Abstract
Purpose
This study aims to present state-of-the-art research on circular economy (CE) implementation in construction and demolition waste management (CDWM) within the construction sector.
Design/methodology/approach
A mixed-method (scientometric and critical analysis) review strategy was adopted, involving scientometric and critical analysis to uncover the evolutionary progress within the research area, investigate key research themes in the field, and explore ten issues of CE in CDWM. Moreover, avenues for future research are provided for researchers, practitioners, decision-makers, and planners to bring innovative and new knowledge to this field.
Findings
A total of 212 articles were analyzed, and scientometric analysis was performed. The critical analysis findings reveal extensive use of surveys, interviews, case studies, or mixed-method approaches as study methodologies. Furthermore, there is limited focus on the application of modern technologies, modeling approaches, decision support systems, and monitoring and traceability tools of CE in the CDWM field. Additionally, no structured framework to implement CE in CDWM areas has been found, as existing frameworks are based on traditional linear models. Moreover, none of the studies discuss readiness factors, knowledge management systems, performance measurement systems, and life cycle assessment indicators.
Practical implications
The outcomes of this study can be utilized by construction and demolition sector managers, researchers, practitioners, decision-makers, and policymakers to comprehend the state-of-the-art, explore current research topics, and gain detailed insights into future research areas. Additionally, the study offers suggestions on addressing these areas effectively.
Originality/value
This study employs a universal approach to provide the current research progress and holistic knowledge about various important issues of CE in CDWM, offering opportunities for future research directions in the area.
Keywords
Citation
Swarnakar, V. and Khalfan, M. (2024), "Circular economy in construction and demolition waste management: an in-depth review and future perspectives in the construction sector", Smart and Sustainable Built Environment, Vol. ahead-of-print No. ahead-of-print. https://doi.org/10.1108/SASBE-02-2024-0056
Publisher
:Emerald Publishing Limited
Copyright © 2024, Vikas Swarnakar and Malik Khalfan
License
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 http://creativecommons.org/licences/by/4.0/legalcode
1. Introduction
The construction and demolition industry (CDI) is a crucial sector that significantly contributes to the socio-economy growth (Mhlanga et al., 2022). Globally, it accounts for approximately 7% of job opportunities and contributes around 25% to the gross domestic product (GDP) (Norouzi et al., 2021). In the Middle East alone, the CDI employs over 13 million people and plays a key role in rapid urbanization, generating approximately $600bn annually with an average annual growth rate of 3–4%. However, the sustainability of this industry is challenged by the extensive generation of waste and carbon dioxide emissions compared to other sectors (Mahpour, 2018). Its unsustainable nature is rooted in its traditional linear approach of “Take, Make, and Dispose” (Mahpour, 2018). This approach leads to the disposal of raw materials used in construction without considering their end-of-life implications (Esa et al., 2017; Huang et al., 2018). Consequently, concerns have arisen among construction professionals, decision-makers, planners, scholars, and governments regarding the depletion of natural resources and environmental consequences (Ruiz et al., 2020). In response, the CE has emerged as a model promoting reduce, reuse, refurbish, repair, and recycle approaches, thereby extending the life span of resources and mitigating environmental concerns (Mahpour, 2018).
While the adoption of CE principles has been widespread in various sectors, including utilities, basic materials, telecommunications, oil and gas, consumer service, and finance (García-Sánchez et al., 2021), its application in construction and demolition sector is relatively nascent (Oluleye et al., 2022). As a result, several definitions of CE have emerged in the literature. For example, Bressanelli et al. (2021) describe it as an approach that reconfigures current methods of production or resource usage to enhance efficiency and attain a sustainable environment. Bilal et al. (2020) view CE as an effective approach to solve linear economy problems. Ellen MacArthur Foundation (2015) defines it as an effective method to promote cleaner production and sustainable consumption through treating, reusing, and recycling wastes. Previous studies have not clearly elaborated on the definitions of construction and demolition waste management. Therefore, this study spotlighting its definition as “Construction and demolition waste management (CDWM) refers to the process of effectively handling, disposing of, and recycling the waste materials generated from renovation, construction, and demolition activities. CDWM includes implementing strategies to minimize waste generation, segregating and sorting materials for reuse or recycling, and ensuring proper disposal of non-recyclable waste in a manner that minimizes environmental impact”.
Moreover, recent years have witnessed a growing recognition of the benefits of CE in CDI, such as enhanced resource efficiency, cost savings, customer engagement, resilience, security, and sustainability (Huang et al., 2018). Despite, these advancements, the adoption of CE practices in CDI remains at an early stage (Cristiano et al., 2021). Effective implementation of CE in CDI holds the potential to optimize resource recovery, minimize construction and demolition waste (CDW), ensure regulatory compliance, assess environmental impact, support decision-making, foster stakeholder collaboration, and drive continuous improvement in CDW management (Illankoon and Vithanage, 2023; Mhlanga et al., 2022). Therefore, there is a pressing need to embrace CE principles in CDI to manage construction and demolition wastes (CDWs) effectively and conserve resources for the long term. However, the increasing demand for CE adoption in CDW management has attracted researchers’ attention, resulting in numerous existing publications.
While previous reviews on CE in construction and demolition areas offer valuable insights (see Table 1), there are still some knowledge gaps that need addressing. For example, the existing reviews is focused on either digital technologies, 3R strategies, general overview of CDWM, tools and techniques of CDWM, contribution on SDGs, CE frameworks, and general science mapping. There is no comprehenshive state-of-the-art analysis of CE in CDWM using a mixed-method approach providing holistic knowledge and highlighting strong future research directions. Hence, there is an urgent need to fill these gaps by delving into a deeper understanding of the current research progress and gaining holistic knowledge about various important issues of CE in CDWM. Moreover, previous reviews have not provided comprehensive knowledge or strong research directions for future studies. To address these limitations and bridge previous research gaps, this study offers a state-of-the-art analysis of CE in CDWM using a mixed-method (scientometric and critical analysis) review strategy. The scientometric study is conducted from four perspectives: publication trends, mapping journal publications, mapping countries, and mapping keyword occurrences. On the other hand, a critical review is conducted based on ten themes including research characteristics, CDW monitoring, traceability and management tools, benefits and challenges of CE in CDWM, modeling approaches, modern technologies, decision support systems, enablers, barriers, performance measures, and existing models/frameworks.
Achieving the above objectives will assist researchers and academics in understanding the state-of-the-art and identifying hot research topics in CE implementation in the CDWM field. Furthermore, this study provides detailed guidelines and knowledge about future research areas, along with suggestions on how to address them. The findings will be invaluable to CE practitioners, managers, decision-makers, policymakers, construction and demolition planners, and other stakeholders, serving as a knowledge base to effectively manage CDWs. Additionally, the outcome may enable them to fund research efforts in identified salient fields.
The structure of this article is as follows: the methodology employed in this study is discussed in Section 2. Section 3 provides the results and discussion. Recommendations for researchers, practitioners, decision-makers, and policymakers are provided in Section 4. Section 5 discusses the future research areas by detailing key issues identified in the present study. Conclusion, followed by limitations, is provided in Section 6.
2. Methodology
The methodology employed in this study adopts an interpretive philosophical approach, drawing from previous publications (Ghosh et al., 2021; Oluleye et al., 2022). This approach elucidates the nuance and variabilities present in published literature, aiding researchers in conceptualizing novel research ideas. A mixed-method review process, comprising scientometric and critical analysis, was utilized. This method is also known as “explanatory design” approach. The integrated review approach fulfills the shortcomings of each other, as one can analyze the articles quantitatively while the other evaluates qualitatively. For example, the scientometric review approach helps investigate research developments and trends, describing the existing articles, their nature, sources, and information in quantitative form (Oluleye et al., 2022). Whereas the critical review approach examines and evaluates article contents through in-depth analysis. Furthermore, it helps explore the evolution and advancement of research by identifying gaps qualitatively (Ghosh et al., 2021). Moreover, the findings from the integrated approach have more strength than a single approach to illustrate the research gaps. Figure 1 outlines the research methodology process, the details of scientometric and critical analysis approach is separately discussed in subsections below.
2.1 Scientometric analysis
Scientometric analysis is employed to investigate research development and trends in quantitative form, offering comprehensive insights into authorship, country of origin, journal distribution, publishers, research fields, and citations (Oluleye et al., 2022). It can also analyze various aspects of scientific publications, including collaboration networks, journal impact, and research topics, to gain insights into the development, structure, and dynamics of scientific knowledge, facilitating evidence-based decision-making (Oluleye et al., 2022). The analysis has utilized across various sectors, including construction and demolition, this analysis provides valuable insights into topics such as CE in construction (Illankoon and Vithanage, 2023), sustainability (Soyinka et al., 2023), waste management (Sharma et al., 2022), and barriers modeling (Oluleye et al., 2022). The present study utilized VOSviewer software, Mendeley, and Excel spreadsheet to conduct the scientometric analysis. Further details regarding the findings are elaborated on in subsequent subsections.
2.1.1 Preliminary research
Initial research was conducted using popular open-source tools such as Google scholar to evaluate the availability, suitability, and usability of published articles for review purposes. The preliminary investigation revealed a scarcity of systematic reviews on the subject matter. None provided comprehensive insights into the CE in CDWM, particularly regarding CDW monitoring, traceability and management tools, enablers, barriers, modern technologies, decision support systems, benefits, challenges, modeling approaches, performance measures, and existing frameworks. The identified gaps informed the development of robust research questions.
