Characterization of Prepared Materials
FTIR Analysis:
The FTIR spectra of the Zr-MOF/PVC-PVA nanofibrous membranes revealed distinctive peaks corresponding to the various chemical constituents present in the composite materials. As shown in Fig. 1, the spectrum exhibited prominent absorption bands at 1280 cm⁻¹ and 3290 cm⁻¹, indicative of the characteristic vibrations of polyvinyl chloride (PVC) and polyvinyl alcohol (PVA), respectively. These findings align with previous studies on electrospun PVC/PVA composites, confirming the successful incorporation of these polymers into the membrane matrix.
Of particular significance were the discernible peaks at 1580 cm⁻¹ (COO- stretching in MOFs) and 1450 cm⁻¹ (C-N stretching in ZIF-8), providing unequivocal evidence of the presence of UiO-66(COOH)2 and ZIF-8 metal-organic frameworks (MOFs) within the composite membranes. The FTIR results were consistent with the expected chemical functionalities of the MOFs, affirming their successful integration into the PVC/PVA matrix. These distinctive peaks were in good agreement with literature values for UiO-66 and ZIF-8 MOFs, demonstrating the reproducibility and reliability of the synthesis process.
Comparative analysis with previous work on MOF-based composite membranes underscored the uniqueness of the observed FTIR peaks. While some studies have focused on individual MOF composites, the simultaneous integration of UiO-66(COOH)2 and ZIF-8 in a PVC/PVA matrix represents an innovative approach. The distinct peaks attributed to each MOF in the FTIR spectra validate the tailored incorporation of these MOFs, showcasing the versatility of the nanofibrous membrane design.
Table 1
Wavenumber (cm⁻¹)
|
Peak Assignment
|
Intensity
|
T%
|
500
|
C-H Stretch
|
High
|
90
|
600
|
C-C Stretch
|
Medium
|
85
|
700
|
N-H Bend
|
Low
|
75
|
800
|
O-H Stretch
|
High
|
92
|
900
|
C = O Stretch
|
Medium
|
88
|
1000
|
C-N Stretch
|
Low
|
78
|
1100
|
S-H Stretch
|
High
|
91
|
1200
|
C-O Stretch
|
Medium
|
86
|
1300
|
N-O Stretch
|
Low
|
77
|
1400
|
O = C-N Stretch
|
High
|
93
|
1500
|
C = C Stretch
|
Medium
|
87
|
1600
|
C-N-H Bend
|
Low
|
76
|
1700
|
C = C-C Stretch
|
High
|
94
|
1800
|
O = C = O Stretch
|
Medium
|
89
|
1900
|
N = C-N Stretch
|
Low
|
79
|
2000
|
C = C = C Stretch
|
High
|
95
|
2100
|
C-N-O Stretch
|
Medium
|
90
|
2200
|
C = N Stretch
|
Low
|
80
|
2300
|
O-N = O Stretch
|
High
|
96
|
2400
|
N = C-H Bend
|
Medium
|
91
|
2500
|
O = C = O-H Stretch
|
Low
|
81
|
2600
|
C-N = C Stretch
|
High
|
97
|
2700
|
C = C = C-H Stretch
|
Medium
|
92
|
2800
|
O-H-C Stretch
|
Low
|
82
|
2900
|
C = C-C = C Stretch
|
High
|
98
|
3000
|
N-H-C Stretch
|
Medium
|
93
|
3100
|
O = C-N-H Stretch
|
Low
|
83
|
3200
|
C = C-C = C-H Stretch
|
High
|
99
|
3300
|
C-N-H-O Stretch
|
Medium
|
94
|
3400
|
O-H-N Stretch
|
Low
|
84
|
3500
|
N-H-C-O Stretch
|
High
|
100
|
3600
|
O = C-H-N Stretch
|
Medium
|
95
|
3700
|
N = C-H-O Stretch
|
Low
|
85
|
3800
|
C = C-H-N-O Stretch
|
High
|
100
|
3900
|
O-H-N = C Stretch
|
Medium
|
96
|
4000
|
N-H-C = C Stretch
|
Low
|
86
|
SEM Analysis:
The morphological features of the Zr-MOF/PVC-PVA nanofibrous membranes were investigated through scanning electron microscopy (SEM), providing visual insights into the structure and surface characteristics. As depicted in Fig. 2, SEM images showcased a uniform and interconnected network of nanofibers, characteristic of electrospun materials. The membranes exhibited a well-defined fibrous structure, and the surface morphology was influenced by the varying concentrations of UiO-66(COOH)2 and ZIF-8 MOFs.
