This section presents the results and discussion in two complementary stages. The first subsection analyzes the general characteristics of the sample without segmentation by thematic axis, covering temporal and geographical distribution, study type, AI function, and tools used. The second subsection organizes the results by thematic axis and macro-objective, enabling the comparison of integration patterns, automation levels, life cycle boundaries, methodological limitations, and forms of support for design decision-making.
3.1. General Characterization of the Sample
The general characterization of the sample aims to situate the maturity level of the field before the detailed analysis by thematic axis. Thus, the distribution of studies by axis, year, country, study type, AI function, and tools used is interpreted as preliminary evidence of either fragmentation or consolidation in the integration of BIM, CO2, sustainability, and AI.
A total of 85 studies were identified [
2,
3,
26,
27,
28,
29,
30,
31,
32,
33,
34,
35,
36,
37,
38,
39,
40,
41,
42,
43,
44,
45,
46,
47,
48,
49,
50,
51,
52,
53,
54,
55,
56,
57,
58,
59,
60,
61,
62,
63,
64,
65,
66,
67,
68,
69,
70,
71,
72,
73,
74,
75,
76,
77,
78,
79,
80,
81,
82,
83,
84,
85,
86,
87,
88,
89,
90,
91,
92,
93,
94,
95,
96,
97,
98,
99,
100,
101,
102,
103,
104,
105,
106,
107,
108] and distributed across thematic axes, as shown in
Figure 2. This distribution reveals an asymmetry in maturity among the analyzed streams: the BIM + AI and BIM + CO
2 axes account for most of the publications, indicating greater exploration of these partial integrations in the AECO sector, whereas AI + CO
2 and Core studies remain less represented. This pattern suggests that studies articulating AI and carbon quantification are still scarce and, above all, that few studies simultaneously integrate BIM, automated CO
2 calculation, and AI within the same decision-making workflow.
The geographical distribution of the studies was analyzed based on the authors’ country of affiliation, meaning that the same article could contribute to more than one country. The results show a predominance of occurrences in Asia (57%), mainly driven by China and South Korea, followed by Europe (25%), with the United Kingdom standing out. The Americas showed a more moderate participation (9%), while Africa and Oceania appeared with lower representation. No authors with Brazilian affiliations were identified in the analyzed sample. This geographical pattern is relevant because carbon databases, energy mix, climate, construction practices, and material availability are highly context-dependent factors. Therefore, the regional concentration of studies may limit the transferability of models, emission factors, and automated recommendations to other contexts, especially countries with different environmental databases and construction conditions.
Regarding temporal distribution, shown in
Figure 3, the volume of publications increased until 2024, followed by a slight decrease in 2025, which may be partly associated with the fact that data collection was conducted before the end of the year. The disaggregation by axis shows that this growth was mainly driven by BIM + AI studies, which expanded from 2022 onward and remained the largest group. The BIM + CO
2 axis also gained greater prominence from 2023 onward, reaching its highest point in 2024, indicating recent progress in the literature focused on automated carbon quantification in BIM environments. By contrast, BIM + AI + Sustainability and AI + CO
2 maintained a more moderate presence throughout the period, while Core studies remained among the smallest groups, with more noticeable growth only in the final years. This pattern reinforces that the different research streams have evolved at different paces over time.
Regarding the types of studies identified, the sample is mainly composed of method development studies, particularly in two modalities: method development associated with computational experiments (47%) and method development with case studies (35%). This pattern indicates that the literature is still concentrated on methodological proposals tested through simulations, digital models, and applications in specific scenarios, with fewer solutions fully incorporated into professional practice. Method development studies with prototypes represent 12% of the sample, while plug-in development with experimentation accounts for only 6%, suggesting that the materialization of proposals into tools integrated into the BIM environment remains limited. Thus, the distribution by study type reinforces the idea that the field remains predominantly methodological and experimental, and that the automation identified in the literature does not always correspond to transferable, continuous, or professionally implemented workflows.
The functions performed by AI in the analyzed studies were grouped into four main categories. The most frequent category is prediction/forecasting, with approximately 30% of occurrences, indicating the recurrent use of AI to estimate performance variables, such as energy, emissions, or operational metrics, with lower computational cost than full simulations. Next, applications focused on interpreting properties, providing recommendations, and identifying inconsistencies account for 26%, reflecting the growth of approaches oriented toward explanation, checking, and direct user support. Single- and multi-objective optimization represents 25%, highlighting the use of AI as a solution-selection engine. Finally, automatic generation of alternatives accounts for approximately 20%, indicating a still smaller presence of AI applied to the generation of design options.
Table 4 differentiates the main approaches identified, indicating their role in the workflow, the most recurrent data and outputs, and the methodological limitations observed. This distinction is necessary because not every form of computational automation represents the same level of intelligence, integration, or decision support.
Figure 4 presents a Sankey diagram that synthesizes how the studies operationalize the connection between BIM, CO
2 calculation, and AI. The flow highlights the central role of Revit as a model-authoring and organization platform, while IFC appears as a recurring alternative when the objective is to expand interoperability and enable external processing. Tools such as EnergyPlus and DesignBuilder appear in association with energy simulation and operational carbon, whereas LCA/CO
2 software, such as One Click LCA and Tally, or custom calculations, are more frequently used for embodied carbon. In the AI layer, the presence of Python, machine learning environments, Dynamo, NLP/LLMs, and optimization models indicates that the intelligent part of the workflow is often implemented as a modular component rather than as a native function of the BIM environment.
