Climate-Sensitive Staged Predictive Framework for Sustainable Residential Retrofit Assessment Using Adaptable Base Model Templates
Abstract
1. Introduction
2. Research Gaps and Innovations
3. Methodology
3.1. Modeling and Simulation Platforms
3.2. Base Models’ Verification and Output Reliability Assessment
3.3. Predictive Modeling Strategy
3.3.1. Stage 1 (Two-Variable Case)
- Establishment of Base Model: At first, it is necessary to establish a base model/case study in a building energy modeling environment (the procedure of establishing our base cases has been discussed in Section 3.1).
- Selection of Decision Variables: Instead of choosing the decision variables arbitrarily, a sensitivity analysis is needed to evaluate the influence of the input parameters on different performance metrics. After that, the two most influential parameters can be selected for analysis on the chosen performance metrics, such as AEC, HL, CL and TDH.
- Design the Parametric Study: In this step, the ranges of the two selected input variables were defined. The sample size was chosen to adequately capture the shape of the curve. A total of 16 unique input combinations (4 values of length × 4 values of aspect ratio) were considered for each orientation, resulting in 128 samples across all eight orientations. Mathematically, the rationale is that the number of points must meet or exceed the number of independent parameters in the function’s formula [60]. Moreover, at least four points are recommended per curve to understand the shape of the curve [61].
- Run Simulations: After the preparation of the sample size, the parametric cases were simulated with the help of an energy simulation tool called jEPlus. Therefore, a complete dataset was established that links inputs to outputs.
- Fit the Curves and Choose a Base Function: At this stage, graphs were plotted by using the dataset to visualize the output trends, with one variable examined across the levels of the other. Each curve was fitted using an appropriate functional form (e.g., polynomial, exponential, or logarithmic). Among these, a quadratic polynomial h(x) = ax2 + bx + c provided the best fit across all curves. A satisfactory fit quality was ensured, with R2 values close to 1 for the fitted quadratic curves. From these fitted curves, a base case (r = 1) was selected as the reference function. A Python (v3.13.5)routine was used to derive the best fit in this study, but any equivalent mathematical environment can also be used.
- Transformation of Other Curves: The idea was to represent each target curve as a transformed version of the selected base curve. Therefore, the transformation equation was defined as , where h(x) = f(α, 1, x) is the base function for r = 1. Here, α represents the fixed variable, while A(r), B(r), C(r) and D(r) are the transformation parameters. Specifically, A(r) controls vertical stretching/compression, B(r) controls horizontal stretching/compression, C(r) controls horizontal shifting, and D(r) controls the vertical shifting. Instead of estimating the transformation parameters separately for each (r) and then fitting them afterward, the coefficients of A(r), B(r), C(r), and D(r) were optimized simultaneously using a global nonlinear least-squares approach. In this formulation, each transformation function was represented as a quadratic function of r (ar2 + br + c), and the optimization minimized the combined error between all transformed base curves and the corresponding fitted target curves within the selected fitting region. A smoothness regularization term was also included to reduce excessive curvature in the transformation functions and improve interpolation stability for intermediate (r) values.
- Prediction: Once fitted, the transformation relation allows the prediction of AEC for unseen input values. By calibrating only four transformation parameters, the need to re-fit individual curves each time was eliminated, making the approach generic and function-independent.
- Validation and Quality Classification: Model accuracy is assessed by comparing predicted and simulated values using MAPE,
3.3.2. Stage 2 (Three-Variable Case)
- Fit the Surfaces and Choose a Base Function: The outputs were visualized in three dimensions by plotting AEC as a function of orientation (z) and length (x) at a fixed aspect ratio (r). The quadratic surface provided the best fit for all the surfaces with R2 = 0.98. This is the simplest polynomial that can effectively represent curvature in both directions and their interrelation. Moreover, r = 1 was selected as the base surface among the surfaces.
- Transformation of Other Surfaces: The transformation function in this case was formulated as . Here, A and D depict vertical scaling and shifting. Moreover, B1 and C1 are horizontal scaling and shifting along the x axis, while B2 and C2 do the same along the z axis. Instead of estimating these transformation parameters separately for each (r) and then fitting them afterward, the coefficients of A(r), B1(r), C1(r), B2(r), C2(r), and D(r) were optimized simultaneously using a global nonlinear least-squares approach. Each transformation function was represented as a quadratic function of r (a0 + a1r + a2r2), and the optimization minimized the combined error between all transformed base surfaces and the corresponding fitted target surfaces across the selected fitting region. A smoothness regularization term was also included to reduce excessive curvature in the transformation functions and improve interpolation stability for intermediate r values.