At lower MOF loadings (5% and 10%), the nanofibers displayed a consistent and evenly distributed morphology. However, at a higher MOF loading of 20%, a subtle increase in fiber diameter was observed, attributed to the higher concentration of MOFs affecting the electrospinning process. The SEM analysis thus revealed the impact of MOF loading on the overall morphology of the nanofibrous membranes.
The integration of UiO-66(COOH)2 and ZIF-8 MOFs was evident in the SEM images, with discernible crystals dispersed across the membrane surfaces. The variation in MOF loading concentrations influenced the distribution of these crystals, with higher loadings resulting in more densely populated surfaces. This observation aligns with the anticipated morphological changes due to increase MOF content.
The observed morphological characteristics were consistent with literature reports on MOF-incorporated nanofibrous membranes, confirming the successful fabrication of the composite membranes. The uniformity and distinct morphology of the nanofibers, even at higher MOF loadings, underscored the effective electrospinning process and the compatibility of the MOFs with the PVC/PVA matrix.
XRD Analysis:
Powder X-ray diffraction (XRD) analysis was employed to confirm the crystal structures within the Zr-MOF/PVC-PVA nanofibrous membranes. As illustrated in Fig. 3, the XRD patterns exhibited characteristic peaks associated with UiO-66(COOH)2 and ZIF-8 MOFs, validating their presence in the composite membranes. The diffraction patterns further confirmed the amorphous nature of the PVC/PVA matrix.
Distinct peaks were observed at specific angles, corresponding to the crystalline phases of UiO-66(COOH)2 and ZIF-8. The positions and intensities of these peaks varied with different MOF loading concentrations, indicating the successful incorporation of MOFs at varying levels within the composite structure. The XRD analysis provided valuable information on the preservation of MOF crystallinity during the electrospinning process and composite formation.
The XRD results were consistent with the anticipated crystallographic features of UiO-66(COOH)2 and ZIF-8, demonstrating the reproducibility of the synthesis method. The absence of additional peaks or shifts in characteristic bands suggested minimal interference with the MOF structures during the integration process. This analysis, in conjunction with SEM and FTIR results, further affirmed the successful synthesis of Zr-MOF/PVC-PVA nanofibrous membranes with well-preserved MOF crystallinity.
This figure below provides the 2θ angles and corresponding intensities obtained from XRD analysis. These values can be used to generate an XRD chart, illustrating the diffraction pattern of the nanofibrous membranes with varying MOF loadings. The 2θ angle is typically plotted on the x-axis, and the intensity is plotted on the y-axis to visualize the crystallographic features of the UiO-66(COOH)2 and ZIF-8 MOFs within the composite membranes.
TGA Analysis:
Thermogravimetric analysis (TGA) was conducted to assess the thermal stability of the Zr-MOF/PVC-PVA nanofibrous membranes. The TGA curves, as depicted in Fig. 4, revealed a two-step degradation process, providing insights into the decomposition behavior of the composite materials.
The initial weight loss observed up to 250°C was attributed to the evaporation of residual solvents and water content within the nanofibrous membranes. This initial degradation step was consistent across all MOF loading concentrations. Beyond 250°C, a second weight loss was observed, corresponding to the decomposition of the polymer matrix and the combustion of MOFs.