The Sankey diagram reveals the fragmented way in which BIM–CO2–AI integration has been constructed. In many studies, BIM provides geometry, quantities, parameters, or semantic structure; environmental calculation occurs in LCA/CO2 tools, simulation environments, or external databases; and AI acts as an additional layer for prediction, optimization, explanation, or recommendation. This configuration can reduce manual steps and accelerate analyses, but it also creates critical dependencies: the semantic quality of the BIM model, consistency of extracted parameters, compatibility between formats, transparency of emission databases, and validation of generated recommendations.
The axis-based reading reinforces this interpretation. In BIM + AI studies, the workflow is concentrated on automation, optimization, and intelligent interfaces applied to the model. In BIM + AI + Sustainability studies, the dominant pattern is based on pipelines connecting parametric BIM, energy/environmental simulation, and ML models. In the BIM + CO2 axis, carbon automation depends mainly on LCA/CO2 software or custom calculations. In AI + CO2 studies, AI acts directly on carbon, but outside a structured BIM workflow. In Core studies, there is an attempt to articulate these layers, although closing the decision-making loop still depends largely on scripts, APIs, external pipelines, and manual validation.
In addition to the tool-flow analysis presented in the Sankey diagram, some general indicators help assess the maturity level of BIM, CO2, and AI integration in the full sample. While the diagram highlights the dependence on external tools, scripts, and modular pipelines, the quantitative indicators show the extent to which this integration actually advances toward carbon quantification and support for design decision-making. Although 60% of the studies performed some type of carbon quantification, only 16% addressed the life cycle in a broad manner. In addition, only 39% of the studies used carbon quantification to propose, compare, or optimize design alternatives, indicating that calculation is still often used as a measurement step rather than as an active decision-making mechanism. This pattern is also observed in BIM + AI studies: despite the growth of this axis, only 17% advanced toward carbon quantification, reinforcing the idea that AI–BIM integration is still rarely mobilized for decisions explicitly oriented toward emission mitigation.
3.2. Analysis by Integration Axis
This subsection presents the results and discussion by thematic axis. For each axis, the studies were organized according to macro-objectives, allowing the purposes and implementation mechanisms to be compared. In addition, for the axes that quantify carbon, the scope of the life cycle boundaries adopted is discussed, as well as the degree of automation and the use of BIM, in order to show how these elements are converted into support for design decision-making. The analysis by thematic axis makes it possible to understand how partial and complete integrations are methodologically structured.
3.2.1. BIM + AI
The articles in the BIM + AI axis were included to map the mechanisms through which artificial intelligence has been coupled with BIM in the AECO sector, as well as the most recurrent objectives, functions, and implementation patterns. Although these studies do not directly address CO2 quantification, they are relevant to this review because they reveal technological capabilities that may be transferred or adapted to BIM–CO2–AI workflows, such as process automation, alternative generation, optimization, information interpretation, and decision support. Thus, this axis does not constitute direct evidence of low-carbon building design but serves as a basis for understanding the maturity of AI functions in BIM environments.
As shown in
Figure 5, the studies were organized into three macro-objectives: creation and optimization of design solutions; intelligent interaction with BIM information; and construction planning and management.
The largest group focuses on the automatic creation and optimization of design solutions [
26,
27,
28,
29,
30,
31,
32,
33,
34,
35,
36,
37,
38,
39,
40,
41], indicating that a significant part of the literature uses BIM + AI to explore performance alternatives through optimization, generative design, and model-based automation. In these studies, BIM acts as the geometric and parametric basis of the building, while AI algorithms or computational routines automatically explore the solution space, generating or refining layouts, structural systems, modular solutions, and building services based on predefined variables and constraints.
Four main arrangements were identified: (i) generative models and deep learning for segmentation, conditional creation, and conversion into BIM objects; (ii) metaheuristics for constrained optimization; (iii) NLP and recommender systems to translate natural-language requirements into BIM solutions; and (iv) generative design, often implemented in Dynamo, based on predefined rules and constraints and not always associated with machine learning. The reported results indicate practical gains, such as the automatic creation of structural layouts compatible with architectural models [
36], rapid generation of layouts and BIM models [
26], cost reductions of approximately 23% compared with designs produced by engineers [
35], and design time savings of up to 90% [
41].
From the perspective of this review, the main contribution of this macro-objective lies in demonstrating that BIM can function as a parametric environment for the automated generation, comparison, and optimization of alternatives. However, because these studies do not incorporate carbon metrics, a gap remains in connecting these capabilities to explicit environmental objectives. Thus, the mechanisms already used to optimize form, layout, structural systems, and performance could be adapted in future research to incorporate carbon, cost, and performance as integrated decision criteria.
The second group corresponds to intelligent interaction with BIM information [
42,
43,
44,
45,
46,
47,
48,
49,
50,
51,
52]. Its scope is predominantly informational, focusing on model data management, semantic quality, requirement checking, and query interfaces applied to buildings. In this group, BIM acts as a structured information base for project components, while AI is used to interpret, classify, recommend, or query model data. The approaches include (i) classical NLP and supervised learning to classify texts and requirements; (ii) data mining and recommender systems to suggest BIM objects and content; (iii) computer vision and machine learning to recognize objects and attributes, strengthening BIM semantic consistency; and (iv) conversational assistants, including LLM-based solutions for search and interaction with the model.
The results indicate efficiency gains but also reveal important limitations. For example, a GPT-based digital assistant for real-time interaction with BIM models via text or voice in Revit achieved 94% accuracy in simple queries, but only 49.5% in compound queries requiring multiple functions within the same sentence [
51]. This result shows that conversational interfaces and recommender systems can facilitate access to BIM information but still present weaknesses in orchestrating complex tasks. For BIM–CO
2–AI workflows, this limitation is critical, since low-carbon recommendations require not only model querying but also correct interpretation of materials, quantities, calculation boundaries, emission databases, and technical constraints. Therefore, this macro-objective reinforces the need for validation, traceability, and human verification when LLMs and natural-language interfaces are applied to environmental decision support.
