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Purpose

Despite the growing interest in tools for designing-out construction and demolition waste (DoC&DW), information needs associated with these tools remain underexplored. This study aims to identify the information needs of the tools for DoC&DW to streamline the waste minimisation process at the design stage.

Design/methodology/approach

A systematic literature review (SLR) was conducted using the PRISMA method, analysing 46 peer-reviewed articles published between 2004 and 2024. The selected articles underwent descriptive and thematic analysis.

Findings

The study highlights the increasing adoption of BIM-enabled tools for DoC&DW, recognised for their automation, robust databases, and interoperability. The information needs of these tools were categorised using the input-process-output (IPO) model. A conceptual framework was proposed to map the BIM-enabled architecture to the IPO model, distinguishing input, process, and output information aligning with designing-out waste (DoW) principle. This provides a foundation for future development of BIM-enabled tools to predict and manage waste at the design stage.

Originality/value

This study is the first of its kind to map input, process, and output information needs relating to identified BIM-enabled tools for DoC&DW, aligned with each DoW principle. Unlike previous studies that focus on the functionalities of the tools or technology applications, this study uniquely and holistically maps information requirements across IPO model and proposed a conceptual framework that clarifies the information architecture needed to support DoW principles. This facilitates the specific information needs and standardisation of the development of new tools for DoC&DW, enabling informed decision-making, enhanced resource efficiency and contributes to sustainability in the built environment.

The construction industry significantly contributes to economic growth and employment but also drives environmental challenges due to rapid urbanisation and resource consumption. It accounts for 40% of global raw materials use and energy consumption leading to resource depletion, pollution and greenhouse gas emissions (Illankoon and Vithanage, 2023). Additionally, it is the largest waste generator, producing 30% of global waste with over 35% ending up in landfills annually (Eze et al., 2024). These impacts not only intensify environmental degradation but also impose economic and social costs, including waste management expenses and health risk (Amaral et al., 2020; Hosseini et al., 2020).

Understanding the types of construction waste is essential for effective minimisation strategies. Lean construction identifies key wastes such as motion, inventory, waiting, overproduction, unused employee knowledge, transportation, and defects (Unnikrishnan and Sudhakumar, 2024). However, the interconnected nature of the two main types of waste, Construction and Demolition Waste (C&DW), necessitates integrated management strategies, as decisions made during construction directly affect both the volume and recycling potential of demolition waste (Nikmehr et al., 2021). During construction phases, waste generation occurs through material inefficiencies, design modifications, and inadequate planning, while demolition contributes substantially to overall waste streams at the end-of-life stage. Moreover, optimising material use throughout all construction stages, including demolition, provides a powerful sustainability strategy by enhancing resource efficiency and reducing environmental impact (WRAP, 2021)

Waste prevention is prioritised in sustainable management, as reflected in the European Union (EU) waste hierarchy; prevent, reuse, recycle, downcycle, landfill (Zhang et al., 2022). Yet, design inefficiencies contribute to 30% of on-site waste (Amaral et al., 2020) often due to poor planning, lack of procedures, and insufficient information for decision-making (Hassan and Alashwal, 2025). Addressing waste during the design phase offers the greatest potential for efficiency and minimal environmental impact (Ghafourian et al., 2016).

Designing out Waste (DoW) is a waste-specific strategy aligned with Circular Economy (CE) principles, focussing on minimising waste at early design stages through predictive and prescriptive approaches (Tong et al., 2024). In contrast, Design for X (DfX) is broader, addressing goals where “X” may refer to manufacturability, cost, quality, or sustainability (Narganes-Pineda et al., 2025). The Waste and Resources Action Programme (WRAP) outlines five DoW principles such as Design for reuse and recycle; Design for off-site construction; Design for material optimisation; Design for resource-efficient procurement; Design for Deconstruction’ and flexibility (WRAP, 2021). These principles are interconnected. The “Design for waste-efficient procurement” approach emphasises collaboration among project stakeholders. “Design for material optimisation” advocates for standardised, recyclable materials, while design for off-site construction promotes prefabricated modules over traditional on-site methods (Utrilla et al., 2020). “Design for Deconstruction” emphasises adaptability, reusability and recycling of materials, encouraging the recovery of materials for future projects (Kelly and Dowd, 2014).Effective decision-making mechanisms during design are crucial to minimise waste caused by design changes (Ajayi et al., 2016; Kelly and Dowd, 2014).

Existing C&DW tools such as SMARTWaste, SWMP, DoWT-B, and SmartAudit provide design guides and checklists but are often applied post-design, limiting waste mitigation at early-stages (Gupta et al., 2022; Mcneil-Ayuk and Jrade, 2024). To address this, tools are increasingly adopted to manage project information at early design stages in line with DoW principles, promoting material reuse and recycling (Tong et al., 2024). Building Information Modelling (BIM) is often identified as a tool to forecast potential waste and supports Design for Disassembly (DfD) (Akbarieh et al., 2020; Mcneil-Ayuk and Jrade, 2024; Susilowati et al., 2024; Dias et al. (2022). Other tools, such as Life Cycle Assessment (LCA), evaluate reusability, recyclability, and energy efficiency at the design phase (Gomis et al., 2023; Kahandawa et al., 2025). Several reviews examine the current state of C&DW minimisation, as shown in Table 1.

According to Table 1, these reviews highlight current literature, tools for measuring waste generation, and gaps in integrating DoW principles in designing out construction and demolition waste (DoC&DW) (Amaral et al., 2020; Majmundar and Ansari, 2018). Ghafourian et al. (2016) noted that C&DW management is not prioritised during the design stage, and few studies focus on waste minimisation at this phase (Mahinkanda et al., 2023; Tong et al., 2024). Recent studies by Nikmehr et al. (2021), Mrema et al. (2023) emphasise the role of BIM in DoC&DW including DfD, and its ability to manage waste during design and construction. BIM is central in limited studies exploring DoW at the design phase (Nawaz et al., 2023; Nikmehr et al., 2021). Integrating technologies like BIM and big data improves decision-making and collaboration (Mahinkanda et al., 2023). While Susilowati et al. (2024) provide a conceptual framework for “Designing Out Waste”, they do not address the tools or specific information requirements needed for implementation. Dias et al. (2022) stress the need for clear and comprehensive information. Existing reviews lack a thorough analysis of information needs in tools supporting DoC&DW aligned with DoW principles, hindering development of a holistic information architecture for waste management (Tong et al., 2024). The research question of this study is:

What are the information needs of the tools for support the designing-out Construction and Demolition Waste (DoC&DW) during the design stage?

To address this gap, a systematic literature review (SLR) was conducted to explore existing tools and their potential information configurations to identify the information needs of the tools for DoC&DW. The IPO model (MacCuspie et al., 2014) offers a structured approach to understanding the information configuration of tools for DoC&DW and supports benchmarking to facilitate circular economy. Accordingly, this paper adapts the IPO model to develop a conceptual framework for the information needs of the tools for DoC&DW. The paper is organised as follows: Section 2 presents the SLR methodology; Section 3 shows descriptive and thematic analyses identifying IPO information in tools; Section 4 discusses BIM-enabled information needs; Section 5 develops the conceptual framework; and Section 6 concludes with future research directions.

This study employs a SLR to critically evaluate existing knowledge and uses content analysis to synthesise novel concepts and provides insights into literature patterns (Fink, 2019). Descriptive analysis, including keyword co-occurrence, was conducted using VOSviewer (Jin et al., 2019). The SLR follows the PRISMA framework, comprising four phases: identification, screening, eligibility, and inclusion, as illustrated in Figure 1.

Based on the defined scope in Section 1, a keyword search was conducted targeting tools for DoC&DW in Scopus and Web of Science which are commonly used, the largest repositories of engineering research (Ali et al., 2017; Mostafa et al., 2016) focussing on titles, abstracts, and keywords.

((“Design*” AND “Waste”) AND (“Deconstruct*” OR “reus*” OR “recycl*”)) AND ((“Technolog*” OR “Tool*” OR “Database*” OR “Prototype*” OR “Architecture*” OR “Platform*” OR “Model*” OR “Framework*” OR “Strateg*” OR “analytic*”)) AND ((“Construction” OR “Demolition”) AND (“Waste”))).

