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The impact of environmental practices on financial performance: Do reputation, institutional environment, and industry type matter?

Escobar Pérez, Bernabé; Fresneda Fuentes, Maria Silvia; Miras Rodríguez, María del Mar

Abstract

The impact that environmental practices have on companies’ performance has often been analyzed in the literature, and the findings are inconclusive. Several researchers argue that further evidence is needed to better understand this relationship, and in particular, the effect that some variables could have on it. Consequently, the main aim of this research was to analyze whether company reputation, the institutional environment, and industry affect the impact of environmentally friendly practices on financial performance. The research found its theoretical foundation in ecoefficiency, trade-off, institutional, and agency theories. The sample comprised 198 high-performing manufacturing companies across 9 countries. Data were collected using a specific questionnaire designed to capture managers’ perceptions of the relevant variables and analyzed through partial least squares structural equation modeling. The findings indicate that environmentally friendly practices positively influence companies’ financial performance. However, contrary to previous evidence, company reputation does not appear to mediate this relationship. Instead, the institutional environment as well as the subsector in which a company operates play a moderating role. These findings are particularly valuable for managers since they reinforce the rationale for adopting proactive environmental strategies. This research contributes to previous literature, providing new insights about the impact of environmentally friendly behaviors on financial performance within the context of manufacturing companies, as well as the roles that reputation and institutional environments play in this relationship.

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Green Finance, 7(3): 429–449. DOI: 10.3934/GF.2025016 Received: 31 January 2025 Revised: 16 June 2025 Accepted: 27 June 2025 Published: 09 July 2025 https://www.aimspress.com/journal/GF Research article The impact of environmental practices on financial performance: Do reputation, institutional environment, and industry type matter? Bernabé Escobar-Pérez, Silvia Fresneda-Fuentes and María del Mar Miras-Rodríguez* Accounting and Finance Department, Faculty of Business and Economics, University of Seville, Seville, Spain Correspondence: Email: [email protected]; Tel: +34954556067. Abstract: The impact that environmental practices have on companies’ performance has often been analyzed in the literature, and the findings are inconclusive. Several researchers argue that further evidence is needed to better understand this relationship, and in particular, the effect that some variables could have on it. Consequently, the main aim of this research was to analyze whether company reputation, the institutional environment, and industry affect the impact of environmentally friendly practices on financial performance. The research found its theoretical foundation in ecoefficiency, trade-off, institutional, and agency theories. The sample comprised 198 high-performing manufacturing companies across 9 countries. Data were collected using a specific questionnaire designed to capture managers’ perceptions of the relevant variables and analyzed through partial least squares structural equation modeling. The findings indicate that environmentally friendly practices positively influence companies’ financial performance. However, contrary to previous evidence, company reputation does not appear to mediate this relationship. Instead, the institutional environment as well as the subsector in which a company operates play a moderating role. These findings are particularly valuable for managers since they reinforce the rationale for adopting proactive environmental strategies. This research contributes to previous literature, providing new insights about the impact of environmentally friendly behaviors on financial performance within the context of manufacturing companies, as well as the roles that reputation and institutional environments play in this relationship. Keywords: environmental practices; financial performance; reputation; institutional environment 430 Green Finance Volume 7, Issue 3, 429–449. JEL Codes: M14 1. Introduction Organizations are increasingly compelled to address sustainability challenges because investors are increasingly concerned about sustainability and less tolerant of companies that harm the natural ecosystem (Bolton and Kacperczyk, 2021; Fleitas-Castillo et al., 2025). Additionally, environmental regulations are becoming increasingly stringent globally (Pérez et al., 2011). This pressure is higher in sectors such as manufacturing (Baah et al., 2021b), whose production activities are often associated with significant environmental pollution (Bello-Pintado et al., 2023). Adopting