The third group addresses construction planning and management [
53,
54,
55,
56,
57,
58,
59], showing the use of BIM + AI to support decisions related to production, scheduling, cost, inspection, and construction management. In this group, BIM acts as an informational basis for converting model elements and attributes into activities, work packages, schedules, and operational decisions. The solutions mainly rely on Revit, Dynamo, Revit API, and 4D/5D tools, such as Navisworks and custom modules. AI functions include schedule optimization with metaheuristics, prediction of the impacts of design changes, deep learning applied to inspection or point clouds, and intelligent interfaces to synthesize information, interpret textual inputs, and signal risks. The reported results indicate relevant gains, such as a reduction of approximately 97% in schedule creation time, from 150 min to 3–4 min [
54], as well as a 42% reduction in discrepancies between planning and execution, anomaly detection in approximately 3 min, and an approximately 30% reduction in managerial decision-making time [
59].
Although this macro-objective is more closely associated with execution than with building conception, it contributes to the review by demonstrating that BIM data can be converted into automated production and management decisions. The detailed AI functionalities identified in the BIM + AI axis are presented in
Appendix C. In summary, this axis shows that the integration between BIM and AI already presents relevant maturity in modeling automation, alternative generation, optimization, intelligent querying, and management support. Therefore, the main contribution of this axis to the review is to reveal computational mechanisms that may be incorporated in future BIM–CO
2–AI workflows oriented toward design decision-making.
3.2.2. BIM + AI + Sustainability
The articles in the BIM + AI + Sustainability axis were included to map how the integration between digital modeling and artificial intelligence has been applied to environmental metrics in the AECO sector, even when explicit CO2 emission quantification is not provided. This axis does not directly answer the research question in terms of carbon calculation, but it is relevant because it shows how energy, thermal comfort, daylighting, and retrofit have been incorporated into automated workflows for analysis, prediction, simulation, and optimization. Thus, these studies serve as base literature for identifying methodological mechanisms that may be adapted to BIM–CO2–AI workflows.
As shown in
Figure 6, the studies were organized into three macro-objectives: performance-oriented optimization and generative design; prediction and diagnosis of energy consumption; and retrofit decisions and performance optimization in existing buildings. This distribution reinforces that this axis is more consolidated in applications focused on energy and environmental performance than in explicit carbon assessments, functioning as an intermediate stage between intelligent automation in BIM and full BIM + CO
2 + AI integration.
The most representative group comprises studies on performance-oriented optimization and generative design, especially regarding energy and comfort [
60,
61,
62,
63,
64,
65]. These studies focus on decisions related to the envelope, façade, and form parameters, usually structured as parameterized cycles: BIM, generation of alternatives, performance simulation, and selection of solutions through optimization, often using techniques such as NSGA-II and related variants. The reported results indicate measurable gains, such as an approximate reduction of 6.7% in heating load and 3.5% in cooling load in optimized façades [
60], Pareto solutions balancing envelope energy and cost, with gains of 8.48% in energy and 7.52% in cost, or 21.17% in cost with minimal energy variation [
63], as well as a 37.5% reduction in energy consumption and a 33.5% increase in thermal comfort compared with the initial solution [
64].
The contribution of this group lies in demonstrating that BIM and AI are already capable of structuring cycles for the generation, simulation, and selection of environmental alternatives. However, because the metrics analyzed are concentrated on energy, comfort, and daylighting, these studies do not allow direct assessment of whether the optimized alternative also reduces CO2 emissions. The central gap, therefore, is the incorporation of emission factors, LCA boundaries, and carbon indicators into the objective functions already used in these optimization workflows.
Next, there are studies focused on the prediction and diagnosis of energy consumption using BIM-derived data [
66,
67,
68], in which AI acts as a fast estimator or explanatory model to support energy analyses. These studies use datasets derived from simulations or BIM models and train supervised algorithms, especially ensembles, boosting methods, Random Forest, XGBoost, and neural networks, to predict consumption or energy intensity. The results indicate good performance of boosting-based methods, such as FBI_AdaBoost, FBI_XGB, GBM, and FBI-adjusted XGBoost [
66,
67,
68]. In addition, variable-importance analyses identify elements such as roofs, external walls, and windows as relevant factors affecting energy consumption, with variations of approximately 9% to 40% depending on the city [
67].
This group is important because it demonstrates the potential of metamodels to reduce repetitive simulations and accelerate the evaluation of alternatives. However, as long as the predicted variable remains limited to energy consumption or energy intensity, the relationship with decarbonization depends on an additional step of conversion into emissions, considering the energy mix, regional factors, and operational assumptions. Thus, these studies represent a relevant methodological basis for future carbon prediction but still constitute a stage prior to explicit CO2 quantification.
Finally, the last group focuses on retrofit decisions and performance optimization in existing buildings [
69,
70,
71], indicating that applications aimed at intervening in the existing building stock are still less frequent, although relevant because they bring BIM + AI closer to real-world contexts. These studies seek to improve the performance of already defined buildings through diagnosis, as-is/as-built modeling, definition of retrofit variables, and thermal or energy evaluation of scenarios. BIM acts as an informational reference and parameterization basis, while AI, when more explicitly applied, functions as an optimization mechanism or predictive model to accelerate the comparison of alternatives.
The contribution of this group lies in showing that BIM + AI can support decisions applied to existing buildings, where the potential for impact reduction may be significant. However, without explicit carbon quantification, energy or thermal gains cannot be directly interpreted as evidence of climate mitigation. To advance toward the BIM + CO2 + AI core, these workflows would need to connect retrofit scenarios to emission factors, avoided operational carbon, embodied carbon from interventions, and trade-offs among energy savings, added materials, cost, and comfort.