The search included peer-reviewed journal articles to ensure high-quality, relevant information from 2004 to 2024 to capture the evolution of existing tools for DoC&DW, including use of BIM, in embracing DoW principles. Although the initial search targeted publications from 2000, as identified by Tong et al. (2024) and Susilowati et al. (2024) as the period when early discussions on the DoW concept and decision support tools began, the first publication relevant to the specific scope of this review appeared in 2004. Publications from 2025 are still ongoing, thus, including them would not provide a complete overview. Limiting the scope to 2024 ensures a full, consistent dataset for a robust analysis.

The quality of the selected articles was ensured through inclusion and exclusion criteria. Duplicates, non-English publications, books, book chapters, conference papers, and review articles were excluded to reduce bias (Wijewickrama et al., 2021; Tong et al., 2024). Inclusion criteria focused on studies addressing tools for DoC&DW. Studies unrelated to DoW and C&DW other domains such as green logistics, supply chain management, disaster response, and sectors like automation, agriculture, and manufacturing were excluded, to improve the reliability and relevance of the synthesised evidence (Mahinkanda et al., 2023). Out of 778 abstracts, 99 were selected for full-text review, resulting in 46 final articles ( Appendix Table A1).

The selected articles were subjected to descriptive and thematic analysis. Descriptive analysis examined publication year, co-occurrence of keywords, while thematic analysis provided an in-depth review of key topics (Liberati et al., 2009). To minimise potential bias and enhance reliability in the thematic analysis, the selected articles were independently reviewed and analysed by the first author, followed by collaborative discussions among all authors to refine and finalise the themes and content aligned with Wijewickrama et al. (2021) to ensure the robustness and reliability of their analysis.

The descriptive analysis categorises selected articles by publication year and keywords. Figure 2 illustrates the distribution of studies on tools for DoC&DW from 2004 to 2024.

Figure 2 shows a gradual rise in publications, with peaks in certain years. Between 2004 and 2016, research was limited, focussing on waste minimisation without modelling perspectives. From 2017 onward, publications increased, with over 80% published in the last decade. The highest peak was in 2019, reflecting growing interest in DoW and BIM. These trends highlight information needs of tools for DoC&DW, supporting sustainable waste reduction.

Keywordsco-occurrence analysis (Figure 3) was performed using “Author Keywords” and “Fractional Counting” via VOSViewer, which provided key insights into research themes (Hosseini et al., 2018; van Eck and Waltman, 2014).

The keyword occurrence threshold was set at two, identifying 25 of 124 keywords. Similar terms like “BIM” and “Building Information Modelling” were merged, resulting in 21 final keywords. In Figure 3, node size, distance, and connecting lines indicate the most frequent topics, including BIM, Waste Management, DfD, and C&DW. Nodes colours divide the keywords into clusters:

  1. Aspects of DoC&DW: strategies like “DfD”, LCA, and material reuse.

  2. Basic waste management strategies and mechanisms: from disposal to recycling, reuse, and reduction, with recycling as the primary diversion

  3. C&DW minimisation: links between construction activities and waste, emphasising demolition waste prediction.

  4. Emerging technologies: BIM and BIM and big data to enhance efficiency via design review, 3D coordination, quantity take-off, and analytics.

The thematic analysis uses the IPO model (MacCuspie et al., 2014) to classify and synthesise the information needs of tools for DoC&DW, organising findings under three stages: Inputs, Processes, and outputs.

Inputs are characterised as requirements from the environment (Bushnell, 1990). Table 2 outlines input classifications, types of data, and potential sources.

“Design specifications” consistently emerge as critical inputs, encompassing project-level attributes such as number of floors, gross floor area, building height, and typology; and element-level attributes such as dimensions, density, material type, lifespan. These underpin waste estimation and recovery, with key sources being architectural/structural drawing, BIM models, and structural calculations (Kunieda et al., 2019). “Material properties” align closely with design specifications. Akinade and Oyedele (2019) identified parameters such as thickness, length, width, and surface area, while Haeusler et al. (2021) noted sources like manufacturer databases and BIM. Keulemans and Adams (2024) demonstrated BIM metadata can enhance waste visualisation by adding historical, ecological, and material quality information to support contextual and sustainability insights. “Economic indicators” though less studied include costs of treatment, transport, and disposal of C&DW (Akinade and Oyedele, 2019) sourced from cost databases and market records which allow for the integration of financial feasibility into tools for DoC&DW (Yeheyis et al., 2013). “C&DW information,” spans waste typology, volumes, and generation data, often derived from audits and historical records but limited by post-design uncertainties (Bilal et al., 2016; Zubair et al., 2024). “Environmental impact categories” and “Life cycle parameters” draw on databases or Environmental Product Declarations, which assess the environmental impact of construction materials. “Social indicators” reflect stakeholder acceptance, participation, and safety in DoC&DW approaches, typically gathered from stakeholder consultations and regulatory requirements (Sanchez et al., 2021; Lu and Yuan, 2010).

Mostly employed information processing systems for tools supporting DoC&DW are BIM-enabled (70%). BIM-enabled tools rely on BIM objects (digital representations of building components such as walls, doors, and beams) embedded with geometric and parametric data (material properties, dimensions and lifecycle performance), and parametric modelling. Parametric modelling enabling real-time, rule-based design analysis and adjustments. These operate across a multi-layered architecture:

Data storage layer: Collects and organises scattered datasets, ensuring accessibility and machine readability. Features include integration and classification systems, real-time data findability, handling of large datasets, and semantic search (Bilal et al., 2016; Akanbi et al., 2019). Semantic layer: Provides access to databases for upper layers. Ontologies enhance this layer by structuring domain knowledge, describing data sources, and enabling advanced queries (Lu et al., 2017). Analytics and functional model layer: Execute core functions such as Whole Life Performance Analytics, Deconstruction Analytics, DfD and visualisation. Algorithms within this layer assess reuse potential, recyclability, and optimal deconstruction strategy (Akanbi et al., 2019; Bilal et al., 2017). Application layer: Provides web/mobile-based user interfaces for visualisation, reporting, and waste analysis (Akanbi et al., 2019; Chileshe et al., 2019), to identify waste hotspots and optimise reprocessing opportunities.

In practice, BIM-enabled tools often use platforms such as Revit, plug-ins to support DoC&DW across project stages, e.g: optimising reinforcement bars, planning off-site construction, and facilitating reuse and deconstruction strategies (Akinade and Oyedele, 2019; Han et al., 2024; Khondoker, 2021; Porwal and Hewage, 2012; Yuan et al., 2022). Llatas et al. (2022) and Zubair et al. (2024) demonstrate the use of BIM-enabled LCA to assess environmental impacts of construction waste and building projects. Both studies show how integrating BIM (and GIS, in Zubair et al., 2024) can support early-stage design decisions, optimise waste management, and provide a holistic evaluation of sustainability in construction.

Mathematical modelling was employed by 15%, which supports assessment scores, waste reduction, and C&DW recycling optimisation (Ekanayake and Ofori, 2004; Sassi, 2008; Hiete et al., 2011; Llatas and Osmani, 2016; Seeboo, 2022). For example, Akanbi et al. (2019) introduced Disassembly and Deconstruction Analytics System (D-DAS) to evaluate building components for reuse and recycling. Building on this foundation, Mohammed et al. (2024) integrated a mathematical model within BIM for steel structures, introducing deconstructability and salvage metrics considering deterioration and reuse potential. Ekanayake and Ofori (2004) applied multi-attribute value techniques to create a waste assessment score, while Llatas and Osmani (2016), developed a waste reduction model simulating DoC&DW. A few used “simulations” (9%) process to enhance demolition efficiency and material sortability (Kunieda et al., 2019; Eckelman et al., 2018; Sadafi et al., 2012). Sadafi et al. (2012) integrated simulation with LCA for DfD structural system.