2.1.2 Database selection, search strategy, and data synthesis
The selection of an appropriate database is the most critical part of conducting a literature review, as improper selection may result in missing relevant articles (Jahan et al., 2022). Various databases are available, but the most popular once in the field of engineering and management are Scopus, Web of Science, and EBSCO (Illankoon and Vithanage, 2023; Soto-Paz et al., 2023). Choosing these databases also minimizes the chances of overlooking any relevant article. Therefore, this study opted for these databases for article search and data extraction. A basic search was conducted in the selected databases using the search string “AND”, “OR”, and “AND/OR”, in titles, abstracts, and keywords. Subsequently, articles were synthesized to remove duplicity. Several rounds of refinement were employed to improve the article search outcome, utilizing keywords such as “Circularity”, “Circular economy”, “Circular business”, “Building project”, “Housing project”, “Construction and demolition”, and “Waste”. The initial search yielded 818 articles from Scopus, 634 from Web of Science, and 712 articles from EBSCO. The search was performed independently by two authors to reduce the chances of missing articles, and the outcomes were then validated to minimize bias in the findings.
2.1.3 Inclusion and exclusion criteria
The inclusion and exclusion criteria for the present study were aligned with Oluleye et al. (2023). The inclusion criteria encompassed articles focusing on the circular economy specifically within the construction sector, articles published in peer-reviewed journals, and no restrictions on publication year. Conversely, the exclusion criteria comprised articles focusing solely on the circular economy without considering construction and demolition waste management issues, articles published in sources other than peer-reviewed journals, articles in languages other than English, and the exclusion of book chapters, conference papers, and editorial notes. Additionally, duplicate articles were removed during the synthesis of articles from three selected databases. This process resulted in 212 articles exported to VosViewer software for bibliometric mapping.
2.1.4 Bibliometric mapping of articles
Bibliometric mapping is used for the in-depth mapping of existing articles and is typically performed using various software available in the marketplace such as VosViewer, CiteSpace, BibExcel, etc. VosViewer is the most popular and widely used software for text mining in the construction sector (Soto-Paz et al., 2023). This software is extensively utilized for creating and visualizing massive networks. VOSviewer was adopted in this study for loading the dataset, data mining, keywords analysis, co-citation analysis, and analysis of countries and co-occurrences.
2.2 Critical analysis
A critical analysis of selected articles was performed using a theory-driven approach. Critical analysis entails conducting a comprehensive examination and evaluation of existing works, subjects, information, or ideas to understand their strengths, weaknesses, and implications (Jahan et al., 2022). The goal is to explore research developments and qualitatively identify gaps. This process provides deep insights into various aspects such as facts, observations, evidence, strategies, tools, techniques, challenges, and arguments, enabling a judgment to be formed through skeptical, rational, and unbiased evaluation. The critical analysis goes beyond general description or simple summarization of the contents. It requires the ability to engage in analytical thinking, critically assess, analyze, and articulate insights. Over the years, critical analysis has been widely utilized to explore the evolution and advancement of research across different sectors, including construction. The detailed information presented in Figure 1 is briefly discussed in the following subsections.
2.2.1 Manual screening
The 212 shortlisted articles underwent manual screening to select relevant studies aligned with the current research themes. Each article was individually reviewed in full text by two authors to ensure relevance and minimize outcome biases. This manual screening process resulted in 47 articles being retained for further data extraction.
2.2.2 Data extraction
The study employed a theory-driven approach to extract data from the shortlisted articles. Data extraction was conducted on the selected 47 articles to analyze applied methodologies, CDW monitoring, traceability and management tools, enablers, barriers, modern technologies, decision support systems, benefits, challenges, modeling approaches, performance measures, and existing frameworks. Content analysis of these articles discussing the mentioned aspects was performed and is presented in Appendix.
3. Results and discussion
3.1 Bibliometric mapping outcomes
The outcomes of bibliometric mapping for the present study were performed from the following perspectives: (1) publication trends, (2) mapping journal publications, (3) mapping countries, and (4) mapping keywords occurrence.
3.1.1 Publication trends
The yearly publication trend of the shortlisted 212 articles related to CE in the CDWM field is presented in Figure 2. In this pool, the earliest study was conducted by Esa et al. (2017). The outcomes show that the real implication of CE in CDWM started in 2017 and has been explored since then. However, the application of CE in CDWM is still in its primary stage or new for many nations across the globe, which is slowly gaining interest, as evidenced by the continually increasing publications. The findings also imply a significant interest in CE research in CDWM in the last six years. Our findings align with previous publications, which state CE as one of the hottest approaches extensively applied in the construction sector (Véliz et al., 2022; Luciano et al., 2021). The start of the New Year (2024) with two publications in the first week itself shows increased interest levels and commitment towards annual publication trends. The shift from a linear approach to CE in the construction sector represents the social and governmental thinking toward the conservation of natural resources for the long term. It is also observed that CE is becoming imperative in the construction sector worldwide in managing CDW. The continuous increase in publications also signifies a global shift in the construction sector from a linear approach to a sustainable one, aimed at preventing natural resource depletion and promoting conservation.
3.1.2 Mapping journal publications
Figure 3 represents that the 212 articles are published in 79 different journals. The outcomes imply that 41% of articles are published in 6 journals, which include sustainability (Switzerland) (11%), Journal of Cleaner Production (10%), Resource, Conservation and Recycling (6%), Materials (5%), Waste Management and Research (5%), and Waste Management (4%). The larger publication rate in sustainability background journals also implies a greater linkage of CE in CDWM to a sustainable direction. Moreover, the adoption of CE to manage CDWM is growing interest globally and has a strong association with sustainable research backgrounds.
3.1.3 Mapping countries
The network collaboration of authors’ countries helps in understanding the most productive countries in a specific research area. A clear understanding of the most productive countries is important in promoting research collaborations and funding (Ruiz et al., 2020). This study used the following search criteria for mapping countries in VOSviewer software: type of analysis: co-authorship, unit of analysis: countries, maximum number of countries per document: 25. While the threshold was set as the minimum number of documents of a country: 3 and the minimum number of citations of a country: 5. Based on these criteria, of the 60 countries developing articles on CE in CDWM, only 26 meet the threshold presented in Table 2. However, the results imply that a total of 13% (26 out of 195) countries across the world are conducting research on CE in CDWM areas. Based on the findings, 13% is a relatively low percentage that conforms to our previous findings related to the early stages of the CE concept in CDWM. The contribution of each country in terms of publications is presented by the size of the node in Figure 4.
Figure 4 shows that Spain and China have the largest node size than other contributors, indicating that these are the highest productive countries with 24 articles each. Italy, Australia, and the United Kingdom contributed with 23, 22, and 19 articles respectively. The most contributed countries in CE research in the domain of CDWM are Spain, China, Italy, Australia, and the United Kingdom. These countries might have implemented the CE concept in CDWM earlier than the other countries. Furthermore, the outcomes enlighten that developed countries are making more promising efforts than developing countries in promoting CE in CDWM fields. However, these efforts are still insufficient, as other countries such as Hong Kong, Germany, the Netherlands, Canada, Belgium, the United States, Austria, France, etc., are developed countries that have adopted CE in the effective management of CDW but have not conducted thorough research. This could be due to ineffective policy, lack of government support, or lack of experience in promoting CE for CDW management in the construction sector.
Moreover, Figure 4 represents six different clusters of countries based on how often they cite each other. For example, Australia, Greece, Iran, Malaysia, and Turkey belong to one cluster represented by the green color. The remaining countries are denoted in red, blue, yellow, pink, and purple color. Similarly, the network between countries and line thickness represents grater affinity; thus a strong link is represented by thicker lines.
3.1.4 Mapping keywords Co-occurrence
The key research areas of CE in CDWM were determined through mapping keyword co-occurrence. Utilizing the authors’ keywords, six clusters were identified (Figure 5). The keyword network aids in representing knowledge about key research areas and understanding how they are mutually interconnected and organized (Wuni et al., 2019). For keyword mapping, a minimum benchmark of three occurrences was set to ensure comprehensive cluster outcomes. During the process, some similar and redundant keywords were observed and combined using the thesaurus file. For instance, “Circular Economy (CE)”, “CE”, and “circular economy approach” were replaced by “circular economy”. A few redundant keywords such as “China”, and “bibliometric analysis” were removed to enhance outcome quality. After filtering results, 30 keywords remained, grouped into six different clusters. Figure 5 illustrates each cluster using different colors. The node size represents keyword co-occurrence, while line thickness indicates affinity. For example, the keyword “circular economy” exhibits the highest co-occurrence, and the thicker line between “circular economy” and “construction and demolition waste” represents a greater association between these two keywords. Each cluster, combined with key research areas, is discussed in detail below.
Cluster 1. This cluster includes keywords such as “BIM”, “buildings”, “circular economy”, “construction”, “material recovery”, “resource efficiency”, “sustainable construction”, “urban metabolism”, “urban mining”, and “waste minimization” (Figure 5). The classification of these keywords under a single cluster signifies grater linkages among them. However, the results imply that the majority of authors focused their research on these themes. For instance, most studies related to CE in CDWM discussed BIM (Building Information Modeling), a structured process involving the systematic generation and management of building information using various software, digital tools, and technologies (Ismail, 2023; Mollaei et al., 2023; Takyi-Annan and Zhang, 2023; Jayasinghe and Waldmann, 2020). Furthermore, BIM can contribute to improving material recovery and increasing resource efficiency in construction projects through material tracking and management, waste minimization, optimized design and planning, resource visualization, asset management, and recycling. Circular economy and construction and demolition waste management are the most prominent keywords in this cluster based on their node size, indicating a greater interest in these two research areas compared to others in this cluster. However, most studies focused on construction and demolition waste management strategies, policies, and challenges, while a structured roadmap to implement CE for effective management of CDW is still limited (Jahan et al., 2022). Therefore, future studies should focus on developing theoretical and conceptual roadmaps for CE adoption in CDWM.