- Prediction: In this step, the transformation relation predicts the AEC for any unseen combination of orientation, length and aspect ratio. Therefore, calibrating six transformation parameters (A, B1, C1, B2, C2 and D) eliminates the need to re-fit individual surfaces, making the workflow generic and computationally efficient.
3.3.3. Stage 3 (Multi-Variable Case)
4. Results and Discussions
4.1. Two-Variable Analysis: Patterns and Fitting
4.2. Prediction Accuracy and Agreement Across Orientations (Two-Variable Case)
4.3. Three-Variable Analysis: Patterns and Fitting
4.4. Prediction Accuracy and Agreement in Three-Variable Case
4.5. Prediction Accuracy and Agreement in Three-Variable Case Using Support Vector Machine (SVM)
4.6. Prediction Accuracy and Agreement in Multi-Variable Case with ANN, SVM, RF, and DT
4.7. Cross-Climate Applicability of the Proposed Framework
5. Conclusions
Supplementary Materials
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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| Parameter | Description |
|---|---|
| Total floor area | 16 m2 (CS), 12 m2 (IS) |
| Orientation | 0° |
| Roof construction R-value | 5.34 m2·K/W. |
| Wall construction R-value | 3.40 m2·K/W |
| Floor construction R-value | 2.46 m2·K/W |
| Glazing specification | U = 2.0 W/m2·K, solar heat gain coefficient (SHGC) = 0.25, visible transmittance (VT) = 0.50 |
| Window-to-wall ratio (WWR) | 30% |
| Heating setpoint | 20 °C |
| Cooling setpoint | 24 °C |
| Infiltration | Air changes/hour (ACH) = 0.75 |
| Lighting | Lighting power density (LPD) = 4 W/m2 |
| Equipment | Laptop = 2.5 W/m2 |
| Occupancy | 1 person (space/space-type) |
| Climate | CS-HL (MJ/m2·a) | CS-CL (MJ/m2·a) | IS-HL (MJ/m2·a) | IS-CL (MJ/m2·a) | NCC HLL (MJ/m2·a) | NCC CLL (MJ/m2·a) | Status |
|---|---|---|---|---|---|---|---|
| Melbourne | 39.48 | 2.88 | 16.80 | 4.20 | 318.00 | 44.90 | Compliant |
| Adelaide | 6.95 | 23.53 | 0.90 | 24.30 | 233.50 | 70.70 | Compliant |
| Brisbane | 2.95 | 51.37 | 1.25 | 58.20 | 77.76 | 283.67 | Compliant |
| Canberra | 56.22 | 7.46 | 28.20 | 8.40 | 403.51 | 75.83 | Compliant |
| Darwin | 0.45 | 234.22 | 0.23 | 236.70 | 4 | 1127.78 | Compliant |
| Hobart | 45.59 | 0.55 | 20.70 | 0.90 | 381.38 | 14.58 | Compliant |
| Perth | 1.06 | 42.83 | 0.95 | 45 | 155.22 | 113.50 | Compliant |
| Sydney | 0.74 | 24.38 | 0.67 | 31.80 | 143.02 | 156.73 | Compliant |
| Comparison Item | Melbourne Residential Reference Model | Proposed CS/IS Models | Consistency Observation |
|---|---|---|---|
| Model scale | Whole detached residential house | Space-level CS and IS templates | Different scales, but both represent residential thermal behavior. |
| Weather file | Melbourne | Melbourne | Same primary climate context. |
| Energy assessment basis | FirstRate5/NatHERS | OpenStudio/EnergyPlus | Different simulation platforms used for residential thermal assessment. |
| Heating/cooling behavior | Heating = 411.0 MJ/m2; Cooling = 81.9 MJ/m2 | CS: HL = 39.48 MJ/m2, CL = 2.88 MJ/m2; IS: HL = 16.80 MJ/m2, CL = 4.20 MJ/m2 | All cases present heating dominated behavior under Melbourne conditions. |