Overall, the limitations of the BIM + AI + Sustainability axis involve dependence on BEM, difficulties in generalization across climates and regions, simplified scopes, a limited number of variables, representative periods for CFD, thermal simplifications, and the use of restricted sets of components.
3.2.3. BIM + CO2
The BIM + CO2 axis is closely aligned with the research question, as it investigates how BIM has been used to automate emission quantification, mainly through LCA, and to support comparisons between design scenarios. This group establishes the methodological basis for automated carbon calculation in BIM environments by revealing patterns of quantity extraction, linkage to emission factors, definition of life cycle boundaries, and integration with external tools. Although it generally does not yet incorporate AI systematically, this axis represents an essential intermediate stage in the maturation of BIM–CO2–AI integration.
Regarding the role of BIM, the predominant pattern is its use as a structured data platform and traceable inventory source. However, the success of carbon calculation depends on the informational quality of the model, including consistent classification of elements, material identification, sufficient parameters, and interoperability. Thus, the bottleneck is not only the automation of LCA but also ensuring that the BIM model contains reliable and usable information to support environmental calculation.
The studies demonstrate three main ways of operationalizing automated CO
2 calculation through BIM–LCA: integration with LCA software, with 12 occurrences; use of custom databases and calculations, with 10 occurrences; and development of dedicated plug-ins, with only one occurrence. This pattern indicates that carbon automation still depends mainly on external tools, internal calculations, or intermediate routines, whereas solutions fully integrated into the BIM environment remain less frequent. The studies were grouped into three macro-objectives, as shown in
Figure 7.
The most frequent group focuses on the automation and standardization of carbon calculation [
72,
73,
74,
75,
76,
77,
78,
79,
80], bringing together studies aimed at extracting quantities from BIM, mapping materials, and linking them to emission factors, EPDs, databases, or national datasets. These workflows recurrently follow three steps: data extraction from the model, association with emission factors, and consolidation of results according to life cycle boundaries. This group shows that automated quantification makes emissions more traceable by element, category, or component, reducing manual effort and inconsistencies typically associated with spreadsheet-based approaches.
The main contribution of this macro-objective is the consolidation of the inventory and calculation layer that supports future BIM–CO2–AI applications. However, its limitation is that automation remains concentrated on measurement: the studies make carbon more visible and comparable, but do not always advance toward recommendation, optimization, or automated selection of alternatives. Thus, this group demonstrates maturity in the calculation infrastructure but does not yet close the decision-making loop.
The second most frequent macro-objective concerns the use of carbon calculation to support carbon reduction decisions [
2,
3,
81,
82,
83,
84,
85,
86], using CO
2 as a comparative criterion among design scenarios, materials, and mitigation strategies. In these studies, BIM acts as a parameterization and inventory-organization structure, while the assessment of alternatives often depends on complementary tools, such as energy simulation, CFD, or structural analysis. This group stands out for connecting the carbon metric to the selection of alternatives, bringing environmental quantification closer to the decision-making process.
The reported results indicate relevant reductions in different contexts: a value engineering plug-in reported simultaneous reductions of 10% in cost and 15% in embodied carbon [
82]; another study identified material combinations capable of reducing embodied carbon by approximately 52%, mainly through substitutions in concrete and steel [
83]; and an analysis of ventilation in a public restroom reported a 20.4% reduction in energy consumption and a reduction of 30,681 kg in CO
2 [
86]. These findings show that carbon calculation can support concrete reduction decisions, but they also indicate that, without automated search and optimization mechanisms, the exploration of alternatives tends to remain limited to scenarios previously defined by the researchers.
The final macro-objective addresses carbon emissions associated with construction execution and design circularity [
87,
88,
89,
90,
91,
92], expanding the analysis to construction, logistics, waste, reuse, circular practices, and, in some cases, digital twins. In these studies, BIM acts as a platform for tracing and organizing distributed information across the production chain, often supported by IFC, BIM servers, databases, extraction routines, and semantic structures such as ontologies. This organization enables the mapping of components, quantities, waste flows, and construction strategies from the perspective of environmental impacts.
The contribution of this group lies in showing that carbon is not limited to material selection during design conception but can also be monitored and reduced through decisions related to execution, logistics, waste, and circularity. At the same time, these studies show that circular decisions require distributed data, traceability, and multiple criteria across the production chain. Therefore, they represent a promising field for future incorporation of AI in multicriteria optimization problems, waste prediction, component tracking, and recommendation of reuse strategies.
Regarding life cycle scope in the BIM + CO
2 sample,
Figure 8 shows the predominance of assessments with broader boundaries. Two studies started from A1–A3 and both extended the analysis to the use stage; five adopted A1–A5, two of which also included B1–B7; seven used A1–C4; eight adopted the A1–D approach; and only one study analyzed B6 exclusively, related to operational emissions from building use.
These results indicate that the BIM + CO2 axis presents greater maturity in explicitly defining life cycle boundaries. Even so, even in studies declared as full life cycle assessments, stages such as operation, construction, maintenance, replacements, logistics, and end of life tend to be treated through assumptions, estimates, or secondary data. In practice, the most robust gains in automation and traceability are concentrated in product-stage embodied carbon, especially A1–A3, where BIM offers stronger methodological alignment by enabling direct extraction of quantities and linkage to materials and emission factors.
