Next Article in Journal
Investigation on Cryogenic Cavitation Characteristics of an Inducer Considering Thermodynamic Effects
Previous Article in Journal
Analysis of Non-Road Mobile Machinery Homologation Standards in Relation to Actual Exhaust Emissions
Previous Article in Special Issue
National Environmental Taxes and Industrial Waste in Countries across Europe
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Impact of Renewable Energy, Business Climate, and Human Capital on CO2 Emissions: Empirical Evidence from BRICS Countries

1
Department of Industrial Engineering, Istanbul University-Cerrahpaşa, 34500 İstanbul, Turkey
2
Department of Public Finance, Bandirma Onyedi Eylul University, 10200 Balikesir, Turkey
3
Department of Educational Sciences, Hasan Ali Yucel Faculty of Education, İstanbul University-Cerrahpaşa, 34500 İstanbul, Turkey
4
Department of Economics, Plekhanov Russian University of Economics (PRUE), 117997 Moscow, Russia
5
Department of Economics, Financial University under the Government of the Russian Federation, 125167 Moscow, Russia
*
Author to whom correspondence should be addressed.
Energies 2024, 17(15), 3625; https://doi.org/10.3390/en17153625
Submission received: 21 June 2024 / Revised: 4 July 2024 / Accepted: 22 July 2024 / Published: 24 July 2024
(This article belongs to the Special Issue Sustainable Energy Economics and Prospects Research)

Abstract

:
Since the 1950s, the remarkable amount of global environmental degradation has heightened environmental concerns at both national and international levels. This shift has spurred intensive research into the causes of environmental degradation and potential remedies, including environmental taxes, fines, education, and regulations. The drivers of CO2 emissions have been widely explored in the literature, but the nexus between business climate, human capital, and CO2 emissions has not been examined sufficiently. Therefore, the purpose of this study is to delve into the interplay between renewable energy, business climate, human capital, and CO2 emissions in BRICS countries from 2000 to 2020 using panel causality and cointegration tests. Our research hypotheses suggest that there are significant mutual interactions among renewable energy, business climate, human capital, and CO2 emissions based on the associated literature. The results of the causality test verify the research hypotheses by uncovering a bidirectional causality between business climate, renewable energy use, human capital, and CO2 emissions. Furthermore, the cointegration analysis reveals that increases in renewable energy use and human capital decrease CO2 emissions at the panel level, but a positive business climate increases CO2 emissions at the panel level. However, the impact of business climate on CO2 emissions at the country level varies among BRICS economies based on environmental policies. In conclusion, investing in green energy technologies and education is a useful tool to decrease CO2 emissions. In addition to this, the positive effect of business climate on CO2 emissions should be balanced by regulations to increase environmental, social, and governance awareness of firms.

1. Introduction

The environment is of vital importance for a healthy life and the presence of life on planet Earth. However, since the Industrial Revolution, the world has witnessed significant environmental degradation in terms of air and water pollution, global warming, deforestation, natural resource depletion, and a decline in biological diversity. Moreover, environmental degradation is foreseen as the top long-term risk in the world, according to the World Economic Forum [1]. Therefore, environmental sustainability has become one of the global priorities and is a constituent part of sustainable development. The environment has been a key aspect of sustainable development since the 1972 Stockholm Conference on the Human Environment [2]. Additionally, four Sustainable Development Goals (SDGs), including climate action, clean water and sanitation, life on land, and life below water, are directly related to the environment [3]. Furthermore, almost all of the remaining SDGs, such as affordable and clean energy, industry, innovation and infrastructure, and responsible consumption and production, are also significant for environmental protection.
The SDGs were adopted by the 193 UN Members in 2015. Some progress towards the achievement of the SDGs was made between 2015 and 2019, and the overall SDG index, which indicates the progress made towards all SDGs, increased from 63.8 to 66.0. However, progress markedly slowed down due to the COVID-19 pandemic, and limited progress has been made towards the environmental goals of the SDGs [4,5]. High-income countries made relatively much more progress towards the achievement of the SDGs when compared with middle-income and low-income countries between 2015 and 2023.
Another concept which is closely related to the achievement of many of the SDGs is ESG (environment, social, and governance), which was officially mentioned in a report called “Who Cares Wins” [6]. ESG indicates a firms’ commitment to environmental, social, and governance factors [7]. In this context, the environmental pillar of the ESG indicates how firms take notice of the environmental issues, such as carbon emissions, waste management, and deforestation, resulting from their business activities. The social pillar of the ESG denotes the approach of the firms towards social issues, including employees, labor standards, gender, human rights, and diversity. Lastly, the governance pillar of the ESG denotes the corporate policies of firms, such as internal audits, company leadership, shareholder rights, and transparency.
In conclusion, the environment is one of the main dimensions of both sustainable development and ESG practices. Therefore, identifying the factors behind environmental degradation is beneficial for countries and businesses to protect and improve the environment. A considerable number of studies have examined the driving micro- and macro-level factors of environmental degradation. These studies have unveiled many factors that are drivers of environmental sustainability, such as GDP per capita [8], economic growth [9,10], population [8,9], urbanization [8], institutional quality and public governance [10,11], education and human capital [11], trade liberalization [10,12], globalization and global value chains [10], industry structure [12], financial development [12], international tourism [12], environmental and market regulations [13,14,15], green innovation [14,15,16,17], natural resources [10,18], technological progress and innovation [19,20], foreign direct investments [17,20], economic openness [21], agriculture [22], renewable and non-renewable energy use and energy intensity [9,10,12,15,18,19,20,22], ESG performance [23,24], and geopolitical risks [25].
This study investigates the interaction among business climate, renewable energy use, human capital, and CO2 emissions in a sample of BRICS countries (the leading emerging markets of Brazil, Russia, India, China, and South Africa) by means of the Westerlund and Edgerton [26] cointegration test and JKS (Juodis–Karavias–Sarafidis) [27] causality test, which produce robust results with the availability of heterogeneity and cross-sectional dependency. BRICS countries make up over 42% of the world’s population, 30% of the world’s territory, 18% of global trade, and 23% of the world’s GDP and have driven the global economy in recent years [28]. Furthermore, all BRICS countries saw improvements in business climate and human capital during the 2000–2020 period. However, Russia and China, in particular, have experienced remarkable improvements in terms of their business climate, while China and India have achieved considerable progress in human capital compared to the other BRICS countries [29]. On the other hand, China, India, and the Russian Federation are also among the top five CO2 emitters in the world, along with the USA and Japan [30]. Lastly, the Russian Federation has a very high level of human development, Brazil, China, and South Africa have high levels of human development, and India has a moderate level of human development [31]. Therefore, countries with different development levels can also benefit from the findings of this research, based on the results of country-level analyses.
This study aims to support the associated empirical literature in two ways. In the empirical literature, the studies of [32,33,34] only investigated the effect of business climate indicators on the environment in developed and developing countries and mainly uncovered that a positive business climate easing the establishment and expansion of business activities negatively affects the environment. However, the effect of the environment on business climate has not been sufficiently researched. Thus, the first empirical contribution of this article is to analyse the reciprocal nexus between business climate and CO2 emissions, differing from the existing limited literature.
Furthermore, human capital is one of the fundamental parameters at the centre of economic activities and, in turn, may influence nearly all activities. Academics have traditionally focused on the economic effects of human capital, reflecting the knowledge, skills, and abilities of a population in an economy, while the effects of human capital on the environment have been largely overlooked until now [35,36,37]. Researchers have largely investigated the effect of human capital on the environment since 2019, and the majority of these studies denoted that human capital contributes to environmental quality [38,39,40,41,42,43,44]. However, Haini [45], Zhang et al. [46], and Sarkodie et al. [47] discovered human capital has a negative effect on the environment. The two-way association between human capital and the environment has been explored by a few researchers, and in turn, the causal relationship between these two variables is still inconclusive [38,48,49,50]. The second empirical contribution of this article is a dual analysis between human capital and CO2 emissions, differing from the associated empirical literature.
The rest of this research article is organized as follows: Section 2 reviews the main findings of the related empirical studies on the nexus between renewable energy, business climate, human capital, and the environment. Section 3 outlines the data and methods of the study. The results and related discussion are presented in Section 4 and Section 5, respectively. The final section concludes with policy implications and recommendations.