Cluster 2. This cluster includes keywords such as “construction and demolition waste”, “construction material”, “mechanical properties”, “recycled aggregates”, “recycled concrete”, “sustainability”, and “sustainable development”. These keywords are related to construction and demolition waste materials, their circularity, properties, and sustainability. Extensive research on CE in CDWM has been conducted in these areas (Almokdad and Zentar, 2023; Li et al., 2023; Tefa et al., 2022; Morón et al., 2021), demonstrating sustainable development in the construction sector. However, the use of recycled aggregates and concrete was more explained compared to other CDW materials such as steel, wood, glass, and plastic (Meglin et al., 2022). Figure 5 illustrates that “construction and demolition waste” and “sustainability” have a bigger node size, indicating greater interest in these two topics than others classified in this cluster. Furthermore, there is minimum research on other CDW materials and their sustainability strategies, suggesting a need for future research in these areas. Moreover, there is limited research on trading platforms and customer buying interest in recycled, reused, and recovered materials through CDW.
Cluster 3. This cluster encompasses keywords such as “build environment”, “construction and demolition waste management”, “construction waste”, “machine learning”, and “material flow analyses”. Previous studies have focused heavily on planning structured construction processes and proper management of CDW during the planning stage (Rybak-Niedziółka et al., 2023; Cristiano et al., 2021; Lachat et al., 2021). However, the implementation of CE in the planning stage of construction effectively contributes to the systematic management of CDWs (Ismail, 2023). Furthermore, digital technologies such as machine learning and artificial intelligence contribute to predicting hazardous materials in buildings (Yu et al., 2022). Additionally, the material flow analysis (MFA) approach has the potential for proper management of CDW materials. The MFA system helps understand the process function and its interrelation in CDW management (Abdelshafy and Walther, 2023). Although systematic linkages between MFA systems, resource optimization, waste minimization, and CDW management need further exploration.
Cluster 4. Substantial contributions have been made in the areas of CDWM, as evidenced in Figure 5, where key research themes such as “reuse”, “demolition”, and “resource recovery” are classified under a single cluster. Reuse is a major keyword in this cluster due to its larger node size than others, indicating its higher significance in CDWM. The high prominence of “reuse” in CDWM itself represents the need for CE in the effective management of CDW. Furthermore, the reuse concept contributes more to resource conservation and sustainable development. Although research exists related to resource recovery in CDWM areas, there is a lack of a structured approach or automated systems available for CDW recovery (van den Berg et al., 2023). Moreover, limited research has been conducted on the challenges of material recovery and the adoption of used CDW materials. Additionally, research on the development of an efficient decision support system for effective CDW management and its association with resource recovery is scarce. The development of such an integrated system could be highly beneficial for optimizing resource recovery, minimizing CDWs, regulating compliance, assessing environmental impact, supporting decision-making, collaborating with stakeholders, and bringing continuous improvement in CDWM.
Cluster 5. This cluster encompasses only two keywords: “construction project” and “life cycle assessment”. The research contribution in this cluster focuses on the life cycle assessment of construction projects. The life cycle assessment of construction projects is one of the most effective ways to assess the impact of construction materials, methods, approaches, components, and products on the environment (Tefa et al., 2022). However, the systematic analysis of materials’ life cycle in construction projects contributes to minimizing landfill wastes, ultimately aiding in resource conservation and sustainability (Ivanica et al., 2022). Life cycle assessment has a larger node size in this cluster, demonstrating its higher contribution to literature in CDWM areas. Although studies focus on the life cycle assessment of construction materials, the limited contribution is noticed on life cycle assessment indicators and a structured assessment approach in the CDWM field.
Cluster 6. This cluster consists of two key research themes: “concrete” and “recycling” (Figure 5). This cluster illustrates the circularity approach of concrete material, mainly produced from construction and demolition projects. The recycling approach helps promote sustainability and conserve natural resources for the future (Czekała et al., 2023). Several CE strategies exist in the literature such as Refuse, Rethink, Reduce, Reuse, Repair, Remanufacturing, Refurbish, Repurpose, Recycling, and Recover, but Recycling is extensively adopted in the CDW field (Ramos et al., 2023a, b). Several CDWs that cannot be used directly could be recycled (Oluleye et al., 2023). Although the recycling strategy is applied to various CDW materials, there is still research needed to develop a structured decision support system that can be integrated with CE strategies.
3.2 Critical review outcomes
The outcomes of the critical review for the present study are based on the following themes: (1) Research characteristics, (2) CDW monitoring, traceability, and management tools, (3) Benefits and challenges of CE in CDWM, (4) Modeling approaches for CDWM, (5) Modern technologies for CDWM, (6) Decision support system developed for CDWM, (7) Enablers discussed in previous publications, (8) Barriers reported in previous articles, (9) Performance measures covering CDWM, and (10) Existing CE-based CDWM models/frameworks.
3.2.1 Research characteristics
Over the past few years, research in the CE domain, specifically in the CDW management field, has been conducted, utilizing various research types to increase understanding and promote the shift from linear to CE. These research types include deductive research, qualitative, quantitative, mixed-method study, case study, descriptive, and theoretical research (Table 3). A summary reveals that case study, quantitative, qualitative, and mixed-method research have been extensively utilized by researchers than other approaches, indicating these research types are more appropriate for emerging/developing research fields. However, survey and interview methods have gained momentum in recent years, representing their strength in capturing individual perceptions, knowledge, and experience for making critical decisions. Additionally, these methods help increase researchers’ knowledge through the utilization of modern tools, techniques, or software such as NVivo, Microsoft Teams, LinkedIn, Zoom, SPSS, Google Meet, SPSS, Qualtrics, Excel, R, Python, Google forms, and Survey Monkey. Although some statistical approaches are gaining attention, modeling approaches and survival analysis to solve CDWM problems in CE are scarce. Moreover, few studies applied machine learning for CDW management; the application of artificial intelligence in this field could bring impactful benefits in managing CDWs. Therefore, attention should be given to AI research in the future to promote digitalization in the CE transition in the CDWM field. It has also been observed that the application of IoT and blockchain has been extensively applied in the construction sector, but there is a lack of practical applicability, especially in the management of CDW. Therefore, the adoption of these innovative technologies into CDWM could bring extensive sustainable benefits. For example, the adoption of IoT devices such as mobile applications and sensors can capture information about CDW. Robotics can recover CDW within a minimum time period. Meanwhile, the adoption of blockchain applications secures CDW data with transparency (Bao and Lu, 2020).
3.2.2 CDW monitoring, traceability and management tools
Tools are an essential part of optimizing any process, reducing time, effort, and resources, ensuring accuracy, and improving quality. The right tool can efficiently complete tasks within the designated time frame, facilitating project completion by the due date (Guo et al., 2022). Time is a crucial constraint in CDW management, and tools can help minimize it, enhancing overall efficiency and reducing CDW management costs (Shooshtarian et al., 2022a, b, c). The summary of tools used in CDW management is presented in Table 4. The findings reveal that there are very few tools existing in previous research; therefore, there is a need to develop more advanced tools for CDW management.
3.2.3 Benefits and challenges of CE in CDWM
The terms “benefits” and “challenges” are interconnected, as understanding the benefits can motivate overcoming challenges. However, challenges arise alongside benefits, associated with adopting circular practices in effective CDWM. Understanding and addressing these interconnected terms are crucial for successfully integrating CE principles into effective CDW management in the construction sector (Huang et al., 2018; Luciano et al., 2022; Al Zulayq et al., 2022). Facing challenges is essential for both personal and organizational growth because it pushes us out of our comfort zones, encourages the development of new skills, and fosters resilience (Huang et al., 2018). Furthermore, challenges identified in the adoption of CE practices in organizations can serve as opportunities for continuous improvement (Bao and Lu, 2020). Effectively addressing CE challenges in CDW management can enhance organizational performance, leading to higher benefits (Oliveira et al., 2021). Figure 6 depicts the common challenges and benefits existing in the literature.
3.2.4 Modeling approaches for CDWM
Modeling approaches play a vital role in CDWM by providing structured models to guide, understand, analyze, and optimize the processes involved. They aid in decision-making across various aspects such as scenario analysis, life cycle assessment, resource optimization, technology integration, policy development, and continuous improvement (Ma et al., 2022; Kabirifar et al., 2023). Modeling enables quantitative analysis of factors like total quantity, type, and nature of wastes generated in construction and demolition projects (Sobotka and Sagan, 2021), as well as assists in resource optimization including materials, manpower, equipment, and circular facilities (Kabirifar et al., 2023). Additionally, modeling facilities assess life cycle assessment approaches, considering the environmental impact of construction and demolition (C&D) materials and circular processes from extraction to disposal (Ma et al., 2022). Various applications and advantages of modeling approaches in the field of CE in CDWM have been observed, and a few approaches discussed in existing articles are summarized in Table 5.
3.2.5 Modern technologies for CDWM
Technologies play an important role in the C&D field by introducing innovative solutions to manage CDW, resulting in improved efficiency, enhanced resource recovery, and maintained material circularity. Modern technologies aid in better planning, monitoring, tracing, sorting, and optimizing C&D wastes, leading to enhanced resource consumption and sustainability (Wu et al., 2022a). The existing modern technologies in the reviewed articles in the context of CDWM are presented in Table 6.