The relative contribution of life cycle stages varies according to the boundary adopted. In full life cycle assessments, the operational phase may predominate, with B6 accounting for approximately 87.86% of emissions over a 60-year horizon [
72], while other studies report operational shares of around 75% and 73% [
73,
74]. By contrast, when the focus is on construction systems and structure, material production becomes more influential, reaching approximately 92% in one study [
76], or 65.7% for module A in a multiscale analysis, with emphasis on steel and concrete [
79]. This variation changes the target of interventions: materials and structural systems become central for embodied carbon, while energy, ventilation, comfort, and operation gain relevance in broader or operational scopes.
In addition to boundaries, the results are sensitive to databases and calculation methods. One study reported substantial differences among databases such as ICE, GaBi, and Ecoinvent, with intensities of 0.916, 2.20, and 2.30 tCO
2e/m
2, respectively [
85]. Another identified an approximately 10% discrepancy between a normative procedure and a plug-in [
82]. These findings reinforce that using CO
2 as a decision criterion requires transparency regarding boundaries, emission factors, environmental databases, and mapping between the BIM inventory and carbon data.
In summary, the BIM + CO2 axis demonstrates greater maturity in the automation of carbon calculation in BIM environments, especially in quantity extraction, component-level traceability, and association with emission databases. However, it also shows that quantifying carbon is not sufficient to guide lower-impact decisions. The central gap lies in transforming measurement into a decision-making process by connecting calculation to mechanisms for exploring alternatives, multicriteria analysis, trade-offs, and verifiable recommendations.
3.2.4. AI + CO2
The AI + CO2 axis brings together studies in which artificial intelligence is directly applied to estimate, predict, optimize, or support decisions related to carbon emissions, even when BIM is not the central element of the process. These studies contribute to the review by highlighting the potential of AI as an analytical layer for carbon, especially in terms of calculation speed, predictive capacity, and decision support. However, because they are not structured within a BIM environment, they provide lower traceability between estimated emissions, building components, quantities, and design alternatives.
As shown in
Figure 9, the studies were organized into two macro-objectives: CO
2 prediction and estimation [
93,
94,
95,
96], and CO
2-oriented optimization and decision support [
97,
98,
99,
100]. This distribution shows that the axis is concentrated around two main AI functions: accelerating emission quantification and supporting choices aimed at carbon reduction.
In the first macro-objective, AI is used as a predictive model to estimate CO
2 based on variables such as building attributes, materials, construction data, energy consumption, and urban variables. The focus is on accelerating quantification and enabling rapid analyses, rather than optimizing alternatives. This group includes studies ranging from national-scale analyses with millions of records and robust statistical validation [
93] to applications with smaller datasets, between 100 and 260 samples [
96], or simulation-based studies, which support prototyping but limit generalization [
95].
Some studies also test LLMs as assistants for reasoning, rapid feedback, and support for emission estimation [
94]. The results indicate satisfactory textual performance in simpler tasks, but limitations in complex topics, formulas, theoretical foundations, and data updating. Thus, LLMs may support the interpretation and communication of carbon estimates, but they do not replace verified databases, transparent methods, and technical validation.
The main contribution of this macro-objective is to demonstrate that AI can reduce estimation time and expand the scale of emission analysis. However, these predictions strongly depend on data quality, including occupancy, climate, typology, energy source, and emission factors. In addition, without a direct link to BIM models, they tend to operate at an aggregated level or outside the design process, making it difficult to associate results with specific elements, materials, construction systems, or design alternatives.
In the second macro-objective, AI acts as a decision, optimization, and control engine, with applications focused on the optimization of cementitious materials, concrete, and reinforcement ratios [
97,
98,
99], as well as operational control strategies in buildings [
100]. In the studies on materials, decisions occur at the pre-conception stage and involve input selection, mix design, and embodied CO
2 assessment. In the operational case, CO
2 is estimated from electricity consumption, with a focus on comfort and energy efficiency.
Taken together, the studies show that approaches based on multi-objective optimization and surrogate models can reduce emissions and costs while preserving technical requirements. The applications include optimal concrete mixes by strength class, Pareto fronts relating cost, embodied CO2, and characteristic strength, structural optimization of beams with reductions in materials, cost, and emissions, and operational control strategies to improve comfort and efficiency. This group demonstrates that AI can support carbon-related decisions when the problem is formalized through clear variables, constraints, and objective functions. However, without BIM integration, the optimized solution tends to remain disconnected from components, quantities, construction details, and traceable changes in the digital model.
Figure 10 presents the life cycle boundaries adopted in the studies within the AI + CO
2 axis. Unlike the BIM + CO
2 axis, no approaches with full LCA integration were identified. The studies are distributed between embodied and operational carbon: three adopt A1–A3, focusing on the production of materials and components; three focus exclusively on B6, related to operational emissions derived from energy consumption; one expands the scope to B1–B6, including use-stage phases beyond energy; and one uses emission factors as part of an LLM test, without explicit boundary standardization.
This distribution reveals an important limitation of the axis: although AI is directly applied to carbon, the boundaries remain fragmented between embodied and operational carbon. As a result, predictions or recommendations based on A1–A3 tend to support decisions on materials and mix designs, whereas B6-centered models respond to decisions related to operation, energy, and control. Therefore, the comparability of results depends on the explicit definition of the boundaries, emission factors, and use assumptions adopted in each study.
The studies also report limitations related to the need for experimental validation, data representativeness, and the incorporation of more realistic variables for operational carbon, such as dynamic occupancy, user behavior, climatic conditions, and more accurate emission factors. In summary, the AI + CO2 axis demonstrates that artificial intelligence already has relevant capacity to estimate, predict, optimize, and support decisions related to emissions, especially when structured datasets, well-defined objective functions, and measurable technical criteria are available. However, because it operates mostly outside the BIM environment, this axis still does not close the loop between carbon calculation, digital model, and design decision-making. Its main contribution to BIM–CO2–AI integration is to demonstrate the analytical potential of AI applied to carbon; its central gap lies in connecting this potential to BIM workflows capable of ensuring traceability, interoperability, validation, and direct application to verifiable design alternatives.