2. Theoretical Background

The environment performs crucial functions, such as providing resources and biodiversity and assimilating wastes for a healthy world. Therefore, the protection of the environment is vital for both current and future generations. However, environmental degradation, resulting in climate change, air and water pollution, resource depletion, and a decline in biological diversity, has considerably raised environmental concerns, especially since the 1950s. This significant degradation of the environment has led researchers to explore the drivers of global environmental degradation. Empirical studies have identified many economic, social, and institutional factors as drivers of environmental degradation. This paper studies the environmental impacts of business climate, human capital, and renewable energy use.
A business climate reflects the attitudes of governments, financial institutions, and labour unions toward the private sector, including aspects like business regulations, tax rates, lending rates, and inflation [51]. Therefore, a positive business climate, including market-oriented business regulations, lower tax and lending rates, or loose labour regulations, which encourage the establishment of new firms or the expansion of the business activities of firms, is expected to impact CO2 emissions [33]. However, the direction of the environmental effect of business climate depends on the current environmental policies of countries. On the other hand, CO2 emissions can also affect firms through labour health, the costs of raw materials, and supply chains, which are sensitive to air and water pollution, climate change, and natural events. Thus, a bilateral or one-way interaction between business climate and CO2 emissions is theoretically expected based on a country’s own institutional, economic, and social characteristics in light of these theoretical considerations.
Human capital is one of the key determinants of innovation, entrepreneurship, green and energy-efficient technologies, technological progress, productivity, and in turn, economic growth and development [39,42,52,53,54]. Therefore, improvements in human capital can decrease CO2 emissions through the development of green and energy-efficient technologies and productivity theoretically. However, the interaction between the environment and economic growth differs based on the environmental Kuznets curve (EKC) [55]. The EKC hypothesis suggests an inverse U-shaped relationship between environmental degradation and economic growth. According to the hypothesis, the environment deteriorates in the early stages of economic growth but sees an improvement after a threshold, due to increases in environmental awareness and the development of green and energy-efficient technologies [18,56]. Lastly, more educated and skilled individuals usually have greater environmental awareness, avoiding attitudes and behaviours that increase CO2 emissions, such as opting for green energy sources and energy-efficient devices and obeying environmental regulations [57,58,59]. On the other hand, increasing CO2 emissions can also impact human capital through direct channels, such as nutrition, health, and well-being, and indirect channels involving changes in markets and economic systems [60]. In conclusion, a bilateral or one-way interaction between human capital and CO2 emissions is theoretically expected based on the studied countries’ development levels in light of these theoretical considerations.
Last, it is predicted that more than three-quarters of global greenhouse gas emissions originate from energy consumption [61]. Therefore, renewable energy sources such as water, the sun, and wind, which emit relatively lower levels of greenhouse gases into the air, are theoretically expected to negatively impact CO2 emissions [62].