The outputs of the selected studies were categorised based on their nature of the output and alignment with waste management hierarchy. Table 3 illustrates output, with 48% focussing on analysing DoC&DW principles, including deconstructability, recovery potential, health impacts, and demolition strategies (Akinade and Oyedele, 2019; Ge et al., 2017; Zubair et al., 2024).

Quantitative Measures (35%) emphasise numerical data to validate DoC&DW (Bilal et al., 2016; Ge et al., 2017). For example, Akanbi et al. (2019) and Mohammed et al. (2024), evaluated salvage performance, quantifying the potential for component reuse at the end of life. Quality of Material (13%) assesses material condition affecting end-of-life impact, while 3% focus on BIM-enabled material/component banks/databases (Jayasinghe and Waldmann, 2020; Keulemans and Adams, 2024; Lima et al., 2023).

Table 3 shows that Reuse (36%) and Reduce (29%) are the primary focus area, reflecting principles like Design for off-site construction and DfD to minimise waste and extend material life (Lu et al., 2017; Mei et al., 2021; Xiao et al., 2023; Keulemans and Adams, 2024). Recycling (22%) highlights the efforts for design for recyclability (Akinade and Oyedele, 2019; Llatas et al., 2022; Xia et al., 2020). Few studies combined reduce, reuse, and recycle strategies for a holistic DoC&DW approach DoC&DW (Seeboo, 2022; Basta et al., 2020; Mayer and Bechthold, 2017).

The descriptive analysis reveals significant insights into the evolution and maturation of DoC&DW research over the past 2 decades. Between 2004–2016, research activity on C&DW was limited and intermittent, suggesting that early approaches were largely reactive rather than implementing proactive design strategies (Ajayi et al., 2016; Yuan and Shen, 2011). Keyword network analysis reinforces this evolution, showing a transition from isolated waste management approaches to integrated digital solutions incorporating BIM, big data analytics, and lifecycle thinking (Susilowati et al., 2024; Lins et al., 2024). This trend also reflects the transition of the construction industry from a linear “take-make-dispose” model to a circular approach, embedding waste prevention into the design process (Gomis et al., 2023).

Based on the findings, Table 4 maps the IPO information to DoW principles. Each DoW principle has specific inputs and outputs with a common process at the semantic, analytics and functional model layers. However, depending on the purpose and application of the tool, the process may have a unique architecture.

The mapping reveals distinct information architectures for different DoW principles, indicating that effective tool development requires principle-specific approaches rather than generic solutions. Tools focused on resource-efficient procurement demonstrate the most comprehensive input requirements, utilising life-cycle parameters, material properties, and design specifications to optimise material procurement (Ajayi and Oyedele, 2018). Procurement-focused tools require the highest level of information integration, reflecting the complexity of balancing cost, environmental impact, and availability factors in material selection processes (Tong et al., 2024). For waste-efficient materials, material and design specifications as primary inputs reflect the geometric nature of cutting pattern optimisation and challenges in quantity estimation (Tong et al., 2024). This shows that geometric precision is more critical than lifecycle data, favouring specialised tools (Lins et al., 2024).

Design for reuse and recycling demonstrates unique reliance on C&DW information and social indicators, distinguishing it from other DoW principles through emphasis on stakeholder perspectives and historical waste data (Yeheyis et al., 2013). This indicates that reuse strategies are inherently more social and contextual than purely technical. This highlights the requirement of tools for DoW to integrate community acceptance, regulatory compliance, and cultural factors alongside technical feasibility assessments (Lins et al., 2024; Tong et al., 2024).

Outputs related to materials recovery and alternative design options are generated by creating material or component banks with reliable traceability. Certification ensures reused materials meet standards and perform effectively in new projects (Jayasinghe and Waldmann, 2020; Bertin et al., 2020). Off-site construction tools emphasise material properties, design specifications, and economic factors leading to improved prefabrication and compliance with codes. While prefabrication minimises waste barriers such as transportation cost limit adoption (Wang et al., 2015) which must be addressed to enhance effectiveness. DfD tools rely on design specifications and BIM models, to produce outputs like deconstruction sequences, where selecting materials that facilitate disassembly is crucial (Akinade et al., 2015). Tools related to design for materials consider key information including material properties, design specifications, and life-cycle parameters to optimise material selection, ensuring sustainability and efficiency and identify hazardous materials to reduce health and environmental risks.

BIM plays a crucial role in simulating the building design and fostering collaboration among stakeholders by integrating design, elements, quantities, and material information (Hassan and Alashwal, 2025). Effective information management at the design stage is crucial, as it feeds into multiple sources throughout the project lifecycle (Tedjosaputro, 2024). BIM-enabled information management is widely recognised for implementing the DoC&DW (Akanbi et al., 2019; Khondoker, 2021; Tong et al., 2024). BIM core and auxiliary features support the development of a plug-in for managing C&DW (Bilal et al., 2016). Table 5 maps key BIM features to layers in a BIM-enabled DoC&DW architecture.

The four-layered BIM architecture represents a significant advancement from traditional CAD-based approaches by enabling systematic information processing rather than mere geometric representation. According to Mcneil-Ayuk and Jrade (2024), this architecture facilitates detailed information exchange and interactions between BIM features and DoW principles, providing a structured approach to waste minimisation decision-making. It enables comprehensive information integration across multiple project phases and stakeholder groups (Lins et al., 2024). BIM core features primarily relate to the application layer, enabling plug-in software for waste minimisation and prediction via the Application Programming Interface (API) platform. However, the predominant focus on application-layer functionality indicates that current tools operate as add-ons rather than integrated solutions, potentially limiting their effectiveness in influencing fundamental design decisions (Bilal et al., 2016).

Intelligent modelling supports the semantic layer by providing a unified data platform for external sources enabling integration of diverse data types and sources required for comprehensive waste analysis (Akanbi et al., 2019). Waste analytics integrate waste intelligence and innovative technologies such as GPS and Radio Frequency Identification tags to automate the collection and analysis, reinforcing DoC&DW strategies (Akinade et al., 2018). Parametric modelling within a BIM library demonstrates the most sophisticated approach to waste reduction by enabling rule-based design modifications that automatically optimise waste generation patterns. This capability facilitates the assessment of design elements based on cost, energy consumption, and waste reduction simultaneously, representing the integration of sustainability considerations into design processes (Lu et al., 2017). The analysis reveals that parametric approaches are most effective when combined with comprehensive databases containing project-specific waste generation data, rather than relying on generic industry averages, suggesting that tool effectiveness is directly related to data quality and contextual relevance (Akanbi et al., 2019).

BIM auxiliary features such as design, visualisation, lifestyle considerations, technology, interoperability, and cost-benefit analysis enhance waste analytics and functional modelling by supporting core features of parametric modelling and intelligent modelling (Bertin et al., 2020; Ge et al., 2017). Interoperability facilitates information exchange, enabling effective assessments at the functional layer and ensuring BIM (Revit) platforms remain accessible through API integration (Tong et al., 2024; Lu et al., 2017). The application layer extends BIM functionality through plug-in, leveraged through the analytics and functional model layer. These plug-ins serve as visualisation platforms, assisting designers during the building design process (Akanbi et al., 2019; Bilal et al., 2016; Chileshe et al., 2019).

The SLR confirmed the significance of BIM as a tool for DoC&DW. Bilal et al. (2016) highlighted the reliance of BIM on large datasets makes it highly compatible with big data technologies. This capability allows designers to anticipate waste generation from materials or construction methods improving decision-making. To illustrate this, a conceptual framework (See Figure 4) applies the IPO model to systematically map the information needs of tools for DoC&DW.

The framework aligns information needs with DoW principles, demonstrating how a BIM-enabled architecture supports designers in minimising waste and improving resource efficiency at the early design stage (Tong et al., 2024). In Figure 4, solid arrows indicate information flow, while dashed lines map information needs against DoW principles.

The framework presents a flow diagram, where the critical flow of information begins with inputs linked to DoW principle, including material properties, design specifications, C&DW information, life-cycle parameters, environmental, economic and social indicators. Dias et al. (2022) stressed the need for comprehensive environmental information for effective DoC&DW. Since the framework is BIM-enabled, input information must align with BIM features (Table 5) such as location, gross and net floor area and building typology (Dias et al., 2022; Bilal et al., 2016).