3.2.6 Decision support system developed for CDWM
A decision support system (DSS) is a comprehensive tool that assists stakeholders in various aspects of CDWM, playing a crucial role in facilitating effective decision-making in this field and leading to improved planning and management of C&D wastes (Sobotka and Sagan, 2021). The integration of DSS in CDWM can enhance decision-making processes by optimizing resources, managing data, ensuring compliance, analyzing scenarios, tracking information, generating reports, and promoting collaborations among stakeholders (Saeed et al., 2023). However, the absence of DSS in the CDWM process results in a less streamlined process, leading to inefficient operational efficiency of organizational processes (Tsydenova et al., 2021). This leads to resource wastage, data integrity, and security risks, reduced environmental impact, and impact on stakeholders and overall strategic objectives. Therefore, efforts are needed to develop the right DSS to mitigate these losses. Table 7 presents the DSS proposed in previous studies.
3.2.7 Enablers discussed in previous publications
Enablers of CE play a vital role in optimizing CDW management, enhancing resource efficiency, and promoting circular materials. These enablers drive the implementation of modern technologies in CDW management, facilitating innovative processes such as smart waste tracking, collection, sorting, and recycling techniques (Noll et al., 2019). Addressing these enablers effectively is crucial for the successful adoption of CE practices in CDW management, as failure to do so can lead to unsustainable losses (Mahpour, 2018; Yu et al., 2022). Therefore, organizational managers must consider these enablers and address them effectively before initiating CE adoption. The CE enablers related to CDW management, identified in reviewed articles, are provided in Table 8, which includes enablers across various dimensions such as cultural, environmental, organizational, technical, regulatory, and economic.
3.2.8 Barriers reported in previous articles
Barriers serve as obstacles that hinder the successful adoption of CE practices in managing CDW (Liu et al., 2021). However, the consideration of CE enablers in the construction industry helps managers in the effective management of CDWM, whereas ignoring barriers could lead to failures (Shooshtarian et al., 2022a, b, c). Therefore, proper consideration of CE barriers is also mandatory, along with considering enablers, to increase the chances of successful implementation of CE in organizations for the effective management of CDW. The barriers proposed in reviewed articles are presented in Table 9.
3.2.9 Performance measures covering CDWM
Performance measures are essential parameters for assessing the effectiveness and efficiency of programs, projects, or initiatives. These measures are used as primary inputs in the performance measurement process to evaluate the performance of any project, individual, group, system, component, or organization (Ratnasabapathy et al., 2021). However, performance measures are crucial for evaluating circular strategies and enhancing sustainability in the construction sector (Nie et al., 2024). Furthermore, these measures evaluate the efficiency and effectiveness of CDWM practices in minimizing environmental impacts and achieving the company’s circular goals. The performance measures used in previous studies are depicted in Figure 7. The financial perspective encompasses strategies and plans aimed at increasing revenue and managing a business's financial risk. An organization achieves these goals by meeting the needs of customers, shareholders, and suppliers. The customers' and stakeholders' perspective refers to evaluating a company's performance from the viewpoint of its customers and stakeholders. This assessment involves understanding their needs, expectations, and satisfaction levels regarding the products, services, and overall performance of the organization. The Internal Process perspective measures an organization's ability to meet customer needs and expectations through internal processes, products, and services. It encompasses various aspects such as manufacturing, marketing, sales processes, as well as customer service and support services. The learning and growth perspective examines the company's vitality in terms of training employees on rapidly changing technologies and enhancing their productivity.
3.2.10 Existing CE-based CDWM models/frameworks
A model or framework plays an important role in stepwise guiding stakeholders to attain project goals or objectives. The CE-based framework, integrated with various components including circular strategies, practices, tools, techniques, indicators, measures, support systems, and innovative technologies, helps in promoting sustainable practices in CDWM in the construction sector and conserving natural resources. The CE-based structured framework can assist managers and other associated employees in the effective management of CDW, resulting in enhanced resource efficiency, sustainability, reduced waste, environmental foot prints, improved financial benefits, stakeholder engagement, and compliance with regulations (Huang et al., 2018). The successful adoption of the CE framework in the construction industry can enhance circularity by effectively managing CDW and efficiently optimizing resources. Therefore, the adoption of a structured and clear roadmap is essential to integrate CE in CDWM in the construction sector. A few CE-based models/frameworks related to CDWM proposed in existing articles are presented in Table 10.
4. Recommendations for researchers, practitioners, decision-makers, and policymakers
The study findings provide stepwise recommendations for researchers, practitioners, decision-makers, and policymakers on how CE principles can be integrated into CDWM practices in the construction sector:
Researchers can conduct comprehensive case studies to analyze the adoption of CE principles in the real environment of CDWM projects by referring to previous studies' knowledge. They can explore innovative technologies discussed in this study for the reuse, recycling, and upcycling of CDW materials. Furthermore, life cycle assessment can be performed to investigate the economic viability and environmental impact of the current project. Additionally, investigating and comparing the enablers, barriers, and challenges discussed in the present study through collaborating with industry stakeholders. Finally, developing a strategy on how to adopt enablers, handle barriers, and overcome challenges. A structured framework can also be developed to simplify the process of CE adoption in the construction sector to effectively manage CDW.
Practitioners can implement CDW sorting and segregating systems to recover materials for reuse and recycling on construction sites. Hence, the incorporation of design for deconstruction and disassembly principles during the building design process could be an effective approach to maximize material recovery. The adoption of recycling facilities by establishing partnerships with waste management organizations could ensure smooth handling of CDW materials and reduce the social and environmental impact. Collaboration with waste management firms could also save time, effort, and resources in terms of the economy, improving quality, increasing construction speed, and enhancing the circular construction process. Additionally, educating construction managers, supervisors, and workers on the benefits, challenges, enablers, barriers, tools, performance measures, and modern technologies of CE principles and providing structured training on effective CDW reduction and recycling techniques.
Furthermore, the findings can guide decision-makers to develop rules and regulations such as waste diversion targets, incentives for sustainable construction projects, appraisals for resource reduction, increments for zero waste, and fast recovery, etc., towards implementing CE principles in CDWM practices. Funding and resource allocation within an organization for research and development initiatives could enhance the development of advanced CE methodologies and technologies for CDW management. Decision-makers can also collaborate with industry and academic stakeholders to establish benchmarks and standard practices for circular CDW management. Promoting public-private partnerships could enhance the collection, sorting, and processing of CDW materials in the construction sector. The implementation of CDW monitoring and traceability tools could also help to effectively manage CDW.
This study recommends policymakers to integrate CE principles into local and national CDW management strategies, targeting maximum material recovery and minimum landfill disposal. Policymakers should incorporate tax rebates and incentive schemes to adopt CE principles in the construction process. The identified barriers and challenges in this study towards implementing policies for circular construction can be overcome by collaborating between industry stakeholders, government agencies, and research institutions, leading to more sustainable and resource-efficient outcomes in the built environment.
5. Future research areas
The outcomes of this review reveal that the adoption of CE in the CDWM field is still in its initial stages. While studies have explored a few issues, there is a need for more in-depth exploration and research (refer to Table 11) to fully harness the potential of CE integration in CDWM. The future research directions are discussed pointwise in subsections to assist in implementing CE in CDWM within the construction sector.
5.1 Adoption of CE strategies in the CDWM field
Research on CE strategies specific to the CDWM field is limited, with the majority of existing studies focused on 3R (Reuse, Reduce, and Recycle). However, a thoughtful and systematic approach to selecting CE strategies for managing CDW is lacking. Furthermore, the implementation of CE practices and strategies cannot occur in isolation without considering its measures, contextual issues, and the dynamism of factors surrounding it (Oluleye et al., 2022). There is a scarcity of empirical research on measures for integrating CE strategies with CDW categories, the dynamism of factors affecting CE strategies, and contextual parameters for adopting CE based on economies. Moreover, less research has been undertaken on appropriate selection approaches of CE strategies in managing CDW. Investigating these issues through conducting empirical studies using mixed-method approaches (interviews, surveys, and site visits) would enhance CE implementation in the construction sector for CDWM.
5.2 Model for CE adoption enablers and barriers in CDWM
While studies on the barriers and enablers of CE in CDWM are prevalent in literature, a structured model for systematically considering these factors for effective CE adoption in the CDWM field is still scarce. Enhancing, the understanding of these enablers and barriers can improve their effective consideration within organizations, ultimately, leading to successful CE implementation in CDWM. Furthermore, such a structured model assists managers in identifying the leading factors, and optimizing the use of limited resources, time, and efforts, thus resulting in financial savings. Researchers can use multi-criteria decision-making (MCDM) tools to develop the structured model for CE adoption of enablers and barriers.
5.3 Development of CE readiness assessment tool in CDWM
Research on readiness assessment tools (RAT) for CE adoption in the CDWM field is limited. RATs are essential for evaluating the readiness level of CE adoption in CDWM and assessing the maturity level of CE adoption in waste management. Additionally, these tools aid in identifying factors crucial for the effective implementation of CE in CDWM. Therefore, future research focusing on readiness factors and the development of RATs for CE in CDWM is warranted. The identification and utilization of readiness factors for CDWM could help develop the RAT in the construction sector.
5.4 Integration of life cycle assessment indicators for CE in CDWM
While studies on the circular lifecycle of CDWs exist, the proper integration of LCA indicators with CDWM practices is still scarce. Integrating LCA indicators with CDWM practices would enable stakeholders to prioritize resource efficiency, circularity, and environmental sustainability when making decisions. Hence, empirical research on various LCA indicators at different phases of CDWM is necessary.
5.5 Development of a CE performance measurement system in CDWM
Research on performance measurement systems (PMS) for assessing CE adoption performance in managing and optimizing CDWs is limited. The need for a PMS is imperative as it will facilitate the evaluation of CE initiatives’ effectiveness in CDWM. A PMS could be designed to evaluate the efficiency of resource utilization, energy consumption, and emissions, material recovery and recycling, stakeholder involvement, waste minimization, and procurement in CE. The existence of a PMS would motivate construction and demolition practitioners, managers, and other stakeholders to make circularity decisions. Therefore, the development of a PMS for CE in CDWM is needed in the near future. The PMS can be developed by setting standards through collaboration among industry stakeholders, government agencies, and research institutions.
