3.1. Microclimate and EUI
The Urban Weather Generator (UWG) model (from Ladybug Tools 1.6.0) estimates the building EUI at the urban scale, particularly considering the interaction between buildings and the urban environment. Athar Kamal et al. utilized the UWG model in conjunction with data from local meteorological stations to simulate building EUI, achieving more accurate predictions of EUI [
45].
Therefore, this study employs the UWG model to reduce errors in EUI simulations. The meteorological data required for microclimate simulations are sourced from the CSWD meteorological dataset for Xingtai City, available on the Ladybug website. The primary factors influencing the microclimate include transportation power, ratio of green space, and others. The specific details are shown in
Table 8.
To minimize the impact of urban microclimate variations, this study selects two actual samples for each residential block type, totaling six residential block samples for experimentation. The simulation results, as shown in
Figure 4, indicate an approximate 11% increase in average cooling EUI, a 13% decrease in heating EUI, and a 2% overall increase in total EUI. These findings align closely with the results of A. Boccalatte et al., who found that cooling EUI in European cities tends to be approximately 10% higher [
46]. Similarly, Michele Zinzi et al. reported that heating EUI in residential buildings in Rome decreased by up to 21%, while office buildings experienced a reduction of up to 18% [
47]. Therefore, the results of this study are considered to be reasonably reliable.
3.2. Multi-Objective Optimization Simulation
The multi-objective optimization process was completed on a Windows 11 system computer (intel Core i7-12650H, 16 GB memory), with a total time of nearly 500 h, and the optimization objective values converged to a stable state. The population size for each optimization group was 30, with 50 iterations, and parameters such as crossover and mutation rates were kept at the platform’s default values. A total of 4500 operations were performed during this optimization (
Figure 5,
Figure 6 and
Figure 7).
The EUI fluctuated between 45.46 kWh/m
2/y and 54.06 kWh/m
2/y, with a fluctuation range of 13.4%, which is within an acceptable range [
48]. The solar energy received per square meter of roof was 1264–1278 kWh/m
2/y, which is very close to Liu’s results [
49]. On the coldest days, if each window receives more than 2 h of sunlight, it meets the standard, and the tests confirmed this standard was met. The following figure shows the optimization process for the three optimization objectives in three residential blocks, including the Standard Deviation and Mean Value Trendline. Each curve in the Standard Deviation graph represents an iteration, with red indicating the first generation and blue indicating the last generation. A steeper curve indicates a smaller standard deviation within the population, as shown in the figure. When the overall Standard Deviation curve shifts leftward, it suggests that the optimization effect is better. The Mean Value Trendline reflects the change in the average value during the optimization process, with the leftmost point representing the first generation and the rightmost point representing the last generation. As shown, the Mean Value Trendline shifts downward, and during the later iterations, it enters a relatively stable phase, indicating a good overall optimization effect and that the results are credible for further analysis.
3.3. Optimization Process
The entire optimization experiment includes the maximum and minimum values for each target across various blocks. Since the same solution might perform equally well in multiple objectives, there are five process solutions in the multi-story residential blocks, four in the high-rise type I residential blocks, and six in the high-rise type II residential blocks, totaling fifteen process cases.
Table 9 presents the evolution trend of block morphology. It is important to note that while EUI performs best when the minimum value is achieved, SEUP and ASH perform better when their maximum values are reached.
