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Purpose

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.

Design/methodology/approach

Using both a systematic literature review and primary investigation, 241 barriers were identified, and the relevant similarities and dissimilarities between them were noted.

Findings

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.

Research limitations/implications

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.

Practical implications

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.

Originality/value

We present a comparative analysis of practitioners’ and academics’ perceptions of circular economy barriers, grounded in the research–practice gap.

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:

RQ1.

What are the barriers to circular textiles and fashion?

RQ2.

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.

The remainder of this paper is structured as follows: Section 2 presents outlines the research results; Section 3 discusses the findings; and Section 4 concludes with theoretical and practical implications.

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.

Figure 1
A flowchart shows records reduced from 117 to 41 after screening and exclusions.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

Figure 1
A flowchart shows records reduced from 117 to 41 after screening and exclusions.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

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Table 1

Inclusion and exclusion criteria

CriteriaDescription
Exclusion (EXC)EXC1Book chapters
EXC2Conferences
EXC3Irrelevant abstract (biochemical, medical, neuroscience, nutritional, luxury and slow fashion
Inclusion (INC)INC1English text only
INC2Full papers found only
Figure 2
A vertical bar graph shows title journals with values on the vertical axis and titles on the horizontal axis.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

Figure 2
A vertical bar graph shows title journals with values on the vertical axis and titles on the horizontal axis.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

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Figure 3
A line graph with years on the horizontal axis and number of publications on the vertical axis.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

Figure 3
A line graph with years on the horizontal axis and number of publications on the vertical axis.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

Close modal
Figure 4
A pie chart shows different years and the corresponding percentages for each year.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

Figure 4
A pie chart shows different years and the corresponding percentages for each year.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

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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.

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.

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.