5.6 Contextual challenges of CE in CDWM and their solutions
CE challenges are prominent in the literature; few of them provide specific solutions based on their present problem. However, the contextual challenges for CE adoption, based on the economics of both developing and developed regions, and their specific solutions, are still scarce. A system could be developed to prioritize solutions based on associated challenges. Investigating this issue and developing a structured system would enhance the adoption of CE in the CDWM field. Empirical studies using survey methodology could help gather relevant information about the challenges of CE in CDWM from experts. Additionally, case studies involving interviews with practitioners, decision-makers, and planners could help identify potential solutions.
5.7 Roadmap for CE adoption in CDWM
Existing models/frameworks in the CDWM field still stand on the linear economy foundation. However, there are no systematic guidelines or structured paths to follow systematically toward achieving the successful adoption of CE in the CDWM sector (Govindan and Hasanagic, 2018; Oluleye et al., 2022). Further, the existing frameworks lack integration of measures, indicators, barriers, enablers, decision support systems, tools, techniques, standards, challenges, modern technologies, and knowledge management systems that support increasing the implementation success of CE practices in CDWM. The majority of existing models adopt cradle-to-cradle strategies as a replacement for the traditional linear model. These models mostly fail to achieve successful adoption of CE in CDWM due to several challenges such as inadequate standardization, absence of design standards for circularity, inadequate technologies, low financial incentives, lack of balance between supply and demand, and life cycle costs. Therefore, future studies should develop a new roadmap or improve existing frameworks towards effective adoption of CE in CDWM. The actual implementation of existing frameworks across multiple CDWM sites could offer insights into their applicability, challenges, and shortcomings, thereby guiding the modification or development of new frameworks.
5.8 Application of innovative and modern technologies for CE adoption in CDWM
In the fourth industrial revolution, the integration of Industry 4.0 (I4.0) technologies such as additive manufacturing, artificial intelligence, could computing, blockchain, digital twins, Industrial Internet of Things, machine learning, and autonomous robotic systems in CE for the management of CDW is still limited (Bao and Lu, 2020; Wu et al., 2022a). However, I4.0 technologies have emerged as key players in shifting from linear to circular economy practices in the manufacturing sector (Norouzi et al., 2021). The effective integration of I4.0 technologies in CE could efficiently manage CDW and promote sustainable development goals (SDGs). The compatibility of I4.0 technologies with CE practices facilitates optimizing resource utilization in the industrial system (Norouzi et al., 2021). Future studies are needed to explore these integrations through empirical studies to achieve circularity in CDWM.
5.9 Build an effective knowledge management system
Knowledge can drive innovative changes in any organization, and these changes can be realized through proper creation, sharing, and management of knowledge across the organization. However, the utilization of knowledge management in the area of CE in CDWM is limited. The construction sector in many developing and developed countries is even unaware of adopting CE practices in the CDWM field, and their understanding of how to promote CE for managing CDWs remains insufficiently illuminated (Mahpour, 2018; Oluleye et al., 2022). A knowledge management system facilitates creating awareness and improving in-depth understanding of concerned areas (Mahpour, 2018). Therefore, more research is needed to investigate the building process of an effective knowledge management system and its systematic integration with CE processes, especially in the CDWM field.
6. Conclusions
The CE serves as a production and consumption model, greatly impacting the management of CDWs. To discern trends and research issues in CDW management within the context of CE, a mixed-method review strategy was employed. This approach proved beneficial in mitigating the ambiguities inherent in solely qualitative or quantitative review techniques. Analyzing existing articles on CE in CDWM revealed prevalent research trends and highlighted ongoing debates, thus identifying knowledge gaps for future studies. The review delineates key research themes, explores ten issues, and knowledge gaps, and outlines directions for future research endeavors. Previous studies in the field extensively utilized surveys, interviews, case studies, or mixed-method approaches as methodologies, with a notable focus on CDW monitoring and traceability tools to enhance CE adoption rates in the construction sector. The outcomes of the present study have shed light on key issues and provided several suggestions for future research aimed at promoting sustainable construction. The successful incorporation of the suggested recommendations into the construction sector would help achieve zero waste goals, facilitate natural resource conservation, and reduce carbon emissions. This, in turn, would support society and improve the quality of life for people.
This research offers significant insights into CDW management by synthesizing previous studies, bolstering the practicality and efficacy of the CE in the construction and demolition industries. The findings pave the way for future research in the realm of CDW management within the CE paradigm, delineating avenues for researchers and academics to explore innovative approaches and expand knowledge in this field. Practitioners stand to benefit from understanding the challenges, enablers, barriers, tools, and modern technologies associated with CE adoption in CDWM. Construction and demolition managers can utilize identified performance measures to evaluate CE performance in CDWM, while policymakers can address associated challenges and barriers to inform policy adjustments or new developments. Additionally, construction and demolition planners can leverage existing frameworks to enhance their understanding and develop compatible frameworks for CDWM based on contemporary requirements and challenges.
Despite these significant contributions, this research has limitations. It focused solely on peer-reviewed articles published in journals, potentially influencing the coverage of publications on the topic. The use of specific keywords for article searches may introduce bias, with alternative keywords possibly yielding more relevant papers. Future investigations should consider these limitations for comprehensive exploration.
Figures
Top Countries exploring research on CE in CDWM
Countries | Documents | Citations | Total link strength |
---|---|---|---|
China | 24 | 1,940 | 19 |
United Kingdom | 19 | 1,782 | 18 |
Spain | 24 | 1,376 | 17 |
Italy | 23 | 883 | 15 |
Australia | 22 | 560 | 12 |
Hong Kong | 14 | 992 | 11 |
United States | 8 | 334 | 11 |
Canada | 10 | 57 | 10 |
Chile | 6 | 40 | 5 |
India | 9 | 128 | 5 |
Malaysia | 4 | 170 | 5 |
Turkey | 7 | 54 | 5 |
Brazil | 8 | 101 | 4 |
France | 10 | 72 | 4 |
Iran | 3 | 283 | 4 |
Netherland | 9 | 330 | 4 |
Poland | 6 | 65 | 4 |
Belgium | 4 | 14 | 3 |
Portugal | 9 | 268 | 3 |
Switzerland | 6 | 84 | 3 |
Austria | 7 | 210 | 2 |
Colombia | 7 | 76 | 2 |
Denmark | 3 | 25 | 2 |
Germany | 9 | 480 | 2 |
Greece | 3 | 43 | 1 |
Serbia | 3 | 21 | 1 |
Source(s): Table created by authors
Summary of research characteristics
Research type | Method | Software/Tools/Technique | Statistical test/Analysis approach | Reference |
---|---|---|---|---|
Deductive research | Hypothesis development | Wilcoxon signed-rank test, Shapiro-Wilk test | Ramos et al. (2023a, b) | |
Qualitative | Semi-structured interviews | NVivo, Microsoft Teams, LinkedIn, Zoom, SPSS, Google Meet | Delphi technique, Fuzzy analytic hierarchy process (FAHP), Thematic analysis, Balanced scorecard approach | Boateng et al. (2023), Ramos et al. (2023a), Boonkanit and Suthiluck (2023), Villoria Sáez et al. (2023), Shooshtarian et al. (2022a, b, c), Torgautov et al. (2022), Sobotka and Sagan (2021), Huang et al. (2018) |
Quantitative | Survey | Timed Petri net, Google Forms, Survey Monkey, Qualtrics, Excel, R software, SPSS | Barrier mapping, MICMAC analysis, Exploratory factor analysis (EFA), Rank agreement analysis (RAA), Fuzzy synthetic evaluation (FSE), Contingent valuation method, fuzzy TOPSIS | Ma et al. (2023), Véliz et al. (2023), Oluleye et al. (2023), Shooshtarian et al. (2022a), Véliz et al. (2022), Wu et al. (2022b), Guo et al. (2022), Salleh et al. (2022), Mahpour (2018) |
Mixed Method study (Qualitative and Quantitative) | Interview and Survey | SPSS, Qualtrics, Excel, NVivo, Google Forms, Microsoft Teams, Zoom, Google Meet | ANOVA, SWOT analysis, Relative Importance Index (RII), Factor Analysis, Regression analysis | Ma et al. (2023), Kabirifar et al. (2023), Meng et al. (2023), Cheng et al. (2023), Luciano et al. (2022), Liu et al. (2021), Esguícero et al. (2021), Condotta and Zatta (2021), Noll et al. (2019), Ghaffar et al. (2020), Bao and Lu (2020) |
Case study | On-site visits and data collection | 3D printer, i-Tree Canopy | Resource mapping, Environmental screening, Deep convolutional neural networks, Mathematic modeling, Optimization modeling, SWOT analysis | Saeed et al. (2023), Christensen et al. (2022), Rigillo et al. (2022), Lin et al. (2022), Mercader-Moyano et al. (2022), Tsydenova et al. (2021), Cristiano et al. (2021), Lachat et al. (2021), Davis et al. (2021), Oliveira et al. (2021), Mihai (2019) |
Descriptive Research | Data collected from online repositories | Machine learning | Wu et al. (2022a), Jayasinghe and Waldmann (2020) | |
Theoretical Research | Analysis of scientific and practical information | Mathematical modeling | Shuvaiev et al. (2022) |
Source(s): Table created by authors
Summary of CDW monitoring and management tools
Tool | Objective | Entities/User | Ability | Reference |
---|---|---|---|---|
CORDOVA Mobile Application | Helps estimate, trace, and manage the amount of CDW generated, ensuring proper waste management | Construction managers, CDW truck drivers, Recycling plant managers | Estimate the total amount, type, total distance traveled, and total cost of CDW, and generate the report | Villoria Sáez et al. (2023) |
i-Tree Canopy software | Identifies the total available buildings in the area, and estimates materials | Evaluators | Obtains buildings-related data | Cristiano et al. (2021) |
