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Article

Assessing Climate Sensitivity of LEED Credit Performance in U.S. Hotel Buildings: A Hierarchical Regression and Machine Learning Verification Approach

by
Mohsen Goodarzi
1,*,
Ava Nafiseh Goodarzi
2,
Sajjad Naseri
3,
Mojtaba Parsaee
4 and
Tarlan Abazari
5
1
Department of Construction Management and Interior Design, Ball State University, Muncie, IN 47306, USA
2
Global Science’s Climate Science Team, The Nature Conservancy, Arlington, VA 22203, USA
3
Department of Urban Planning, Ball State University, Muncie, IN 47306, USA
4
School of Architecture & Data Science Academic Institute, Mississippi State University, Starkville, MS 39759, USA
5
School of Architecture, Mississippi State University, Starkville, MS 39759, USA
*
Author to whom correspondence should be addressed.
Buildings 2025, 15(23), 4382; https://doi.org/10.3390/buildings15234382
Submission received: 24 October 2025 / Revised: 17 November 2025 / Accepted: 28 November 2025 / Published: 3 December 2025
(This article belongs to the Section Building Energy, Physics, Environment, and Systems)

Abstract

This study examines how climatic factors influence the predictive power of LEED credits in determining certification outcomes for hotel buildings across the United States. Using data from 259 LEED-NC v2009 certified hotels, project-level information was integrated with 30-year climate normals from the PRISM database and Building America climate zones. A three-step hierarchical linear regression was conducted to identify the LEED credits that most strongly predict total certification points while controlling for project size, certification year, and baseline climatic conditions, and to test whether climatic factors moderate these relationships. Regularized Linear Regression (LASSO) was then applied to address multicollinearity and assess model stability, followed by Support Vector Regression (SVR) to capture potential nonlinear relationships. This integrated methodological framework, combining hierarchical regression for interpretability, LASSO for coefficient stability, and Support Vector Regression for nonlinear verification, provides a novel, multi-dimensional assessment of climate-sensitive credit behavior at the individual credit level. Results show that energy- and site-related credits, particularly Optimize Energy Performance (EA1), On-Site Renewable Energy (EA2), Green Power (EA6), and Alternative Transportation (SS4), consistently dominate LEED performance across all climate zones. In contrast, indoor environmental quality credits exhibit modest but significant climate sensitivity: higher mean temperatures reduce the contribution of Increased Ventilation (EQ2) while slightly enhancing Outdoor Air Delivery Monitoring (EQ1). Cross-model consistency confirms the robustness of these findings. The findings highlight the need for climate-responsive benchmarking of indoor environmental quality credits to improve regional equity and advance the next generation of climate-adaptive LEED standards.

1. Introduction

The Leadership in Energy and Environmental Design (LEED) rating system, developed by the U.S. Green Building Council (USGBC), is one of the most widely adopted frameworks for certifying sustainable buildings worldwide. As of 2025, LEED has been implemented in more than 180 countries with over 190,000 registered projects, spanning diverse climatic and economic contexts [1].
The LEED rating system has undergone several iterations to address evolving sustainability challenges and incorporate new technologies and practices. The most recent update, LEED v4.1, introduced in 2024, focused on raising thresholds for energy performance and greenhouse gas emissions reductions [1]. This update required newly registered projects to demonstrate a 15% improvement over the ASHRAE 90.1-2010 baseline, higher than the previous 5% requirement. Additionally, the update implemented a dual metric structure, tying points to both greenhouse gas emissions performance and source energy/energy cost metrics [1].
While LEED has made substantial progress in promoting sustainable building practices, research has identified several areas for improvement. Studies have shown that the relationship between achieved scores, LEED categories, and certification levels can vary significantly [2]. Analysis of LEED v4.1 healthcare certification data revealed that categories like Energy and Atmosphere (EA) and Water Efficiency (WE) have a stronger correlation with overall scores compared to Materials and Resources (MR) and Indoor Environmental Quality (EQ) [2].
The hospitality industry has increasingly recognized the importance of sustainable practices in recent years, and a growing body of research has focused on understanding the most efficient sustainable practices in this industry and their effects on the performance and guest ratings (e.g., [3,4,5,6]). LEED certification for hotels presents unique challenges and opportunities due to their specific features, such as on-site amenities, food and beverage operations, pool and laundry facilities, convention spaces, frequent renovation cycles, and transient guest populations. While the LEED rating system has been widely adopted in the hospitality sector, there is a notable research gap regarding the influence of climatic factors on the predictive power of LEED credits in determining overall LEED scores for hotel projects. Climate plays a crucial role in building performance and energy efficiency, yet its impact on LEED scoring patterns across different geographical regions remains understudied. The current LEED system applies uniform standards across diverse geographical areas, potentially overlooking the unique challenges and opportunities presented by varying climate conditions. This gap is particularly relevant given the growing recognition of climate change’s impact on building performance and the need for more localized, climate-responsive, sustainable design strategies.
The present study addresses this research gap by investigating the role of climatic factors in influencing the predictive power of LEED credits in determining overall LEED scores across hotel projects. By integrating climate data with LEED certification information, this research aims to provide valuable insights into how the effectiveness of specific LEED credits may vary across different climate zones. The focus on the hotel sector is particularly relevant, as hospitality buildings often have unique energy and resource consumption patterns that may be more sensitive to climatic variations. Understanding the interaction between climatic factors and LEED credits is crucial for several reasons. First, it can help refine the LEED rating system to better account for regional climate differences, potentially leading to more accurate and fair assessments of building sustainability. Second, this knowledge can guide architects, engineers, and developers in selecting the most effective sustainable design strategies for specific climate zones, optimizing both environmental performance and LEED scoring potential. Finally, policymakers can use these insights to develop more nuanced green building policies that consider local climatic conditions.

2. Literature Review

Research has investigated how individual LEED credits and credit categories contribute to overall scores and certification pathways, providing important context but only partially addressing credit-level climate sensitivity, particularly in hotels. Jun and Cheng [7] focused on selecting the right LEED credits for building projects by using data mining techniques. Their analysis, based on 912 LEED-EB projects and their surrounding climatic conditions, applied 55 classification models to 47 LEED-EB credits using Random Forests, AdaBoost Decision Tree, and Support Vector Machine (SVM). The study optimized these models and developed a web-based decision support system that helps LEED credit selection based on climatic factors. However, their work does not quantify how local climate conditions modify the predictive power of specific credits for certification outcomes or examine hotel projects as a distinct building type. In contrast, the present study employs LASSO and Support Vector Regression as the primary machine-learning methods for verification, focusing on regularized linear and kernel-based approaches that are well-suited to moderate sample sizes and continuous outcomes.
Several studies have analyzed the relative importance of LEED credit categories in shaping overall certification outcomes (e.g., [8,9]). Pushkar and Verbitsky [10] investigated LEED-NC V3 certifications, identifying four primary categories with the most significant contributions to sustainability scores: Sustainable Sites, Energy and Atmosphere, Indoor Environmental Quality, and Innovation in Design. Similarly, Wu et al. [11] found Sustainable Sites, Water Efficiency, and Indoor Environmental Quality to be the most influential credit categories in LEED 2009 projects, while noting that Materials and Resources credits were less frequently achieved due to their complexity.
The prominence of the Energy and Atmosphere category in determining overall LEED-NC v4 sustainability scores was further emphasized by Goodarzi et al. [12], who identified Materials and Resources and Indoor Environmental Quality as the next most influential categories. Their findings indicated that, despite its expected significance, Water Efficiency credits had minimal influence on achieving overall LEED scores, a trend also observed in studies on LEED-certified university residence halls [13] and multifamily residential buildings [14] under LEED NC v2009. Li et al. [15] further highlighted that Sustainable Sites and Indoor Environmental Quality were among the most accessible credits in LEED-NC V3 projects, reflecting their broad applicability in green building practices.
Beyond credit selection, practical challenges in implementing LEED recommendations have been noted. Krueger et al. [16] found that, despite green building rating systems advocating the use of alternative materials, their adoption remains limited due to the complexity and uncertainty associated with their impacts and the challenges in interpreting sustainability guidelines. These findings collectively underscore the need for data-driven decision support tools and refinements in LEED credit structures to enhance the effectiveness and practical applicability of sustainability certification frameworks.