Table 2

Findings of barriers from the literature

CodeBarrier descriptionReferences
B1Insufficient backing from governmental bodiesde Aguiar Hugo et al. (2021), Ki et al. (2020), Guo (2022), Abdelmeguid et al. (2022), Degenstein et al. (2023), Silva et al. (2023) 
B2Deficiency in public policies, regulations, and legal frameworksPedersen 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) 
B3Inadequate connection between policy creators and the fashion sectorAbdelmeguid et al. (2022) 
B4Absence of consumer commitment to endorse circular approachesAbdelmeguid et al. (2022) 
B5Lack of national initiatives, incentives, objectives, and benchmarksGomes et al. (2021) 
B6Present tax systems do not correspond with Circular Economy principlesSaccani et al. (2023) 
B7Value Added Tax (VAT) supports conventional sales models rather than circular modelsPeleg Mizrachi and Tal (2022) 
B8Absence of global regulations for implementing circular methodologiesManshoven and Van Opstal (2022), Abdelmeguid et al. (2022) 
B9Outsourcing fashion production to regions with lower environmental concernsAbdelmeguid et al. (2022) 
B10Trade regulations impeding the exchange of second-hand apparelJain et al. (2021) 
B11Substantial investments with minimal financial yieldPedersen 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) 
B12Circular goods may undermine existing productsSaccani et al. (2023) 
B13Challenges in obtaining financial fundingAbdelmeguid et al. (2022) 
B14Absence of means and support for financial scalabilityKi et al. (2020), Abdelmeguid et al. (2022), Marques and Manzanares (2023) 
B15Trial runs are more feasible for bigger and international firmsAbdelmeguid et al. (2022) 
B16Inexpensive pricing of unprocessed materialsPedersen et al. (2019) 
B17Rapid depreciation of product value encourages a take-make-waste approachPeleg Mizrachi and Tal (2022) 
B18Typical financial evaluation methods prefer linear economic models to circular onesPeleg Mizrachi and Tal (2022) 
B19Elevated costs in research and developmentAbbate et al. (2023) 
B20High expenses in transforming collected materials into new raw resourcesThinakaran et al. (2022) 
B21Financial challenges in managing reverse logistics at a global scaleManshoven and Van Opstal (2022), Abdelmeguid et al. (2022) 
B22Hygiene concerns related to secondhand fashion and rentalsHur (2020), Arrigo (2021), Charnley et al. (2022), de Aguiar Hugo et al. (2023), Fani et al. (2022) 
B23Distrust issues associated with secondhand fashionCharnley et al. (2022) 
B24Opacity in pricing of secondhand fashion itemsCharnley et al. (2022) 
B25Concerns of real or perceived contamination in rented itemsClube and Tennant (2020) 
B26Reluctance in engaging with previously used or touched productsClube and Tennant (2020) 
B27No liability on users for secondhand or shared consumption productsArrigo (2021), Saccani et al. (2023) 
B28Misalignment of renting and secondhand options with personal social imageHur (2020), Arrigo (2021), Fani et al. (2022) 
B29Restrictions in trying on items when rentingFani et al. (2022) 
B30Perceived wastefulness in renting for short-term ownershipFani et al. (2022) 
B31Hidden costs associated with damages in rented itemsFani et al. (2022) 
B32Barriers in visibility/accessibility to swapping for consumersRay and Nayak (2023) 
B33Challenges in quality and performance risk of used products in collaborative consumptionHur (2020), Arrigo (2021), Colasante and D’Adamo (2021) 
B34Consumer culture and low social awareness leading to discomfort in wearing used clothesPedersen et al. (2019), Hur (2020), Ki et al. (2020), de Aguiar Hugo et al. (2021) Charnley et al. (2022), Wu et al. (2022) 
B35Perception of clothing styles as unfashionableHur (2020), de Aguiar Hugo et al. (2023) 
B36Challenges in customer acquisition and retention for rental business modelsBodenheimer et al. (2022) 
B37Perception of secondhand products as cheap and low qualityHur (2020) 
B38Difficulty in finding suitable style, size, and colour in secondhand itemsHur (2020) 
B39Innovative organisational culture absenceHur (2020) 
B40Strategic vision deficienciesKovacs (2021) 
B41Lack of leadership and support from top managementCamacho-Otero et al. (2019), de Aguiar Hugo et al. (2023), Saccani et al. (2023) 
B42Other business priorities overshadowing circular initiativesSaccani et al. (2023) 
B43Organisational culture as a barrier to changede Aguiar Hugo et al. (2021), Garcia-Ortega et al. (2023) 
B44Risk aversion and uncertainties related to associated risksde Aguiar Hugo et al. (2021), Abdelmeguid et al. (2022) 
B45Fear of drastic organisational changes required for new modelsAbdelmeguid et al. (2022) 
B46Financial and operational risks for CE solution providersRay and Nayak (2023) 
B47Uncertainty in returns of end-of-use productsKovacs (2021) 