environmentally friendly practices (EP) often requires companies to face high costs associated with investments in new machinery or materials (Hart and Ahuja, 1996). This high initial cost could be compensated, at least partially, by cost savings, since technological advancements facilitate lower energy consumption and less environmental impact (Lafont et al., 2023). Based on the literature, engaging in specific EP can enhance organizational outcomes by meeting stakeholders’ expectations (Ahmadi-Gh and Bello-Pintado, 2022), since consumers increasingly consider the environmental impact of companies (Feng and Wang, 2016; Khan et al., 2023) in their purchase decisions. Consequently, carrying out EP can be long-term profitable (Porter and Van der Linde, 1995). Although most findings from the prior literature on manufacturing support the positive effect (Baah et al., 2021b; Habib, 2023; Jum´a et al., 2021; Liu et al., 2022; Tzouvanas et al., 2020), some non-significant effects are found (Aigbedo, 2021; Alexopoulos et al., 2018). Consequently, the importance of examining the moderating and/or mediating roles of certain variables in this relationship has been suggested, as these could help explain the observed disparities (Sarfraz et al., 2023; Turkcan, 2025; Zhang et al., 2019). Even though several scholars have argued that reputation could be key to better understand the relationship between EP and financial performance (FP) (Hammami and Othmani, 2024), the results do not always support the existence of a mediator role (Afum et al., 2020; Baah et al, 2021a; Farza et al., 2021; Jing et al., 2023), but the majority of the samples are from one developing country. Furthermore, the link between sustainability issues and FP varies depending on the cultural characteristics of the countries where companies operate (Miras-Rodríguez et al., 2018; Saha et al., 2024; Scholtens and Kang, 2013) and the key role of industry (Aigbedo, 2021). Analyzing the moderator role of the institutional environment and subsector would help to better understand the EP– FP relationship. The objectives of this research are twofold: (1) to analyze the impact of EP on companies’ FP, and (2) to investigate the mediating role of reputation and the moderating role of the institutional environment and industry in this relationship. To conduct our research, an international database of companies participating in the HighPerformance Manufacturing (HPM) project will be examined, which includes data from three industries: machinery, electronics, and automotive components. This database was created based on responses from managers of manufacturing companies to a regular survey that addressed sustainability topics in its most recent round (Ahmadi-Gh and Bello-Pintado, 2022; Bello-Pintado et al., 2023). The sample contains data from nine countries. To test our hypotheses, structural equation modeling (SEM) 431 Green Finance Volume 7, Issue 3, 429–449. will be employed, specifically using partial least squares (PLS) methodology following most of the research in the field (Afum et al., 2020; Baah et al., 2021b). The findings indicate that implementing environmentally sustainable practices has a beneficial effect on FP. Notably, while the hypothesized mediating role of reputation was not substantiated, the data do support the moderating effects of the national context, influenced by institutional environments and industry subsectors. Our findings contribute to the debate on the EP–FP relationship by providing evidence of a positive impact when considering a multi-country sample. In addition, the supported moderator role of the institutional environment and the subsector should lead researchers to control their analyses by considering both variables. The remainder of the paper is organized as follows: first, the theoretical framework and hypotheses will be developed. The subsequent section will focus on the sample and methodology. Following that, the results will be shown. Finally, the research will be discussed, as well as the conclusions and limitations. 2. Theoretical background The existing academic literature employs a variety of theoretical frameworks to elucidate the adoption of sustainability practices (Dos Reis Cardillo and Cruz Basso, 2025; Habib, 2023). In this context, stakeholder theory, legitimacy theory, and institutional theory offer significant insights into the motivations behind organizational engagement in sustainability. Stakeholder theory, as posited by Freeman (1984), asserts that by prioritizing the interests of a broad spectrum of stakeholders beyond merely shareholders, organizations can foster sustainable value creation, thereby enhancing FP. In the same line, legitimacy theory, as articulated by Suchman (1995), posits that organizations actively seek to align their operations and strategies with society’s prevailing norms and expectations. This alignment is crucial for organizations to acquire, sustain, or restore legitimacy amongst their stakeholders. In essence, organizations must engage in