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Article

How Circular Economy Disclosure Responds to Institutional Determinants Empirical Evidences in Non-Financial European Firms

1
Department of Law, Parthenope University, 80133 Naples, Italy
2
Department of Business and Law, Pegaso University, 80143 Naples, Italy
*
Author to whom correspondence should be addressed.
Sustainability 2023, 15(22), 16069; https://doi.org/10.3390/su152216069
Submission received: 2 October 2023 / Revised: 6 November 2023 / Accepted: 14 November 2023 / Published: 17 November 2023

Abstract

:
Despite the increasing attention that the circular economy (CE) has received at the international level in recent years, the literature has paid limited attention to the importance of institutional factors that may influence firms’ disclosure of CE. Thus, there is a gap in the study of CE disclosure, especially when compared with other studies dedicated to environmental disclosure. This paper aims to fill this gap by investigating the institutional pressures, in terms of coercive, normative, and mimetic factors, that influence firms’ behavior with respect to CE disclosure. This research focuses on a sample of 366 nonfinancial firms, operating in 14 EU countries between 2015 and 2020. The results show that coercive and mimetic institutional pressures positively influence the level of CE disclosure issued by the firms. More specifically, the stringency of the environmental policy (coercive pressure) and the belonging to an environmentally sensitive sector (mimetic pressure) have a positive impact on the CE disclosure provided. With respect to normative pressure, the results are mixed. In fact, only the adoption of Global Reporting Initiatives’ (GRIs) standard requirements is positively and significantly related to CE disclosure. The presence of an external assurance, as well as the commitment to the SDGs, is not significantly related to the CE disclosure. The absence of an analytical standard that organically addresses the issue of CE, by guiding companies in their disclosure, may explain the irrelevance of these factors in the process of convergence of the information produced. This research contributes to this area by filling a gap in the CE literature, providing some insights into the determinants of disclosure and the role of institutional pressures in influencing the level of CE information. In addition, the research adds to previous studies on disclosure by measuring the CE information provided by companies with an indicator developed based on specific environmental items collected from the Refinitiv Eikon database, which could be used in future research. The findings of this paper have some important practical implications. In particular, the results confirm to policymakers that stricter regulations have a positive impact on disclosures related to the CE. Thus, a new specific European regulation should promote more homogeneous and analytical CE disclosure, increasing the sensitivity among firms and practitioners on this topic. A similar approach may be followed for the same purpose by other regional or local policymakers. The paper also emphasizes the necessity of introducing more stringent regulations on assurance and SDGs by the regulatory or professional bodies to achieve greater uniformity of behavior by firms.

1. Introduction

1.1. The Reason for a New Study on Circular Economy Disclosures

The circular economy (CE) has progressively gained more attention in recent years. The CE and circular business model concepts are only relatively recent [1]. In many cases, the CE has been addressed as a specific feature of the sustainability approach adopted by people and organizations [2].
Regulators and civil society have increased their sensibility toward environmental issues, focusing on the potential consequences for local and global communities arising from inappropriate behaviors. This orientation involves operations of the firms whose involvement in the management of public resources is crucial.
It has been observed how the introduction of CE models can support entities developing their businesses [3].
The CE can produce benefits in the entities’ operating activities, aligning products with customers’ expectations [4]. Public opinion concerning resource use has changed dramatically over the past few years, and customers have gradually shifted their sensibilities about behaviors in order to be responsible for communities and the planet. People have become more conscious of the dangerousness of some products and prefer greener and safer products. This orientation also involves growth in the economy related to new business models with a consequent ability to create jobs [5].
In relation to this, corporate disclosure can be a tool that encourages companies to spread their strategic vision and management of circular economy models. By doing this, companies legitimize their role in the context in which they operate, engaging with stakeholders and maintaining public support [6]. Corporate disclosures reduce information gaps on sensitive issues like the CE and provide information on emerging issues that could be relevant for stakeholders to make economic decisions.
According to the above, the analysis of the factors determining the level of CE disclosure in corporate reporting appears to be meaningful as a basis for future debates about the role and development of CE and disclosure.
That said, even if regulators are, today, sensitive to the issue of CE, there is a gap in investigating CE disclosures, especially when compared with other bodies of literature dedicated to environmental disclosures [7,8].
The aim is to provide an investigation of firms’ CE disclosure behaviors and the impact that institutional pressures related to regulatory, coercive, and mimetic factors may have on them.

1.2. The Institutional Context

In this context, public institutions and regulators require firms to illustrate their sustainability engagement, especially when their operations involve a wide range of stakeholders, providing an ever more exhaustive set of environmental, social, and governance (ESG) disclosures. The European Union (EU) is playing a relevant role in promoting and supporting corporate social responsibility by proposing sustainable finance methods and requiring a standardized set of sustainability disclosures to provide stakeholders with instruments to judge the firms’ sensitivity toward ESG issues.
Currently, large European companies, which are public interest entities, are applying Directive 2014/95/EU [9] on the disclosure of non-financial and diversity information (“Non-financial Reporting Directive”—“NFRD”). The directive requires ESG disclosure by providing certain types of environmental information, including resource use, but not CE information.
The NFRD requires that the information provided be based on national, European, or international frameworks by specifying the frameworks adopted. In accordance with international practice, the European sustainability disclosures are usually presented in accordance with the standards issued by the Global Reporting Initiative (GRI) [10], which are technical requirements globally recognized and addressed by financial markets as a symptom of high credibility (KPMG, 2022). Member states may require that the information provided be subject to external assurance from an independent assurance provider.
In the process oriented to provide stakeholders with a comprehensive corporate report, the EU enacted Directive 2022/2464 [11] (“Corporate Sustainability Reporting Directive”—“CSRD”), which expands the number of European companies required to prepare a sustainability report. This directive requires that sustainability reports be subject to external assurance by an independent assurance provider. CSRD is effective for financial years beginning on or after 1 January 2024.
The directive replaces the term “non-financial information” with “sustainability information”, which is considered more appropriate as it can also be a useful type of disclosure from a financial perspective, in line with international practice (recital 7).
Among other things, the directive requires reporting on resource use and the CE (Art. 29.b). There is an increased focus on the CE, in line with the growing role of the CE in the EU agenda and the increase in initiatives by European institutions.
The EU has taken several policy initiatives to facilitate the transition to a sustainable economy; in this perspective, the European Green Deal [12], enacted at the end of 2019, represents the EU’s biggest initiative, having the ultimate goal of achieving climate neutrality by 2050 [13]. Among these initiatives is the new CE 2020 Action Plan [14]. This plan includes legislative and nonlegislative measures to promote the transformation of a linear economic model into a circular one in order to reduce the dependency on nonrenewable resources and mitigate the environmental impact of production and consumption [15].
The CSRD requires sustainability reports to be prepared in accordance with the European Sustainability Reporting Standards (ESRS), which specify the content and, where applicable, the structure to be used to present the information required by the CSRD.
As a result, the European Commission adopted the first set of ESRS at the end of July 2023, which includes five general environmental standards, including one specific to the circular economy ESRS 5 E5 “Resource Use and Circular Economy”.
ESRS 5 defines the circular economy as follows: “an economic system in which the value of products, materials and other resources in the economy is maintained for as long as possible, enhancing their efficient use in production and consumption, thereby reducing the environmental impact of their use, minimizing waste and the release of hazardous substances at all stages of their life cycle, including through the application of the waste hierarchy. The goal is to maximize and maintain the value of the technical and biological resources, products, and materials by creating a system that allows for durability, optimal use or reuse, refurbishment, remanufacturing, recycling, and nutrient cycling”.
This definition arises in a context where there is a lack of a generally accepted definition by academia and practice. Current definitions of the CE and its application are considered unclear, inconsistent, and controversial [16]. As a result, this lack has an impact on both academic studies and corporate sustainability reporting itself, making homogeneous behavior more difficult.

1.3. Focal Points and Organization of the Paper

Moving from their review of 114 CE definitions, many studies [17,18] state that the recurrent components are as follows: reduce, reuse, recycle, rot, repurpose, and rethink, followed by recover (7R dimensions). Reference [19], trying to find a definition that can reproduce those concepts consolidated in academia and practice, defined the CE as “an economic system that represents a change of paradigm in the way that human society is interrelated with nature and aims to prevent the depletion of resources, close energy, and materials loops, and facilitate sustainable development through its implementation at the micro (enterprises and consumers), meso (economic agents integrated in symbiosis) and macro (city, regions and governments) levels. Attaining this circular model requires cyclical and regenerative environmental innovations in the way society legislates, produces, and consumes”.
The introduction of a definition of the CE in a mandatory reporting standard in an important economic region such as the EU should promote greater homogeneity in CE studies and the reporting of CE information by companies.
According to the neo-institutional theory, the extent and structure of the CE information provided and, thus, its homogeneity depend on the institutional pressures exerted on them [20].
The literature has devoted limited attention to the relevance of institutional factors that may influence the CE-related disclosure provided by companies. The lack of common definitions, objectives, and forms of implementation of CE has made this type of study challenging.
This paper aims to fill that gap by investigating the impact of institutional pressures related to normative, coercive, and mimetic factors on firms’ behaviors concerning CE disclosures.
Specifically, this research explores and analyzes the following research questions: H1—the level of environmental policy stringency index has a positive effect on CE disclosure; H2—GRI adoption positively influences CE disclosure; H3—the adoption of assurance has a positive impact on CE disclosure; H4—the level of commitment to SDGs positively influences CE disclosure; and H5—belonging to an environmentally sensitive sector positively influences CE disclosure.
The presented research focuses on a sample of 366 non-financial companies, operating in 14 UE countries between 2015 and 2020, and data are extracted from the Refinitiv Eikon dataset.
This research is based on the institutional theory, examining how the adoption of recognized and standardized tools implemented by companies in response to normative, coercive, and mimetic pressures can affect CE disclosures [21,22,23].
Specifically, this paper concludes that each form of institutional pressure, which are coercive, normative, and mimetic factors, influences CE information at different levels. As far as normative pressure is concerned, this study stresses that the declaration of the adoption of GRI standards is positively and significantly related to the CE disclosure, while external assurance and the commitment to the SDGs are not significantly related.
Several implications are emerging from this paper. First of all, this study has found that stricter regulations have a positive impact on CE disclosures. Increased disclosure also means that firms pay more attention to the issue of CE. This consequently stresses that the introduction of more stringent regulations on external assurance and SDGs could also imply a more appropriate impact of these instruments on CE disclosures.
This study provides an initial answer on the mechanisms that can foster greater dissemination and homogeneity of information on the CE and contributes to the literature by examining these mechanisms with respect to several countries operating within the same institutional frame of reference.
In order to pursue our objectives, in the following section, the paper presents a relevant literature review and the aforementioned research questions. The next section illustrates the selection and collection of the dataset and presents the methodology used, describing the variables used to capture the coercive, normative, and mimetic institutional factors, as well as the control variables. The study then presents and examines the obtained results, providing some contextual observations on the data collection. Finally, the research conclusions are presented, highlighting the contribution to the ongoing literature, the main implications, and the limitations arising from the research.

