Although the circular economy is an emerging topic, the related concepts remain at the development stage. For example, 114 definitions of the circular economy exist. However, despite such a significant quantity of research, there is still a considerable gap between theory and practice. This study aims to investigate the level of consensus between practice and academia in perceiving the circular economy, with a specific focus on the perceived barriers to circularity in the fast fashion industry.
Using both a systematic literature review and primary investigation, 241 barriers were identified, and the relevant similarities and dissimilarities between them were noted.
The results demonstrate a lack of clear certification and an overlap between sustainability and circularity. Nevertheless, there was some convergence between the two study groups.
It is crucial to acknowledge potential variations in findings among the studies included because of their unique features and the challenges of generalising them to other contexts.
This research can help align academic insights with practical challenges, enabling fast fashion companies to more effectively address circular economy barriers and implement sustainable strategies.
We present a comparative analysis of practitioners’ and academics’ perceptions of circular economy barriers, grounded in the research–practice gap.
1. Introduction
Global materials consumption and waste generation are projected to double annually by 2050, making the transformation toward sustainable economic and production systems imperative (Liu et al., 2022). In this context, resource efficiency using fewer of the Earth’s already limited materials has become a central principle of sustainable development. The rational use of scarce resources aligns with the objectives of the circular economy (CE), widely recognised as a leading framework for promoting sustainability. Accordingly, transitioning from a linear to a circular economy is essential to achieving both economic and environmental sustainability and has become a strategic priority across nations.
Despite this momentum, defining and overcoming barriers to CE implementation remains a persistent challenge. While many organisations have begun adapting their business models to integrate circularity principles, the actual adoption of circular economy business models within the manufacturing sector is still limited. Raspini et al. (2022) emphasise that the transition from linear to circular systems is complex, and progress in overcoming the associated barriers has been slow.
This study is particularly motivated by developments in the textiles and fashion sectors, where annual consumption has doubled in recent decades (Shirvanimoghaddam et al., 2020), leading to shorter clothing lifecycles and a dramatic increase in post-consumer textile waste. For instance, in the UK alone, approximately £140 million worth of clothing is discarded in landfills each year. The fast fashion segment poses specific difficulties due to the high volume of production and rapid consumption cycles. Studies suggest that the growth of fast fashion has been largely driven by impulse buying behaviours (Fares and Lloret, 2023; Fares et al., 2023a, b, c).
Within this context, our work builds on the ongoing academic–practitioner paradox, which concerns the limited practical relevance of much academic research. Bartunek and Rynes (2014) argue that academics and practitioners operate under distinct logics: scholars focus on theory-building and methodological rigour, while business organisations prioritise problem-solving and performance outcomes. This divergence highlights the importance of studying how knowledge flows between academia and practice.
Previous research has underscored this divide, often referred to as the “research–practice gap” (Schleper et al., 2021). The growing demand for research that directly benefits society and business has intensified the interaction between scholars and practitioners, but also increased competition and fragmentation between the two communities (Schultz and Hatch, 2005). Several studies have traced this divide to epistemological differences (Bansal et al., 2012). For instance, in supply chain forecasting, researchers have been criticised for overlooking issues of immediate practical relevance, leaving theory lagging behind real-world practice (Syntetos et al., 2016). Hence, this gap represents a tension between those who create knowledge and those who apply it.
To address this conceptual gap, this study draws upon the theory of concepts, which provides an analytical lens for understanding how concepts are structured, acquired, and applied. Rast (2018) explains that concepts are embedded within broader theoretical systems, involving higher-order cognitive processes such as reasoning, inference, explanation, and categorisation. This approach requires attention to formal elements like nominalisation and the assessment of similarity and typicality. Similarly, Hjørland (2009) views concepts as contextually defined within theoretical frameworks, emphasising the causal relationships that underpin conceptual understanding. However, as he notes, consensus remains limited regarding the classification and definition of concepts.
Recent scholarship has further advanced the debate on circular economy adoption in the textile industry. For instance, De Felice et al. (2025) conducted a systematic review on CE practices in textiles, concluding that factors such as technology type, work intensity, and supply chain structure strongly influence CE adoption and sustainable performance. Similarly, Das et al. (2025) proposed a sustainable circular economy model for textile waste reduction and value creation, highlighting strategies like resale, reuse, repurposing, and rental, alongside their environmental and economic benefits. However, despite these contributions, there remains a clear gap in comparing barriers to CE implementation as understood by academics versus those recognised by practitioners. This distinction is vital, as misalignment between theoretical and practical understandings can hinder real progress toward circular transformation.
Based on this, the following research questions guide the present study:
What are the barriers to circular textiles and fashion?
How do these barriers differ when defined from academic and practitioner perspectives?
This paper contributes to the circular economy literature by offering an integrated analysis of barriers to CE adoption in the fashion and textile industries, combining insights from both academic research and practitioner experience. It bridges theoretical frameworks with practical realities, advancing understanding of how diverse barriers influence circular implementation.
From a practical standpoint, the study provides industry professionals with an evidence-based overview of the key challenges in transitioning toward circular models, as well as strategies informed by practitioner experience to overcome them. These insights can inform both managerial decision-making and policy development, hence supporting a more effective and equitable shift toward sustainability in the global textile and fashion sectors.
2. Methodology of the research
2.1 Systematic literature review
A systematic literature review (SLR) was used due to its capacity to methodically address the formulated questions while mitigating biases related to content evaluation and source selection (Senali et al., 2022). Specifically, we used the Preferred Reporting Items for Systematic Reviews and Meta-Analysis (PRISMA) framework for its ability to precisely identify and evaluate existing published research. Moreover, PRISMA ensures transparency and robustness throughout the analysis process, encompassing stages such as identification, screening, eligibility, and inclusion.
Records were identified using the Scopus and Web of Science databases. The “AND” operator was employed to combine the keywords under investigation: “barrier,” AND “circular,” AND “fashion.” For Scopus, the research encompassed the article title, abstract, and keywords, while Web of Science used the “Topic” search, covering the title, abstract, and keywords. Following the PRISMA protocol (Figure 1), eligibility criteria were established early in the process. Table 1 delineates the inclusion and exclusion criteria formulated for this study. Journals are depicted in Figure 2. The Sustainability journal holds the top ranking, followed by the Journal of Cleaner Production. It is noteworthy that papers included in the study were published since 2019, affirming the emergence of the topic. In fact, when conducting research on Scopus by using the keywords: “circular” AND “economy” AND “fashion” AND “green”, we found that the first paper was in 2017, with a maximum number of publications in 2022 (Figure 3). That is why we focused on papers between 2019 and 2023 (Figure 4). Scopus is chosen because it is one of the largest and most reputable abstract and citation databases for peer-reviewed literature, covering a wide range of disciplines. It ensures high-quality and up-to-date sources, making it ideal for comprehensive and credible literature reviews. Additionally, Scopus provides advanced search tools and citation analysis features that support rigorous academic research.