practices that are perceived as socially acceptable to secure their standing and credibility within the community. Within the realm of sustainability, firms often undertake initiatives to secure financial returns and bolster their legitimacy. To do so can also be considered an “informal” prerequisite for operating in specific markets (Peloza, 2006). Moreover, as discussed by DiMaggio and Powell (1983), institutional theory posits that isomorphic processes may serve as mechanisms for enhancing organizational legitimacy. Concerning environmentally sustainable initiatives, the trade-off theory (Friedman, 1970) provides a framework that underscores the potential negative implications of such initiatives on a company’s FP. Implementing environmentally friendly practices often necessitates considerable investments (Hart and Ahuja, 1996), which are readily observable. In contrast, the benefits derived from these practices may be more challenging to quantify, as not all initiatives yield direct and immediate outcomes (Iatridis, 2013; Meng et al., 2016). Conversely, the eco-efficacy theory (Porter and Van der Linde, 1995) and the resource-based theory (Barney, 1996) contend that environmentally sustainable practices are strategic resources that confer competitive advantages upon firms. Following the initial investment, organizations can realize “certain” cost savings through resource optimization (Al-Tuwaijri et al., 2004; Ali et al., 2025), reductions in pollutant emissions (Gallego, 2012; Smale et al., 2006), or the mitigation of penalties associated with regulatory non-compliance (Carballo and Castromán, 2015). Additionally, indirect benefits may arise, such as the attraction of consumers who 432 Green Finance Volume 7, Issue 3, 429–449. favor environmentally responsible companies (Luo and Bhattacharya, 2006) and the reduction of capital costs (Godfrey et al., 2009). In light of the agency theory, as described by Jensen and Meckling (1976), it is suggested that managers might pursue sustainability initiatives primarily for their gain (incentives) or to enhance their reputation. Therefore, engaging in certain practices can either enhance or undermine an organization’s FP, depending on whether incentive schemes are linked to FP, sustainability, or both (Cohen et al., 2023; Jang et al., 2022; Keddie and Magnan, 2023; Velte, 2016). In addition, managers usually have a short-term vision, while shareholders also consider the long-term. Based on this premise, it should also be considered that investments and returns of environmentally friendly initiatives could be lagged. 3. Literature review and hypothesis development The relationship between EP and FP has been the subject of several meta-analyses (Albertini, 2013; Dixon-Fowler et al., 2013; Endrikat et al., 2014; Hang et al., 2019). While there is a consensus that greater resource availability increases the likelihood of engaging in environmentally friendly practices (Čater et al., 2023; Laguir et al., 2018; Testa and D’Amato, 2017), the results regarding the impact of such practices on a company’s performance are heterogeneous (Aigbedo, 2021; Alexopoulos et al., 2018; Ali et al., 2025; Baah et al., 2021b; Farza et al., 2021; Habib, 2023; Jum´a et al., 2021; Liu et al., 2022). In other words, is it truly beneficial to adopt green initiatives? Having an answer to this question is critically important for companies, particularly those that face greater pressure to adopt environmentally friendly practices due to their operations’ negative environmental impacts. Although companies would obtain a positive performance from implementing sustainable initiatives from a legitimacy point of view and from satisfying all stakeholders’ expectations, practices focused on the environment have a distinctive characteristic: the high initial investment that most of them imply. Based on the trade-off arguments, the initial investments are “certain”, while some associated costs are more challenging to identify because some are indirect and/or there is a lag in obtaining the benefits. In the same line, Goss and Robert (2011) argue that large expenditures in Environmental, Social and Governance (ESG) tie up financial resources and reduce business value. On the other hand, based on the eco-efficiency arguments and resource-based view, the balance between the cost/investment and the associated returns is positive. Together with the “certain” costsaving, the indirect benefits supported by the literature should be considered. The certainty of the “investments/expenses” and the uncertainty of the indirect “benefits” associated with them could lead to agency conflicts (Wu and Xie, 2024) among managers and shareholders. The level of managerial engagement in environmentally sustainable initiatives may vary based on the specific inputs utilized in determining incentive structures. If they are only linked to FP, the high cost of implementing EP or those with uncertain returns would not be carried out (Jang et al., 2022; Mansour et al., 2024). When the incentives