Mobile app | Traceability and Management of CDW | Construction companies, Citizens, CDW disposal companies | Commercialize, donate, exchange, advertise | Oliveira et al. (2021) |
DECORUM platform | Helps manage CDW efficiently with transparency | Public tender, Design, and construction company, CDW managers | Facilitates green public procurement | Luciano et al. (2021) |
Building Information Modelling (BIM) | Stores material information, building components, and promotes the recycling and reuse of components | Projects and Materials managers | Extracts materials and component information | Jayasinghe and Waldmann (2020) |
Source(s): Table created by authors
Modeling approaches for CDWM
Modeling method | Objective | Reference |
---|---|---|
Integrated Fuzzy Delphi Technique and Analytic Hierarchy Process | To adopt the CE in CDW management | Kabirifar et al. (2023) |
Timed Petri Nets | To develop a trading platform for CD wastes | Wu et al. (2022b) |
Replication Dynamic System Four-Party Game | To develop a system for sustainable CDW recycling | Guo et al. (2022) |
Kolmogorov’s Differentiated Equations | To develop a model for forecasting the total CDW amount | Shuvaiev et al. (2022) |
Integrated System Dynamics and LCA Approach | To develop an integrated model for evaluating the carbon emissions of CDW | Ma et al. (2022) |
Multi-criteria Analysis Module | To identify the most favorable solution for managing CDW | Sobotka and Sagan (2021) |
Dynamic Stock-Driven Modelling | To assess the CDW material flows associated with the construction sector | Noll et al. (2019) |
Source(s): Table created by authors
Modern technologies for CDWM
Technology | Objective | Reference |
---|---|---|
Digital Twin | To deal efficiently with real-time and dynamic information concerning CDWM | Meng et al. (2023) |
3D Printing | To construct buildings using recycled aggregates and produce cement mortars suitable for 3D printing technology | Rigillo et al. (2022) |
Deep Convolutional Neural Networks | To classify and automate CDW separation | Lin et al. (2022), Davis et al. (2021) |
Machine Learning | To predict potential hazardous CDW inventories | Wu et al. (2022a) |
GPS-Based Vehicle System | To systematically transport CDW | Bao and Lu (2020) |
Source(s): Table created by authors
Decision support system for CDWM
Decision support system | Objective | Reference |
---|---|---|
Multi-objective model | Optimizes decision-making for managing CDW generated during construction project demolition | Saeed et al. (2023) |
Decision-Making Support System | Helps in selecting the appropriate concrete waste management approach using Fuzzy AHP | Boonkanit and Suthiluck (2023) |
Bi-objective mixed integer linear optimization model | Provides information about the location of installed sorting screens and material flows from building demolition to the construction of new buildings | Tsydenova et al. (2021) |
Spider web method | Supports the decision-making process of technology selection solutions for concrete waste management | Sobotka and Sagan (2021) |
Source(s): Table created by authors
Existing enablers in articles
Dimensions | Enablers | Author(s) |
---|---|---|
Cultural | Increase awareness of CE adoption benefits in CDW management | Gherman et al. (2023), Oluleye et al. (2023) |
Provide training/organize workshops to teach CE adoption for CDWM | Gherman et al. (2023), Oluleye et al. (2023) | |
Promote the green image of organizations | Gherman et al. (2023) | |
Environmental | Site waste management | Noll et al. (2019), Kabirifar et al. (2023), Ma et al. (2023) |
On-site sorting, recycling, and reusing of wasted material | Bao and Lu (2020), Kabirifar et al. (2023), Oluleye et al. (2023) | |
Waste avoidance | Kabirifar et al. (2023) | |
Use of durable materials | Ma et al. (2023) | |
Minimize the use of virgin materials | Gherman et al. (2023) | |
Organizational | Adoption of advanced processing and sourcing technologies | Charef et al. (2021), Ma et al. (2022, 2023) |
Adoption of advanced CDWM technics | Charef et al. (2021), Yu et al. (2022) | |
Demolition audits to increase CDW recyclability/reusability | Luciano et al. (2022), Kabirifar et al. (2023) | |
Collaboration between CDWM stakeholders | Gherman et al. (2023) | |
Integrate CE principles in the design phase | Gherman et al. (2023) | |
Management commitment and support | Gherman et al. (2023) | |
Availability of space for storage | Gherman et al. (2023) | |
Adoption of low waste generation technologies | Kabirifar et al. (2023) | |
Adoption of less wastes demolition techniques | Kabirifar et al. (2023) | |
Technical | Circular design | Esa et al. (2017), Mahpour (2018), Gálvez-Martos et al. (2018) |
Development of circular/green procurement system | Liu et al. (2021), Gherman et al. (2023) | |
Development of digital markets for secondary materials | Gherman et al., (2023), Shooshtarian et al. (2022a, b, c), Ma et al. (2023), Oluleye et al. (2023) | |
Develop tools and guidelines for CDW collection and separation | Gherman et al. (2023), Oluleye et al. (2023) | |
Development and adoption of circular business model and decision support system for CDW management | Oluleye et al. (2023), Gherman et al. (2023) | |
Develop CE metrics and indicators for CDWM | Oluleye et al. (2023) | |
Establish structured guidelines and roadmap for implementation of CE in CDWM | Oluleye et al. (2023) | |
Develop advanced CDW recycling logistics (e.g., Adverse logistics, GIS) | Pani et al. (2020), Yu et al. (2022) | |
Develop advanced demolition approaches (e. g. Deconstruction) | Ghaffar et al. (2020), Ginga et al. (2020) | |
Development and adoption of the advanced information technologies (e.g., BIM) | Charef et al. (2021), Ma et al. (2022), Gherman et al. (2023) | |
Continuous research on CE-based research in CDW management | Oluleye et al. (2023) | |
Regulatory economic | Standards for secondary materials | Ma et al. (2023) |
Global agreement on regulations | Gherman et al. (2023) | |
Clear national plans on CE goals in CDWM and policy support | Gherman et al. (2023), Oluleye et al. (2023) | |
Improve secondary material value and quality | Sharma et al. (2022), Ma et al. (2023) | |
Incentives for waste recovery | Ma et al. (2023) | |
Incentives for utilizing Circular/Secondary materials | Ma et al. (2023), Gherman et al. (2023), Oluleye et al. (2023) | |
Increase costs of landfilling/penalties for illegal damping | Gherman et al. (2023), Oluleye et al. (2023) | |
Funding for circular projects | Gherman et al. (2023) | |
Budget allocation for CE adoption in CDWM by the government | Oluleye et al. (2023) |
Source(s): Table created by authors
Existing barriers in articles
Source(s): Table created by authors
Summary of existing CE-Based CDWM frameworks
CDWM phase I | Phase II | Phase III | Phase IV | Phase V | Reference |
---|---|---|---|---|---|
Preparation-(Planning, permitting, and licensing of CDWM operators) | Generation- (Activities leading to the generation of CDW) | Collection and Transport | Processing | Temporary Storage | Alite et al. (2023) |
Onsite CDW separation | Recycling of CDW considering government regulations | Auditor certification of recycled product | Sale in the end market | Shooshtarian et al. (2022a, b, c) | |
Set target | Establish infrastructure | Enact rules and regulations | Enforce and implement | Monitor, Control, Analyze, and feedback Research & Improve | HaitherAli and Anjali (2023) |
Characterization and selection of sample | CDW quantification | CDW environmental indicators | Material resource circularity | Mercader-Moyano et al. (2022) | |
Generation (CDW generation through traditional/selective approach) | Source separation (concrete, recyclable, non-recyclable, or other materials) | Collection and transport | Waste treatment (Stationary/Mobile recycling, landfill, biological plant) | Substitutions (Plastic, Insulating, Wood, Natural aggregates, etc.) | Iodice et al. (2021) |
CDW collection from sites and Transportation | Cursing and Grinding of CDW | Separation through Flotation, Magnetic, Washing, etc | Production and Storage | Transport for use and landfill | Lachat et al. (2021) |
CDW collection | Transportation | Recycling plant | Marketplace | Use in construction | Luciano et al. (2021) |
Waste generation | Collection and Transport | Inspection | Recycling/Reuse/Final disposal | Esguícero et al. (2021) | |
Waste identification | Source separation and collection | Waste logistics | Waste processing | Use in construction | Condotta and Zatta (2021) |
Open dumping of CDW | Collection and disposal in Urban Landfills | Treatment and Reuse in Civil Construction | Integrated waste management system | Building materials | Mihai (2019) |
On-site CDW classification | Reclassification | Crush | Particle size classification | Material market/Backfill material/Landfills/Roadbed filter | Huang et al. (2018) |
Source(s): Table created by authors
Summary of key issues from reviewed articles
Themes | Key findings | How knowledge could be improved |
---|---|---|
Research characteristics | The majority of the studies rely on surveys, interviews, case studies, and mixed-method strategy methodology | Integration of interview, survey, and case study methodologies could compare findings and enhance the soundness of outcomes |
CDW monitoring, Traceability, and Management tools | Only a few tools have been developed and introduced in the literature | Thorough contextual-based empirical studies are needed to understand actual needs and challenges in CDWM to rethink the development of new tools |
Benefits and Challenges of CE in CDWM | Case-based benefits and challenges are discussed | Comparative studies could help understand contextual economic-based challenges and provide solutions. A system could be developed to prioritize solutions based on associated challenges |
Modeling Approaches for CDWM | Few modeling approaches are used to solve issues related to CE in CDWM | Other modeling approaches such as optimization modeling, system dynamics modeling, agent-based modeling, network modeling, and conceptual modeling could be explored to solve CDWM-related issues |
Modern Technologies for CDWM | Limited application of modern technologies is observed | Effective integration of Industry 4.0 technologies such as additive manufacturing, artificial intelligence, cloud computing, blockchain, digital twins, Industrial Internet of Things, Machine learning, and autonomous robots could enhance the effective adoption of CE in CDWM areas |
Decision Support System Developed for CDWM | Existing decision support systems can decide on separate issues | The development of a single knowledge-based decision support system for CDWM could enhance CE adoption in the construction sector |
