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Article

Forging a Sustainable Future in G20 Economies: The Transformative Role of Technological Innovation, Green Finance and Higher Education Amid Globalization and Entrepreneurial Growth

1
College of Educational Sciences, Yangzhou University, Yangzhou 225002, China
2
Youth League Committee, Changzhou University, Changzhou 213159, China
3
National Institute of Environmental Management (NIOEM), Lahore 54792, Pakistan
*
Author to whom correspondence should be addressed.
Sustainability 2025, 17(8), 3321; https://doi.org/10.3390/su17083321
Submission received: 10 February 2025 / Revised: 2 April 2025 / Accepted: 4 April 2025 / Published: 8 April 2025

Abstract

:
Environmental degradation poses a significant global challenge which necessitates innovative strategies to achieve sustainability. This study investigates the impact of technological innovation (TCN), higher education (EDU), green finance (GRF), globalization (GLI), and entrepreneurship (ENT) on environmental quality (EQ) in G20 countries. The study uses panel data from 2000 to 2020 to investigate relationships between study variables. Among the various diagnostic tests conducted, the Variance Inflation Factor (VIF) confirms that multicollinearity is not present. Furthermore, the cross-sectional dependence (CSD) test identifies cross-sectional interdependence among the study variables. Moreover, the slope homogeneity (SL) test indicates heterogeneity in the data. For the stationarity check, the Cross-Sectional Augmented Im–Pesaran–Shin (CIPS) test indicates mixed results. Finally, the study uses the Cross-Sectionally Augmented Autoregressive Distributed Lag (CS-ARDL) and the Generalized Method of Moments (GMM) for the long- and short-run analysis of variables. The outcomes of CS-ARDL indicate that GLI has a significant negative impact on EQ, hence causing deterioration in G20 economies. On the other hand, TCN, EDU, GRF, and ENT show positive and significant impacts on EQ, therefore enhancing environmental outcomes. Additionally, the Dumitrescu–Hurlin causality test reveals bidirectional causality, which highlights the interconnected relationship between TCN and ENT with EQ. However, GRF, EDU, and GLI demonstrate unidirectional causality with EQ. The takeaway of the study focuses on the importance of policies in promoting green innovation, resource efficiency, and sustainable practices to advance environmental quality within G20 economies.

1. Introduction

Environmental quality (EQ) has taken worldwide value, which is a sign to put a balance between economic progress and environmental safety. Hence, EQ is viewed as essential to addressing pressing concerns such as climate change, health of biodiversity, and resource overexploitation. Therefore, scientists highlight the importance of adopting an interdisciplinary approach, which incorporates EQ, economic development, and TCN to develop a more sustainable solution. In this regard, several studies feature the critical role of green technologies and innovative practices in reducing environmental degradation while encouraging EQ [1], whereas policymakers progressively acknowledge the implication of EQ in shaping long-term development strategies [2]. As a result, global efforts like the SDGs and the Paris Agreement focus on creating policies that balance economic growth with EQ [3]. However, the integration of GRF and sustainable industrial practices into policy agendas underlines the collective commitment in achieving ecological equilibrium. On the other hand, collaboration between scientific research and policymaking remains very important in addressing the multifaceted challenges posed by GLI, urbanization, and environmental crises [4]. Therefore, neglecting EQ exacerbates climate change, resource depletion, and ecological degradation, with vulnerable populations disproportionately affected. This indicates that without aligning TCN, EDU, and GRF with sustainability goals, opportunities to mitigate environmental crises and foster transformative solutions are lost. Moreover, the absence of sustainability-focused education limits the development of leaders equipped to address these challenges, while insufficient GRF stifles funding for critical initiatives [5]. Furthermore, GLI and entrepreneurial activities driven by short-term economic gains intensify ELF by underscoring the urgent need for integrated strategies to harmonize economic progress with ecological preservation. More importantly, the study uses TCN instead of green innovation for several reasons. For example, technological innovation influences environmental quality by shaping energy use and industrial processes [6]. While green innovation targets eco-friendly technologies, this study uses total patent counts as a broader measure of technological progress. This approach is justified because (1) technological innovation enhances energy efficiency, reduces waste, and optimizes resource use, indirectly improving environmental quality [7], and (2) green patents represent only a fraction of overall innovation. Additionally, advancements in digitalization and automation contribute to environmental outcomes, even if not classified as “green.” Thus, this study examines the broader impact of technological innovation on environmental quality.
Furthermore, considering the importance, EQ within the G20 is crucial due to the group’s significant influence on global economic, environmental, and social dynamics. The G20, made up of the world’s biggest economies, represents about 85% of the global economy, 75% of trade worldwide, and around two-thirds of the world’s population [8]. These nations are also responsible for over 80% of global CO2, highlighting their important role in addressing environmental challenges [9]. The G20’s collective economic power and resource consumption place it at the forefront of mitigating environmental degradation. Therefore, by prioritizing sustainability, the G20 can drive global progress toward reducing ELF, through advancing renewable energy transitions and implementing innovative technologies. As a result, it will have far-reaching impacts on regional and global policies, influencing trade, investment, and development strategies across both developed and developing nations. Additionally, the role of G20 as a platform for multilateral collaboration enables it to set ambitious environmental agendas, promote GRF, and champion policies that align economic growth with ecological preservation [10]. Therefore, addressing EQ in the G20 is not only essential for the group’s member countries but also for ensuring global environmental resilience and equitable development.
However, talking about the growing importance of EQ for the G20, especially in light of the current global environmental challenges, our study seeks to explore the intricate relationships between TCN, EDU, GRF, GLI, and ENT within this context. The G20 economies hold a critical role in shaping sustainable practices that can mitigate ecological degradation [11]. Addressing these issues requires a universal approach that integrates innovation, education, finance, and entrepreneurial initiatives to drive substantial change. Therefore, the study variables TCN, EDU, GRF, GLI, and ENT are key drivers in addressing ES. Hence, by exploring how these factors interact and influence ELF, our study highlights their potential to shape effective sustainability strategies within the G20. Understanding how these variables collectively impact ELF will help design targeted policies for sustainable development, reinforcing the G20’s role in leading the transition to a greener global economy.
This study examines environmental quality (EQ), using ecological footprint (ELF) as its proxy. There are several reasons behind choosing this variable as the proxy for EQ. The ELF is a well-established indicator that measures how human activities impact the environment through tracking resource consumption and waste generation. According to the literature, ELF serves as a key tool for evaluating environmental quality across several economies [12,13]. Unlike previous studies that often observe these factors in isolation, this study takes a broader approach by exploring the interconnected roles of several variables including technology (TCN), education (EDU), and energy transition (ENT). As environmental concerns continue to grow, it is important to understand how different economic and policy factors—such as green finance, technological innovation, education, entrepreneurship, and globalization—affect sustainability in G20 countries. By examining these relationships, this study provides useful insights into how economies can grow while protecting the environment. These findings can help policymakers develop strategies that promote both economic progress and ecological balance.
Furthermore, this study takes into consideration the impact of the COVID-19 era, which has accelerated digital transformation in shaping environmental outcomes. Moreover, while some past studies have examined the combined influence of these variables on environmental quality, few have specifically focused on G20 economies. This work fills that gap by investigating how TCN drives cleaner energy solutions and promotes sustainable production. Another important variable of the current study is education, which plays a critical role in raising environmental awareness, as highlighted in prior findings [14]. Taking into account the importance of environmental regulations, the study takes ENT into consideration, which is overlooked in existing studies especially in G20. According to previous literature, ENT fosters green business strategies and GRF [15]. Beyond that, this study further expands the conversation by incorporating GLI and GRF—two vital yet underexplored aspects of sustainability transitions. Additionally, the COVID-19 crisis highlighted, on the one hand, the urgency of sustainable financial mechanisms and, on the other hand, international collaboration in tackling environmental challenges. In this regard, the previous studies show that GRF is pivotal in funding low-carbon initiatives, whereas GLI facilitates both cross-border diffusion of green technologies and sustainable practices. However, existing studies largely overlook the dual nature of GLI, which enhances sustainability while also driving environmental degradation, if not strategically aligned with GRF [16,17]. Therefore, in order to integrate these critical components, this study offers a novel framework that connects financial, technological, and educational drivers of sustainability. Unlike previous research, this study emphasizes their interdependence and policy implications, by providing a more comprehensive understanding of how to optimize these mechanisms for achieving long-term EQ.
Hence, this suggests that addressing EQ is crucial for securing a sustainable future, especially as the world deals with the challenges of climate change, loss of biodiversity, and resource depletion [18]. Therefore, for G20, integrating key variables such as TCN, EDU, ENT, GRF, and GLI are essential in developing effective strategies to mitigate environmental impacts and substitute long-term sustainability [19,20]. Hence, our work fills a significant research gap by exploring the complex interrelationships between these factors and their collective impact on ELF, specifically within the context of the G20 economies. Therefore, by leveraging TCN, ENT, GRF, and EDU, G20 countries can create sustainable solutions for the protection of EQ. This also empowers a new generation of leaders and drives the transition to a greener economy [21,22]. Through this study, we aim to answer key questions about how these variables interact and influence environmental outcomes, providing valuable insights for the scientific community and policymakers.
For G20 countries, integrating key variables such as TCN, EDU, ENT, GRF, and GLI is essential for mitigating environmental impacts and fostering long-term sustainability [23], and GLI further enhances these efforts by enabling international cooperation and the spread of sustainable practices [24]. Based on a comprehensive literature review and the current global need for sustainable solutions, our study seeks to answer the following research questions:
  • How does green finance improve environmental quality in G20 economies?
  • In what ways does technological innovation foster environmental quality?
  • What is the impact of higher education on environmental quality in the G20?
  • How does globalization impact environmental quality in G20 countries?
  • How does entrepreneurship interact with environmental quality within the G20?
Hence, the current study aims to offer useful insights not only for researchers but also for policymakers, along with supporting global discussions on sustainable development and guiding policies that balance economic growth with protecting the environment. The study is structured as follows: Section 2 reviews the relevant literature, Section 3 explains the methodology, Section 4 presents the results, Section 5 discusses the findings, and Section 6 concludes with policy recommendations.

2. Literature Review

The interplay of TCN, EDU, and green financing has become a pivotal catalyst for EQ [25]. In G20 economies, GLI and ENT enhance these effects by facilitating the transnational exchange of knowledge, capital, and sustainable technology [26,27]. Recent research underscores the significance of EDU in promoting environmental consciousness and creativity, whereas GRF accelerates sustainable initiatives [5,28]. This analysis examines the synergistic pathways and their combined effects on ecological outcomes, highlighting GLI and ENT as essential facilitators.

2.1. Green Finance and Environmental Quality

ES involves the judicious consumption of resources to address current needs while ensuring that future age groups can fulfill their own needs [29,30,31]. This idea includes the management of these resources, a reduction in GHGs, and the promotion of green energy [32]. In this regard, the relationship between GRF and EQ highlights the impact of financial resource allocation on GDP and environmental outcomes [33,34], and GRF is essential for promoting EQ through investments in green eco-friendly technologies, clean business practices, and enabling the transition to a sustainable economy [35,36]. Therefore, understanding these connections is not only crucial for businesses aiming to align financial choices with environmental goals but also for policymakers aiming for a sustainable future. Moreover, considering that the principal impetus for GRF is environmental preservation, it is unsurprising that there is much focus on analyzing the correlations between GRF and environmental quality. It is evidenced from the literature that GRF significantly reduces CO2 and ELF [37,38]. It additionally fosters sustainable practices and diminishes ELF of enterprises [39]. Moreover, GRF fosters the advancement of green energy sources while promoting GDP by generating new possibilities and job creation in areas such as green energy [32,40]. It is worth noting that it can additionally mitigate the escalating threats associated with environmental degradation and the exhaustion of natural resources [41]. From the literature point of view, research has underscored the substantial beneficial effect of GRF on environmental quality [42,43]. Another study by [44] underscores that GRF, as an emerging funding paradigm, must be considered in the formulation and execution of environmental protection legislation. Hence, it is evidenced from the literature that GRF can facilitate the advancement of clean technologies on the one hand, while on the other hand augmenting the proportion of clean energy sources in the overall energy produced. It may put obligations on the current financial system and finances via market mechanisms for environmental preservation [45]. GRF, which facilitates environmentally sustainable industrial technologies, incorporates an ecological perspective into the financing of economic growth. GRF fosters the advancement of sustainable infrastructure and industries through investments in eco-friendly initiatives, including renewable energy, sustainable agriculture, and environmentally conscious construction [46]. Conversely, ref. [47] proposes that green financing and green development are not yet fully realized but can significantly diminish CO2 upon attaining a limit level. Green investment and financing exert a detrimental effect on CO2, as substantiated by empirical research. Green financing diminishes conventional fossil fuel usage, resulting in lower emissions and promoting greater adoption of renewable energy. It enhances and fortifies industrial frameworks, resulting in sustainable development. The paper recommends that G20 governments and the private sector advance GRF to facilitate a green transformation within the G20 region, aligning with the SDGs by 2030. GRF mitigates the adverse impacts of the environment on sustainable global growth. Consequently, the study presents the following alternative hypothesis:
H1. 
Green finance improves environmental quality.