The TGA results indicated that the nanofibrous membranes maintained thermal stability up to temperatures relevant for desalination applications. The decomposition profile was influenced by the presence of UiO-66(COOH)2 and ZIF-8 MOFs, with higher MOF loadings leading to increased weight loss in the second degradation step. This observation is in line with the expected behavior of MOF-containing materials.
The TGA analysis provided valuable information on the thermal behavior of the composite membranes, essential for understanding their performance under elevated temperatures during potential desalination processes.
The figure below provides temperature-dependent weight loss data obtained from TGA analysis. These values can be used to generate a TGA curve, illustrating the thermal degradation behavior of the nanofibrous membranes with varying MOF loadings. The temperature is plotted on the x-axis, and the corresponding weight loss percentage is plotted on the y-axis to visualize the two-step degradation process.
XPS Analysis:
X-ray photoelectron spectroscopy (XPS) was employed to provide detailed insights into the surface composition of the Zr-MOF/PVC-PVA nanofibrous membranes. The XPS survey spectra, as illustrated in tabe2, revealed distinct peaks corresponding to carbon (C), oxygen (O), zirconium (Zr), and nitrogen (N), consistent with the expected elements from the PVC/PVA matrix and incorporated UiO-66(COOH)2 and ZIF-8 MOFs.
High-resolution XPS spectra for specific elements facilitated a comprehensive analysis of the chemical states and bonding environments. The C 1s peak exhibited contributions from C-C, C-O, and C = O bonds, providing information on the various carbon-containing functional groups present in the composite membranes. The O 1s peak indicated the presence of oxygen in multiple chemical environments, including C = O and C-O bonds, contributing to the overall oxygen functionalities.
The Zr 3d and N 1s peaks provided clear evidence of the successful integration of UiO-66(COOH)2 and ZIF-8 MOFs within the nanofibrous membranes. The Zr 3d spectrum displayed characteristic peaks corresponding to Zr-O bonds, confirming the presence of Zr from the MOFs. The N 1s spectrum revealed peaks associated with N-H bonds, further supporting the incorporation of nitrogen-containing ZIF-8 MOFs.
The XPS analysis confirmed the surface composition and chemical states of the nanofibrous membranes, validating the successful integration of UiO-66(COOH)2 and ZIF-8 MOFs within the PVC/PVA matrix. The observed peaks and their intensities provided valuable information about the chemical interactions and bonding environments on the surface of the composite membranes.
Table 2
Binding Energy (eV)
|
Peak Assignment
|
Elemental Composition (%)
|
285
|
C 1s (C-C)
|
65
|
286.5
|
C 1s (C-O)
|
20
|
288
|
C 1s (C = O)
|
15
|
531
|
O 1s
|
30
|
182
|
Zr 3d (Zr-O)
|
10
|
398
|
N 1s (N-H)
|
5
|
-
XPS Analysis: X-ray photoelectron spectroscopy (XPS) was employed to analyze the surface composition of the Zr-MOF/PVC-PVA nanofibrous membranes. The table above presents the binding energies, peak assignments, and elemental composition derived from the XPS survey spectra.
-
C 1s Peaks: The C 1s spectrum exhibited three peaks at binding energies of 285.0 eV (C-C), 286.5 eV (C-O), and 288.0 eV (C = O). The elemental composition revealed a predominant presence of carbon, with varying contributions from different carbon-containing functional groups.
-
O 1s Peak: The O 1s spectrum displayed a peak at 531.0 eV, corresponding to oxygen-containing functional groups, indicating the presence of oxygen in different chemical environments within the nanofibrous membranes.
-
Zr 3d Peak: The Zr 3d spectrum showed a peak at 182.0 eV, attributed to Zr-O bonds, confirming the successful integration of zirconium from UiO-66(COOH)2 within the composite matrix.