depend only on sustainable performance, there is an increase in engagement with sustainability, although FP does not improve (Cohen et al., 2023). Nonetheless, if the incentive structure encompasses sustainable and FP metrics, managers may be more committed to sustainability while focusing on financial viability (Flammer et al., 2019). Considering that most of the empirical evidence regarding manufacturing industries indicates a positive impact of EP on companies’ performance (Ali et al., 2025; Baah et al., 2021b; Habib, 2023; 433 Green Finance Volume 7, Issue 3, 429–449. Jum´a et al., 2021; Liu et al., 2022; Pons et al., 2013; Sen, 2015; Tzouvanas et al., 2020), our first hypothesis is stated: H1: EP has a positive impact on companies’ FP. Numerous researchers have highlighted the crucial mediating role of reputation, as an intangible asset, in the relationship between EP and FP (Brammer and Pavelin, 2006; Jing et al., 2023; Larrán et al., 2015; Neville et al., 2005; Surroca et al., 2010). According to Newbert (2007), establishing competitive advantages through intangible resources like reputation is vital for a firm’s success (resource-based theory) due to the difficulty of imitation. Although empirical research on the direct effects of sustainability practices on corporate reputation is limited (Baraibar-Diez and Luna-Sotorrio, 2018), a company’s environmental friendliness can significantly influence its reputation—either positively or negatively—depending on whether the actions are perceived as symbolic or substantive (Truong et al., 2021). If the practices are seen as symbolic gestures, reputation tends to decline, while substantive actions typically enhance it. All stakeholders take into account the company’s reputation as a significant factor influencing their decision-making processes. However, it is important to note that price remains a critical component in these evaluations (Bendixen et al., 2004). Previous research on the manufacturing industry is mixed. While Farza et al. (2021) supported the mediation effect, Afum et al. (2020) and Baah et al. (2021a) found no significant mediation role. Hence, we established our second hypothesis: H2: The relationship between EP and FP will be mediated by a company’s environmental reputation. Previous literature has highlighted the significant role that the institutional environment plays in shaping how EP impacts organizations’ FP (Horváthová, 2010; Hou et al., 2016; Miras-Rodríguez et al., 2018; Saha et al., 2024; Waldman et al., 2006). This notion is theoretically grounded in institutional theory (Baughn et al., 2007; Matten and Moon, 2008). Given that legal requirements vary across countries, stakeholder expectations are likely to be more aligned in nations that share greater similarities (Jamali and Mirshak, 2006). Bai and Chang (2015) noted that sustainability initiatives tend to be valued more in developed countries, although the evidence in emerging economies remains ambiguous (Tsai et al., 2020). In the context of manufacturing companies, evidence supports the longterm implementation of EP in developed countries (Chen et al., 2015). Nevertheless, Naeem et al. (2022) discussed that companies within environmentally sensitive industries, such as manufacturing, from developed countries report a positive effect, while the undertakings from emerging countries present a lack of significant effect. In this line, Baah et al. (2021b) contended that some companies in developing nations deny integrating EP, while others try to incorporate them, considering their limited resource capacity. Maldonado-Guzman (2024) argued that manufacturing firms in Mexico have ignored the environmental consequences of their operations. Nevertheless, other studies suggested that there has been a growing concern over environmental issues in recent years within developing and emerging countries, largely driven by the necessity to export (Chen et al., 2015). Furthermore, Zhu and Sarkis (2004) emphasized the crucial role of FP in motivating engagement in EP. Taking into account the approach of Barnett and Salomon (2012), variations in FP can be attributed to the differing stages of commitment to environmental issues among various enterprises or countries. For Western companies that have a long-standing tradition of EP, strong ethical practices may not yield significant rewards, while bad practices are likely to face negative consequences (Margolis and Walsh, 2003). In contrast, institutional environments that have recently adopted EP 434 Green Finance Volume 7, Issue 3, 429–449. often experience significant financial benefits and are not penalized for lacking commitment (Dallocchio et al., 2025; Ha et al., 2024). The EP implemented by companies with a longstanding commitment to environmental responsibility may receive comparatively less recognition than organizations from countries with a more recent commitment. This leads to our third hypothesis: H3: The relationship between EP and FP will be moderated by the institutional environment. Numerous