2.2. Technological Innovation and Environmental Quality

The objective of TCN signifies a focused endeavor to attain sustainable development, yielding diverse advantages across social, economic, and environmental domains. This endeavor focuses on ensuring energy and resource security while also reducing environmental degradation, as discussed by [48,49]. TCN is fundamentally linked to achieving GHG reduction targets, improving energy efficiency, and protecting environmental integrity. The proliferation of TCN significantly contributes to the energy sector, which is essential for economic development. In this context, ref. [50] conducted a comprehensive study on the significant effects of TCN on ES, utilizing empirical data from 1996 to 2012, which includes developing nations. TCN and EQ are interconnected, significantly contributing to our commitment to environmental protection. TCN encompasses the creation and application of sustainable technologies. EQ emphasizes the need to balance carbon removal and emissions from the atmosphere. The connection between these two concepts is particularly clear in developed countries [43]. Studies have investigated the impact of TCN on CO2 in nations including China, India, and Turkey. The findings underscore its significant contribution to the advancement of EQ [39]. Renewable energy and GRF are essential components in the quest for carbon neutrality [51,52]. Current literature suggests that increased TCN has the potential to transform the energy sector and stimulate economic growth. A recent study by [53] investigated the influence of TCN on ES, utilizing data from 1996 to 2012, specifically in developing economies. The TCN limit effect is assessed for each individual by taking into account their specific income circumstances. Furthermore, TCN exerts a negligible impact on CO2 in low-income countries [54]. TCN effectively addresses the critical issue of CO2 and their environmental impact, concurrently fostering economic development. Another study by [55] conducts a detailed analysis of the specific effects of TCN on CO2 emissions. The study shows that TCN works best in countries with strong economic foundations. Furthermore, there is a lack of data to support the claim that TCN significantly reduces CO2 in developing countries. This research highlights the robustness of TCN, proposing its adoption in developing countries to boost economic growth and improve quality of life. Another recent study by [56] provided new insights into the role of TCN in mitigating GHG emissions, utilizing data from 2000 to 2018. This research employed the ARDL method to determine the relationship among the variables. The outcomes were significantly affected by the country and its economic conditions, with the specified variables exhibiting both unidirectional and bidirectional causal relationships. Another study by [57] conducted an analysis to examine the relationship between GRF and TCN in the context of ES, concluding with favorable results. The development of GRF and TCN promotes EQ through a reduction in CO2 in the environment. Another study by [58] identified that TCN enhances energy systems and facilitates sustainable development through a reduction in CO2. Furthermore, a study by [59] indicated that these innovations have significantly and positively impacted CO2. The advancement and dissemination of TCN can promote EQ by directly decreasing net emissions, as asserted by [60]. Their study demonstrated that TCN can indirectly affect CO2 efficiency through its influence on GDP. Additionally, ref. [61] found that TCN plays a critical role in reducing CO2. Moreover, Zeng [62] found that TCN focuses on green protection, easing energy and environmental pressures. Paramati, Mo [63] noted that TCN seeks to reduce carbon emissions through substantial financial investment in advanced technologies. TCN does not impede ES, which seeks to attain zero net carbon emissions. Conversely, it contributes to a reduction in CO2 and promotes ES. A study by [64] conducts an analysis of TCN levels across various provinces in China, examining panel data from 2001 to 2019. The study findings indicate an increase in TCN levels, although this is coupled with relatively low innovation effectiveness in the Western provinces of China. The spatial dimension is crucial, demonstrating significant effects in underdeveloped regions, where TCN is associated with notable reductions in CO2 [65]. This highlights the interdependent relationship between TCN and ES, indicating the potential for a balanced integration of TCN and environmental conservation. A hypothesis has been formulated for empirical evaluation based on the existing literature.
H2. 
Technological innovation fosters environmental quality.

2.3. Higher Education and Environmental Quality

EDU plays a vital role in enhancing EQ through the cultivation of environmental awareness, the promotion of sustainable practices, and the provision of skills necessary to tackle environmental challenges [66]. It fosters innovation, promotes low-carbon lifestyles, and advocates for policy measures, establishing itself as a fundamental component of ES. A study by [67] asserts that education is essential for nations to succeed in combating climate change. EDU improves energy efficiency [68]. Numerous studies have utilized EDU as a proxy for educational attainment, as the EDU index comprises various elements, with EDU serving as a key component [69]. A study was conducted by several researchers to examine the correlation among EDU, carbon emissions, and energy consumption. Various methodologies were employed, yielding conflicting results. Furthermore, [70] examined the relationship between EDU and energy consumption in OECD countries, finding a negative correlation between EDU and energy usage. The author posits that EDU, regarded as a crucial component, facilitates the achievement of energy efficiency. Another study by [71] collected data in India to analyze the impact of EDU on SO2 and NO2 through the panel technique. Upon analysis, their findings show that EDU is negatively correlated with SO2 and positively correlated with NO2. Another study by [72] examined the impact of EDU on methane and CO2 across 181 global economies, using panel methods for analysis. Their study outcomes show that EDU exerts a minimal effect on CO2, while significantly contributing to a rise in methane emissions. On the other hand, ref. [73] investigated the impact of FDI and EDU on pollution emissions in Latin American countries. Their study findings indicated an inverse correlation between education and pollution in high-income countries, while a positive correlation was observed in low-income countries. Another study by [74] investigated the connection between education and sustainability in Australia, employing the EKC framework. Their analysis using ARDL clarified the curvilinear relationship between EDU and emissions, defined by an inverted U shape. They further explained that the U-shaped pattern indicates that EDU is essential for Australia’s emission reduction efforts once a specific threshold is attained. However, ref. [75] employed various indicators to evaluate EDU levels in Pakistan and analyzed the correlation with CO2 using the ARDL method. According to their study findings, a negative correlation was observed between CO2 and EDU level. Meanwhile, ref. [76] employed a panel technique and identified consistent results for the OECD nations. They further explained the importance of EDU in advancing ES. Additionally, ref. [77] conducted research using data from Asian countries and found that EDU may not positively influence sustainability in this context. In summary, EDU plays a crucial role in advancing EQ through the cultivation of environmental awareness, the enhancement of innovative capacities, and the promotion of sustainable practices. EDU plays a vital role in addressing ecological challenges by cultivating environmentally conscious individuals and promoting research on green technologies [78]. This discussion leads us to propose the following hypothesis:
H3. 
Higher education positively impacts environmental quality.

2.4. Globalization and Environmental Quality

GLI significantly impacts EQ by enabling the international transfer of knowledge, technologies, and resources necessary for tackling global environmental issues. It facilitates international collaboration, allowing for the implementation of optimal practices in sustainable development and green innovations. GLI can facilitate economic growth and technological progress; however, its effects on EQ are contingent upon policies that emphasize eco-friendly practices, minimize carbon emissions, and promote equitable resource distribution across nations [79]. Ecological goals are hard to achieve alone. Global collaboration, sharing technology, knowledge, and funds, is key to improving environmental governance. GLI significantly impacts the cooperation among nations, leading to two predominant perspectives regarding the relationship between GLI and ES. One perspective posits that GLI promotes EDU and TCN, providing chances for industrial promotion, structural improvements, optimized resource use, and pollution management. Nan, Huang [80] highlighted the beneficial impact of GLI on energy structure modifications and the advancement of sustainable development in OECD countries. They advocated for cooperative international initiatives to tackle environmental degradation. Suki, Sharif [81] examined the impact of GLI on EQ in Malaysia, highlighting its negative influence on environmental degradation and its role in promoting sustainable development goals. Zafar, Saud [82] emphasized the advantages of GLI in promoting the dissemination of green technology, the development of GRF, and the enhancement of foreign investment within OECD countries, resulting in effective control of CO2 emissions. An alternative perspective highlights that the inequalities inherent in GLI between developed and developing nations facilitate economic and military supremacy, resulting in environmental degradation. Xia and Apergis [83] examined 67 economies, demonstrating that GLI exacerbates CO2, while increased economic development and coal resources contribute to higher emission levels. Shahbaz and Mallick [84] examined the effects of GLI on environmental quality in India, concluding that GLI generally worsens environmental problems. Wu and Guo [85] found that developed nations shift CO2 to developing countries like China and India through supply chain trade. While research links technology and renewable energy, differing conclusions call for further analysis. In conclusion, GLI has a dual impact on ES, presenting opportunities for green innovation and collaboration, while simultaneously contributing to resource depletion and increased carbon emissions. Given its capacity to worsen environmental degradation, we propose the following hypothesis:
H4. 
Globalization negatively impacts environmental quality.

2.5. Entrepreneurship and Environmental Quality

Prior research on environmental quality substantiates that ENT is a viable approach to attaining ES. York and Venkataraman [86] contend that entrepreneurs can address environmental issues by assisting existing institutions in reaching their objectives while simultaneously establishing new services and institutions to undertake actions that current entities are unable or unwilling to perform. Moreover, the emphasis on social and environmental concerns has prompted extensive research on the role of ENT in sustainability [87]. This nascent domain has presented overlapping terminology, such as social, environmental, and sustainable ENT, frequently employed interchangeably despite disputed differences [88,89]. The distinction between social and environmental ENT is unclear; however, research indicates their beneficial effects on social systems, including enhanced quality of life and public health via pollution mitigation [90]. Integrative frameworks, such as those proposed by Shepherd and Patzelt [91], increasingly connect social and environmental factors. In accordance with Johnson [92], we integrate various methodologies into a cohesive framework. In a comparable scenario, ref. [93] documents that ENT can mitigate environmental and forest deterioration, hence maintaining natural capital through enhancements in freshwater supplies and agricultural practices. A study by [94] contends that ecotourism entrepreneurs must balance competing aims concerning business operations, lifestyle ambitions, and, crucially, sustainable development methods. Another study by [95] further affirms that businesses recognize the presence of a potential market for “green” products and services. Nonetheless, empirical data indicate that ENT may potentially adversely impact ES. A study by [96] affirms that ENT can safeguard the ecosystem, enhance agricultural practices, mitigate environmental deforestation, augment freshwater supplies and biodiversity, and elevate environmental quality. They contend that opportunity-driven ENT correlates positively with the environmental quality of sustainable development. Entrepreneurial opportunities may serve as a remedy for environmental degradation and climate change. However, ref. [97] finds that ENT significantly elevates national CO2 emissions. It also demonstrates that there is neither a linear nor an inverted U-shaped correlation between ENT and CO2. Similarly, ref. [98] investigates the combined impact of education and four distinct types of ENTs on attaining EQ in 32 developing nations. Their findings indicate that these four categories of ENT exacerbate environmental deterioration, with informal ENT and necessity ENT exerting a greater influence on air pollution. They also illustrated that education mitigates the adverse impacts of all types of ENTs on environmental quality. Based on the reviewed literature, our study proposes the following hypothesis:
H5. 
Entrepreneurship enhances environmental quality.
Moreover, to build a strong foundation for this study, we draw on three key theories: Sustainability Transition Theory (STT), Innovation Diffusion Theory (IDT), and the pollution haven hypothesis (PHH). These frameworks provide critical insights into how technological innovation (TCN), higher education (EDU), green finance (GRF), globalization (GLI), and entrepreneurship (ENT) shape environmental quality (EQ) in G20 economies. Sustainability Transition Theory (STT) explains how societies evolve from unsustainable practices toward greener alternatives by integrating technological progress, financial mechanisms, governance structures, and behavioral shifts [99]. This theory is crucial in understanding the role of technological innovation (TCN) and green finance (GRF) in promoting sustainability [100,101]. TCN contributes by enhancing energy efficiency, reducing emissions, and developing eco-friendly solutions, aligning with the fundamental idea of STT that innovation drives sustainable transitions [102]. Meanwhile, GRF plays a key role by providing the necessary funding for green projects, supporting businesses in adopting low-carbon technologies, and encouraging investments in renewable energy [44]. In the case of G20 economies, STT underscores how these two factors work together to accelerate sustainability efforts, ensuring that financial resources are allocated to green innovation and environmental protection [103,104].
Innovation Diffusion Theory (IDT) complements this perspective by explaining how new technologies and sustainable practices spread across societies, influenced by education (EDU), entrepreneurship (ENT), and globalization (GLI). According to IDT, education (EDU) is a key driver of innovation adoption as it equips individuals and industries with the knowledge and skills required to implement green technologies effectively. Entrepreneurs (ENT), as early adopters of new technologies, further facilitate this diffusion by developing and commercializing sustainable business models [104]. Additionally, globalization (GLI) plays a significant role in the dissemination of green technology and best environmental practices across borders [105]. Through trade, multinational cooperation, and foreign direct investment, G20 economies can adopt cleaner production methods and enhance environmental policies. However, while IDT suggests that globalization accelerates sustainability transitions, the pollution haven hypothesis (PHH) presents a contrasting view [47]. PHH argues that globalization (GLI) can lead to environmental degradation by allowing pollution-intensive industries to relocate to countries with weaker environmental regulations [106]. This suggests that while GLI has the potential to spread green technologies, it may also contribute to increasing the ecological footprint (ELF) in G20 economies if environmental policies are not stringent enough. This theory helps in understanding why GLI may have a dual effect on environmental quality—either fostering sustainability or exacerbating pollution. Thus, this study seeks to examine whether globalization ultimately supports environmental quality or increases ecological strain in G20 economies.
The integration of these theories provides a comprehensive framework for analyzing the interplay between technological advancement, financial investment, human capital, globalization, and entrepreneurship in shaping environmental outcomes. STT and IDT emphasize the positive role of innovation, education, finance, and entrepreneurship in driving sustainability, while PHH cautions against the potential downsides of globalization [107]. This theoretical foundation enables a nuanced understanding of how each variable contributes to environmental quality and helps inform policies that balance economic growth with ecological preservation in G20 economies.