The flowchart is divided into three vertical stages labeled “Identification”, “Screening and eligibility”, and “Included”. The flowchart begins with the “Identification” stage, which contains two rounded rectangles reading “Records identified through Scopus (n equals 54 records)” and “Records identified through Web of Science (n equals 63 records)”. Each rectangle has a downward arrow pointing to a central rounded rectangle in the “Screening and eligibility” stage. In the “Screening and eligibility” stage, the rectangle reads “Total records from all databases (n equals 117 records)”, which then points downward to another rounded rectangle reading “Records after considering E X C 1 and E X C 2 and removal of duplications (n equals 70 records)”. A final downward arrow points to a bottom rounded rectangle in the “Included” stage. In the “Included” stage, the rectangle reads “Studies included in review considering E X C 3, I N C 1, and I N C 2 (n equals 41 records)”.PRISMA protocol
The flowchart is divided into three vertical stages labeled “Identification”, “Screening and eligibility”, and “Included”. The flowchart begins with the “Identification” stage, which contains two rounded rectangles reading “Records identified through Scopus (n equals 54 records)” and “Records identified through Web of Science (n equals 63 records)”. Each rectangle has a downward arrow pointing to a central rounded rectangle in the “Screening and eligibility” stage. In the “Screening and eligibility” stage, the rectangle reads “Total records from all databases (n equals 117 records)”, which then points downward to another rounded rectangle reading “Records after considering E X C 1 and E X C 2 and removal of duplications (n equals 70 records)”. A final downward arrow points to a bottom rounded rectangle in the “Included” stage. In the “Included” stage, the rectangle reads “Studies included in review considering E X C 3, I N C 1, and I N C 2 (n equals 41 records)”.PRISMA protocol
Inclusion and exclusion criteria
| Criteria | Description | |
|---|---|---|
| Exclusion (EXC) | EXC1 | Book chapters |
| EXC2 | Conferences | |
| EXC3 | Irrelevant abstract (biochemical, medical, neuroscience, nutritional, luxury and slow fashion | |
| Inclusion (INC) | INC1 | English text only |
| INC2 | Full papers found only |
| Criteria | Description | |
|---|---|---|
| Exclusion (EXC) | EXC1 | Book chapters |
| EXC2 | Conferences | |
| EXC3 | Irrelevant abstract (biochemical, medical, neuroscience, nutritional, luxury and slow fashion | |
| Inclusion (INC) | INC1 | English text only |
| INC2 | Full papers found only |
The vertical axis ranges from 0 to 12 in increments of 2 units. The horizontal axis is labeled “Journals” and includes multiple journal categories arranged from left to right as follows: “Cleaner and Responsible Consumption”, “COMPUTERS IN INDUSTRY”, “Corporate Social Responsibility and Environmental Management”, “Environment Development and Sustainability”, “FASHION PRACTICE: THE JOURNAL OF DESIGN CREATIVE”, “Frontiers in Sustainability”, “I E E E ACCESS”, “INTERNATIONAL JOURNALS OF OPERATIONS AND PRODUCT”, “JOURNAL OF CLEANER PRODUCTION”, “Journal of Consumer Behaviour”, “JOURNAL OF FASHION MARKETING AND MANAGEMENT”, “Polish Journal of Management Studies”, “REGE-REVISTA DE GESTAO”, “RESOURCES CONSERVATION AND RECYCLING”, “S N APPLIED SCIENCES”, “SOCIAL RESPONSIBILITY JOURNAL”, “Sustainability”, “Sustainability: Science, Practice, and Policy”, “Sustainable Chemistry and Pharmacy”, “Sustainable Production and Consumption”, “Textile Research Journal”, and “WASTE MANAGEMENT AND RESEARCH”. Each journal category contains a single vertical bar representing the number of articles published in that journal. The data for the bars from left to right is as follows: Cleaner and Responsible Consumption: 1 article. COMPUTERS IN INDUSTRY: 1 article. Corporate Social Responsibility and Environmental Management: 1 article. Environment Development and Sustainability: 2 articles. FASHION PRACTICE: THE JOURNAL OF DESIGN CREATIVE: 1 article. Frontiers in Sustainability: 1 article. I E E E ACCESS: 1 article. INTERNATIONAL JOURNALS OF OPERATIONS AND PRODUCT: 1 article. JOURNAL OF CLEANER PRODUCTION: 5 articles. Journal of Consumer Behaviour: 1 article. JOURNAL OF FASHION MARKETING AND MANAGEMENT: 3 articles. Polish Journal of Management Studies: 1 article. REGE – Revista de Gestão: 1 article. RESOURCES CONSERVATION AND RECYCLING: 1 article. S N APPLIED SCIENCES: 1 article. SOCIAL RESPONSIBILITY JOURNAL: 1 article. Sustainability: 11 articles. Sustainability: Science, Practice, and Policy: 1 article. Sustainable Chemistry and Pharmacy: 1 article. Sustainable Production and Consumption: 2 articles. Textile Research Journal: 1 article. WASTE MANAGEMENT AND RESEARCH: 1 article. Note: All numerical data values are approximated.Publications by journal
The vertical axis ranges from 0 to 12 in increments of 2 units. The horizontal axis is labeled “Journals” and includes multiple journal categories arranged from left to right as follows: “Cleaner and Responsible Consumption”, “COMPUTERS IN INDUSTRY”, “Corporate Social Responsibility and Environmental Management”, “Environment Development and Sustainability”, “FASHION PRACTICE: THE JOURNAL OF DESIGN CREATIVE”, “Frontiers in Sustainability”, “I E E E ACCESS”, “INTERNATIONAL JOURNALS OF OPERATIONS AND PRODUCT”, “JOURNAL OF CLEANER PRODUCTION”, “Journal of Consumer Behaviour”, “JOURNAL OF FASHION MARKETING AND MANAGEMENT”, “Polish Journal of Management Studies”, “REGE-REVISTA DE GESTAO”, “RESOURCES CONSERVATION AND RECYCLING”, “S N APPLIED SCIENCES”, “SOCIAL RESPONSIBILITY JOURNAL”, “Sustainability”, “Sustainability: Science, Practice, and Policy”, “Sustainable Chemistry and Pharmacy”, “Sustainable Production and Consumption”, “Textile Research Journal”, and “WASTE MANAGEMENT AND RESEARCH”. Each journal category contains a single vertical bar representing the number of articles published in that journal. The data for the bars from left to right is as follows: Cleaner and Responsible Consumption: 1 article. COMPUTERS IN INDUSTRY: 1 article. Corporate Social Responsibility and Environmental Management: 1 article. Environment Development and Sustainability: 2 articles. FASHION PRACTICE: THE JOURNAL OF DESIGN CREATIVE: 1 article. Frontiers in Sustainability: 1 article. I E E E ACCESS: 1 article. INTERNATIONAL JOURNALS OF OPERATIONS AND PRODUCT: 1 article. JOURNAL OF CLEANER PRODUCTION: 5 articles. Journal of Consumer Behaviour: 1 article. JOURNAL OF FASHION MARKETING AND MANAGEMENT: 3 articles. Polish Journal of Management Studies: 1 article. REGE – Revista de Gestão: 1 article. RESOURCES CONSERVATION AND RECYCLING: 1 article. S N APPLIED SCIENCES: 1 article. SOCIAL RESPONSIBILITY JOURNAL: 1 article. Sustainability: 11 articles. Sustainability: Science, Practice, and Policy: 1 article. Sustainable Chemistry and Pharmacy: 1 article. Sustainable Production and Consumption: 2 articles. Textile Research Journal: 1 article. WASTE MANAGEMENT AND RESEARCH: 1 article. Note: All numerical data values are approximated.Publications by journal
The horizontal axis is labeled “Years” and ranges from 2017 to 2024 in increments of 1 year. The vertical axis is labeled “Number of publications” and ranges from 0 to 18 in increments of 2 units. The graph shows a single line with circular markers. The line begins in 2017 at a value of 2 publications, decreases in 2018 to 0, rises in 2019 to 3, falls slightly in 2020 to 2, rises again in 2021 to 4, increases sharply in 2022 to reach the highest value of 16 publications, then declines in 2023 to 10, and finally decreases slightly in 2024 to 9. Note: All numerical data values are approximated.Publications in Scopus
The horizontal axis is labeled “Years” and ranges from 2017 to 2024 in increments of 1 year. The vertical axis is labeled “Number of publications” and ranges from 0 to 18 in increments of 2 units. The graph shows a single line with circular markers. The line begins in 2017 at a value of 2 publications, decreases in 2018 to 0, rises in 2019 to 3, falls slightly in 2020 to 2, rises again in 2021 to 4, increases sharply in 2022 to reach the highest value of 16 publications, then declines in 2023 to 10, and finally decreases slightly in 2024 to 9. Note: All numerical data values are approximated.Publications in Scopus
A pie-chart shows the percentage distribution for the years 2019, 2020, 2021, 2022, and 2023. The data from the chart in the clockwise sense are as follows: 2019: 10 percent. 2020: 7 percent. 2021: 23 percent. 2022: 25 percent. 2023: 35 percent.Yearly publications included in the research
A pie-chart shows the percentage distribution for the years 2019, 2020, 2021, 2022, and 2023. The data from the chart in the clockwise sense are as follows: 2019: 10 percent. 2020: 7 percent. 2021: 23 percent. 2022: 25 percent. 2023: 35 percent.Yearly publications included in the research
One hundred seventeen published papers were initially identified. Duplications were deleted during the screening process, reducing the number of records to 70. No restrictions were imposed on the type of paper to be included (empirical, theoretical, or case study). Finally, taking the eligibility criteria into account, 41 records were included in the review.
2.2 Surveys and interviews
The collection of qualitative data was performed using surveys and interviews. The surveys and interviews were conducted over a period of several months to allow sufficient time for participant engagement. Participation was entirely voluntary, which contributed to a relatively low response rate. Despite extended availability, many potential respondents chose not to take part, reflecting common challenges in voluntary data. To frame the open questionnaire, the questions were designed using the PEST framework. The PEST framework has been used to analyse the barriers to circular economy adoption in the fashion textile industry because it helps systematically examine external macro-environmental factors, namely, political, economic, social, and technological, that influence industry practices. This approach allows for a comprehensive understanding of how regulations, market dynamics, consumer behaviour, and technological innovation impact the transition to circular models. By identifying these external pressures and limitations, PEST supports more informed strategic planning and policy development. Twenty-six experts took part, with 18 surveys distributed remotely and eight interviews conducted, five in person and three via calls. All interviews were performed on an individual basis, except for two experts who were interviewed simultaneously.
To achieve a coherent connection between the systematic literature review and the primary investigation, a triangulation method was employed. The systematic literature review served as the starting point of the research, which enabled the identification of a comprehensive list of 204 obstacles to adopting a circular economy in the fast fashion sector. This list laid the groundwork for developing the survey and interview tools focused on key thematic areas (governmental, financial, consumer, market, technical, and organisational). In the primary investigation, practitioners were encouraged not only to validate this list but also to share their own definitions and views of barriers to circularity based on their professional experiences. This method allowed the research to capture both explicit and implicit variations in how barriers are perceived in practice compared to academic perspectives. The qualitative data were subsequently analysed through an inductive approach and contrasted with the literature-derived list to pinpoint similarities, differences, and new emergent barriers. This iterative integration assured that the empirical findings enhanced and enriched the literature review, offering a more nuanced and validated comprehension of the barriers to a circular economy within the fast fashion context.
