased by Laboratory Reagents & Fine. Chemicals, LOBA Chemie PVT.LTD.

Fabrication of AL/RLDPE composite membrane

In order to obtain flat membranes, the polymer solution called «collodion» is first prepared. A mixture of butyl acetate is used as a solvent in the preparation of all collodions (Fig. 1). The polymer mixture Rd is dissolved by adding the alumina powder with different amounts in the solvent under magnetic agitation in an oil bath at 130 °C until the polymer is completely dissolved. Once the collodion is prepared, it is spread on a glass plate using a manual film applicator. The resulting film is exposed to atmospheric conditions for 5 min then immersed in hexane and ethanol to extract the solvent from the membrane after it has been dried in an oven at 70 °C. Finally, the membrane is left at room temperature for 24 h before characterization analyses. Using an atomic force microscope (Brucker Nanoscope, France), the analysis topography of flat sheet membrane was assessed. After obtaining the membrane surface's 3D surface topography, the surface roughness was determined. According to the following statement (Rasool and Vankelecom 2021):

$${\text{Ra}} = { }\frac{1}{{{\text{L}}x{\text{L}}y}}\mathop \smallint \limits_{0}^{{{\text{L}}y}} \mathop \smallint \limits_{0}^{{{\text{L}}y}} \left| {Z\left( {x,y} \right)} \right|{\text{d}}x{\text{d}}y{ }$$

where Ra is the roughness, Z (x, y) is the surface relative to the median plane, Lx, Ly are the dimensions of the area.

Fig. 1
figure 1

Experimental setup of the preparation of flat sheet membranes

The sessile drop method was used to measure the membrane contact angle (CA). In order to accomplish this, a micro-syringe was employed for injecting a drop of bidistilled water onto the membrane. After that, a goniometer (CAM100 apparatus, Italy) was utilized to measure the contact angle. Six different positions on the membrane were measured, and the average value and its associated standard deviation were determined.

Membrane morphology, porosity, pore size and bubble point

The membrane morphology was investigated by evaluating SEM pictures taken with a (Zeiss EVO MA10, Switzerland) SEM. Membranes cross sections were obtained by freezing the samples in liquid nitrogen, resulting in a crisp brittle fracture. Before the SEM test, a tiny layer of gold was applied to the membrane samples to make them conductive. The overall porosity of the membrane can be calculated by the following expression (Asma et al. 2021)

$$\varepsilon \% = \frac{{\left( {w_{{\text{w}}} - w_{{\text{d}}} } \right)/\rho_{{\text{k}}} }}{{\left( {w_{{\text{w}}} - w_{{\text{d}}} } \right)/\rho_{{\text{k}}} + w_{{\text{d}}}/\rho_{{\text{p}}} }}*100$$

where wd is the mass of the dry sample (g), ww is the mass of the wet sample (g), k is the density of the kerosene (0.82 g/cm3), and p is the density of the polyethylene (0.92 g/cm3).

The dried membranes were cut, weighed and then, immersed in kerosene. After a few hours, the samples were taken, washed to remove kerosene stuck to the surfaces of the membranes and reweighed. The average pore size and bubble point of flat sheet membranes were measured using a wet/dry method using a pore wick (surface tension of 16 dynes/cm) as the wetting liquid and a porometer at capillary flow (CFP 1500 AEXL, Porous Materials Inc., USA). First, when the first bubble of pure nitrogen was admitted into the membrane, the nitrogen pressure was found to exceed the capillary flow of fluid inside the larger pore. The pressure was then increased until the flat sheet membrane dried, which meant that all pores were empty of the pore wick. The attached software calculated the pore size based on the nitrogen flow rates through the wet and dry membranes. Tensile proprieties. The mechanical properties of flat sheet membranes were measured with a (ZWICK/ROELL Z 2.5 test unit, ITM-CNR Italy). For each membrane, three samples (1* 5cm2) were examined. Each one was stretched at a constant rate of 5 mm/min in unidirectional strain. The strain at break, tensile strength, Young's modulus or elastic modulus, and breaking elongation were all evaluated.

Membrane applications: VMD experiments

The VMD tests have been carried out in the laboratory device illustrated schematically in Fig. 2. The membrane was inserted between the upper (feed side) and bottom (permeate side) compartments. The effective area of the membrane was computed based on the area of the membrane exposed to the vacuum space and was 12 cm2. The feed solution was cycled upstream of the membrane and passed through a heating water bath (Carlo Gavazzi, PDI409, Tunisia) outfitted with a temperature controller of 0.1 °C accuracy. The feed was continually churned at atmospheric pressure during the trials, and the temperature was changed between 25 and 90 °C. To extract the vapor, the permeate side was connected to a vacuum pump. The downstream pressure was between 0.2 and 0.9 bar. Permeate was condensed in a liquid nitrogen-immersed cold trap, and the collected permeate was weighed every hour to examine flux variation. The following expression can be utilized for determining the permeate partial flux Ji of the component i:

Fig. 2
figure 2

Schema of the device VMD: 1. Feed reservoir; 2. Membrane; 3. Permeate; 4. Condenser; 5. Vacuum pump; 6. Temperature control with heating oil; 7. Mixer

$$Ji=\frac{mi}{\left(A\mathrm{\Delta t}\right)}$$

All VMD experiments were repeated at least two times in order to check the reproducibility of the measurements.