3. Empirical Literature Review

In the literature, the nexus between business climate and the environment has been analysed only by Gani and Sharma [32], Rieger [33], and Omri and Afi [34] in a sample of developed and developing countries using regression analyses, as shown in Table 1. These studies have found that a positive business climate, which facilitates the establishment and expansion of business activities, has negatively affected the environment. However, the use of the regression approach in these studies does not enable us to see country-level differences. Therefore, our study will be one of the first studies to analyse the two-way relationship between business climate and CO2 emissions, and the use of the AMG (augmented mean group) estimator in our study allows us to make country-level inferences about the nexus between business climate and CO2 emissions, differing from the previous limited empirical studies.
In the associated literature, the nexus between renewable energy use and the environment has been widely investigated by different countries and country groups, and the studies shown in Table 2 have largely uncovered a negative effect of renewable energy use on greenhouse gases and CO2 emissions.
The relationship between human capital and the environment was neglected until 2019. However, several studies listed in Table 3 included human capital in their empirical analyses as a determinant of the environment. These studies also analysed the drivers of environmental degradation between 2019 and 2023 for different countries and country groups, using regression, co-integration, and causality analyses as econometric techniques. A large portion of these studies revealed a mitigating effect of human capital on CO2 emissions [38,39,40,41,42,43,44,76,77,78,79,80,81,82]. However, a few studies have also uncovered a positive influence of human capital on CO2 emissions [45,46,47]. Furthermore, the causality between CO2 emissions and human capital has been analysed in a small number of studies. Bano et al. [48], Abdouli and Omri [49], and Joof and Zhakanova Isiksal [50] uncovered a bilateral causal relationship between human capital and CO2 emissions. Ahmed et al. [77] discovered a unilateral causal relationship between human capital and ecological footprint, and Zafar et al. [38] revealed an insignificant causal relationship between human capital and ecological footprint. In conclusion, our article will be one of the limited studies to investigate the mutual interaction between human capital and CO2 emissions.
Three hypotheses in this article are created based on the associated theoretical aspects and empirical research articles.
H1. 
There is a significant interplay between renewable energy use and CO2 emissions.
H2. 
There is a significant interplay between business climate and CO2 emissions.
H3. 
There is a significant interplay between human capital and CO2 emissions.

4. Materials and Methods

This research paper investigates the relationship between business climate, renewable energy use, human capital, and CO2 emissions through Westerlund and Edgerton [26] bootstrap cointegration test and JKS [27] causality test considering the methodologies of similar recent empirical studies [15,63,84,85]. The variables used in the empirical section are displayed in Table 4. In this context, environment (CO2) is represented by CO2 emissions (metric tons per capita), obtained from the World Bank [86]. Business climate (BUSCLIM) is proxied by the private sector index from UNCTADSTAT [29]. This index indicates the ease of international trade in terms of time and related costs, as well as financial and regulatory support to businesses in terms of credit availability, the time required to start a business, and speed of contract enforcement. Renewable energy (RNWEN) is proxied by renewable energy use as a percentage of total final energy use and obtained from World Bank [87]. Last, human capital (HCAP) is represented by the index of human capital from UNCTADSTAT [29], reflecting the status of education, skills, health of individuals, and overall R&D activities in a country.
The BRICS economies, consisting of Brazil, the Russian Federation, India, China, and South Africa, are the focal point of this study, covering the period from 2000 to 2020. This timeframe was chosen because the business climate variable is available from 2000, and the CO2 emissions and renewable energy use variables are available up to 2020. The econometric analyses are implemented using Stata 17.0, Gauss 12.0, and EViews 13.0 statistical packages. Based on the descriptive statistics given in Table 5, the average value of the CO2 variable is 5.589 metric tons per capita, the average value of the BUSCLIM index is 51.517, the average value of RNWEN is 22.739%, and the average value of the HCAP index is 45.663. The variables of RNWEN, BUSCLIM, and HCAP exhibit notable volatility during the period between 2000 and 2020.
The effect of business climate, renewable energy use, and human capital on CO2 emissions in BRICS states is scrutinized within the scope of the model described in Equation (1). The dependent variable is CO2 emissions (CO2), and the explanatory variables are business climate (BUSCLIM), renewable energy use (RNWEN), and human capital (HCAP).
C O 2 i t = α i + β 1 B U S C L I M i t + β 2 R N W E N i t + β 3 H C A P i t + ε i t
where i and t, respectively, represent the countries and years.
In the empirical analysis, the methodology presented in Figure 1 is followed [85]. First, LM, LMadj., and LM cross-section dependency (CD) tests are conducted, which are, respectively, suggested by Breusch and Pagan [88], Pesaran et al. [89], and Pesaran [90]. Then homogeneity tests of delta tilde by Pesaran and Yamagata [91] are conducted to determine the presence of homogeneity or heterogeneity. The stationarity of the variables is examined by means of panel CIPS test of Pesaran [92] considering the presence of heterogeneity among the series. The short-run and long-run interactions among business climate, renewable energy use, human capital, and CO2 emissions are, respectively, investigated using the JKS [27] causality test and AMG estimator of Eberhardt and Bond [93].
The short-run interaction among business climate, renewable energy use, human capital, and CO2 emissions is investigated using JKS [27] causality test in view of the fact that there is heterogeneity and cross-sectional dependence among the series. The causality test examines whether one variable is useful in predicting another variable [94]. JKS [27] causality test regards heterogeneity and produces robust results under the presence of cross-sectional dependence. Furthermore, the half-panel jackknife (HPJ) technique of Dhaene and Jochmans [95] used in the test mitigates Nickell bias. Consequently, the JKS [27] test is a robust causality test, especially in complex models for which traditional methods might fall short.
On the other hand, cointegration test determines whether series under consideration moves together or displays a common long-term trend. In other words, two series with stochastic trends are accepted as cointegrated if the linear combination of two variables eliminates the trends or becomes I(0) [96]. In this context, the JKS [27] causality test, which is developed for heterogeneous panel datasets, is used to determine the presence of a short-term interplay of business environment, renewable energy use, human capital, and CO2 emissions. The test rests on the linear dynamic panel data model, as shown in Equation (2):
y i t = 0 i + p = 1 P p , i y i , t p + p = 1 P β p , i x i , t p + ε i t
For i = 1, …, N and t = 1, …, T, x i t is postulated to be scalar for simplification. The parameters of 0 i and p , i , respectively, indicate individual-specific effects and heterogeneous autogressive coefficients (p = 1, …, P). Furthermore, β p , i are the Granger causality parameters, and ε i t are the error terms [97]. JKS [27] causality test allows the HPJ estimator to tackle the pooled estimator’s bias problem, and HPJ estimator’s variance is derived from bootstrapping if cross-sectional dependence exists. The null hypothesis, which suggests that x i t is not Granger cause of y i t , and the alternative hypothesis are formulated as follows:
H 0 : β p , i = 0 ,   f o r   a l l   i   a n d   p H 1 : β p , i 0 ,   f o r   s o m e   i   a n d   p
The long-run interaction among business climate, renewable energy use, human capital, and CO2 emissions is analysed by Westerlund and Edgerton’s [26] bootstrap cointegration test, which is derived from Equation (3), because the test considers heterogeneity and generates robust results for small samples.
y i t = α i + x i t β i t + Z i t  
Z i t = μ i t + V i t = J = 1 t ŋ i j
where i and t, respectively, represent the cross-section and time dimensions of the dataset. Z i t is the disturbance term. The LM statistic is calculated as follows:
L M N + = 1 N T 2 i = 1 N t = 1 T w ^ i 2 s i t 2        
In Equation (5), s i t 2 is the partial sum of Z i t , and w ^ i 2 is the long-run variance of μ i t . Both are generated from cointegration model via fully modified ordinary least squares regression. The H0 of the cointegration test suggests the presence of cointegration relationship among the series under consideration [26]. The bootstrapping critical values are regarded if cross-sectional dependence exists. Otherwise, asymptotic probability values from normal distribution are taken into account. Last, cointegration coefficients are estimated through the AMG (augmented mean group) estimator of Eberhardt and Bond [93] to determine the presence of heterogeneity and countries’ cointegration coefficients.