From
Table 9, it can be seen that the lowest EUI for multi-story residential blocks is 46.37 kWh/m
2/y, which is a 10.96% decrease from the maximum EUI of 52.08 kWh/m
2/y. The maximum SEUP is 244.13 kWh/m
2/y, a 44.32% increase compared to the minimum SEUP of 168.46 kWh/m
2/y. The maximum ASH is 8.44 h, which is a 26.61% increase compared to the minimum ASH of 6.94 h. For high-rise type I residential blocks, the lowest EUI is 47.35 kWh/m
2/y, an 11.69% decrease compared to the maximum EUI of 53.62 kWh/m
2/y. The maximum SEUP is 116.75 kWh/m
2/y, a 39.8% increase from the minimum SEUP of 83.51 kWh/m
2/y. The maximum ASH is 7.91 h, a 36.85% increase compared to the minimum ASH of 5.78 h. For high-rise type II residential blocks, the lowest EUI is 45.46 kWh/m
2/y, a 9.96% decrease compared to the maximum EUI of 50.49 kWh/m
2/y. The maximum SEUP is 62.54 kWh/m
2/y, a 16.68% increase compared to the minimum SEUP of 53.60 kWh/m
2/y. The maximum ASH is 7.14 h, a 9.51% increase compared to the minimum ASH of 6.52 h.
In terms of the overall optimization potential of building performance across different residential block types, the results are as follows: multi-story > high-rise type I > high-rise type II. Ratti et al., through research in London, Toulouse, and Berlin, found that the impact of urban morphology on building EUI can reach up to 10% [
50]. This study closely aligns with that trend. Additionally, Liu et al. found that the overall optimization trend for solar radiation potential in Jianhu city could be improved by approximately 30%, which is consistent with this study [
51]. Overall, as the optimization progresses, all targets for each residential block have been optimized, reducing the EUI required for housing while increasing residential comfort.
3.4. Comparison of Pareto and Dominated Solutions
After removing duplicate solutions, the multi-story residential blocks yielded a total of 1125 solutions, with 93 Pareto optimal solutions; the high-rise type I residential blocks yielded a total of 1092 solutions, with 134 Pareto optimal solutions; the high-rise type II residential blocks yielded a total of 929 solutions, with 146 Pareto optimal solutions.
In a multi-criteria setup with conflicting objectives, these objectives cannot all reach an optimal state simultaneously. We typically aim to bring these objectives to their best state within a certain range. This is known as multi-objective optimization, and Pareto optimal solutions are generally regarded as the best solutions that minimize conflicts between all objectives [
52]. The other solutions, excluding Pareto optimal ones, are referred to as dominated solutions. The relationship between Pareto optimal and dominated solutions is illustrated in the following graph (
Figure 8), where the Pareto optimal solutions for multi-story residential blocks are EUI 46.86 kWh/m
2/y, SEUP 208.76 kWh/m
2/y, and ASH 8.14 h; the dominated solutions are EUI 47.08 kWh/m
2/y, SEUP 201.64 kWh/m
2/y, and ASH 7.98 h. For high-rise type I residential blocks, the Pareto optimal solutions are EUI 47.54 kWh/m
2/y, SEUP 100.23 kWh/m
2/y, and ASH 7.16 h; the dominated solutions are EUI 47.89 kWh/m
2/y, SEUP 98.30 kWh/m
2/y, and ASH 6.89 h. For high-rise type II residential blocks, the Pareto optimal solutions are EUI 45.87 kWh/m
2/y, SEUP 58.90 kWh/m
2/y, and ASH 7.01 h; the dominated solutions are EUI 46.29 kWh/m
2/y, SEUP 58.30 kWh/m
2/y, and ASH 6.96 h. Both in terms of solution distribution space and mean values, the Pareto optimal solutions for all three types of residential blocks show better performance than the dominated solutions, with noticeable improvements in all aspects.
Existing research indicates that differences in residential block spatial forms can impact EUI, SEUP, and ASH. By interpreting the residential block forms corresponding to the Pareto optimal solutions, we can conclude that these three energy-efficient, comfortable residential block forms have the following characteristics:
- (1)
BD: Compared to dominated solutions, Pareto optimal solutions have higher BD values, with the optimal BD for multi-story, high-rise type I, and high-rise type II residential blocks corresponding to 0.2914, 0.1628, and 0.1304, respectively. Compared to the dominated solutions with BD values of 0.2851, 0.1592, and 0.1271, these represent increases of 2.23%, 2.23%, and 2.63%, respectively.