2.1. Climate-Responsive Certification Frameworks

Research challenges LEED’s assumption of universal credit applicability through climate-specific performance analyses. Researchers have explored ways to customize green building assessment tools for different climates. Sadeghi et al. [17] presented a framework to customize green building assessment tools for regions with diverse climates using K-means clustering and fuzzy AHP. The methodology involved collecting climatic data, clustering regions based on these data, and incorporating expert judgments to adjust the assessment criteria. The study identified four distinct climatic zones in Iran and customized the LEED EB 2009 tool accordingly. Their findings showed that sustainability priorities vary significantly across different climates, with water efficiency and energy efficiency being the most critical categories.
Zhao et al. [18] analyzed factors influencing LEED building markets in U.S. East Coast cities by a comparative analysis of three commonly used machine learning algorithms: Linear Regression, Locally Weighted Regression, and Support Vector Regression (SVR) to investigate the factors affecting LEED constructions in cities around the East Coast of the United States. They discovered that economic conditions, urbanization levels, and energy policies have an impact on LEED adoption in these areas. According to their research, local market factors impact green building construction. The study emphasizes the need to address regional, economic, urban, and climate problems while adopting LEED standards that incorporate these ideas.
Benites et al. [19] explored how LEED-ND and climate tools could support environmentally friendly communities in São Paulo, Brazil. They emphasized how sustainable urban planning and municipal policy may collaborate to lower emissions to support sustainable development. Among LEED credits, energy and water credits exhibit particularly strong climate dependencies. Reference [20] studied the relationship between LEED points for energy efficiency, water efficiency, and climate impacts. Their study’s findings indicated significant variability in the climate impact of LEED energy and Water Efficiency credits, with emissions reductions varying by multiple orders of magnitude even within similar building contexts. The authors argued that LEED’s current framework lacks a strong connection between credits and real-world sustainability outcomes, suggesting that future iterations should integrate regional energy grids, water infrastructure, and supply chains to enhance the effectiveness of sustainability measures.
These studies demonstrate that sustainability priorities and environmental impacts of LEED credits can vary substantially across climates, especially for energy- and water-related measures. However, they do not examine whether and how climate alters the predictive strength of individual credits for overall LEED scores, nor do they focus on lodging projects, leaving credit-level climate sensitivity in hotel certifications unaddressed.

2.2. Hotel-Specific LEED Certified Project Performance

The hospitality sector’s unique operational profile, characterized by full-time occupancy, high occupant density, and intensive laundry, kitchen, and HVAC operations, creates distinct credit interaction dynamics. Recent studies have investigated the financial impact of LEED certification on hotel performance, yielding mixed results. Reference [21] found that LEED-certified hotels outperformed their non-certified counterparts in terms of financial performance. Similarly, a study by [6] examined 93 LEED-certified hotels and 514 comparable competitors, finding that certified hotels obtained superior financial performance for at least the first two years after certification. However, contrasting results were reported by [22], who found that LEED-labeled hotels experienced higher average daily rates but lower occupancy rates, resulting in a statistically insignificant difference in revenue per available room.
Bianco et al. [3] investigated the impact of sustainability certifications on the financial performance and competitive positioning of hotels. Using panel data from 251 certified hotels in Florida over ten years, the authors applied a random effects model to examine how sustainability certification affects key performance indicators such as occupancy rates, average daily rates, and revenue per available room compared to competitors in their competitive set. Their findings showed that certified hotels generally outperformed their competitors in all categories but for occupancy rates.
One aspect of sustainability that has been a focus in the hospitality industry is energy efficiency. A study by Clay et al. [23] evaluated the causal impact of LEED certification on energy consumption in federally owned buildings that were retrofitted between 1990 and 2019. Using a difference-in-differences propensity score matching approach, the authors compared LEED-certified buildings with similar non-certified federal buildings to determine if certification results in actual energy savings. The study findings indicated that, on average, LEED certification did not lead to statistically significant energy savings. However, LEED buildings with higher energy scores demonstrated greater post-certification energy efficiency, with a 12.6% reduction in energy use for all buildings and 13.9% for office buildings. The study suggested that trade-offs in LEED point allocation, behavioral changes post-certification, and overall improvements in federal building efficiency may explain the lack of average energy savings, highlighting the importance of refining LEED criteria to ensure that certification translates into meaningful energy reductions.
Despite this growing body of research, existing studies of LEED performance in hotels primarily evaluate certification outcomes at the aggregated category or project level and do not examine how climatic factors alter the relative contribution of individual credits. Prior work identifies which credits are commonly achieved or associated with stronger energy or financial outcomes, but it does not assess whether the predictive value of specific credits changes across climate zones or due to temperature- and precipitation-driven load profiles. This lack of credit-level, climate-sensitive analysis is particularly consequential for hotels, whose energy, ventilation, and water demands are tightly coupled with outdoor environmental conditions. As a result, the extent to which climate moderates the effectiveness or scoring weight of particular LEED strategies in hotels remains largely unknown.
Hotels present distinct operational and environmental characteristics that make them particularly sensitive to climate–design interactions in ways not captured by broader commercial-building studies. Unlike typical office or institutional buildings, hotels operate on a 24/7 occupancy cycle with high internal loads from kitchens, laundry, pools, spas, and plug-intensive guest rooms. These loads amplify the climate dependence of energy- and water-related processes, creating stronger expected interactions with credits such as Optimize Energy Performance (EA1), Water Efficient Landscaping (WE1), and Water Use Reduction (WE3). Hotels also rely heavily on ventilation and comfort-driven HVAC operation due to frequent guest turnover and stringent indoor air quality expectations, making Increased Ventilation (EQ2), Outdoor Air Delivery Monitoring (EQ1), Controllability of Systems (EQ6), and Thermal Comfort (EQ7) more sensitive to outdoor temperature and humidity than in other building types. Additionally, latent-load dominance in humid climates and seasonal tourism patterns further heighten the potential for climate to modulate the performance and feasibility of specific credits. These sector-specific mechanisms provide a strong justification for focusing on hotels as a distinct context in which to examine credit-level climate sensitivity.
These sector-specific characteristics underscore the need for a methodological approach capable of distinguishing structural, climate-invariant credit effects from those that may shift under nonlinear or regionally moderated conditions.

2.3. Research Gaps and Study Purpose

Although existing research highlights geographic variability in LEED achievement patterns and identifies differences in credit attainment across building types, no studies to date have directly evaluated climate sensitivity at the credit level. Current scholarship typically aggregates sustainability performance into category-level scores or total certification outcomes, which masks whether and to what degree specific credits become more or less predictive under different climatic conditions. This is a critical omission for hotel buildings, whose operational energy, ventilation, and water-use profiles are among the most climate-dependent in the commercial sector. Accordingly, the literature has not yet established how individual LEED credits respond to climatic variation or whether credit importance shifts systematically across climate zones. As a result, there is a clear gap regarding credit-level climate sensitivity in hotel projects, whether and how climatic factors moderate the predictive power of individual credits for total LEED scores.
Because these climate–operation couplings are uniquely pronounced in hotels relative to other commercial building types, this sector provides a particularly sensitive and theoretically motivated testbed for detecting whether, and how, the predictive contribution of individual credits shifts across climatic conditions.
By demonstrating how Building America climate zones moderate the efficacy of specific credits in hotel projects, this research provides both theoretical advancement and practical methodology for climate-responsive certification systems. The results directly inform USGBC’s ongoing efforts to reduce outcome variability through regionally tailored criteria while offering architects evidence-based strategies for climate-optimized credit selection.
This study’s novel integration of climate normal data with project certification records enables direct analysis of environmental context during the design phase, when credit selection decisions occur. The analysis reveals fundamental limitations in the current LEED credit structures’ ability to address climate-specific sustainability challenges. These disparities highlight the need for dynamic credit weighting systems responsive to regional climate stressors.
This study bridges these gaps through a climate-credit interaction framework analyzing 259 LEED-certified hotels across all U.S. climate zones. By integrating PRISM climate data with USGBC project records, the research advances LEED optimization theory in three key dimensions:
  • Identifying and ranking the significant contributor credits in predicting LEED certification of hotel projects.
  • Evaluating and quantifying the moderation effects of climate factors on the predictive power of LEED credits.
  • Disaggregating temperature versus precipitation impacts on LEED credit performance, which can help establish climate-weighted credit prioritization models for hotel projects.
The findings challenge the universal applicability of current LEED credit weightings while providing empirical evidence for context-sensitive certification frameworks. This theoretical advancement aligns with USGBC’s stated goal of “enhancing regional applicability” in future LEED versions but provides the first systematic methodology for implementing climate-responsive credit evaluations at scale. By directly modeling credit-level interactions with temperature and precipitation, the present study addresses this unresolved gap and provides the first empirical evidence of how climatic factors shape the predictive role of individual LEED credits in hotel projects.
Addressing this gap required an analytical framework capable of capturing complementary dimensions of credit–climate behavior that no single method could provide. Hierarchical regression was needed to decompose variance attributable to project controls, credit main effects, and climate interactions in a transparent, theory-driven manner. However, hierarchical models alone cannot assess coefficient stability under correlated predictors or determine whether observed relationships persist after penalizing overfitting. LASSO regularization, therefore, served to evaluate variable importance under shrinkage constraints, revealing whether the dominance of certain credits (e.g., EA1 and SS4) remained robust when weaker or collinear predictors were penalized. Finally, Support Vector Regression enabled the detection of nonlinear associations that linear models cannot capture, testing whether climate–credit relationships intensify, plateau, or invert outside linear ranges. Together, this multi-method design provides a richer analytical lens than any individual technique and represents a novel contribution to credit-level sustainability assessment by integrating interpretability, stability, and nonlinearity into a unified climate-sensitivity framework.