5. Results

In the results section, the subsistence of CD and heterogeneity is examined through econometric tests first. The subsistence of CD among CO2, BUSCLIM, RNWEN, and HCAP is investigated using the LM, LMadj., and LM CD tests, and their results are exhibited in Table 6. The null hypothesis in terms of cross-section independence is negated because the probability values of the three tests are lower than 5%. In conclusion, the cross-sectional dependence among CO2 emissions, business climate, renewable energy use, and human capital is unveiled.
The subsistence of homogeneity is also examined using two delta tilde tests, and these two tests’ results are indicated in Table 7. The null hypothesis in terms of homogeneity is negated for both tests, and the availability of heterogeneity is unveiled. Therefore, econometric tests of unit root, cointegration, and causality developed for heterogeneous panel datasets can lead us to attain relatively stronger results.
The stationarity of CO2, BUSCLIM, RNWEN, and HCAP is investigated by means of a panel CIPS test developed for the series with CD, and the test statistics are reported in Table 8. The results of the tests show that the variables of CO2, BUSCLIM, RNWEN, and HCAP are not stationary at their level values, but the first differences of these series have become stationary.
The cointegration interplay between human capital, business climate, renewable energy use, and CO2 emissions is analysed using the Westerlund and Edgerton [26] bootstrap cointegration test. The test statistics, asymptotic, and bootstrap probability values are introduced in Table 9. As a result of the cointegration analysis, the H0 hypothesis, which indicated the presence of a long-term relationship between the variables, is accepted (p > 0.05).
The cointegration coefficients are forecasted by means of the AMG estimator and reported in Table 10. The estimated cointegration coefficients indicate that human capital and renewable energy negatively impact CO2 emissions, but business climate positively influences CO2 emissions on the panel level. However, the BRICS countries’ cointegration coefficients indicate that renewable energy use negatively impacts CO2 emissions in all countries, and human capital also affects CO2 emissions negatively in all of the countries except Russia. On the other hand, business climate increases CO2 emissions in China, Russia, and South Africa.
The causal relationship among business climate, renewable energy use, human capital, and CO2 emissions in the BRICS countries’ economies between 2000 and 2020 is analysed using the JKS [27] panel causality test, and the findings are reported in Table 11. The test findings point out that the bilateral causal connection among BUSCLIM, RNWEN, HCAP, and CO2 is present. In other words, a reciprocal relationship between business climate, renewable energy, human capital, and CO2 emissions exists.