- (2)
AF: Compared to dominated solutions, Pareto optimal solutions have lower AF values, with the optimal AF for multi-story, high-rise type I, and high-rise type II residential blocks corresponding to 6.14, 12.78, and 21.68, respectively. Compared to the dominated solutions with AF values of 6.35, 12.99, and 21.90, these represent reductions of 3.37%, 1.64%, and 1.03%, respectively.
- (3)
L/D: Compared to dominated solutions, Pareto optimal solutions have lower L/D values, with the optimal L/D for multi-story, high-rise type I, and high-rise type II residential blocks corresponding to 3.49, 3.06, and 2.49, respectively. Compared to the dominated solutions with L/D values of 3.50, 3.09, and 2.57, these represent reductions of 0.34%, 0.79%, and 3.11%, respectively.
- (4)
BSF: Compared to dominated solutions, Pareto optimal solutions have lower BSF values, with the optimal BSF for multi-story, high-rise type I, and high-rise type II residential blocks corresponding to 0.2157, 0.2032, and 0.1807, respectively. Compared to the dominated solutions with BSF values of 0.2160, 0.2054, and 0.1841, these represent reductions of 0.16%, 1.05%, and 1.83%, respectively.
3.5. K-Means Cluster Analysis
K-means clustering analysis, as a machine learning algorithm, automatically divides data objects into multiple categories or clusters by mining the inherent structure and patterns in the data [
53]. In this paper, this algorithm is used to classify the Pareto optimal solutions of multi-story residential blocks and high-rise type I residential blocks into two categories, while the Pareto optimal solutions of high-rise type II residential blocks are divided into three categories, providing a clearer view of the performance of each Pareto optimal solution in different objectives (
Figure 9).
In
Table 10, the clustering results for the three residential blocks are presented. In the two clusters of multi-story residential blocks, Cluster 1 has fewer Pareto optimal solutions, with better performance in SEUP and ASH objectives, while Cluster 2 shows better performance in the EUI objective. In the two clusters of high-rise type I residential blocks, the distribution of Pareto optimal solutions is relatively balanced, with Cluster 1 showing better performance in EUI, and Cluster 2 showing better performance in SEUP and ASH objectives. High-rise type II residential blocks are divided into three clusters, with a relatively balanced distribution of Pareto optimal solutions in each cluster. Cluster 1 demonstrates superior performance in the EUI objective, Cluster 2 excels in ASH, and Cluster 3 shows better performance in the SEUP objective, demonstrating that this clustering classification is reasonable.
Through the K-means clustering analysis, we aim to address two key issues: first, the relationship among the three optimization objectives; second, how to prioritize the optimization of a specific objective in a multi-objective optimization.
- (1)
The clustering analysis results indicate that EUI is negatively correlated with SEUP and ASH, while SEUP and ASH are positively correlated. Specifically, an outstanding EUI performance is typically accompanied by moderate SEUP and ASH performance, whereas an excellent SEUP performance is usually associated with a strong ASH performance. The differences between the two clustered spatial morphology groups are primarily reflected in variations in FAR, BD, SVF, SD, and BSF, while other spatial morphology parameters do not exhibit consistent trends across different residential blocks.
- (2)
In multi-objective optimization, if the priority is to minimize EUI, this can be achieved by increasing FAR and decreasing BSF. Compared to the clusters with better SEUP and ASH performance, the average FAR in multi-story, high-rise type I, and high-rise type II residential blocks increased by 1.15%, 1.39%, and 1.21%, respectively, while BSF decreased by 0.38, 0.19, and 0.24, respectively. Conversely, if the priority is to optimize SEUP and ASH, this can be accomplished by increasing SVF and decreasing SD. Compared to the clusters with a better EUI performance, the average SVF in multi-story, high-rise type I, and high-rise type II residential blocks increased by 0.4916, 0.9569, and 0.5867, respectively, while SD decreased by 2.26, 0.65, and 4.69, respectively.