2. Literature Review and Research Hypothesis

2.1. Literature Review

CE disclosure has received increasing attention in the sustainability reporting literature in recent years [24,25]. CE disclosures are generally meant as public information related to the CE provided in sustainability reporting. The content of the disclosure depends on how the researchers choose to define CE [16]. As there may be some differences in the CE definitions used in various studies, it follows that, sometimes, the results found in some parts may not be completely homogeneous.
Scholars focus on the CE-related information provided in the sustainability reports of firms operating primarily in the manufacturing industry and its specific sectors. These studies cover countries that have regulated aspects associated with the CE (e.g., the EU and China) and those that do not have specific regulations.
One branch of studies has investigated the content of CE information disclosed by companies in their sustainability report. The authors of [26] analyzed sustainability reports produced by firms from different countries around the world operating in the fast-moving consumer goods sector and found a focus on information related to end-of-life management and sourcing strategies rather than circular product design and business model strategies. The authors of [27] observed that European food retailers mainly disclose information on waste management practices and greenhouse gas emission reductions. The authors of [28] found that the circularity disclosure provided by Italian cosmetics companies is insufficient in the areas of governance, management, strategy, and performance. Other studies confirmed the limited and reductive use of the concept of CE within sustainability reporting [16].
Several studies have examined the extent of CE-related disclosure conveyed by companies in their sustainability reports. The authors of [25] noted that CE disclosure within sustainability reports is often superficial and inconsistent in the European Union. The authors of [29] stated that in Europe, CE disclosure is in an early phase in the financial sector since only a minority of CE issues are disclosed without being subject to external assurance. Other studies found an absence or vagueness in the CE information provided [16,30,31,32,33]. The authors of [34] demonstrated a low level of information provided by Sri Lankan companies on specific keywords related to CE principles.
Some research shows that only a minority of companies adopt a specific set of quantitative key performance indicators (KPIs) on CE issues [16,28,35,36]. According to [24], this is due to the vagueness and inconsistency of CE disclosure guidance.
The authors of [28] emphasized the importance of reducing the number of reporting guidelines available in practice to promote more homogeneous and comparable reporting by companies. Some scholars have pointed to the need for increased institutional pressure through new regulatory requirements as a way of meeting stakeholders’ expectations [28,33]. However, it should be mentioned that this need for regulation is less felt for certain types of firms or in certain sectors.
Some research has investigated those corporate factors that may influence the level of CE disclosure through sustainability reporting. The authors of [37] demonstrated that some characteristics of the board (e.g., size and gender diversity, presence of the sustainability committee) have a positive impact on the level of CE disclosed by European companies. The authors of [38] found a positive relationship between CE disclosure and firm size, financial leverage, and company profitability, while [39] demonstrated that for Chinese companies, ownership concentration, asset size, and institutional pressure have a positive impact on CE disclosure.
Other studies have focused on institutional factors that may influence CE disclosure. The authors of [40] showed that in China, larger and environmentally sensitive companies tend to disclose more CE information to meet stakeholders’ needs. Similar results were provided by [41], who observed that Spanish companies operating in industry sectors that are more sensitive to institutional pressures (e.g., the oil and energy sector) are more active in disclosing information on the CE. The authors of [33] observed that, internationally, companies operating in the automotive sector are more engaged in disclosing CE-related information than those operating in the defense, transportation, and aerospace sectors.
Few studies analyzed the impact of the different institutional forces on the dissemination of CE disclosure through sustainability reporting. Specific attention was given by [39] who found that European manufacturing companies seek to legitimate their actions by reflecting the institutional logic focused on normative and mimetic (best practices) rather than coercive factors. The authors of [39] highlighted that listed Chinese companies that are required to disclose sustainability information tend to disclose more CE information, providing investors with a more comprehensive understanding of the company’s circularity activities to reduce negative environmental impacts.
The literature has devoted limited attention to the relevance of institutional factors that may influence the CE-related disclosure provided by companies. Thus, there is a gap in empirical research in this area compared with other areas of sustainability disclosure where the topic has been widely studied [8,40,41,42].

2.2. Theoretical Framework and Hypothesis

2.2.1. Institutional Theory

The neo-institutional theory argues that the success and future survival of companies depend on the sociopolitical and economic system in which they operate [23,43].
To carry out their activities, firms need to be accepted by the key stakeholders in their institutional environment [44].
Companies, therefore, have a problem of legitimacy. Legitimacy is defined by [27] as a “generalised perception or assumption that the actions of an entity are desirable, proper, or appropriate within the same socially constructed system of norms, values, beliefs and definitions”. Legitimacy is, on the one hand, a prerequisite for a continuous flow of resources and the continued support of stakeholders and institutions and, on the other hand, a critical resource for the survival and success of the firm [45].
Legitimacy is achieved both by conforming actions to existing social norms and by communicating the actions taken. Sustainability disclosure and, therefore, CE disclosure are tools used by companies to legitimize themselves in the context in which they operate, to meet the expectations of stakeholders and institutions, and to maintain appropriate public support [6,46,47].
The pressure of the institutional environment leads firms to adapt their processes and practices to follow homogeneous behavior [48]. Consequently, in a homogeneous institutional environment, firms tend to become more similar in structure and performance— hence, the realization of processes of institutional isomorphism and, thus, alignment in the organizational behavior of firms. This alignment also affects sustainability reporting and CE reporting [30,49].
The isomorphic forces, i.e., the institutional pressures that drive this homogenization process, are of different kinds. Although they often operate together, there are three main mechanisms: coercive, normative, and mimetic [21].
Coercive isomorphism arises from political, legal, or regulatory influences. It is the result of formal and informal forces exerted by the state or other controlling organizations [50].
Coercive isomorphism occurs when external authorities, like government bodies, impose pressure to conform. Normative isomorphism refers to the pressure to adhere to established standards, norms, values, and cultures, as well as to adopt systems and techniques that are recognized as legitimate by relevant professional groups. Mimetic isomorphism arises from the pressure to copy or imitate the managerial practices of successful organizations [51,52].
In this frame, this paper aims to analyze the extent to which these isomorphic forces (coercive, normative, and mimetic isomorphism) influence the CE disclosure provided by European companies.
To assess the existence and magnitude of the effect of isomorphism in a homogeneous institutional context, this paper examines a set of leading European firms operating in a homogeneous institutional context (EU countries) over a homogeneous period (2015 to 2020). For this purpose, specific parameters have been identified and used in this paper to measure the existence of different types of isomorphism.

2.2.2. Coercive Isomorphism and CE Disclosure

Coercive isomorphism arises from political, legal, or regulatory influences. It is the result of formal and informal forces exerted by the state or other controlling organizations [50]. This mechanism operates mainly through norms, regulations, sanctions, and controls. The stricter the norms and their enforcement, the stronger the isomorphic pressure on firms; environmental reporting legislation is an example of this type of pressure [53].
The level of the environmental policy stringency index is an indicator of government coercive pressure on companies to disclose the CE (see Section 3.2). This indicator is expected to have a positive effect on CE disclosure. Thus, as the level of the environmental policy stringency index increases, the CE information disclosed by companies should increase.
Therefore, the first hypothesis of this study can be stated as follows:
Hypothesis 1 (H1). 
The level of the environmental policy stringency index has a positive effect on CE disclosure.

