Interpretable AI for Site-Adaptive Soil Liquefaction Assessment
Abstract
1. Introduction
2. Materials and Methods
2.1. Data
2.2. Rough Set Machine Learning
- Data Examination: The raw dataset was reviewed for completeness, ensuring each seismic event included all necessary geotechnical parameters. Independent (condition) and dependent (decision) attributes were identified (see Table 2).
- Initial Discretization of Continuous Variables: As RST requires categorical inputs, continuous parameters were discretized into bins using thresholds based on median values. Extreme values (i.e., outliers) were labeled “Very Low” or “Very High” to address skewed distributions. Median-based discretization has been shown to be an effective binning approach in previous liquefaction studies [26,27]. Geotechnical parameters are often characterized by skewed distributions, for which the median provides a more representative measure of central tendency than the mean, as it is less sensitive to outliers and extreme values [27,31,32]. Consequently, median-based thresholds offer a robust and physically interpretable basis for discretizing continuous variables in liquefaction assessment.
- Creation of Decision Tables: Discretized data were organized into decision tables, forming the basis for rule induction (Table 3 provides a sample format). The qualitative labels used in Table 3 (e.g., ‘low,’ ‘high,’ ‘very high’) correspond to discretized ranges of each continuous parameter as defined by the rule-based model. For clarity, the numerical thresholds that delineate these categories (e.g., the specific range of classified as ‘high’) are provided in Figure 4. These thresholds allow consistent interpretation and implementation of the qualitative descriptors.
- Rule Induction: Decision rules were generated using the exhaustive algorithm in RSES 2.2, which yielded optimal accuracy and coverage.
- Rule Optimization: Redundant or weak rules were removed through filtering and shortening features of RSES 2.2, retaining only those that captured essential parameter interactions.
- Rule Set Evaluation: Rule sets were assessed by their accuracy, coverage, and size, balancing generalization and predictive strength.
- Final Optimization: Discretization thresholds were iteratively refined using statistical feedback (i.e., balancing accuracy and coverage) and geotechnical literature. Figure 4 shows the final discretization adopted in this study. The resulting rule set represents a framework for liquefaction assessment.
2.3. Interpretive Analysis
2.3.1. Sensitivity Analysis Using Ablation
2.3.2. Scenario and Parameter Interaction Maps
2.4. Evaluation and Application
3. Results and Discussion
3.1. Data
3.2. Rough Set Machine Learning
3.2.1. The Best Rule Set
3.2.2. Interpretation of Rules
3.3. Interpretive Analysis
3.3.1. Sensitivity Analysis
3.3.2. Scenario Map
3.3.3. Parameter Interaction Map
3.4. Evaluation and Application
3.4.1. Rule-Based Predictive Model
- Data Collection: All parameters required for liquefaction assessment are collected, as described in Section 2.2.
- Susceptibility Screening: Soil layers that are not susceptible to liquefaction are excluded from further analysis. These include:
- (1)
- layers located below the groundwater table,
- (2)
- layers classified as high-plasticity soils, and
- (3)
- layers with raw SPT -values greater than 30.
- Completeness of Parameters: Borehole sites with incomplete parameter sets are excluded from the analysis, and alternative site-specific liquefaction investigation methods are recommended for such cases.
- Discretization of Parameters: Continuous input variables are discretized using the parameter discretization scheme shown in Figure 4.
- Activated Rule Determination: The discretized parameters of each soil layer are compared against the rule set generated by the RSML (Table 7). All rules that are satisfied by the input conditions are identified as activated rules.
- Prediction and Interpretation: The final liquefaction prediction is determined by the activated rule with the highest certainty factor. Any remaining activated rules are used to aid interpretation of the site conditions. If no rule is activated, this indicates that similar site conditions are not represented in the historical dataset, and the rule-based model is considered not applicable for that site.