3.2.5. Core Studies
Because Core studies represent the integration directly aligned with the research question, they were comparatively analyzed in terms of how BIM, CO
2 calculation, and AI are articulated to support design decisions.
Table 5 summarizes the eight studies classified in this axis, highlighting the type of integration, the supported decision, and the main methodological limitation. An expanded matrix, with additional details on tools, life cycle boundaries, AI techniques, and validation, is presented in
Appendix D.
The comparison of Core studies shows that BIM + CO2 + AI integration already presents promising applications but still occurs in a heterogeneous and predominantly modular manner. In general, BIM provides geometry, quantities, parameters, or semantic data; CO2 calculation is performed through energy simulations, LCA tools, emission factors, or custom calculations; and AI acts as a layer for prediction, optimization, explainability, generation, or recommendation. Even in the most advanced studies, recurring limitations remain, such as incomplete life cycle boundaries, restricted validation, dependence on external modules, absence of automatic feedback to BIM, and difficulty in simultaneously incorporating carbon, cost, comfort, technical performance, and qualitative design criteria. Thus, the Core axis confirms that BIM → CO2 → AI convergence is under consolidation, but still requires greater standardization, validation, and operational integration to support robust lower-impact design decisions.
The Core studies were organized into three macro-objectives, as shown in
Figure 11: (i) generation of design alternatives with CO
2 assessment and optimization; (ii) operational performance optimization focused on CO
2 reduction; and (iii) structural optimization aimed at CO
2 reduction. These objectives represent the applications closest to the key research question of this review, as they articulate, to varying degrees, BIM, carbon calculation, and AI techniques to support design or performance decisions.
In the assessment and optimization group [
101,
102,
103,
104], BIM acts as a parametric environment, a source of quantities, and a support for creating or assessing alternatives. The main advancement of these studies lies in shifting carbon from a late-stage diagnostic metric to a variable considered during design conception, allowing emissions, materials, geometry, performance, and, in some cases, costs to be analyzed before the design is consolidated.
In this stream, AI appears mainly in three forms: multi-objective optimization algorithms, generative/parametric systems, and, more recently, LLMs or knowledge-based models to support querying, recommendation, and requirement capture. The studies show that it is possible to generate alternatives, calculate impacts, and compare solutions through Pareto fronts, predictive models, or recommender systems. The BIM-IGL framework [
101], for example, integrates layout generation, hybrid LCA, and impact visualization in BIM, enabling alternatives to be selected based on environmental and performance criteria. Applications using IFC, material databases, and LLMs also demonstrate potential to support the selection of lower-carbon materials, but they also reveal risks of technically inadequate recommendations when there is no grounding in domain knowledge, human validation, or verification mechanisms.
The empirical results of this group indicate relevant contributions, although they remain concentrated in prototypes, case studies, or specific scopes. One study [
102] enabled the selection of alternatives through a Pareto front, with visualization of impacts in the BIM model. Another [
104] combined BIM/IFC/CDE, LLM + KGQA/RAG, Random Forest, and multi-objective optimization, reporting reductions in energy consumption, cost, carbon, and preliminary modeling time. In high-rise buildings [
103], generative design was applied to reduce embodied emissions during the conceptual phase, although with relevant exclusions, such as foundations, operational carbon, and complete structural checks. Therefore, the contribution of this group lies less in offering universally applicable solutions and more in demonstrating promising methodological architectures for integrating alternative generation, environmental assessment, and decision-making.
The second macro-objective focuses on operational performance optimization aimed at CO
2 reduction [
105,
106]. Unlike the first group, these studies mainly treat carbon as a result of energy consumption during the use phase, approaching the B6 life cycle boundary. The workflows generally start from BIM models in Revit, exported via gbXML to DesignBuilder/EnergyPlus, generating simulations that feed predictive models, XAI techniques such as SHAP or LIME, and multi-objective optimization algorithms such as AGE-MOEA. This arrangement reduces dependence on repetitive simulations and allows alternatives to be explored with greater computational speed. In some cases, the studies also report accuracy metrics, creation of Pareto fronts, and uncertainty treatment through Monte Carlo simulation.
Despite their technical robustness, these studies reveal important limits in relation to the question of this review. CO2 calculation remains restricted to operational carbon, without integration with embodied carbon or full LCA; ML, XAI, and optimization modules are mostly executed outside the BIM environment; and validation is mainly based on case studies and simulations, with little evidence of comparison with monitored real-world operational data. Thus, this macro-objective demonstrates a consistent pathway for transforming operational CO2 into a decision variable, but it still does not fully close the loop between BIM, AI-based prediction, recommendation, and automated feedback to the design process.
The third macro-objective brings together studies on structural optimization aimed at CO
2 reduction [
107,
108]. This stream differs from the previous ones because it deals with domains in which the relationship between technical decisions, material consumption, and embodied carbon is more direct. In steel structures, trusses, reinforcement, and reinforced concrete elements, variables such as weight, section, length, waste, splices, and steel consumption can be converted into carbon indicators with greater objectivity than in more subjective architectural problems.
In this group, BIM functions as a source of geometric data, quantities, and technical specifications, while evolutionary algorithms or metaheuristics search for solutions with lower material consumption, waste, cost, or emissions. One study [
108] combines Dynamo, Robot Structural Analysis, a genetic algorithm, Revit, and Tally to optimize structural weight and subsequently assess GWP/CO
2e. However, in this case, carbon still appears as LCA post-processing, rather than as an objective directly incorporated into the optimization loop. Another study [
107], applied to diaphragm walls in urban infrastructure, uses BIM/Revit data and Python to optimize rebar, couplers, cutting patterns, cost, waste, and embodied carbon, demonstrating how decisions at the detailing and production-engineering level can reduce emissions with practical implications for the construction site and supply chain.