2.2.3. Normative Isomorphism and CE Disclosure

Normative isomorphism is associated with the standards and practices adopted by professionals in a particular field or industry. These rules are the result of interaction between professionals, industries, and other organizations operating in a specific field. These rules are assimilated by practitioners through training and experience until they become a genuine form of self-regulation (soft law) that leads to consistency [23,54,55]. This force is primarily the result of professionalization and is based on a social consensus about the ‘right thing to do’—so much so that compliance with specific professional rules is taken for granted [56]. Sustainability standards are an example of professional rules. They, if generally accepted, standardize the way of acting in companies so that they come to behave in a similar way.
Internationally, there are various sustainability frameworks and standards issued by professional bodies. Currently, the most widely used and recognized standards worldwide are those published by the GRI (KPMG, 2022). In fact, GRI has gained wide recognition among firms in recent decades and is considered the most consistent reporting methodology [57]. The GRI helps companies disclose their sustainability activities and, also, requires companies to report qualitative and quantitative indicators to describe and measure their circularity activities. The GRI is a key normative body for sustainability disclosure and CE information [49]. The authors of [58] argued that the adoption of GRI guidelines plays a role as a solicitor toward companies to release CE information. The adoption of the GRI requirements for the disclosure of CE information is an indicator of the existence of normative pressure. This study, therefore, hypothesizes the following:
Hypothesis 2 (H2). 
GRI adoption positively influences CE disclosure.
Another practice that indicates the existence of normative isomorphism is the use of external assurance on sustainability disclosure and, by extension, on CE disclosure. Companies may use external assurance from an independent third party to increase the credibility of the information provided. Previous research on this topic has produced conflicting results. Some studies recognize the positive effect of external assurance on the information produced. The authors of [30] found that companies that provide voluntary external assurance report more environmental performance indicators from a CE perspective than companies that do not provide such assurance. The authors of [20] found that voluntary assurance acts as a legitimization tool used by companies in response to, among other things, normative pressure. Other studies show that shareholders react negatively to environmental information subject to assurance due to the questionable quality, independence, and transparency of these practices [59]. The authors of [29] found that CE disclosures in the financial sector are not subject to external assurance. This issue, therefore, merits further investigation. In line with the findings of the only study to examine the issue from a CE perspective in the manufacturing sector, it has been expected a positive impact of external assurance on CE disclosure. Thus, this study hypothesized the following:
Hypothesis 3 (H3). 
The adoption of assurance has a positive impact on CE disclosure.
The level of commitment to the Sustainable Development Goals (SDGs) is another variable used to measure the normative pressure. The SDGs were issued in 2015 by the United Nations with the aim to promote the worldwide adoption of sustainable behaviors and achieve sustainable development. In response to the issue of the SDGs, countries, citizens, organizations, and firms adopted different actions, presenting various degrees of compliance with the SDGs, revealing a different level of attention toward sustainability practices [60,61]. The CE can contribute to achieving many SDGs, not just the closest one (SDG 12: Sustainable Consumption and Production). The authors of [25,62] found the existence of a direct relationship between the CE and SDG 6 (Clean Water and Sanitation), SDG 7 (Affordable and Clean Energy), SDG 8 (Decent Work and Economic Growth), and SDG 15 (Life on Land).
In line with these considerations, this research expects that higher degrees of commitment to the SDGs are positively associated with greater levels of CE disclosure, proposing the following hypothesis:
Hypothesis 4 (H4). 
The level of commitment to the SDGs positively influences CE disclosure.

2.2.4. Mimetic Isomorphism and CE Disclosure

Mimetic isomorphism is often a response to institutional uncertainty, leading companies to imitate the behavior and practices of successful firms to strengthen their legitimacy. Firms tend to imitate competitors that constitute the benchmark in the industry [63]. Thus, they follow the path taken by successful competitors [53].
Mimetic pressure is particularly relevant in times of institutional change and is a response to the uncertainties caused by these changes [7]. The behavior is to copy successful firms. More environmentally sensitive firms face a situation of uncertainty, given the recent focus on the issue by stakeholders and institutions. It is, therefore, likely that these firms provide more information on CE by referring to leading firms. In previous studies, this relationship was found in specific sectors [41] and in China [40]. This study extends the analysis to other sectors and a different geographical area. It is assumed that this positive correlation is also found in these sectors and the EU area.
Therefore, the hypothesized relationship between the environmentally sensitive sector and CE information is stated as follows:
Hypothesis 5 (H5). 
Belonging to an environmentally sensitive sector positively influences CE disclosure.

3. Method

3.1. Sample Selection and Data Source

This study is based on a sample of 366 companies and 1261 observations of European non-financial companies operating in 14 European countries between 2015 and 2020.
The analysis considered the time interval from 2015 to 2020 to investigate what happened after the introduction of some limited form of CE regulation (the first CE Action Plan was issued in 2015). Moreover, 2015 was chosen as the starting year because it was the year following the enactment of Directive 2014/95/EU, by which the European legislature introduced a requirement for specific categories of large companies to disclose non-financial information in sustainability reports (SRs). The last year analyzed was 2020 because it was the first year after the issuing of the report on the implementation of the new CE action plan and the European Green Deal.
Through the Refinitiv Eikon dataset, it was possible to collect accounting and financial data, as well as environmental information (Table 1).

3.2. Dependent, Independent, Moderating and Control Variables

Table 2 summarizes all the variables used in the analysis, specifying the ways in which they were measured and the source of data for each one.
The dependent variable, CE-related disclosure (CEDisc), is the result of the unweighted sum of 11 environmental items entered into the Refinitiv Eikon database, measuring a company’s level of environmental disclosure on CE transition issues. To each of the 11 items considered, a score of 1 was assigned when the company disclosed specific environmental information; otherwise, a score of 0 was assigned [64,65,66,67].
The 11 environmental items used to define the CEDisc value belong to three different categories as follows: 6 items, emissions; 3, innovation; and 2, resource use (see Table 3). The emissions category contains information regarding the company’s commitment and success as a function of reducing environmental emissions in production processes. The innovation category defines companies’ willingness to reduce environmental costs and obligations by making use of new green technologies and circularity [73]. Finally, the category of resource use defines the behavior of companies toward adopting the 7Rs paradigm, pursuing the goal of ensuring that future generations also use resources in a manner consistent with the SDGs, improving supply chain management.
The model used different independent variables to measure the coercive, normative, and mimetic pressures. More specifically, we used Stri_Env_Reg, referring to the environmental policy stringency index developed by the OECD [74]. This index represents a country-specific measure of the stringency of the environmental policy. The OECD defines stringency as the level to which environmental regulations identify a price on polluting or environmentally detrimental behavior. The index varies from 0 (not stringent) to 6 (highest level of stringency). This score represents coercive pressure.
To measure the normative pressures, the model considered the GRI variable, which takes the value of 1 if the company adopts GRIs and discloses information about them; otherwise, it takes the value of 0, and the Ass variable, which takes the value of 1 if the company obtains the assurance and 0 otherwise. Moreover, it has used the Commitment_SDG, which represents the percentage of SDG achievement, measuring a company’s total progress toward reaching all 17 SDGs. A score of 100 means that the company achieved all SDGs.
In the end, the regression considered EnvSensSect as an independent variable measuring mimetic pressure. In particular, this variable is dichotomous, so it takes a value of 1 if the company belongs to the ecological sector with environmental sensitivity and a value of 0 otherwise [3,69,70,71,72].
In addition, the model included some control variables to resolve possible endogeneity problems due to the omitted variables and to avoid biased results:
-
Firm Size (FirmSize): natural logarithm of total assets;
-
Leverage (Lev): long-term debt divided by total assets;
-
ROA (ROA): return on assets;
-
Year (Year): dummies to control for their fixed effects.

3.3. Regression Analysis

To test the above hypotheses, this research developed the following regression models:
C E D i s c =   α + β 1 S t r i E n v R e g + β 2   A S S + β 3 C o m m i t m e n t _ S D G + β 4 E n v S e n s S e c t + β 5 F i r m S i z e + β 6 B o L e v + β 7 R O A + β 8 y e a r + ε

4. Results

4.1. Descriptive Statistics

Table 4 shows the descriptive statistics of all the variables included in the analysis.
The analysis shows that, on average, companies in the sample published about the four indicators on environmental issues, noting little attention to issues related to the CE paradigm. The variable assumes a value from 0 to 10.
This means that companies provided information on less than half of the CE-related items identified, showing little attention to CE-related issues.
It can be seen in Table 4 that some companies disclosed little information regarding the CE, and the minimum value is 0.
The ranking of Stri_Env_Reg varies between 2.44 and 4.89, with a mean of 3.63%, indicating that values near 0 present policies defined as “not stringent”, while those near 6 are considered “highest level of stringency” policies. The mean value is 3.6, indicating that half of the sample companies operate in the state, presenting policies with a relatively high level of stringency.
The GRI takes minimum and maximum values of 0 and 1; the mean value is 99%, revealing that almost all companies in the sample referred to the GRI and disclosed information in this regard for the period analyzed. The minimum and maximum values of Ass are 0 and 1, respectively; the mean value is 90%, revealing that not all companies decided to have their report assured.
The percent of Commitment_SDG is 82.56%, highlighting a limited achievement of the SDGs by the companies analyzed. It varies relatively among the companies in the sample, ranging from 79.01 to 86.51.
The sampled companies have a mean EnvSensSect of 0.64. This means that 64 percent of companies operate in an environmentally conscious sector.
In terms of the control variables, the average value of ROA is 0.43%, assuming values from −33 to 41. Lev assumes values from 0 to 86, with a mean of 21.10%.
Before performing the regression analysis, the correlations between variables were analyzed (Table 5).
Stri_Env_Reg is positively correlated with CEDisc. Commitment_SDG is negatively correlated with CEDisc. Ass and GRI are positively correlated with CEDisc. EnvSensSec is also positively correlated with CEDisc. In addition, almost all control variables are correlated with CEDisc. In particular, FirmSize is positively correlated with CEDisc. ROA is positively correlated with CEDisc, while year, on the other hand, is negatively correlated with CEDisc.