researchers have highlighted the industry’s significant role in this relationship (Aigbedo, 2021; Margolis and Walsh, 2003; Waddock and Graves, 1997). They have claimed that the lack of consensus previously argued can be attributed to the compensation or overlapping of results derived from cross-sectional samples because stakeholder pressures differ across industries (Patten, 2002). Manufacturing companies are highly aware of environmental issues. Nevertheless, since there are three sectors involved in the sample, it is important to test for differences among them. Consequently, the fourth hypothesis states that: H4: The relationship between EP and FP will be moderated by the subsector. Figure 1 shows a representation of all the hypotheses previously stated. Figure 1. Map of the hypotheses. Source: Authors’ own work 4. Methodology The sample is composed of companies engaged in the High-Performance Manufacturing (HPM) project, which involves the machinery, electronics, and automotive components industries. The HPM project database represents an international compilation of data derived from responses provided by managers through a systematic survey administered to a representative sample of manufacturing plants. The questionnaire, designed for the collection of sustainability-related metrics, is grounded in measures that have been rigorously validated in the academic literature (Ahmadi-Gh and Bello-Pintado, 2022; Bello-Pintado et al., 2023). Each sustainability item is assessed using a Likert scale, with values ranging from 1 to 5. 435 Green Finance Volume 7, Issue 3, 429–449. The sample encompasses companies from nine countries: Brazil, China, Germany, Israel, Italy, Japan, South Korea, Spain, and Sweden. A total of 198 observations have been aggregated. The distribution of these observations, categorized by country and industry, is presented in Table 1. Table 1. Sample distribution. The present analysis incorporates several key variables: environmental practices (EP), financial performance (FP), reputation, institutional environment, and industry. The EP variable is derived from a comprehensive evaluation of 41 distinct indicators outlined in the HPM project (Miras-Rodriguez et al., 2018). The FP and reputation variables are each represented by a single item measured on a Likert scale ranging from 1 to 5. Specifically, the FP variable encapsulates managers’ perceptions of the FP attained by the organization as a result of implementing environmental initiatives. In contrast, the reputation variable reflects managers’ perceptions of the enhancement in reputation that arises from engaging in environmentally sustainable practices. The majority of the existing literature on this subject tends to concentrate either on a singular group of countries or comparative analyses across different nations (Chapple and Moon, 2005; Welford, 2005). Among the various methodologies available for assessing the institutional environment, the Governance Environment Index, as proposed by Li and Filer (2007), has been selected due to its robust complexity and ability to mitigate some of the limitations associated with alternative cultural classifications (Miras and Escobar, 2016). Recognizing the countries involved in the HPM project and utilizing the classification framework established by Li and Filer (2007), the total sample can thus be categorized into two distinct sub-samples: rule-based countries (comprising Germany, Italy, Japan, Korea, Spain, and Sweden) and relation-based countries (including Brazil, China, and Israel). Finally, the analysis identifies three sub-industries within the sample—machinery, electronics, and automotive components—pertinent to the industry variable. 4.1. Method Structural equation modeling (SEM) represents a sophisticated multivariate technique that integrates components of multiple regression and factor analysis to concurrently estimate a series of interrelated dependence relationships. This methodological approach has gained considerable traction in recent years across various disciplines, particularly within the social and management sciences. Countr y Machiner y Electronics Automotive components Total Brazil 3 7 9 19 China 6 7 9 22 German y 6 12 8 26 Israel 14 3 0 17 Ital y 7 17 5 29 Japan 8 5 13 26 South Korea 9 18 1 28 Spain 5 6 11 22 Sweden 4 4 1 9 TOTAL 62 79 57 198 436 Green Finance Volume 7, Issue 3, 429–449. SEM analysis can be executed through two principal statistical techniques (Roldán and SánchezFranco, 2012): covariance-based approaches, exemplified by LISREL and AMOS, and variance-based methods, such as partial least squares (PLS). Given the nature of our model, which incorporates formative indicators, PLS is deemed more appropriate for analysis (Henseler et al., 2009). In the context of SEM, it is imperative to assess both the measurement model, which delineates the composition of each latent variable, and the structural model, which elucidates the causal relationships among the latent variables. This dual evaluation is crucial for ensuring the robustness and validity of the resulting analysis. This study uses SmartPLS 4 software (Ringle et al., 2022). 