Multi-Objective Optimization Design of a Metakaolin–Slag-Based Binary Solid Waste Geopolymer Mortar Mix Proportion Using Response Surface Methodology
Abstract
1. Introduction
2. Experiments
2.1. Raw Materials
2.2. Experimental Design
2.3. Preparation and Testing Methods for Geopolymer Materials
2.3.1. Preparation of Geopolymer Mortar
2.3.2. Mechanical Testing
2.3.3. Durability Testing
2.3.4. SEM Test
2.3.5. XRD Test
2.3.6. MIP Test
3. Results and Discussion
3.1. Compressive Strength
3.2. Water Absorption Rate
3.3. Response Surface Methodology for Optimizing MK–Slag Mix Proportion
3.3.1. Regression Equations and Analysis of Variance
3.3.2. Analysis of Response Surface Model Prediction Accuracy
3.3.3. Response Surface Analysis
3.4. Microstructural Analysis
3.4.1. SEM Analysis
3.4.2. XRD Analysis
3.4.3. MIP Analysis
4. Conclusions
- Single-factor experiments demonstrated that metakaolin–slag content, water/binder ratio, and water glass modulus significantly affect MK–slag properties. Increasing slag content improves mechanical strength and durability. Higher water/binder ratios decrease both strength and durability. Compressive strength initially increases and then decreases with water glass modulus, while water absorption is lowest at intermediate modulus values. At a modulus of 1.2, water absorption reaches 4.49%.
- RSM analysis yielded a quadratic polynomial model for 7-day and 28-day compressive strength and water absorption. Significant interactions among factors were observed. At a metakaolin–slag ratio of 45:55, water/binder ratio of 0.45, and water glass modulus of 1.3, 7-day and 28-day compressive strengths reached 73.8 MPa and 79.6 MPa, respectively, with water absorption at 3.36%.
- SEM, XRD, and MIP analyses show that with curing age, MK–slag hydration products increase, forming abundant N-A-S-H and C-(A)-S-H gels. These gels interlock to form a dense structure, enhancing mechanical strength and durability and clarifying the reaction mechanism of MK–slag.
- A comparative analysis with traditional cementitious materials shows that geopolymer materials reduce carbon emissions by 81.26–85.50% and lower carbon emission costs by 60.07–72.64%, demonstrating significant environmental benefits and a strong potential for practical application. For further details, refer to Appendix A.
- Although water absorption was used in this study as an indicator of pore connectivity to assess durability performance, this approach has certain limitations. Future research should incorporate additional durability indicators, such as moisture absorption and chloride ion permeability, to provide a more comprehensive evaluation of the durability of MK–slag mortar. Building on existing research, a more robust multi-objective optimization framework should be proposed to offer a theoretical basis for the development of solid waste-based green cementitious materials with excellent performance and cost-effectiveness.
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
Appendix A
| Indicator Name | Traditional Portland Cement | MK–Slag Geopolymer Materials (This Study) | Comparison of Differences | Data Sources and Explanation |
|---|---|---|---|---|
| Material Carbon Emissions (kg CO2/t) | 814–870 | 462–682 | Reduced by 21.61–43.24% | Calculated based on experimental results |
| Carbon emission costs (yuan/t) | 57.52 | 15.74–22.97 | Reduced by 60.07–72.64% | Without large-scale limestone calcination and high-temperature combustion processes |
| Carbon Footprint of Cementitious Materials (kg CO2-eq per t Slag) | High (919) | Low (767–839) | Geopolymer materials are more environmentally friendly | Slag is an industrial by-product |
| Industrial solid waste utilization rate | Low (0–20%) | High (55%) | The effect is obvious | Increase waste utilization |
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| Oxides | SiO2 | Al2O3 | Fe2O3 | CaO | MgO | SO3 | Other |
|---|---|---|---|---|---|---|---|