| Orientation effect | Total load varies from 492.9 to 517.7 MJ/m2 across 0–315° orientations | CS total load varies from 60.53 to 111.83 MJ/m2; IS total load varies from 39.30 to 87.60 MJ/m2 across 0–315° orientations | Both demonstrate orientation dependent thermal response. |
| Improved envelope response | At 0°, total load reduces from 492.9 to 109.8 MJ/m2 in the improved/insulated case | At 0°, CS total load reduces from 109.35 to 60.53 MJ/m2 and IS total load reduces from 71.70 to 39.30 MJ/m2 in the improved/insulated case | Both cases represent that improved envelope performance reduces the total energy load. |
| Climate | Model | First Stable Interval | Avg |Δμ*| AEC (%) | Avg |Δμ*| HL (%) | Avg |Δμ*| CL (%) | Avg |Δμ*| TDH (%) | Stability Criterion | Meets Criterion? |
|---|---|---|---|---|---|---|---|---|
| Melbourne | CS | 300 → 400 | 4.55 | 7.09 | 6.96 | 6.84 | ≤10–15% | Yes |
| Melbourne | IS | 100 → 200 | 3.19 | 5.03 | 7.29 | 6.33 | ≤10–15% | Yes |
| Adelaide | CS | 300 → 400 | 1.79 | 4.06 | 5.10 | 10.08 | ≤10–15% | Yes |
| Adelaide | IS | 300 → 400 | 3.10 | 4.66 | 6.83 | 5.10 | ≤10–15% | Yes |
| Brisbane | CS | 200 → 300 | 5.35 | 10.17 | 4.63 | 9.49 | ≤10–15% | Yes |
| Brisbane | IS | 200 → 300 | 5.76 | 9.91 | 8.43 | 3.93 | ≤10–15% | Yes |
| Canberra | CS | 100 → 200 | 3.81 | 5.55 | 6.56 | 6.40 | ≤10–15% | Yes |
| Canberra | IS | 200 → 300 | 2.59 | 2.94 | 10.13 | 8.32 | ≤10–15% | Yes |
| Darwin | CS | 400 → 500 | 4.25 | 12.95 | 6.19 | 4.86 | ≤10–15% | Yes |
| Darwin | IS | 400 → 500 | 3.39 | 20.16 | 6.34 | 3.99 | ≤10–15% | Partial |
| Hobart | CS | 300 → 400 | 2.91 | 5.98 | 9.35 | 7.99 | ≤10–15% | Yes |
| Hobart | IS | 200 → 300 | 5.36 | 4.54 | 11.35 | 10.95 | ≤10–15% | Yes |
| Perth | CS | 300 → 400 | 4.12 | 8.98 | 6.33 | 3.69 | ≤10–15% | Yes |
| Perth | IS | 200 → 300 | 3.15 | 3.14 | 9.98 | 3.82 | ≤10–15% | Yes |
| Sydney | CS | 200 → 300 | 3.51 | 2.91 | 7.72 | 7.97 | ≤10–15% | Yes |
| Sydney | IS | 100 → 200 | 4.80 | 8.52 | 9.01 | 4.91 | ≤10–15% | Yes |
| Decision Variables | Range | Step |
|---|---|---|
| Orientation | 0–315° | 45 |
| HSP | 18–23 | 1 |
| CSP | 24–28 | 1 |
| Roof R values | 1–6 | 1 |
| Wall R values | 1–4 | 1 |
| Window U values | 1–6 | 1 |
| Climate | Corner Space (CS) Train MAPE, Median (Range) (%) | Corner Space (CS) Extra-Validation MAPE, Median (Range) (%) | Intermediate Space (IS) Train MAPE, Median (Range) (%) | Intermediate Space (IS) Extra-Validation MAPE, Median (Range) (%) |
|---|---|---|---|---|
| Melbourne | 0.27 (0.15–0.39) | 0.32 (0.24–0.51) | 0.62 (0.40–1.13) | 0.71 (0.42–1.19) |
| Adelaide | 0.20 (0.15–0.29) | 0.25 (0.14–0.56) | 0.36 (0.28–0.56) | 0.35 (0.25–1.21) |
| Brisbane | 0.12 (0.08–0.20) | 0.15 (0.10–0.23) | 0.16 (0.10–0.57) | 0.15 (0.12–0.51) |
| Canberra | 0.12 (0.09–0.22) | 0.17 (0.12–0.35) | 0.30 (0.20–0.63) | 0.36 (0.22–0.77) |
| Darwin | 0.04 (0.02–0.06) | 0.09 (0.03–0.56) | 0.05 (0.03–0.07) | 0.83 (0.17–2.07) |
| Hobart | 0.32 (0.27–0.52) | 0.40 (0.24–0.69) | 1.08 (0.63–1.18) | 0.82 (0.50–1.15) |