4.2. Regression Results

Table 6 shows the results of the regression analysis conducted using Stata 16 Software. More specifically, the table reports the findings for the tests of H1, H2, H3, H4, and H5.
Model OLS shows the findings for the test of the direct effect of all the independent variables on CE-related disclosure.
In the ordinary least squares regression (OLS), the year variable was inserted to control for its fixed effects. The results reported in the OLS model confirm hypothesis H1, showing a positive and significant relationship between Stri_Env_Reg and CE-related disclosure. More specifically, the coefficient of Stri_Env_Reg is positive and statistically significant at better than the 1 percent level to explain variations in CEDisc (β = 0.7292, p < 0.01).
This result is in line with the findings of most previous studies that investigated the relationship between Stri_Env_Reg and the wider concept of environmental disclosure, highlighting that the presence of Stri_Env_Reg increases the level of environmental information disclosed by companies [40,67,75,76,77,78,79,80].
Therefore, companies operating in countries characterized by higher levels of regulatory quality tend to release more information to respond to coercive pressure. Although there are other forms of coercive pressure, such as the country’s legal system and market regulation [30], the presence and issue of specific rules are considered the main source of coercive isomorphism, leading companies to provide environmental disclosure to be compliant with laws [81].
Hypothesis H2 is confirmed, showing that GRI positively influences CE-related disclosure. More specifically, the coefficient of GRI is positive and statistically significant at better than the 1 percent level to explain variations in CEDisc (β = 3.1585, p < 0.01).
This result confirms the findings of previous studies on the positive effect of the adoption of GRI standards on environmental disclosure [30], revealing that companies release CE disclosures to follow the standards issued by professional organizations [82]. This way, companies operate in a way that is considered right according to the professionalization of the specific field.
Hypothesis H3 is not confirmed because the coefficient of Assurance is not statistically significant.
Hypothesis H4 is not confirmed, showing that the coefficient of Commitment_SDG is not statistically significant.
Hypothesis H5 is confirmed because EnvSenSect, representing mimetic pressure, has a good influence on the disclosure related to the CE. More specifically, the coefficient of EnvSenSect is positive and statistically significant at better than the 1 percent level to explain variations in CEDisc (β = 1.4222, p < 0.01), revealing that companies tend to adopt the same behaviors of other companies operating in the same industry. The findings of the present study confirm those of previous research according to which the presence within an industry of companies that release environmental information positively influences the environmental data provided by the other companies operating in the same sector [30,75].
With respect to the control variables, Table 6 reports that firm size positively and significantly influences the level of CE disclosure (β = 0.6007197, p < 0.01). In line with the findings of previous studies, these results reveal that the bigger the company is, the higher the level of CE disclosure provided [38]. From a stakeholder theory perspective, bigger companies tend to attract interest from a greater number of stakeholders and, therefore, present greater visibility. To satisfy the interests of all these stakeholders, larger companies tend to release more information [7]. In addition, bigger companies have more resources to invest in the communication process [83].
Table 6 also reveals that the leverage negatively and significantly affects the CE disclosure released (β = −1.677465, p < 0.01). Although, according to the stakeholder theory, companies with higher levels of leverage should release more data to satisfy the information needs of debtholders [84], the findings of this study show a negative association between leverage and CE disclosure. A possible explanation could be that companies tend to privately provide information to banks, reducing the corporate disclosure publicly released to all stakeholders [85]. This happens especially in companies operating in bank-oriented countries, such as Italy.

4.3. Robustness Tests

This study could benefit from more robustness tests. More specifically, different proxies were used to measure the dependent variable. The CEDisc was split into its three components: the emissions category, the innovation category, and the resource use category.
The proxy can be used without any or with minimal application code modifications.
Regarding this, it seems appropriate to test different OLS regression models.
The first proxy used as the dependent variable is the emissions category, and by conducting an OLS analysis, the following variables are found to be statistically significant: Stri_Env_Reg, EnvSensSect, and GRI. These results confirm hypotheses H1, H2, and H5 regarding their positive relationship with CE disclosure. Therefore, coercive, normative, and mimetic pressures have a positive impact on the disclosure of the CE.
The second proxy is composed of the innovations category; in this case, the regression results show that H1 and H5 are confirmed.
The third proxy concerns the resource use category and confirms the H1 and H2 hypotheses in line with the results of the main model.
The details of the robustness analysis are not presented here but are available from the authors upon request.

5. Discussion

The findings of this paper show the relevance of institutional factors in influencing the CE-related disclosure provided by companies.
On the side of coercive pressure, this paper analyzes the impact of Stri_Env_Reg on CE disclosure to understand whether and to what extent formal and informal forces exerted by the rules [50] succeed in stimulating a greater and more homogeneous production of CE information. Stri_Env_Reg greatly increases the level of information dissemination regarding the CE.
This finding is consistent with the results of empirical research on environmental reporting [30,76], according to which companies tend to provide more and more consistent information after the introduction of stricter regulations. Hence, some scholars call for new regulations for more comprehensive and analytical CE disclosure [28,33].
This result suggests that there may be an improvement in the quantity and homogeneity of CE information as a result of the more stringent European sustainability legislation (CSRD and ESRS S5).
It should be noted, however, that this coercive effect does not mean that the quality of disclosure will automatically improve. Some research has found that Stri_Env_Reg is not a driving factor for better CE disclosure because when regulations are too stringent, companies are more concerned with complying with the specific existing regulation(s) than disclosing CE information [60,64,74]. On the other hand, isomorphism satisfies the need for legitimacy but not the need for organizational efficiency and transparency [23]. Companies may engage in behaviors that appear to meet stakeholder expectations in order to create a positive image of themselves while masking their actions [86,87]—hence, the risk of greenwashing, even in the presence of stricter regulations [88].
On the side of normative pressure, this paper examines the impact of GRI, external assurance, and SDGs on CE disclosure. The obtained results are mixed.
GRI adoption positively influences CE disclosure. Thus, under normative pressure, firms tend to comply with GRI requirements. The findings of this paper reveal that coherently with normative isomorphism, companies have widely internalized the GRI standards, probably because they consider these standards the ‘right thing to do’ [7]. The GRIs, in fact, are the most widely used standards worldwide [11,89,90]. More probably, this could be the consequence of their normative nature, reported in the purpose paragraph of GRI 1 Foundation: The GRI standards enable an organization to publicly disclose its most significant impacts on the economy, environment, and people, including impacts on their human rights and how the organization manages these impacts (GRI 1 Foundation).
This result should be interpreted together with the findings revealing the low amount of CE disclosure released. Several studies have found low levels of CE disclosure [16,25,32,33].
The wide adoption of the GRI by companies may partly explain these findings.
The GRI guidelines only address some aspects of the CE [34], so the CE is never mentioned in the consolidated GRI sustainability reporting standards (GRI, 2016). The disclosure of the CE required by GRI lacks an organic view of the CE, in line with what happens in other sustainability frameworks [24]. Consequently, the lack of a CE standard could explain the paucity of disclosed CE information.
In Europe, this critical issue is expected to be addressed with the adoption of ESRS, which includes a specific standard on CE: ESRS 5 E5 “Resource Use and Circular Economy”. This will help companies understand what actions they need to take to comply with regulatory requirements and, thus, what types of CE information they need to provide in their sustainability report.
The other variable that indicates the existence of normative isomorphism is the use of external assurance in sustainability disclosure and, by extension, in CE disclosure. Assurance, provided by an independent third party, increases the credibility and reliability of the information provided. Assurance acts as a legitimization tool for stakeholders [91] and is used by companies in response to external pressure. This research shows that assurance does not statistically affect CE disclosure. The non-stringent provisions of the GRI, especially for CE disclosure, may explain this result. While the use of assurance practices helps to improve the credibility and completeness of the information disclosed [77], it loses its usefulness when it refers to general provisions. The lack of detailed rules to refer to makes it more difficult to perform assurance because there is no specific parameter to which the completeness and accuracy of the information disclosed can be referred (CSRD, 2022). This could explain the lack of a significant correlation between assurance and disclosure of the CE disclosed.
Regarding the level of Commitment_SDG, the findings show that it does not have a positive effect on the diffusion of the CE. This result is partially consistent with [68] that found that the level of commitment to the SDGs has a weak accelerating effect in this dimension. These findings seem to indicate a limited perception in practice of the link between the different SDGs and the CE. The introduction of specific guidelines could help practitioners to make this link more explicit.
Finally, on the side of mimetic pressure, the environmentally sensitive sector has a positive relationship with the dissemination of CE information.
There is a lot of uncertainty around the CE. There are numerous EU initiatives on the CE as part of the Green Deal 2019. The EU set out its own action plan on the CE, which aims to facilitate the EU’s transition to a circular economy by creating sustainable growth and jobs. The plan includes both legislative and nonlegislative measures.
Companies tend to provide more homogeneous information on CE in response to the existing economic and regulatory uncertainties that this situation creates [7,92]. To this end, companies benchmark their activities and disclosures against leading companies that are recognized as best practices in their institutional context [93]. Thus, there is a convergence of practices as a result of mimetic pressure.
Our finding is consistent with previous studies that have found that environmentally sensitive firms tend to be more active in disclosing information on the CE [40,41].

