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Transforming environmental waste into valuable resources: characterization of clayey sludge from aggregate quarries for sustainable traditional ceramics

Published online by Cambridge University Press:  25 March 2026

Safaa Zahir*
Affiliation:
Georesources, Geoenvironment and Civil Engineering Laboratory (L3G), Faculty of Science and Technology, Cadi Ayyad University, Marrakech, Morocco
Lahcen Daoudi
Affiliation:
Georesources, Geoenvironment and Civil Engineering Laboratory (L3G), Faculty of Science and Technology, Cadi Ayyad University, Marrakech, Morocco
Meriam El Ouahabi
Affiliation:
Laboratory of Clay, Geochemistry and Sedimentary Environment (AGEs), Department of Geology, University of Liege, Belgium
Nathalie Fagel
Affiliation:
Laboratory of Clay, Geochemistry and Sedimentary Environment (AGEs), Department of Geology, University of Liege, Belgium
*
Corresponding author: safaa zahir; Email: safaa.zohir@gmail.com
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Abstract

The clayey sludge resulting from aggregate washing in quarries of the Marrakech region generates significant environmental impacts and adds an economic burden to the industry. This study aims to characterize these clayey sludges in order to explore their potential for ceramic applications. Fifteen samples were collected from various quarries along the major waterways of the Marrakech region. The physical properties of the clayey materials were analysed according to particle-size distribution and plasticity limits. The mineralogical composition was determined using X-ray diffraction and Fourier-transform infrared spectroscopy. The chemical composition was determined using X-ray fluorescence spectroscopy. The carbonate and volatile contents were determined by calcimetry and loss on ignition at 500°C and 950°C, respectively. SiO2 and Al2O3 are main constituents, while quartz, feldspars and clay minerals are the main phases, along with minor calcite and hematite. Illite is the dominant clay mineral, followed by kaolinite and chlorite. The clayey material exhibits low to medium plasticity and variable particle-size distributions. The chemical composition of these sludges confirms their potential for red ceramic applications. However, their low plasticity, variable particle-size distribution and mineralogical composition, characterized by a low clay mineral content, limit their direct applicability. To improve their suitability for ceramic production, adding clay-rich tempers is essential to enhancing their mineralogical composition, granulometry and plasticity. Furthermore, the results provide a valuable guide for selecting local materials for Marrakech pottery and can serve as a model for other regions.

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Type
Article
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0), which permits unrestricted re-use, distribution and reproduction, provided the original article is properly cited.
Copyright
© The Author(s), 2026. Published by Cambridge University Press on behalf of The Mineralogical Society of the United Kingdom and Ireland.
Figure 0

Figure 1. Geological map of the Tensift watershed and locations of the samples studied.

Figure 1

Figure 2. (a) Direct discharge of clayey sludge. (b & c) Clay extracted from sedimentation basins and then stored.

Figure 2

Table 1. Mineralogical composition of the bulk and clay fractions (wt.%).

Figure 3

Figure 3. SEM images of the samples: (a) NF2, (b) TN2 and (c) ZAT1.

Figure 4

Figure 4. FTIR spectra of the studied samples.

Figure 5

Table 2. FTIR absorption band assignment.

Figure 6

Figure 5. Projection of the studied samples in the ternary diagram modified from Strazzera et al. (1997).

Figure 7

Table 3. Chemical compositions (wt.%) of the raw samples.

Figure 8

Figure 6. Projection of the chemical compositions of the samples onto a (Fe2O3 + CaO + MgO)–Al2O3–(Na2O + K₂O) diagram (modified from Fiori et al., 1989).

Figure 9

Table 4. Physicochemical properties of the analysed samples.

Figure 10

Figure 7. SEM images of the samples: (a) ZAT1 and (b) LHJER1.

Figure 11

Figure 8. (a) Projection of the analysed samples in the ternary diagram modified from Shepard (1954); (b) textural classification modified from McManus (1988).

Figure 12

Figure 9. Projection of the studied clayey samples onto a diagram modified from Holtz & Kovacs (1981).

Figure 13

Figure 10. Projection of the studied clayey materials onto a diagram modified from Bain & Highley (1979).

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