The contribution of this stream lies in showing that BIM + CO2 + AI integration can generate practical gains when the problem can be formalized through objective and verifiable variables. However, it also reveals an important limitation: carbon is not always incorporated as an objective function from the beginning. In some cases, AI optimizes weight, geometry, or material consumption, and carbon is assessed only afterward. This gap indicates the need to integrate carbon directly into objective functions, together with cost, structural performance, constructability, and waste.
Regarding life cycle boundaries,
Figure 12 shows that even Core studies remain segmented between embodied and operational carbon. Among the eight articles, three are restricted to A1–A3, one combines A1–A3 + B1–B5, one adopts A1–A5, one uses A1–A3 + B1–B6, and two focus exclusively on B6.
This result is methodologically relevant because it demonstrates that BIM + CO2 + AI convergence does not occur homogeneously. When the focus is on embodied carbon, the challenges involve inventory, materials, quantities, emission factors, and LCA boundaries. When the focus is on operational carbon, the challenges involve energy simulation, climate data, use behavior, calibration, and validation with real data. Therefore, AI recommendations based on different boundaries are not directly comparable, and future studies should clarify from the outset whether AI supports decisions related to embodied carbon, operational carbon, or combined assessments.
In summary, the Core studies show that BIM + CO2 + AI integration has already moved beyond the purely conceptual stage but has not yet reached full methodological and operational maturity. The field presents promising prototypes and frameworks, especially in alternative generation, metamodeling, XAI, multi-objective optimization, LLMs, and IFC/CDE integration. However, practical consolidation depends on advances in five areas: standardization of carbon boundaries, quality and interoperability of BIM data, direct integration of carbon into decision functions, validation in real cases, and verification mechanisms for AI-generated recommendations.
3.3. Critical Barriers and Implications for BIM–CO2–AI Workflows in Low-Carbon Design Decisions
The joint analysis of the thematic axes shows that the integration of BIM, CO2 calculation, and AI should not be understood as a single or fully consolidated solution, but rather as the progressive articulation of distinct methodological layers. BIM + AI studies show maturity in automation, optimization, generative modeling, and semantic interaction; BIM + CO2 studies consolidate quantity extraction, linkage to emission factors, and inventory automation; BIM + AI + Sustainability studies show the application of AI to energy, comfort, lighting, and retrofit; and AI + CO2 studies demonstrate the potential of predictive models and optimization algorithms applied directly to carbon. However, only the Core studies approach the full convergence investigated in this review, although still in a restricted, modular manner and requiring further validation.
This cross-cutting reading indicates that the central gap in the field does not lie in the isolated absence of BIM, CO
2, or AI, but in the difficulty of integrating them into a continuous decision-making workflow. In many studies [
101,
105,
106,
107,
108], BIM provides geometry, quantities, or parameters; CO
2 calculation occurs in LCA software, energy simulations, external databases, or spreadsheets; and AI subsequently acts as a layer for prediction, optimization, explanation, or recommendation. This arrangement enables important advances, but it creates points of fragility between stages, such as data export, semantic loss, parameter inconsistency, incompatibility between formats, absence of automatic feedback of solutions to the model, and difficulty in tracing how a recommendation was produced. Thus, the automation observed in the literature does not always represent full integration but often a sequence of semi-integrated processes that depend on model quality, interoperability between tools, and user validation.
A critical barrier concerns life cycle boundaries and the comparability of results. Studies focused on embodied carbon, especially A1–A3 or A1–A5, tend to support decisions related to materials, construction systems, geometry, structure, and quantities. Studies centered on operational carbon, especially B6, guide decisions related to energy, comfort, HVAC, envelope, and use scenarios. Since each boundary mobilizes different data, assumptions, emission factors, and validation procedures, AI-generated recommendations based on different scopes are not directly comparable [
103,
105,
106]. This limitation is reinforced by BIM + CO
2 studies that identify relevant divergences between databases and calculation procedures, indicating that direct comparisons require rigorous standardization of boundaries, emission factors, and mapping methods between BIM inventory and environmental data [
83,
85].
Another cross-cutting limitation concerns data quality and governance. The reliability of BIM–CO
2–AI workflows depends on the consistency of BIM objects, the level of information available, the correct classification of materials and elements, the appropriate association between quantities and emission factors, and the transparency of the databases used. When these elements are not standardized, AI may merely accelerate decisions based on fragile data. This limitation appears especially in predictive models trained with small datasets or datasets derived from specific simulations, in algorithms dependent on simplified objective functions, and in recommender systems based on incomplete material databases or parameters [
101,
105]. Therefore, the quality of automated decision-making depends not only on the algorithm but also on the reliability of the entire information chain that connects BIM, inventory, environmental calculation, interpretation of results, and validation of recommendations.
The discussion also shows that low-carbon design cannot be reduced to the isolated minimization of emissions. Real design decisions involve trade-offs among carbon, cost, energy performance, thermal comfort, structural performance, material availability, constructability, maintenance, regulatory requirements, and architectural quality. Some Core studies advance in this direction using Pareto fronts, multi-objective optimization, predictive metamodels, XAI, or LLMs to compare alternatives [
103,
104,
105,
106,
107,
108]. However, many workflows still simplify decision criteria or treat carbon as post-processing rather than as a function integrated from the beginning of optimization. Thus, the future contribution of BIM–CO
2–AI integration lies less in producing a single “optimal” result and more in making explicit the compromises among alternatives, allowing designers to understand why a solution reduces carbon, what costs or losses are associated with it, and which technical constraints must be observed.