The information processing system, designed based on core BIM functionalities and auxiliary features, ensures effective information handling and seamless integration, thereby reducing the technical limitations and compatibility issues encountered in real-world implementations (Bilal et al., 2016). The semantic layer plays a critical role in structuring and standardising raw data from diverse source (Akanbi et al., 2019). Although the analytics and functional layer enable predictive waste assessment, current implementations tend to emphasise prediction over prescription, offering waste estimates without corresponding design modification recommendations. This limitation reduces the potential of the framework to impact on actual design decisions, indicating that future developments should prioritise actionable guidance over analytical accuracy, particularly in relation to specific DoW principles. This holistic IPO-based framework helps address fragmentation in information needs in tools for DoC&DW. Without industry-wide data standards, the framework's interoperability benefits may remain theoretical; therefore, it should be developed as a BIM-enabled prototype empirically assessed and applied in practice to validate its impact (Dias et al., 2022).

This SLR follows PRISMA guidelines and employs descriptive and thematic analysis to investigate the information needs of the tools for DoC&DW using the IPO model. A total of 46 journal articles published since 2004 were analysed to identify the input, process and output information needs. The review highlights the increasing focus on tools for DoC&DW tools as a key approach to waste minimisation through DoW principles, revealing a paradigm shift from reactive waste management to proactive design intervention. Despite the variety of tools for BIM-enabled approaches stand out reflecting the recognition that effective waste minimisation requires comprehensive integration of information, automation, robust databases, and interoperability across project phases, stakeholders, and decision points. This challenges traditional project delivery methods that treat waste management as post-design rather than a core design driver. Therefore, this review proposes a conceptual framework, holistically mapping the information needs of the tools for DoC&DW based on IPO model. Findings are significant for both practical and theoretical applications, supporting integrated BIM operations to efficiently divert C&DW from landfills and promote sustainable waste minimisation.

The findings provide practical implications for Architects, Engineers, Designers, and Construction managers aiming to minimise C&DW at the design stage. By mapping information needs to the IPO model, BIM-enabled tools provide designers a streamlined approach incorporating waste management strategies into the conceptual design (Mcneil-Ayuk and Jrade, 2024) and actionable insights on material properties, waste generation potential, and reuse or recycling opportunities (Wijewickrama et al., 2021). This enables evidence-based decisions to reduce waste before construction. The framework demonstrates how specific DoW principles can be embedded in BIM-enabled tools. Practitioners can use this framework as a blueprint to develop future tools and ensure design choices align with circular economy objectives, improving resource efficiency and reducing environmental impacts (Tong et al., 2024). Software vendors can use this framework to create standardised platforms predicting, analysing, and managing C&DW at the design stage, while practitioners can customise the information inputs and process layers to suit specific project requirements, enhancing the applicability of BIM-enabled DoC&DW principles. Adoption of this approach can reduce environmental impacts, lower costs, and improve project sustainability.

This study builds on established theoretical frameworks to examine how tools for DoC&DW facilitate C&DW minimisation during design. By applying the IPO model, the study categorises the information needs of BIM-enabled tools, aligning them with DoW principles and highlighting the need for pilot tests or case studies to validate the model. The conceptual framework helps future BIM model designers understand the functions of each layer and guide researchers in developing BIM plug-in for DoC&DW (Tong et al., 2024). The study aligns with circular economy principles, advocating DoW and keeping materials in use. By aligning BIM-enabled DoC&DW tools with CE principles, study emphasises the importance of information configurations that support sustainable design and reduce C&DW through informed decision-making. While the study focuses on identifying information needs rather than evaluating the performance of the tool, the analysis reveals critical limitations in existing tools with theoretical implications. Current tools demonstrate fragmented data, poor interoperability between BIM platforms, and inadequate real-time decision support capabilities (Bilal et al., 2016; Akinade et al., 2018). These limitations highlight theoretical gaps in operationalising DoW principles within digital environments, particularly the disconnect between conceptual frameworks and practical implementation, which can be addressed in future research. Figure 5 outlines these limitations and potential research pathways.

Addressing them will strengthen the empirical foundation, expand the applicability of the IPO-based framework, and guide the development of more effective, data-driven, and context-sensitive tools for DoC&DW at the design stage.

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Published by Emerald Publishing Limited. This article is published under the Creative Commons Attribution (CC BY 4.0) licence. Anyone may reproduce, distribute, translate and create derivative works of this article (for both commercial and non-commercial purposes), subject to full attribution to the original publication and authors. The full terms of this licence may be seen at Link to the terms of the CC BY 4.0 licence.

Data & Figures

Figure 1
A PRISMA flow diagram shows the systematic process of identifying, screening, and including papers for a study.The PRISMA flow diagram consists of three main stages aligned vertically, labeled on the left: “Identification”, “Screening and Eligibility”, and “Include”. In the “Identification” stage, a rectangular box labeled “Records identified through database search (n equals 1531)”. A downward arrow leads to the next stage, while a side arrow points to a gray box labeled “Records excluded”. This box lists three categories: “Duplicate records and non-English articles were removed (n equals 84)”, “Removed review articles (n equals 64)”, and “Removed book extracts: 9, book chapters: 62, conference papers: 452, Conference review: 75, editorials: 1, Data paper: 1, Note: 2, Short Survey: 1 equals (n equals 603)”. In the “Screening and Eligibility” stage, a box labeled “Titles and abstracts assessed for eligibility (n equals 780)”. A downward arrow leads to “Full texts assessed for eligibility (n equals 101)”. Next to each of these steps, side arrows point to gray exclusion boxes. The first exclusion box states, “Papers excluded: Not relevant and do not meet quality criteria (screening by abstract) (n equals 679)”. The second exclusion box states, “Papers excluded: Do not fall within the required scope (n equals 55)”. In the final “Include” stage, a downward arrow points to the bottom box labeled “Final papers included (n equals 46)”.

PRISMA flow diagram of the literature review process. Source: Adapted by Moher et al. (2009) 

Figure 1
A PRISMA flow diagram shows the systematic process of identifying, screening, and including papers for a study.The PRISMA flow diagram consists of three main stages aligned vertically, labeled on the left: “Identification”, “Screening and Eligibility”, and “Include”. In the “Identification” stage, a rectangular box labeled “Records identified through database search (n equals 1531)”. A downward arrow leads to the next stage, while a side arrow points to a gray box labeled “Records excluded”. This box lists three categories: “Duplicate records and non-English articles were removed (n equals 84)”, “Removed review articles (n equals 64)”, and “Removed book extracts: 9, book chapters: 62, conference papers: 452, Conference review: 75, editorials: 1, Data paper: 1, Note: 2, Short Survey: 1 equals (n equals 603)”. In the “Screening and Eligibility” stage, a box labeled “Titles and abstracts assessed for eligibility (n equals 780)”. A downward arrow leads to “Full texts assessed for eligibility (n equals 101)”. Next to each of these steps, side arrows point to gray exclusion boxes. The first exclusion box states, “Papers excluded: Not relevant and do not meet quality criteria (screening by abstract) (n equals 679)”. The second exclusion box states, “Papers excluded: Do not fall within the required scope (n equals 55)”. In the final “Include” stage, a downward arrow points to the bottom box labeled “Final papers included (n equals 46)”.

PRISMA flow diagram of the literature review process. Source: Adapted by Moher et al. (2009) 

Close modal
Figure 2
A bar graph shows the number of papers published across various years from 2004 to 2024.The vertical axis is labeled “Number of papers” and ranges from 0 to 9 with increments of 1. The horizontal axis is labeled “Year of publication” and lists specific years from 2004 to 2008 in increments of 4 years and then from 2008 to 2024 in increments of one year. From left to right, the number of papers per year is as follows: 2004 to 2011: The publication count is stable at 1 paper. 2012: The count increases to 2 papers. 2013: The count drops back to 1 paper. 2015 and 2016: The count is 2 papers for each year. 2017: A significant increase occurs, reaching 5 papers. 2018: The count decreases to 3 papers. 2019: The graph reaches its highest peak with 8 papers. 2020: The count decreases to 4 papers. 2021: The count rises again to 5 papers. 2022: The count decreases to 3 papers. 2023: The count is 2 papers. 2024: The final year shown has a count of 4 papers.