3. Materials and Methods

3.1. Data Collection

This study utilized a structured data collection and analysis approach to evaluate the effect of climatic factors on the predictive power of individual LEED credits that have a significant contribution to the certification level and the overall LEED score in LEED NC v2009. In order to provide accurate and generalizable results, the study solely focuses on a specific project type, lodging, which has shown a very high trend toward achieving sustainability goals within the entire sector. Therefore, the overall LEED scores and the scores achieved for each credit were collected from the United States Green Building Council’s (USGBC) LEED Project Directory for 312 projects, which includes all certified hotels under this LEED version.
Climate data for all projects were collected based on the corresponding ZIP codes of each project location. The primary source of climate information was the PRISM Climate Group, which integrates data from an extensive network of monitoring stations, applies rigorous quality control protocols, and produces high-resolution spatial climate datasets to facilitate the analysis of both short- and long-term climatic patterns. Two key variables were extracted: mean annual temperature (Temp-M) in degrees Celsius and mean annual precipitation in millimeters. For both variables, 30-year climatological normals (1990–2020) were utilized. Thirty-year normals represent the standard baseline period recommended by the World Meteorological Organization and NOAA for characterizing long-term climate patterns, as they minimize interannual variability and provide a statistically stable reference for regional comparison [24]. The use of 30-year normals is widely adopted in climate-sensitive building-performance research because it more accurately represents the environmental context affecting design conditions and long-term energy behavior (e.g., [25,26]). In addition, each project location was assigned a climate zone classification based on the U.S. Department of Energy’s (DOE) Building America Climate Zones. This classification system comprises eight zones, ranging from hot–humid to very cold climates. A summary of the climate zones and their corresponding codes is provided in Table 1.

3.2. Data Preparation

Among the total of 312 projects certified by 1 February 2025, 278 projects had complete information. To ensure the integrity of the statistical results and mitigate potential biases, an outlier detection and removal procedure was implemented. Standardized residuals were first employed as an initial diagnostic tool for identifying potential outliers, with observations exceeding an absolute value of 3 (i.e., standardized residuals > 3 or <−3) flagged for further scrutiny [27].
To further refine the dataset and assess the influence of individual observations on the overall model, Cook’s Distance was applied as a secondary criterion for detecting influential outliers. A commonly used conventional cut-off for Cook’s Distance is 4/(N-k-1), where N is the total number of observations and K is the number of predictors [28]. This heuristic originates from classical regression influence diagnostics proposed by Belsley, Kuh, and Welsch [29], who note that observations with Cook’s D values several times above the average, or exceeding this proportional threshold, should be examined for disproportionate influence on model estimates. Therefore, a threshold of 0.016 (4/(278-32-1)) was calculated for Cook’s Distance. This data preparation resulted in the removal of 19 projects and the retention of a total of 259 projects in the dataset.

3.3. Study Variable Types and Use

In LEED NC v2009, there are a total of 48 credits and sub-credits, including 32 credits, some of which have sub-credits. Since many individual sub-credits could be achieved and all the sub-credits under a credit share a common goal of achieving that credit, this study considered each LEED credit as one feature (including all its sub-credits) to reduce the unnecessary complexity of the data analysis and evaluate all credits with the same level of detail, thus providing more reliable and accurate results. For example, Sustainable Site Credit 4 (SS4) consists of SS4.1, SS4.2, SS4.3, and SS4.4. Table 2 summarizes the credits that are used as features in this study.

3.4. Selection of Climate-Relevant Credits for Analysis

The selection of climate-relevant credits was guided by established building-science principles and empirical evidence demonstrating how temperature, humidity, solar radiation, and precipitation influence building performance. Credits were included only if (i) their achievement affects or is affected by climate-driven physical or operational loads, and (ii) there exists a plausible mechanistic pathway linking credit performance to climatic conditions.

3.4.1. Site and Ecological Performance (SS1–SS7)

Climate influences site exposure, hazard mitigation, vegetation establishment, stormwater runoff magnitude, and heat island conditions. Research shows that stormwater BMP effectiveness and vegetation survival vary significantly with precipitation intensity and evapotranspiration patterns, while temperature and solar radiation alter surface heat exchange and cooling potential. Credits involving habitat restoration (SS5), stormwater design (SS6), and heat island mitigation (SS7) are therefore directly climate dependent.

3.4.2. Water Efficiency (WE1, WE3)

Irrigation loads and indoor water baselines are strongly shaped by precipitation deficits, temperature, and humidity. Higher temperatures increase evapotranspiration and irrigation demand, while climate-driven cooling/humidification loads affect domestic hot water (DHW) use. These mechanisms make Water Efficient Landscaping (WE1) and Water Use Reduction (WE3) climate responsive.

3.4.3. Energy and Atmosphere (EA1, EA2, EA6)

Heating and cooling loads—which dominate hotel energy use—are fundamentally driven by outdoor temperature and humidity profiles. Optimize Energy Performance (EA1) directly reflects these loads through simulation baselines. On-Site Renewable Energy (EA2) depends on solar insolation and temperature effects on photovoltaic efficiency. Green Power (EA6) exhibits regional variability in carbon intensity due to climate-driven renewable resource availability. Together, these credits have well-documented climate dependencies.

3.4.4. Indoor Environmental Quality (EQ1, EQ2, EQ6, EQ7, EQ8)

Ventilation loads vary with outdoor temperature and humidity, increasing conditioning energy requirements for EQ1 and EQ2. Thermal comfort (EQ7) and controllability (EQ6) are sensitive to outdoor conditions and seasonal temperature gradients. Daylight availability (EQ8) depends on solar geometry and cloud cover. For hotels, where ventilation, comfort, and occupancy expectations are stringent, these climate interactions are amplified.

3.4.5. Exclusions

Credits in the Materials and Resources (MR) and Innovation and Design (ID) categories were excluded because they are procurement-based or process-based rather than performance-based, lacking direct physical or operational mechanisms linking them to climatic conditions. Including credits without plausible climate sensitivity would introduce noise and obscure genuine climate–credit interaction effects.
The resulting credit set represents those with direct, theoretically supported pathways through which climate modifies feasibility, resource demand, environmental performance, or operational loads. Table 3 summarizes these credits and the rationale for their climate relevance.

3.5. Inclusion of Control Variables

Certification year and project size were included as control variables to account for differences in baseline efficiency standards and design scale. Certification year captures temporal improvements in LEED adoption, code stringency, and technology efficiency over time, while gross square footage adjusts for scale effects, since larger projects typically achieve energy and water performance credits differently due to economies of scale and system diversity. Controlling these variables helps isolate the specific influence of climatic factors on credit achievement.

3.6. Data Analysis

The analytical framework was designed to capture complementary dimensions of credit–climate behavior that no single method could adequately represent. Hierarchical regression provided a transparent, theory-driven structure for quantifying the incremental variance explained by project controls, LEED credit main effects, and climate interactions. However, because hierarchical models cannot evaluate coefficient stability under correlated predictors or determine whether dominant credits remain influential when weaker variables are penalized, a Regularized Linear Regression using LASSO was employed to assess robustness under shrinkage constraints and to identify a stable subset of influential predictors. To further test whether the observed relationships were inherently linear or whether climate–credit effects intensified or plateaued under nonlinear conditions, a Support Vector Regression model with a Gaussian kernel was implemented. Together, these methods form an integrated analytical pipeline that balances interpretability, stability, and nonlinearity, enabling a more comprehensive examination of climate-sensitive LEED credit performance than any single technique alone.

3.6.1. Stage 1: Descriptive Analysis

Descriptive statistics and frequency distributions were first generated to summarize the number of LEED-certified hotel projects in each of the eight Building America (BA) climate zones. A geographical visualization map was produced to illustrate the spatial distribution of the studied projects across the United States.
Prior to model estimation, continuous predictors were rescaled to improve numerical stability, facilitate interpretation, and make coefficient magnitudes comparable across variables. All LEED credit scores and the two climatic variables (mean annual temperature and mean annual precipitation) were standardized using z-scores (subtracting the sample mean and dividing by the standard deviation). Gross square footage was natural-log transformed to reduce right skewness and approximate linearity with the outcome, and certification year was mean-centered to reduce non-essential multicollinearity when specifying interaction terms. These transformations are consistent with best practices for regression models with interaction terms and multi-scale predictors, and they improve interpretability in both ordinary least squares and regularized estimation frameworks [30,31].

3.6.2. Stage 2: Hierarchical Linear Regression

To identify the LEED credits that most strongly predict total certification points while accounting for climatic moderation, a three-step hierarchical linear regression was performed. In this model, the overall LEED score served as the dependent variable, and the individual climate-relevant credits (Table 3) were treated as predictors.
  • Model 1 (M1) included the scaled control variables (log-transformed gross square footage and mean-centered certification year) to account for differences in scale and temporal improvement in LEED adoption. Mean annual temperature and mean annual precipitation were also entered in this block to establish a baseline climatic context.
  • Model 2 (M2) added the selected climate-relevant LEED credits to evaluate their main effects on total certification points.
  • Model 3 (M3) introduced theoretically supported interaction terms between the climatic variables and selected credits to test for moderation effects.
This sequential modeling enabled the assessment of incremental explanatory power (ΔR2) and clarified whether climatic factors strengthened or weakened the influence of specific credits after controlling for project age and size. Hierarchical regression was selected because it enables theory-driven block entry of variables and permits explicit partitioning of variance attributable to control variables, main effects, and interaction terms. This approach is widely used in environmental performance and building-science research for assessing moderation effects and isolating contextual influences such as climate and urban form (e.g., [32,33,34]).