6. Conclusions, Implications, and Limitations

This study uses neo-institutional theory to analyze the CE disclosure of a set of 366 companies, not restricted by sector, operating in 14 EU countries between 2015 and 2020. The year 2015 was selected as this was the year after the adoption of the NFRD, while 2020 was the first year after the publication of the report on the implementation of the European Green Deal (2019) and the new CE Action Plan (2020).
This study aimed to understand the forces influencing the disclosure of CE information in the sustainability reporting of European companies and their convergence toward common practices after the introduction of mandatory disclosure by law and some relevant EU initiatives in the field of the CE (CE Action Plan).
This paper shows that the institutional pressures exerted by coercive, normative, and mimetic factors affect the CE information disclosed by a category of listed large European non-financial firms under study. The results show that all three forms of institutional pressure influence the level of CE disclosure issued by the firms.
More specifically, the stringency of the environmental policy (coercive pressure), as well as the adoption of the GRI standards (normative pressure) and belonging to an environmentally sensitive sector (mimetic pressure), influences the level of the information provided.
However, with specific regard to the normative pressure, the results obtained are mixed. In fact, the exclusive adoption of GRI is positively and significantly related to the CE disclosure. The presence of an external assurance, as well as the commitment to the SDGs, is not significantly related to the CE disclosure. The absence of an analytical standard that organically addresses the issue of CE, by guiding companies in the provision of their information, may explain the irrelevance of these factors in the process of convergence of the information produced.
According to [24], to date, only five documents refer to the CE—the documents are issued by the following organizations: GRI, World Economic Forum (WEF), Eco-Management and Audit Scheme (EMAS), British Standards Institute (BSI), and Underwriters Laboratories (UL). The last three documents illustrate how the companies can implement the CE principles within their organization, providing only indirect suggestions on the CE information to report. On the other hand, the GRI and WEF specifically give suggestions on the CE information to disclose. More precisely, the GRI 306 illustrates the information to release on waste management, and the WEF provides suggestions on the quantitative metrics to release on resource circularity. However, there is no unique standard that provides suggestions on the information, both quantitative and qualitative, to release on all aspects of the CE.
It should be verified whether CSRD requests to adopt ESRSs and produce a mandatory assurance on sustainability disclosures (and, then, also on ESRS 5) can determine a different orientation.
This research adds to previous studies on the determinants of disclosure in different ways.
First, it focuses on CE information, which is a less studied topic compared with the widely conducted studies on environmental or sustainability disclosure.
Moreover, this study adds to previous studies on the determinants of sustainability disclosure by analyzing the institutional factors rather than the widely investigated firm-specific and corporate governance factors. Most previous studies demonstrated that both firm-specific factors, such as the firm size, leverage, or profit, and the corporate governance characteristics, such as the composition of the board of directors, influence the amount of environmental or sustainability information disclosed by firms. However, few studies investigated the role of institutional pressures in influencing the level of disclosure, particularly CE information. In doing so, a doctrinal gap is filled by helping to complete the studies on the subject.
Finally, this research adds to previous studies on disclosure by measuring the CE information provided by companies with an indicator developed on the basis of specific environmental items gathered by the Refinitiv Eikon database, which could be used in future research.
The findings of this paper have some important practical implications, particularly the following:
-
This paper provides evidence for policymakers that stricter regulations have a positive impact on disclosures related to the CE. Increased disclosure also means that firms pay more attention to the issue of the CE. To provide transparency, firms must organize themselves to monitor and communicate outcomes pertaining to the matter disclosed. Therefore, one possible way to enhance the companies’ attention toward CE topics could be to increase the rules and standards devoted to this issue. In this regard, the recent European initiatives on CE disclosure (CSRD and ESRS) are commendable. The issues of CSRD and ESRS should promote more homogeneous and analytical CE disclosure, resulting in increased sensitivity among firms on this topic. A similar approach may be followed for the same purpose by other regional or local policymakers.
-
This paper emphasizes the necessity of introducing more stringent regulations on assurance and SDGs by the regulator or professional bodies to achieve greater uniformity of behavior by firms.
-
This paper offers scholars and practitioners measurement tools to build more precise and comprehensive models that measure the relationship between institutional mechanisms of isomorphism and CE reporting.
This research has limitations.
First, the selected variables are not the only possible options, others can be chosen as well.
Second, although it is a longitudinal study, the research does not investigate the years prior to the issuance of any kind of regulation on the non-financial information to be disclosed (NFRD). Future research could extend the analysis to the period before 2015 to further understand whether the issue of disclosure regulation is an institutional factor that influences the company’s decision to disclose CE information.
Future research could also extend the analysis to the period after 2020—that is, after the issuing of the report on the implementation of the CE Action Plan and the European Green Deal—to understand their institutional pressures on companies’ disclosure behavior. At the same time, similar studies could investigate the CE disclosure after the enactment (and the adoption) of the CSRD and ESRS 5. Finally, this research exclusively investigated the quantity of the CE information released, and it did not consider the quality of disclosure.

Author Contributions

Conceptualization, R.N., S.P., M.V. and M.P. methodology, R.N. and S.P.; software, R.N.; validation, M.V.; formal analysis, R.N. and S.P.; investigation, R.N., S.P., M.V. and M.P.; resources, M.V., M.P. and S.P; data curation, R.N.; writing—original draft preparation, M.P., R.N., S.P. and M.V.; writing—review and editing, M.P., R.N., S.P. and M.V.; visualization, M.P., supervision, M.P.; project administration, S.P.; funding acquisition, M.V., M.P. and S.P. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Informed Consent Statement

Informed consent was obtained from all subjects involved in the study.