B48Loss of ownership value risks in servitizationAbbate et al. (2023), Khan et al. (2023) 
B49Privacy and data security concerns in collecting intelligent productsCamacho-Otero et al. (2019), Gomes et al. (2021) 
B50Resistance to change in organisationsCamacho-Otero et al. (2019) 
B51Circular premium risks affecting consumer behaviourCamacho-Otero et al. (2019) 
B52Sustainability and circularity dilemmas, risk of biasDiddi and Yan (2019), McQueen et al. (2023) 
B53Challenges in estimating data based on assumptionsDiddi and Yan (2019), McQueen et al. (2023) 
B54Unpredictable market demandDiddi and Yan (2019), McQueen et al. (2023) 
B55Profitability uncertaintiesMcQueen et al. (2023) 
B56Risks of product cannibalisationMcQueen et al. (2023) 
B57Control loss and brand impact from third-party CE activitiesMcQueen et al. (2023) 
B58Risks associated with circular economy reboundMcQueen et al. (2023) 
B59Addressing attitude-behaviour gapsSilva et al. (2023) 
B60Changing consumer behaviours and attitudes towards circular productsThinakaran et al. (2022) 
B61Anticipating and managing consumer-related challengesSaccani et al. (2023) 
B62Conflict with external conditions and social normsAbdelmeguid et al. (2022) 
B63Efforts required for consumer educationAbdelmeguid et al. (2022) 
B64Building consumer demand for ethical fashionAbdelmeguid et al. (2022) 
B65Communication with customers to motivate participation in circular initiativesAbdelmeguid et al. (2022) 
B66High expenses in transforming collected materials into new raw resourcesAbdelmeguid et al. (2022) 
B67Global scale reverse logistics financial challenges as a significant obstacleAbdelmeguid et al. (2022) 
B68Hygiene concerns related to secondhand fashion and rentalsAbdelmeguid et al. (2022) 
B69Distrust issues associated with secondhand fashionPiller (2023) 
B70Opacity in pricing of secondhand fashion itemsPiller (2023) 
B71Concerns of real or perceived contamination in rented itemsPiller (2023) 
B72Reluctance in engaging with previously used or touched productsPiller (2023) 
B73No liability on users for secondhand or shared consumption productsPiller (2023) 
B74Misalignment of renting and secondhand options with personal social imageBodenheimer et al. (2022) 
B75Restrictions in trying on items when rentingOstermann et al. (2021) 
B76Perceived wastefulness in renting for short-term ownershipPedersen et al. (2019) 
B77Hidden costs associated with damages in rented itemsManshoven and Van Opstal (2022) 
B78Barriers in visibility/accessibility to swapping for consumersDegenstein et al. (2023) 
B79Challenges in quality and performance risk of used products in collaborative consumptionGuo (2022) 
B80Consumer culture and low social awareness leading to discomfort in wearing used clothesGuo (2022) 
B81Perception of clothing styles as unfashionableSilva et al. (2023) 
B82Challenges in customer acquisition and retention for rental business modelsKhan et al. (2023) 
B83The perception that used goods are low-cost but also low in qualityThinakaran et al. (2022) 
B84Challenges in locating secondhand items with the desired style, size, and colourWang et al. (2020) 
B85Absence of a culture that fosters innovation within the organisationWang et al. (2020) 
B86Strategic vision deficienciesWang et al. (2020) 
B87Lack of leadership and support from top managementWang et al. (2020) 
B88Circular initiatives being deprioritized due to other business objectivesGalatti and Baruque-Ramos (2019) 
B89The organisational culture hindering changeSaccani et al. (2023) 
B90Caution and uncertainty regarding the risks involvedSaccani et al. (2023) 
B91Fear of drastic organisational changes required for new modelsSaccani et al. (2023) 
B92Financial and operational risks for CE solution providersSaccani et al. (2023) 
B93Uncertainty in returns of end-of-use productsSaccani et al. (2023) 
B94Potential loss of asset value associated with servitizationSaccani et al. (2023) 
B95Privacy and data security concerns in collecting intelligent productsde Aguiar Hugo et al. (2021) 
B96Resistance to change in organisationsAbdelmeguid et al. (2022) 
B97Circular premium risks affecting consumer behaviourAbdelmeguid et al. (2022) 
B98Sustainability and circularity dilemmas, risk of biasAbdelmeguid et al. (2022) 
B99Challenges in estimating data based on assumptionsAbdelmeguid et al. (2022) 
B100Unpredictable market demandOstermann et al. (2021) 
B101Profitability uncertaintiesAbbate et al. (2023) 
B102Potential for new products to reduce sales of existing onesGomes et al. (2021) 
B103Risks to brand image and operational control arising from external CE initiativesPapamichael et al. (2023) 
B104Threats resulting from rebound effects in circular economy initiativesMishra et al. (2021) 
B105Addressing attitude-behaviour gapsSaccani et al. (2023) 