Year of publication. Source: Authors’ own work

Figure 2
A bar graph shows the number of papers published across various years from 2004 to 2024.The vertical axis is labeled “Number of papers” and ranges from 0 to 9 with increments of 1. The horizontal axis is labeled “Year of publication” and lists specific years from 2004 to 2008 in increments of 4 years and then from 2008 to 2024 in increments of one year. From left to right, the number of papers per year is as follows: 2004 to 2011: The publication count is stable at 1 paper. 2012: The count increases to 2 papers. 2013: The count drops back to 1 paper. 2015 and 2016: The count is 2 papers for each year. 2017: A significant increase occurs, reaching 5 papers. 2018: The count decreases to 3 papers. 2019: The graph reaches its highest peak with 8 papers. 2020: The count decreases to 4 papers. 2021: The count rises again to 5 papers. 2022: The count decreases to 3 papers. 2023: The count is 2 papers. 2024: The final year shown has a count of 4 papers.

Year of publication. Source: Authors’ own work

Close modal
Figure 3
A bibliometric network map displays keyword clusters related to selected search area.The bibliometric network map uses colored nodes and curved connecting lines to illustrate research clusters and their relationships. At the top, a blue cluster focuses on sustainability and circularity, with nodes for “reuse”, “recycling”, “deconstruction”, “sustainability”, and “building information modeling ”. In the center, a purple cluster serves as a major hub with two large nodes: “waste management” and “construction and demolition waste”. To the left, a red cluster includes “construction waste minimisation”, “big data analytics”, “construction”, “construction waste”, “building information modelling (BIM)”, and “circular economy”. At the bottom center, a yellow cluster features “design for deconstruction”, “critical success factors”, and “material reuse”. On the right, a green cluster focuses on digital integration, including “building information modeling”, “design for deconstruction”, “greenhouse gas emissions”, and “building information modeling (b i m)”. Curved lines of various colors weave between the clusters, showing strong cross-disciplinary links, particularly between “waste management” and the red and blue clusters.

Keyword co-occurrence. Source: Authors’ generated using VOSviewer

Figure 3
A bibliometric network map displays keyword clusters related to selected search area.The bibliometric network map uses colored nodes and curved connecting lines to illustrate research clusters and their relationships. At the top, a blue cluster focuses on sustainability and circularity, with nodes for “reuse”, “recycling”, “deconstruction”, “sustainability”, and “building information modeling ”. In the center, a purple cluster serves as a major hub with two large nodes: “waste management” and “construction and demolition waste”. To the left, a red cluster includes “construction waste minimisation”, “big data analytics”, “construction”, “construction waste”, “building information modelling (BIM)”, and “circular economy”. At the bottom center, a yellow cluster features “design for deconstruction”, “critical success factors”, and “material reuse”. On the right, a green cluster focuses on digital integration, including “building information modeling”, “design for deconstruction”, “greenhouse gas emissions”, and “building information modeling (b i m)”. Curved lines of various colors weave between the clusters, showing strong cross-disciplinary links, particularly between “waste management” and the red and blue clusters.

Keyword co-occurrence. Source: Authors’ generated using VOSviewer

Close modal
Figure 4
A system architecture diagram illustrates the flow from Input Information to Information Processing and Output Information.The diagram is divided into three vertical sections labeled “Input Information”, “Information Processing”, and “Output Information”. The “Input Information” section on the left lists seven categories connected by dashed lines to the central section: “Material properties”, “Design Specifications”, “C and D waste information”, “Life cycle Parameters”, “Economic Indicators”, “Social Indicators”, and “Environmental Impact Categories”. A rightward arrow from the top of this section leads to the central section. The central “Information Processing” section contains a vertical flow of four gray rectangular layers: “Data Storage layer”, “Semantic Layer”, “Analytics and functional model layer”, and “Application Layer”, connected by downward-pointing thick black arrows. The “Analytics and functional model layer” contains a sub-box titled “Designing out waste principles” which lists five items: “Design for waste-efficient procurement”, “Design for material optimisation”, “Design for off-site construction”, “Design for reuse and recycling”, and “Design for deconstruction”. Dashed arrows from the input items converge into the sub-blocks within the “Designing out waste principles” box, connecting each input category to multiple design principle blocks. A rightward arrow from the bottom of this section leads to the right section. The “Output Information” section on the right lists fourteen outcomes labeled from top to bottom as “Design-related activities as detailing, clash detection, visualisation”, “Quantification of environmental damage”, “Critical factors of BIM acceptance towards improved waste minimisation”, “Design alternatives”, “Efficiency of the demolition process”, “Interactive construction waste analytics”, “Whole life cycle costing”, “Decision-making criteria on selecting optimal materials”, “Identification of hazardous materials”, “Compliance of building codes and stability”, “Prefabrication potential”, “Evaluating options and potentials for reusing slash recycling”, “Potential for deconstruction”, and “Disassembly sequence slash Technical ability to be dismantled”. Dashed arrows connect each design principle block in the central section to multiple items in this output list. At the bottom, a legend shows a solid arrow labeled “Information flow” and a dashed arrow labeled “Information – DoW Mapping”.

Conceptual framework on BIM-enabled architecture for DoC&DW. Source: Authors’ own work

Figure 4
A system architecture diagram illustrates the flow from Input Information to Information Processing and Output Information.The diagram is divided into three vertical sections labeled “Input Information”, “Information Processing”, and “Output Information”. The “Input Information” section on the left lists seven categories connected by dashed lines to the central section: “Material properties”, “Design Specifications”, “C and D waste information”, “Life cycle Parameters”, “Economic Indicators”, “Social Indicators”, and “Environmental Impact Categories”. A rightward arrow from the top of this section leads to the central section. The central “Information Processing” section contains a vertical flow of four gray rectangular layers: “Data Storage layer”, “Semantic Layer”, “Analytics and functional model layer”, and “Application Layer”, connected by downward-pointing thick black arrows. The “Analytics and functional model layer” contains a sub-box titled “Designing out waste principles” which lists five items: “Design for waste-efficient procurement”, “Design for material optimisation”, “Design for off-site construction”, “Design for reuse and recycling”, and “Design for deconstruction”. Dashed arrows from the input items converge into the sub-blocks within the “Designing out waste principles” box, connecting each input category to multiple design principle blocks. A rightward arrow from the bottom of this section leads to the right section. The “Output Information” section on the right lists fourteen outcomes labeled from top to bottom as “Design-related activities as detailing, clash detection, visualisation”, “Quantification of environmental damage”, “Critical factors of BIM acceptance towards improved waste minimisation”, “Design alternatives”, “Efficiency of the demolition process”, “Interactive construction waste analytics”, “Whole life cycle costing”, “Decision-making criteria on selecting optimal materials”, “Identification of hazardous materials”, “Compliance of building codes and stability”, “Prefabrication potential”, “Evaluating options and potentials for reusing slash recycling”, “Potential for deconstruction”, and “Disassembly sequence slash Technical ability to be dismantled”. Dashed arrows connect each design principle block in the central section to multiple items in this output list. At the bottom, a legend shows a solid arrow labeled “Information flow” and a dashed arrow labeled “Information – DoW Mapping”.

