3.2. Assessment of CE
Assessing the principles of the CE is essential in understanding their real-world impact. It provides us with a way to understand how well different industries are incorporating circular strategies into their practices, essentially showing us how they're adapting to a more sustainable approach. By evaluating the real-world application, knowledge is gained, various problems, barriers and possibilities for improvement for the transition to a circular economy are identified. In addition, assessment promotes transparency and continuous improvement, ultimately leading society towards a more harmonious and sustainable relationship with our planet's limited resources.
Circularity assessment tools evaluate the impact or benefits of a circular system, aiding in selecting preferred circular strategies or gauging the sustainability enhancement of existing systems. These tools are divided into two categories: assessment frameworks and assessment indicators. Frameworks offer multiple indicators tailored to specific cases, while indicator-based tools provide assessment through a single indicator like resource potential. Both types encompass burden-based measures (e.g., CO2 equivalent, mineral resources, fossil fuel energy) and value-based indicators (e.g., euros, years), which evaluate economic value added or extended utility within the analyzed system. The most known assessment frameworks for CE are developed upon three foundational methodologies: specifically, Life Cycle Assessment (LCA), Material Flow Analysis (MFA), and Input-Output analysis.
Life Cycle Assessment (LCA) stands as a predominant tool frequently utilized for quantifying and assessing the advantages or consequences of CE strategies, often serving as a means to deliberate and select from among various circular approaches [
22]. For many years, the main use of LCA was to assess the environmental impacts only. Presently, LCA emerges as the most well-defined framework for scrutinizing environmental aspects, capable of comprehensively evaluating circular systems, Product Service Systems, and recycling mechanisms [
23]. Stijn et al.[
24] introduced the Circular Economy Life Cycle Assessment (CE-LCA) model, which adapts existing LCA standards to account for multiple use cycles and employs a circular allocation approach in order to facilitate circular building component development . Antwi-Afari et al. [
25] have broaden the scope of LCA to encompass cradle-to-cradle considerations, and in combination with the prognostic circularity indicator for building systems. This comprehensive approach facilitated the assessment of environmental, technical, functional, and systemic aspects across the product system. Lei et al. [
26] examined the integration of life cycle assessment (LCA) into the circular economy framework, emphasizing its potential to mitigate additional environmental impacts associated with increased circularity. The paper systematically reviews LCA's applications in the context of the built environment within a circular economy approach, highlighting the need for its incorporation. Larsen et al. [
27] examined the integration of life cycle thinking, including LCA, Life Cycle Costing (LCC), and Social Life Cycle Assessment (S-LCA), into an integrated methodology called Life Cycle Sustainability Assessment (LCSA) to facilitate the transition of the construction industry toward a CE. Finally, Chen et al. [
28] provided a comprehensive summary and systematic evaluation of the utilization of LCA and Product Service System (PSS) integration within the circular economy framework, focusing on a micro-level perspective. Drawing from this analysis, the study highlights the research challenges and suggests possible avenues for future research aimed at advancing the implementation of LCA within the circular economy paradigm, particularly from a business perspective.
Material Flow Analysis (MFA) is a method that evaluates the dynamics and alterations within material flows of a system by quantifying mass balances within a specific spatial context. While MFA provides insights into the quantity of materials utilized, it lacks information regarding material quality and scarcity. The primary hurdles faced in MFA studies include data uncertainty and availability. However, due to its adaptable and uncomplicated nature, MFA can be employed across all levels of analysis, encompassing macro, meso, and micro scales [
22]. Barkhausen et al. [
29] a systematic literature review examines 44 prospective studies that utilize material flow analysis and life cycle assessment in combination, revealing a diverse landscape of integrated approaches with significant potential for assessing circular economy policy impacts, particularly within the context of the eco-design framework.
The last assessment framework for CE is the Input output analysis. Input-output analysis (IO analysis) was developed to explore economic interdependencies among sectors within regional, national, or international economies. It has been extended to assess environmental and socio-economic impacts associated with these sectors, often in conjunction with LCA to overcome limitations of process-based LCA [
22].