3. Results
This section presents the qualitative investigations of the barriers to circular fast fashion from the perspective of both study groups. Tables 2 and 3 outline the barriers to findings from the literature and the empirical investigation, respectively. After content analysis and a summative investigation, 204 barriers were identified from the literature, and the relevant references are presented in Table 2. 37 barriers were found from the empirical inspection. Thus, a total of 241 barriers will be discussed. In this research, content analysis involves a thorough review of practitioners’ qualitative feedback to determine how they perceive and articulate the obstacles to adopting a circular economy. This analysis was succeeded by a summative review, which included compiling and contrasting the prevalence and significance of the identified categories of barriers. These procedures facilitated the alignment of the practitioners’ viewpoints with the 204 barriers identified in the literature, ensuring an integration of both scholarly and practical perspectives in the findings.
Findings of barriers from the literature
| Code | Barrier description | References |
|---|---|---|
| B1 | Insufficient backing from governmental bodies | de Aguiar Hugo et al. (2021), Ki et al. (2020), Guo (2022), Abdelmeguid et al. (2022), Degenstein et al. (2023), Silva et al. (2023) |
| B2 | Deficiency in public policies, regulations, and legal frameworks | Pedersen et al. (2019), Gomes et al. (2021), Repp et al. (2021), Manshoven and Van Opstal (2022), Sharkey and Coggins (2022), Abdelmeguid et al. (2022), Papamichael et al. (2023), Silva et al. (2023) |
| B3 | Inadequate connection between policy creators and the fashion sector | Abdelmeguid et al. (2022) |
| B4 | Absence of consumer commitment to endorse circular approaches | Abdelmeguid et al. (2022) |
| B5 | Lack of national initiatives, incentives, objectives, and benchmarks | Gomes et al. (2021) |
| B6 | Present tax systems do not correspond with Circular Economy principles | Saccani et al. (2023) |
| B7 | Value Added Tax (VAT) supports conventional sales models rather than circular models | Peleg Mizrachi and Tal (2022) |
| B8 | Absence of global regulations for implementing circular methodologies | Manshoven and Van Opstal (2022), Abdelmeguid et al. (2022) |
| B9 | Outsourcing fashion production to regions with lower environmental concerns | Abdelmeguid et al. (2022) |
| B10 | Trade regulations impeding the exchange of second-hand apparel | Jain et al. (2021) |
| B11 | Substantial investments with minimal financial yield | Pedersen et al. (2019), Colasante and D’Adamo (2021), Guo (2022), Abdelmeguid et al. (2022), Degenstein et al. (2023), Saccani et al. (2023), Silva et al. (2023) |
| B12 | Circular goods may undermine existing products | Saccani et al. (2023) |
| B13 | Challenges in obtaining financial funding | Abdelmeguid et al. (2022) |
| B14 | Absence of means and support for financial scalability | Ki et al. (2020), Abdelmeguid et al. (2022), Marques and Manzanares (2023) |
| B15 | Trial runs are more feasible for bigger and international firms | Abdelmeguid et al. (2022) |
| B16 | Inexpensive pricing of unprocessed materials | Pedersen et al. (2019) |
| B17 | Rapid depreciation of product value encourages a take-make-waste approach | Peleg Mizrachi and Tal (2022) |
| B18 | Typical financial evaluation methods prefer linear economic models to circular ones | Peleg Mizrachi and Tal (2022) |
| B19 | Elevated costs in research and development | Abbate et al. (2023) |
| B20 | High expenses in transforming collected materials into new raw resources | Thinakaran et al. (2022) |
| B21 | Financial challenges in managing reverse logistics at a global scale | Manshoven and Van Opstal (2022), Abdelmeguid et al. (2022) |
| B22 | Hygiene concerns related to secondhand fashion and rentals | Hur (2020), Arrigo (2021), Charnley et al. (2022), de Aguiar Hugo et al. (2023), Fani et al. (2022) |
| B23 | Distrust issues associated with secondhand fashion | Charnley et al. (2022) |
| B24 | Opacity in pricing of secondhand fashion items | Charnley et al. (2022) |
| B25 | Concerns of real or perceived contamination in rented items | Clube and Tennant (2020) |
| B26 | Reluctance in engaging with previously used or touched products | Clube and Tennant (2020) |
| B27 | No liability on users for secondhand or shared consumption products | Arrigo (2021), Saccani et al. (2023) |
| B28 | Misalignment of renting and secondhand options with personal social image | Hur (2020), Arrigo (2021), Fani et al. (2022) |
| B29 | Restrictions in trying on items when renting | Fani et al. (2022) |
| B30 | Perceived wastefulness in renting for short-term ownership | Fani et al. (2022) |
| B31 | Hidden costs associated with damages in rented items | Fani et al. (2022) |
| B32 | Barriers in visibility/accessibility to swapping for consumers | Ray and Nayak (2023) |
| B33 | Challenges in quality and performance risk of used products in collaborative consumption | Hur (2020), Arrigo (2021), Colasante and D’Adamo (2021) |
| B34 | Consumer culture and low social awareness leading to discomfort in wearing used clothes | Pedersen et al. (2019), Hur (2020), Ki et al. (2020), de Aguiar Hugo et al. (2021) Charnley et al. (2022), Wu et al. (2022) |
| B35 | Perception of clothing styles as unfashionable | Hur (2020), de Aguiar Hugo et al. (2023) |
| B36 | Challenges in customer acquisition and retention for rental business models | Bodenheimer et al. (2022) |
| B37 | Perception of secondhand products as cheap and low quality | Hur (2020) |
| B38 | Difficulty in finding suitable style, size, and colour in secondhand items | Hur (2020) |
| B39 | Innovative organisational culture absence | Hur (2020) |
| B40 | Strategic vision deficiencies | Kovacs (2021) |
| B41 | Lack of leadership and support from top management | Camacho-Otero et al. (2019), de Aguiar Hugo et al. (2023), Saccani et al. (2023) |
| B42 | Other business priorities overshadowing circular initiatives | Saccani et al. (2023) |
| B43 | Organisational culture as a barrier to change | de Aguiar Hugo et al. (2021), Garcia-Ortega et al. (2023) |
| B44 | Risk aversion and uncertainties related to associated risks | de Aguiar Hugo et al. (2021), Abdelmeguid et al. (2022) |
| B45 | Fear of drastic organisational changes required for new models | Abdelmeguid et al. (2022) |
| B46 | Financial and operational risks for CE solution providers | Ray and Nayak (2023) |
| B47 | Uncertainty in returns of end-of-use products | Kovacs (2021) |
| B48 | Loss of ownership value risks in servitization | Abbate et al. (2023), Khan et al. (2023) |
| B49 | Privacy and data security concerns in collecting intelligent products | Camacho-Otero et al. (2019), Gomes et al. (2021) |
| B50 | Resistance to change in organisations | Camacho-Otero et al. (2019) |
| B51 | Circular premium risks affecting consumer behaviour | Camacho-Otero et al. (2019) |
| B52 | Sustainability and circularity dilemmas, risk of bias | Diddi and Yan (2019), McQueen et al. (2023) |
| B53 | Challenges in estimating data based on assumptions | Diddi and Yan (2019), McQueen et al. (2023) |
| B54 | Unpredictable market demand | Diddi and Yan (2019), McQueen et al. (2023) |
| B55 | Profitability uncertainties | McQueen et al. (2023) |
| B56 | Risks of product cannibalisation | McQueen et al. (2023) |
| B57 | Control loss and brand impact from third-party CE activities | McQueen et al. (2023) |
| B58 | Risks associated with circular economy rebound | McQueen et al. (2023) |
| B59 | Addressing attitude-behaviour gaps | Silva et al. (2023) |
| B60 | Changing consumer behaviours and attitudes towards circular products | Thinakaran et al. (2022) |
| B61 | Anticipating and managing consumer-related challenges | Saccani et al. (2023) |
| B62 | Conflict with external conditions and social norms | Abdelmeguid et al. (2022) |
| B63 | Efforts required for consumer education | Abdelmeguid et al. (2022) |
| B64 | Building consumer demand for ethical fashion | Abdelmeguid et al. (2022) |
| B65 | Communication with customers to motivate participation in circular initiatives | Abdelmeguid et al. (2022) |
| B66 | High expenses in transforming collected materials into new raw resources | Abdelmeguid et al. (2022) |
| B67 | Global scale reverse logistics financial challenges as a significant obstacle | Abdelmeguid et al. (2022) |
| B68 | Hygiene concerns related to secondhand fashion and rentals | Abdelmeguid et al. (2022) |
| B69 | Distrust issues associated with secondhand fashion | Piller (2023) |
| B70 | Opacity in pricing of secondhand fashion items | Piller (2023) |
| B71 | Concerns of real or perceived contamination in rented items | Piller (2023) |
| B72 | Reluctance in engaging with previously used or touched products | Piller (2023) |
| B73 | No liability on users for secondhand or shared consumption products | Piller (2023) |
| B74 | Misalignment of renting and secondhand options with personal social image | Bodenheimer et al. (2022) |
| B75 | Restrictions in trying on items when renting | Ostermann et al. (2021) |
| B76 | Perceived wastefulness in renting for short-term ownership | Pedersen et al. (2019) |
| B77 | Hidden costs associated with damages in rented items | Manshoven and Van Opstal (2022) |
| B78 | Barriers in visibility/accessibility to swapping for consumers | Degenstein et al. (2023) |
| B79 | Challenges in quality and performance risk of used products in collaborative consumption | Guo (2022) |
| B80 | Consumer culture and low social awareness leading to discomfort in wearing used clothes | Guo (2022) |
| B81 | Perception of clothing styles as unfashionable | Silva et al. (2023) |
| B82 | Challenges in customer acquisition and retention for rental business models | Khan et al. (2023) |
| B83 | The perception that used goods are low-cost but also low in quality | Thinakaran et al. (2022) |
| B84 | Challenges in locating secondhand items with the desired style, size, and colour | Wang et al. (2020) |
| B85 | Absence of a culture that fosters innovation within the organisation | Wang et al. (2020) |