Data Availability Statement

The data presented in this study are available on request from the corresponding author.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Bagnoli, C.; Massaro, M.; Mas, F.D.; Demartini, M. Defining the concept of business model: Searching for a business model framework. Int. J. Knowl. Syst. Sci. 2018, 9, 48–64. [Google Scholar] [CrossRef]
  2. Korhonen, J.; Honkasalo, A.; Seppälä, J. Circular Economy: The Concept and its Limitations. Ecol. Econ. 2018, 143, 37–46. [Google Scholar] [CrossRef]
  3. Liu, L.; Ramakrishna, S. (Eds.) An Introduction to Circular Economy; Springer: Singapore, 2021. [Google Scholar] [CrossRef]
  4. MacArthur, E.; Zumwinkel, K.; Stuchtey, M.R. Growth within: A Circular Economy Vision for a Competitive Europe; Ellen MacArthur Foundation: Whatstandwell, UK, 2015. [Google Scholar]
  5. Kumar, V.; Sezersan, I.; Garza-Reyes, J.A.; Gonzalez, E.D.; Al-Shboul, M.A. Circular economy in the manufacturing sector: Benefits, opportunities and barriers. Manag. Decis. 2019, 57, 1067–1086. [Google Scholar] [CrossRef]
  6. Heras-Saizarbitoria, I.; Boiral, O.; Testa, F. Circular economy at the company level: An empirical study based on sustainability reports. Sustain. Dev. 2023, 31, 2307–2317. [Google Scholar] [CrossRef]
  7. De Villiers, C.; Rinaldi, L.; Unerman, J. Integrated Reporting: Insights, gaps and an agenda for future research. Acc. Audit. Account. J. 2014, 27, 1042–1067. [Google Scholar] [CrossRef]
  8. Lewis, B.W.; Walls, J.L.; Dowell, G.W.S. Difference in degrees: CEO characteristics and firm environmental disclosure. Strat. Manag. J. 2013, 35, 712–722. [Google Scholar] [CrossRef]
  9. European Union Directive. Directive 2014/95/EU of the European Parliament and of the Council of 22 October 2014 Amending Directive 2013/34/EU as Regards Disclosure of Non-Financial and Diversity Information by Certain Large Undertakings and Groups. 2014. Available online: https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX%3A32014L0095 (accessed on 31 July 2023).
  10. GRI. Consolidated Set of GRI Sustainability Reporting Standards. 2016. Available online: https://www.ekvilib.org/wp-content/uploads/2018/03/GRI-standardi-2016.pdf (accessed on 31 July 2023).
  11. European Union Directive. Directive 2022/2464 of the European Parliament and of the Council of 14 December 2022 Amending Regulation (EU) No 537/2014, Directive 2004/109/EC, Directive 2006/43/EC and Directive 2013/34/EU, as Regards Corporate Sustainability Reporting. 2022. Available online: https://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri=CELEX:32022L2464&from=EN (accessed on 31 July 2023).
  12. European Commission. Communication from the Commission to the European Parliament, the European Council, the Council, the European Economic and Social Committee and the Committee of the Regions. The European Green Deal COM/2019/640 Final. 2019. Available online: https://eur-lex.europa.eu/resource.html?uri=cellar:b828d165-1c22-11ea-8c1f-01aa75ed71a1.0006.02/DOC_1&format=PDF (accessed on 31 July 2023).
  13. Eckert, E.; Kovalevska, O. Sustainability in the European Union: Analyzing the Discourse of the European Green Deal. J. Risk Financ. Manag. 2021, 14, 80. [Google Scholar] [CrossRef]
  14. European Commission. A New Circular Economy Action Plan for a Cleaner and More Competitive Europe. COM(2020)98. Available online: https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=COM%3A2020%3A98%3AFIN (accessed on 31 July 2023).
  15. Scarpellini, S.; Marín-Vinuesa, L.M.; Aranda-Usón, A.; Portillo-Tarragona, P. Dynamic capabilities and environmental accounting for the circular economy in businesses. Sustain. Account. Manag. Policy J. 2020, 11, 1129–1158. [Google Scholar] [CrossRef]
  16. Heras-Saizarbitoria, I.; Urbieta, L.; Boiral, O. Organizations’ engagement with sustainable development goals: From cherry-picking to SDG-washing? Corp. Soc. Responsib. Environ. Manag. 2021, 29, 316–328. [Google Scholar] [CrossRef]
  17. Jestratijevic, I.; Maystorovich, I.; Vrabič-Brodnjak, U. The 7 Rs sustainable packaging framework: Systematic review of sustainable packaging solutions in the apparel and footwear industry. Sustain. Prod. Consum. 2021, 30, 331–340. [Google Scholar] [CrossRef]
  18. Kirchherr, J.; Hekkert, M.; Bour, R.; Huijbrechtse-Truijens, A.; KostenseSmit, E.; Muller, J. Breaking the Barriers to the Circular Economy. 2017. Available online: https://circulareconomy.europa.eu/platform/sites/default/files/171106_white_paper_breaking_the_barriers_to_the_circular_economy_white_paper_vweb-14021.pdf (accessed on 31 July 2023).
  19. Prieto-Sandoval, V.; Jaca, C.; Ormazabal, M. Towards a consensus on the circular economy. J. Clean. Prod. 2018, 179, 605–615. [Google Scholar] [CrossRef]
  20. Martínez-Ferrero, J.; García-Sánchez, I.-M. Coercive, normative and mimetic isomorphism as determinants of the voluntary assurance of sustainability reports. Int. Bus. Rev. 2017, 26, 102–118. [Google Scholar] [CrossRef]
  21. DiMaggio, P.J.; DiMaggio, P.J.; Powell, W.W.; Powell, W.W. The Iron Cage Revisited: Institutional Isomorphism and Collective Rationality in Organizational Fields. Am. Sociol. Rev. 1983, 48, 147–160. [Google Scholar] [CrossRef]
  22. Martínez-Ferrero, J.; Ruiz-Cano, D.; García-Sánchez, I. The Causal Link between Sustainable Disclosure and Information Asymmetry: The Moderating Role of the Stakeholder Protection Context. Corp. Soc. Responsib. Environ. Manag. 2015, 23, 319–332. [Google Scholar] [CrossRef]
  23. Scott, W.R. Institutions and Organizations; Foundations for Organizational Science; Sage: London, UK, 1995. [Google Scholar]
  24. Opferkuch, K.; Caeiro, S.; Salomone, R.; Ramos, T.B. Circular economy in corporate sustainability reporting: A review of organisational approaches. Bus. Strat. Environ. 2021, 30, 4015–4036. [Google Scholar] [CrossRef]
  25. Opferkuch, K.; Caeiro, S.; Salomone, R.; Ramos, T.B. Circular economy disclosure in corporate sustainability reports: The case of European companies in sustainability rankings. Sustain. Prod. Consum. 2022, 32, 436–456. [Google Scholar] [CrossRef]
  26. Istudor, L.-G.; Suciu, M.-C. Bioeconomy and Circular Economy in the European Food Retail Sector. Eur. J. Sustain. Dev. 2020, 9, 501–511. [Google Scholar] [CrossRef]
  27. Suchman, M.C. Managing legitimacy: Strategic and institutional approaches. Acad. Manag. Rev. 1995, 20, 571–610. [Google Scholar] [CrossRef]
  28. Tiscini, R.; Martiniello, L.; Lombardi, R. Circular economy and environmental disclosure in sustainability reports: Empirical evidence in cosmetic companies. Bus. Strategy Environ. 2022, 31, 892–907. [Google Scholar] [CrossRef]
  29. Moneva, J.M.; Scarpellini, S.; Aranda-Usón, A.; Etxeberria, I.A. Sustainability reporting in view of the European sustainable finance taxonomy: Is the financial sector ready to disclose circular economy? Corp. Soc. Responsib. Environ. Manag. 2022, 30, 1336–1347. [Google Scholar] [CrossRef]
  30. Dagiliene, L.; Frendzel, M.; Sutiene, K.; Wnuk-Pel, T. Wise managers think about circular economy, wiser report and analyze it. Research of environmental reporting practices in EU manufacturing companies. J. Clean. Prod. 2020, 274, 121968. [Google Scholar] [CrossRef]
  31. Janik, A.; Ryszko, A.; Szafraniec, M. Greenhouse Gases and Circular Economy Issues in Sustainability Reports from the Energy Sector in the European Union. Energies 2020, 13, 5993. [Google Scholar] [CrossRef]
  32. Marco-Fondevila, M.; Llena-Macarulla, F.; Callao-Gastón, S.; Jarne-Jarne, J. Are circular economy policies actually reaching organizations? Evidence from the largest Spanish companies. J. Clean. Prod. 2020, 285, 124858. [Google Scholar] [CrossRef]
  33. Roberts, L.; Georgiou, N.; Hassan, A.M. Investigating biodiversity and circular economy disclosure practices: Insights from global firms. Corp. Soc. Responsib. Environ. Manag. 2022, 30, 1053–1069. [Google Scholar] [CrossRef]
  34. Gunarathne, N.; Wijayasundara, M.; Senaratne, S.; Kanchana, P.D.K.; Cooray, T. Uncovering corporate disclosure for a circular economy: An analysis of sustainability and integrated reporting by Sri Lankan companies. Sustain. Prod. Consum. 2021, 27, 787–801. [Google Scholar] [CrossRef]
  35. Stewart, R.; Niero, M. Circular economy in corporate sustainability strategies: A review of corporate sustainability reports in the fast-moving consumer goods sector. Bus. Strategy Environ. 2018, 27, 1005–1022. [Google Scholar] [CrossRef]
  36. Cunha, F.; Dinis-Carvalho, J.; Sousa, R.M. Performance Measurement Systems in Continuous Improvement Environments: Obstacles to Their Effectiveness. Sustainability 2023, 15, 867. [Google Scholar] [CrossRef]
  37. Esposito, B.; Raimo, N.; Malandrino, O.; Vitolla, F. Circular economy disclosure and integrated reporting: The role of corporate governance mechanisms. Bus. Strat. Environ. 2023. early view. [Google Scholar] [CrossRef]
  38. Vitolla, F.; Raimo, N.; Rubino, M.; Garegnani, G.M. Do cultural differences impact ethical issues? Exploring the relationship between national culture and quality of code of ethics. J. Int. Manag. 2021, 27, 100823. [Google Scholar] [CrossRef]
  39. Wang, P.; Che, F.; Fan, S.; Gu, C. Ownership governance, institutional pressures and circular economy accounting information disclosure: An institutional theory and corporate governance theory perspective. Chin. Manag. Stud. 2014, 8, 487–501. [Google Scholar] [CrossRef]
  40. Kuo, L.; Chang, B.-G. The affecting factors of circular economy information and its impact on corporate economic sustainability-Evidence from China. Sustain. Prod. Consum. 2021, 27, 986–997. [Google Scholar] [CrossRef]
  41. García-Sánchez, I.-M.; Somohano-Rodríguez, F.-M.; Amor-Esteban, V.; Gonzalez-Valdueza, B. Circular Economy Projects and Firm Disclosures in an Encouraging Institutional Environment. Sustainability 2022, 14, 1149. [Google Scholar] [CrossRef]
  42. Cubilla-Montilla, M.I.; Galindo-Villardón, P.; Nieto-Librero, A.B.; Galindo, M.P.V.; García-Sánchez, I.M. What companies do not disclose about their environmental policy and what institutional pressures may do to respect. Corp. Soc. Responsib. Environ. Manag. 2019, 27, 1181–1197. [Google Scholar] [CrossRef]
  43. Lombardi, R.; Secundo, G. The digital transformation of corporate reporting—A systematic literature review and avenues for future research. Meditari Account. Res. 2020, 29, 1179–1208. [Google Scholar] [CrossRef]