Conceptual framework on BIM-enabled architecture for DoC&DW. Source: Authors’ own work

Close modal
Figure 5
A two-column table showing limitations and corresponding future directions connected by arrows.The table, titled “RESEARCH THEMES: FUTURE RESEARCH AGENDA”, is organized into two main columns: “LIMITATION” and “FUTURE DIRECTION”. Eight rows connected by thick black right-pointing arrows detail the following: Row 1: The limitation states, “Though this SLR ensures high-quality evidence, it excludes insights from conference papers, industry reports, and grey literature”. The corresponding future direction is “Expand literature review scope: To include grey literature, industry reports to capture broader insights on tools for DoC&DW”. Row 2: The limitation states, “The current framework applies a general IPO model without specifying DoC&DW principles individually”. The future direction is “SLR to develop IPO model specific to each DoW principle: Conduct an SLR to develop IPO models tailored to each DoW principle, highlighting variations in inputs, processes, and outputs”. Row 3: The limitation states, “The proposed conceptual framework for BIM-enabled DoC&DW lacks empirical validation”. The future direction is “Validation of BIM-Enabled Framework” with two bullet points: “Validate the framework with domain experts and real-world construction projects to ensure practical relevance, comprehensiveness, and adoption feasibility” and “Conduct case studies to compare actual information needs with the IPO model predictions, refining the model for each principle”. Row 4: The limitation states, “Study identified common information needs across building elements without element-specific analysis”. The future direction is “Element-Specific Information Needs: Focus on building-element-specific information requirements, applying relevant DoW principles to identify targeted waste minimisation strategies”. Row 5: The limitation states, “The role of input information in effective BIM-enabled processing for DoC&DW has not been quantified”. The future direction is “Significance of Input Information: Empirically analyse input information significance, identifying its influence on the effectiveness of BIM-based DoC&DW processes”. Row 6: The limitation states, “Current tools have not been systematically evaluated for multi-dimensional limitations”. The future direction is “Limitations of Existing DoC&DW Tools: Conduct empirical evaluations of existing DoC&DW tools, provide recommendations, and improve tools based on multi-dimensional analysis”. Row 7: The limitation states, “The study introduced BIM-enabled architecture but did not integrate circular economy (CE) principles fully”. The future direction is “Integration with Circular Economy Principles: Extend the conceptual framework to incorporate CE principles, examine information needs per  DoW principle, and integrate CE indicators into the IPO model”. Row 8: The limitation states, “Focused exclusively on BIM, other technologies such as simulation, mathematical models, or multi-criteria decision-making tools were not considered”. The future direction is “Exploration of Other Technologies: Explore alternative technologies for DoC&DW and analyse their comparative effectiveness, providing implications for adoption beyond BIM”.

Limitations and future research directions. Source: Authors’ own work

Figure 5
A two-column table showing limitations and corresponding future directions connected by arrows.The table, titled “RESEARCH THEMES: FUTURE RESEARCH AGENDA”, is organized into two main columns: “LIMITATION” and “FUTURE DIRECTION”. Eight rows connected by thick black right-pointing arrows detail the following: Row 1: The limitation states, “Though this SLR ensures high-quality evidence, it excludes insights from conference papers, industry reports, and grey literature”. The corresponding future direction is “Expand literature review scope: To include grey literature, industry reports to capture broader insights on tools for DoC&DW”. Row 2: The limitation states, “The current framework applies a general IPO model without specifying DoC&DW principles individually”. The future direction is “SLR to develop IPO model specific to each DoW principle: Conduct an SLR to develop IPO models tailored to each DoW principle, highlighting variations in inputs, processes, and outputs”. Row 3: The limitation states, “The proposed conceptual framework for BIM-enabled DoC&DW lacks empirical validation”. The future direction is “Validation of BIM-Enabled Framework” with two bullet points: “Validate the framework with domain experts and real-world construction projects to ensure practical relevance, comprehensiveness, and adoption feasibility” and “Conduct case studies to compare actual information needs with the IPO model predictions, refining the model for each principle”. Row 4: The limitation states, “Study identified common information needs across building elements without element-specific analysis”. The future direction is “Element-Specific Information Needs: Focus on building-element-specific information requirements, applying relevant DoW principles to identify targeted waste minimisation strategies”. Row 5: The limitation states, “The role of input information in effective BIM-enabled processing for DoC&DW has not been quantified”. The future direction is “Significance of Input Information: Empirically analyse input information significance, identifying its influence on the effectiveness of BIM-based DoC&DW processes”. Row 6: The limitation states, “Current tools have not been systematically evaluated for multi-dimensional limitations”. The future direction is “Limitations of Existing DoC&DW Tools: Conduct empirical evaluations of existing DoC&DW tools, provide recommendations, and improve tools based on multi-dimensional analysis”. Row 7: The limitation states, “The study introduced BIM-enabled architecture but did not integrate circular economy (CE) principles fully”. The future direction is “Integration with Circular Economy Principles: Extend the conceptual framework to incorporate CE principles, examine information needs per  DoW principle, and integrate CE indicators into the IPO model”. Row 8: The limitation states, “Focused exclusively on BIM, other technologies such as simulation, mathematical models, or multi-criteria decision-making tools were not considered”. The future direction is “Exploration of Other Technologies: Explore alternative technologies for DoC&DW and analyse their comparative effectiveness, providing implications for adoption beyond BIM”.

Limitations and future research directions. Source: Authors’ own work

Close modal
Table 1

Comparative study of related contemporary literature reviews

AuthorsKey themes investigatedFuture research suggestions
Raza (2020) Waste management, sustainable development, closed loop of supply chains
  • Evolution of Closed Loop Supply Chain (CLSC) research periodically

  • Explore the impact of the emerging tools from big data and artificial intelligence in CLSC

Lu and Yuan (2010) C&DW reduction, minimization, recycling performance measurement, reuse, tools and regulatory environment
  • Investigate C&DW issues in wider scopes including design, maintenance and demolition

  • Develop a measurement tool for waste generation to compare Waste Management (WM) performance across various economies

  • Enhance the effectiveness of WM approaches

Jin et al. (2019) CWM (Construction & Demolition Waste Management)
(Waste treatment methods, Sustainability impact, Waste materials and technical studies, waste management approaches, quantification of waste generation, new immerging technologies)
  • Design and planning for waste diversion

  • A comprehensive evaluation of the performance of CDW diversion

  • Human factors in CWM

  • Integration of BIM and Big Data into C&DW management

Ghafourian et al. (2016) Generation, reduction, reuse, recycling, human factors of C&DW
  • Not provided

Majmundar and Ansari (2018) Design for Disassembly
  • DfD is a fruitful area for future research

Amaral et al. (2020) Design, construction waste, waste management, reuse and recycling of building materials, embodied carbon, sustainable construction
  • Close the loop through Return on Equity (ROE) assessments, so stakeholders and communities have the right tools for decision-making, to reduce waste and promote sustainable building operation

Chileshe et al. (2019) Reverse Logistics, CLSC, Information, DoW
  • Development of optimisation models for recovery facilities

  • Risk management in PEoLB operations

  • Information-based strategic management approaches (BIM-enabled environmental and economic assessment of recovery strategies)

Gupta et al. (2022) CWM strategies and tools, BIM-based strategies for CWM, CWM tools with their application areas, BIM compliant tools, their features and limitations
  • Employing any BIM-compliant tool for CWM

  • BIM-based design tool for identification of probable causes of C&DW and to support in design optimization

Nikmehr et al. (2021) Waste, Building Information modelling
  • Most advanced BIM-based technologies for dealing with C&DW problems

Mrema et al. (2023) Current status of BIM and C&DW Management and their interconnections
  • Development of tools that can automatically evaluate environmental impact assessment of C&DW

Aziminezhad and Taherkhani (2023) Challenges and opportunities related to integrating BIM in deconstruction
  • Conduct research on BIM for deconstruction

Nawaz et al. (2023) Construction waste management studies
  • Identifying the research gap in the construction waste management studies, including gaps in major knowledge domains

Rayhan and Bhuiyan (2024) Classification, components, and composition of C&DW, sources, causes, and impacts of CDW generation
  • A significant number of studies have been done to quantity or estimate the generated amount of C&DWs.