| B86 | Strategic vision deficiencies | Wang et al. (2020) |
| B87 | Lack of leadership and support from top management | Wang et al. (2020) |
| B88 | Circular initiatives being deprioritized due to other business objectives | Galatti and Baruque-Ramos (2019) |
| B89 | The organisational culture hindering change | Saccani et al. (2023) |
| B90 | Caution and uncertainty regarding the risks involved | Saccani et al. (2023) |
| B91 | Fear of drastic organisational changes required for new models | Saccani et al. (2023) |
| B92 | Financial and operational risks for CE solution providers | Saccani et al. (2023) |
| B93 | Uncertainty in returns of end-of-use products | Saccani et al. (2023) |
| B94 | Potential loss of asset value associated with servitization | Saccani et al. (2023) |
| B95 | Privacy and data security concerns in collecting intelligent products | de Aguiar Hugo et al. (2021) |
| B96 | Resistance to change in organisations | Abdelmeguid et al. (2022) |
| B97 | Circular premium risks affecting consumer behaviour | Abdelmeguid et al. (2022) |
| B98 | Sustainability and circularity dilemmas, risk of bias | Abdelmeguid et al. (2022) |
| B99 | Challenges in estimating data based on assumptions | Abdelmeguid et al. (2022) |
| B100 | Unpredictable market demand | Ostermann et al. (2021) |
| B101 | Profitability uncertainties | Abbate et al. (2023) |
| B102 | Potential for new products to reduce sales of existing ones | Gomes et al. (2021) |
| B103 | Risks to brand image and operational control arising from external CE initiatives | Papamichael et al. (2023) |
| B104 | Threats resulting from rebound effects in circular economy initiatives | Mishra et al. (2021) |
| B105 | Addressing attitude-behaviour gaps | Saccani et al. (2023) |
| B106 | Changing consumer behaviours and attitudes towards circular products | Sharkey and Coggins (2022) |
| B107 | Anticipating and managing consumer-related challenges | Sharkey and Coggins (2022) |
| B108 | Conflict with external conditions and social norms | Pedersen et al. (2019), Degenstein et al. (2023), Silva et al. (2023) |
| B109 | Efforts required for consumer education | Wu et al. (2022) |
| B110 | Building consumer demand for ethical fashion | Thinakaran et al. (2022) |
| B111 | Communication with customers to motivate participation in circular initiatives | Thinakaran et al. (2022) |
| B112 | Risk of product cannibalisation in circular models | Ray and Nayak (2023) |
| B113 | Loss of control and brand impact from third-party circular activities | Ray and Nayak (2023) |
| B114 | Circular economy rebound effects on consumer behaviour | Degenstein et al. (2023) |
| B115 | Bridging the gap between attitudes and behaviours towards circularity | Kovacs (2021) |
| B116 | Shifting consumer behaviours and attitudes towards circular products | Abdelmeguid et al. (2022) |
| B117 | Managing challenges related to consumer behaviour in circular models | Garcia-Ortega et al. (2023) |
| B118 | Conflicts with external conditions and social norms in circular adoption | Abdelmeguid et al. (2022) |
| B119 | Efforts required for comprehensive consumer education in circularity | Abdelmeguid et al. (2022) |
| B120 | Building consumer demand for ethical and circular fashion | Abdelmeguid et al. (2022) |
| B121 | Effective communication to motivate customer participation in circular initiatives | Thinakaran et al. (2022), Silva et al. (2023) |
| B122 | Necessity for robust material tracking in the circular economy | Thinakaran et al. (2022) |
| B123 | Challenges with limited or unfit recycling materials for circular practices | Thinakaran et al. (2022) |
| B124 | Struggles in obtaining high-quality second-hand materials for circular use | Thinakaran et al. (2022) |
| B125 | Barriers in scaling upcycling due to inconsistent material quality | Jain et al. (2021) |
| B126 | Issues with the affordability of sustainable fabrics | Kovacs (2021) |
| B127 | Problems posed by low-quality materials in circular practices | Saccani et al. (2023) |
| B128 | Lack of necessary technologies, processes, and materials for circularity | Guo (2022) |
| B129 | Complications with mixed-material configurations in circular practices | Thinakaran et al. (2022) |
| B130 | Inadequate technical support for processing collected waste materials | Thinakaran et al. (2022) |
| B131 | Difficulties in segregating diverse waste material sources | de Aguiar Hugo et al. (2021), Thinakaran et al. (2022) |
| B132 | The state of clothing significantly impacting its potential for reuse/recycling | Degenstein et al. (2023) |
| B133 | Environmental impact challenges of natural fibre production | Auerbach George et al. (2022) |
| B134 | Obstacles in recycling cotton efficiently | Marques and Manzanares (2023) |
| B135 | Presence of persistent organic pollutants in recycled materials | Sharkey and Coggins (2022) |
| B136 | Challenges with chemical additives in circular economy materials | Sharkey and Coggins (2022) |
| B137 | Barriers in translating pro-environmental attitudes into circular actions | Silva et al. (2023)Guo (2022) |
| B138 | Deficiency of technological solutions for circular economy practices | Guo (2022) |
| B139 | Gaps in information sharing within green manufacturing | Ki et al. (2020), Gomes et al. (2021), Ostermann et al. (2021), Abbate et al. (2023), Silva et al. (2023) |
| B140 | Inefficient recovery processes and high technology costs | Thinakaran et al. (2022) |
| B141 | Lack of environmental knowledge impacting green manufacturing | Saccani et al. (2023) |
| B142 | Scarcity of information on environmental improvement potential | Guo (2022) |
| B143 | Absence of reliable performance indicators and measurement systems | Guo (2022) |
| B144 | Limited technical know-how in companies for circular economy practices | Thinakaran et al. (2022), Abbate et al. (2023), Saccani et al. (2023), Silva et al. (2023) |
| B145 | Rapid fashion changes challenging long-lasting product designs | Thinakaran et al. (2022) |
| B146 | Design complexity obstructing effective recovery process management | Saccani et al. (2023) |
| B147 | Misalignment of existing standards with circular economy objectives | Saccani et al. (2023) |
| B148 | Lack of focus on regeneration in product design | Abbate et al. (2023), Saccani et al. (2023) |
| B149 | Issues with tracing product origins and material compositions | de Aguiar Hugo et al. (2021), Saccani et al. (2023) |
| B150 | Shortage of skilled labour force in circular economy | Saccani et al. (2023) |
| B151 | Challenges in protecting circular economy know-how | Saccani et al. (2023) |
| B152 | Resource constraints in developing human capital for circular economy | Pedersen et al. (2019), Ki et al. (2020), Abbate et al. (2023), Abdelmeguid et al. (2022), Degenstein et al. (2023), Saccani et al. (2023), Thinakaran et al. (2022) |
| B153 | Difficulties in utilising rare, unique, and non-substitutable resources | Saccani et al. (2023) |
| B154 | Ineffective utilisation of resources and capabilities in circular economy | Abdelmeguid et al. (2022) |
| B155 | Opportunities and challenges in creating value from waste and secondary flows | Abdelmeguid et al. (2022) |
| B156 | Knowledge and awareness gaps among stakeholders regarding circular practices | Abdelmeguid et al. (2022) |
| B157 | Maturity issues in circular economy education focusing on sustainable fashion | Ostermann et al. (2021) |
| B158 | Challenges in executing circular economy practices at the organisational level | Ki et al. (2020), Colasante and D’Adamo (2021), Thinakaran et al. (2022) |
| B159 | Work conditions and marginalisation issues during production and post-use phases | Sehnem et al. (2023) |
| B160 | Significant losses in production and waste generation in the fashion industry | Jain et al. (2021) |
| B161 | Environmentally damaging effects caused by improper disposal of textiles | Gomes et al. (2021) |
| B162 | Lack of applied research in circularity, transparency, and traceability | Gomes et al. (2021) |
| B163 | Difficulties in making circular products feasible, scalable, and valuable | Gomes et al. (2021) |
| B164 | Managerial capability gaps in spreading circular practice knowledge | Gomes et al. (2021) |
| B165 | Dominance of self-interests over broader social, economic, and environmental goals | Gomes et al. (2021) |
| B166 | Circular economy benefit awareness deficit among stakeholders | Abdelmeguid et al. (2022) |
| B167 | Challenges in implementing effective operational management and integration | Abdelmeguid et al. (2022) |
| B168 | Difficulties in managing independent behaviours within organisations | Manshoven and Van Opstal (2022), Abdelmeguid et al. (2022) |
| B169 | Employee motivation and commitment challenges in transition to circularity | Abdelmeguid et al. (2022) |
| B170 | Inventory management barriers in rental business models | Abdelmeguid et al. (2022) |
| B171 | Brand size and scalability issues in circular economy adoption | Abdelmeguid et al. (2022) |
| B172 | Diverse value perspectives complicating circular economy practices | Bodenheimer et al. (2022) |
| B173 | Lack of specific training and progress monitoring at the company level | Degenstein et al. (2023) |
| B174 | Absence of innovative organisational culture supporting circular economy | Abbate et al. (2023) |
| B175 | Strategic vision deficiencies in adopting circular economy | Guo (2022), Thinakaran et al. (2022) |
| B176 | Lack of leadership and commitment from top management | Silva et al. (2023) |
| B177 | Other business priorities competing with circular initiatives | Silva et al. (2023) |
| B178 | Organisational culture as an obstacle to embracing change | Silva et al. (2023) |
| B179 | Uncertainties and risk aversion related to circular economy adoption | Ki et al. (2020) |
| B180 | Apprehension about major organisational restructuring required for new models | Degenstein et al. (2023) |
| B181 | Financial risks for circular economy solution providers | Manshoven and Van Opstal (2022), Abdelmeguid et al. (2022) |
| B182 | Operational risks in circular economy implementation | Silva et al. (2023) |