  44. Posadas, S.C.; Ruiz-Blanco, S.; Fernandez-Feijoo, B.; Tarquinio, L. Institutional isomorphism under the test of Non-financial Reporting Directive. Evidence from Italy and Spain. Meditari Account. Res. 2023, 31, 26–48. [Google Scholar] [CrossRef]
  45. Cosentino, A.; Venuti, M. The Issue of Gender Inequalities in the Non-financial Statements. An Empirical Analysis. In When the Crisis Becomes an Opportunity; Paoloni, P., Lombardi, R., Eds.; SIDREA Series in Accounting and Business Administration; Springer: Cham, Switzerland, 2023. [Google Scholar] [CrossRef]
  46. Kostova, T.; Roth, K.; Dacin, M.T. Institutional Theory in the Study of Multinational Corporations: A Critique and New Directions. Acad. Manag. Rev. 2008, 33, 994–1006. [Google Scholar] [CrossRef]
  47. Silva, S. Corporate contributions to the Sustainable Development Goals: An empirical analysis informed by legitimacy theory. J. Clean. Prod. 2021, 292, 125962. [Google Scholar] [CrossRef]
  48. Carungu, J.; Di Pietra, R.; Molinari, M. Mandatory vs voluntary exercise on non-financial reporting: Does a normative/coercive isomorphism facilitate an increase in quality? Meditari Account. Res. 2020, 29, 449–476. [Google Scholar] [CrossRef]
  49. Tran, M.; Beddewela, E. Does context matter for sustainability disclosure? Institutional factors in Southeast Asia. Bus. Ethic Eur. Rev. 2020, 29, 282–302. [Google Scholar] [CrossRef]
  50. DiMaggio, P.J.; Powell, W.W. The New institutionalism in Organizational Analysis; University of Chicago Press: Chicago, IL, USA, 1991; pp. 1–38.22. [Google Scholar]
  51. Amoako, G.K.; Adam, A.M.; Tackie, G.; Arthur, C.L. Environmental Accountability Practices of Environmentally Sensitive Firms in Ghana: Does Institutional Isomorphism Matter? Sustainability 2021, 13, 9489. [Google Scholar] [CrossRef]
  52. Lee, D.; Fu, Y.; Zhou, D.; Nie, T.; Song, Z. Is There a Missing Link? Exploring the Effects of Institutional Pressures on Environmental Performance in the Chinese Construction Industry. Int. J. Environ. Res. Public Health 2022, 19, 11787. [Google Scholar] [CrossRef] [PubMed]
  53. Castro-Lopez, A.; Iglesias, V.; Santos-Vijande, M.L. Organizational capabilities and institutional pressures in the adoption of circular economy. J. Bus. Res. 2023, 161, 113823. [Google Scholar] [CrossRef]
  54. Christmann, P.; Taylor, G. Globalization and the Environment: Determinants of Firm Self-Regulation in China. J. Int. Bus. Stud. 2001, 32, 439–458. [Google Scholar] [CrossRef]
  55. Shnayder, L.; van Rijnsoever, F.J.; Hekkert, M.P. Motivations for Corporate Social Responsibility in the packaged food industry: An institutional and stakeholder management perspective. J. Clean. Prod. 2016, 122, 212–227. [Google Scholar] [CrossRef]
  56. Oliver, C. Strategic responses to institutional processes. Acad. Manag. Rev. 1991, 16, 145–179. [Google Scholar] [CrossRef]
  57. Boiral, O. Accounting for the Unaccountable: Biodiversity Reporting and Impression Management. J. Bus. Ethics 2014, 135, 751–768. [Google Scholar] [CrossRef]
  58. Hahn, R.; Lülfs, R. Legitimizing negative aspects in GRI-Oriented sustainability reporting: A Qualitative Analysis of Corporate Disclosure Strategies. J. Bus. Ethics 2014, 123, 401–420. [Google Scholar] [CrossRef]
  59. Radhouane, I.; Nekhili, M.; Nagati, H.; Paché, G. Is voluntary external assurance relevant for the valuation of environmental reporting by firms in environmentally sensitive industries? Sustain. Account. Manag. Policy J. 2020, 11, 65–98. [Google Scholar] [CrossRef]
  60. Pisano, S.; Lepore, L.; Celentano, A.; Alvino, F. The Influence of Institutional Factors on the Relationship between Board of Directors and Environmental Disclosure: A Meta-Analysis. Int. Rev. Environ. Resour. Econ. 2022, 16, 229–280. [Google Scholar] [CrossRef]
  61. Allen, C.; Metternicht, G.; Wiedmann, T. National pathways to the Sustainable Development Goals (SDGs): A comparative review of scenario modelling tools. Environ. Sci. Policy 2016, 66, 199–207. [Google Scholar] [CrossRef]
  62. Schroeder, P.; Anggraeni, K.; Weber, U. The Relevance of Circular Economy Practices to the Sustainable Development Goals. J. Ind. Ecol. 2019, 23, 77–95. [Google Scholar] [CrossRef]
  63. Dubey, R.; Gunasekaran, A.; Childe, S.J.; Papadopoulos, T.; Wamba, S.F.; Song, M. Towards a theory of sustainable consumption and production: Constructs and measurement. Resour. Conserv. Recycl. 2015, 106, 78–89. [Google Scholar] [CrossRef]
  64. Chen, S.; Bouvain, P. Is Corporate Responsibility Converging? A Comparison of Corporate Responsibility Reporting in the USA, UK, Australia, and Germany. J. Bus. Ethics 2008, 87, 299–317. [Google Scholar] [CrossRef]
  65. Du, S.; Bhattacharya, C.; Sen, S. Maximizing Business Returns to Corporate Social Responsibility (CSR): The Role of CSR Communication. Int. J. Manag. Rev. 2010, 12, 8–19. [Google Scholar] [CrossRef]
  66. Gallego-Álvarez, I.; Ortas, E. Corporate environmental sustainability reporting in the context of national cultures: A quantile regression approach. Int. Bus. Rev. 2017, 26, 337–353. [Google Scholar] [CrossRef]
  67. Kolk, A.; Fortanier, F. Internationalization and environmental disclosure: The role of home and host institutions. Multinatl. Bus. Rev. 2013, 21, 87–114. [Google Scholar] [CrossRef]
  68. Guerrero-Villegas, J.; Pérez-Calero, L.; Hurtado-González, J.M.; Giráldez-Puig, P. Board Attributes and Corporate Social Responsibility Disclosure: A Meta-Analysis. Sustainability 2018, 10, 4808. [Google Scholar] [CrossRef]
  69. Constantine Cannon. “Top Ten Environmental Fraud Settlements for 2018”. 2019. Available online: https://constantinecannon.com/whistleblower/whistleblower-insider-blog/top-ten-environmental-fraud-settlements-for-2018/ (accessed on 31 July 2023).
  70. Griffin, P. The Carbon Majors Database CDP Carbon Majors Report 2017; Climate Accountability Institute: Snowmass, CO, USA, 2017. [Google Scholar]
  71. Siano, A.; Vollero, A.; Conte, F.; Amabile, S. “More than words”: Expanding the taxonomy of greenwashing after the Volkswagen scandal. J. Bus. Res. 2017, 71, 27–37. [Google Scholar] [CrossRef]
  72. Liu, W.; Zhan, J.; Wang, C.; Li, S.; Zhang, F. Environmentally sensitive productivity growth of industrial sectors in the Pearl River Delta. Resour. Conserv. Recycl. 2018, 139, 50–63. [Google Scholar] [CrossRef]
  73. Yuan, H.; Su, M.; Zywiolek, J.; Rosak-Szyrocka, J.; Javed, A.; Yousaf, Z. Towards Innovation Performance of the Hospitality and Tourism Industry: Interplay among Business Ethics Diffusion, Service Innovation, and Knowledge-Sharing. Sustainability 2023, 15, 886. [Google Scholar] [CrossRef]
  74. Adel, C.; Hussain, M.M.; Mohamed, E.K.; Basuony, M.A. Is corporate governance relevant to the quality of corporate social responsibility disclosure in large European companies? Int. J. Account. Inf. Manag. 2019, 27, 301–332. [Google Scholar] [CrossRef]
  75. Zeng, S.X.; Xu, X.D.; Yin, H.T.; Tam, C.M. Factors that drive Chinese listed companies in voluntary disclosure of environmental information. J. Bus. Ethics 2012, 109, 309–321. [Google Scholar] [CrossRef]
  76. Fatima, N.; Yanting, Z.; Guohua, N. Interrelationship among environmental policy stringency, financial globalization in OECD countries, and CO2 emission with the role of technological innovation and financial development. Environ. Sci. Pollut. Res. 2022, 30, 34085–34100. [Google Scholar] [CrossRef] [PubMed]
  77. O’dwyer, B. Managerial perceptions of corporate social disclosure. Account. Audit. Account. J. 2002, 15, 406–436. [Google Scholar] [CrossRef]
  78. Emma, G.-M.; Jennifer, M.-F. Is SDG reporting substantial or symbolic? An examination of controversial and environmentally sensitive industries. J. Clean. Prod. 2021, 298, 126781. [Google Scholar] [CrossRef]
  79. Halkos, G.; Skouloudis, A. Exploring the current status and key determinants of corporate disclosure on climate change: Evidence from the Greek business sector. Environ. Sci. Policy 2016, 56, 22–31. [Google Scholar] [CrossRef]
  80. Ane, P. An Assessment of the Quality of Environmental Information Disclosure of Corporation in China. Syst. Eng. Procedia 2012, 5, 420–426. [Google Scholar] [CrossRef]
  81. Ferdous, M.I.; Adams, C.A.; Boyce, G. Institutional drivers of environmental manage-ment accounting adoption in public sector water organisations. Account. Audit. Acc. -Abil. J. 2019, 32, 984–1012. [Google Scholar] [CrossRef]
  82. Mateo-Márquez, A.J.; González-González, J.M.; Zamora-Ramírez, C. The influence of countries’ climate change-related institutional profile on voluntary environmental disclosures. Bus. Strat. Environ. 2020, 30, 1357–1373. [Google Scholar] [CrossRef]
  83. Skouloudis, A.; Jones, N.; Malesios, C.; Evangelinos, K. Trends and determinants of cor-porate non-financial disclosure in Greece. J. Clean. Prod. 2014, 68, 174–188. [Google Scholar] [CrossRef]
  84. Chan, M.C.; Watson, J.; Woodliff, D. Corporate Governance Quality and CSR Disclosures. J. Bus. Ethics 2013, 125, 59–73. [Google Scholar] [CrossRef]
  85. D’Amico, E.; Coluccia, D.; Fontana, S.; Solimene, S. Factors Influencing Corporate Environmental Disclosure. Bus. Strat. Environ. 2014, 25, 178–192. [Google Scholar] [CrossRef]
  86. Ashforth, B.E.; Gibbs, B.W. The Double-Edge of Organizational Legitimation. Organ. Sci. 1990, 1, 177–194. [Google Scholar] [CrossRef]
  87. Hopwood, A.G. Accounting and the environment. Account. Organ. Soc. 2009, 34, 433–439. [Google Scholar] [CrossRef]
  88. Huang, R.; Xie, X.; Zhou, H. ‘Isomorphic’ behavior of corporate greenwashing. Chin. J. Popul. Resour. Environ. 2022, 20, 29–39. [Google Scholar] [CrossRef]
  89. De Groen, W.P.; Alcidi, C.; Simonelli, F.; Campmas, A.; Di Salvo, M.; Musmeci, R.; Oliinyk, I.; Tadi, S. Study on the Non-Financial Reporting Directive; Publications Office of the European Union: Luxembourg, 2020. [Google Scholar]
  90. Doni, F.; Martini, S.B.; Corvino, A.; Mazzoni, M. Voluntary versus mandatory non-financial disclosure: EU Directive 95/2014 and sustainability reporting practices based on empirical evidence from Italy. Meditari Account. Res. 2019, 28, 781–802. [Google Scholar] [CrossRef]
  91. Lock, I.; Seele, P. The credibility of CSR (corporate social responsibility) reports in Europe. Evidence from a quantitative content analysis in 11 countries. J. Clean. Prod. 2016, 122, 186–200. [Google Scholar] [CrossRef]