| Perth | 0.12 (0.04–0.19) | 0.14 (0.06–0.20) | 0.23 (0.15–0.39) | 0.25 (0.10–0.45) |
| Sydney | 0.13 (0.07–0.31) | 0.19 (0.09–0.40) | 0.33 (0.23–0.46) | 0.29 (0.23–0.59) |
| Climate | (CS) A-Tr MAPE (%) | (CS) A-EV MAPE (%) | (CS) S-Tr MAPE (%) | (CS) S-EV MAPE (%) | (IS) A-Tr MAPE (%) | (IS) A-EV MAPE (%) | (IS) S-Tr MAPE (%) | (IS) S-EV MAPE (%) |
|---|---|---|---|---|---|---|---|---|
| Melbourne | 8.38 | 5.82 | 0.75 | 0.77 | 13.37 | 9.33 | 0.89 | 0.94 |
| Adelaide | 9.56 | 7.75 | 0.27 | 0.63 | 14.94 | 12.72 | 0.94 | 0.81 |
| Brisbane | 9.15 | 8.67 | 0.31 | 0.45 | 15.54 | 15.57 | 0.36 | 0.51 |
| Canberra | 7.68 | 5.51 | 1.03 | 1.10 | 11.09 | 7.72 | 0.97 | 1.25 |
| Darwin | 6.72 | 6.74 | 0.27 | 0.38 | 10.20 | 10.57 | 0.31 | 1.75 |
| Hobart | 11.84 | 8.26 | 0.77 | 1.02 | 17.07 | 11.94 | 1.10 | 1.51 |
| Perth | 9.19 | 8.58 | 0.30 | 0.50 | 16.14 | 15.01 | 0.35 | 0.55 |
| Sydney | 11.51 | 10.02 | 0.25 | 0.62 | 16.91 | 14.80 | 0.39 | 0.73 |
| Climate | Sample Sizes | |||||||||
|---|---|---|---|---|---|---|---|---|---|---|
| 100 | 200 | 300 | 400 | 500 | ||||||
| CS | IS | CS | IS | CS | IS | CS | IS | CS | IS | |
| Melbourne | SVM | SVM | SVM | SVM | ANN | ANN | RF | ANN/RF | ANN | ANN/RF |
| Adelaide | SVM | SVM | SVM | SVM | ANN | ANN/RF | ANN/RF | ANN/RF | ANN/RF | ANN/RF |
| Brisbane | SVM/RF | RF | SVM/RF | RF | ANN | RF | ANN/RF/SVM | RF | ANN/RF | ANN/RF |
| Canberra | SVM | SVM | SVM | SVM | ANN/RF/SVM | ANN/RF/SVM | RF/ SVM | ANN | ANN/RF/SVM | ANN/RF |
| Darwin | RF | RF | RF | SVM | RF/DT | RF/DT | RF * | RF * | RF * | RF * |
| Hobart | SVM | SVM | SVM | SVM | SVM/RF | ANN | RF | ANN/RF | ANN/RF | ANN/RF |
| Perth | SVM | RF | SVM | RF | ANN/RF/SVM | ANN/RF | ANN | ANN/RF | ANN | ANN/RF |
| Sydney | SVM | SVM | SVM | SVM | ANN/SVM | ANN | ANN/RF | ANN/RF/SVM | ANN/RF | ANN/RF |
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Reza-E-Rabbi, S.; Dodampegama, S.; Bhuiyan, M.A.; Zhang, G.; Atapattu, K. Climate-Sensitive Staged Predictive Framework for Sustainable Residential Retrofit Assessment Using Adaptable Base Model Templates. Sustainability 2026, 18, 7230. https://doi.org/10.3390/su18147230
Reza-E-Rabbi S, Dodampegama S, Bhuiyan MA, Zhang G, Atapattu K. Climate-Sensitive Staged Predictive Framework for Sustainable Residential Retrofit Assessment Using Adaptable Base Model Templates. Sustainability. 2026; 18(14):7230. https://doi.org/10.3390/su18147230
Chicago/Turabian StyleReza-E-Rabbi, Sk., Shanuka Dodampegama, Muhammed A. Bhuiyan, Guomin (Kevin) Zhang, and Kanishka Atapattu. 2026. "Climate-Sensitive Staged Predictive Framework for Sustainable Residential Retrofit Assessment Using Adaptable Base Model Templates" Sustainability 18, no. 14: 7230. https://doi.org/10.3390/su18147230
APA StyleReza-E-Rabbi, S., Dodampegama, S., Bhuiyan, M. A., Zhang, G., & Atapattu, K. (2026). Climate-Sensitive Staged Predictive Framework for Sustainable Residential Retrofit Assessment Using Adaptable Base Model Templates. Sustainability, 18(14), 7230. https://doi.org/10.3390/su18147230