| B183 | Unclear outcomes regarding the recovery or value of end-of-life products | Thinakaran et al. (2022) |
| B184 | Apprehension about reduced ownership benefits resulting from servitization | Saccani et al. (2023) |
| B185 | Challenges in safeguarding data privacy in end-of-life product collection processes | Saccani et al. (2023) |
| B186 | Resistance to organisational change in adopting circular practices | Saccani et al. (2023) |
| B187 | Risks of circular premium affecting consumer behaviour | Saccani et al. (2023) |
| B188 | Sustainability dilemmas and risk of bias in circularity | Saccani et al. (2023) |
| B189 | Challenges in estimating data based on assumptions | Abdelmeguid et al. (2022), Saccani et al. (2023) |
| B190 | Unpredictability of market demand in circular economy | Abdelmeguid et al. (2022) |
| B191 | Uncertainty of profitability in circular economy models | Abdelmeguid et al. (2022) |
| B192 | Risk that circular practices may erode the market of current products | Abdelmeguid et al. (2022) |
| B193 | Potential loss of managerial oversight and brand integrity from external CE activities | Abdelmeguid et al. (2022) |
| B194 | Challenges associated with counterproductive outcomes in circular economy implementation | Abdelmeguid et al. (2022) |
| B195 | Bridging the attitude-behaviour gap in circular economy adoption | Pedersen et al. (2019) |
| B196 | Challenges in changing consumer behaviours and attitudes | Saccani et al. (2023) |
| B197 | Anticipating and managing consumer-related challenges in circular economy | Abdelmeguid et al. (2022) |
| B198 | Conflicts with external conditions and social norms | Abdelmeguid et al. (2022) |
| B199 | Need for extensive consumer education in circularity | Abdelmeguid et al. (2022) |
| B200 | Building consumer demand for ethical and circular fashion | Abdelmeguid et al. (2022) |
| B201 | Communicating effectively with customers to motivate circular participation | Abdelmeguid et al. (2022) |
| B202 | Enhanced effort required for comprehensive consumer education on circularity | Ray and Nayak (2023) |
| B203 | Fostering consumer interest in ethical and sustainable fashion practices | Mishra et al. (2021) |
| B204 | Effective strategies for engaging customers in circular economy participation | Abdelmeguid et al. (2022) |
| Code | Barrier description | References |
|---|---|---|
| B1 | Insufficient backing from governmental bodies | |
| B2 | Deficiency in public policies, regulations, and legal frameworks | |
| B3 | Inadequate connection between policy creators and the fashion sector | |
| B4 | Absence of consumer commitment to endorse circular approaches | |
| B5 | Lack of national initiatives, incentives, objectives, and benchmarks | |
| B6 | Present tax systems do not correspond with Circular Economy principles | |
| B7 | Value Added Tax (VAT) supports conventional sales models rather than circular models | |
| B8 | Absence of global regulations for implementing circular methodologies | |
| B9 | Outsourcing fashion production to regions with lower environmental concerns | |
| B10 | Trade regulations impeding the exchange of second-hand apparel | |
| B11 | Substantial investments with minimal financial yield | |
| B12 | Circular goods may undermine existing products | |
| B13 | Challenges in obtaining financial funding | |
| B14 | Absence of means and support for financial scalability | |
| B15 | Trial runs are more feasible for bigger and international firms | |
| B16 | Inexpensive pricing of unprocessed materials | |
| B17 | Rapid depreciation of product value encourages a take-make-waste approach | |
| B18 | Typical financial evaluation methods prefer linear economic models to circular ones | |
| B19 | Elevated costs in research and development | |
| B20 | High expenses in transforming collected materials into new raw resources | |
| B21 | Financial challenges in managing reverse logistics at a global scale | |
| B22 | Hygiene concerns related to secondhand fashion and rentals | |
| B23 | Distrust issues associated with secondhand fashion | |
| B24 | Opacity in pricing of secondhand fashion items | |
| B25 | Concerns of real or perceived contamination in rented items | |
| B26 | Reluctance in engaging with previously used or touched products | |
| B27 | No liability on users for secondhand or shared consumption products | |
| B28 | Misalignment of renting and secondhand options with personal social image | |
| B29 | Restrictions in trying on items when renting | |
| B30 | Perceived wastefulness in renting for short-term ownership | |
| B31 | Hidden costs associated with damages in rented items | |
| B32 | Barriers in visibility/accessibility to swapping for consumers | |
| B33 | Challenges in quality and performance risk of used products in collaborative consumption | |
| B34 | Consumer culture and low social awareness leading to discomfort in wearing used clothes | |
| B35 | Perception of clothing styles as unfashionable | |
| B36 | Challenges in customer acquisition and retention for rental business models | |
| B37 | Perception of secondhand products as cheap and low quality | |
| B38 | Difficulty in finding suitable style, size, and colour in secondhand items | |
| B39 | Innovative organisational culture absence | |
| B40 | Strategic vision deficiencies | |
| B41 | Lack of leadership and support from top management | |
| B42 | Other business priorities overshadowing circular initiatives | |
| B43 | Organisational culture as a barrier to change | |
| B44 | Risk aversion and uncertainties related to associated risks | |
| B45 | Fear of drastic organisational changes required for new models | |
| B46 | Financial and operational risks for CE solution providers | |
| B47 | Uncertainty in returns of end-of-use products | |
| B48 | Loss of ownership value risks in servitization | |
| B49 | Privacy and data security concerns in collecting intelligent products | |
| B50 | Resistance to change in organisations | |
| B51 | Circular premium risks affecting consumer behaviour | |
| B52 | Sustainability and circularity dilemmas, risk of bias | |
| B53 | Challenges in estimating data based on assumptions | |
| B54 | Unpredictable market demand | |
| B55 | Profitability uncertainties | |
| B56 | Risks of product cannibalisation | |
| B57 | Control loss and brand impact from third-party CE activities | |
| B58 | Risks associated with circular economy rebound | |
| B59 | Addressing attitude-behaviour gaps | |
| B60 | Changing consumer behaviours and attitudes towards circular products | |
| B61 | Anticipating and managing consumer-related challenges | |
| B62 | Conflict with external conditions and social norms | |
| B63 | Efforts required for consumer education | |
| B64 | Building consumer demand for ethical fashion | |
| B65 | Communication with customers to motivate participation in circular initiatives | |
| B66 | High expenses in transforming collected materials into new raw resources | |
| B67 | Global scale reverse logistics financial challenges as a significant obstacle | |
| B68 | Hygiene concerns related to secondhand fashion and rentals | |
| B69 | Distrust issues associated with secondhand fashion | |
| B70 | Opacity in pricing of secondhand fashion items | |
| B71 | Concerns of real or perceived contamination in rented items | |
| B72 | Reluctance in engaging with previously used or touched products | |
| B73 | No liability on users for secondhand or shared consumption products | |
| B74 | Misalignment of renting and secondhand options with personal social image | |
| B75 | Restrictions in trying on items when renting | |
| B76 | Perceived wastefulness in renting for short-term ownership | |
| B77 | Hidden costs associated with damages in rented items | |
| B78 | Barriers in visibility/accessibility to swapping for consumers | |
| B79 | Challenges in quality and performance risk of used products in collaborative consumption | |
| B80 | Consumer culture and low social awareness leading to discomfort in wearing used clothes | |
| B81 | Perception of clothing styles as unfashionable | |
| B82 | Challenges in customer acquisition and retention for rental business models | |
| B83 | The perception that used goods are low-cost but also low in quality | |
| B84 | Challenges in locating secondhand items with the desired style, size, and colour | |
| B85 | Absence of a culture that fosters innovation within the organisation | |
| B86 | Strategic vision deficiencies | |
| B87 | Lack of leadership and support from top management | |
| B88 | Circular initiatives being deprioritized due to other business objectives | |
| B89 | The organisational culture hindering change | |
| B90 | Caution and uncertainty regarding the risks involved | |
| B91 | Fear of drastic organisational changes required for new models | |
| B92 | Financial and operational risks for CE solution providers | |
| B93 | Uncertainty in returns of end-of-use products | |
| B94 | Potential loss of asset value associated with servitization | |
| B95 | Privacy and data security concerns in collecting intelligent products | |
| B96 | Resistance to change in organisations | |
| B97 | Circular premium risks affecting consumer behaviour | |
| B98 | Sustainability and circularity dilemmas, risk of bias | |
| B99 | Challenges in estimating data based on assumptions | |
| B100 | Unpredictable market demand | |
| B101 | Profitability uncertainties | |
| B102 | Potential for new products to reduce sales of existing ones | |
| B103 | Risks to brand image and operational control arising from external CE initiatives | |
| B104 | Threats resulting from rebound effects in circular economy initiatives | |
| B105 | Addressing attitude-behaviour gaps | |
| B106 | Changing consumer behaviours and attitudes towards circular products | |
| B107 | Anticipating and managing consumer-related challenges | |
| B108 | Conflict with external conditions and social norms | |
| B109 | Efforts required for consumer education | |
| B110 | Building consumer demand for ethical fashion | |
| B111 | Communication with customers to motivate participation in circular initiatives | |