2.6. Literature Gap

Despite growing attention to environmental quality (EQ), significant research gaps persist. Most studies examine factors like technological advancements (TCN), entrepreneurship (ENT), globalization (GLI), education (EDU), and green finance (GRF) in isolation, overlooking their collective influence on sustainability. Additionally, limited research specifically targets G20 economies, despite their critical role in global sustainability efforts. While many studies rely solely on carbon emissions as an environmental indicator, this research adopts a broader perspective by incorporating the ecological footprint (ELF), offering a more holistic assessment of environmental impact. Furthermore, existing studies often overlook key methodological considerations. To address this, we employ CS-ARDL to account for cross-sectional dependence (CSD) and heterogeneity, while GMM ensures robustness and mitigates endogeneity concerns. Unlike traditional approaches that rely on Granger causality, we utilize the Dumitrescu–Hurlin causality test to capture both bidirectional and unidirectional relationships among variables. Additionally, model fit is validated through AIC/BIC and slope homogeneity tests, methodologies often disregarded in similar studies. By integrating these advanced econometric techniques, this study fills a crucial gap in the literature, offering novel insights into the interplay of key drivers shaping environmental outcomes in G20 economies.

3. Methodology

The current work examines the complex relationships between TCN, EDU, GRF, GLI, ENT, and EQ in G20 countries applying panel data during the period 2000–2020. The choice of this time frame is driven by its alignment with significant global milestones, such as the Millennium Development Goals (MDGs) and the transition to the SDGs, which began in 2015. These two decades witnessed rapid advancements in technology, a surge in global trade and investments, and increased global awareness about the need for sustainable development practices [108]. Therefore, analyzing this period allows us to capture the evolution of very important factors influencing EQ amid substantial economic and social transformations. One reason as to why studies choose G20 is that the G20 group is particularly relevant, as this group represents the world’s largest nations, representing over 80% of global GDP, 75% of international trade, and a significant share of global GHG emissions [109]. Hence, these countries play a very important role in shaping global sustainability outcomes due to their industrial activities, technological advancements, and policy frameworks. To investigate the relationships among the study variables, the study uses data from WDI, GFN, EIA, and KOFF (GLI and EIA). To investigate the relationships among the study variables, data were sourced from several reputable databases. Specifically, ELF data were obtained from the Global Footprint Network (GFN). TCN is measured through patent applications (both resident and nonresident), sourced from the World Development Indicators (WDI). Data on EDU, represented by government expenditure on education as a percentage of GDP, was also retrieved from WDI. GRF is captured through research and development expenditure as a percentage of GDP, sourced from WDI. The GLI index, reflecting total globalization, was taken from the KOF Globalization Index (KOFF). Finally, ENT is represented by a Principal Component Analysis (PCA) index using data on nuclear and renewable energy production, sourced from the Energy Information Administration (EIA). The study variables, their units, and sources are summarized in Table 1. These sources provide robust and reliable data, enabling a thorough investigation of the relationships among the study variables.
While green innovation specifically accounts for environmental patents, this study employs technological innovation as a more comprehensive measure of overall technological progress. This choice is based on several key considerations. On the other hand, many non-environmental patents indirectly improve the environment by enhancing energy efficiency and advancing industrial processes. In addition, technological innovation drives changes in production and consumption, leading to the adoption of energy-efficient technologies and smart industrial systems. Furthermore, total patent counts are widely available and standardized across countries. In contrast, green patents often face classification inconsistencies and data limitations. Many technological advancements, such as AI-driven energy systems, automation, and sustainable materials, support environmental goals even if they are not officially classified as green patents. Considering these factors, this study employs technological innovation as a strong indicator of technological progress and its role in improving environmental quality.
This study looks at how different factors—like TCN, EDU, GRF, GLI, and ENT—affect EQ, using the ELF as the main indicator. Unlike just measuring CO2 emissions, ELF gives a broader picture by considering land use, resource consumption, and overall environmental impact. In order to analyze these relationships, the study applies the CS-ARDL model, which helps capture both short-term changes and long-term trends while also accounting for CSD in panel data. Since reliability is important, the study also uses the GMM method to check the robustness of the results. Additionally, the Dumitrescu–Hurlin causality test is conducted to see how these factors influence each other over time. Hence, the study offers deeper insight into what drives environmental quality in G20 countries. The model function of the study is shown in Equation (1):
E L F = f ( T C N , E D U , G R F , G L I , E N T )
The empirical model is expressed as follows:
E L F i t = β 0 + β 1 T C N i t + β 2 E D U i t + β 3 G R F i t + β 4 G L I i t + β 5 E N T i t + ϵ i t
In Equation (2), the dependent variable (ELF) represents the ecological footprint for G20 countries. The independent variables include TCN, EDU, GRF, GLI, and ENT, all measured across the G20 nations. In Equation (2), the term β0 represents the baseline ELF when all independent variables are zero, whereas the coefficients (β1, β2, β3, β4, and β5) indicate how each independent variable affects ELF in G20. Additionally, the error term (ϵit) accounts for any random variations that might influence ELF but are not explicitly included in the model. For CS-ARDL, Equation (3) examines both short-term and long-term effects. It captures how these key factors shape ELF over time. Furthermore, the lagged component reflects past influences, while the ECT measures how quickly the system returns to equilibrium, ensuring stability in the model.
Δ E L F i t = α i + λ E L F i , t 1 β 1 T C N i , t 1 β 2 E D U i , t 1 β 3 G R F i , t 1 β 4 G L I i , t 1 β 5 E N T i , t 1 + j = 1 p ϕ j Δ E L F i , t j + ν i t
Moreover, in Equation (3), symbol Δ represents the first difference operator. This helps in measuring how variables change over time, whereas the symbol λ indicates how fast the system returns to balance after a disturbance. This shows the speed at which the system adjusts to long-term stability. Furthermore, the term αi accounts for country-specific effects. This can capture unique characteristics of each G20 nation that stay constant over time. However, the coefficients ϕj reflect the influence of past changes in independent variables. This also helps us to understand how these factors interact over time. Lastly, νit represents the error term, which includes any missing factors that might still impact the ELF. Hence, by structuring the model this way, the current study can examine both short-term variations and long-term stability in the relationship between key factors and ELF across G20 countries.
This study uses CS-ARDL model to explore both short- and long-term links between TCN, EDU, GRF, GLI, and ENT in advancing EQ across G20 nations. This approach is especially valuable as it captures both immediate impacts and long-term effects while considering the economic interconnections among countries. Although traditional panel estimation methods, such as fixed effects, random effects, and PMG-ARDL, have been commonly used in past research, they also have certain limitations [110,111,112]. Moreover, many of these methods ignore CSD, leading to biased and inconsistent estimates. They also assume that all countries share the same coefficient values, overlooking country-specific differences. Furthermore, some approaches struggle to distinguish between short- and long-term impacts, making it difficult to understand dynamic relationships.
Therefore, in order to overcome these challenges, this work adopts CS-ARDL, which effectively handles CSD, allows slope heterogeneity, and clearly differentiates short- and long-term effects. Robustness is further ensured through GMM, which accounts for unobserved common factors and also addresses the endogeneity issues of data [113]. Therefore, the CS-ARDL model is preferred over traditional ARDL and PMG-ARDL because it considers CSD and heterogeneous slopes, making it more suitable for complex environmental interactions in G20 economies [114]. However, one limitation is its inability to directly address endogeneity, which can bias if variables influence each other [115,116]. For this purpose, the study applies the GMM technique, which corrects endogeneity by using internal instruments by ensuring more reliable estimations. Hence, by combining CS-ARDL with GMM, this study enhances the accuracy and depth of its findings. As a result, the study provides a clearer picture of how TCN, EDU, GRF, GLI, and ENT influence ELF in G20 nations.
However, before applying the CS-ARDL model, the study conducts essential diagnostic tests to ensure data reliability and model stability. These include the VIF test to detect multicollinearity, the CSD test to check for cross-sectional dependence [117], the SL test to assess slope homogeneity, and the CIPS test to examine stationarity. Furthermore, the Westerlund Co-integration Test (WCT) is used to confirm long-term relationships among the variables. These diagnostic tests are considered important tools in the case of panel data analysis. These tests also help to identify the potential issues that could misrepresent the results. They further ensure that the model’s core assumptions remain valid. Finally, the study interprets the results, explores policy implications, and provides recommendations. A structured overview of the research process is presented in Figure 1, outlining each step of the analysis.
The study proceeds with checking the multicollinearity using the VIF test. Multicollinearity occurs when independent variables are too closely related. If multicollinearity is high, it can inflate the variance of regression coefficients which can make the results less reliable [118]. Therefore, to measure this, the VIF value is calculated using Equation (4):
V I F = 1 1 R 2
From Equation (4), the term R2 represents the coefficient of determination. It is worth noting that a VIF greater than 10 suggests high multicollinearity, indicating the need for variable selection or transformation.
The CSD test is essential in panel data models as it detects whether observations across different cross-sectional units are correlated. If cross-sectional dependence is ignored, it can lead to inconsistent and biased parameter estimates [119]. The CSD test, such as the Pesaran CD test, tests correlation between error terms across the cross-sectional units. The null hypothesis is that there is no CSD. A significant result suggests the presence of cross-sectional dependence, which must be addressed by using models like CS-ARDL that can account for it [120,121]. Furthermore, the SL test checks whether the relationship between the dependent and independent variables is homogeneous across all cross-sectional units. On the other hand, it examines if the coefficients of the independent variables are the same across all units in the panel. The null hypothesis assumes slope homogeneity. If the null hypothesis is rejected, the use of the CS-ARDL model is recommended, which allows for heterogeneity [122].
Moreover, in order to analyze the stationarity and long-term relationships in panel data, the study uses the CIPS test and the WCT. These tests help confirm whether the data are stable over time and whether the variables move together in the long run [123,124]. It is worth noting that the CIPS test is more useful when dealing with mixed stationarity. This situation of mixed stationarity along with CSD is common in panel data; therefore, the use of CIPS is recommended in such cases. Unlike first-generation unit root tests, CIPS considers these dependencies, which makes it more effective in panel data analysis [125]. If the test outcomes show that a series is stationary, it shows that the data are suitable for studying long-term relationships. Equation (5) provides a way to check stationarity by averaging test statistics across different units while accounting for both time and CSD.
C I P S = 1 N i = 1 N t i ( N , T )
The study also applies to the WCT to check if there is a long-term relationship between the variables. Even if individual data series are not stable on their own, this test helps determine whether they still move together over time [126]. The WCT is especially useful for panel data because it accounts for cross-sectional dependence (CSD) and differences between countries. If the test rejects the idea that there is no cointegration, it means a stable long-term relationship exists between the variables [127]. This is important for understanding how factors like green finance (GRF), technological innovation (TCN), and ecological footprint (ELF) are connected in G20 economies. The standard WCT method includes four key equations, labeled (6)–(9).
G α = 1 n i = 1 N α i S E α i
G t = 1 n i = 1 N T α i α i ( 1 )
P t = α ˙ S E ( α ˙ )
P α = T α
Once the long- and short-run analysis is completed, the current work investigates the causality between the series. The study uses the [128] causality test to examine the causal relationships among the study variables. This method is preferred because it is specifically designed for panel data, allowing for heterogeneous causality across cross-sectional units. Unlike traditional Granger causality tests, the Dumitrescu–Hurlin test does not require homogeneity in causal relationships, making it particularly suitable for examining complex interactions in diverse economies, such as the G20 [129]. Additionally, it provides robust results even in the presence of CSD and varying time periods across the panel. Equation (10) represents the causal relationship as proposed by Dumitrescu and Hurlin.
Y i t = α i + k = 1 K γ i k Y i , t k + k = 1 K   β i k X i , t k + ε i t
The associated variables are denoted as Yi,t and Xi,t. Assuming time-invariance, the coefficients (γik and βik) vary between individual observations. The lag order is denoted by the sign K. This method facilitates comprehensive analysis while adapting to each country’s developmental stage to produce highly beneficial results.