  • Research efforts on forecasting or predicting the generated amount of C&DWs is a potential theme for investigation

Source(s): Authors’ own work
Table 2

Input classification groups

Input data classificationTypes of input dataPotential sources
Material properties
  • Element dimensions

  • Element density

  • Element composition

  • Element weight

  • Lifespan

  • Amount of virgin Materials

  • Material databases

  • Manufacturer specifications

  • Environmental product declarations

  • BIM models

Design specifications
  • Total floor area

  • Building Structure

  • Building MEP (Mechanical, Electrical, and plumbing)

  • Site information

  • Building Usage

  • Dimensions

  • Life span

  • Architectural drawings

  • BIM models

  • Structural calculations

C&DW information
  • C&DW types

  • C&DW generation

  • Waste records

  • C&DW estimation

  • Degradable organic carbon fraction of C&D waste

  • Faction of actual degradable carbon

  • Historical project data

  • Waste audits

  • Industry benchmarks

Life cycle parameters
  • Transportation distances

  • Fuel consumption

  • Landfill types

  • Energy

  • LCA databases

  • Carbon footprint calculators

Economic indicators
  • Cost of C&DW disposal

  • Net cost of operating and maintaining recycling facilities

  • Cost databases

  • Market prices

  • Disposal costs

Social indicators
  • Public acceptance of C&DW management plans and actions

  • Public participation in planning and implementation

  • Perspective of industry professionals

  • Working Safety

  • Stakeholder requirements

  • Regulatory compliance data

Environmental impact categories
  • GHG types

  • GHG sources

  • Impact of each material

  • Impact assessment databases

  • Regional environmental factors

Source(s): Authors’ own work
Table 3

Outputs based on the nature of the output and the levels in the waste management hierarchy

ReferencesNature of the outputLevels in waste management hierarchy
Impacts and potentialsQuantitative measuresQuality of materialDatabaseReduceRecycleReuseRecoverRelocate
Akanbi et al. (2019)  x  x x  
Akinade et al. (2015) x     x x
Akinade et al. (2017) x      x 
Akinade et al. (2018) x   x    
Akinade and Oyedele (2019)  x  xxx  
Baldwin et al. (2009) x   x    
Basta et al. (2020) x     xx 
Bertin et al. (2020)   x   x  
Bilal et al. (2016)   x x    
Bilal et al. (2017)  x  x    
Chileshe et al. (2019) x    xx  
Denis et al. (2018) x   x    
Eckelman et al. (2018) x     x  
Ekanayake and Ofori (2004)  x  xx   
Ge et al. (2017)  x   xx  
Haeusler et al. (2021)  x  x    
Hiete et al. (2011) x    x   
Honic et al. (2019a, b)   x   x  
Jayasinghe and Waldmann (2020)    x xx  
Keulemans and Adams (2024)    x  x  
Khondoker (2021)  x  x    
Kunieda et al. (2019) x      x 
Liu et al. (2015)  x  x    
Llatas and Osmani (2016) x   x    
Lu and Yuan (2010) x   x    
Lu et al. (2017)  x    xx 
Marzouk and Elmaraghy (2021)   x   x  
Mayer and Bechthold (2017) x      x 
Mohammed et al. (2024)  x    xx 
Porwal and Hewage (2012)  x  x    
Sadafi et al. (2012) x     xx 
Sassi (2008)   x xxx  
Seeboo (2022) x   x    
Whittaker et al. (2021) x    xx  
Xia et al. (2020) x    xx  
Xu et al. (2019)  x  x    
Yeheyis et al. (2013)  x  xxx  
Han et al. (2024) xx   xx  
Yuan et al. (2022)  x  x    
Llatas et al. (2022) xx   x   
Lima et al. (2023) x xx xx  
Mei et al. (2021)  x    x  
Sanchez et al. (2021) x     x  
Xiao et al. (2023) x x  xx  
Zubair et al. (2024) xx  x    
Source(s): Authors’ own work
Table 4

IPO information of tools against key principles of DoW concepts

DoW principlesInputProcessOutput
Design for resource-efficient procurement
  • Environmental impact categories

  • Life cycle parameters

  • Material properties

  • Social indicators

  • Design Specifications

Applied in the analytics and functional modelling layer (See section 5.2)
  • Enhanced design-related activities as detailing, clash detection, visualisation

  • Quantifying environmental damage

  • Critical factors of BIM acceptance towards improved waste minimisation

  • Material waste estimation and calculation of residual material

  • Waste-efficient optimum building layout

  • Optimized cutting patterns from available market lengths to minimise waste generation

  • Compliance of building codes and stability

  • Design alternatives

  • Efficiency of the demolition process

  • Decision-making criteria for selecting optimal materials

  • Interactive construction waste analytics

  • Whole life cycle costing

Design for materials optimisation
  • Material properties

  • Environmental impact categories

  • Design specifications

  • Economic indicators

  • Life cycle parameters

  • Social indicators

  • Decision-making criteria on selecting optimal materials

  • Identification of hazardous materials

Design for off-site construction
  • Material properties

  • Environmental impact categories

  • Design specifications

  • Economic indicators

  • Social indicators

  • Compliance of building codes and stability

  • Prefabrication potential

Design for reuse and recycling
  • Environmental impact categories

  • Economic indicators

  • CDW information

  • BIM models of the design

  • Social indicators

  • Design alternatives

  • Material recovery potential

  • Evaluating options and potentials for reusing/recycling

Design for deconstruction
  • Design specifications

  • BIM models of the design

  • Social indicators

  • Potential for deconstruction

  • Disassembly sequence/Technical ability to be dismantled

Source(s): Authors’ own work
Table 5

Critical BIM features mapped against the key layers in BIM-enabled architectures

Critical BIM featuresDefinitionKey layers in a BIM-enabled architecture
DSSAFA
BIM core features
Object parametric modelling
  • Context-driven waste information is modelled by capturing the design intent of the building

  • Building objects (to reflect behaviour and attributes of materials and elements) are assigned geometric and non-geometric data

  • Could be implemented in a plug-in

X XX
Bi-directional associativity
  • Calculating the impact of the design changes and then accurately applying the changes to the relevant parts of the building model

  • Facilitates a change management functionality

  • Could be implemented in a plug-in

  XX
Intelligent modelling
  • Attach supplementary data (dimensions, quantities, relative locations, schedules and specifications) to building objects once and have the ability to extract information repeatedly for different analytical and reporting

  • Have semantic capabilities where the external sources and building objects are linked

  • Could be implemented in a plug-in

 XXX
BIM auxiliary features and waste management criteria
Design
  • Incorporating waste minimisation into the design stage

  • Five design principles for DoW should be addressed for resource efficiency

  X 
Visualization
  • Important in waste prediction and minimisation where the associated waste potential of the materials and design changes for waste efficiency are visualised

  X 
Data
  • Different sources of data should be provided related to design, procurement, and construction

X   
Holistic and life cycle
  • Waste prediction and minimisation considering all factors leading to construction waste

  X 
Interoperability
  • Facilitate the readability of the data from different sources, and analyse and evaluate the construction waste

  • Support understanding the trends in waste analytics

  • Three ways to achieve interoperability

  • Through open database connectivity (OBDC), which acts as an API for accessing the database management system of the plug-in software

  • As programs in the form of API

  • As open data exchange standards

 XXX
Technology
  • Facilitates both exploratory and descriptive waste analytics

  • Facilitates automated algorithms and computational capabilities

  X 
Cost/benefit analysis
  • Support cost minimisation by quantifying the cost-benefit analysis for every design change

  X 
The application layer
Plug-in-support
  • User interaction layer

  • Extends the functionality of the existing BIM model

  • Incorporate waste minimisation and prediction tools

  XX

Note(s): DS = Data storage layer; S=Semantic Layer; AF = Analytics and functional model layer; A = Application layer)