3.4.2. Model Evaluation
3.4.3. Rule-Based Model Application on the 2023 Turkey Earthquake
3.4.4. Practical Applications
3.5. Discussion
3.5.1. Core Findings of the Study
3.5.2. Methodological Advantages and Comparison with the Existing Models
3.5.3. Limitations and Opportunities for Improvement
4. Conclusions
Supplementary Materials
Author Contributions
Funding
Data Availability Statement
Acknowledgments
Conflicts of Interest
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| ID | Event | M | amax (g) | R (km) | Avg Depth (m) | Depth GWT (m) | N60 | FC | Liq? |
|---|---|---|---|---|---|---|---|---|---|
| 1 | 1944 Tohnankai | 8.1 | 0.2 | 171.5 | 5.2 | 2.1 | 5.9 | 10 | Yes |
| 2 | 1944 Tohnankai | 8.1 | 0.2 | 167.5 | 4.3 | 2.4 | 2.3 | 30 | Yes |
| 3 | 1944 Tohnankai | 8.1 | 0.2 | 170.1 | 3.7 | 2.1 | 1 | 27 | Yes |
| 4 | 1948 Fukui | 7 | 0.4 | 3.4 | 4 | 1.2 | 8 | 0 | Yes |
| 5 | 1948 Fukui | 7 | 0.35 | 6.8 | 7.5 | 3.7 | 17.3 | 4 | Yes |
| 6 | 1964 Niigata | 7.6 | 0.09 | 158.6 | 3.3 | 1 | 2.6 | 5 | Yes |
| Attributes | Definition | Condition or Decision | Range of Values | Continuous or Categorical |
|---|---|---|---|---|
| M | Moment Magnitude | Condition | 5.9 to 8.3 | Continuous |
| amax (g) | Maximum Acceleration | Condition | 0.052 to 0.84 | Continuous |
| R (km) | Epicentral Distance | Condition | 2.2 to 257.1 | Continuous |
| Avg depth (m) | Average Depth | Condition | 1.8 to 14.3 | Continuous |
| Depth GWT (m) | Depth of Groundwater Table | Condition | 0 to 7.7 | Continuous |
| N60 | SPT N-value corrected to 60% Hammer Efficiency | Condition | 1.0 to 50.8 | Continuous |
| FC (%) | Fines Content | Condition | 0 to 92 | Continuous |
| Liq? | No or Yes | Decision | N/A | Categorical |
| M | amax (g) | R (km) | Avg Depth (m) | Depth GWT (m) | N60 | FC (%) | Liq? |
|---|---|---|---|---|---|---|---|
| High | High | High | High | High | Low | High | No |
| High | High | High | Low | High | Low | High | No |
| High | High | High | Low | High | Low | High | No |
| High | Very High | Low | Low | Low | Low | Low | No |
| High | Very High | Low | High | High | High | Low | No |
| High | Low | High | Low | Low | Low | High | No |
| High | Low | High | High | Low | Low | Low | No |
| Parameters | Manila City | Quezon City |
|---|---|---|
| Number of borehole data | 88 | 63 |
| Moment magnitude | 7.5 | |
| Maximum horizontal acceleration | 0.38 g | 0.39 g |
| Epicentral distance (from the Marikina West Valley Fault) | 10.65 km | 4.34 km |
| Hammer efficiency correction (CE) | 1.25 | |
| Borehole diameter correction (CB) | 1.00 | |
| Rod length correction (CR) | 3–4 m (10–13 ft) 4–6 m (13–20 ft) 6–10 m (20–30 ft) >10 m (>30 ft) | 0.75 0.85 0.95 1.00 |
| Sampling method correction (CS) | 1.20 | |
| Correction due to overburden pressure (CN) | Liao and Whitman (m = 0.5) | |
| Statistic | M | amax (g) | R (km) | Avg Depth (m) | Depth GWT (m) | N60 | FC (%) |
|---|---|---|---|---|---|---|---|
| Minimum | 5.90 | 0.05 | 2.23 | 1.80 | 0.00 | 1.00 | 0.00 |
| Maximum | 8.30 | 0.84 | 257.05 | 14.30 | 7.70 | 50.80 | 92.00 |
| Range | 2.40 | 0.79 | 254.82 | 12.50 | 7.70 | 49.80 | 92.00 |
| Median | 6.93 | 0.24 | 36.60 | 4.60 | 1.80 | 10.00 | 8.00 |
| Mean | 7.15 | 0.30 | 60.01 | 5.10 | 1.98 | 12.15 | 17.58 |
| Standard deviation (n-1) | 0.52 | 0.16 | 46.09 | 2.15 | 1.24 | 8.78 | 21.77 |
| Skewness (Pearson) | −0.18 | 1.01 | 1.17 | 1.05 | 1.49 | 1.58 | 1.69 |
| Rule Set Characteristics | Initial Discretization | Selected Best Rule Set |
|---|---|---|
| Shortening Ratio | 0.8 | 0.8 |