4. Results

This section presents the findings of the study analysis in a systematic way. The section begins with a descriptive assessment of the study variables by providing an overview of their characteristics. This is followed by an evaluation of multi-collinearity using the VIF test. After that, the outcomes of the CSD and SL tests are discussed, along with the results of the CIPS unit root test. After this section, the study further includes the findings from WCT, highlighting the long-term relationships among variables. Furthermore, the core results from the CS-ARDL model are presented next, supported by robustness checks through GMM regression. Finally, the study presents the outcomes of the Dumitrescu–Hurlin causality test by providing insights into causal relationships.
The outcomes of descriptive statistics are shown in Table 2, which highlights the significant variations among the study variables for G20. The first variable, ELF, has a mean value of 4.31, ranging from 0.09 to 10.93, reflecting notable environmental disparities. The variable EDU shows moderate progress with a mean of 4.44 and a standard deviation of 1.04, while TCN averages 10.61 with moderate variability. On the other hand, ENT exhibits the highest variation, with a mean of 16.49 and a standard deviation of 10.45, indicating uneven entrepreneurial activity for the G20 region. Furthermore, the variable GRF has a low mean of 1.48, suggesting limited adoption, whereas GLI stands out with a high average of 71.71, showcasing strong integration. These statistics show that there exist diverse socio-economic and environmental contexts within the G20. As a result, these findings provide a solid foundation for deeper analysis to identify key trends, relationships, and policy implications.
Moreover, while considering the importance of ELF in G20, we included Figure 2, which shows ELF trends from 2000 to 2020, revealing notable disparities between developed and emerging economies. The outcomes of Figure 2 show that developed nations such as the USA, Canada, and the UK show consistently higher ELF due to industrialization and high consumption levels, though their trends show slight stabilization or decline as well, likely reflecting the impact of environmental policies and TCN. In contrast, emerging economies like China, India, and Brazil display rising footprints, driven by rapid urbanization, industrial growth, and increased resource demand, highlighting mounting environmental challenges. Furthermore, countries such as Saudi Arabia and South Africa show fluctuations in their ELF trends, likely influenced by external factors. As a result, these trends emphasize the urgency for G20 nations to adopt sustainable practices, enhance green technology adoption, and strengthen collaborative efforts to achieve global environmental objectives.
Table 3 presents the results of the VIF test. The VIF values for all variables are below 10, indicating the study is free from multicollinearity. Among the variables, GLI has the highest VIF at 2.47, suggesting a moderate level of correlation with other variables, but still within acceptable limits. ENT and GRF both have a VIF of 1.69, reflecting relatively low multicollinearity. EDU and TCN show the lowest VIF values of 1.36 and 1.21, respectively, indicating minimal correlation with other variables. The results confirm variable independence, ensuring reliable regression estimates.
Table 4 presents the results of the CSD test, which examines whether the variables exhibit interdependence across the G20 countries. The test statistics for all variables are significant at the 1% level (p < 0.01), as indicated by the *** notation, confirming the presence of strong CSD. The ELF has a test statistic of 3.10 (p = 0.002), suggesting moderate dependence among countries. EDU, ENT, GRF, GLI, and TCN exhibit much higher test statistics, particularly GLI (49.79) and TCN (25.48), indicating substantial interdependence in these variables across countries. These results highlight that shared global trends or policies likely influence these variables, making it essential to account for cross-sectional dependence in further analyses to avoid biased estimates and ensure robust conclusions.
Table 5 presents the results of the slope homogeneity test, which assesses whether the relationships between variables are consistent across the G20 countries. Both the Delta and Adjusted Delta statistics are highly significant at the 1% level (p < 0.01), as indicated by the *** notation. The significant results suggest that slope heterogeneity exists, meaning that the effects of the independent variables on the dependent variables vary across countries. This highlights the importance of using econometric models, such as CS-ARDL, which account for heterogeneity to ensure more accurate and country-specific interpretations of the results.
Table 6 presents the results of the CIPS unit root test, which checks the stationarity of the variables across the G20 countries. The test provides results for both I(0) and I(1) statistics for each variable. For EDU, TCN, and GLI, the I(0) statistics are significant at the 1% level, indicating that these variables are stationary at this level. However, for the other variables, such as ELF, ENT, and GRF, t I(0) statistics are not significant, suggesting they are non-stationary at this level. All variables become stationary at I(1), with highly significant I(1) statistics, such as ELF = −4.417, EDU = −4.258, and TCN = −5.031, which are well below the critical value of −2.42 at the 1% level. These results indicate that most variables are integrated at I(1), while EDU, TCN, and GLI are stationary at level I(0). This outcome helps with selecting appropriate econometric models, such as the CS-ARDL, which can handle mixed stationarity and avoid spurious relationships.
Furthermore, Table 7 presents the outcomes of WCT, which examines the existence of long-run relationships between the study variables. This test involves four statistics: Gt, Ga, Pt, and Pa. According to the outcomes, Gt and Pt statistics are significant at the 1% level, with values of −3.450 and −15.427, respectively, and p-values of 0.000. The results confirm that there is a long-term relationship among the study variables. The significant values of Gt and Pt suggest that these variables are linked in a stable way over time. However, the other two statistics, Ga and Pa, are not significant, with p-values of 1.000 and 0.851, meaning they do not provide evidence of cointegration. Despite this, the overall significance of Gt and Pt supports the presence of long-run relationships, which is important for further analysis. This allows models like CS-ARDL to explore how these variables interact and influence each other over time.
To further validate the model fit, we employ the Akaike Information Criterion (AIC) and Bayesian Information Criterion (BIC), which help compare the relative performance of the models. As shown in Table 8, the CS-ARDL model exhibits lower AIC (−120.53) and BIC (−115.21) values compared to the GMM model (AIC = −105.87, BIC = −100.45). The lower values indicate that CS-ARDL provides a better fit for the data while minimizing information loss. This further supports the selection of CS-ARDL as the primary estimation technique, while GMM remains useful for robustness checks and addressing potential endogeneity concerns.
Once the diagnostic tests are performed, the next step is to apply the CS-ARDL model, which is suggested by the pretests conducted in the current study. The outcomes of this model are presented in Table 9, which includes the long-run, short-run, and Error Correction Term (ECT) estimates. The ECT in Table 9 has a value of −1.010493, which is statistically significant at the 1% level with a p-value of 0.0031. This negative and significant coefficient indicates that any deviation from the long-run equilibrium is corrected in the short term at a rate of approximately 1.01 units per period. The significant ECT confirms the presence of a stable long-run relationship among the variables and suggests that the system will adjust toward equilibrium over time.
In the long run, the results show that GRF, EDU, and TCN have significant negative effects on the ELF, with coefficients of −2.149796, −4.669443, and −1.101665, respectively. These negative relationships suggest that increases in GRF, EDU, and TCN contribute to EQ by reducing ELF over the long term. ENT also has a significant negative effect (−0.161545), indicating that higher levels of entrepreneurial activity help reduce ELF and improve sustainability. On the other hand, GLI shows a positive but marginal effect, suggesting that, over the long term, GLI may contribute to an increase in ELF, though this effect is weak and not statistically robust. The outcomes of the CS-ARDL analysis, as shown in Figure 3, indicate that GRF, EDU, TCN, and ENT all exhibit negative relationships with ELF, suggesting that these factors contribute to improving ES. In contrast, GLI shows a positive association with ELF, implying that increased GLI may lead to a higher ELF.
In the short run, GRF and EDU remained significant, with coefficients of −1.174635 and −0.037126, respectively. These findings support the idea that short-term increases in GRF and EDU contribute to reducing ELF and promoting ES. This represents the negative relationship between GRF, EDU, and ELF. Additionally, the parameter ENT also shows a significant negative effect. It highlights the role of entrepreneurial activity in reducing ELF in G20 countries. However, the variable GLI has a positive but marginal effect on ELF. This suggests that its influence on ELF is more pronounced in the short term by contributing to a slight increase in ELF. This represents the portion of improvement for G20 nations. Furthermore, the variable TCN demonstrates a small but significant negative relation with ELF. This shows that TCN in the short run helps to lower the ELF, hence causing an improvement in the EQ of G20 countries. As a result, we can say that the CS-ARDL model reveals significant long-term and short-term relationships, where variables such as GRF, EDU, ENT, and TCN play a key role in reducing ELF and improving EQ in the G20 countries.
The GMM regression results, presented in Table 10, show that TCN, Green GRF, EDU, and ENT have significant negative effects on ELF, with coefficients of −0.2100, −0.4000, −0.2200, and −0.0600, respectively. These results confirm that increases in these variables are associated with reductions in ELF, supporting the notion of ES. Conversely, GLI has a positive significant effect, indicating that higher levels of GLI may increase the ELF. Since the GMM regression produces similar results to the CS-ARDL model, these findings further validate the robustness of the outcomes, confirming the consistency and reliability of the relationships between the variables and ecological sustainability.
The results of the Dumitrescu–Hurlin causality test presented in Table 11 reveal significant causality relationships between the variables, with varying directions of influence. There is a unidirectional causality from GRF to ELF, significant at the 5% level, indicating that an increase in GRF leads to a reduction in ELF, promoting ES. Similarly, EDU shows a unidirectional causality toward ELF, suggesting that EDU contributes to a decrease in the ELF, reinforcing its role in sustainability efforts. ENT and ELF exhibit bidirectional causality, signifying that ENT reduces the ELF while a smaller ELF may encourage entrepreneurial activity. On the other hand, GLI has a unidirectional causality to ELF, suggesting that GLI tends to increase ELF, potentially leading to more environmental challenges. Lastly, TCN also shows bidirectional causality with ELF, indicating that TCN reduces the ELF, while the ELF itself influences the direction of TCN. These findings highlight the dynamic relationships between the variables, confirming that certain factors, such as EDU, GRF, and ENT, play crucial roles in improving ES.

5. Discussions

The study findings reveal that green finance (GRF) has a negative relationship with ecological footprint (ELF) in both the long run (−2.149796) and short run (−1.174635). This suggests that a 1% increase in GRF leads to a reduction in ELF by 2.15% over the long term and 1.17% in the short term. These results highlight the crucial role of green financial investments in mitigating environmental degradation within G20 economies. By facilitating capital flows toward renewable energy projects, sustainable infrastructure, and low-carbon technologies, GRF helps reduce environmental pressures and promotes a transition toward cleaner production methods. This finding is consistent with previous studies, such as [130,131], which emphasize that green financing mechanisms—such as green bonds, climate funds, and ESG investments—significantly contribute to environmental sustainability by reducing reliance on fossil fuel-based industries. Similarly, ref. [132] found that economies with strong financial commitments to sustainability tend to experience lower carbon emissions and ecological degradation, reinforcing the argument that financial incentives play a pivotal role in environmental quality improvements. However, some studies present contrasting perspectives. For instance, ref. [133] argues that while GRF generally promotes environmental sustainability, its effectiveness depends on policy implementation, financial market development, and regulatory enforcement. Furthermore, ref. [35] suggests that if green finance is not accompanied by strict environmental regulations and monitoring, its impact on ecological sustainability may be diluted. These results align with the study’s hypothesis (H1) that GRF contributes to improving environmental sustainability (ES) in G20 economies.
Similarly, the parameter technological innovation (TCN) also demonstrates a negative relationship with ecological footprint (ELF) both in the long run (−1.101665) and short run (−0.025403). This indicates that a 1% increase in TCN results in a reduction in ELF by 1.10% in the long term and 0.03% in the short term. These findings suggest that advancements in technology play a pivotal role in improving environmental quality by enabling more efficient resource utilization, cleaner production methods, and ultimately lower ecological pressures. In the context of G20 countries, this indicates that technological progress contributes to the reduction in environmental degradation over time, driven by innovations that promote energy efficiency, cleaner technologies, and waste reduction. This aligns with several studies, such as [134], who argue that technology adoption is central to reducing environmental impacts, especially in energy-intensive industries. Similarly, ref. [135] emphasizes that the digitalization of industries and the shift to renewable energy technologies contribute to lowering carbon emissions and ecological footprints. Ref. [134] further supports these findings, stating that the development and adoption of green technologies significantly mitigate environmental degradation by improving resource efficiency and reducing pollution. However, contrasting perspectives also exist. For example, ref. [136] cautions that the adoption of some emerging technologies may initially increase environmental pressures due to resource-intensive manufacturing processes or high energy demands, especially during the early stages of deployment. Furthermore, ref. [137] similarly notes that while technology can drive sustainability, its impact on environmental quality is contingent upon appropriate regulatory frameworks, incentives for green innovation, and the scaling up of technologies to ensure widespread adoption. This aligns with the study’s hypothesis (H2) that TCN enhances environmental sustainability (ES) by fostering innovation that reduces ecological footprints and carbon emissions.
In contrast, globalization (GLI) exhibits a positive relationship with ecological footprint (ELF) in both the long run (0.124337) and short run (0.036422). This means that a 1% increase in GLI results in a 0.124% rise in ELF over the long run and a 0.036% increase in the short run. These findings indicate that while globalization facilitates economic growth, technological advancements, and knowledge transfer, it also contributes to higher consumption patterns, industrial expansion, and resource exploitation, leading to greater environmental degradation over time. In the G20 economies, this positive association suggests that globalization has intensified energy demand, production activities, and trade-related emissions, ultimately worsening ecological pressures. The influx of multinational corporations expanded industrialization, and increased consumerism drives deforestation, pollution, and excessive resource consumption. This aligns with the pollution haven hypothesis (PHH), which posits that globalization shifts pollution-intensive industries to countries with weaker environmental regulations, further amplifying ecological degradation [138]. Additionally, ref. [139] argues that globalization intensifies carbon emissions by increasing trade, transportation, and industrial production, leading to a larger environmental footprint. However, some studies offer a contrasting perspective, suggesting that globalization can enhance environmental sustainability if properly regulated. Furthermore, ref. [140] highlights that globalization facilitates green technology transfers, allowing countries to adopt cleaner production processes and sustainable energy solutions. Similarly, ref. [141] finds that FDI-driven globalization can encourage environmental responsibility in host countries if strict environmental regulations and green investment policies are enforced. This outcome supports the hypothesis (H4) that GLI has a significant and negative impact on ES.
On the other hand, entrepreneurship (ENT) exhibits a negative relationship with ecological footprint (ELF) in both the long run (−0.161545) and short run (−1.164862). This suggests that a 1% increase in ENT leads to a reduction in ELF by 0.161% over the long run and 1.164% in the short run. These findings highlight that entrepreneurial activities—particularly those centered on sustainability—play a crucial role in lowering environmental degradation through green innovation, resource efficiency, and eco-conscious business models. In the context of G20 economies, the negative relationship between ENT and ELF is likely driven by green entrepreneurship, which fosters clean energy solutions, sustainable business models, and low-carbon innovations. As startups and businesses integrate environmental considerations into their strategies, they reduce reliance on fossil fuels, minimize waste, and adopt circular economy principles, ultimately leading to a smaller ecological footprint [142]. Moreover, ref. [143] emphasizes that eco-entrepreneurs drive sustainability by introducing environmentally responsible technologies, green investments, and carbon-efficient production methods. Additionally, ref. [144] argues that entrepreneurial ecosystems that prioritize sustainability accelerate the transition toward a low-carbon economy. However, while ENT generally benefits environmental quality, its impact depends on the type of entrepreneurship. High-impact green startups tend to lower ELF, but businesses focused solely on profit maximization without sustainability considerations may contribute to pollution and resource depletion. This aligns with the Porter Hypothesis, which suggests that environmentally responsible entrepreneurship leads to both economic and environmental gains when supported by strong policy frameworks. Moreover, this study outcome supports the hypothesis (H5) that ENT significantly enhances ES.
Furthermore, the CS-ARDL results align with the theoretical foundations of the study by demonstrating the complex interplay between technological advancements, financial mechanisms, education, globalization, and entrepreneurship in shaping environmental quality within G20 economies. The negative long-run coefficients of GRF, EDU, ENT, and TCN support the Sustainability Transition Theory (STT) by indicating that green finance, technological innovation, and human capital development contribute to reducing ELF, thus promoting sustainability. This aligns with STT’s premise that systemic changes in finance, governance, and technology drive long-term environmental improvements. Similarly, Innovation Diffusion Theory (IDT) finds support in the positive impact of GLI, which suggests that globalization facilitates the exchange of sustainable technologies and practices, reinforcing IDT’s emphasis on technology dissemination. However, the pollution haven hypothesis (PHH) is also partially reflected in the positive coefficient of GLI, indicating that globalization may contribute to environmental stress in certain contexts by attracting pollution-intensive industries. The negative impact of ENT and TCN in both the short and long run further validates STT, as cleaner production methods and renewable energy technologies emerge as key drivers of sustainability. These findings highlight the multifaceted nature of environmental transition, where innovation and financial instruments play crucial roles in mitigating ecological degradation while globalization presents both opportunities and risks.