6. Discussion

Business climate is a significant factor in the decision to start a business or expand business activities. According to this connection, more market-oriented business regulations, fewer procedures to start a business, lower tax and lending rates, and loose labour regulations, which represent a positive business climate, are expected to increase the establishment of companies or the business activities of existing firms. Therefore, a positive business climate can impact CO2 emissions through the channel of economic growth theoretically, because economic growth and CO2 emissions are closely related [98]. However, the interaction between business climate and CO2 emissions can change depending on national environmental policies and ESG practices. Our results indicate that the business climate increases CO2 emissions in China, Russia, and South Africa in the long run because the mean values of the environmental policy stringency index for China, Russia, and South Africa over 2000–2020 are, respectively, 0.84, 0.82, and 0.71 (on a scale from 0, not stringent, to 6, the highest degree of stringency) [99]. In conclusion, a positive business climate, coupled with loose environmental regulations, results in increased CO2 emissions in China, Russia, and South Africa. However, the relationship between business climate and CO2 emissions in Brazil and India is found to be insignificant, which might result from their current business climate and relatively lower level of economic development. The findings of Imran et al. [100] on BRICS countries also support our findings, and our findings are also consistent with the theoretical expectation and the results of Gani and Sharma [32], Rieger [33], and Omri and Afi [34], who revealed a positive relationship between business climate and CO2 emissions. Last, the bidirectional causality between business climate and CO2 emissions is compatible with theoretical considerations, because CO2 emissions can also impact the business climate through labour health, the costs of raw materials, and supply chains.
Renewable energy sources, which emit relatively lower amounts of greenhouse gases emissions than fossil energy sources, are expected to decrease CO2 emissions. According to this connection, a negative effect of renewable energy use on CO2 emissions is theoretically expected. Our results indicate that renewable energy use has a negative effect on CO2 emissions in all BRICS countries in the long run. Therefore, our findings are consistent with the related theoretical considerations and results of Abbas et al. [14], Imran et al. [21], Justice et al. [62], Dogan and Seker [63], Koengkan and Fuinhas [64], Ben Jebli et al. [65], Bayar et al. [66], Petruška et al. [67], Jaforullah and King [69], Ben Jebli and Youssef [70], Khoshnevis Yazdi and Beygi [71], Saidi and Omri [73], Szetela et al. [74], and Nan et al. [75]. However, few studies have investigated the causality between renewable energy use and CO2 emissions. In this context, Ben Jebli et al. [65], Khoshnevis Yazdi and Beygi [71], and Saidi and Omri [73] discovered different causal relationship between the two variables, but our findings are consistent with the results of Saidi and Omri [73]. Therefore, our results together with the limited empirical literature indicate that renewable energy use is also effective to counter environmental degradation as approximated by CO2 emissions in the short term.
Lastly, human capital is one of the main drivers of production and consumption and may impact CO2 emissions through environmental awareness, entrepreneurship, innovation, green and energy efficient technologies, labour productivity, and physical capital investment. But the effect of human capital on CO2 emissions can be changed theoretically based on countries’ own characteristics. Our findings denote that improvements in human capital reduce CO2 emissions in all BRICS countries except Russia in the long run. Our findings might be due to the fact that Brazil, China, India, and South Africa achieved significant progress in human capital, but Russia already had a high human capital during 2000–2020 [29]. In conclusion, our results are consistent with the related theoretical views and the results of [38,39,40,41,42,43,44,76,77,78,79,80,81,82]. Furthermore, our bilateral causality between CO2 emissions and human capital is compatible with the results of Bano et al. [48], Abdouli and Omri [49], and Joof and Zhakanova Isiksal [50].

7. Conclusions, Policy Implications, and Limitations

The world has achieved significant progress in terms of welfare since the Industrial Revolution, but this has been accompanied by noteworthy environmental degradation. Consequently, concerns about environmental problems have intensified since the 1950s, leading researchers and policymakers to focus on factors that can disrupt the environment. This article examines the influence of business climate, renewable energy use, and human capital on CO2 emissions in the BRICS countries’ economies, which are also among the top global CO2 emitters. The study addresses the insufficient number of studies on the nexus between business climate, human capital, and CO2 emissions, despite their critical importance for all economic activities, through causality and cointegration tests that account for cross-sectional dependency and heterogeneity.
The results of the causality test indicate a bidirectional causal relationship among business climate, renewable energy use, human capital, and CO2 emissions. On one hand, business climate, renewable energy use, and human capital have a significant influence on CO2 emissions. On the other hand, CO2 emissions also have a significant impact on business climate, renewable energy use, and human capital. In other words, there exists a feedback interaction among these factors in the short term. In the long-term analysis, improvements in renewable energy use support the decrease in CO2 emissions in all BRICS countries, and improvements in human capital also decrease CO2 emissions in all BRICS countries except Russia. However, the effect of human capital on CO2 emissions is much higher than that of renewable energy use in all BRICS countries’ economies. Lastly, having a positive business climate enhances CO2 emissions in China, India, and Russia, which have loose environmental regulations. On the other hand, the results of the causality test indicate a mutual interaction between business climate, renewable energy use, human capital, and CO2 emissions and support these long-term findings.
Based on the results of our research, three policy recommendations are made to decrease CO2 emissions, as follows:
First, human capital has the largest impact on CO2 emissions when compared with the impacts of renewable energy and business climate because human capital can impact CO2 emissions through multiple channels. Therefore, it is recommended that environmental awareness among individuals should be fostered by education policies in terms of lifelong educational and training programs. All of the countries except Russia can keep decreasing their CO2 emissions by improving their human capital through educational investments.
Secondly, renewable energy use is an effective tool to decrease CO2 emissions in all BRICS countries. Therefore, the clean energy transition should be accelerated to reduce CO2 emissions in all BRICS countries.
Last, business climate is revealed to increase CO2 emissions in China, Russia, and South Africa, which had fewer environmental regulations during 2000–2020. All countries, especially China, Russia, and South Africa, should encourage firms to move towards ESG practices through business climate and environmental policies.
This article has several limitations that could guide future studies. First, the sample is limited to BRICS countries and could be expanded to include developing and developed countries. Secondly, the availability of business climate and CO2 emissions data restricts our analysis to the period between 2000 and 2020. Thirdly, the study investigated the overall effect of human capital, renewable energy use, and business climate on CO2 emissions. Future research could focus on the influence of secondary, tertiary, and vocational education on the interplay between human capital and CO2 emissions.