Therefore, it can be preliminarily concluded that BSF has a strong correlation with EUI, while SD has a significant impact on SEUP. In the following section, Pearson correlation analysis will be used to assess the relationship between spatial morphology factors and optimization objectives to validate the reliability of this study.
3.6. Correlation Analysis
This section aims to quantitatively explore the impact of residential block spatial morphology on EUI and SEUP. It is important to note that the mechanism through which block morphology influences these two objectives is complex. Therefore, to better understand the relationship between the morphological factors of the block and EUI and SEUP, as well as the correlations between the various influencing factors, Pearson correlation analysis is essential [
54]. When the Pearson correlation coefficient exceeds 0.6, it indicates a significant correlation, and when it exceeds 0.8, the correlation is considered strong (
Figure 10).
Since this paper primarily focuses on building energy efficiency analysis, and ASH is a supplementary optimization indicator, it is sufficient to meet the residential design requirements. Therefore, Pearson and regression analyses are not conducted for ASH. Through a Pearson correlation analysis, the correlation relationships between the spatial morphology of each residential block and the two relevant objectives are as follows in
Table 11:
- (1)
EUI shows a strong correlation with OSR and BSF, both of which are positively correlated with EUI, while FAR is negatively correlated;
- (2)
SEUP shows a strong correlation with multiple spatial morphology factors of residential blocks, including FAR, BD, Fmax, SVF, AF, ED, BER, L/D, and BSF. Specifically, BD, ED, L/D, and BSF are positively correlated with SEUP, whereas FAR, Fmax, SVF, AF, SD, and BER exhibit negative correlations;
Xu et al. conducted research on buildings in Wuhan and found that BSF had the greatest impact on EUI, aligning with the research trend on block morphology [
5]. This may be because lower BSF reduces heat loss and heat gain, thereby improving energy efficiency. In SEUP research, Fmax, BSF, and SVF are critical influencing factors that cannot be ignored [
26]. Additionally, Liu et al., in their study on photovoltaic power generation in Jianhu city, found that FAR and AF are negatively correlated with SEUP, whereas BD is positively correlated, which is consistent with the trend observed in SEUP studies [
49].
These findings indicate that the research trends in this experiment are valid. Furthermore, they suggest that while subsequent zoning may introduce some variations in the study, the influence mechanisms of certain factors remain similar.
3.7. Regression Analysis
Through a Pearson correlation analysis, the factors with the highest correlation under the influence of a single variable were identified. In the subsequent multiple regression analysis, the spatial morphological indicators of residential blocks were treated as independent variables X, while the two optimization objectives, EUI and SEUP, were treated as dependent variables, with the aim to quantify the main morphological factors influencing EUI and residential comfort. A Pearson correlation coefficient greater than 0.6 indicates a significant correlation, and a value above 0.8 signifies a strong correlation (
Table 12).
Three spatial morphological factors of the building block affect EUI, namely SVF, SD, and BSF. Using these as independent variables for regression analysis, we found:
where X
1 = SVF; X
2 = SD; X
3 = BSF.
The R2 value of the model is 0.843, meaning that SVF, SD, and BSF can explain 84.3% of the variation in EUI. All VIF values in the model are less than 5, indicating that there is no collinearity problem, and the model is reliable.
Three spatial morphological factors of the building block affect SEUP, namely BD, SD, and L/D. Using these as independent variables for regression analysis, we found:
where X
1 = BD; X
2 = SD; X
3= L/D.
The R2 value of the model is 0.970, meaning that BD, SD, and L/D can explain 97.0% of the variation in EUI. All VIF values in the model are less than 5, indicating that there is no collinearity problem, and the model is reliable.