| Minimum Number of Supports per Rule | 5 | 5 |
| Number of Rules | 30 | 25 |
| Accuracy (All Data) | 86.8% | 86.2% |
| Coverage (All Data) | 87.3% | 86.4% |
| Accuracy (90/10 Split) | 82.6% | 86.4% |
| Coverage (90/10 Split) | 88.5% | 84.6% |
| Rules | M | amax (g) | R (km) | Avg Depth (m) | GWT | Avg Nm | FC (%) | Liq |
|---|---|---|---|---|---|---|---|---|
| 1 | Very High | Low | Yes | |||||
| 2 | High | Low | High | Yes | ||||
| 3 | High | Low | High | Yes | ||||
| 4 | High | High | Low | Yes | ||||
| 5 | High | Low | Low | Yes | ||||
| 6 | High | High | Low | Yes | ||||
| 7 | Very High | Low | Yes | |||||
| 8 | Very High | Very High | Yes | |||||
| 9 | High | Very High | Yes | |||||
| 10 | High | Low | Low | Low | Yes | |||
| 11 | Low | High | Low | Yes | ||||
| 12 | Low | Low | Low | Yes | ||||
| 13 | High | Low | Low | Yes | ||||
| 14 | High | High | Low | Yes | ||||
| 15 | High | Low | High | Yes | ||||
| 16 | Very High | No | ||||||
| 17 | Low | High | No | |||||
| 18 | High | High | No | |||||
| 19 | Low | High | No | |||||
| 20 | High | High | No | |||||
| 21 | Low | Low | No | |||||
| 22 | Low | High | No | |||||
| 23 | High | Low | No | |||||
| 24 | Low | High | No | |||||
| 25 | Low | Low | High | High | No |
| Attribute Removed | Total Accuracy (k = 10 Folds) | Total Accuracy (k = 100 Folds) |
|---|---|---|
| No Attribute Removed | 78.8 | 79.5 |
| Moment Magnitude | 76.0 | 77.5 |
| Maximum Acceleration | 71.2 | 70.5 |
| Epicentral Distance | 75.2 | 75.0 |
| Average Depth | 76.0 | 76.0 |
| Depth of Groundwater Table | 76.0 | 76.0 |
| N value corrected to 60% Hammer Efficiency | 53.2 | 50.0 |
| Fines Content | 78.4 | 78.5 |
| Metrics | Formula | Solution | Value |
|---|---|---|---|
| Accuracy | (TP + TN)/(TP + TN + FP + FN) | (466 + 565)/(1099) | 93.81% |
| Precision | TP/(TP + FP) | 466/(466 + 32) | 93.57% |
| Recall | TP/(TP + FN) | 466/(466 + 36) | 92.83% |
| Specificity | TN/(TN + FP) | 565/(565 + 32) | 94.64% |
| F1 Score | 2 × (Precision × Recall)/(Precision + Recall) | 93.20% | |
| Parameters | Boulanger and Idriss Model | Rule-Based Model |
|---|---|---|
| Moment magnitude | 7.8 (Pazarcik) & 7.6 (Elbistan) | |
| Maximum horizontal acceleration | 0.45 g | |
| Epicentral distance | - | 85 km (Pazarcik) 55 km (Elbistan) |
| Average depth | 1.50–19.50 m | |
| Depth of Groundwater Table | 1.9 m | |
| SPT N-value corrected to 60% Hammer Efficiency | 8–23 | |
| Fines Content | 35% | |
| Liquefied? (in Actual) | Yes | |
| Tool/Tool Combination | Proposed Applications |
|---|---|
| Decision Rules |
|
| Scenario Maps |
|
| Interaction Maps |
|
| Decision Rules + Scenario Maps |
|
| Decision Rules + Parameter Interaction Maps |
|
| Scenario + Parameter Interaction Maps |
|
| All Three Tools Combined |
|
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Torres, E.; Dungca, J. Interpretable AI for Site-Adaptive Soil Liquefaction Assessment. Geosciences 2026, 16, 25. https://doi.org/10.3390/geosciences16010025
Torres E, Dungca J. Interpretable AI for Site-Adaptive Soil Liquefaction Assessment. Geosciences. 2026; 16(1):25. https://doi.org/10.3390/geosciences16010025
Chicago/Turabian StyleTorres, Emerzon, and Jonathan Dungca. 2026. "Interpretable AI for Site-Adaptive Soil Liquefaction Assessment" Geosciences 16, no. 1: 25. https://doi.org/10.3390/geosciences16010025
APA StyleTorres, E., & Dungca, J. (2026). Interpretable AI for Site-Adaptive Soil Liquefaction Assessment. Geosciences, 16(1), 25. https://doi.org/10.3390/geosciences16010025