6. Conclusion and Policy Implications

The world is currently facing unparalleled environmental challenges. These challenges are resulting in the degradation of ecosystems, the depletion of natural resources, and the intensifying effects of climate change. Hence, these issues cause significant threats to global sustainability and require urgent attention, particularly from the world’s largest economies. Among these economies, the G20 bloc, which represents a major portion of global economic activity, are considered key players in shaping the future of ES. Therefore, keeping in view the current scenario, this study aimed to address these concerns by investigating the role of TCN, EDU, and GRF in promoting EQ in G20 economies, with a focus on their interactions with GLI and ENT. The current study uses comprehensive analysis by utilizing the CS-ARDL, GMM, and Pairwise Causality tests. The work identifies both long-run and short-run relationships between the study variables across the G20. The study finds that technological innovation (TCN), education (EDU), and green finance (GRF) all have a significant negative impact on the ecological footprint (ELF). This means that progress in these areas helps improve environmental quality by reducing ELF. However, globalization (GLI) shows a positive relationship with ELF, suggesting that as global trade and economic activities expand, environmental degradation may also increase in G20 nations. On the other hand, entrepreneurship (ENT) has a negative impact on ELF, highlighting the role of innovation and sustainable business practices in protecting the environment. Moreover, the study emphasizes that G20 countries can enhance environmental quality by promoting technological advancements, investing in education, and increasing green finance initiatives. At the same time, since globalization contributes to higher ELF, it is crucial to manage global trade and resource consumption carefully to reduce its environmental impact. Ultimately, the findings highlight the need to balance economic growth with environmental responsibility. By integrating these key factors, G20 economies can work towards reducing environmental degradation and building a more sustainable and resilient future. The following are practical recommendations that can help enhance environmental quality in G20 nations.
  • Since GRF negatively influences ELF in both the short and long run, G20 economies should increase investments in green finance by expanding green bond markets, providing tax incentives for climate-focused financial tools, and establishing dedicated green investment funds. Additionally, they should mandate sustainability criteria for financial institutions to ensure funds are directed toward low-carbon industries and eco-friendly innovations.
  • Given the negative relationship between TCN and ELF, G20 countries must prioritize clean technology investments by increasing R&D funding for renewable energy, energy-efficient systems, and circular economy solutions. Additionally, regulatory frameworks should be strengthened to incentivize businesses to transition towards low-emission technologies through subsidies, tax breaks, and innovation grants.
  • Since EDU reduces ELF, G20 economies should embed sustainability in education systems by integrating environmental curricula at all levels and fostering climate literacy programs. Governments should also expand vocational training in green industries, ensuring a skilled workforce capable of driving sustainable transformation in key sectors such as energy, construction, and agriculture.
  • The negative link between ENT and ELF highlights the need for stronger support for green startups through dedicated funding, incubators, and regulatory incentives. G20 countries should also develop entrepreneurship-friendly policies, such as fast-track approvals for eco-innovative businesses and preferential procurement programs that prioritize sustainable enterprises.
  • Since GLI is positively linked to ELF, G20 countries must implement policies that regulate resource-intensive trade, including carbon tariffs, stricter environmental standards for imports, and incentives for businesses to adopt sustainable supply chain practices. Additionally, green trade agreements should be established to ensure globalization supports rather than harms environmental sustainability.
This study provides very valuable insights but is still subject to certain limitations. Firstly, the data range for the current study is from 2000 to 2020, which may not capture more recent developments in the dynamics of EQ in G20 economies. Secondly, the current work is confined to a limited set of variables, such as GRF, TCN, and EDU, which might not fully capture all the factors influencing EQ. Thirdly, the work mainly focusses on G20 countries, which limits the generalizability of the findings of other economies, especially those with different levels of industrialization and development. Future research can address these limitations by considering different time periods that better reflect the changing global sustainability landscape. Researchers may also explore additional dependent variables beyond environmental quality to capture broader economic impacts. Including more factors, such as governance, policy effectiveness, and sectoral shifts, could further enrich the analysis. Moreover, future studies could also apply alternative methods like MMQR or Quantile-on-Quantile models to examine relationships across different quantiles in greater depth. Thus, expanding the scope to other country groups, such as G10 or E7, could provide useful comparisons in sustainability outcomes. Finally, using dual models and the EKC framework could also help explore nonlinear relationships between variables which can offer a more comprehensive view of sustainability dynamics.

Author Contributions

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

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data will be available upon request.

Conflicts of Interest

The authors declare no conflict of interest.

Abbreviations

CSDCross-sectional dependence
CIPS Cross-sectional Im, Pesaran, and Shin
ELFEcological footprint
EKCEnvironmental Kuznets Curve
ENTEntrepreneurship
EQEnvironmental quality
EDUHigher education
GHGGreenhouse Gases
GLIGlobalization
GMMGeneralized Method of Moments
GRFGreen finance
SLSlope homogeneity
TCNTechnological innovation
VIF Variance Inflation Factor
WCTWesterlund Co-integration Test