B106Changing consumer behaviours and attitudes towards circular productsSharkey and Coggins (2022) 
B107Anticipating and managing consumer-related challengesSharkey and Coggins (2022) 
B108Conflict with external conditions and social normsPedersen et al. (2019), Degenstein et al. (2023), Silva et al. (2023) 
B109Efforts required for consumer educationWu et al. (2022) 
B110Building consumer demand for ethical fashionThinakaran et al. (2022) 
B111Communication with customers to motivate participation in circular initiativesThinakaran et al. (2022) 
B112Risk of product cannibalisation in circular modelsRay and Nayak (2023) 
B113Loss of control and brand impact from third-party circular activitiesRay and Nayak (2023) 
B114Circular economy rebound effects on consumer behaviourDegenstein et al. (2023) 
B115Bridging the gap between attitudes and behaviours towards circularityKovacs (2021) 
B116Shifting consumer behaviours and attitudes towards circular productsAbdelmeguid et al. (2022) 
B117Managing challenges related to consumer behaviour in circular modelsGarcia-Ortega et al. (2023) 
B118Conflicts with external conditions and social norms in circular adoptionAbdelmeguid et al. (2022) 
B119Efforts required for comprehensive consumer education in circularityAbdelmeguid et al. (2022) 
B120Building consumer demand for ethical and circular fashionAbdelmeguid et al. (2022) 
B121Effective communication to motivate customer participation in circular initiativesThinakaran et al. (2022), Silva et al. (2023) 
B122Necessity for robust material tracking in the circular economyThinakaran et al. (2022) 
B123Challenges with limited or unfit recycling materials for circular practicesThinakaran et al. (2022) 
B124Struggles in obtaining high-quality second-hand materials for circular useThinakaran et al. (2022) 
B125Barriers in scaling upcycling due to inconsistent material qualityJain et al. (2021) 
B126Issues with the affordability of sustainable fabricsKovacs (2021) 
B127Problems posed by low-quality materials in circular practicesSaccani et al. (2023) 
B128Lack of necessary technologies, processes, and materials for circularityGuo (2022) 
B129Complications with mixed-material configurations in circular practicesThinakaran et al. (2022) 
B130Inadequate technical support for processing collected waste materialsThinakaran et al. (2022) 
B131Difficulties in segregating diverse waste material sourcesde Aguiar Hugo et al. (2021), Thinakaran et al. (2022) 
B132The state of clothing significantly impacting its potential for reuse/recyclingDegenstein et al. (2023) 
B133Environmental impact challenges of natural fibre production‏Auerbach George et al. (2022) 
B134Obstacles in recycling cotton efficientlyMarques and Manzanares (2023) 
B135Presence of persistent organic pollutants in recycled materialsSharkey and Coggins (2022) 
B136Challenges with chemical additives in circular economy materialsSharkey and Coggins (2022) 
B137Barriers in translating pro-environmental attitudes into circular actionsSilva et al. (2023)Guo (2022) 
B138Deficiency of technological solutions for circular economy practicesGuo (2022) 
B139Gaps in information sharing within green manufacturingKi et al. (2020), Gomes et al. (2021), Ostermann et al. (2021), Abbate et al. (2023), Silva et al. (2023) 
B140Inefficient recovery processes and high technology costsThinakaran et al. (2022) 
B141Lack of environmental knowledge impacting green manufacturingSaccani et al. (2023) 
B142Scarcity of information on environmental improvement potentialGuo (2022) 
B143Absence of reliable performance indicators and measurement systemsGuo (2022) 
B144Limited technical know-how in companies for circular economy practicesThinakaran et al. (2022), Abbate et al. (2023), Saccani et al. (2023), Silva et al. (2023) 
B145Rapid fashion changes challenging long-lasting product designsThinakaran et al. (2022) 
B146Design complexity obstructing effective recovery process managementSaccani et al. (2023) 
B147Misalignment of existing standards with circular economy objectivesSaccani et al. (2023) 
B148Lack of focus on regeneration in product designAbbate et al. (2023), Saccani et al. (2023) 
B149Issues with tracing product origins and material compositionsde Aguiar Hugo et al. (2021), Saccani et al. (2023) 
B150Shortage of skilled labour force in circular economySaccani et al. (2023) 
B151Challenges in protecting circular economy know-howSaccani et al. (2023) 
B152Resource constraints in developing human capital for circular economyPedersen 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) 
B153Difficulties in utilising rare, unique, and non-substitutable resourcesSaccani et al. (2023) 
B154Ineffective utilisation of resources and capabilities in circular economyAbdelmeguid et al. (2022) 
B155Opportunities and challenges in creating value from waste and secondary flowsAbdelmeguid et al. (2022) 