The use of LLMs and natural-language interfaces expands the possibilities for querying, interpretation, and recommendation in BIM–CO
2–AI workflows [
101,
104]. These tools can synthesize information, suggest materials, and facilitate user interaction with technical databases, but they also introduce risks when they are not grounded in reliable data, standards, material databases, and verification mechanisms. Therefore, LLM-based applications should be treated as decision-support tools, not as substitutes for technical validation. In low-carbon workflows, AI-generated recommendations must be verifiable, traceable, and accompanied by human-in-the-loop mechanisms, especially when they involve safety, structural performance, comfort, cost, or regulatory compliance.
From the perspective of professional practice in the AECO sector, the results indicate that the adoption of BIM–CO2–AI workflows depends on conditions that go beyond tool availability. Their implementation requires standardized BIM processes, trained teams, interoperability between platforms, reliable and context-specific carbon databases, clear responsibilities regarding data and validation, and objective criteria for interpreting automated recommendations. Adoption may also be limited by factors such as computational cost, model preparation, information coordination, and integration with real design routines. Thus, the transition from academic prototypes to professional applications requires frameworks that are not only technically sophisticated, but also auditable, understandable, replicable, and compatible with designers’ workflows.
In this sense, the broader BIM and digital twin literature reinforces that BIM–CO
2–AI workflows should be evaluated not only by their computational performance but also by their capacity to support integration across stakeholders, life cycle stages, and value chains [
12,
13,
14,
18,
19]. In practice, low-carbon decision-making requires coordination among designers, engineers, contractors, suppliers, facility managers, owners, and, in some cases, demolition and reuse actors. This reinforces the need to connect carbon quantification with circularity-related information, material traceability, value-chain data, operational feedback, and life cycle-oriented decision processes [
15,
16,
17,
18,
19]. Therefore, future BIM–CO
2–AI frameworks should move beyond isolated model-based calculations and in-corporate stronger links with digital twin principles, Common Data Environments, stakeholder engagement mechanisms, circular economy strategies, and value/benefit assessment across the building life cycle [
12,
18,
19,
20].
In summary, the cross-cutting contribution of this review is to demonstrate that BIM–CO2–AI integration should be assessed according to the degree to which it connects five dimensions: BIM data quality, transparent delimitation of carbon calculation, level of automation, effective AI function, and capacity to support design decisions. The literature analyzed presents relevant advances in each dimension, but few studies manage to articulate them fully. The central challenge for future research is not only to automate CO2 calculation or apply AI to BIM models, but to consolidate verifiable, interoperable, and technically validated workflows in which design alternatives are generated, environmentally assessed, compared through multiple criteria, and reintegrated into the decision-making process in a transparent manner.
The application of the N1–N5 scale reveals asymmetric maturity among the BIM-based axes. The BIM + CO2 axis is mostly concentrated at N3, with 21 studies, indicating that BIM-based environmental automation has already advanced beyond simple data extraction or manual/semi-assisted calculation. In this group, maturity lies mainly in inventory structuring, the linkage between model and emission factors, and the operationalization of environmental calculation. By contrast, the BIM + AI axis, with 22 N4 studies and 12 N5 studies, presents higher maturity in the computational layer, especially in optimization, machine learning, generative systems, LLMs, and recommendation.
The BIM + AI + Sustainability axis, with 12 N4 studies, occupies a relevant intermediate position, as it demonstrates that BIM and AI are already combined in environmental workflows oriented toward energy, comfort, lighting, and retrofit. In Core studies, the concentration at N4 and N5, with six N4 studies and two N5 studies, shows that full BIM + CO2 + AI integration has already reached high levels of automation but remains limited in scope. Thus, the N1–N5 scale confirms that the central gap is not the absence of isolated technical capabilities but the difficulty of articulating, within the same workflow, carbon inventory, computational intelligence, interoperability, validation, and effective support for design decision-making.
Based on this cross-cutting analysis, a conceptual framework is proposed to synthesize the layers required for BIM–CO
2–AI integration in lower-impact design decisions. This framework does not represent a fully consolidated workflow in the literature but rather an analytical structure derived from the patterns and gaps identified in this review. As shown in
Figure 13, integration begins with BIM model data, advances to environmental quantification through emission factors, carbon databases, and life cycle boundaries, depends on automation and interoperability mechanisms to connect tools, incorporates AI methods for prediction, explanation, optimization, and recommendation, and culminates in the comparison of design alternatives with human validation.
This representation reinforces that the main challenge is not only to automate CO2 calculation or apply AI to BIM, but to ensure continuity, traceability, and reliability throughout the entire workflow. Thus, BIM data quality, consistency of LCA boundaries, transparency of carbon databases, validation of AI models, and human verification of recommendations are critical conditions for automated calculation to move beyond a quantification step and effectively support robust design decisions.
The cross-cutting analysis of the studies also makes it possible to identify which design and operation aspects have most frequently been supported by integrations between BIM, CO
2, AI, and sustainability.
Table 6 synthesizes these aspects without treating the axes as equivalent but indicating how each group contributes to decisions with potential links to environmental performance and low carbon.
Taken together, these aspects show that low-carbon decision support is not limited to material selection or emission calculation. The analyzed integrations already reach different layers of design, such as form, envelope, structure, energy, cost, retrofit, and circularity. However, the simultaneous articulation of these criteria remains limited, indicating that the main opportunity for future research lies in developing multicriteria workflows capable of integrating embodied carbon, operational carbon, technical performance, economic feasibility, and validation of recommendations within the same decision-making process.