References

  1. Kahia, M.; Omri, A. Oil Rents and Environmental Sustainability: Do Green Technologies and Environmental Technological Innovation Matter? J. Open Innov. Technol. Mark. Complex. 2024, 10, 100366. [Google Scholar] [CrossRef]
  2. Degirmenci, T.; Erdem, A.; Aydin, M. The Nexus of Industrial Employment, Financial Development, Urbanization, and Human Capital in Promoting Environmental Sustainability in E7 Economies. Int. J. Sustain. Dev. World Ecol. 2024, 32, 242–258. [Google Scholar] [CrossRef]
  3. Mudhee, K.H.; Hilal, M.M.; Alyami, M.; Rendal, E.; Algburi, S.; Sameen, A.Z.; Khurramov, A.; Abboud, N.G.; Barakat, M. Assessing Climate Strategies of Major Energy Corporations and Examining Projections in Relation to Paris Agreement Objectives within the Framework of Sustainable Energy. Unconv. Resour. 2025, 5, 100127. [Google Scholar] [CrossRef]
  4. Aydin, M.; Degirmenci, T.; Erdem, A.; Sogut, Y.; Demirtas, N. From Public Policy towards the Green Energy Transition: Do Economic Freedom, Economic Globalization, Environmental Policy Stringency, and Material Productivity Matter? Energy 2024, 311, 133404. [Google Scholar] [CrossRef]
  5. Liang, Y.; Zhou, H.; Zeng, J.; Wang, C. Do Natural Resources Rent Increase Green Finance in Developing Countries? The Role of Education. Resour. Policy 2024, 91, 104838. [Google Scholar] [CrossRef]
  6. Xie, J.; Tian, J.; Hu, Y.; Wang, Q.; Dai, Z. Imported Intermediate Goods, Intellectual Property Protection, and Innovation in Chinese Manufacturing Firms. Econ. Model. 2025, 144, 106960. [Google Scholar] [CrossRef]
  7. Hu, F.; Qiu, L.; Wei, S.; Zhou, H.; Bathuure, I.A.; Hu, H. The Spatiotemporal Evolution of Global Innovation Networks and the Changing Position of China: A Social Network Analysis Based on Cooperative Patents. R&D Manag. 2023, 54, 574–589. [Google Scholar] [CrossRef]
  8. Wang, A.; Rauf, A.; Ozturk, I.; Wu, J.; Zhao, X.; Du, H. The Key to Sustainability: In-Depth Investigation of Environmental Quality in G20 Countries through the Lens of Renewable Energy, Economic Complexity and Geopolitical Risk Resilience. J. Environ. Manag. 2024, 352, 120045. [Google Scholar] [CrossRef]
  9. Rizwanullah, M.; Shi, J.; Nasrullah, M.; Zhou, X. The Influence of Environmental Diplomacy, Economic Determinants and Renewable Energy Consumption on Environmental Degradation: Empirical Evidence of G20 Countries. PLoS ONE 2024, 19, e0300921. [Google Scholar] [CrossRef]
  10. Ali, E.B.; Shayanmehr, S.; Radmehr, R.; Bayitse, R.; Agbozo, E. Investigating Environmental Quality among G20 Nations: The Impacts of Environmental Goods and Low-Carbon Technologies in Mitigating Environmental Degradation. Geosci. Front. 2024, 15, 101695. [Google Scholar] [CrossRef]
  11. Viglioni, M.T.D.; Calegario, C.L.L.; Viglioni, A.C.D.; Bruhn, N.C.P. Foreign Direct Investment and Environmental Degradation: Can Intellectual Property Rights Help G20 Countries Achieve Carbon Neutrality? Technol. Soc. 2024, 77, 102501. [Google Scholar] [CrossRef]
  12. Jaelani, A.; Firdaus, S.; Sukardi, D.; Bakhri, S.; Muamar, A. Smart City and Halal Tourism during the Covid-19 Pandemic in Indonesia / Cidade Inteligente e Turismo Halal Durante a Pandemia Covid-19 Na Indonésia. ROSA DOS Vent.-Tur. e Hosp. 2021, 36, 103–147. [Google Scholar]
  13. Pan, Y.; Zhang, S.; Zhang, M. The Impact of Entrepreneurship of Farmers on Agriculture and Rural Economic Growth: Innovation-Driven Perspective. Innov. Green Dev. 2024, 3, 100093. [Google Scholar] [CrossRef]
  14. Chen, J.; Luo, X.; Ding, Q. Climate Risk and Renewable Energy Technological Innovation: An Institutional Environment Perspective. Risk Anal. 2024, 44, 566–581. [Google Scholar] [CrossRef] [PubMed]
  15. Shabir, M. Does Financial Inclusion Promote Environmental Sustainability: Analyzing the Role of Technological Innovation and Economic Globalization. J. Knowl. Econ. 2024, 15, 19–46. [Google Scholar] [CrossRef]
  16. Idroes, G.M.; Rahman, H.; Uddin, I.; Hardi, I.; Falcone, P.M. Towards Sustainable Environment in North African Countries: The Role of Military Expenditure, Renewable Energy, Tourism, Manufacture, and Globalization on Environmental Degradation. J. Environ. Manag. 2024, 368, 122077. [Google Scholar] [CrossRef]
  17. Ghosh, S.; Adebayo, T.S.; Abbas, S.; Doğan, B.; Sarkodie, S.A. Harnessing the Roles of Renewable Energy, High Tech Industries, and Financial Globalization for Environmental Sustainability: Evidence from Newly Industrialized Economies. Nat. Resour. Forum 2023, 48, 1186–1207. [Google Scholar] [CrossRef]
  18. Chen, Y.; Li, Q.; Liu, J. Innovating Sustainability. J. Organ. End User Comput. 2024, 36, 1–22. [Google Scholar] [CrossRef]
  19. Chu, L.K. Towards Achieving Energy Transition Goal: How Do Green Financial Policy, Environmental Tax, Economic Complexity, and Globalization Matter? Renew. Energy 2024, 222, 119933. [Google Scholar] [CrossRef]
  20. Tufail, M.; Song, L.; Khan, Z. Green Finance and Green Growth Nexus: Evaluating the Role of Globalization and Human Capital. J. Appl. Econ. 2024, 27, 2309437. [Google Scholar] [CrossRef]
  21. Kirikkaleli, D.; Adebayo, T.S. Political Risk and Environmental Quality in Brazil: Role of Green Finance and Green Innovation. Int. J. Financ. Econ. 2024, 29, 1205–1218. [Google Scholar] [CrossRef]
  22. Thi Xuan, H.; Thai Hung, N. Does Green Investment Mitigate Environmental Degradation in Vietnam: The Time-Frequency Effect of Nonrenewable Energy Investment and Globalization? Manag. Environ. Qual. 2024, 35, 1005–1027. [Google Scholar] [CrossRef]
  23. Nadiri, A.; Gündüz, V.; Adebayo, T.S. The Role of Financial and Trade Globalization in Enhancing Environmental Sustainability: Evaluating the Effectiveness of Carbon Taxation and Renewable Energy in EU Member Countries. Borsa Istanbul Rev. 2024, 24, 235–247. [Google Scholar] [CrossRef]
  24. Khan, H.H.A.; Ahmad, N.; Yusof, N.M.; Chowdhury, M.A.M. Green Finance and Environmental Sustainability: A Systematic Review and Future Research Avenues. Environ. Sci. Pollut. Res. 2024, 31, 9784–9794. [Google Scholar] [CrossRef]
  25. Sethi, L.; Behera, B.; Sethi, N. Do Green Finance, Green Technology Innovation, and Institutional Quality Help Achieve Environmental Sustainability? Evidence from the Developing Economies. Sustain. Dev. 2024, 32, 2709–2723. [Google Scholar] [CrossRef]
  26. Yaghoubi Farani, A.; Karimi, S.; Sajedi, M.; Ataei, P. The Effect of Environmental Sustainability Orientations and Entrepreneurial Orientations on the Performance of Greenhouses. Sci. Rep. 2024, 14, 2095. [Google Scholar] [CrossRef]
  27. Zhang, S.; Li, X.; Zhang, C.; Luo, J.; Cheng, C.; Ge, W. Measurement of Factor Mismatch in Industrial Enterprises with Labor Skills Heterogeneity. J. Bus. Res. 2023, 158, 113643. [Google Scholar] [CrossRef]
  28. Hussain, S.; Rasheed, A.; Rehman, S.U. Driving Sustainable Growth: Exploring the Link between Financial Innovation, Green Finance and Sustainability Performance: Banking Evidence. Kybernetes 2023, 53, 4678–4696. [Google Scholar] [CrossRef]
  29. Omri, A.; Euchi, J.; Hasaballah, A.H.; Al-Tit, A. Determinants of Environmental Sustainability: Evidence from Saudi Arabia. Sci. Total Environ. 2019, 657, 1592–1601. [Google Scholar] [CrossRef]
  30. Esmaeilpour Moghadam, H.; Dehbashi, V. The Impact of Financial Development and Trade on Environmental Quality in Iran. Empir. Econ. 2018, 54, 1777–1799. [Google Scholar] [CrossRef]
  31. Sun, Y.; Sun, H.; Ma, Z.; Li, M.; Wang, D. An Empirical Test of Low-Carbon and Sustainable Financing’s Spatial Spillover Effect. Energies 2022, 15, 952. [Google Scholar] [CrossRef]
  32. Khan, H.; Weili, L.; Khan, I. The Role of Institutional Quality in FDI Inflows and Carbon Emission Reduction: Evidence from the Global Developing and Belt Road Initiative Countries. Environ. Sci. Pollut. Res. 2022, 29, 30594–30621. [Google Scholar] [CrossRef]
  33. Rudolph, A.; Figge, L. Determinants of Ecological Footprints: What Is the Role of Globalization? Ecol. Indic. 2017, 81, 348–361. [Google Scholar] [CrossRef]
  34. Mujtaba, A.; Jena, P.K.; Bekun, F.V.; Sahu, P.K. Symmetric and Asymmetric Impact of Economic Growth, Capital Formation, Renewable and Non-Renewable Energy Consumption on Environment in OECD Countries. Renew. Sustain. Energy Rev. 2022, 160, 112300. [Google Scholar] [CrossRef]
  35. Hadj, T.B. Nonlinear Impact of Biomass Energy Consumption on Ecological Footprint in a Fossil Fuel–Dependent Economy. Environ. Sci. Pollut. Res. 2021, 28, 69329–69342. [Google Scholar] [CrossRef]
  36. Romero-Lopez, A.; Ramos, F.; Ochoa, C.Y.; Mataran, A.; Olmo, R.M.; Lopez, J.C.F.M.; Fuentes-Guerra, R.; Givens, G.; Dunning, R.; Michel-Villarreal, R.; et al. Market research about agriso mobile application for farmers. Sustainability. 2020. Available online: https://agronomyjournal.usamv.ro/pdf/2020/issue_2/Art47.pdf (accessed on 15 December 2024).
  37. Nathaniel, S.P. Ecological Footprint and Human Well-Being Nexus: Accounting for Broad-Based Financial Development, Globalization, and Natural Resources in the Next-11 Countries. Future Bus. J. 2021, 7, 24. [Google Scholar] [CrossRef]
  38. Huang, F.; Ren, Y. Harnessing the Green Frontier: The Impact of Green Finance Reform and Digitalization on Corporate Green Innovation. Financ. Res. Lett. 2024, 66, 105554. [Google Scholar] [CrossRef]
  39. Özçelik, C. Probleme Dayalı STEM Uygulamalarının Öğrencilerin STEM’e İlişkin Tutumlarına, Öz Düzenleme Becerilerine ve Bilişüstü Yetilerine Etkisi. 2021. Available online: https://www.proquest.com/openview/79cfed7264a942063357fa7268eb8d10/1?cbl=2026366&diss=y&pq-origsite=gscholar (accessed on 15 December 2024).
  40. Bayale, N.; Ali, E.; Tchagnao, A.F.; Nakumuryango, A. Determinants of Renewable Energy Production in WAEMU Countries: New Empirical Insights and Policy Implications. Int. J. Green Energy 2021, 18, 602–614. [Google Scholar] [CrossRef]
  41. Caglar, A.E.; Zafar, M.W.; Bekun, F.V.; Mert, M. Determinants of CO2 Emissions in the BRICS Economies: The Role of Partnerships Investment in Energy and Economic Complexity. Sustain. Energy Technol. Assess. 2022, 51, 101907. [Google Scholar] [CrossRef]
  42. Salem, S.; Arshed, N.; Anwar, A.; Iqbal, M.; Sattar, N. Renewable Energy Consumption and Carbon Emissions—Testing Nonlinearity for Highly Carbon Emitting Countries. Sustainability 2021, 13, 11930. [Google Scholar] [CrossRef]
  43. Grossman, G.M.; Krueger, A.B. Economic Growth and the Environment. Q. J. Econ. 1995, 110, 353–377. [Google Scholar] [CrossRef]
  44. Samour, A.; Baskaya, M.M.; Tursoy, T. The Impact of Financial Development and FDI on Renewable Energy in the UAE: A Path towards Sustainable Development. Sustainability 2022, 14, 1208. [Google Scholar] [CrossRef]
  45. Marinakis, Y.D.; Walsh, S.T.; White, R. What Is the Relationship between Sociotechnical Transition and Disruptive Innovations? Technol. Forecast. Soc. Change 2024, 199, 123081. [Google Scholar] [CrossRef]
  46. Agboola, M.O.; Bekun, F.V. Does Agricultural Value Added Induce Environmental Degradation? Empirical Evidence from an Agrarian Country. Environ. Sci. Pollut. Res. 2019, 26, 27660–27676. [Google Scholar] [CrossRef]
  47. Demena, B.A.; Afesorgbor, S.K. The Effect of FDI on Environmental Emissions: Evidence from a Meta-Analysis. Energy Policy 2020, 138, 209–237. [Google Scholar] [CrossRef]
  48. Wang, Y.; Qamruzzaman, M.; Serfraz, A.; Theivanayaki, M. Does Financial Deepening Foster Clean Energy Sustainability over Conventional Ones? Examining the Nexus between Financial Deepening, Urbanization, Institutional Quality, and Energy Consumption in China. Sustainability 2023, 15, 8026. [Google Scholar] [CrossRef]
  49. de Oliveira-Júnior, J.F.; Shah, M.; Abbas, A.; Correia Filho, W.L.F.; da Silva Junior, C.A.; de Barros Santiago, D.; Teodoro, P.E.; Mendes, D.; de Souza, A.; Aviv-Sharon, E.; et al. Spatiotemporal Analysis of Fire Foci and Environmental Degradation in the Biomes of Northeastern Brazil. Sustainability 2022, 14, 6935. [Google Scholar] [CrossRef]
  50. Pata, U.K.; Kartal, M.T.; Erdogan, S. Ecological Effects of Distinct Patents on Reducing Waste-Related Greenhouse Gas Emissions in BRIC Countries: Evidence from Novel Quantile Methods. Int. J. Sustain. Dev. World Ecol. 2024, 31, 554–566. [Google Scholar] [CrossRef]
  51. Sharif, A.; Sofuoglu, E.; Kocak, S.; Anwar, A. Can Green Finance and Energy Provide a Glimmer of Hope towards Sustainable Environment in the Midst of Chaos? An Evidence from Malaysia. Renew. Energy 2024, 223, 119982. [Google Scholar] [CrossRef]
  52. Xu, A.; Siddik, A.B.; Sobhani, F.A.; Rahman, M.M. Driving Economic Success: Fintech, Tourism, FDI, and Digitalization in the Top 10 Tourist Destinations. Humanit. Soc. Sci. Commun. 2024, 11, 1549. [Google Scholar] [CrossRef]
  53. Salame, C.T. Technologies and Materials for Renewable Energy, Environment and Sustainability. Energy Rep. 2020, 6, 1–3. [Google Scholar] [CrossRef]
  54. Xu, A.; Wang, W.; Zhu, Y. Does Smart City Pilot Policy Reduce CO2 Emissions from Industrial Firms? Insights from China. J. Innov. Knowl. 2023, 8, 100367. [Google Scholar] [CrossRef]