Furthermore, the second category of the circularity assessment is the assessment indicators. Corona et al. [
22] conducted a literature review that identifies a range of CE assessment indicators, categorized into distinct types. Among them, four standalone CE assessment indicators, four derived from LCA methodology, and one derived from the MFA framework were found. The first one is the longevity Indicator. It is a non-monetary measure of how long a material remains within a product system, incorporating initial lifetime and durability gained through reuse and recycling, without addressing the decrease in recycled material quality [
30]. Also, the Resource Potential Indicator (RPI) which evaluates the intrinsic value of a material for reuse, accounting for technological feasibility in recycling based on the average recoverable material share using available recycling technologies [
31]. The next one is the Value Based Resource Efficiency (VRE) Indicator that quantifies circularity as the percentage of value from stressed resources incorporated in a product returned after its end-of-life, considering both market value of resources and their societal and environmental implications [
32]. Furthermore, the Sustainable Circular Index (SCI) is a composite indicator that reflecting the sustainability and circularity degree of an organization, comprising economic, social, environmental, and circularity dimensions [
33]. The next four indicators derived from LCA methodologies, each offering distinct perspectives on environmental and economic integration. The Eco-Efficient Value Ratio (EVR) [
23] and the Eco-efficiency Index (EEI) employ monetization techniques to integrate environmental and economic considerations. They focus on increasing value added, benefiting both producers and consumers, with the assumption that such value reflects consumer willingness to pay for a service. The EEI combines value added and ReCiPe method-based environmental impacts, with monetization involving stakeholder preferences. In contrast, the EVR compares environmental burden to value added, using marginal prevention costs for monetization. The Global Resource Indicator (GRI) was introduced as a midpoint characterization indicator for resource use in LCA. It considers scarcity, geopolitical availability, and recyclability of resources. Scarcity incorporates extraction rates and available reserves, geopolitical availability addresses distribution homogeneity, and recyclability factors in recycling and dispersion rates [
34]. Finally, the Circular Performance Indicator (CPI) measures the ratio of environmental benefit achieved through waste treatment compared to the maximum potential benefit based on material quality. This indicator quantifies reduced resource consumption through Cumulative Exergy Extraction from the Natural Environment (CEENE), accounting for predefined material quality factors [
35]. Khadim et al. [
36] conducted an evaluation and examination of 35 currently available tools by conducting an expanded systematic analysis of 51 meticulously chosen sources encompassing both scholarly and non-academic literature.
Several researchers have recognized the complex nature of circularity and have used multi-criteria approaches (MCDM) and fuzzy logic to evaluate them. Ng and Martinez Hernandez [
37] developed a decision-making framework that combines multi-criteria analysis and process modelling to evaluate the performance of CE. Shen et al. [
38] utilized a fuzzy multi-criteria approach to assess green supply chain performance, while Olugu and Wong [
39] employed an expert fuzzy rule-based system for closed-loop supply chain performance measurement. Moreover, Sassanelli et al. [
40] except for the Multi-criteria approaches (MCDM) and fuzzy logic methods above for the assessment of CE, conducted a literature review and presented also other ways to make the assessment possible. For instance, the assessment of CE could be achieved with the design for X (DfX) methodologies such as Design for Disassembly (DfD), Design for End-of-Life (DfEoL) etc. and guidelines or with the Analytic Hierarchy Process (AHP) that is a decision-making tool that helps evaluate the performance of CE systems based on multiple criteria. AHP allows for the prioritization and comparison of different factors, such as energy consumption, resource recycling, environmental protection, costs, and social aspects. There are also approaches that combine assessment methods in order to assess CE. Markatos and Pantelakis [
41] introduced a decision support tool that combines life-cycle-based metrics that encompass ecological and economic aspects, along with a circular economy indicator (CEI) centered on material/component attributes. This CEI is associated with quality characteristics and accommodates the quality decline of materials through multiple recycling loops. The tool works with a multi-criteria decision analysis (MCDA) approach to mitigate subjectivity while prioritizing the importance of the criteria being considered.
Figure 3 shows the possible tools for the circular assessment.
Last but not least, currently there are existing tools for the assessment of the circularity in different areas. Valls-Val et al. [
42] conducted a review in order to evaluate distinct tools specifically designed to assess organizational circularity. The investigation extends to the essential information required by these tools, covering inquiries, categorizations, input data, achievable outcomes, and communication methods. The review underscores the escalating presence of circular assessment tools while underlining the lack of standardization in terms of features and content. Although these tools offer an initial reference, it's crucial to recognize that their application in decision-making could yield contrasting outcomes within the same context, depending on the tool chosen. Ιn reference, some of the available tools are the Acodea [
43], CEEI [
44], CIRCelligence [
45], CircularTRANS [
46], Circulytics [
47], CTI Tool [
48], Inedit [
49], MATChE Readiness Assessment [
50], MCI (Material Circularity Indicator) [
51], TECNUN [
52].