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Sustainable utilization of clay mineral-rich engineering muck via acid and alkali activation: a comparative study

Published online by Cambridge University Press:  03 July 2026

Ting Yu
Affiliation:
School of Environmental Science and Engineering, Guangdong University of Technology, Guangzhou, Guangdong, China Guangzhou Institute of Geochemistry, Chinese Academy of Sciences, Guangzhou, China
Jiarong Chen
Affiliation:
Guangzhou Institute of Geochemistry, Chinese Academy of Sciences, Guangzhou, China
Xiang Zhou
Affiliation:
Guangzhou Panyu Polytechnic, China
Baifa Zhang
Affiliation:
School of Environmental Science and Engineering, Guangdong University of Technology, Guangzhou, Guangdong, China
Mohammad Fahimizadeh
Affiliation:
School of Environmental Science and Engineering, Guangdong University of Technology, Guangzhou, Guangdong, China
Thammaros Pantongsuk
Affiliation:
Guangzhou Institute of Geochemistry, Chinese Academy of Sciences, Guangzhou, China
Jinghan Luo
Affiliation:
Guangzhou Institute of Geochemistry, Chinese Academy of Sciences, Guangzhou, China
Peng Yuan*
Affiliation:
School of Environmental Science and Engineering, Guangdong University of Technology, Guangzhou, Guangdong, China
*
Corresponding author: Peng Yuan; Email: yuanpeng@gdut.edu.cn
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Abstract

Engineering muck (EM) is an underutilized construction waste rich in clay minerals. The mechanical properties, composition, microstructures and reaction mechanisms of various EM-based geopolymers produced via acid or alkali activation are comprehensively compared and discussed in this study. The results indicate that EM mainly contains clay minerals (kaolinite, halloysite and dioctahedral mica), feldspar and quartz. The geopolymerization reactivity of EM was improved following crushing and calcination pretreatments, which destroyed the microstructure of the clay minerals and formed a reactive amorphous phase. Acid activation of calcined EM (EM700°C) resulted in greater geopolymerization reactivity than alkali activation. The highest 7 and 28 day compressive strengths of phosphoric acid-activated EM-based geopolymers reached 27.31 and 24.37 MPa, respectively, under a water/binder mass ratio of 0.7 and an Al/P molar ratio of 0.9. Comparatively, the maximum 7 and 28 day compressive strengths of alkali-activated EM-based geopolymers were only 7.82 and 11.66 MPa, respectively, under a water/binder mass ratio of 0.6 and a SiO2/Na2O molar ratio of 1.75. For phosphoric acid activation, reactive Al3+ mainly from calcined clay (e.g. metakaolinite) in EM700°C geopolymerized with PO43– and silica, forming phosphate-containing phases and amorphous silico-aluminophosphate (SAP; Si–O–Al–O–P) gels. In contrast, reactive SiO2 and Al2O3 from EM700°C participated in the geopolymerization process in alkaline solution, forming sodium aluminosilicate hydrate (N–A–S–H) gels and the byproduct faujasite. The geopolymerization reactivity of EM700°C and the resulting composition variations in various solutions contributed to the differences in the compressive strengths of EM-based geopolymers. This study provides a theoretical basis for preparing acid/alkali-activated geopolymers from EM.

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Article
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. Experimental process of acid and alkaline EM-based geopolymer preparation.Figure 1 long description.

Figure 1

Table 1. Mixture design of PG and AG.Table 1 long description.

Figure 2

Table 2. Chemical composition of the EM and EM700°C (wt.%).Table 2 long description.

Figure 3

Figure 2. (a & b) XRD traces, (c) FTIR spectra, (d) TG/DTG results and SEM images of (e) EM and (f) EM700°C.Figure 2 long description.

Figure 4

Figure 3. Compressive strength of PGs with different (a) water/binder mass ratios and (b) Al/P molar ratios. Compressive strength of AGs with different (c) water/binder mass ratios and (d) SiO2/Na2O molar ratios. d = day.Figure 3 long description.

Figure 5

Figure 4. XRD results of PGs with different (a) water/binder mass ratios and (b) Al/P molar ratios. XRD results of AGs with different (c) water/binder mass ratios and (d) SiO2/Na2O molar ratios.Figure 4 long description.

Figure 6

Figure 5. FTIR spectra of (a) PGs with various Al/P molar ratios and (b) AGs with various SiO2/Na2O molar ratios.Figure 5 long description.

Figure 7

Table 3. Wavenumbers and assignments of the FTIR spectroscopy peaks.Table 3 long description.

Figure 8

Figure 6. SEM images of PG with various Al/P molar ratios: (a–c) Al/P = 0.7, (d–f) Al/P = 0.9 and (g–i) Al/P = 1.1.

Figure 9

Figure 7. SEM images of AG with various SiO2/Na2O molar ratios: (a–c) W = 1.25, (d–f) W = 1.50 and (g–i) W = 1.75.

Figure 10

Figure 8. Pore structures of PG with various Al/P molar ratios and AG with various SiO2/Na2O molar ratios: (a) total porosity and (b) pore-size distribution.Figure 8 long description.

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