| B112 | Risk of product cannibalisation in circular models | |
| B113 | Loss of control and brand impact from third-party circular activities | |
| B114 | Circular economy rebound effects on consumer behaviour | |
| B115 | Bridging the gap between attitudes and behaviours towards circularity | |
| B116 | Shifting consumer behaviours and attitudes towards circular products | |
| B117 | Managing challenges related to consumer behaviour in circular models | |
| B118 | Conflicts with external conditions and social norms in circular adoption | |
| B119 | Efforts required for comprehensive consumer education in circularity | |
| B120 | Building consumer demand for ethical and circular fashion | |
| B121 | Effective communication to motivate customer participation in circular initiatives | |
| B122 | Necessity for robust material tracking in the circular economy | |
| B123 | Challenges with limited or unfit recycling materials for circular practices | |
| B124 | Struggles in obtaining high-quality second-hand materials for circular use | |
| B125 | Barriers in scaling upcycling due to inconsistent material quality | |
| B126 | Issues with the affordability of sustainable fabrics | |
| B127 | Problems posed by low-quality materials in circular practices | |
| B128 | Lack of necessary technologies, processes, and materials for circularity | |
| B129 | Complications with mixed-material configurations in circular practices | |
| B130 | Inadequate technical support for processing collected waste materials | |
| B131 | Difficulties in segregating diverse waste material sources | |
| B132 | The state of clothing significantly impacting its potential for reuse/recycling | |
| B133 | Environmental impact challenges of natural fibre production | |
| B134 | Obstacles in recycling cotton efficiently | |
| B135 | Presence of persistent organic pollutants in recycled materials | |
| B136 | Challenges with chemical additives in circular economy materials | |
| B137 | Barriers in translating pro-environmental attitudes into circular actions | |
| B138 | Deficiency of technological solutions for circular economy practices | |
| B139 | Gaps in information sharing within green manufacturing | |
| B140 | Inefficient recovery processes and high technology costs | |
| B141 | Lack of environmental knowledge impacting green manufacturing | |
| B142 | Scarcity of information on environmental improvement potential | |
| B143 | Absence of reliable performance indicators and measurement systems | |
| B144 | Limited technical know-how in companies for circular economy practices | |
| B145 | Rapid fashion changes challenging long-lasting product designs | |
| B146 | Design complexity obstructing effective recovery process management | |
| B147 | Misalignment of existing standards with circular economy objectives | |
| B148 | Lack of focus on regeneration in product design | |
| B149 | Issues with tracing product origins and material compositions | |
| B150 | Shortage of skilled labour force in circular economy | |
| B151 | Challenges in protecting circular economy know-how | |
| B152 | Resource constraints in developing human capital for circular economy | |
| B153 | Difficulties in utilising rare, unique, and non-substitutable resources | |
| B154 | Ineffective utilisation of resources and capabilities in circular economy | |
| B155 | Opportunities and challenges in creating value from waste and secondary flows | |
| B156 | Knowledge and awareness gaps among stakeholders regarding circular practices | |
| B157 | Maturity issues in circular economy education focusing on sustainable fashion | |
| B158 | Challenges in executing circular economy practices at the organisational level | |
| B159 | Work conditions and marginalisation issues during production and post-use phases | |
| B160 | Significant losses in production and waste generation in the fashion industry | |
| B161 | Environmentally damaging effects caused by improper disposal of textiles | |
| B162 | Lack of applied research in circularity, transparency, and traceability | |
| B163 | Difficulties in making circular products feasible, scalable, and valuable | |
| B164 | Managerial capability gaps in spreading circular practice knowledge | |
| B165 | Dominance of self-interests over broader social, economic, and environmental goals | |
| B166 | Circular economy benefit awareness deficit among stakeholders | |
| B167 | Challenges in implementing effective operational management and integration | |
| B168 | Difficulties in managing independent behaviours within organisations | |
| B169 | Employee motivation and commitment challenges in transition to circularity | |
| B170 | Inventory management barriers in rental business models | |
| B171 | Brand size and scalability issues in circular economy adoption | |
| B172 | Diverse value perspectives complicating circular economy practices | |
| B173 | Lack of specific training and progress monitoring at the company level | |
| B174 | Absence of innovative organisational culture supporting circular economy | |
| B175 | Strategic vision deficiencies in adopting circular economy | |
| B176 | Lack of leadership and commitment from top management | |
| B177 | Other business priorities competing with circular initiatives | |
| B178 | Organisational culture as an obstacle to embracing change | |
| B179 | Uncertainties and risk aversion related to circular economy adoption | |
| B180 | Apprehension about major organisational restructuring required for new models | |
| B181 | Financial risks for circular economy solution providers | |
| B182 | Operational risks in circular economy implementation | |
| B183 | Unclear outcomes regarding the recovery or value of end-of-life products | |
| B184 | Apprehension about reduced ownership benefits resulting from servitization | |
| B185 | Challenges in safeguarding data privacy in end-of-life product collection processes | |
| B186 | Resistance to organisational change in adopting circular practices | |
| B187 | Risks of circular premium affecting consumer behaviour | |
| B188 | Sustainability dilemmas and risk of bias in circularity | |
| B189 | Challenges in estimating data based on assumptions | |
| B190 | Unpredictability of market demand in circular economy | |
| B191 | Uncertainty of profitability in circular economy models | |
| B192 | Risk that circular practices may erode the market of current products | |
| B193 | Potential loss of managerial oversight and brand integrity from external CE activities | |
| B194 | Challenges associated with counterproductive outcomes in circular economy implementation | |
| B195 | Bridging the attitude-behaviour gap in circular economy adoption | |
| B196 | Challenges in changing consumer behaviours and attitudes | |
| B197 | Anticipating and managing consumer-related challenges in circular economy | |
| B198 | Conflicts with external conditions and social norms | |
| B199 | Need for extensive consumer education in circularity | |
| B200 | Building consumer demand for ethical and circular fashion | |
| B201 | Communicating effectively with customers to motivate circular participation | |
| B202 | Enhanced effort required for comprehensive consumer education on circularity | |
| B203 | Fostering consumer interest in ethical and sustainable fashion practices | |
| B204 | Effective strategies for engaging customers in circular economy participation |
Empirical findings of barriers
| Code | Barrier description |
|---|---|
| b1 | Most fast fashion brands outsource production to countries with lower sustainability standards |
| b2 | Absence of regulations, allowing producers to ignore waste reduction |
| b3 | Insufficient government support for sustainable manufacturing practices |
| b4 | No tax incentives for investing in eco-friendly machinery |
| b5 | Limited financial resources for developing recycling infrastructure |
| b6 | Decarbonisation depends on political decision-making |
| b7 | High initial costs for setting up recycling processes |
| b8 | Recycled materials are more costly compared to synthetic alternatives |
| b9 | Reverse logistics for reuse and recycling are financially demanding |
| b10 | High treatment costs for textile waste management |
| b11 | Unclear financial benefits from sustainable investments |
| b12 | Sustainable products often come with higher price tags |
| b13 | Producing fibres sustainably incurs significant energy expenses |
| b14 | Consumer preference for buying new rather than repairing |
| b15 | Resistance toward purchasing or exchanging second-hand clothing |
| b16 | Low consumer awareness and engagement in eco-friendly practices |
| b17 | Fast fashion consumers frequently updating wardrobes to follow trends |
| b18 | Cheap pricing of fast fashion promotes a consumption-driven lifestyle |
| b19 | Lack of consumer participation in recycling initiatives |
| b20 | Discomfort with clothing made from recycled materials |
| b21 | Charity shops and second-hand culture are not widespread in some regions |
| b22 | Fast fashion business model emphasises low quality and short lifespan |
| b23 | Small textile factories used by brands lack investment in recycling |
| b24 | Consumer spending is vital for capitalist economies, hindering consumption reduction |
| b25 | No effective alternatives to synthetic materials |
| b26 | Frequent maintenance issues of textile machines increase waste |
| b27 | Complex material composition hinders recyclability |
| b28 | Recycled materials often suffer from quality issues |
| b29 | Challenges in chemically recycling textiles |
| b30 | Inadequate industrial infrastructure for textile waste processing |
| b31 | 3D printing technology is underutilised in the textile industry |
| b32 | Fibres from recycled materials tend to be shorter in length |
| b33 | Limited access to technology like AI for garment disaggregation |
| b34 | Insufficient R&D in textile factories for waste management |
| b35 | Lack of expertise in sorting and recycling textiles into yarns |
| b36 | Textile industry’s limited collaboration with others on circularity |