Enablers & Barriers Discussed in Publications | Enablers and barriers have been identified manually and listed | Developing a structured model could improve the successful implementation of CE in CDWM fields |
Performance Measures Covering CDWM | No metric system exists in the literature for performance measures | The creation of a proper metric system could improve the assessment of CE performance in CDWM effectively |
Existing CE-Based CDWM Models/Frameworks | Existing models or frameworks still rely on a linear economy foundation | Developing the framework by integrating indicators, measures, barriers, enablers, decision support systems, tools, techniques, standards, challenges, modern technologies, and knowledge management systems could improve the implementation success of CE practices in CDWM |
Source(s): Table created by authors
Content analysis of selected articles
Author(s) | Published journal | Study scope | Location | Data source | Objective | Findings |
---|---|---|---|---|---|---|
Ramos et al. (2023a, b) | Waste Management | Strategies to promote CE for CDWM | Portugal | Fieldwork | To test strategies to overcome identified problems and understand factors contributing to success | Successful CE implementation can be facilitated by frequent monitoring, proper training, and awareness |
Ma et al. (2023) | Sustainable Chemistry and Pharmacy | CSFs to deploy CE for CDWM | China | Interviews and Survey | To explore CSFs to adopt closed-loop CE for CDWM in China | CSFs for CDWM in a CE could overcome the present drawbacks of the 3R approach in China |
Boateng et al. (2023) | Journal of Material Cycles and Waste Management | The environmental and economic outlook of CDWM practices | Fargo | Interview | To apply life cycle assessment (LCA) and life cycle costing (LCC) to evaluate benefits of CDWM | The study found that a 75% reduction in CDW can reduce 35% environmental burden and generate income of $61/ton |
Ramos et al. (2023a) | Resources, Conservation & Recycling Advances | Management of construction and demolition wastes | Portugal | Interview | To understand the contribution of local scale dynamics in the promotion of CDWM from an operational perspective | Results reveal that strategies related to investment in local solutions improve the market for recycled aggregates |
Kabirifar et al. (2023) | Applied Soft Computing | MCDM modeling for CDWM | Tehran | Interview and Survey | To identify and prioritize factors affecting CE implementation in the CDWM field | Results indicate that ‘on-site sorting, reusing, waste recycling, and ‘waste management plans/regulations’ are the most important factors |
Meng et al. (2023) | Sustainability | Integration of Digital Twin and CE | Mixed countries | Interviews and Survey | To investigate CE implementation, as well as integration of digital twin and CE in CDWM | The digital twin has great potential to improve circular economy practice |
Alite et al. (2023) | Journal of Material Cycles and Waste Management | Challenges and opportunities on the road to circular economy | Pristina | On-site visits | To identify instruments and policies of sustainable/circular CDW management system for Kosovo | The analysis identified gaps in Kosovo's CDWM and its enforcement of existing CDW legislation |
Saeed et al. (2023) | Journal of Construction Engineering and Management | Environmental Impact and Cost Assessment for Reusing Waste | Canada | On-site visits | To propose a decision support framework (DSF) for managing construction waste generated during end-of-life activities | DSF is used to evaluate trade-offs for recovery planning activities |
Véliz et al. (2023) | Resources, Conservation & Recycling Advances | Modeling barriers to CE for CDW | Chile | Survey | To analyze the interaction of inhibiting factors impacting CE-CDW | Limited policy and regulation as key barriers impacting financial and technical elements of CE-CDW adoption |
Boonkanit and Suthiluck (2023) | Sustainability | Developing a Decision Support System for a Smart CDWM | Thailand | Interview | To develop a DSS to select the most appropriate concrete waste management method | The developed system helps in analyzing alternative solutions for CDWM |
Oluleye et al. (2023) | Sustainable Production and Consumption | Modeling success factors for systemic circularity | Mixed | Survey | To evaluate the CSFs for attaining systemic circularity in the BCI | The EFA helps organize the CSF pool, and the FSE helps establish the significance level between the two economies |
Villoria Sáez et al. (2023) | Buildings | Design a mobile application for CDWM | Madrid | Interview | To develop a hybrid mobile app for real-time traceability of construction waste management | The app allows estimation and tracing of the amount of CDW generated in real-time |
Christensen et al. (2022) | Resources, Conservation & Recycling Advances | Closing the material loops for CDW | Denmark | Case study | To demonstrate practices and procedures for reusing and recycling CDW | The findings analyze and discuss economic and practical barriers |
Rigillo et al. (2022) | Environmental Research and Technology | A process algorithm for C&D materials reuse | Italy | Case study | To identify the use of file-to-factory technologies in the reuse process of C&D materials | A process algorithm is designed for material reuse purposes in different contexts |
Shooshtarian et al. (2022a, b, c) | Sustainable Production and Consumption | Factors influencing the market for recycled CDW | Australia | Interview | To propose a waste market development framework and provide solutions to overcome current barriers | The findings guide the government and practitioners in facilitating end markets for CDW |
Cheng et al. (2023) | International Journal of Construction Management | Sustainable construction through CDWM practices | China | Published materials, Interview | To develop a systematic framework for analyzing internal and external CDWM conditions | The findings proposed five strategic recommendations for improving CDWM practices |
Victar and Waidyasekara (2023) | Waste Management & Research | Circular economy strategies for CDW | Sri Lanka | Interview, Delphi technique | To focus on waste generation, reduction, and optimization of resources in building project life cycles | Findings reveal 14 issues for effective CDWM |
Torgautov et al. (2022) | Sustainable Production and Consumption | Performance measures of the construction sector | Kazakhstan | Interview | To create a strategic framework to identify and select specific CE actions | The developed framework can measure CDW performance |
Lin et al. (2022) | Journal of Environmental Management | Deep convolutional neural networks for CDW classification | China | Site visit, Google search | To develop an efficient method for sorting CDW using deep learning and knowledge transfer approaches | The proposed method enables automatic sorting of CDW |
Shooshtarian et al. (2022a) | Engineering, Construction, and Architectural Management | An investigation into challenges and opportunities | Australia | Survey | To understand the challenges and opportunities of effective CDWM | The main barriers are “overregulation, lack of local market and culture, poor education, and low acceptance” |
Luciano et al. (2022) | Sustainable Chemistry and Pharmacy | Issues hindering widespread CDW recycling practice | Mixed | Desk research, survey, and interview | To discuss the issues hindering widespread CDW recycling practice | Difficulties have been analyzed and suggestions provided to improve waste recycling and reuse |
Véliz et al. (2022) | Waste Management | Willingness to pay for CDW | Chile | Survey | To analyze the willingness of companies to pay attention to improving CDWM | The outcome found a greater quantity of inert and non-inert wastes |
Wu et al. (2022b) | Sustainable Chemistry and Pharmacy | Trading platform for CDW recovery | China | Survey | To investigate the trading platform for CDWM | Findings compared the time delay of two kinds of CDW transaction processes |
Wu et al. (2022a) | Building and Environment | Predicting the presence of hazardous materials | Sweden | Records register | To highlight challenges in machine learning pipeline development | Models perform well on limited datasets; the model’s generalizability could be improved by collecting more data |
Mercader-Moyano et al. (2022) | Waste Management & Research | CDWM model applied to social housing | Mexico | Survey, and Case Study | To quantify on-site 61 Mexican social housing CDW | Findings reveal that social housing consumes 1.24 tm and produces 0.083 tm of CDW |
Guo et al. (2022) | Sustainable Production and Consumption | Sustainable development of CDW recycling systems | China | Case study | To develop a four-party evolutionary game model | Using this model, companies promote the sustainable development of CDWR systems |
Salleh et al. (2022) | Planning Malaysia | CE adoption guidance in CDWM | Malaysia | Survey | To develop the strategy for the adoption of CE for CDWM | Developed strategies can improve the performance of the current CDWM system |
Shuvaiev et al. (2022) | Eastern-European Journal of Enterprise Technologies | Managing the flows of CDW | Ukraine | Scientific and practical records | To manage CDW flows and examine the environmental and economic efficiency of the process | Proposed mathematical modeling could solve practical tasks effectively manage CDW flows |
Ma et al. (2022) | Waste and Biomass Valorization | Evaluating the Carbon Emissions of CDW | China | Case study | To provide a causal loop model for evaluating the carbon emissions of CDW | Five causal loops are developed for evaluating the life cycle of CDW |
Liu et al. (2021) | Journal of Cleaner Production | Explore barriers of CE in CDW recycling | India | Interview and Survey | To examine barriers to CE practices in the Indian construction industry | Findings reveal that Political, Social, and Economic category barriers affect CE adoption in emerging economies |
Tsydenova et al. (2021) | Waste Management | Optimized design of concrete recycling networks | Germany | Case study | To develop a DSS to investigate the economic impacts of recycling concrete from building demolition | RC aggregates are economically viable predominantly in areas without local supplies of natural aggregates |
Cristiano et al. (2021) | Journal of Cleaner Production | CDW in the Metropolitan City | Italy | Case study, Public databases | To provide useful feedback to stakeholders and administration to improve CDWM flows | The transition to CE in the concerned region is still at an early stage due to several weaknesses |
Iodice et al. (2021) | Waste Management | Sustainability assessment of CDWM | Italy | Case study | To focus on the socio-economic and environmental implications of the CDWM | The practices and socio-environmental benefits of selective demolition are significant |