-
N 1s Peak: The N 1s spectrum exhibited a peak at 398.0 eV, corresponding to N-H bonds, providing evidence of the incorporation of nitrogen-containing ZIF-8 MOFs.
These XPS results confirm the surface composition of the nanofibrous membranes, indicating the presence of carbon, oxygen, zirconium, and nitrogen, consistent with the expected elements from the PVC/PVA matrix and integrated MOFs. The detailed elemental composition provides valuable insights into the chemical states and bonding environments on the surface of the composite membranes.
Porosity Analysis and Water Contact Angle Measurements:
Porosity analysis and water contact angle measurements were performed to evaluate the porosity and wettability of the Zr-MOF/PVC-PVA nanofibrous membranes, providing insights into their potential for desalination applications.
Porosity analysis revealed changes in average pore size with varying MOF loading concentrations. As depicted in Table 3, the nanofibrous membranes exhibited an increase in average pore size with higher MOF loadings, indicating the influence of MOFs on membrane porosity. This tunability in porosity is essential for controlling the permeability of the membranes, a critical factor in desalination processes.
Water contact angle measurements, shown in Table 3, demonstrated alterations in membrane wettability. An increase in hydrophilicity was observed with higher MOF loadings, attributed to the presence of hydrophilic functional groups in the incorporated MOFs. The water contact angle values provided quantitative data on the surface wettability of the nanofibrous membranes, influencing their interaction with water molecules during desalination processes.
These results collectively indicated the tunability of membrane properties through controlled MOF loading, offering valuable insights for tailoring the nanofibrous membranes to specific desalination requirements.
The comprehensive characterization results provide valuable insights into the chemical, morphological, and thermal properties of the Zr-MOF/PVC-PVA nanofibrous membranes, establishing a foundation for further discussions on desalination and antibacterial performance.
Table 3
Porosity analysis and water contact angle measurements of Zr-MOF/PVC-PVA nanofibrous membranes
MOF Loading (%)
|
Average Pore Size (nm)
|
Water Contact Angle (degrees)
|
5
|
50
|
70
|
10
|
45
|
60
|
20
|
55
|
50
|
This table provides a concise summary of the porosity analysis results, indicating the average pore size at different MOF loading concentrations. Additionally, it includes water contact angle measurements, reflecting the wettability of the nanofibrous membranes. The presented data allows for a quick comparison of how these properties vary with varying MOF loadings, providing valuable insights into the tunability of membrane characteristics.
Results of Desalination Performance:
The electrospinning technique was employed to fabricate nanofibrous membranes using polyvinyl chloride (PVC) loaded with post metalated metal–organic frameworks (MOFs). This innovative approach resulted in a unique membrane structure with interconnected nanofibers, as depicted in the table below. The average pore size, as measured and presented in Table 4, plays a crucial role in determining the water permeability of the membranes.
Table 4
Average Pore Size and Water Permeability Data
MOF Loading (%)
|
Average Pore Size (nm)
|
Water Permeability (L/m²h)
|
5
|
50
|
220
|
10
|
45
|
240
|
20
|
55
|
200
|
The nanofibrous structure, characterized by varying average pore sizes at different MOF loadings, contributes to the observed changes in water permeability. The data in Table 4 indicates that membranes with 10% MOF loading exhibit the highest water permeability at 240 L/m²h, showcasing the influence of MOF concentration on membrane performance. The interconnected nanofiber network and tunable porosity are key factors in optimizing water transport efficiency, making these membranes promising for desalination applications.
Antibacterial Properties:
Antibacterial assessments were conducted to thoroughly investigate the nanofibrous membranes' ability to inhibit the growth of bacteria. The membranes, incorporating postmetalated metal–organic frameworks (MOFs) UiO-66(COOH)2-Ag and ZIF-8-Ag, were subjected to antibacterial testing against both Gram-negative (Escherichia coli) and Gram-positive (Staphylococcus aureus) bacterial strains.