Author Contributions

Conceptualization, F.H.S., Y.B., G.S. and M.D.; methodology, F.H.S., Y.B. and M.D.; data curation, M.D. and G.S.; writing—original draft preparation, F.H.S., Y.B., G.S. and M.D.; writing—review and editing, F.H.S., Y.B., G.S. and M.D.; supervision, F.H.S. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Data Availability Statement

The original data presented in the study are openly available in UNCTADSTAT and the World Bank’s databases through the links in the references section.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. World Economic Forum. The Global Risks Report 2021. Available online: https://www.weforum.org/publications/the-global-risks-report-2021/ (accessed on 19 July 2023).
  2. United Nations. Conferences | Environment and Sustaainable Development. 2023. Available online: https://www.un.org/en/conferences/environment (accessed on 22 July 2023).
  3. United Nations. The 17 Goals. 2023. Available online: https://sdgs.un.org/goals (accessed on 22 July 2023).
  4. Sach, J.D.; Lafortune, G.; Fuller, G.; Drumm, E. Sustainable Development Report 2023. Available online: https://s3.amazonaws.com/sustainabledevelopment.report/2023/sustainable-development-report-2023.pdf (accessed on 17 May 2024).
  5. Ali, N.; Hu, X.; Hussain, J.; Nilofar, M. Assessing the Environmental Impacts of COVID-19; A Review. Pol. J. Environ. Stud. 2021, 30, 4401–4403. [Google Scholar] [CrossRef]
  6. UNEPFI. Who Cares Wins. 2004. Available online: https://www.unepfi.org/fileadmin/events/2004/stocks/who_cares_wins_global_compact_2004.pdf (accessed on 18 May 2024).
  7. Chen, S.; Song, Y.; Gao, P. Environmental, Social, and Governance (ESG) Performance and Financial Outcomes: Analyzing the Impact of ESG on Financial Performance. J. Environ. Manag. 2023, 345, 118829. [Google Scholar] [CrossRef] [PubMed]
  8. Huiqing, Z.; Jian, H.; Feng, H.; Hongyuan, Z. Determinants of Carbon Dioxide Emissions and Their Peaking Prospect: Evidence from China. Front. Environ. Sci. 2022, 10, 913835. [Google Scholar] [CrossRef]
  9. Daniyal, M.; Tawiah, K.; Qureshi, M.; Haseeb, M.; Asosega, K.A.; Kamal, M.; ur Rehman, M. An Autoregressive Distributed Lag Approach for Estimating the Nexus between CO2 Emissions and Economic Determinants in Pakistan. PLoS ONE 2023, 18, e0285854. [Google Scholar] [CrossRef]
  10. Wahab, S.; Imran, M.; Ahmed, B.; Rahim, S.; Hassan, T. Navigating Environmental Concerns: Unveiling the Role of Economic Growth, Trade, Resources and Institutional Quality on Greenhouse Gas Emissions in OECD Countries. J. Clean. Prod. 2024, 434, 139851. [Google Scholar] [CrossRef]
  11. Bayar, Y.; Smirnov, V.; Danilina, M.; Kabanova, N. Impact of Institutions and Human Capital on CO2 Emissions in EU Transition Economies. Sustainability 2022, 14, 353. [Google Scholar] [CrossRef]
  12. Balogh, J.M.; Jámbor, A. Determinants of CO2 emission: A Global Evidence. Int. J. Energy Econ. Policy 2017, 7, 217–226. [Google Scholar]
  13. 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, 1–27. [Google Scholar] [CrossRef]
  14. Xu, D.; Abbas, S.; Rafique, K.; Ali, N. The Race to Net-zero Emissions: Can Green Technological Innovation and Environmental Regulation be the Potential Pathway to Net-zero Emissions? Technol. Soc. 2023, 75, 102364. [Google Scholar] [CrossRef]
  15. Abbas, S.; Gui, P.; Chen, A.; Ali, N. The Effect of Renewable Energy Development, Market Regulation, and Environmental Innovation on CO2 Emissions in BRICS Countries. Environ. Sci. Pollut. Res. 2022, 29, 59483–59501. [Google Scholar] [CrossRef]
  16. Wen, J.; Ali, W.; Hussain, J.; Khan, N.A.; Hussain, H.; Ali, N.; Akhtar, R. Dynamics between Green Innovation and Environmental Quality: New Insights into South Asian Economies. Econ. Politica 2022, 39, 543–565. [Google Scholar] [CrossRef]
  17. Ali, N.; Phoungthong, K.; Techato KAli, W.; Abbas, S.; Dhanraj, J.A.; Khan, A. FDI, Green Innovation and Environmental Quality Nexus: New Insights from BRICS Economies. Sustainability 2022, 14, 2181. [Google Scholar] [CrossRef]
  18. Jahanger, A.; Awan, A.; Anwar, A.; Adebayo, T.S. Greening the Brazil, Russia, India, China and South Africa (BRICS) Economies: Assessing the Impact of Electricity Consumption, Natural Resources, and Renewable Energy on Environmental Footprint. Nat. Resour. Forum. 2023, 47, 484–503. [Google Scholar] [CrossRef]
  19. Imran, M.; Ali, S.; Shahwan, Y.; Zhang, J.; Al-Swiety, I.A. Analyzing the Effects of Renewable and Nonrenewable Energy Usage and Technological Innovation on Environmental Sustainability: Evidence from QUAD Economies. Sustainability. 2022, 14, 15552. [Google Scholar] [CrossRef]
  20. Rauf, A.; Ali, N.; Sadiq, M.N.; Abid, S.; Kayani, S.A.; Hussain, A. Foreign Direct Investment, Technological Innovations, Energy Use, Economic Growth, and Environmental Sustainability Nexus: New Perspectives in BRICS Economies. Sustainability 2023, 15, 14013. [Google Scholar] [CrossRef]