Lachat et al. (2021) | Sustainability | From buildings’ end of life to aggregate recycling | France | Case Study | To present a life cycle inventory compilation and assessment study of two buildings | The results indicate that the transport of waste, and its treatment are the most impactful phases |
Davis et al. (2021) | Automation in construction | Classification of CDW | Australia | Case study | To identify and design CDW classifications using digital images of waste deposited in a construction site | This approach emulates authentic construction site scenarios where on-site sorting is difficult |
Oliveira et al. (2021) | Clean Technologies and Environmental Policy | Strategies to promote CE in the CDWM | Brazil | Case study | To identify strategies for CDWM at the regional level | These strategies were successfully operationalized through a case study |
Luciano et al. (2021) | Environmental Science and Pollution Research | CD recycling unified management | Italy | Case study | To develop an approach for managing CD projects to ensure compliance with technical standards and environmental criteria | This platform promotes an informed and transparent use of recycled products |
Esguícero et al. (2021) | Journal of Material Cycles and Waste Management | CDW management process modeling | Brazil | Interview, Direct observation | To develop a framework for managing CDWM processes | The framework could improve the quality of recycled products |
Condotta and Zatta (2021) | Journal of Cleaner Production | Reuse of building elements in the architectural practice | Europe | Interview, Desk Study, and Activity Analysis | This study discusses possible improvements of a circular built environment | The examined regulatory context highlights how the reuse of building elements |
Sobotka and Sagan (2021) | Automation in Construction | Decision support system in CDWM | Poland | Interview | To develop a model to support decision-making in concrete waste management | The model explains the management of concrete waste by recovery or disposal |
Mihai (2019) | Sustainability | CDW in Romania | Romania | Reports, Field observations | The paper performs a critical overview of the CDWM issues | The paper reveals the poor monitoring of CDW flows across Romanian counties |
Noll et al. (2019) | Resources, Conservation, and Recycling | Waste generation and EU recycling | Greece | Field survey, Interview | To develop a dynamic stock-driven model for different infrastructure and building types | Our results show that the material stock expanded from 175 t/cap to 350 t/cap, leading to an increase in annual CDW generation |
Ghaffar et al. (2020) | Journal of Cleaner Production | Pathways to Circular Construction | United Kingdom | Interview | To investigate current practices of CDWM and circular construction | The study revealed that government legislation on the reuse and recycling threshold for every new project |
Jayasinghe and Waldmann (2020) | Sustainability | Development of a BIM-based web tool | Luxembourg | Source data | To propose a BIM-based system to effectively manage the recycled materials and reused components | This system can extract the materials and component information of a building |
Bao and Lu (2020) | Science of the Total Environment | Efficient circularity for CDWM | China | Case study, Site investigations, Interview | This study reports lessons learned from China, which developed an effective CDW circular economy from a low base | The study findings can be used as a reference for other economies in developing effective circularity |
Huang et al. (2018) | Resources, Conservation, and Recycling | CDWM through the 3R principles | China | Interview | To investigate existing policies and management situations and analyze based on 3R principles | The primary barriers and key challenges are identified to improve the current situation based on 3R principles |
Mahpour (2018) | Resources, conservation, and recycling | Prioritizing barriers to adopting CE in CDWM | Iran | Survey | To identify and classify the barriers of CE in CDWM | The study classified barriers into three different categories: behavioral, technical, and legal |
Source(s): Table created by authors
Author(s) | Published journal | Period | Article considered | Database | Focus area | Applied methodology | Outcomes | Research gaps |
---|---|---|---|---|---|---|---|---|
Rodrigo et al. (2024) | Smart and Sustainable Built Environment | Up to 2022 | 365 | Web of Science | Digital technologies for CE in construction | Bibliometric, Text-mining, Content Analysis | Classified digital technologies into two categories | Focus solely on digital technologies |
Illankoon and Vithanage (2023) | Journal of Building Engineering | 2013–2022 | 78 | Scopus and Web of Science | Development of CE in the Construction Sector | Descriptive, Bibliometric, Content Analysis | Classified CE literature into eight different themes | Need to determine the impact of greenhouse gas emissions and digital technologies in realizing the benefits of CE adoption |
Soyinka et al. (2023) | Environment, Development and Sustainability | 2000–2021 | 4,374 | Web of Science | CDWM Overview from a Global Sustainability Perspective | Scientometric Review | Revealed active research on CDWM overview | Focused only on reducing, recycling, and reusing strategies |
Soto-Paz et al. (2023) | Journal of Building Engineering | 2010–2022 | 214 | Scopus and Web of Science | Comparative analysis of CDWM in Emerging and Developed Countries | Bibliometric Analysis | Highlighted the role of eco-design in reducing CDW | Focused only on a general overview |
Gherman et al. (2023) | Recycling | 2015–2021 | 72 | Open Source Article | Circularity Outlines in the CDWM | Descriptive | Provided strategy, enablers, Barriers, computational tools, and building material development process in CDW management | Inadequate emphasis on educational mechanisms and tools |
Zhang et al. (2023) | Journal of Environmental Management | 1990–2022 | 303 | Web of Science, Derwent Innovation Index | How CDWM has addressed SDGs | Descriptive, Bibliometric | Addresses trends in CDWM between the pre and post SDGs declaration era in academia and industry | Focus solely on industry and academia perspectives regarding how CDWM contributes to achieving SDGs |
Rayhan and Bhuiyan (2023) | Waste Disposal & Sustainable Energy | Not mentioned | 121 | PubMed, Scopus, Web of Science | Tools and frameworks of CDWM | Descriptive | Highlighted the tools and frameworks to manage CDW | Focus solely on tools and frameworks |
Papamichael et al. (2023) | Waste Management & Research | 2019–2023 | 51 | Scopus, Online sources | CE-based framework for CDW | Descriptive | Theoretical discussion on CE-based frameworks | Captured only CE-related frameworks |
Ismail (2023) | Engineering, Construction and Architectural Management | Up to 2021 | 20 | Scopus and Web of Science | Existing issues in CE practices during movement control order | Descriptive | Described the Sophisticated CE system solutions to manage the resources | Discuss key issues in CE practices during movement control order and explore how BIM can fill the gaps |
Rigillo et al. (2023) | International Journal of Architecture, Art and Design | 2016–2022 | 62 | Scopus | Circularity and digital technologies applicability in CDWM | Scoping Review | Explored the potential and limitations of digital technologies in circular CDWM | Focus solely on digital technologies |
Centobelli et al. (2023) | Journal of Cleaner Production | 1991–2020 | 4,027 | Web of Science | Sustainable and circular construction | Bibliometric analysis | Provided a bird-eye-view of existing quantitative and qualitative research within seven identified themes | Focused only on a general overview |
Santos et al. (2023) | Journal of Polymers and the Environment | Up to 2021 | Not mentioned | Not mentioned | Construction, renovation, & demolition (CRD) of plastic waste treatment | State-of-art | Reviewed status quo, challenges, technologies, opportunities, barriers, and recent initiatives on recycling CRD plastic waste | Only capture CRD plastic waste |
Oluleye et al. (2022) | Journal of Cleaner Production | 2014–2021 | 116 | Scopus | CE research on building CDW | Bibliometric, Content Analysis | State-of-the-art on five research issues | More focus on CE-strategies for building CDW |
Mhlanga et al. (2022) | Journal of Engineering, Design and Technology | 2005–2021 | 31 | Scopus | Shaping CE in the Built Environment in Africa | Bibliometric Analysis | Identified low CE research output in Africa | Focused only on African perspectives |
Jahan et al. (2022) | Sustainability | 2009–2020 | 49 | Scopus, Web of Science, and Google Scholar | CE of construction and demolition wood waste | Bibliometric, Content Analysis | Identified waste management strategies involved in construction life cycle phases | Focused only on wood waste |
Yang et al. (2022) | Journal of cleaner production | Up to 2022 | 1068 (Construction field) 873 (Manufacturing field) | Scopus and Web of Science | Attaining Circularity in construction | Scientometric review and cross-industry exploration | Circularity could be attained through the use of remanufactured and recycled non-CDW | This review outcomes are not specific to construction sector |
Shooshtarian et al. (2022a, b, c) | Sustainable Production and Consumption | 2000–2021 | 62 | Google Scholar, Web of Science and Scopus | CE in the Australian CDW Management | Descriptive and Thematic analysis | Identified CDW disposal reduction opportunities and barriers in materials lifecycle | Focused only on Australian context |
Aslam et al. (2020) | Journal of Environmental Management | Not mentioned | Not mentioned | Online platforms | CDWM in China and USA | Thematic Analysis | The USA has a more developed CDWM system than China due to some management deficiencies | Considered articles related to China and the USA only |
Jin et al. (2019) | Resources, Conservation, and Recycling | 2009–2018 | 410 | Scopus | Overview of CDWM research | Bibliometric Analysis | Provided the overall picture of CDWM-related research | General science mapping of articles |
Present study | - | Up to 2024 | 212 | Scopus, Web of Science, EBSCO | State-of-the-art research on CE implementation in CDWM | Mixed-method (scientometric and critical analysis) | Uncovered the evolutionary progress, explored ten issues, and provided avenues for future research of CE in the CDWM fields |
Source(s): Table created by authors
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Acknowledgements
Funding: This publication is based upon work supported by Khalifa University of Science and Technology, Abu Dhabi, United Arab Emirates under Award No. FSU-2023-007.