| Metakaolin | 52.22 | 43.49 | 0.63 | 0.52 | 1.09 | 0.37 | 1.68 |
| Slag | 31.44 | 14.29 | 0.31 | 42.07 | 8.64 | 2.18 | 2.07 |
| Number | MK–Slag Content/% | Water/Binder Ratio | Water Glass Modulus |
|---|---|---|---|
| 1 | 20:80 | 0.46 | 1.2 |
| 2 | 35:65 | 0.46 | 1.2 |
| 3 | 50:50 | 0.46 | 1.2 |
| 4 | 65:35 | 0.46 | 1.2 |
| 5 | 80:20 | 0.46 | 1.2 |
| 6 | 65:35 | 0.42 | 1.2 |
| 7 | 65:35 | 0.44 | 1.2 |
| 8 | 65:35 | 0.46 | 1.2 |
| 9 | 65:35 | 0.48 | 1.2 |
| 10 | 65:35 | 0.50 | 1.2 |
| 11 | 65:35 | 0.48 | 0.8 |
| 12 | 65:35 | 0.48 | 1.0 |
| 13 | 65:35 | 0.48 | 1.2 |
| 14 | 65:35 | 0.48 | 1.4 |
| 15 | 65:35 | 0.48 | 1.6 |
| Influencing Factors | Factor Number | Coded Value | ||
|---|---|---|---|---|
| −1 | 0 | 1 | ||
| Metakaolin-slag content/% | X1 | 45:55 | 55:45 | 65:35 |
| water/binder ratio | X2 | 0.45 | 0.47 | 0.49 |
| water glass modulus | X3 | 1.1 | 1.3 | 1.5 |
| Number | Metakaolin–Slag Content/% | Water/Binder Ratio | Water Glass Modulus | Y1/MPa | Y2/MPa | Y3/% |
|---|---|---|---|---|---|---|
| 1 | −1 | 0.45 | 1.3 | 75.2 | 79.5 | 3.21 |
| 2 | 1 | 0.45 | 1.3 | 61.8 | 69.3 | 4.01 |
| 3 | −1 | 0.49 | 1.3 | 68.1 | 68.4 | 3.96 |
| 4 | 1 | 0.49 | 1.3 | 55.9 | 60.5 | 4.72 |
| 5 | −1 | 0.47 | 1.1 | 68.4 | 75.5 | 3.72 |
| 6 | 1 | 0.47 | 1.1 | 50.2 | 67.3 | 4.66 |
| 7 | −1 | 0.47 | 1.5 | 63.1 | 75.4 | 3.98 |
| 8 | 1 | 0.47 | 1.5 | 58.2 | 61.3 | 4.48 |
| 9 | 0 | 0.45 | 1.1 | 58.1 | 74.2 | 3.63 |
| 10 | 0 | 0.49 | 1.1 | 56.7 | 66.7 | 4.52 |
| 11 | 0 | 0.45 | 1.5 | 67.5 | 73.4 | 3.74 |
| 12 | 0 | 0.49 | 1.5 | 54.6 | 59.9 | 4.35 |
| 13 | 0 | 0.47 | 1.3 | 64.6 | 75.1 | 3.59 |
| 14 | 0 | 0.47 | 1.3 | 65 | 73.7 | 3.64 |
| 15 | 0 | 0.47 | 1.3 | 63.9 | 73.3 | 3.51 |
| 16 | 0 | 0.47 | 1.3 | 63.8 | 75 | 3.68 |
| 17 | 0 | 0.47 | 1.3 | 62.2 | 72.4 | 3.63 |
| Source | 7 d Compressive Strength | 28 d Compressive Strength | Water Absorption | |||
|---|---|---|---|---|---|---|
| F-Value | p-Value | F-Value | p-Value | F-Value | p-Value | |
| Model | 55.39 | <0.0001 | 52.37 | <0.0001 | 117.76 | <0.0001 |
| X1 | 251.92 | <0.0001 | 179.92 | <0.0001 | 374.11 | <0.0001 |
| X2 | 79.17 | <0.0001 | 184.40 | <0.0001 | 364.20 | <0.0001 |
| X3 | 10.62 | 0.0139 | 20.69 | 0.0026 | 0.0166 | 0.9010 |
| X1X2 | 0.3059 | 0.5974 | 1.17 | 0.3160 | 0.1330 | 0.7261 |
| X1X3 | 37.58 | 0.0005 | 7.67 | 0.0277 | 16.10 | 0.0051 |
| X2X3 | 28.10 | 0.0011 | 7.94 | 0.0259 | 6.52 | 0.0379 |
| X12 | 3.94 | 0.0874 | 9.21 | 0.0190 | 92.84 | <0.0001 |
| X22 | 0.3220 | 0.5881 | 31.23 | 0.0008 | 16.18 | 0.0050 |
| X32 | 88.56 | <0.0001 | 22.29 | 0.0022 | 164.25 | <0.0001 |
| Lack-of-fit | 1.05 | 0.4608 | 0.6635 | 0.6616 | 0.3574 | 0.7878 |
| = 0.9862 | = 0.8901 | R2 = 0.9854 | = 0.9666 | R2 = 0.9934 | = 0.9697 | |
| = 0.9683 | C.V. = 1.74% | = 0.9666 | C.V. = 1.51% | = 0.9688 | C.V. = 1.39% | |
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Yin, R.; Zhu, L.; Cheng, D.; Liang, P.; Gao, R. Multi-Objective Optimization Design of a Metakaolin–Slag-Based Binary Solid Waste Geopolymer Mortar Mix Proportion Using Response Surface Methodology. Buildings 2026, 16, 402. https://doi.org/10.3390/buildings16020402
Yin R, Zhu L, Cheng D, Liang P, Gao R. Multi-Objective Optimization Design of a Metakaolin–Slag-Based Binary Solid Waste Geopolymer Mortar Mix Proportion Using Response Surface Methodology. Buildings. 2026; 16(2):402. https://doi.org/10.3390/buildings16020402
Chicago/Turabian StyleYin, Ruize, Lianyong Zhu, Dawei Cheng, Pengchang Liang, and Renfei Gao. 2026. "Multi-Objective Optimization Design of a Metakaolin–Slag-Based Binary Solid Waste Geopolymer Mortar Mix Proportion Using Response Surface Methodology" Buildings 16, no. 2: 402. https://doi.org/10.3390/buildings16020402
APA StyleYin, R., Zhu, L., Cheng, D., Liang, P., & Gao, R. (2026). Multi-Objective Optimization Design of a Metakaolin–Slag-Based Binary Solid Waste Geopolymer Mortar Mix Proportion Using Response Surface Methodology. Buildings, 16(2), 402. https://doi.org/10.3390/buildings16020402