| b37 | Supply chains in the industry are not designed for the circular economy |
| Code | Barrier description |
|---|---|
| b1 | Most fast fashion brands outsource production to countries with lower sustainability standards |
| b2 | Absence of regulations, allowing producers to ignore waste reduction |
| b3 | Insufficient government support for sustainable manufacturing practices |
| b4 | No tax incentives for investing in eco-friendly machinery |
| b5 | Limited financial resources for developing recycling infrastructure |
| b6 | Decarbonisation depends on political decision-making |
| b7 | High initial costs for setting up recycling processes |
| b8 | Recycled materials are more costly compared to synthetic alternatives |
| b9 | Reverse logistics for reuse and recycling are financially demanding |
| b10 | High treatment costs for textile waste management |
| b11 | Unclear financial benefits from sustainable investments |
| b12 | Sustainable products often come with higher price tags |
| b13 | Producing fibres sustainably incurs significant energy expenses |
| b14 | Consumer preference for buying new rather than repairing |
| b15 | Resistance toward purchasing or exchanging second-hand clothing |
| b16 | Low consumer awareness and engagement in eco-friendly practices |
| b17 | Fast fashion consumers frequently updating wardrobes to follow trends |
| b18 | Cheap pricing of fast fashion promotes a consumption-driven lifestyle |
| b19 | Lack of consumer participation in recycling initiatives |
| b20 | Discomfort with clothing made from recycled materials |
| b21 | Charity shops and second-hand culture are not widespread in some regions |
| b22 | Fast fashion business model emphasises low quality and short lifespan |
| b23 | Small textile factories used by brands lack investment in recycling |
| b24 | Consumer spending is vital for capitalist economies, hindering consumption reduction |
| b25 | No effective alternatives to synthetic materials |
| b26 | Frequent maintenance issues of textile machines increase waste |
| b27 | Complex material composition hinders recyclability |
| b28 | Recycled materials often suffer from quality issues |
| b29 | Challenges in chemically recycling textiles |
| b30 | Inadequate industrial infrastructure for textile waste processing |
| b31 | 3D printing technology is underutilised in the textile industry |
| b32 | Fibres from recycled materials tend to be shorter in length |
| b33 | Limited access to technology like AI for garment disaggregation |
| b34 | Insufficient R&D in textile factories for waste management |
| b35 | Lack of expertise in sorting and recycling textiles into yarns |
| b36 | Textile industry’s limited collaboration with others on circularity |
| b37 | Supply chains in the industry are not designed for the circular economy |
One expert mentioned that “The eco responsibility from consumers is absent, as they are not aware if the material is recycled or not, and will look for the cheapest one, regardless of the reuse” This comment highlights a common barrier to advancing sustainable consumption: the gap between environmental values and actual consumer behaviour. It suggests that without greater awareness or incentives, many consumers prioritise cost over circular practices like reuse or recycling, which can hinder the effectiveness of circular economy initiatives.
The categorisation of barriers into governmental, financial, and consumer perspectives emerged directly from the analysis of the collected data. Through thematic analysis of interviews and survey responses, recurring patterns and concerns were identified and grouped based on their nature and origin. These themes were not predetermined but developed inductively, allowing the data to guide the structure of the findings. This grounded approach ensures that the categories reflect the actual experiences and viewpoints of participants.
4. Discussion
This section discusses the similarities and differences between both study groups (Table 4).
Classification of barriers
| Category | Literature findings | Empirical findings | |
|---|---|---|---|
| Governmental | Support and regulation | B1-B5 | B1-B6 |
| Taxation legislation | B6-B7 | ||
| International policies | B8-B10 | ||
| Financial | Circularity investments | B11-B19 | B7-B13 |
| Reverse logistics costs | B20-B21 | ||
| Consumer behaviour | Second hand, renting and swapping | B22-B40 | B14-B20 |
| Purchasing behaviour | B41-B51 | ||
| Repairing | B52-B58 | ||
| Market and external business environment | Business model | B59-B78 | B21-B24 |
| Fashion supply chain | B79-B107 | ||
| Infrastructure | B108-B109 | ||
| Certification | B110-B115 | ||
| Stakeholder pressure | B116-B120 | ||
| Technical | Material | B121-B136 | b25-b33 |
| Technology | B137-B141 | ||
| Organisational | Organisational knowledge and human capability | B142-B166 | B34-B37 |
| Organisational structure | B167-B174 | ||
| Organisational involvement | B175-B181 | ||
| Organisational risk | B182-B197 | ||
| Organisational management of consumer behaviour | B198-B204 | ||
| Category | Literature findings | Empirical findings | |
|---|---|---|---|
| Governmental | Support and regulation | B1-B5 | B1-B6 |
| Taxation legislation | B6-B7 | ||
| International policies | B8-B10 | ||
| Financial | Circularity investments | B11-B19 | B7-B13 |
| Reverse logistics costs | B20-B21 | ||
| Consumer behaviour | Second hand, renting and swapping | B22-B40 | B14-B20 |
| Purchasing behaviour | B41-B51 | ||
| Repairing | B52-B58 | ||
| Market and external business environment | Business model | B59-B78 | B21-B24 |
| Fashion supply chain | B79-B107 | ||
| Infrastructure | B108-B109 | ||
| Certification | B110-B115 | ||
| Stakeholder pressure | B116-B120 | ||
| Technical | Material | B121-B136 | b25-b33 |
| Technology | B137-B141 | ||
| Organisational | Organisational knowledge and human capability | B142-B166 | B34-B37 |
| Organisational structure | B167-B174 | ||
| Organisational involvement | B175-B181 | ||
| Organisational risk | B182-B197 | ||
| Organisational management of consumer behaviour | B198-B204 | ||
At the governmental level, practitioners stated that there is a lack of jurisdiction (b2). Silva et al. (2023) also noted the absence of government support and public policies. Manshoven and Van Opstal (2022) stated that there is a lack of enforceable regulations and laws to promote circularity throughout the supply chain, a trend that occurs more often in less developed countries (b1). Abdelmeguid et al. (2022) agreed that fashion outsourcing occurs in countries with fewer ecological priorities. Additionally, manufacturers face limitations (b3), including issues such as tax exemption (b4) and funding for recycling infrastructure (b5). This aligns with the observation that Value Added Tax does not favour used materials and products over newer ones (Peleg Mizrachi and Tal, 2022), as second-hand and recycled products are taxed in B2C transactions. Finally, experts have emphasised that decarbonisation is a political choice (b6). Rosenbloom et al. (2018) discussed how changes in political situations can facilitate a more fundamental reorganisation of ownership models, allowing decision-makers to adopt new priorities for market rules instead of government-directed investments.
From a financial perspective, the investment costs associated with production recycling (b7) and recycled material (b8) are notably high. Consistent with findings in the literature, Pedersen et al. (2019) confirm that price remains a crucial determinant of sustainability. Consequently, Saccani et al. (2023) argue that the cost of circular products may exceed that of conventional ones (b12), given the comparatively lower cost of virgin materials (Pedersen et al., 2019). Experts also highlight financial barriers related to the high costs of textile waste treatment (b10) and the energy expenses for fibre production (b13). In this context, Sharkey and Coggins (2022) confirm that the presence of specific chemical additives can hinder textile recycling operations by rendering end-of-life materials hazardous. Mainly, the authors point out that, in 2018, the European Union generated an estimated minimum of 1.7 million tonnes of hazardous and unrecyclable textile waste. Lastly, challenges associated with reverse logistics costs (b9) and uncertainty regarding the return on investment in circularity (b11) pose significant obstacles to developing a closed-loop supply chain network and a reverse logistics environment. These challenges necessitate new approaches to customer involvement, as customers transition into suppliers (Pedersen et al., 2019).
In terms of consumer behaviour, practitioners emphasise the limited engagement observed in activities such as swapping (b15), collecting old items (b19), and wearing garments crafted from used materials (b20). Aligning with existing literature, Arrigo (2021) categorises the primary forms of collaborative consumption in the fashion industry as swapping, resale, and rental. Swapping involves the permanent transfer of ownership of unwanted or underused fashion items, enhancing their utilisation and lifespan. Resale entails the selling of second-hand fashion products to other consumers, thereby diminishing the demand for newly manufactured items. Fashion rental involves providing another party with an item for a fixed period in exchange for a fee without a transfer of ownership. Furthermore, there exists a limited consumer awareness of sustainable initiatives (b16), with consumption largely driven by fashion lifestyle (b18), as consumers exhibit a consistent eagerness to adopt the latest fashionable trends (b17). This aligns with the findings of McNeill and Moore (2015), who observed that some consumers perceive sustainable fabrics as less fashionable. Lastly, practitioners argue that consumers tend to prefer buying new items over repairing old ones (b14). This inclination may be attributed to both possessing the necessary skills for repair and a negative perception associating visibly mended clothing with poverty and economic hardship, as indicated by Diddi and Yan (2019) and McQueen et al. (2023).