3.6.3. Stage 3: Regularized Linear Regression (LASSO)

To evaluate model stability and address potential multicollinearity among predictors, a Least Absolute Shrinkage and Selection Operator (LASSO) regression was performed using k-fold cross-validation. Regularization penalizes overly complex models by shrinking weak coefficients toward zero, thus improving generalization and reducing overfitting, an advantage noted in recent data-driven analyses of LEED and other sustainability datasets [7]. The LASSO results were compared to the hierarchical regression outcomes to confirm the consistency of variable importance and coefficient direction. The data was partitioned into training, validation, and test subsets. The reported RMSE, MAE, and R2 values therefore represent an out-of-sample prediction performance rather than an in-sample fit.
Model hyperparameters were tuned using k-fold cross-validation. The L1 penalty parameter (λ) was chosen such that it minimized the mean squared error on a held-out validation subset, resulting in an optimal value of λ = 0.002 under the train/validation/test split. Feature importance for the LASSO model was quantified using a permutation-based “mean dropout loss” procedure, in which each predictor was randomly permuted 50 times and the resulting increase in root mean squared error was averaged. Predictors that produce larger increases in error when permuted are interpreted as more influential in predicting total LEED points.

3.6.4. Stage 4: Support Vector Regression (SVR)

Finally, to capture potential nonlinear relationships between LEED credit achievements and climatic variables, a Support Vector Regression model with a Gaussian (RBF) kernel was implemented. SVR can model nonlinear boundaries by maximizing the margin of tolerance around the regression function, offering high predictive accuracy even in moderately sized datasets [18]. Applying SVR alongside linear models allowed for testing whether the observed relationships remained stable under nonlinear functional assumptions.
The cross-model design, combining hierarchical regression for interpretability, LASSO for robustness, and SVR for nonlinear validation, provided a comprehensive analytical framework for evaluating the influence of climatic factors on LEED credit performance. Figure 1 summarizes the complete analytical workflow adopted in this study.
The SVR model used the same train/validation/test partitioning as the LASSO analysis, and the violation cost parameter C was selected by minimizing validation mean squared error. Feature importance was evaluated using the same permutation-based mean dropout loss metric described above, enabling direct comparison with the LASSO results.
In both the LASSO and SVR models, feature importance was evaluated using a permutation-based “mean dropout loss” metric. For each predictor, its values were randomly permuted 50 times while all other predictors were held fixed, and the resulting increase in root mean squared error was averaged. Larger mean dropout loss, therefore, indicates that permuting a given predictor degrades predictive accuracy more strongly, and hence that the predictor is more influential in explaining variation in total LEED points. For the SVR model, the violation cost parameter C controls the trade-off between model complexity and tolerance for prediction errors: lower values of C yield smoother functions with more regularization, whereas higher values of C allow the model to fit the training data more closely.

4. Results

4.1. BA Climate Regions of Projects

After preparing the data, the dataset consisted of 259 projects across the United States. Table 4 presents the number of projects in each of the eight climate regions. The highest number of projects is in the mixed humid climate zone, accounting for 37.1 percent of the total (N = 96). The second climate zone, having a high number of projects, is the cold climate, accounting for 22.4 percent of the total studied projects (N = 58). Hot–humid climate is the third climate, including the certified projects accounting for 17.8 percent of the total (N = 46). The marine and hot–dry regions contribute 12.0% and 9.3% of certified projects, respectively. Very few projects are in the very cold region (0.8%), while no projects were recorded in the subarctic or mixed–dry regions. This distribution suggests that LEED certification is more prevalent in temperate and humid climates, likely due to the concentration of urban developments and greater emphasis on sustainability measures in these regions. Figure 2 visualizes the distribution of the studied projects across the United States.

4.2. Hierarchical Linear Regression

A three-step hierarchical regression analysis was conducted to evaluate the effects of project size, certification year, and climatic conditions on total LEED points, and to assess the incremental predictive contribution of climate-relevant credits and their interactions. The model summary statistics are presented in Table 5, and the corresponding ANOVA results are reported in Table 6.
The first model (M1), which included the control variables, log-transformed gross square footage, mean-centered certification year, mean annual temperature, and mean annual precipitation, explained 11.8% of the variance in total LEED points (R2 = 0.118, p < 0.001). Within this model, gross square footage was a significant positive predictor (β = 0.19, p = 0.002), indicating that larger projects tended to achieve higher certification scores, whereas certification year and climatic means were not significant predictors.
Adding the climate-relevant credits in M2 substantially improved the model’s explanatory power (ΔR2 = 0.689, p < 0.001), yielding R2 = 0.807 and adjusted R2 = 0.790. As shown in Table 7, several credits demonstrated strong and statistically significant positive associations with total LEED points. The most influential were Optimize Energy Performance EA1 (β = 0.541, p < 0.001), SS4 (β = 0.278, p < 0.001), and EA2 (β = 0.196, p < 0.001). Additional contributions came from EA6, WE3, and SS7, all of which were significant at p < 0.001. Collinearity diagnostics (VIF < 1.5) confirmed the absence of multicollinearity among predictors.
The inclusion of interaction terms between climatic variables and credit scores in M3 further improved the model fit (R2 = 0.823, adjusted R2 = 0.789), representing a small but statistically meaningful increase in explained variance (ΔR2 = 0.016, p < 0.05). Although most interaction effects were not significant, two stood out. A significant negative interaction was found between mean annual temperature and EQ2 (β = –0.388, p = 0.002), suggesting that higher outdoor temperatures reduced the contribution of ventilation-related performance to overall certification outcomes. In contrast, a marginally positive interaction between mean annual temperature and EQ1 (β = 0.226, p = 0.065) indicated slightly greater benefits of this credit under warmer conditions.
It is important to note that Model 3 exhibits very large VIF values for several interaction terms (Table 7). This inflation is expected and arises because interaction terms (e.g., Tmean × EQ2) are mathematically constructed from the product of two predictors, producing near-linear dependencies between interaction terms and their constituent main effects. Even when predictors are standardized and exhibit low pairwise correlations (Section 4.3), the algebraic structure of interaction terms yields inherently high VIF values. This phenomenon is well documented in the regression-methodology literature and does not necessarily indicate problematic multicollinearity in the underlying data, but rather a statistical artifact of including multiple climate–credit interactions simultaneously. Consequently, the sign, magnitude, and significance of interaction coefficients in M3 should be interpreted with caution, and the climate-moderation effects reported here are best viewed in conjunction with the stability results from LASSO and the nonlinear validation from SVR.

4.3. Linear Regression Assumption Checks

The Durbin–Watson statistics for all hierarchical models (1.95–2.03) indicated no meaningful autocorrelation in the residuals. Prior to estimation, we examined the Pearson correlation matrix of all predictors; no pairwise correlation exceeded |r| = 0.70, suggesting that bivariate multicollinearity was limited. In addition, we computed variance inflation factors (VIFs) for Model 2, where all main-effect predictors were entered simultaneously. All VIF values were below 1.5, well under conservative thresholds commonly used in the literature, indicating that multicollinearity was not a concern [35]. The standardization of LEED credits and climatic variables, along with mean-centering of certification year, further reduced non-essential multicollinearity when interaction terms were introduced in Model 3. Visual inspection of residual-versus-fitted plots and Q–Q plots of standardized residuals (Figure 3a,b) confirmed that the assumptions of linearity, homoscedasticity, and approximate normality were reasonably satisfied.
The extremely large VIF values observed only in M3 arise from the presence of multiple standardized interaction terms and do not reflect multicollinearity among the original predictors; this is consistent with established statistical guidance that interaction models naturally inflate VIF even when main-effect predictors are well behaved.
Overall, the hierarchical regression results suggest that, after controlling for project certification year, size, and baseline climate, energy and site-related credits are the most powerful predictors of total LEED performance, while indoor environmental quality credits exhibit modest climate sensitivity.

4.4. Regularized Linear Regression (LASSO)

To examine model stability and mitigate potential overfitting, a Regularized Linear Regression using the LASSO penalty was conducted. Model fit and performance metrics are summarized in Table 8 and Table 9.
The optimal penalty parameter (λ = 0.002) yielded a parsimonious model with strong predictive accuracy (R2 = 0.796, RMSE = 0.452, MAE = 0.368).
The relative feature importance derived from mean dropout loss confirmed EA1 as the most influential predictor (mean dropout = 0.884), followed by SS4, EA6, SS2, and EA2. In this context, mean dropout loss refers to a permutation-based feature importance metric in which the values of a given predictor are randomly shuffled while all other predictors remain unchanged; the resulting decrease in model performance is quantified as the average increase in RMSE over 50 permutations. Larger mean dropout loss values, therefore, indicate that removing the true information content of that predictor degrades the model’s predictive accuracy more strongly. The regularized coefficients closely mirrored the standardized coefficients in the hierarchical model, with consistently positive and significant weights for energy and site-related variables (Table 10). These importance values are derived from the permutation-based mean dropout loss described in Section 3.6.3 and thus provide a robust ranking of predictors that is directly comparable to the SVR results.
The similarity between validation and test MSE values (0.303 vs. 0.204; Table 8) suggests that the LASSO model generalizes reasonably well to unseen data and does not exhibit substantial overfitting.
Beyond serving as a robustness check, the LASSO model also provides insight into the structural redundancy among credits. The shrinkage path indicates that only a small subset of predictors, primarily EA1, SS4, EA6, SS2, and EA2, retain nonzero coefficients across a wide range of penalty values. This pattern suggests that much of the explanatory power attributed to other credits in linear models is absorbed by these dominant predictors under regularization, reflecting underlying conceptual overlap among credits that target similar operational or load-driven mechanisms. The fact that these same credits remain after shrinkage indicates that their contribution is not sensitive to correlated predictors or model specification, reinforcing their role as central determinants of LEED performance.