Source(s): Authors’ own work
Table A1

Details of the selected articles

NoYearAuthorsTopicName of the journalCountry/ContextMethodologyTools for information processing
12019Akanbi et al. (2019) Disassembly and deconstruction analytics system (D-DAS) for construction in a circular economyJournal of Cleaner ProductionUKMathematical Approach + Case StudyBIM-enabled
22015Akinade et al. (2015) Waste minimisation through deconstruction: A BIM based Deconstructability Assessment Score (BIM-DAS)Resources, Conservation and RecyclingUKCase StudyBIM-enabled
32017Akinade et al. (2017) Design for Deconstruction (DfD): Critical success factors for diverting end-of-life waste from landfillsWaste ManagementUKFocus group + questionnaireGuide
42018Akinade et al. (2018) Designing out construction waste using BIM technology: Stakeholders' expectations for industry deploymentJournal of Cleaner ProductionUKFocus group + questionnaire SurveyBIM-enabled
52019Akinade and Oyedele (2019) Integrating construction supply chains within a circular economy: An ANFIS-based waste analytics system (A-WAS)Journal of Cleaner ProductionUKAdaptive Neuro-Fuzzy Inference System (ANFIS) + Case studyBIM-enabled
62009Baldwin et al. (2009) Designing out waste in high-rise residential buildings: Analysis of precasting methods and traditional constructionRenewable EnergyHong KongAnalytical design planning technique (ADePT)Software application
72020Basta et al. (2020) A BIM-based framework for quantitative assessment of steel structure deconstructabilityAutomation in ConstructionEgyptMathematical ApproachBIM-enabled
82020Bertin et al. (2020) A BIM-based framework and databank for reusing load-bearing structural elementsSustainabilitySwitzerlandCase studyBIM-enabled
92016Bilal et al. (2016) Big data architecture for construction waste analytics (CWA): A conceptual frameworkJournal of Building EngineeringUKMathematical ApproachBIM-enabled
102017Bilal et al. (2017) The application of web of data technologies in building materials information modelling for construction waste analyticsSustainable Materials and TechnologiesUKCase StudyBIM-enabled
112020Xia et al. (2020) Life cycle assessment of concrete structures with reuse and recycling strategies: A novel framework and case studyWaste ManagementChinaCase studyBIM-enabled
122019Chileshe et al. (2019) Information flow-centric approach for reverse logistics supply chainsAutomation in ConstructionAustraliaSemi-structured interviews and action researchBIM-enabled
132018Denis et al. (2018) Using network analysis and BIM to quantify the impact of Design for DisassemblyBuildingsBelgiumNetwork Analysis Method-Mathematical ApproachBIM-enabled
142018Eckelman et al. (2018) Life cycle energy and environmental benefits of novel design-for-deconstruction structural systems in steel buildingsBuilding and EnvironmentUSACase StudySimulation
152004Ekanayake and Ofori (2004) Building waste assessment score: design-based toolBuilding and EnvironmentSingaporeQuestionnaire surveyMathematical
162017Ge et al. (2017) Deconstruction waste management through 3d reconstruction and bim: a case studyVisualization in EngineeringAustraliaCase StudyBIM-enabled
172021Haeusler et al. (2021) (Computationally) designing out waste: Developing a computational design workflow for minimising construction and demolition waste in early-stage architectural designInternational Journal of Architectural ComputinggeneralAction researchBIM-enabled
182024Han et al. (2024) The development of an integrated BIM-based visual demolition waste management planning system for sustainability-oriented decision-makingJournal of Environmental ManagementAustraliaCase StudyBIM-enabled
192011Hiete et al. (2011) Matching construction and demolition waste supply to recycling demand: A regional management chain modelBuilding Research and InformationGermanyCase studyBIM-enabled
202019Honic et al. (2019b) Data- and stakeholder management framework for the implementation of BIM-based Material PassportsJournal of Building EngineeringAustriaCase StudyBIM-enabled
212019Honic et al. (2019a) Improving the recycling potential of buildings through Material Passports (MP): An Austrian case studyJournal of Cleaner ProductionAustraliaCase StudyBIM-enabled
222020Jayasinghe and Waldmann (2020) Development of a BIM-Based Web Tool as a Material and Component Bank for a Sustainable Construction IndustrySustainabilityLuxembourg and EuropeAction ResearchBIM-enabled
232024Keulemans and Adams (2024) Emergent digital possibilities for design-led reuse within circular economyUrban sustainabilityAustraliaCase StudyBIM-enabled
242021Khondoker (2021) Automated reinforcement trim waste optimization in RC frame structures using building information modeling and mixed-integer linear programmingAutomation in ConstructionBangladeshMathematical ApproachBIM-enabled
252019Kunieda et al. (2019) Increasing the efficiency and efficacy of demolition through computerised 4D simulationEngineering, Construction and Architectural ManagementUKCase study and Simulation methodSimulation
262023Lima et al. (2023) Integration of BIM and design for deconstruction to improve circular economy of buildingsJournal of Building EngineeringBrazilCase StudyBIM-enabled
272015Liu et al. (2015) A BIM-aided construction waste minimisation frameworkAutomation in ConstructionUKQuestionnaire survey and InterviewBIM-enabled
282016Llatas and Osmani (2016) Development and validation of a building design waste reduction modelWaste ManagementSpainMathematical Approach + Case StudyMathematical
292022Llatas et al. (2022) Environmental Impact Assessment of Construction Waste Recycling versus Disposal Scenarios Using an LCA-BIM Tool during the Design StageRecyclingSpainCase StudyBIM-enabled
302010Lu and Yuan (2010) Exploring critical success factors for waste management in construction projects of ChinaResources, Conservation and RecyclingChinaQuestionnaire survey + semi-structured interviewsGuides
312017Lu et al. (2017) Computational Building Information Modelling for construction waste management: Moving from rhetoric to realityRenewable and Sustainable Energy ReviewsHong KongMathematical ApproachBIM-enabled
322021Marzouk and Elmaraghy (2021) Design for Deconstruction Using Integrated Lean Principles and BIM ApproachSustainabilityEgyptCase StudyBIM-enabled
332017Mayer and Bechthold (2017) Development of policy metrics for circularity assessment in building assembliesEconomics and Policy Energy and the EnvironmentUSAMathematical Approach + Case StudyMathematical
342021Mei et al. (2021) BIM-Based Framework for Formwork Planning
Considering Potential Reuse
Journal of Management in EngineeringChinaCase StudyBIM-enabled
352024Mohammed et al. (2024) Design for steel structures deconstruction: an analytics system for construction waste minimization in a circular economy through BIM technologyInnovative Infrastructure SolutionsEgyptMathematical Approach and case studyBIM-enabled + Mathematical
362012Porwal and Hewage (2012) Building Information Modelling–Based Analysis to Minimize Waste Rate of Structural ReinforcementJournal of Construction Engineering and ManagementCanadaMathematical Approach and case studyBIM-enabled
372012Sadafi et al. (2012) Assessment of industrial and adaptable building components for a residential layoutInternational Journal of the Physical SciencesMalaysiaSimulation modelSimulation
382021Sanchez et al. (2021) A framework for BIM-based disassembly models to support reuse of building componentsResources, Conservation and RecyclingMexica, Canda and GermanyCase studyBIM-enabled
392008Sassi (2008) Defining closed-loop material cycle constructionBuilding Research and InformationUKCase StudyMathematical
402022Seeboo (2022) Designing out waste by optimizing floor layout with locally available building materialsJournal of cleaner ProductionMauritiusSurveyMathematical
412019Whittaker et al. (2021) Novel construction and demolition waste (CDW) treatment and uses to maximize reuse and recyclingAdvances in Building Energy ResearchEuropeCase studyBIM-enabled
422023Xiao et al. (2023) Deconstruction evaluation method of building structures based on digital technologyJournal of Building EngineeringChinaCase StudyBIM-enabled
432019Xu et al. (2019) A BIM-Based construction and demolition waste information management system for greenhouse gas quantification and reductionJournal of cleaner productionChinaMathematical ApproachBIM-enabled
442013Yeheyis et al. (2013) An overview of construction and demolition waste management in Canada: a lifecycle analysis approach to sustainabilityClean Techn Environ PolicyCanadaMathematical ApproachMathematical
452022Yuan et al. (2022) A system dynamic model for simulating the potential of prefabrication on construction waste reductionEnvironmental Science and Pollution ResearchChinaCase StudySimulation
462024Zubair et al. (2024) BIM- and GIS-Based Life-Cycle-Assessment Framework for Enhancing Eco Efficiency and Sustainability in the Construction SectorBuildingPakistanCase StudyBIM-enabled
Source(s): Authors’ own work

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