  21. Hu, X.; Ali, N.; Malik, M.; Hussain, J.; Fengyi, J.; Nilofar, M. Impact of Economic Openness and Innovations on the Environment: A New Look into ASEAN Countries. Pol. J. Environ. Stud. 2021, 30, 3601–3613. [Google Scholar] [CrossRef]
  22. Wang, J.; Jiang, C.; Li, M.; Zhang, S.; Zhang, X. Renewable Energy, Agriculture, and Carbon Dioxide Emissions Nexus: Implications for Sustainable Development in Sub-Saharan African Countries. Sustain. Environ. Res. 2023, 33, 31. [Google Scholar] [CrossRef]
  23. Ye, J.; Xu, W. Carbon Reduction Effect of ESG: Empirical Evidence from Listed Manufacturing Companies in China. Front. Ecol. Evol. 2023, 11, 1311777. [Google Scholar] [CrossRef]
  24. Li, J.; Xu, X. Can ESG Rating Reduce Corporate Carbon Emissions?—An Empirical Study from Chinese Listed Companies. J. Clean. Prod. 2023, 434, 140226. [Google Scholar] [CrossRef]
  25. Ahmed, B.; Wahab, S.; Rahim, S.; Imran, M.; Khan, A.A.; Ageli, M.M. Assessing the Impact of Geopolitical, Economic, and Institutional Factors on China’s Environmental Management in the Russian-Ukraine Conflicting Era. J. Environ. Manag. 2024, 356, 120579. [Google Scholar] [CrossRef]
  26. Westerlund, J.; Edgerton, D.L. A Panel Bootstrap Cointegration Test. Econ. Lett. 2007, 97, 185–190. [Google Scholar] [CrossRef]
  27. Juodis, A.; Karavias, Y.; Sarafidis, V. A Homogeneous Approach to Testing for Granger Non-causality in Heterogeneous Panels. Empir. Econ. 2021, 60, 93–112. [Google Scholar] [CrossRef]
  28. BRICS2023. BRICS and Africa: Partnership for Mutually Accelerated Growth, Sustainable Development and Inclusive Multilateralism. 2023. Available online: https://brics2023.gov.za/ (accessed on 24 July 2023).
  29. UNCTADSTAT. Productive Capacities Index, Annual, 2000–2022. 2023. Available online: https://unctadstat.unctad.org/datacentre/dataviewer/US.PCI (accessed on 17 July 2023).
  30. World Bank. CO2 Emissions (kt). 2023. Available online: https://data.worldbank.org/indicator/EN.ATM.CO2E.KT (accessed on 17 July 2023).
  31. UNDP. Human Development Reports. 2023. Available online: https://hdr.undp.org/data-center/documentation-and-downloads (accessed on 2 August 2023).
  32. Gani, A.; Sharma, B. The Effect of the Business Environment on Pollution. International Trade and Finance Association 19th International Conference Working Papers. 2019. Available online: https://services.bepress.com/cgi/viewcontent.cgi?referer=&httpsredir=1&article=1145&context=itfa (accessed on 1 August 2023).
  33. Rieger, A. Doing Business and Increasing Emissions? An Exploratory Analysis of the Impact of Business Regulation on CO2 Emissions. Hum. Ecol. Rev. 2019, 25, 69–85. [Google Scholar] [CrossRef]
  34. Omri, A.; Afi, H. How can Entrepreneurship and Educational Capital Lead to Environmental Sustainability? Struct. Chang. Econ. Dyn. 2020, 54, 1–10. [Google Scholar] [CrossRef]
  35. Romer, P.M. Endogenous Technological Change. J. Polit. Econ. 1990, 98, S71–S102. [Google Scholar] [CrossRef]
  36. Eriksson, C.; Lindén, J.; Papahristodoulou, C. Human Capital, Innovation, and Growth. Int. J. Econ. Theory 2022, 19, 343–369. [Google Scholar] [CrossRef]
  37. Cervellati, M.; Meyerheim, G.; Sunde, U. Human Capital and the Diffusion of Technology. Econ. Lett. 2023, 226, 111108. [Google Scholar] [CrossRef]
  38. Zafar, M.W.; Zaidi, S.A.H.; Khan, N.R.; Mirza, F.M.; Hou, F.; Kirmani, S.A.A. The Impact of Natural Resources, Human Capital, and Foreign Direct Investment on the Ecological Footprint: The Case of the United States. Resour. Policy 2019, 63, 101428. [Google Scholar] [CrossRef]
  39. Yao, Y.; Ivanovski, K.; Inekwe, J.; Smyth, R. Human Capital and CO2 Emissions in the Long Run. Energy Econ. 2020, 91, 104907. [Google Scholar] [CrossRef]
  40. Rahman, M.M.; Nepal, R.; Alam, K. Impacts of Human Capital, Exports, Economic Growth and Energy Consumption on CO2 Emissions of a Cross-Sectionally Dependent Panel: Evidence from the Newly Industrialized Countries (NICs). Environ. Sci. Policy 2021, 121, 24–36. [Google Scholar] [CrossRef]
  41. Hao, L.N.; Umar, M.; Khan, Z.; Ali, W. Green Growth and Low Carbon Emission in G7 Countries: How Critical the Network of Environmental Taxes, Renewable Energy and Human Capital Is? Sci. Total Environ. 2021, 752, 141853. [Google Scholar] [CrossRef]
  42. Jahanger, A.; Yang, B.; Huang, W.C.; Murshed, M.; Usman, M.; Radulescu, M. Dynamic Linkages between Globalization, Human Capital, and Carbon Dioxide Emissions: Empirical Evidence from Developing Economies. Environ. Dev. Sustain. 2023, 25, 9307–9335. [Google Scholar] [CrossRef]
  43. Adikari, A.P.; Liu, H.; Dissanayake, D.; Ranagalage, M. Human Capital and Carbon Emissions: The Way Forward Reducing Environmental Degradation. Sustainability 2021, 15, 2926. [Google Scholar] [CrossRef]