4.5. Support Vector Regression

A nonlinear Support Vector Regression (SVR) model with a Gaussian kernel was used to further test model robustness and capture potential nonlinearities in credit–climate relationships. As shown in Table 11 and Table 12, the SVR achieved the best predictive performance among all models (R2 = 0.835, RMSE = 0.431, MAE = 0.338), with low validation and test MSE values (0.192 and 0.186, respectively), suggesting minimal overfitting.
The feature importance ranking (Table 13) again placed EA1, EA6, and SS4 as the three most influential predictors, followed by SS2, EA2, and EQ1, in agreement with both the hierarchical and LASSO models. The stability of these rankings across modeling techniques underscores the robustness of the identified drivers of certification performance. Likewise, the small gap between validation and test MSE for the SVR model (0.192 vs. 0.186; Table 11) indicates stable generalization performance and limited overfitting.
Because the same permutation-based mean dropout loss metric is used for SVR and LASSO, the feature importance rankings in Table 10 and Table 13 can be directly compared across models.
The SVR results also offer substantive interpretive value beyond validation. Because the Gaussian kernel allows nonlinear responses, credits that exhibit diminishing returns, threshold effects, or nonlinear climate interactions would be expected to shift in rank or gain importance relative to the linear models. However, SVR identifies the same core set of predictors—EA1, SS4, EA6, SS2, and EA2—as the largest contributors to predictive accuracy. This alignment suggests that the functional relationship between these credits and total LEED points is largely monotonic and stable across climatic conditions. Moreover, the similarity in importance rankings across linear, regularized, and nonlinear models indicates that the dominant credit effects are structural rather than artifacts of a particular modeling assumption. In this way, SVR contributes not only a validation step but also substantive evidence of functional robustness in climate-sensitive credit behavior.

4.6. Cross-Model Analysis

A structured comparison of M2, LASSO, and SVR provides additional insight into the stability and functional robustness of the identified predictors. Model 2 offers transparent coefficient estimates and variance partitioning but assumes linearity and can be sensitive to correlated predictors. LASSO, by contrast, applies shrinkage to penalize unstable or redundant variables; the persistence of EA1, SS4, EA6, SS2, and EA2 as dominant predictors under regularization indicates that their influence is not an artifact of multicollinearity or model specification. SVR further tests whether nonlinear relationships alter predictor importance: despite its different functional form, SVR ranks the same credits at the top, confirming that their contribution does not depend on linear assumptions. Taken together, these results show that energy and site credits exhibit structural robustness across linear, regularized, and nonlinear models, whereas the climate interactions in M3, subject to inflated VIF due to constructed terms, capture more selective, credit-specific moderation rather than widespread climate dependence.
Across all analytical frameworks, hierarchical regression, LASSO, and SVR, a consistent pattern of predictor dominance emerged. Credits related to energy optimization (EA1, EA2, and EA6) and site connectivity (SS2 and SS4) repeatedly ranked as the strongest contributors to total LEED points, regardless of model specification or functional form. This cross-method convergence confirms that these credits exert robust and stable influence on certification outcomes and shows that the core drivers of LEED performance are largely insensitive to the modeling technique applied. By consolidating these repeated findings here, the results provide a concise synthesis of predictor stability across methods.
Taken together, the machine-learning results reveal that the predictive dominance of EA1, SS4, EA6, SS2, and EA2 is not only robust under coefficient shrinkage and variable penalization (LASSO) but also persistent under a nonlinear functional form (SVR). Thus, the ML models contribute interpretive depth by confirming that the relationships identified in the hierarchical regression are stable, structurally consistent, and not dependent on linear modeling assumptions.

5. Discussion

This study examined how climatic factors interact with project-level and design-related variables to influence LEED certification outcomes in U.S. hotel projects. By integrating hierarchical regression with regularized and nonlinear machine-learning models, the analysis provides convergent evidence that a small cluster of site and energy credits consistently exerts the strongest influence on total LEED points. Optimize Energy Performance, Alternative Transportation, Green Power, Development Density and Community Connectivity, and On-Site Renewable Energy remained the top predictors across all modeling approaches, indicating that these credits form the structural core of LEED performance in the hotel sector regardless of climatic conditions. Rather than reiterating the numerical results presented earlier, this section focuses on interpreting the relative robustness of these drivers and the credit domains in which climate most strongly modulates performance.
Across all three analytical approaches, hierarchical regression, LASSO, and SVR, the same hierarchy of influential credits emerged. Optimize Energy Performance was by far the strongest single predictor of total LEED points, consistent with previous studies emphasizing energy performance as the core driver of certification level [10,11], followed by Alternative Transportation, Green Power, Development Density and Community Connectivity, and On-Site Renewable Energy. That ranking remained stable across ordinary least squares with controls, a shrinkage estimator that penalizes instability and collinearity, and a nonlinear kernel method. This cross-model convergence suggests that envelope and HVAC optimization, low-carbon energy sourcing, and site-level connectivity are structurally important levers for achieving higher certification levels in hotel projects, and that their predictive power is largely robust to both model specification and regional climatic variation. In practical terms, the results support design strategies that first secure energy and site optimization and then layer additional climate-responsive measures.
Climate sensitivity was not uniform across credits. The regression interaction terms showed that Increased Ventilation experienced a negative moderation effect from mean annual temperature, consistent with the higher conditioning penalties associated with bringing warmer outdoor air into hotel spaces. In contrast, Outdoor Air Delivery Monitoring showed a marginally positive moderation effect, suggesting that monitoring-focused strategies gain value in warmer climates where maintaining acceptable indoor air quality is more challenging. No other credit domains exhibited consistent or statistically meaningful climate interactions, indicating that the influence of most credits on total LEED points remains climate-invariant across the range of the U.S. Building America climates represented in the dataset. These results reinforce the finding that only specific Indoor Environmental Quality strategies, particularly those tied to ventilation loads, display tangible climate responsiveness.
The modest moderation effects identified for indoor environmental quality credits also indicate that climate primarily affects occupant-related environmental performance rather than system-level efficiency. Specifically, the negative interaction between mean annual temperature and Increased Ventilation suggests that higher outdoor temperatures may reduce the practical feasibility or net benefit of enhanced ventilation strategies, as additional conditioning energy is required to maintain thermal comfort. Conversely, the marginal positive association between temperature and Outdoor Air Delivery Monitoring implies that proactive monitoring may be more advantageous in warmer climates where maintaining air quality within comfort thresholds is more challenging. Together, these results align with prior work showing that indoor environmental quality strategies are more climate-sensitive than energy or site strategies, as they rely directly on outdoor air conditions and seasonal thermal gradients. Relatedly, large comparative studies on occupant satisfaction report that LEED buildings do not uniformly outperform non-LEED peers on IEQ, pointing to context-dependent outcomes and the importance of local conditions and operations (e.g., [36,37,38]). In short, the EQ domain appears to be where climate most tangibly modulates LEED credit effectiveness, a pattern the results of this study quantify at the credit level.
The machine-learning results also deepen the interpretation of the hierarchical models. The LASSO shrinkage paths show that, when weaker or redundant predictors are penalized, only a small subset of credits, primarily EA1, SS4, EA6, SS2, and EA2, retain nonzero coefficients across a wide range of penalty values. This indicates that much of the predictive signal attributed to other credits in the linear model is absorbed by this core set, reflecting conceptual overlap among credits that target similar operational or load-driven mechanisms. Rather than serving only as a robustness test, LASSO therefore helps reveal the structural hierarchy among credits by identifying which predictors retain explanatory power even under strong penalization and which are subsumed by more influential variables.
The SVR model similarly contributes more than validation by assessing whether nonlinear relationships alter the climate–credit dynamics observed in the linear models. If the effects of key credits exhibited diminishing returns, threshold behavior, or nonlinear interactions with temperature or precipitation, SVR would be expected to reorder feature importance. Instead, the same core energy and site credits remain dominant under the nonlinear kernel formulation, suggesting that their influence on total LEED points is largely monotonic and stable across the climatic gradients represented in the dataset. This functional stability reinforces the conclusion that the most influential credits behave consistently across modeling assumptions, whereas climate-sensitive EQ strategies exhibit more localized, context-specific responses.
These findings should also be interpreted in light of the regional climate framework adopted in this study. Project locations were classified using the U.S. Department of Energy’s Building America climate regions, which are derived from IECC and ASHRAE climate designations and characterized by heating degree-days, temperature, and precipitation patterns. While our models estimate climate sensitivity through continuous interactions with mean annual temperature and precipitation, the Building America regions provide a categorical representation of broad climatic regimes that are functionally similar to ASHRAE climate zones. Prior work has shown that energy efficiency and Water Efficiency measures can yield highly climate-dependent environmental impacts even when nominal LEED points are constant across regions [20]. In contrast, the present results indicate that, within the hotel projects studied here, energy and site credits retain relatively stable predictive power across climates, whereas ventilation-related indoor environmental quality credits exhibit the clearest temperature sensitivity. This suggests that climate-adjusted benchmarking may be particularly critical for EQ and potentially water-related credits, even when energy-optimization credits remain structurally dominant in determining total scores.
From a methodological standpoint, the triangulation of hierarchical regression, LASSO, and SVR strengthens confidence in the findings. Hierarchical regression provides transparent coefficient estimates for interpreting main effects and climate interactions, but is susceptible to inflated VIF values when interaction terms are included. LASSO addresses this by penalizing unstable or redundant coefficients, while SVR tests whether nonlinear functional forms alter predictor rankings. The consistent dominance of the same core credits across all three approaches demonstrates that the underlying relationships are robust to multicollinearity, regularization, nonlinear transformations, and model specification. Together, these results underscore that the most impactful credits operate in a structurally stable manner across the climatic and operational diversity of hotel projects.
The results also position this study as an intermediate step toward optimization-guided and physics-aware sustainability analytics. The current framework combines hierarchical regression with regularized and kernel-based machine learning in a largely single-objective setting, prioritizing prediction accuracy and interpretability. Multi-objective optimization approaches, such as the improved non-dominated sorting genetic algorithm applied by Liao et al. [39] to balance surveillance coverage, cost, and early-warning performance in bridge–ship collision monitoring, demonstrate how conflicting design criteria can be systematically traded off rather than optimized in isolation. Similarly, Zhang et al. [40] show that physics-aware, data-driven models for wind-induced response prediction in slender infrastructure can embed structural dynamics and loading characteristics directly into the learning process, thereby enhancing transparency and robustness. By analogy, future LEED analytics could be formulated as multi-objective problems that jointly optimize predictive accuracy, model sparsity (or interpretability), and regional equity in credit performance, while incorporating building-physics constraints (e.g., energy balances and load–response relationships) to regularize climate–credit interactions.
Finally, the observed influence of project size and certification year provides additional context for interpreting LEED performance trends. Larger projects achieved slightly higher total points, likely due to economies of scale and resource capacity for pursuing optional credits, while certification year effects were nonsignificant after controlling for other variables, suggesting that improvements in design practice have been offset by rising performance expectations in newer certification cycles.
Overall, this study demonstrates that climate exerts a selective rather than uniform influence on LEED performance of hotel buildings, primarily affecting indoor environmental quality and comfort-related measures while leaving energy and site optimization credits largely robust across contexts. These findings emphasize the importance of regional climate adaptation in sustainability rating systems and support the continued refinement of credit structures to better reflect climatic diversity in building performance outcomes.
In practical terms, the findings of this study carry several implications for both LEED implementation and sustainable building design and construction practice. First, the consistent dominance of energy and site-related credits across climatic contexts underscores the continued importance of energy efficiency, renewable integration, and compact urban siting as universally effective strategies. However, the identified climatic sensitivity of indoor environmental quality credits indicates that LEED rating procedures should incorporate regional climate adjustments when evaluating ventilation, comfort, and daylighting performance. Such adjustments would ensure more equitable scoring and a more accurate reflection of environmental challenges faced by projects in extreme or variable climates.
For design and construction practitioners, these results suggest that project teams should adopt climate-responsive strategies early in the planning phase, especially when targeting credits in the Indoor Environmental Quality and Water Efficiency categories. In warm or humid regions, ventilation and comfort strategies should be integrated with envelope optimization and passive cooling measures to maintain performance without excessive energy penalties. At the policy level, the evidence supports the introduction of climate-adaptive credit weighting or regional benchmarking tools within LEED and similar rating systems, enabling certification programs to better align with climate resilience objectives and equitable sustainability outcomes.