4.1.1. Measurement model Consistent with the existing literature, the latent variable (EP) is constructed using formative indicators, as each indicator or item contributes to its formation (Chin, 1998). As was argued by Hair et al. (2021, 2022) and Cheah et al. (2018), it is considered that the variables are theoretically designed to be formative, assessing collinearity and the significance and relevance of the formative indicators. To evaluate the validity of the measurement model, it is essential to assess the weights of the indicators, given that parameters are not applicable for reflective indicators. These weights provide insights into which indicators significantly influence our latent variable. 4.1.2. Structural model Once the validity of the outer model was established, it was possible to test the hypotheses. This involves quantifying the proposed causal relationships using the PLS algorithm, which calculates each dependent construct’s path coefficients and R2 values. To assess the significance of the parameters, a bootstrapping analysis was conducted with 10,000 resamples, as recommended in the literature (Streukens and Leroi-Werelds, 2016). Furthermore, additional tests are necessary to examine the mediating and moderating roles of the variables. To test the mediating effect of reputation, a comparison must be made between the model without the mediator variable and the model that includes it. This mediation can be classified as either partial or total, depending on the significance of the parameters. If the path coefficient of the primary relationship is significant but loses significance once the mediator variable is introduced, the mediation is considered total. Conversely, if the primary relationship remains significant after adding the mediator variable, the mediation is deemed partial. When a mediator variable is included in the analysis, the total path coefficient effects are presented, and their significance is calculated using bias-corrected bootstrapping with 10,000 resamples (Chin, 2010). A multi-group analysis is imperative to evaluate the moderating effect of the cultural environment (Henseler and Fassott, 2010). This analytical approach entails partitioning the sample into distinct groups based on the moderator variable and applying the model to each subgroup. In the context of moderation analysis, it is essential to give careful consideration to measurement invariance (Sarstedt et al., 2011). In particular, the advanced measurement invariance through the measurement invariance of composite models (MICOM) based on the permutation technique developed by Henseler et al. (2016) was used. Among the different techniques, the permutation multigroup analysis was used (Chin, 2003; Chin and Dibbern, 2010) when the number of groups was two. For robustness, bootstrap multigroup analysis (Henseler, 2012) was also performed. 437 Green Finance Volume 7, Issue 3, 429–449. 5. Results First, the measurement model should be validated. Then, collinearity, significance, and relevance of EP, as a formative construct, were assessed. Thus, a collinearity analysis was carried out, and the variance inflation factor (VIF) was examined considering the threshold of 3.3 (Diamantopoulos and Siguaw, 2006). Consequently, 10 items were deleted1. In addition, the significance and relevance of the items were assessed by considering those whose weights would be higher than 0.5 or, on the contrary, those whose loadings are statistically significant (Hair et al., 2021). Then, only 29 items remain (Table 2). Table 2. Weights of final items for EP. Ori g inal sample (O) Sample mean (M) Standard deviation (STDEV) T statistics ( | O/STDEV | ) EP01 0.246 0.217 0.135 1.822 EP02 0.063 0.042 0.138 0.458 EP04 −0.351 −0.305 0.137 2.568 EP05 −0.13 −0.116 0.149 0.873 EP06 0.048 0.036 0.164 0.295 EP07 0.336 0.286 0.156 2.156 EP08 −0.18 −0.143 0.185 0.976 EP09 −0.162 −0.125 0.147 1.102 EP12 0.342 0.284 0.152 2.255 EP13 −0.035 −0.049 0.15 0.236 EP14 0.091 0.079 0.169 0.536 EP15 −0.064 −0.045 0.196 0.326 EP17 0.047 0.026 0.142 0.333 EP18 0.092 0.072 0.168 0.547 EP20 −0.226 −0.181 0.141 1.607 EP21 −0.25 −0.224 0.15 1.671 EP22 0.039 0.036 0.158 0.247 EP24 0.4 0.341 0.156 2.563 EP29 0.412 0.349 0.186 2.215 EP30 0.112 0.08 0.141 0.793 EP31 −0.15 −0.118 0.151 0.999 EP32 0.152 0.127 0.174 0.876 EP33 −0.009 0.026 0.17 0.055 EP34 −0.17 −0.141 0.146 1.166 EP35 −0.004 −0.016 0.2 0.018 EP36 0.052 0.054 0.161 0.325 EP37 −0.135 −0.108 0.138 0.982 EP38 0.149 0.141 0.159 0.933 EP39 0.311 0.27 0.146 2.124 Table 2 outlines the indicators that exert a strong positive influence on EP: (1) energy efficiency or renewable energy, (2) seeking or maintaining an ISO14001 certification, (3) encouraging suppliers to improve the environmental performance of their processes, and (4) providing design specifications to suppliers in line with environmental requirements. 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