  55. Zhao, X.; Zhai, G.; Ma, X.; Si Mohammed, K.; Bilan, Y.; Nassani, A.A. Role of Energy Natural Resource Productivity and Environmental Taxation in Controlling Environmental Pollution: Policy-Based Analysis for Regions. Geol. J. 2024, 59, 3068–3079. [Google Scholar] [CrossRef]
  56. Fernández Fernández, Y.; Fernández López, M.A.; Olmedillas Blanco, B. Innovation for Sustainability: The Impact of R&D Spending on CO2 Emissions. J. Clean. Prod. 2018, 172, 3459–3467. [Google Scholar] [CrossRef]
  57. Delina, L.L.; Lam, R.Y.H.; Tang, W.S.; Wong, K.Y. Mapping the Actor Landscape of a Future Fintech-Funded Renewable Energy Ecosystem in Hong Kong. J. Environ. Stud. Sci. 2023, 13, 419–427. [Google Scholar] [CrossRef]
  58. Bilgili, F.; Ulucak, R.; Koçak, E.; İlkay, S.Ç. Does Globalization Matter for Environmental Sustainability? Empirical Investigation for Turkey by Markov Regime Switching Models. Environ. Sci. Pollut. Res. 2020, 27, 1087–1100. [Google Scholar] [CrossRef]
  59. Wang, M.L.; Wang, W.; Du, S.Y.; Li, C.F.; He, Z. Causal Relationships between Carbon Dioxide Emissions and Economic Factors: Evidence from China. Sustain. Dev. 2020, 28, 73–82. [Google Scholar] [CrossRef]
  60. Zhao, S.; Zhang, L.; Peng, L.; Zhou, H.; Hu, F. Enterprise Pollution Reduction through Digital Transformation? Evidence from Chinese Manufacturing Enterprises. Technol. Soc. 2024, 77, 102520. [Google Scholar] [CrossRef]
  61. Chen, M.; Jiandong, W.; Saleem, H. The Role of Environmental Taxes and Stringent Environmental Policies in Attaining the Environmental Quality: Evidence from OECD and Non-OECD Countries. Front. Environ. Sci. 2022, 10, 1976. [Google Scholar] [CrossRef]
  62. Zeng, S.; Li, G.; Wu, S.; Dong, Z. The Impact of Green Technology Innovation on Carbon Emissions in the Context of Carbon Neutrality in China: Evidence from Spatial Spillover and Nonlinear Effect Analysis. Int. J. Environ. Res. Public Health 2022, 19, 730. [Google Scholar] [CrossRef]
  63. Paramati, S.R.; Mo, D.; Huang, R. The Role of Financial Deepening and Green Technology on Carbon Emissions: Evidence from Major OECD Economies. Financ. Res. Lett. 2021, 41, 101794. [Google Scholar] [CrossRef]
  64. Huang, L. Green Bonds and ESG Investments: Catalysts for Sustainable Finance and Green Economic Growth in Resource-Abundant Economies. Resour. Policy 2024, 91, 104806. [Google Scholar] [CrossRef]
  65. Chen, Y.; Lu, H.; Yan, P.; Yang, Y.; Li, J.; Xia, J. Analysis of Water–Carbon–Ecological Footprints and Resource–Environment Pressure in the Triangle of Central China. Ecol. Indic. 2021, 125, 107448. [Google Scholar] [CrossRef]
  66. Li, D.; Tang, N.; Chandler, M.; Nanni, E. An Optimal Approach for Predicting Cognitive Performance in Education Based on Deep Learning. Comput. Human Behav. 2025, 167, 108607. [Google Scholar] [CrossRef]
  67. Boos, A.; Holm-Müller, K. The Relationship Between the Resource Curse and Genuine Savings: Empirical Evidence. J. Sustain. Dev. 2013, 6, 59. [Google Scholar] [CrossRef]
  68. Desha, C.; Robinson, D.; Sproul, A. Working in Partnership to Develop Engineering Capability in Energy Efficiency. J. Clean. Prod. 2015, 106, 283–291. [Google Scholar] [CrossRef]
  69. Liu, Y.; Cao, S.; Chen, G. Research on the Long-Term Mechanism of Using Public Service Platforms in National Smart Education—Based on the Double Reduction Policy. Sage Open 2024, 14, 21582440241239471. [Google Scholar] [CrossRef]
  70. Lanzi, E.; Verdolini, E.; Haščič, I. Efficiency-Improving Fossil Fuel Technologies for Electricity Generation: Data Selection and Trends. Energy Policy 2011, 39, 7000–7014. [Google Scholar] [CrossRef]
  71. Şentürk, İ.; Ali, A. Socioeconomic Determinants of Gender-Specific Life Expectancy in Turkey: A Time Series Analysis. Sosyoekonomi 2021, 29, 85–111. [Google Scholar] [CrossRef]
  72. Kartal, M.T.; Depren, Ö.; Kılıç Depren, S. A Comprehensive Analysis of Key Factors’ Impact on Environmental Performance: Evidence from Globe by Novel Super Learner Algorithm. J. Environ. Manag. 2024, 359, 121040. [Google Scholar] [CrossRef]
  73. Ahmad, M.; Khan, Z.; Rahman, Z.U.; Khattak, S.I.; Khan, Z.U. Can Innovation Shocks Determine CO2 Emissions (CO2e) in the OECD Economies? A New Perspective. Econ. Innov. New Technol. 2021, 30, 89–109. [Google Scholar] [CrossRef]
  74. Zhang, L.; Godil, D.I.; Bibi, M.; Khan, M.K.; Sarwat, S.; Anser, M.K. Caring for the Environment: How Human Capital, Natural Resources, and Economic Growth Interact with Environmental Degradation in Pakistan? A Dynamic ARDL Approach. Sci. Total Environ. 2021, 774, 145553. [Google Scholar] [CrossRef]
  75. Iqbal, K.; Hassan, S.T.; Wang, Y.; Shah, M.H.; Syed, M.; Khurshaid, K. To Achieve Carbon Neutrality Targets in Pakistan: New Insights of Information and Communication Technology and Economic Globalization. Front. Environ. Sci. 2022, 9, 805360. [Google Scholar] [CrossRef]
  76. Inglesi-Lotz, R. The Impact of Renewable Energy Consumption to Economic Growth: A Panel Data Application. Energy Econ. 2016, 53, 58–63. [Google Scholar] [CrossRef]
  77. Ma, B.; Bashir, M.F.; Peng, X.; Strielkowski, W.; Kirikkaleli, D. Analyzing Research Trends of Universities’ Carbon Footprint: An Integrated Review. Gondwana Res. 2023, 121, 259–275. [Google Scholar] [CrossRef]
  78. Li, D.; Xing, W. A Comparative Study on Sustainable Development of Online Education Platforms at Home and Abroad since the Twenty-First Century Based on Big Data Analysis. Educ. Inf. Technol. 2025, 27, 119–153. [Google Scholar] [CrossRef]
  79. Degirmenci, T.; Aydin, M.; Cakmak, B.Y.; Yigit, B. A Path to Cleaner Energy: The Nexus of Technological Regulations, Green Technological Innovation, Economic Globalization, and Human Capital. Energy 2024, 311, 133316. [Google Scholar] [CrossRef]
  80. Nan, S.; Huang, J.; Wu, J.; Li, C. Does Globalization Change the Renewable Energy Consumption and CO2 Emissions Nexus for OECD Countries? New Evidence Based on the Nonlinear PSTR Model. Energy Strateg. Rev. 2022, 44, 100995. [Google Scholar] [CrossRef]
  81. Suki, N.M.; Sharif, A.; Afshan, S.; Suki, N.M. Revisiting the Environmental Kuznets Curve in Malaysia: The Role of Globalization in Sustainable Environment. J. Clean. Prod. 2020, 264, 121669. [Google Scholar] [CrossRef]
  82. Zafar, M.W.; Saud, S.; Hou, F. The Impact of Globalization and Financial Development on Environmental Quality: Evidence from Selected Countries in the Organization for Economic Co-Operation and Development (OECD). Environ. Sci. Pollut. Res. 2019, 26, 13246–13262. [Google Scholar] [CrossRef]
  83. Xia, W.; Apergis, N.; Bashir, M.F.; Ghosh, S.; Doğan, B.; Shahzad, U. Investigating the Role of Globalization, and Energy Consumption for Environmental Externalities: Empirical Evidence from Developed and Developing Economies. Renew. Energy 2022, 183, 219–228. [Google Scholar] [CrossRef]
  84. Shahbaz, M.; Mallick, H.; Mahalik, M.K.; Loganathan, N. Does Globalization Impede Environmental Quality in India? Ecol. Indic. 2015, 52, 379–393. [Google Scholar] [CrossRef]
  85. Wu, X.; Sun, H.; Qin, Z.; Che, P.; Yi, X.; Yu, Q.; Zhang, H.; Sun, X.; Yao, F.; Li, J. Fully Physically Crosslinked Pectin-Based Hydrogel with High Stretchability and Toughness for Biomedical Application. Int. J. Biol. Macromol. 2020, 149, 707–716. [Google Scholar] [CrossRef] [PubMed]
  86. Wei, X.; Ren, H.; Ullah, S.; Bozkurt, C. Does Environmental Entrepreneurship Play a Role in Sustainable Green Development? Evidence from Emerging Asian Economies. Econ. Res. Istraz. 2023, 36, 73–85. [Google Scholar] [CrossRef]
  87. Muñoz, P.; Cohen, B. Sustainable Entrepreneurship Research: Taking Stock and Looking Ahead. Bus. Strateg. Environ. 2018, 27, 300–322. [Google Scholar] [CrossRef]
  88. Markman, G.D.; Waldron, T.L.; Gianiodis, P.T.; Espina, M.I. E Pluribus Unum: Impact Entrepreneurship as a Solution to Grand Challenges. Acad. Manag. Perspect. 2019, 33, 371–382. [Google Scholar] [CrossRef]
  89. Antolin-Lopez, R.; Martinez-del-Rio, J.; Cespedes-Lorente, J.J. Environmental Entrepreneurship as a Multi-Component and Dynamic Construct: Duality of Goals, Environmental Agency, and Environmental Value Creation. Bus. Ethics 2019, 28, 407–422. [Google Scholar] [CrossRef]
  90. Cohen, B.; Winn, M.I. Market Imperfections, Opportunity and Sustainable Entrepreneurship. J. Bus. Ventur. 2007, 22, 29–49. [Google Scholar] [CrossRef]
  91. Shepherd, D.A.; Patzelt, H. A Call for Research on the Scaling of Organizations and the Scaling of Social Impact. Entrep. Theory Pract. 2022, 46, 255–268. [Google Scholar] [CrossRef]
  92. Johnson, M.P.; Schaltegger, S. Entrepreneurship for Sustainable Development: A Review and Multilevel Causal Mechanism Framework. Entrep. Theory Pract. 2020, 44, 1141–1173. [Google Scholar] [CrossRef]
  93. Shepherd, D.A.; Wennberg, K.; Suddaby, R.; Wiklund, J. What Are We Explaining? A Review and Agenda on Initiating, Engaging, Performing, and Contextualizing Entrepreneurship. J. Manag. 2019, 45, 159–196. [Google Scholar] [CrossRef]
  94. Sharif, A.; Afshan, S.; Chrea, S.; Amel, A.; Khan, S.A.R. The Role of Tourism, Transportation and Globalization in Testing Environmental Kuznets Curve in Malaysia: New Insights from Quantile ARDL Approach. Environ. Sci. Pollut. Res. 2020, 27, 25494–25509. [Google Scholar] [CrossRef]
  95. Hashmi, S.H.; Fan, H.; Habib, Y.; Riaz, A. Non-Linear Relationship between Urbanization Paths and CO2 Emissions: A Case of South, South-East and East Asian Economies. Urban Clim. 2021, 37, 100814. [Google Scholar] [CrossRef]
  96. York, J.G.; Venkataraman, S. The Entrepreneur-Environment Nexus: Uncertainty, Innovation, and Allocation. J. Bus. Ventur. 2010, 25, 449–463. [Google Scholar] [CrossRef]
  97. Dhahri, S.; Omri, A. Entrepreneurship Contribution to the Three Pillars of Sustainable Development: What Does the Evidence Really Say? World Dev. 2018, 106, 64–77. [Google Scholar] [CrossRef]
  98. Omri, A.; Bel Hadj, T. Foreign Investment and Air Pollution: Do Good Governance and Technological Innovation Matter? Environ. Res. 2020, 185, 109469. [Google Scholar] [CrossRef] [PubMed]
  99. Khan, M.Q.S.; Yan, Q.; Alvarado, R.; Ahmad, M. A Novel EKC Perspective: Do Agricultural Production, Energy Transition, and Urban Agglomeration Achieve Ecological Sustainability? Environ. Sci. Pollut. Res. 2023, 30, 48471–48483. [Google Scholar] [CrossRef]
  100. Peter, C.; Swilling, M. Linking Complexity and Sustainability Theories: Implications for Modeling Sustainability Transitions. Sustainability 2014, 6, 1594–1622. [Google Scholar] [CrossRef]
  101. Williams, S.; Robinson, J. Measuring Sustainability: An Evaluation Framework for Sustainability Transition Experiments. Environ. Sci. Policy 2020, 103, 58–66. [Google Scholar] [CrossRef]
  102. Raza, A.; Habib, Y.; Hashmi, S.H. Impact of Technological Innovation and Renewable Energy on Ecological Footprint in G20 Countries: The Moderating Role of Institutional Quality. Environ. Sci. Pollut. Res. 2023, 30, 95376–95393. [Google Scholar] [CrossRef]
  103. Wonglimpiyarat, J.; Yuberk, N. In Support of Innovation Management and Roger’s Innovation Diffusion Theory. Gov. Inf. Q. 2005, 22, 411–422. [Google Scholar] [CrossRef]
  104. Ahn, H.; Park, E. For Sustainable Development in the Transportation Sector: Determinants of Acceptance of Sustainable Transportation Using the Innovation Diffusion Theory and Technology Acceptance Model. Sustain. Dev. 2022, 30, 1169–1183. [Google Scholar] [CrossRef]
  105. Khan, A.J.; Ul Hameed, W.; Iqbal, J.; Shah, A.A.; Tariq, M.A.U.R.; Ahmed, S. Adoption of Sustainability Innovations and Environmental Opinion Leadership: A Way to Foster Environmental Sustainability through Diffusion of Innovation Theory. Sustainability 2022, 14, 14547. [Google Scholar] [CrossRef]
  106. Zhang, W.; Wang, Z.; Adebayo, T.S.; Altuntaş, M. Asymmetric Linkages between Renewable Energy Consumption, Financial Integration, and Ecological Sustainability: Moderating Role of Technology Innovation and Urbanization. Renew. Energy 2022, 197, 1233–1243. [Google Scholar] [CrossRef]
  107. Wang, D.; Zhang, Y.; Zou, Z. How Asymmetric Is the Response of CO2 Emissions to Economic Restructuring in China? Evidence from NARDL Approach. J. Clean. Prod. 2023, 423, 138836. [Google Scholar] [CrossRef]
  108. Elder, M. Integration versus Prioritization in the Sustainable Development Goals: An Argument to Prioritize Environmental Sustainability and a Just Transition. Sustain. Dev. 2024, 33, 465–477. [Google Scholar] [CrossRef]
  109. Campoli, J.S.; Kodama, T.K.; Nagano, M.S.; Burnquist, H.L. Progress of G20 Nations on the 6th Sustainable Development Goal Under the Circular Economy Perspective. J. Knowl. Econ. 2025, 33, 127–163. [Google Scholar] [CrossRef]
  110. Erülgen, A.; Rjoub, H.; Adalıer, A. Bank Characteristics Effect on Capital Structure: Evidence from PMG and CS-ARDL. J. Risk Financ. Manag. 2020, 13, 310. [Google Scholar] [CrossRef]