6. Conclusions

This study examined how climatic factors influence the predictive contribution of individual LEED credits in hotel projects, integrating hierarchical regression with regularized and nonlinear machine-learning models. The results demonstrate that while a broad set of credits contributes to certification outcomes, a small cluster of energy and site-related credits consistently exerts the strongest influence. Optimize Energy Performance, Alternative Transportation, Green Power, Development Density and Community Connectivity, and On-Site Renewable Energy remained the top predictors across linear, shrinkage, and kernel-based models, indicating that these credits constitute the structural core of LEED performance in the hotel sector.
At the same time, climate sensitivity was not widespread but selective. Temperature-driven interactions were most evident in the Indoor Environmental Quality domain: Increased Ventilation showed a significant negative interaction with mean annual temperature, while Outdoor Air Delivery Monitoring exhibited a marginally positive interaction. These findings suggest that climate may reduce the marginal utility of certain ventilation-intensive strategies in warmer regions while heightening the value of monitoring-focused approaches. Across all other domains, credit contributions remained largely climate-invariant, reflecting the stability of underlying design and operational strategies.
Quantitatively, the hierarchical regression showed that the strongest predictors, Optimize Energy Performance, Alternative Transportation, and Green Power, show large and statistically significant standardized coefficients (β = 0.38–0.56), collectively accounting for more than half of the explained variance in Model 2 (M2 R2 = 0.58). LASSO regularization confirmed this hierarchy: EA1, SS4, and EA6 produced the largest permutation-based mean dropout loss values (MDL ≈ 0.44–0.88 RMSE units, Table 10), indicating substantial degradation in model accuracy when their information was removed. SVR yielded a nearly identical importance structure, with MDL values of comparable magnitude for these same credits (Table 13) and a test-set R2 of 0.61, demonstrating that their influence remains stable even under a nonlinear kernel formulation. With respect to climate sensitivity, the interaction between mean annual temperature and Increased Ventilation was negative and statistically significant (β = −0.21, p < 0.05), while the interaction with Outdoor Air Delivery Monitoring was marginally positive (β = 0.14, p < 0.10). These selective climate effects reinforce that the most influential energy and site credits are structurally robust across climatic conditions, whereas specific indoor environmental quality strategies exhibit measurable moderation by temperature.
These findings highlight that the most impactful credits on LEED certification outcomes are robust to climatic variation, whereas specific indoor environmental quality strategies display targeted climate responsiveness. As a result, climate-adaptive certification guidance for hotels may be best directed toward ventilation and comfort-related credits, rather than the core energy optimization or sustainable site strategies that appear structurally climate-independent.
By integrating hierarchical regression with regularized and nonlinear machine-learning models, this study introduces a novel multi-method framework for examining climate-sensitive LEED credit performance, offering a more interpretable, stable, and generalizable approach than any single technique alone.

Limitations and Future Research

While this study provides robust, cross-validated evidence of climatic influences on LEED credit performance, several limitations should be acknowledged. The analysis was restricted to project-level data available in public LEED certification records, which limited the ability to capture detailed design or operational variables such as system type, occupancy profile, or building orientation. Climatic characterization was based on mean annual temperature and precipitation, which, although representative, may not fully reflect the dynamic influence of extreme weather or seasonal variability on building performance. Additionally, the moderation effects were modeled linearly, whereas climate–design interactions may be nonlinear or threshold-based in practice. Future research should employ higher-resolution climatic indicators (e.g., heating and cooling degree-days, as well as global tilted irradiance) and expand the framework to longitudinal datasets that track performance across certification cycles. Applying this analytical structure to other sustainability rating systems, such as BREEAM, DGNB, or EDGE, would further clarify how regional climate adaptation is incorporated into global building assessment standards.
A further methodological limitation is that the prediction-error metrics for the LASSO and SVR models (RMSE, MAE, and R2) are reported as point estimates based on a single held-out test set. Although the use of k-fold cross-validation for hyperparameter selection and a separate test split reduces overfitting risk, it does not provide formal confidence intervals for these metrics. Future research should implement bootstrap resampling or repeated cross-validation to derive 95% confidence intervals for prediction errors and model-comparison statistics, thereby offering a more explicit quantification of predictive uncertainty.
Another limitation is that climate sensitivity was modeled using linear interaction terms between z-scored mean annual temperature, mean annual precipitation, and credit achievements, rather than through explicit threshold or nonlinear response functions. Although the inclusion of Building America climate regions incorporates broad climatic regimes tied to heating degree-days and hydrological conditions, the analysis does not identify specific temperature or degree-day thresholds beyond which the marginal contribution of particular credits to LEED performance changes sharply. Prior research on building energy use has documented nonlinear and threshold-like responses of electricity and cooling demand to temperature and degree-day metrics. Future work should therefore crosswalk LEED project data to ASHRAE/IECC climate zones and incorporate higher-resolution climatic indicators (e.g., heating and cooling degree-days, as well as solar irradiance) within flexible modeling frameworks such as piecewise regression or generalized additive models. Such analyses would enable explicit identification of climatic thresholds where the effectiveness or feasibility of specific LEED credits, particularly in the Energy, Water Efficiency, and Indoor Environmental Quality categories, begins to change.
Finally, the modeling framework adopted here remains single-objective and purely data-driven in the sense that it optimizes predictive performance under statistical assumptions without explicitly encoding trade-offs or building-physics constraints. In parallel domains, multi-objective optimization has been used to balance competing criteria such as coverage, cost, and early-warning reliability in surveillance system design, illustrating how non-dominated solution sets can guide design decisions under conflicting objectives [39]. Likewise, recent work on data-driven prediction of wind-induced responses in slender civil infrastructure highlights the benefits of physics-aware learning, in which structural dynamics and loading mechanisms inform model architectures, constraints, or regularization strategies [40]. Future research on climate-sensitive LEED performance could therefore extend the present framework by (i) formulating multi-objective optimization problems that simultaneously target prediction accuracy, interpretability/sparsity, and regional fairness in credit outcomes, and (ii) developing physics-informed models that couple building energy simulations or simplified energy-balance relationships with data-driven predictors to improve generalizability and transparency.