- (1)
EUI performs better: SVF, SD, and BSF are positively correlated with EUI. According to the standardized coefficients (Beta), BSF has the greatest impact on EUI, approximately 2.10 times that of SVF and 3 times that of SD. This is likely due to the reduction in heat loss and heat gain, which improves energy efficiency [
12]. Therefore, to obtain a low-EUI residential block, one can reduce the building’s BSF and simultaneously reduce the SVF and SD of the residential block.
- (2)
SEUP performs better: BD and L/D are positively correlated, while SD is negatively correlated. According to the standardized coefficients (Beta), BD has the greatest impact on EUI, approximately 17.38 times that of SD and 3.34 times that of L/D. This is likely achieved through heat conduction, convection, and radiation between the building and outdoor air [
55]. Therefore, to obtain a high-SEUP residential block, one can increase BD while simultaneously reducing the SD of the building and improving L/D.
These results are consistent with the overall trends found in the previous Pareto optimal solutions, K-means clustering analysis, and Pearson correlation analysis, indicating that the experiment has integrity, continuity, and the results are persuasive.
A summary of the above analysis indicates that optimizing all three objectives simultaneously can be achieved by increasing BD while reducing AF, L/D, and BSF. Specifically, increasing BD enhances building density, which helps improve the region’s solar radiation potential, mitigate the urban heat island effect, and increase energy efficiency. Reducing AF can primarily be accomplished by lowering the height of buildings on the southern side, thereby minimizing shading effects and enhancing sunlight exposure and solar radiation potential. Lowering L/D and BSF reduces heat loss, thereby improving energy efficiency and decreasing EUI. Additionally, BSF has a significant impact on EUI, while BD has a greater influence on SEUP.
Additionally, Trepci et al. have confirmed that a higher urban density leads to better energy efficiency [
56]. However, it is important to note that while a higher FAR can contribute to EUI reduction, an excessively large BD increases SEUP. If both factors become too high, they may significantly constrain the residents’ activity space within the residential block. Moreover, research by Quan et al. has identified a threshold effect between FAR and EUI, indicating the necessity of setting limitations for these parameters [
57]. In this optimization, the FAR range is set between 1.31 and 3.15, while BD is maintained between 0.094 and 0.293, ensuring optimization within these boundaries.
3.8. Experimental Verification
To validate the feasibility of the proposed optimization method, this study selected three actual residential blocks in Xingtai City for simulation-based optimization. In addition to enriching the existing theoretical framework, this also helps verify the accuracy of multi-objective optimization. These three residential blocks correspond to a mixed mid-rise and high-rise type I residential block, a high-rise type I residential block, and a high-rise type II residential block (
Table 13).
By applying the above strategies in the optimization process—namely, increasing BD while reducing AF, L/D, and BSF—the final optimized spatial morphology factors are shown in
Table 14. The optimized models were then imported into the Grasshopper platform for building performance simulation.
A comparison between the simulated building performance before and after optimization is presented in
Table 15. It shows that, for the mid-rise residential block, building EUI decreased by 2.65 kWh/m
2/y, a reduction of 5.03%; solar energy utilization potential increased by 9.17 kWh/m
2/y, an improvement of 7.07%; and average sunlight duration increased by 0.12 h, a rise of 2.61%. For the high-rise type I residential block, building EUI decreased by 3.22 kWh/m
2/y, a reduction of 6.27%; solar energy utilization potential increased by 7.89 kWh/m
2/y, an improvement of 10.5%; and average sunlight duration increased by 0.18 h, a rise of 3.3%. For the high-rise type II residential block, building EUI decreased by 1.39 kWh/m
2/y, a reduction of 2.86%; solar energy utilization potential increased by 2.53 kWh/m
2/y, an improvement of 5.16%; and average sunlight duration increased by 0.22 h, a rise of 4.50%.
This validation confirms that the optimization strategies proposed through simulation are feasible. It is hoped that this study can provide insights into the relationship between urban block morphology and building performance.