Examining the market and the broader business environment, practitioners argue that the adoption of the charity shop concept remains limited (b21), particularly within liberal economies (b24). This constraint may be attributed to both the immaturity of the market, as noted by Silva et al. (2023), and resistance from the traditional industry to deviating from established practices, as highlighted by Piller (2023). Additionally, the swift pace of fashion changes poses a challenge for products designed to last, as they struggle to keep up with continuous technological advancements (Saccani et al., 2023). Meanwhile, the prevalent business model of fast fashion, characterised by low-quality products, accelerates the shortening of the product life cycle (b22). Moreover, most international brands tend to outsource their production to smaller textile factories (b23), primarily due to challenges associated with sourcing raw materials for production within circular practices (Ostermann et al., 2021).
From a technical point of view, practitioners raise various concerns, including the absence of substitutes for synthetic materials (b25) and challenges related to recyclability (b27 and b29), as confirmed in the literature. Recycling processes often produce fibres that are too short for effective yarn spinning, contributing to the potentially low quality of recycled materials (b28). Moreover, fibres derived from recycled materials are frequently too short (b32). Thinakaran et al. (2022) elaborate on the difficulties arising from the mixed material composition of fashion items, hindering their use in circular economy (CE) practices and resulting in poor-quality second-hand materials collected for CE purposes. The quality and quantity of inputs also play a crucial role in production, influencing the final product’s quality, with issues such as the frequent maintenance problems of textile machines (b26) impacting the production process (Silva et al., 2023). Additionally, challenges in translating positive environmental attitudes into practical actions (Guo, 2022) contribute to the limited adoption of 3D printing (b31) and AI (b33) in the textile industry for circularity objectives. Lastly, there are concerns about the inefficiency of recovery processes from a technological perspective (Saccani et al., 2023), leading to a lack of industrial infrastructure for the treatment and reuse of textile waste (b30).
From an organisational point of view, there is a noticeable absence of research and development in textile factories concerning waste management (b34) and a deficiency in expertise (b35). This deficiency can be attributed to a lack of emphasis on circular economy practices in educational programs, favouring assumptions in support of sustainable fashion (Sehnem et al., 2023), and the limited execution capabilities of individual organisations (Jain et al., 2021). Practitioners also highlight the insufficient collaboration with other industries for benchmarking circular practices (b36) as a significant barrier, given that many supply chains are not originally designed for circularity (b37). According to the literature, this may stem from a lack of awareness regarding the benefits of the circular economy and the challenges of managing independent behaviours within an organisation (Abdelmeguid et al., 2022; Manshoven and Van Opstal, 2022). It has been argued that sustainability and circularity pose dilemmas and a perceived risk of bias, with businesses often fearing that transitioning to a new model would necessitate a drastic overhaul of organisational structure and functioning (Thinakaran et al., 2022).
4.1 Theoretical implications
The results of this research make a meaningful contribution to the theoretical comprehension of obstacles to adopting a circular economy in the fashion sector by incorporating perspectives from both scholarly literature and industry practitioners. By methodically juxtaposing the barriers noted in existing literature with empirical insights from industry professionals, this study validates, expands upon, and in some cases, questions current theoretical assumptions.
To begin with, the findings support previous research that highlights the essential role of governmental assistance, regulatory frameworks, and policy alignment in promoting circular transitions (Pedersen et al., 2019; Silva et al., 2023). Insights from practitioners, particularly regarding the absence of jurisdiction, tax incentives, and political decision-making, strengthen the literature’s claim that governmental support is crucial for facilitating circular practices, particularly in developing regions (Manshoven and Van Opstal, 2022; Abdelmeguid et al., 2022). This congruence reinforces the theoretical assertion that adopting a circular economy involves more than just technical or managerial hurdles; it is significantly influenced by the socio-political landscape.
Secondly, the study enhances knowledge concerning financial and operational barriers. While earlier research points to high investment costs and the uncertainty of returns as significant challenges (Saccani et al., 2023; Pedersen et al., 2019), perspectives from practitioners offer deeper insights into how these financial limitations directly impact decision-making across various levels, from recycling infrastructure to reverse logistics. This illustrates that financial factors are a key mechanism influencing organisational behaviour and strategy, thereby supporting theories of resource dependency and economic decision-making in sustainability transitions.
Thirdly, the findings provide advancements in theoretical understanding of consumer behaviour within circular models. Prior studies have indicated that low awareness, limited engagement, and preference for fashion hinder sustainable consumption (McNeill and Moore, 2015; Arrigo, 2021). The empirical results confirm and add nuance to this comprehension by uncovering specific consumer actions, such as hesitance to repair, swap, or wear second-hand garments, that interact with both organisational and market-level constraints. This highlights the necessity of merging consumer behaviour theories with frameworks of the circular economy to craft more comprehensive models of adoption.
Fourth, this research contributes to the theoretical debate on technical and organisational barriers. The existing literature has explored challenges relating to materials, technology, and institutional capabilities (Thinakaran et al., 2022; Guo, 2022; Saccani et al., 2023). Insights from practitioners reveal how practical limitations, like mixed-material textiles, short fibre lengths, and insufficient collaboration, offering empirical support for theories surrounding organisational learning and innovation within circular contexts. These insights highlight the relationship between technical viability and organisational capacity in advancing or impeding circular practices.
Lastly, by weaving insights from both literature and practitioners, this study addresses the ongoing gap between theoretical models of circular economy adoption and practical implementation. It demonstrates that many barriers proposed in theory are encountered in practice; however, the nuances vary based on organisational size, market position, and regional context. Consequently, the research offers a more contextually nuanced theoretical background for understanding circular adoption, paving the way for future studies to formulate models that are informed by empirical evidence and relevant to practical scenarios.
4.2 Practical implications
The present research and its findings can benefit companies and industries by identifying the specific barriers hindering the adoption of circular economy practices, allowing them to develop targeted strategies to overcome these challenges and enhance sustainability performance. For policymakers, the insights offer evidence-based guidance to design supportive regulations, incentives, and frameworks that facilitate circular transitions in the fashion and textile sector.
Unless stakeholder barriers are addressed, circular systems are unachievable. Because of the financial pressures of implementing the circularity concept, it is a debate of money versus planet. There are two takeaways for practitioners: first, with performance tracking. Circularity strategies should be in line with the C-indicators. C-indicators (Circularity Indicators) are metrics or tools used to measure and assess the circularity performance of products, companies, industries, or economies. They help determine how well an entity is applying circular economy (CE) principles, such as reducing waste, keeping materials in use, and regenerating natural systems. Factors such as Product-Level Circularity Metric (PLCM), Material Reutilisation Score (MRS) and Material Circularity Indicator (MCI) (Syu et al., 2022) could be relevant to efficient circularity performance.
The second takeaway is associated with the net-zero goals; it is time to rethink carbon. To truly push the fashion industry towards carbon circularity and ensure long-term sustainability and resilience, current approaches are insufficient. It is therefore crucial to analyse the relationship between society, energy, and chemistry. The textile industry’s shift to achieve net-zero emissions (NZE) by 2050 is a remarkable step towards tackling climate change. By taking this bold initiative, the industry is committing to reducing its carbon footprint and leading the way for other industries.
5. Conclusion
This study provides a comprehensive examination of the barriers to adopting circular economy practices in the fast fashion industry by integrating insights from both academic literature and industry practitioners. By revealing the overlapping and complementary nature of these barriers, the research bridges the gap between theoretical concepts and real-world challenges, offering a nuanced understanding of the complexities hindering circularity in fashion. Practically, the findings equip companies and policymakers with targeted strategies to address financial, technical, organisational, and consumer-related obstacles, thereby facilitating more effective circular transitions. Theoretically, the study advances circular economy scholarship by emphasising the need for context-specific, actionable frameworks that reflect industry realities, encouraging future research to focus on multidisciplinary and systemic approaches. Hence, this work contributes to accelerating sustainable transformation in fashion by aligning academic knowledge with practical solutions, paving the way for a resilient and low-carbon textile sector.
Several important limitations need consideration in this study. Firstly, the open questions employed did not cover the subject of recycling, an important point in waste reduction and sustainability. Future discussions should address this. Additionally, the distribution of practitioners across regions lacked balance, warranting efforts to ensure global parity in prioritising sustainability. Moreover, it is crucial to acknowledge potential variations in findings among the studies included because of their unique features and the challenges of generalising them to other contexts.
Future research should adopt a holistic approach to circular ecosystems, emphasising a comprehensive perspective to effectively promote sustainability. This would involve a thorough examination of the assumptions guiding consumer awareness, policy and regulation, and investor behaviour. A specific area requiring attention is the issue of certifications for circularity. Analysing similarities and differences between industries and avoiding unnecessary overlap in certification programs is essential. Establishing a more streamlined and effective system for promoting sustainability across diverse sectors can then be achieved. This study provides a comprehensive examination of the barriers to adopting circular economy practices in the fast fashion industry by integrating insights from both academic literature and industry practitioners. By revealing the overlapping and complementary nature of these barriers, the research bridges the gap between theoretical concepts and real-world challenges, offering a nuanced understanding of the complexities hindering circularity in fashion. Practically, the findings equip companies and policymakers with targeted strategies to address financial, technical, organisational, and consumer-related obstacles, thereby facilitating more effective circular transitions. Theoretically, the study advances circular economy scholarship by emphasising the need for context-specific, actionable frameworks that reflect industry realities, encouraging future research to focus on multidisciplinary and systemic approaches. Hence, this work contributes to accelerating sustainable transformation in fashion by aligning academic knowledge with practical solutions, paving the way for a resilient and low-carbon textile sector.