B156Knowledge and awareness gaps among stakeholders regarding circular practicesAbdelmeguid et al. (2022) 
B157Maturity issues in circular economy education focusing on sustainable fashionOstermann et al. (2021) 
B158Challenges in executing circular economy practices at the organisational levelKi et al. (2020), Colasante and D’Adamo (2021), Thinakaran et al. (2022) 
B159Work conditions and marginalisation issues during production and post-use phasesSehnem et al. (2023) 
B160Significant losses in production and waste generation in the fashion industryJain et al. (2021) 
B161Environmentally damaging effects caused by improper disposal of textilesGomes et al. (2021) 
B162Lack of applied research in circularity, transparency, and traceabilityGomes et al. (2021) 
B163Difficulties in making circular products feasible, scalable, and valuableGomes et al. (2021) 
B164Managerial capability gaps in spreading circular practice knowledgeGomes et al. (2021) 
B165Dominance of self-interests over broader social, economic, and environmental goalsGomes et al. (2021) 
B166Circular economy benefit awareness deficit among stakeholdersAbdelmeguid et al. (2022) 
B167Challenges in implementing effective operational management and integrationAbdelmeguid et al. (2022) 
B168Difficulties in managing independent behaviours within organisationsManshoven and Van Opstal (2022), Abdelmeguid et al. (2022) 
B169Employee motivation and commitment challenges in transition to circularityAbdelmeguid et al. (2022) 
B170Inventory management barriers in rental business modelsAbdelmeguid et al. (2022) 
B171Brand size and scalability issues in circular economy adoptionAbdelmeguid et al. (2022) 
B172Diverse value perspectives complicating circular economy practicesBodenheimer et al. (2022) 
B173Lack of specific training and progress monitoring at the company levelDegenstein et al. (2023) 
B174Absence of innovative organisational culture supporting circular economyAbbate et al. (2023) 
B175Strategic vision deficiencies in adopting circular economyGuo (2022), Thinakaran et al. (2022) 
B176Lack of leadership and commitment from top managementSilva et al. (2023) 
B177Other business priorities competing with circular initiativesSilva et al. (2023) 
B178Organisational culture as an obstacle to embracing changeSilva et al. (2023) 
B179Uncertainties and risk aversion related to circular economy adoptionKi et al. (2020) 
B180Apprehension about major organisational restructuring required for new modelsDegenstein et al. (2023) 
B181Financial risks for circular economy solution providersManshoven and Van Opstal (2022), Abdelmeguid et al. (2022) 
B182Operational risks in circular economy implementationSilva et al. (2023) 
B183Unclear outcomes regarding the recovery or value of end-of-life productsThinakaran et al. (2022) 
B184Apprehension about reduced ownership benefits resulting from servitizationSaccani et al. (2023) 
B185Challenges in safeguarding data privacy in end-of-life product collection processesSaccani et al. (2023) 
B186Resistance to organisational change in adopting circular practicesSaccani et al. (2023) 
B187Risks of circular premium affecting consumer behaviourSaccani et al. (2023) 
B188Sustainability dilemmas and risk of bias in circularitySaccani et al. (2023) 
B189Challenges in estimating data based on assumptionsAbdelmeguid et al. (2022), Saccani et al. (2023) 
B190Unpredictability of market demand in circular economyAbdelmeguid et al. (2022) 
B191Uncertainty of profitability in circular economy modelsAbdelmeguid et al. (2022) 
B192Risk that circular practices may erode the market of current productsAbdelmeguid et al. (2022) 
B193Potential loss of managerial oversight and brand integrity from external CE activitiesAbdelmeguid et al. (2022) 
B194Challenges associated with counterproductive outcomes in circular economy implementationAbdelmeguid et al. (2022) 
B195Bridging the attitude-behaviour gap in circular economy adoptionPedersen et al. (2019) 
B196Challenges in changing consumer behaviours and attitudesSaccani et al. (2023) 
B197Anticipating and managing consumer-related challenges in circular economyAbdelmeguid et al. (2022) 
B198Conflicts with external conditions and social normsAbdelmeguid et al. (2022) 
B199Need for extensive consumer education in circularityAbdelmeguid et al. (2022) 
B200Building consumer demand for ethical and circular fashionAbdelmeguid et al. (2022) 
B201Communicating effectively with customers to motivate circular participationAbdelmeguid et al. (2022) 
B202Enhanced effort required for comprehensive consumer education on circularityRay and Nayak (2023) 
B203Fostering consumer interest in ethical and sustainable fashion practicesMishra et al. (2021) 
B204Effective strategies for engaging customers in circular economy participationAbdelmeguid et al. (2022) 
Table 3