  92. Galani, D.; Gravas, E.; Stavropoulos, A. Company Characteristics and Environmental Policy. Bus. Strat. Environ. 2011, 21, 236–247. [Google Scholar] [CrossRef]
  93. Dacin, M.T. Isomorphism in context: The power and prescription of institutional norms. Acad. Manag. J. 1997, 40, 46–81. [Google Scholar] [CrossRef]
Table 1. The sample.
Table 1. The sample.
Panel A. Sample I by Geographic ZonePanel B. Sample I by Industries
Country of
Headquarters
n. of Firmsn. of
Obs
% of
Obs
Sectorn. of Firmsn. of
Obs
% of
Obs
1Austria15393.09%1Accommodation and Food Services6191.5%
2Belgium17574.52%2Admin. and Supp., Waste Manag., and Remed. Services7221.76%
3Czech Republic110.07%3Agriculture, Forestry, Fishing, and Hunting120.15%
4Denmark10393.09%4Arts, Entertainment, and Recreation230.23%
5Finland291149.04%5Construction25695.57%
6France8231424.90%6Educational Services110.07%
7Germany9725220%7Health Care and Social Assistance230.23%
8Hungary120.15%8Information421229.87%
9Ireland9403.17%9Manufacturing15463450.30%
10Netherlands25988%10Mining, Quarrying, Oil and Gas Extraction5201.58%
11Poland110.07%11Other Services (except Public Administration)120.15%
12Portugal11191.50%12Professional, Scientific, and Technical Services21574.52%
13Spain42564.44%13Real Estate, Rental and Leasing31947.42%
14Sweden2622918.16%14Retail Trade23614.73%
Tot.3661261100.00%15Transportation and Warehousing20665.23%
16Utilities18574.42%
17Wholesale Trade7292.27%
Tot.3661261100.00%
Table 2. Description of variables and measurement.
Table 2. Description of variables and measurement.
VariableDescriptionMeasurementSource
CEDiscCE-related disclosureDisclosure index is given by the unweighted sum of the different environmental items disclosed by companies related to the circular economy; it is assigned 1 when the company presents information on that environmental aspect; otherwise, it is assigned 0 [64,65,66,67]. Eikon
Stri_Env_RegEnvironmental Policy Stringency IndexThis index represents a country-specific measure of the stringency of environmental policy. The index varies from 0 (not stringent) to 6 (highest level of stringency).OECD
GRIGlobal Reporting InitiativeThe GRI variable takes the value 1 if the company adopts GRIs and discloses information about them; otherwise, it takes the value 0.Eikon
ASSAssuranceThis variable takes values 1 if the company obtains the assurance; otherwise, it takes 0.Eikon
Commitment_
SDG
Commitment SDGThis variable measures what percentage of the SDGs has been achieved, measuring a company’s total progress toward achieving all 17 SDGs. A score of 100 represents that the company has achieved all SDGs [68].Eikon
EnvSensSectEnvironmentally Sensitive SectorsThis variable is dichotomous: it takes the value of 1 if the company belongs to the ecological sector with environmental sensitivity; otherwise, it takes 0 [3,69,70,71,72].Eikon
FirmSizeFirm SizeNatural logarithm of total assets.Eikon
LevLeverageLong-term debt divided by total assets.Eikon
ROAROAReturn On Assets.Eikon
yearYearThis variable represents the dummies to control for their fixed effects.Eikon
Table 3. Description of environmental disclosure items related to circular economy.
Table 3. Description of environmental disclosure items related to circular economy.
CE-Related Disclosure
Emissions CategoryInnovation CategoryResource Use Category
TitleTitleTitle
DescriptionDescriptionDescription
VOC or Particulate Matter Emissions ReductionEco-Design ProductsEnvironmental Materials Sourcing
The company discloses information regarding initiatives to reduce, replace, or eliminate volatile organic compounds (VOCs) or particulate matter less than ten microns in diameter (PM10).The company provides information on products specifically designed with the aim of being recycled, reused or disposed of without negative impacts on the environment
(discussion intended as an explanation of the possible environmental concerns that arise from the design of the product).
The company is required to state whether it uses environmental criteria to source or dispose of materials such as life cycle assessment.
NOx and SOx Emissions ReductionTake-back and Recycling InitiativesToxic Chemicals Reduction
Does the company report on initiatives to reduce, reuse, recycle, substitute, or phase out SOx (sulfur oxides) or NOx (nitrogen oxides) emissions?
- Any new project undertaken or initiated to reduce NOx (nitrogen oxide) and SOx (sulfur oxide) emissions;
- General legal compliance is not qualified data;
- In line with the legal compliance or government-imposed processes to reduce SOx (sulfur oxides) or NOx (nitrogen oxides), which are well described and qualified;
- Follow greenhouse gas (GHG) protocol for all our emission classifications by type.
Does the company report about take-back procedures and recycling programs to reduce the potential risks of products entering the environment?
- Take back or recycle the company’s own product at the end of use;
- Waste management company collecting various products and recycling is not in the scope;
- A product recall is not considered qualified data.
The company is required to disclose information on reducing, reusing, replacing, or phasing out toxic substances or chemicals, such as PBT (persistent and bioaccumulative toxicants) and PVC (polyvinyl chloride).
VOC Emissions ReductionProduct Impact Minimization
Does the company report on initiatives to reduce, substitute, or phase out volatile organic compounds (VOC)?
- Processes, mechanisms, or programs in place as to what the company is doing to reduce or phase out volatile organic compounds in its operations;
- Any new project undertaken to reduce VOC emissions;
- General legal compliance is not qualified data;
- In line with the legal compliance or government-imposed processes to reduce VOC, which are well described and qualified.
Does the company report on take-back procedures and recycling programs to reduce the potential risks of products entering the environment or does the company report on product features or services that will promote responsible and environmentally preferable use?
Particulate Matter Emissions Reduction
Does the company report on initiatives to reduce, substitute, or phase out particulate matter less than ten microns in diameter (PM10)?
- Initiatives that the company has put in place to reduce, substitute, or phase out particulate matter less than ten microns in diameter (PM10);
- Any new project undertaken, focusing on the reduction of particulate matter emissions;
- Dust, fugitive dust, and soot are also considered particulate matter.
Waste Reduction Initiatives
Does the company report on initiatives to recycle, reduce, reuse, substitute, treat, or phase out total waste?
- Initiatives to reduce any type of waste generated by reporting organization;
- Partnership with waste management companies to treat waste generated;
- Does not include the data on waste management companies that collect and recycle the waste for their customers.
E-waste Reduction
Does the company report on initiatives to recycle, reduce, reuse, substitute, treat, or phase out e-waste?
- Any initiatives that the company has put in place to reduce e-waste;
- E-waste is used as a generic term embracing all types of waste containing electrically powered components;
- E-waste may contain hazardous materials that require special handling and recycling methods;
- Includes all products covered under WEEE (waste electrical and electronic equipment) regulations, like fluorescent tubes, sodium lamps, computers, mobiles, telephones, fax machines, copiers, printers, washing machines, dryers, refrigerators, air-conditioners, televisions, VCR/DVD/CD players, Wi-Fi sets, radios, drills, electric saws, sewing machines, batteries, toner cartridges.
Table 4. Descriptive statistics.
Table 4. Descriptive statistics.
Variablesn. obsMeanSdMinMax
CEDisc1.2613.9722862.238651010
Stri_Env_Reg1.2613.6363590.59585192.444.89
GRI1.2610.99137250.092518801
ASS1.2610.90405620.294629101
Commitment_
SDG
1.26182.565492.25016979.0186.51
EnvSensSect1.2610.6481909 0.477718701
FirmSize1.26122.881080.1238350318.8626.93
Lev1.2610.2113934 0.128350300.86
ROA1.2610.04378750.061055−0.330.41
Year1.2612017.9991.72156620152020
Table 5. Correlation Matrix.
Table 5. Correlation Matrix.
CEDiscCommitment~GEnvSensSec Stri_Env_RegGRIAssFirmSizeLevROAYear
CEDisc1.0000
GRI 0.0483 *1.0000
Ass0.1263 ***−0.03071.0000
Commitment_SDG−0.0531 *−0.082 ***−0.1448 ***1.0000
Stri_Env_Reg0.1421 ***−0.03300.0735 ***0.2210 ***1.0000
EnvSensSect0.3244 ***−0.0322−0.0898 ***0.1149 ***−0.1189 ***1.0000
FirmSize0.3840 ***−0.0049 * 0.2586 ***−0.2957 *** −0.0267 0.0535 ** 1.0000
Lev−0.1729 ***0.00813 ***−0.0034−0.1768 *** −0.0214−0.3503 *** 0.0899 ***1.0000
ROA0.0164−0.2507 **−0.0770 **0.1933 **−0.0631*0.0806 *** −0.1307 *** −0.2579 *** 1.0000
Year−0.0468 * −0.0053 −0.0048 −0.0340 0.1000 *** −0.0172 −0.1758 ***0.1777 ***−0.1270 *** 1.0000
Note: ***, **, * represent significance at 1%, 5%, 10% levels, respectively.
Table 6. Regression results.
Table 6. Regression results.
VariablesModel (1)
Ordinary Least Squares Regression (OLS)
Stri_Env_Reg0.7292799***
(0.0954462)
GRI2.158516***
(0.5965779)
Ass0.3504524
Commitment_SDG(0.190078)
−0.0366598
(0.0264842)
EnvSensSect1.422219***
(0.1244045)
FirmSize0.6007197***
(0.6007197)
Lev0428213***
(0.475077)
ROA2.38054***
(2.38054)
Year9539686
0.0332996
(0.0327912)
Constant−79.71523
(66.5745)
Note: *** represents significance at 1% levels.
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Pozzoli, M.; Nastari, R.; Pisano, S.; Venuti, M. How Circular Economy Disclosure Responds to Institutional Determinants Empirical Evidences in Non-Financial European Firms. Sustainability 2023, 15, 16069. https://doi.org/10.3390/su152216069

AMA Style

Pozzoli M, Nastari R, Pisano S, Venuti M. How Circular Economy Disclosure Responds to Institutional Determinants Empirical Evidences in Non-Financial European Firms. Sustainability. 2023; 15(22):16069. https://doi.org/10.3390/su152216069

Chicago/Turabian Style

Pozzoli, Matteo, Raffaela Nastari, Sabrina Pisano, and Marco Venuti. 2023. "How Circular Economy Disclosure Responds to Institutional Determinants Empirical Evidences in Non-Financial European Firms" Sustainability 15, no. 22: 16069. https://doi.org/10.3390/su152216069

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