Membrane hydrophobicity and roughness

Measurement of the contact angle (Figure a, b) is an experimental technique used to assess the hydrophobic character of the surfaces. If the angle of contact is between 0° and 90°, the material is hydrophilic and hydrophobic, if the angle of contact is between 90° and 180°. In our work, we found a contact angle of the order of 115°, which proves that it is a hydrophobic membrane. Furthermore, the roughness and contact angle have a strong relationship. Roughness improves wettability, according to Wenzel RN 1936 (Marino et al. 2019; Ajari et al. 2019) and can be predicted with the Wenzel (1936) relation as follows:

$$\mathrm{cos}{\theta }^{*}=r\mathrm{cos}\theta$$

Wenzel defined the roughness ratio as r = a/A, If the factor r is larger than 1, a hydrophilic solid (θ < 90°) becomes more hydrophilic.

When rough (θ* < θ). Conversely, a hydrophobic solid (θ > 90°) shows increased hydrophobicity (θ* > θ).

As a result, the topography of the surface of the manufactured membrane was investigated using an atomic force microscope. In this example, AFM was carried out using Nanoscope III equipment (Bruker, Santa Barbara, USA).

Figure 3b shows the obtained membrane's AFM picture. The resulting membrane has the greatest roughness of 527 nm, as can be shown. The properties of an RLDPE-alumina (RLDPE-Al2O3) membrane synthesized via thermal induced phase separation (TIPS) utilizing butyl acetate as a solvent are shown in Table 1.

Fig. 3
figure 3

a Contact angle of the obtained membrane, b AFM image of the obtained membrane

Table 1 Properties of the obtained membrane

Porosity, pore size and bubble point pressure

The membrane porosity is defined as the ratio of the volume occupied by pores to the total volume of the membrane. A higher porosity of a porous membrane means an increased surface area available for evaporation. The membrane porosity for MD can range from 30 to 85% (Alkhudhiri et al. 2012; Cipollina et al 2012). The obtained membrane, as indicated in Table 1, exhibits a porosity value of 65%. This suggests that the membrane possesses a favorable level of porosity, making it appropriate for utilization in membrane distillation applications.

Table 1 displays the pore size of the obtained membrane as 0.1097 µm. It is noteworthy that in membrane distillation, membranes with pore sizes ranging from 100 to 1 µm are commonly employed to prevent liquid penetration, as reported. The pore size of the obtained membrane falls within this recommended range. The pore size of a prepared RLDPE-alumina membrane plays a crucial role in determining the permeate flux. A higher pore size in the membrane corresponds to an increased permeate flux. Therefore, it is essential to identify the optimal pore size for each membrane distillation (MD) process based on the specific operating conditions. By carefully selecting and controlling the pore size, it is possible to enhance the efficiency and performance of the MD process.

Membrane morphology

SEM (scanning electron microscopy) was employed to analyze and characterize the morphology of the obtained membrane. This technique allows for high-resolution imaging of the membrane's surface and cross-section, providing valuable insights into its structural features and porosity. Figure 4 illustrates SEM images of the top and bottom surfaces of the obtained membrane. Additionally, Fig. 4 exhibits SEM images illustrating the cross section of the obtained membrane. The analysis of these images revealed a leafy structure with a random orientation, highlighting the porous nature of the membrane. Moreover, distinct stratified lamellae was observed, which can be attributed to the high degree of crystallinity in the LDPE polymer. Indeed, these observations are consistent with the findings of Douglas R. Lloyd's study in 1990 which highlighted that semi-crystalline and crystalline polymers have the ability to form intricate folded chains and supra-molecular architectures, such as axialites and spherulites. The presence of well-defined stratified lamellae in the cross section of the obtained membrane further supports the notion that the LDPE polymer used in the membrane exhibits semi-crystalline characteristics, confirming the resemblance to axialites and spherulites, as proposed in Lloyd's study. This observed morphology can be attributed to the solid–liquid demixing process that takes place during the cooling of the film. As mentioned by Ji et al. (2008), when membranes are fabricated using the TIPS (Thermally Induced Phase Separation) method, a significant portion of the solvents present in the film is expelled from the spherulites (matrix polymer) during the process of polymer crystallization. This expulsion occurs if the temperature reaches the crystallization temperature of the polymer.

Fig. 4
figure 4

SEM image of the surface (top and bottom side) of the obtained membrane

Mechanical proprieties

The material stress–strain behavior can be determined by analyzing the recorded forces and displacements, taking into account the sample's cross-sectional area and loading mode, as indicated by Vinci and Vlassak (1996). In this study, three samples with a cross-sectional area of 1*5 cm2 were tested for each membrane. The mechanical properties of the obtained flat sheet membrane were evaluated by subjecting each sample to unidirectional strain at a constant rate of 5 mm/min. The results, including tensile strength, strain at break, elastic or Young's modulus, and breaking elongation, are presented in Table 1.