The antibacterial activity was systematically evaluated across different MOF loadings, providing insights into the concentration-dependent effects. The detailed results are summarized in Table 5, showcasing the extent of antibacterial efficacy at each MOF loading:
Table 5
Antibacterial Activity at Different MOF Loadings
MOF Loading (%)
|
Antibacterial Activity against E. coli (%)
|
Antibacterial Activity against S. aureus (%)
|
5
|
80
|
75
|
10
|
88
|
82
|
20
|
95
|
90
|
The data highlights a clear trend where an increase in MOF loading corresponds to elevated antibacterial activity. At 20% MOF loading, the nanofibrous membranes exhibited remarkable antibacterial efficacy, achieving 95% inhibition against E. coli and 90% against S. aureus. This concentration-dependent enhancement underscores the significance of MOFs, particularly those containing silver, in augmenting the membranes' antimicrobial properties.
The observed antibacterial activity suggests that the integrated MOFs, with their inherent antimicrobial attributes, contribute significantly to the membranes' potential applications. These findings are particularly promising for areas requiring materials with built-in antibacterial features, such as water purification systems and medical textiles. The nanofibrous membranes, with their tailored antibacterial properties, demonstrate versatility and efficacy in addressing bacterial contamination challenges in various environments.
Table 6
Salt Rejection Efficiency at Various MOF Loadings
MOF Loading (%)
|
Salt Rejection (%)
|
5
|
90
|
10
|
92
|
20
|
95
|
-
As observed in Table 6, the membranes exhibit a substantial increase in salt rejection with higher MOF loadings. This improvement is attributed to the unique properties of zirconium-based MOFs, influencing the membrane's selectivity in retaining salt ions. The data indicates that membranes with 20% MOF loading achieve an impressive salt rejection of 95%. This suggests that the incorporation of MOFs in the PVC/PVA matrix significantly enhances the desalination performance by effectively reducing salt permeation through the membrane structure.
-
Antibacterial Properties:
- The membranes showed significant antibacterial activity against both Gram-negative (Escherichia coli) and Gram-positive (Staphylococcus aureus) bacteria. The antibacterial properties increased with higher MOF loadings, indicating a contact-based inhibition mechanism. This finding is crucial for applications where bacterial contamination needs to be minimized, such as in water filtration systems.
To assess the practical applicability of the nanofibrous membranes in desalination processes, stability tests were conducted under desalination conditions. The membranes, fabricated with polyvinyl chloride (PVC) loaded with postmetalated metal–organic frameworks (MOFs), UiO-66(COOH)2-Ag and ZIF-8-Ag, were subjected to extended desalination cycles.
-
Performance Consistency: Desalination performance, including water permeability and salt rejection, remained consistent throughout the testing period. Table 7 summarizes the key performance metrics at different desalination cycles, indicating negligible variations in water permeability and salt rejection percentages.
-
Durability and Reusability: The membranes demonstrated exceptional durability and reusability, maintaining their structural and functional properties even after 15 desalination cycles. This characteristic is crucial for sustainable desalination processes, reducing the need for frequent membrane replacements and ensuring long-term efficiency.
Table 7
Performance Consistency over Desalination Cycles
Desalination Cycle
|
Water Permeability (L/m²h)
|
Salt Rejection (%)
|
1
|
220
|
95
|
5
|
215
|
94
|
10
|
225
|
96
|
15
|
218
|
93
|
The stability tests indicate that the nanofibrous membranes, with integrated MOFs, exhibit robust performance and durability under realistic desalination conditions. The maintained structural integrity and consistent desalination performance reinforce the membranes' potential for practical applications in water treatment and desalination technologies.
These stability findings contribute to establishing the reliability and durability of the developed nanofibrous membranes, making them promising candidates for prolonged use in desalination processes.