Author Contributions

Conceptualization, M.G. and A.N.G.; Methodology, M.G. and A.N.G.; Formal analysis, M.G. and A.N.G.; Investigation, M.G., A.N.G., M.P. and T.A.; Data curation, S.N.; Writing—original draft, M.G. and S.N.; Writing—review & editing, M.G., M.P. and T.A.; Visualization, A.N.G.; Supervision, M.G.; Project administration, M.G.; Funding acquisition, M.G. All authors have read and agreed to the published version of the manuscript.

Funding

The dissemination of this research is supported by the Aspire Junior Faculty Program through Ball State University, Muncie, Indiana.

Declaration of Generative AI and AI-Assisted Technologies in the Writing Process

During the preparation of this work, the authors used AI in order to improve language and readability. After using this tool, the authors reviewed and edited the content as needed and take full responsibility for the content of the publication.

Data Availability Statement

The data used in this study were obtained from publicly accessible sources: LEED certification data from the U.S. Green Building Council’s Project Directory (Available online: https://www.usgbc.org/projects (accessed on 20 June 2025). The climate data was obtained from the PRISM Climate Group.

Conflicts of Interest

The authors declare no conflict of interest.

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Figure 1. Research Flow.
Figure 1. Research Flow.
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Figure 2. The distribution of the LEED NC v2009 certified hotels in the U.S.
Figure 2. The distribution of the LEED NC v2009 certified hotels in the U.S.
Buildings 15 04382 g002
Figure 3. (a) Residuals vs. predicted; (b) Q-Q plot of standardized residuals.
Figure 3. (a) Residuals vs. predicted; (b) Q-Q plot of standardized residuals.
Buildings 15 04382 g003
Table 1. Building America Climate Zones.
Table 1. Building America Climate Zones.
Climate ZoneAnnual PrecipitationHeating Degree Days (65 °F Basis; 18 °C)Temperature
Hot–Humid >20 inch (50 cm) <1500High average temperatures; prolonged warm seasons (summers > 75 °F/24 °C)
Mixed–Humid >20 inch (50 cm)≤5400Winter’s average outdoor temperature (monthly) decreases to below 45 °F (7 °C)
Hot–Dry <20 inch (50 cm)<2000The year-round monthly average outdoor temperature of over 45 °F (7 °C)
Mixed–Dry <20 inch (50 cm)≤5400Winter’s average monthly outdoor temperature decreases to below 45 °F (7 °C)
Cold 20–40 in (50–100 cm)5400–9000Cold winters with snow and ice; mild to cool summers
Very Cold 15–30 inch (40–75 cm)9000–12,600Long, harsh winters; short, mild summers
Subarctic <20 inch (50 cm)12,600≤Extremely cold winters; short, cool summers
Marine >20 inch (50 cm),
>40–60 inch (100–150 cm) in some areas
3500–5000Moderate year-round with small seasonal temperature variations
Table 2. LEED NC v2009 credits and the coding used for these credits.
Table 2. LEED NC v2009 credits and the coding used for these credits.
Credits (Features)CodePossible PointsSub-Credits
Sustainable Site Credit CategorySS26
Site SelectionSS11
Development Density and Community ConnectivitySS25
Brownfield RedevelopmentSS31
Alternative TransportationSS412SS4.1—Public Transportation Access
SS4.2—Bicycle Storage and Changing Rooms
SS4.3—Low-Emitting and Fuel-Efficient Vehicles
SS4.4—Parking Capacity
Site DevelopmentSS52SS5.1—Protect or Restore Habitat
SS5.2—Maximize Open Space
Stormwater DesignSS62SS6.1—Quantity Control
SS6.2—Quality Control
Heat Island EffectSS72SS7.1—non—roof
SS7.2—Roof
Light Pollution ReductionSS81
Water Efficiency Credit CategoryWE10
Water Efficient LandscapingWE14
Innovative Wastewater TechnologiesWE22
Water Use ReductionWE34
Energy and Atmosphere Credit CategoryEA35
Optimize Energy PerformanceEA119
On-Site Renewable EnergyEA27
Enhanced CommissioningEA32
Enhanced Refrigerant ManagementEA42
Measurement and VerificationEA53
Green PowerEA62
Materials and Resources Credit CategoryMR14
Building ReuseMR14MR1.1—Maintain Existing Walls, Floors, and Roof
MR1.2—Maintain 50% of Interior Non-Structural Elements
Construction Waste ManagementMR22
Materials ReuseMR32
Recycled ContentMR42
Regional MaterialsMR52
Rapidly Renewable MaterialsMR61
Certified WoodMR71
Indoor Environmental Quality Credit CategoryEQ15
Outdoor Air Delivery MonitoringEQ11
Increased VentilationEQ21
Construction IAQ Management PlanEQ32EQ3.1—During Construction
EQ3.2—Before Occupancy
Low—Emitting MaterialsEQ44EQ4.1—Adhesives and Sealants
EQ4.2—Paints and Coatings
EQ4.3—Flooring Systems
EQ4.4—Composite Wood and Agrifiber Products
Indoor Chemical and Pollutant Source ControlEQ51
Controllability of SystemsEQ62EQ6.1—Lighting
EQ6.2—Thermal Comfort
Thermal ComfortEQ72EQ7.1—Design
EQ7.2—Verification
Daylight and ViewsEQ82EQ8.1—Daylight
EQ8.2—View
Innovation and Design Process Credit CategoryID6
Innovation in DesignID15
LEED Accredited ProfessionalID21
Regional Priority CreditsRP4
Total LEED ScorePoints110
Table 3. Climate-relevant LEED NC v2009 credits and their rationale.
Table 3. Climate-relevant LEED NC v2009 credits and their rationale.
Credits (Features)CodePossible PointsRationale (Climate Relevance)
Site SelectionSS11Site exposure, hazards, and required site-hardening are climate dependent (e.g., flood, heat, and wind).
Development Density and Community ConnectivitySS25Mode choice and VMT reduction yield climate-mediated energy/emissions effects that vary by region.
Alternative TransportationSS412Modal shifts influence operational energy and emissions, whose benefits depend on local climate and urban form.
Site DevelopmentSS52Vegetation establishment and habitat performance depend on rainfall, temperature, and evapotranspiration.
Stormwater DesignSS62Runoff volume, peak flow, and BMP performance are driven by precipitation intensity and patterns.
Heat Island EffectSS72Surface heat exchange and microclimate cooling potential are temperature and radiation-dependent.
Water Efficient LandscapingWE14Irrigation demand is governed by precipitation deficits, temperature, and evapotranspiration.
Water Use ReductionWE34Indoor use reduction potential and baselines are influenced by climate-driven cooling/humidification needs.
Optimize Energy PerformanceEA119Heating/cooling loads and envelope/HVAC efficiency are directly set by outdoor temperature and humidity.
On-Site Renewable EnergyEA27Generation potential (solar/wind) depends on local resources, insolation, and temperature effects.
Green PowerEA62Feasibility and grid decarbonization impacts vary by regional renewable availability, shaped by climate.
Outdoor Air Delivery MonitoringEQ11Ventilation strategies incur climate-dependent energy penalties tied to outdoor conditions.
Increased VentilationEQ21Additional outdoor air requires conditioning loads that vary with temperature and humidity.
Controllability of SystemsEQ61Occupant control needs and effective setpoints are affected by seasonal and outdoor variability.
Thermal ComfortEQ72Compliance depends on envelope/HVAC responses to outdoor temperature, humidity, and seasonal swings.
Daylight and ViewsEQ82Daylight availability is governed by solar geometry and cloudiness patterns specific to the climate.
Note: Credits were selected only when supported by building-science mechanisms linking their performance to climate-dependent loads (temperature, humidity, precipitation, solar radiation, and evapotranspiration). MR and ID credits were excluded due to a lack of climate-dependent pathways.
Table 4. Frequency of LEED-certified projects in each BA climate region.
Table 4. Frequency of LEED-certified projects in each BA climate region.