Empirical findings of barriers

CodeBarrier description
b1Most fast fashion brands outsource production to countries with lower sustainability standards
b2Absence of regulations, allowing producers to ignore waste reduction
b3Insufficient government support for sustainable manufacturing practices
b4No tax incentives for investing in eco-friendly machinery
b5Limited financial resources for developing recycling infrastructure
b6Decarbonisation depends on political decision-making
b7High initial costs for setting up recycling processes
b8Recycled materials are more costly compared to synthetic alternatives
b9Reverse logistics for reuse and recycling are financially demanding
b10High treatment costs for textile waste management
b11Unclear financial benefits from sustainable investments
b12Sustainable products often come with higher price tags
b13Producing fibres sustainably incurs significant energy expenses
b14Consumer preference for buying new rather than repairing
b15Resistance toward purchasing or exchanging second-hand clothing
b16Low consumer awareness and engagement in eco-friendly practices
b17Fast fashion consumers frequently updating wardrobes to follow trends
b18Cheap pricing of fast fashion promotes a consumption-driven lifestyle
b19Lack of consumer participation in recycling initiatives
b20Discomfort with clothing made from recycled materials
b21Charity shops and second-hand culture are not widespread in some regions
b22Fast fashion business model emphasises low quality and short lifespan
b23Small textile factories used by brands lack investment in recycling
b24Consumer spending is vital for capitalist economies, hindering consumption reduction
b25No effective alternatives to synthetic materials
b26Frequent maintenance issues of textile machines increase waste
b27Complex material composition hinders recyclability
b28Recycled materials often suffer from quality issues
b29Challenges in chemically recycling textiles
b30Inadequate industrial infrastructure for textile waste processing
b313D printing technology is underutilised in the textile industry
b32Fibres from recycled materials tend to be shorter in length
b33Limited access to technology like AI for garment disaggregation
b34Insufficient R&D in textile factories for waste management
b35Lack of expertise in sorting and recycling textiles into yarns
b36Textile industry’s limited collaboration with others on circularity
b37Supply 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.

This section discusses the similarities and differences between both study groups (Table 4).

Table 4

Classification of barriers

CategoryLiterature findingsEmpirical findings
GovernmentalSupport and regulationB1-B5B1-B6
Taxation legislationB6-B7
International policiesB8-B10
FinancialCircularity investmentsB11-B19B7-B13
Reverse logistics costsB20-B21
Consumer behaviourSecond hand, renting and swappingB22-B40B14-B20
Purchasing behaviourB41-B51
RepairingB52-B58
Market and external business environmentBusiness modelB59-B78B21-B24
Fashion supply chainB79-B107
InfrastructureB108-B109
CertificationB110-B115
Stakeholder pressureB116-B120
TechnicalMaterialB121-B136b25-b33
TechnologyB137-B141
OrganisationalOrganisational knowledge and human capabilityB142-B166B34-B37
Organisational structureB167-B174
Organisational involvementB175-B181
Organisational riskB182-B197
Organisational management of consumer behaviourB198-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).

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.

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.

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.

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