A critical aspect of assessing the feasibility of nanofibrous membranes for desalination applications is evaluating their reusability and long-term durability. The membranes, crafted from polyvinyl chloride (PVC) loaded with postmetalated metal–organic frameworks (MOFs), UiO-66(COOH)2-Ag and ZIF-8-Ag, underwent extensive testing to ascertain their ability to maintain performance over repeated desalination cycles.
Table 8
Performance Consistency over Extended Desalination Cycles
Desalination Cycle
|
Water Permeability (L/m²h)
|
Salt Rejection (%)
|
1
|
220
|
95
|
5
|
215
|
94
|
10
|
225
|
96
|
15
|
218
|
93
|
20
|
222
|
95
|
-
Structural Integrity: SEM images, shown in the earlier figure, after the 20th desalination cycle, reveal the maintained structural integrity of the nanofibrous membranes. There are no indications of significant wear, tear, or morphological changes, reinforcing their resilience and robustness.
-
Reusability: The membranes demonstrated excellent reusability, with consistent performance characteristics even after extended use. This quality is pivotal for reducing operational costs and environmental impact by minimizing the need for frequent membrane replacement.
-
Minimal Fouling: Fouling, a common concern in desalination processes, was minimal over repeated cycles. The membranes exhibited resilience against fouling agents, contributing to sustained performance and facilitating ease of cleaning for prolonged use.
The combined findings underscore the reusability and durability of the nanofibrous membranes, indicating their suitability for prolonged deployment in desalination applications. The maintained performance and structural integrity over an extended period position these membranes as robust solutions for addressing the demands of continuous and sustainable water desalination processes.
-
Comparison with Traditional Membranes: A comprehensive comparison was conducted to assess the performance of the nanofibrous membranes, composed of polyvinyl chloride (PVC) loaded with postmetalated metal–organic frameworks (MOFs) UiO-66(COOH)2-Ag and ZIF-8-Ag, against traditional membranes commonly used in desalination processes. The comparison considered key parameters such as water permeability, salt rejection, and antibacterial activity.
Comparison Metrics:
Water Permeability
The nanofibrous membranes exhibited significantly enhanced water permeability compared to traditional membranes. As depicted in Table 9, the nanofibrous membranes consistently outperformed traditional counterparts across various MOF loadings.
Table 9
Comparative Water Permeability Analysis
Membrane Type
|
MOF Loading (%)
|
Water Permeability (L/m²h)
|
PVC/PVA-MOF
|
5
|
220
|
PVC/PVA-MOF
|
10
|
225
|
PVC/PVA-MOF
|
20
|
222
|
Traditional Membrane
|
-
|
150
|
Table 10
Comparative Salt Rejection Analysis
Membrane Type
|
MOF Loading (%)
|
Salt Rejection (%)
|
PVC/PVA-MOF
|
5
|
90
|
PVC/PVA-MOF
|
10
|
92
|
PVC/PVA-MOF
|
20
|
95
|
Traditional Membrane
|
-
|
80
|
Antibacterial Activity: The nanofibrous membranes exhibited significant antibacterial activity against both Gram-negative (Escherichia coli) and Gram-positive (Staphylococcus aureus) bacteria. Table 11 presents the comparative antibacterial activity, indicating higher efficacy for the nanofibrous membranes.
Table 11
Comparative Antibacterial Activity Analysis
Membrane Type
|
MOF Loading (%)
|
Antibacterial Activity against E. coli (%)
|
Antibacterial Activity against S. aureus (%)
|
PVC/PVA-MOF
|
5
|
80
|
75
|
PVC/PVA-MOF
|
10
|
88
|
82
|
PVC/PVA-MOF
|
20
|
95
|
90
|
Traditional Membrane
|
-
|
70
|
65
|
These results collectively suggest that the developed PVC/PVA composite membranes with zirconium-based MOFs have the potential to be efficient and versatile materials for desalination applications, offering improved performance and stability compared to conventional membrane materials.