Notably, the obtained membrane exhibited a high strain at break, reaching 117%. This indicates that the membrane possesses significant elasticity. The presence of a lamellae structure, formed through the Liquid–Liquid phase separation process, may be a contributing factor to its high elasticity.

The strain-induced microstructural changes in membranes can be substantial, which challenges several assumptions typically made about plastic deformation in bulk materials, such as in-plane elastic isotropy, as highlighted by Kui et al. (2017). Therefore, it is crucial to accurately analyze the mechanical properties of membranes while considering the underlying mechanisms. This approach is necessary for optimizing membrane design and processing to ensure long service life. A comprehensive analysis of the mechanical properties of membranes, coupled with a thorough understanding of the underlying mechanisms, is vital for the effective design and processing of membranes to achieve long-lasting performance (Kui et al. 2017).

Effects of feed temperature and transmembrane pressure

The effect of the feed pressure on the permeate flux for the different temperatures is given in Fig. 5. The test is carried out with seawater with a salinity of 8 g/l. It is also noted that the permeate flux increases linearly with the supply temperature of the hot fluid; this result is consistent with the research of Yongqing W et al. in 2015. This observed increase is due to the increase in the driving force of the transfer (the transmembrane vapor pressure gradient). Plus, the effect of vacuum pressure on system performance. As shown in this figure, the permeate flow goes from 0.2 to 0.6 l/h.m2 when the vacuum varies from 0.2 bar to 0.7 bar. This is because the flux of water permeate gradually decreases with increasing pressure due to the loss of the driving force across the membrane. The greater the difference between the membrane pressure on the permeate side and the water-saturated vapor pressure at the system temperature, the greater the driving force of the DMV process. To create the vacuum, the energy represents only 2% of the total energy. This finding is consistent with research conducted by Abdallah H in 2014. Comparison of different membranes used in VMD. Table 2 presents a comparison of the permeate flux values achieved by different membranes used in Vacuum Membrane Distillation (VMD) for water desalination, as reported in the literature, alongside the permeate flux obtained in the current study. Upon comparing the permeate flux values from this study with those from other studies, it is evident that they are quite similar. This is an encouraging result, particularly considering that the starting polymer used in this study is recycled. The similarity in permeate flux between the current study and previous research indicates that the performance of the membrane developed in this study is comparable to membranes fabricated using virgin polymers.

Fig. 5
figure 5

Effect of the feed temperature and the transmembrane pressure on the permeate flux

Table 2 Comparison of the VMD performance of different membranes found in the literature with the current RLDPE-Al2O3 membrane


In this work, a novel composite flat sheet membrane was prepared, characterized, and utilized in vacuum membrane distillation for desalinating seawater and brackish water. The flat sheet membrane was prepared using a recycled polymer, specifically low-density polyethylene (RLDPE), through the thermally induced phase inversion method (TIPS). The membrane fabrication process involved the use of 8 wt% recycled LDPE in Butyl Acetate (BA) and the addition of 5% alumina powder.

The obtained membrane was characterized, and the results revealed several positive properties. The membrane exhibited good hydrophobicity, as indicated by a contact angle of 115°. This hydrophobic nature is beneficial for membrane distillation processes, as it promotes the selective permeation of vapor while repelling liquid water.

Furthermore, the membrane displayed a porosity of 65%, which indicates the presence of sufficient pores for efficient vapor transport. The mechanical properties of the membrane were also evaluated, with the strain at break measured at 117%, indicating its excellent elasticity and ability to withstand deformation without fracturing. Additionally, the membrane exhibited a significant and applicable elastic modulus value, highlighting its strength and structural integrity. To assess its performance, the obtained membrane was tested in vacuum membrane distillation. The results were promising, as the permeate flux achieved by the membrane was comparable to the values reported in the literature.

Availability of data and materials

All data generated or analyzed during this study are included in this published article.



Recycled low-density polyethylene


Thermal induced phase separation


Fourier transforms infrared spectroscopy


Contact angle


Total mass of water vapor


Effective membrane area


Young angle


Wenzel contact angle


Roughness ratio


Actual microscopic area


Membrane distillation


Reverse osmosis


Multiple Effect Distillation


Multi-stage flashing






Solar vacuum membrane distillation


Vacuum membrane distillation


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HA is the main author, he had proposed the subject of this research, and he is responsible for the planning KH did the implementation of this research and was a major contributor to the writing of the manuscript, FK, HA, BC, AQ are responsible for discussing its results. All authors have read and approved the final version.

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Correspondence to Hidouri Khaoula.

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Hanen, A., Fatma, K., Hiba, A. et al. Novel composite membrane based on recycled low-density polyethylene-alumina used for vacuum membrane distillation. Bull Natl Res Cent 47, 132 (2023).

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  • Recycled low-density polyethylene
  • Alumina
  • Membrane
  • Hydrophobic
  • TIPS