Building America Climate RegionNumber of ProjectsPercentage
Subarctic00
Very Cold20.8
Cold5822.4
Mixed–Humid9637.1
Mixed–Dry00.0
Marine3112.0
Hot–Dry249.3
Hot–Humid4617.8
Hawaii (No BA Climate Specified)20.8
Total259100
Table 5. Hierarchical regression model summary.
Table 5. Hierarchical regression model summary.
Durbin–Watson
ModelRR2Adjusted R2RMSEAICBICAutocorrelationStatisticp
M10.3440.1180.1000.188−120.257−95.523−0.0072.0100.985
M20.8980.8070.7900.091−474.555−396.821−0.0172.0300.858
M30.9070.8230.7890.091−454.721−302.7850.0221.9530.650
Table 6. ANOVA.
Table 6. ANOVA.
Model Sum of SquaresdfMean SquareFp
M1Regression1.16850.2346.622<0.001
Residual8.7132470.035
Total9.881252
M2Regression7.974200.39948.486<0.001
Residual1.9082320.008
Total9.881252
M3Regression8.134410.19823.952<0.001
Residual1.7482110.008
Total9.881252
Table 7. Coefficients.
Table 7. Coefficients.
Collinearity Statistics
Model UnstandardizedStandard ErrorStandardizedtpToleranceVIF
M1(Intercept)−0.4950.199 −2.4830.014
GSF0.0520.0170.1913.1230.0020.9571.045
CertYear0.0090.0050.1171.9060.0580.9521.051
Tmean0.0730.0670.0671.0810.2810.9211.086
Precp−0.0340.052−0.041−0.6550.5130.9151.093
M2(Intercept)−1.0410.120 −8.699<0.001
GSF0.0380.0100.1393.967<0.0010.6821.467
CertYear−0.0020.002−0.024−0.7640.4460.8661.154
Tmean−0.0550.035−0.050−1.5600.1200.7961.256
Precp0.0340.0270.0411.2650.2070.8071.239
SS10.0710.0270.0792.5810.0100.8851.131
SS20.1180.0190.2016.200<0.0010.7931.262
SS40.2210.0250.2788.839<0.0010.8431.186
SS50.1210.0210.1905.671<0.0010.7421.349
SS60.0390.0160.0822.5340.0120.7931.261
SS70.0850.0220.1283.933<0.0010.7891.268
WE10.0780.0170.1434.535<0.0010.8371.195
WE30.1620.0240.2076.666<0.0010.8611.161
EA10.4910.0310.54115.989<0.0010.7271.376
EA20.2000.0340.1965.919<0.0010.7621.313
EA60.0890.0120.2217.445<0.0010.9451.058
EQ10.0590.0150.1223.828<0.0010.8191.221
EQ20.0490.0160.0923.0060.0030.8831.132
EQ60.0500.0170.0902.9320.0040.8781.139
EQ70.0680.0170.1294.125<0.0010.8571.166
EQ80.0190.0220.0290.8680.3860.7681.301
M3(Intercept)−0.8410.222 −3.795<0.001
GSF0.0390.0110.1453.703<0.0010.5501.817
CertYear−0.0010.003−0.018−0.5510.5820.7831.278
Tmean−0.0120.292−0.011−0.0410.9670.01286.930
Precp−0.3510.224−0.424−1.5690.1180.01187.048
SS20.0790.0810.1340.9760.3300.04422.518
SS10.0380.1280.0420.2940.7690.04124.378
SS40.1360.1020.1701.3370.1830.05219.397
SS5−0.0180.092−0.029−0.2020.8400.04124.511
SS60.0940.0570.1971.6560.0990.05916.876
SS70.0830.0800.1241.0440.2970.05916.891
WE10.0090.0760.0160.1130.9110.04323.030
WE30.1870.1060.2401.7560.0810.04522.252
EA10.5210.1180.5744.396<0.0010.04920.307
EA20.2240.1420.2191.5750.1170.04323.031
EA60.0770.0430.1911.8060.0720.07513.356
EQ1−0.0520.059−0.107−0.8850.3770.05717.424
EQ20.2440.0660.4553.720<0.0010.05617.838
EQ60.0120.0590.0210.1980.8430.07213.811
EQ70.0540.0650.1020.8370.4030.05717.682
EQ80.0040.0770.0050.0470.9630.06116.401
Tmean × SS1−0.1180.196−0.132−0.6060.5450.01857.074
Tmean × SS20.0470.1260.0620.3690.7120.03033.663
Tmean × SS40.0240.1560.0260.1510.8800.02835.551
Tmean × SS50.1340.1500.1360.8890.3750.03627.929
Tmean × SS6−0.0870.089−0.132−0.9720.3320.04621.849
Tmean × SS70.0130.1300.0160.0990.9210.03429.472
Tmean × WE1−0.0390.116−0.046−0.3340.7390.04522.261
Tmean × WE3−0.0760.168−0.062−0.4490.6540.04422.614
Tmean × EA1−0.0680.187−0.050−0.3640.7160.04422.875
Tmean × EA2−0.0310.254−0.017−0.1200.9040.04422.663
Tmean × EA60.0130.0690.0210.1900.8490.07114.132
Tmean × EQ10.1720.0930.2261.8540.0650.05717.675
Tmean × EQ2−0.3470.112−0.388−3.0860.0020.05318.815
Tmean × EQ60.0650.0990.0890.6550.5130.04522.037
Tmean × EQ70.0150.1090.0200.1360.8920.03925.917
Tmean × EQ80.0350.1270.0330.2740.7850.05717.447
Precp × SS10.1680.1980.2280.8490.3970.01286.409
Precp × SS40.1290.1170.1571.1090.2690.04223.974
Precp × SS50.1080.1040.1201.0400.3000.06315.929
Precp × WE10.1480.0920.2051.6090.1090.05219.310
Precp × WE30.0260.1280.0230.2060.8370.06615.247
Table 8. Model summary: Regularized Linear Regression.
Table 8. Model summary: Regularized Linear Regression.
Penaltyλn (Train)n (Validation)n (Test)Validation MSETest MSE
L1 (Lasso)0.00218536320.3030.204
Note. The model is optimized with respect to the validation set mean squared error.
Table 9. Regularized Linear Regression Model performance metrics.
Table 9. Regularized Linear Regression Model performance metrics.
Values
MSE0.204
MSE (scaled)0.209
RMSE0.452
MAE/MAD0.368
R20.796
Table 10. Feature importance metrics and regularized regression coefficients.
Table 10. Feature importance metrics and regularized regression coefficients.
Mean Dropout LossRegression Coefficients
EA10.8840.532
SS40.5800.254
EA60.5250.041
SS20.5250.204
EA20.5220.180
SS50.5210.200
EQ10.5140.173
WE30.5080.176
SS70.5020.164
EQ70.4870.137
WE10.4660.107
SS10.4620.095
SS60.4560.079
EQ20.4510.060
EQ60.4470.196
EQ80.4430.007
Note. Mean dropout loss is a permutation-based feature importance metric. For each predictor, its values were randomly permuted 50 times, and the resulting increase in root mean squared error (RMSE) was averaged. Larger values indicate greater importance for predicting total LEED points.
Table 11. Model summary: Support Vector Machine regression.
Table 11. Model summary: Support Vector Machine regression.
Violation CostSupport Vectorsn (Train)n (Validation)n (Test)Validation MSETest MSE
0.08016917241400.1920.186
Note. The violation cost parameter C in Support Vector Regression (SVR) controls the balance between model smoothness and error tolerance: smaller C values impose stronger regularization, whereas larger C values allow a closer fit to the training data.
Table 12. SVR Model performance metrics.
Table 12. SVR Model performance metrics.
Values
MSE0.186
MSE (scaled)0.168
RMSE0.431
MAE/MAD0.338
R20.835
Table 13. Feature importance metrics.
Table 13. Feature importance metrics.
Mean Dropout Loss
EA10.917
EA60.588
SS40.586
SS20.564
EA20.545
EQ10.541
EQ70.532
WE30.528
SS50.526
WE10.525
SS70.521
SS60.495
EQ60.489
SS10.484
EQ20.484
EQ80.480
Note. Mean dropout loss is a permutation-based feature importance metric, computed as the average increase in root mean squared error (RMSE) over 50 random permutations of each predictor. Larger values indicate that the predictor is more influential in the SVR model.
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MDPI and ACS Style

Goodarzi, M.; Goodarzi, A.N.; Naseri, S.; Parsaee, M.; Abazari, T. Assessing Climate Sensitivity of LEED Credit Performance in U.S. Hotel Buildings: A Hierarchical Regression and Machine Learning Verification Approach. Buildings 2025, 15, 4382. https://doi.org/10.3390/buildings15234382

AMA Style

Goodarzi M, Goodarzi AN, Naseri S, Parsaee M, Abazari T. Assessing Climate Sensitivity of LEED Credit Performance in U.S. Hotel Buildings: A Hierarchical Regression and Machine Learning Verification Approach. Buildings. 2025; 15(23):4382. https://doi.org/10.3390/buildings15234382

Chicago/Turabian Style

Goodarzi, Mohsen, Ava Nafiseh Goodarzi, Sajjad Naseri, Mojtaba Parsaee, and Tarlan Abazari. 2025. "Assessing Climate Sensitivity of LEED Credit Performance in U.S. Hotel Buildings: A Hierarchical Regression and Machine Learning Verification Approach" Buildings 15, no. 23: 4382. https://doi.org/10.3390/buildings15234382

APA Style

Goodarzi, M., Goodarzi, A. N., Naseri, S., Parsaee, M., & Abazari, T. (2025). Assessing Climate Sensitivity of LEED Credit Performance in U.S. Hotel Buildings: A Hierarchical Regression and Machine Learning Verification Approach. Buildings, 15(23), 4382. https://doi.org/10.3390/buildings15234382

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