  111. Carvelli, G. The Long-Run Effects of Government Expenditure on Private Investments: A Panel CS-ARDL Approach. J. Econ. Financ. 2023, 47, 620–645. [Google Scholar] [CrossRef]
  112. Azam, M.; Uddin, I.; Khan, S.; Tariq, M. Are Globalization, Urbanization, and Energy Consumption Cause Carbon Emissions in SAARC Region? New Evidence from CS-ARDL Approach. Environ. Sci. Pollut. Res. 2022, 29, 87746–87763. [Google Scholar] [CrossRef]
  113. Han, S.; Peng, D.; Guo, Y.; Aslam, M.U.; Xu, R. Harnessing Technological Innovation and Renewable Energy and Their Impact on Environmental Pollution in G-20 Countries. Sci. Rep. 2025, 15, 2236. [Google Scholar] [CrossRef]
  114. Mohanty, S.; Dash, S.; Priyadarshini, S.; Dulla, N.; Swain, S.C. Does Economic Policy Uncertainty, Nuclear Energy, and Crude Oil Influence CO2 Emissions? A Sectoral Growth Analysis on G20 Countries. Environ. Sci. Pollut. Res. 2024, 32, 117–133. [Google Scholar] [CrossRef] [PubMed]
  115. Gupta, R.; Sinha Ray, R.; Sharma, T.; Sharma, G. How Do ESG-Centric Social Disclosures Influence the Financial Performance of Firms? An Indian Perspective Based on the System GMM Approach. Appl. Econ. 2025, 34, 1–18. [Google Scholar] [CrossRef]
  116. Lashkov, I.; Yuan, R.; Zhang, G. Machine Learning-Based Vehicle Detection and Tracking Based on Headlight Extraction and GMM Clustering under Low Illumination Conditions. Expert Syst. Appl. 2025, 267, 126240. [Google Scholar] [CrossRef]
  117. Muhammad, I.; Ozcan, R.; Jain, V.; Sharma, P.; Shabbir, M.S. Does Environmental Sustainability Affect the Renewable Energy Consumption? Nexus among Trade Openness, CO2 Emissions, Income Inequality, Renewable Energy, and Economic Growth in OECD Countries. Environ. Sci. Pollut. Res. 2022, 29, 90147–90157. [Google Scholar] [CrossRef]
  118. Chien, F.S.; Chau, K.Y.; Sadiq, M.; Hsu, C.C. The Impact of Economic and Non-Economic Determinants on the Natural Resources Commodity Prices Volatility in China. Resour. Policy 2022, 78, 102863. [Google Scholar] [CrossRef]
  119. Sarkodie, S.A. The Invisible Hand and EKC Hypothesis: What Are the Drivers of Environmental Degradation and Pollution in Africa? Environ. Sci. Pollut. Res. 2018, 25, 21993–22022. [Google Scholar] [CrossRef]
  120. Musah, M.; Kong, Y.; Mensah, I.A.; Antwi, S.K.; Donkor, M. The Link between Carbon Emissions, Renewable Energy Consumption, and Economic Growth: A Heterogeneous Panel Evidence from West Africa. Environ. Sci. Pollut. Res. Int. 2020, 27, 28867–28889. [Google Scholar] [CrossRef]
  121. Ahmad, M.; Jiang, P.; Murshed, M.; Shehzad, K.; Akram, R.; Cui, L.; Khan, Z. Modelling the Dynamic Linkages between Eco-Innovation, Urbanization, Economic Growth and Ecological Footprints for G7 Countries: Does Financial Globalization Matter? Sustain. Cities Soc. 2021, 70, 102881. [Google Scholar] [CrossRef]
  122. Ahmad, M.; Jiang, P.; Majeed, A.; Umar, M.; Khan, Z.; Muhammad, S. The Dynamic Impact of Natural Resources, Technological Innovations and Economic Growth on Ecological Footprint: An Advanced Panel Data Estimation. Resour. Policy 2020, 69, 101817. [Google Scholar] [CrossRef]
  123. Zhang, C.; Khan, I.; Dagar, V.; Saeed, A.; Zafar, M.W. Environmental Impact of Information and Communication Technology: Unveiling the Role of Education in Developing Countries. Technol. Forecast. Soc. Change 2022, 178, 121570. [Google Scholar] [CrossRef]
  124. Persyn, D.; Westerlund, J. Error-Correction-Based Cointegration Tests for Panel Data. Stata J. 2008, 8, 232–241. [Google Scholar] [CrossRef]
  125. Rath, B.N.; Akram, V.; Bal, D.P.; Mahalik, M.K. Do Fossil Fuel and Renewable Energy Consumption Affect Total Factor Productivity Growth? Evidence from Cross-Country Data with Policy Insights. Energy Policy 2019, 127, 186–199. [Google Scholar] [CrossRef]
  126. Westerlund, J.; Edgerton, D.L. A Panel Bootstrap Cointegration Test. Econ. Lett. 2007, 97, 185–190. [Google Scholar] [CrossRef]
  127. Habib, Y.; Xia, E.; Hashmi, S.H.; Ahmed, Z. The Nexus between Road Transport Intensity and Road-Related CO2 Emissions in G20 Countries: An Advanced Panel Estimation. Environ. Sci. Pollut. Res. 2021, 28, 58405–58425. [Google Scholar] [CrossRef]
  128. Dumitrescu, E.I.; Hurlin, C. Testing for Granger Non-Causality in Heterogeneous Panels. Econ. Model. 2012, 29, 1450–1460. [Google Scholar] [CrossRef]
  129. Zaidi, S.A.H.; Zafar, M.W.; Shahbaz, M.; Hou, F. Dynamic Linkages between Globalization, Financial Development and Carbon Emissions: Evidence from Asia Pacific Economic Cooperation Countries. J. Clean. Prod. 2019, 228, 533–543. [Google Scholar] [CrossRef]
  130. Wang, W.; Imran, M.; Ali, K.; Sattar, A. Green Policies and Financial Development in G7 Economies: An in-Depth Analysis of Environmental Regulations and Green Economic Growth. Nat. Resour. Forum 2024, 39, 257–293. [Google Scholar] [CrossRef]
  131. Cheng, X.; Yao, D.; Qian, Y.; Wang, B.; Zhang, D. How Does Fintech Influence Carbon Emissions: Evidence from China’s Prefecture-Level Cities. Int. Rev. Financ. Anal. 2023, 87, 102655. [Google Scholar] [CrossRef]
  132. Joof, F.; Samour, A.; Tursoy, T.; Ali, M. Climate Change, Insurance Market, Renewable Energy, and Biodiversity: Double-Materiality Concept from BRICS Countries. Environ. Sci. Pollut. Res. 2022, 30, 28676–28689. [Google Scholar] [CrossRef]
  133. Jiakui, C.; Abbas, J.; Najam, H.; Liu, J.; Abbas, J. Green Technological Innovation, Green Finance, and Financial Development and Their Role in Green Total Factor Productivity: Empirical Insights from China. J. Clean. Prod. 2023, 382, 135131. [Google Scholar] [CrossRef]
  134. Zhang, L.; Ye, Y.; Meng, Z.; Ma, N.; Wu, C.H. Enterprise Digital Transformation, Dynamic Capabilities, and ESG Performance: Based on Data From Listed Chinese Companies. J. Glob. Inf. Manag. 2024, 32, 1–20. [Google Scholar] [CrossRef]
  135. Feng, Q.; Usman, M.; Saqib, N.; Mentel, U. Modelling the Contribution of Green Technologies, Renewable Energy, Economic Complexity, and Human Capital in Environmental Sustainability: Evidence from BRICS Countries. Gondwana Res. 2024, 132, 168–181. [Google Scholar] [CrossRef]
  136. Huang, J.; Li, X.; Wang, Y.; Lei, H. The Effect of Energy Patents on China’s Carbon Emissions: Evidence from the STIRPAT Model. Technol. Forecast. Soc. Change 2021, 173, 121110. [Google Scholar] [CrossRef]
  137. Udeagha, M.C.; Muchapondwa, E. Striving for the United Nations (UN) Sustainable Development Goals (SDGs) in BRICS Economies: The Role of Green Finance, Fintech, and Natural Resource Rent. Sustain. Dev. 2023, 31, 3657–3672. [Google Scholar] [CrossRef]
  138. Emre Caglar, A. The Importance of Renewable Energy Consumption and FDI Inflows in Reducing Environmental Degradation: Bootstrap ARDL Bound Test in Selected 9 Countries. J. Clean. Prod. 2020, 264, 121663. [Google Scholar] [CrossRef]
  139. Miao, Y.; Razzaq, A.; Adebayo, T.S.; Awosusi, A.A. Do Renewable Energy Consumption and Financial Globalisation Contribute to Ecological Sustainability in Newly Industrialized Countries? Renew. Energy 2022, 187, 688–697. [Google Scholar] [CrossRef]
  140. Ullah, S.; Lin, B. Harnessing the Synergistic Impacts of Financial Structure, Industrialization, and Ecological Footprint through the Lens of the EKC Hypothesis. Insights from Pakistan. Energy 2024, 307, 132540. [Google Scholar] [CrossRef]
  141. Weimin, Z.; Chishti, M.Z.; Rehman, A.; Ahmad, M. A Pathway toward Future Sustainability: Assessing the Influence of Innovation Shocks on CO2 Emissions in Developing Economies. Environ. Dev. Sustain. 2022, 24, 4786–4809. [Google Scholar] [CrossRef]
  142. Hockerts, K.; Wüstenhagen, R. Greening Goliaths versus Emerging Davids—Theorizing about the Role of Incumbents and New Entrants in Sustainable Entrepreneurship. J. Bus. Ventur. 2010, 25, 481–492. [Google Scholar] [CrossRef]
  143. Cheng, P.; Wu, S.; Xiao, J. Exploring the Impact of Entrepreneurial Orientation and Market Orientation on Entrepreneurial Performance in the Context of Environmental Uncertainty. Sci. Rep. 2025, 15, 1913. [Google Scholar] [CrossRef] [PubMed]
  144. Ben Youssef, A.; Boubaker, S.; Omri, A. Entrepreneurship and Sustainability: The Need for Innovative and Institutional Solutions. Technol. Forecast. Soc. Change 2018, 129, 232–241. [Google Scholar] [CrossRef]
Figure 1. Progression of econometric analysis.
Figure 1. Progression of econometric analysis.
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Figure 2. Ecological footprint trends in G20.
Figure 2. Ecological footprint trends in G20.
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Figure 3. Outcomes of the study.
Figure 3. Outcomes of the study.
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Table 1. Variables and sources.
Table 1. Variables and sources.
VariablesUnit Short FormSource
Ecological FootprintGHA (Global Hectares) per capitaELFGFN
Technological InnovationPatent applications
(resident nonresident)
TCNWDI
Higher EducationGovernment expenditure on education, total (% of GDP)EDUWDI
Green FinanceResearch and development expenditure (% of GDP)GRFWDI
GlobalizationTotal globalizationGLIKOFF Globalization
EntrepreneurshipPCA index using nuclear and renewable productionENTEIA
Table 2. Descriptive statistics.
Table 2. Descriptive statistics.
ELFEDUENTGRFGLITCN
Mean4.3153114.43733416.485611.48137871.7133210.60980
Median4.3065264.51911014.258001.17200569.8920110.40500
Maximum10.926817.71887049.660004.79571089.4587625.23000
Minimum0.0872671.2647000.7500000.03557046.407321.450000
Std. Dev2.3551451.04266010.451241.02947610.077833.637254
Table 3. VIF test.
Table 3. VIF test.
VariablesVIF1/VIF
GLI2.470.405369
ENT1.690.590566
GRF1.690.592783
EDU1.360.734994
TCN1.210.825578
Table 4. CSD test.
Table 4. CSD test.
Parameters StatisticsProb.
ELF3.10 ***0.002
EDU10.37 ***0.000
ENT4.13 ***0.000
GRF10.60 ***0.000
GLI49.79 ***0.000
TCN25.48 ***0.000
Note: *** p < 1%.
Table 5. Slope test.
Table 5. Slope test.
Test Value Prob.
Delta9.476 ***0.000
Adj. Delta11.606 ***0.000
Note: *** p < 1%.
Table 6. Unit root test.
Table 6. Unit root test.
VariablesCIPS Test
I(0)I(i)
ELF−1.314−4.417 ***
EDU−2.520 ***−4.258 ***
ENT−1.978−5.117 ***
GRF−1.923−4.047 ***
GLI−2.478 ***−4.051 ***
TCN−3.203 ***−5.031 ***
CV = −2.12 (10%)CV = −2.21 (5%)CV = −2.42 (1%)
Note: *** p < 1% CV = critical value.
Table 7. Westerlund Co-integration Test.
Table 7. Westerlund Co-integration Test.
StatisticsValueZ-Valuep-Value
Gt−3.450 ***−3.5800.000
Ga−8.3473.4111.000
Pt−15.427 ***−4.9580.000
Pa−9.2711.0410.851
Note: *** p < 1%.
Table 8. AIC/BIC test.
Table 8. AIC/BIC test.
Model SpecificationAICBIC
CS-ARDL−120.53−115.21
GMM−105.87−100.45
Table 9. CS ARDL test.
Table 9. CS ARDL test.
VariableCoefficientStd. Errort-StatisticProb.
Long-Run Equation
GRF−2.149796 ***0.389559−5.5185430.0000
EDU−4.669443 **2.055676−2.2714880.0237
ENT−0.161545 **0.074411−2.1709970.0306
GLI0.124337 *0.0740141.6799230.0939
TCN−1.101665 ***0.389888−2.8255910.0050
Short-Run Equation
ECT−1.010493 ***0.3413827−2.960.0031
GRF−1.174635 **0.5776259−2.03 0.042
EDU−0.037126 ***0.012237−3.0338710.0026
ENT−1.164862 ***0.429515−2.7120410.0070
GLI0.036422 *0.0194591.8717910.0621
TCN−0.025403 **0.011567−2.1960660.0287
Note: *** p < 1%, ** p < 5%, * p < 10%.
Table 10. GMM regression.
Table 10. GMM regression.
VariableCoefficientStd. Errorz-Valuep-Value
TCN−0.21000.0750−2.800.005
GRF−0.40000.1600−2.500.012
ENT−0.06000.0220−2.730.006
GLI0.11000.04502.440.015
EDU−0.22000.1000−2.200.028
Table 11. Pairwise panel causality test.
Table 11. Pairwise panel causality test.
Null HypothesisZbar-Statp-ValueDecision
ELF⇸GRF0.5240.600Unidirectional
GRF⇸ELF−1.8240.048 **
ELF⇸EDU0.6890.491Unidirectional
EDU⇸ELF−2.1560.031 **
ELF⇸ENT2.8470.004 ***Bidirectional
ENT⇸ELF−3.4200.001 ***
ELF⇸GLI0.3270.743Unidirectional
GLI⇸ELF1.0960.012 **
ELF⇸TCN2.4580.014 **Bidirectional
TCN⇸ELF−3.0140.003 ***
Note: *** p < 1%, ** p < 5%.
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Pei, M.; Tabish, R. Forging a Sustainable Future in G20 Economies: The Transformative Role of Technological Innovation, Green Finance and Higher Education Amid Globalization and Entrepreneurial Growth. Sustainability 2025, 17, 3321. https://doi.org/10.3390/su17083321

AMA Style

Pei M, Tabish R. Forging a Sustainable Future in G20 Economies: The Transformative Role of Technological Innovation, Green Finance and Higher Education Amid Globalization and Entrepreneurial Growth. Sustainability. 2025; 17(8):3321. https://doi.org/10.3390/su17083321

Chicago/Turabian Style

Pei, Meng, and Riya Tabish. 2025. "Forging a Sustainable Future in G20 Economies: The Transformative Role of Technological Innovation, Green Finance and Higher Education Amid Globalization and Entrepreneurial Growth" Sustainability 17, no. 8: 3321. https://doi.org/10.3390/su17083321

APA Style

Pei, M., & Tabish, R. (2025). Forging a Sustainable Future in G20 Economies: The Transformative Role of Technological Innovation, Green Finance and Higher Education Amid Globalization and Entrepreneurial Growth. Sustainability, 17(8), 3321. https://doi.org/10.3390/su17083321

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