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Low-cost membrane supports for wastewater treatment made from local clay and calcite mixtures

Published online by Cambridge University Press:  22 August 2025

Boukhemis Boudaira
Affiliation:
Laboratory of Photonic Physics and Multifunctional Nanomaterials, LPPNM, Mohamed Khider University, Biskra 07000, Algeria
Tarek Melki*
Affiliation:
Laboratory of Photonic Physics and Multifunctional Nanomaterials, LPPNM, Mohamed Khider University, Biskra 07000, Algeria
Mohamed Mouadh Messaoui
Affiliation:
Laboratory of Molecular Chemistry and Environment, LMCE, Mohamed Khider University, Biskra 07000, Algeria
Abdelhek Amri
Affiliation:
Laboratory of Metallic and Semiconducting Materials, LMSM, Mohamed Khider University, Biskra 07000, Algeria
Fatma Amraoui
Affiliation:
Laboratory of Metallic and Semiconducting Materials, LMSM, Mohamed Khider University, Biskra 07000, Algeria
Lobna Messeddek
Affiliation:
Laboratory of Metallic and Semiconducting Materials, LMSM, Mohamed Khider University, Biskra 07000, Algeria
Djamel Belamri
Affiliation:
Laboratory of Photonic Physics and Multifunctional Nanomaterials, LPPNM, Mohamed Khider University, Biskra 07000, Algeria
Boudjemaa Ghouil
Affiliation:
Laboratory of Condensed Matter Physics and Nanomaterials, Jijel University, Jijel 18000, Algeria
Abdelhamid Harabi
Affiliation:
Ceramics Laboratory, Physics Department, Faculty of Exact Science, Constantine University 1, Constantine 25000, Algeria
*
Corresponding author: Tarek Melki; Email: tarek.melki@univ-biskra.dz
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Abstract

Wastewater treatment is critically important and ceramic-membrane engineering is one of the most effective technologies for water filtration and purification. However, the materials used in the preparation of ceramic membranes are usually expensive, e.g. ZrO and Al2O3 membranes, reverse osmosis materials such as carbon-based thin-film nanocomposite TFNC ‘carbon nanotube, graphene-oxide’. Delicate, thin membranes employed for small-scale filtration usually require optimal supports for effective operation. The purpose of the present research, therefore, was to find a less expensive material for membrane supports while, at the same time, enhancing performance. Membrane supports were thus prepared from local clay materials and (25 wt.%) CaCO3 using an extrusion technique, which enabled the production of tubular supports. The CaCO3 is responsible for creating the pores in the samples during heat treatment due to the evolution of CO2 gas. Some characteristics of the supports were evaluated using X-ray diffraction, which identified quartz, gehlenite, sillimanite, H-bearing aluminous stishovite, and wollastonite. The support treated at 1000°C displayed significant mechanical properties (flexural strength, 11.58 MPa, measured using three-point bending tests) compared with supports treated at other temperatures. Moreover, the support sintered at 1000°C had an estimated permeability factor of 1052 L/h m2.bar after performing both time- and pressure-dependent flux measurements. Such properties make it possible to use these supports as multi-scale filtration membranes for purification and filtration applications after performing a standard filtration application on dirty water, resulting in a significant difference in terms of turbidity and waste content.

Information

Type
Original Paper
Copyright
© The Author(s), 2025. Published by Cambridge University Press on behalf of The Clay Minerals Society
Figure 0

Figure 1. Illustration of thermal processing: the first ascending temperature gradient of 2°C min–1 reaching 250°C was designed to expel volatile organic residues slowly and to avoid structural cracks or defects. It was held at this temperature for 30 min. A further gradient of 5°C min–1 followed until the desired sintering temperature was reached, with the slow release of CO2 and the burning off of organic additives from the mixture. This led to the formation of clean organized pores, followed by a 9°C min–1 cool down rate to avoid any thermal shock that may affect the ceramic support structure.

Figure 1

Figure 2. Schematic representation of the customized crossflow instrument used; both directions of compressed air and water flow are denoted with two circular arrows, and the applied pressure on the membrane support was controlled and monitored using the positioned V1, V2, V3, and V4 valves and the manometer.

Figure 2

Table 1. XRF elemental analysis of the raw clay powder and calcite

Figure 3

Figure 3. XRD patterns of clay powder before and after calcination (‘Raw clay’ 25°C; ‘Calcined clay’ 600°C). Q = quartz (ref: 00-046-1045); C = calcium oxide (ref: 00-005-0586); A = alumina (ref: 00-010-0173); H = hematite (ref: 00-024-0072); D = dolomite (ref: 00-036-0426); B = bredigite (ref: 00-036-0399); and P = palygorskite (ref: 00-031-0783).

Figure 4

Figure 4. XRD pattern of calcite. The intense calcite peaks indicated its high purity and quality.

Figure 5

Figure 5. Particle-size distribution for both of the materials used to produce ceramic supports. (A) Particle size distribution pattern of the bentonite after pre-processing via calcination and sieving. The effects of the treatments on the size of most bentonite grains were clear, and this is very important for controlling the pore sizes. (B) The same was true of the calcium carbonate used to ensure the uniform texture of the ceramic paste needed for extrusion, hence the exertion of CO2 gas while maintaining optimal pore sizes in the ceramic supports after calcination.

Figure 6

Figure 6. XRD patterns of sintered supports. (A) Two structures showed clear predominance in the 950°C supports, orthorhombic and tetragonal structures for sillimanite and gehlenite, respectively. (B) A clear dominance of orthorhombic gehlenite is seen in the supports sintered at 1000°C. (C) Wollastonite 1A became predominant in the supports sintered at 1050°C.

Figure 7

Figure 7. SEM images showing the surface morphology of sintered membrane supports. The decline in pore sizes with increased temperature (A: 950°C; B: 1000°C; C: 1050°C) was very evident. The supports sintered at 950°C (A) clearly had disordered welding networks at all scales, especially the images on the left-hand side (scale bars, 5 μm). The overall homogeneity of the surfaces of the supports at higher temperatures (1000°C, B; and 1050°C, C) sees the welding network disorder reduce disproportionately with sintering temperature, suggesting that the emergence of wollastonite as a major phase was responsible for surface harmonization, thus leading to the organized welding system.

Figure 8

Figure 8. Mechanical properties as a function of sintering temperature. The support sintered at 1000°C shows better bending stress and Young’s coefficient, due to the previously discussed relation between the proportion of gehlenite and its Mohs hardness, both of which affect the fragility of the supports.

Figure 9

Figure 9. Time-resolved flux rate under various levels of pressure for the support sintered at 1000°C. The increase in applied flux pressure was proportional to the mean flux rate. Increasing the flux pressure helped to increase the fluctuation, hence the instability in the flux through the supports. This suggests that extended measurements over a longer time range would eventually lead to a stabilizing flux rate.

Figure 10

Figure 10. Flux change as a function of the applied pressure. The permeability factor, k, was determined by linear fitting of three flux measurements at three different pressures: 0.5, 0.75, and 1 bar.

Figure 11

Figure 11. Variation in phase clarity and turbidity before and after filtering, proving the reliability of the ceramic support for filtration applications.