  44. Zhang, Y.C.; Liu, X.H.; Ullah, A.; Mehmood, U. Effects of Human Capital, Natural Resource, Urbanization, Energy Consumption on Carbon Emissions in the Top Ten Emitter Countries. Econ. Res. Ekon. Istraživanja 2023, 36, 2149589. [Google Scholar] [CrossRef]
  45. Haini, H. Examining the Impact of ICT, Human Capital and Carbon Emissions: Evidence from the ASEAN Economies. Int. Econ. 2021, 166, 116–125. [Google Scholar] [CrossRef]
  46. 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]
  47. Sarkodie, S.A.; Adams, S.; Owusu, P.A.; Leirvik, T.; Ozturk, I. Mitigating Degradation and Emissions in China: The Role of Environmental Sustainability, Human Capital and Renewable Energy. Sci. Total Environ. 2020, 719, 137530. [Google Scholar] [CrossRef]
  48. Bano, S.; Zhao, Y.; Ahmad, A.; Wang, S.; Liu, Y. Identifying the Impacts of Human Capital on Carbon Emissions in Pakistan. J. Clean. Prod. 2018, 183, 1082–1092. [Google Scholar] [CrossRef]
  49. Abdouli, M.; Omri, A. Exploring the Nexus among FDI Inflows, Environmental Quality, Human Capital, and Economic Growth in the Mediterranean Region. J. Knowl. Econ. 2021, 12, 788–810. [Google Scholar] [CrossRef]
  50. Joof, F.; Zhakanova Isiksal, A. Do Human Capital and Export Diversification Decline or Augment CO2 Emissions? Empirical Evidence from the MINT Economies. J. Environ. Account. Manag. 2021, 9, 111–125. [Google Scholar] [CrossRef]
  51. Chandan, H.C. Corruption, Business Climate, and Economic Growth. In Handbook of Research on Global Business Opportunities; Christiansen, B., Ed.; IGI Global: Hershey, PA, USA, 2015; pp. 469–491. [Google Scholar] [CrossRef]
  52. Blackman, A.; Kildegaard, A. Clean technological change in developing-country industrial clusters: Mexican leather tanning. Environ. Econ. Policy Stud. 2010, 12, 115–132. [Google Scholar] [CrossRef]
  53. Kwon, D.-B. Human Capital and Its Measurement. In Proceedings of the 3rd OECD World Forum, Busan, Republic of Korea, 27–30 October 2009. [Google Scholar]
  54. Barro, R.J. Human capital and growth. Am. Econ. Rev. 2001, 91, 12–17. [Google Scholar] [CrossRef]
  55. Grossman, G.M.; Krueger, A.B. Economic Growth and the Environment. Q. J. Econ. 1995, 110, 353–377. [Google Scholar] [CrossRef]
  56. Jahanger, A.; Zaman, U.; Hossain, M.R.; Awan, A. Articulating CO2 emissions limiting roles of nuclear energy and ICT under the EKC hypothesis: An application of non-parametric MMQR approach. Geosci. Front. 2023, 14, 101589. [Google Scholar] [CrossRef]
  57. Alvarado, R.; Deng, Q.; Tillaguango, B.; Méndez, P.; Bravo, D.; Chamba, J.; Alvarado-Lopez, M.; Ahmad, M. Do economic development and human capital decrease non-renewable energy consumption? Evidence for OECD countries. Energy 2021, 215, 119147. [Google Scholar] [CrossRef]
  58. Padhan, H.; Padhang, P.C.; Tiwari, A.K.; Ahmed, R.; Hammoudeh, S. Renewable energy consumption and robust globalization (s) in OECD countries: Do oil, carbon emissions and economic activity matter? Energy Strategy Rev. 2020, 32, 100535. [Google Scholar] [CrossRef]
  59. Magazzino, C.; Mele, M.; Morelli, G. The relationship between renewable energy and economic growth in a time of COVID-19: A machine learning experiment on the Brazilian economy. Sustainability 2021, 13, 1285. [Google Scholar] [CrossRef]
  60. Caruso, G.; de Marcos, I.; Noy, I. Climate Changes Affect Human Capital. CESifo Working Paper. 2023. No. 10374. Available online: https://www.cesifo.org/en/publications/2023/working-paper/climate-changes-affect-human-capital (accessed on 25 July 2023).
  61. IEA. Greenhouse Gas Emissions from Energy Data Explorer 2024. Available online: https://www.iea.org/data-and-statistics/data-tools/greenhouse-gas-emissions-from-energy-data-explorer (accessed on 15 July 2023).
  62. Justice, G.; Nyantakyi, G.; Isaac, S.H. The Effect of Renewable Energy on Carbon Emissions through Globalization. Heliyon 2024, 10, e26894. [Google Scholar] [CrossRef]
  63. Dogan, E.; Seker, F. The Influence of Real Output, Renewable and Non-renewable Energy, Trade and Financial Development on Carbon Emissions in the Top Renewable Energy Countries. Renew. Sustain. Energy Rev. 2016, 60, 1074–1085. [Google Scholar] [CrossRef]
  64. Koengkan, M.; Fuinhas, J.A. The Negative Impact of Renewable Energy Consumption on Carbon Dioxide Emissions: An Empirical Evidence from South American Countries. Rev. Bras. de Energ. Renováveis 2017, 6, 893–914. [Google Scholar] [CrossRef]
  65. Ben Jebli, M.; Ben Youssef, S.; Apergis, N. The Dynamic Linkage between renewable Energy, Tourism, CO2 Emissions, Economic Growth, Foreign Direct Investment, and Trade. Lat. Am. Econ. Rev. 2019, 28, 2. [Google Scholar] [CrossRef]
  66. Bayar, Y.; Gavriletea, M.D.; Sauer, S.; Paun, D. Impact of Municipal Waste Recycling and Renewable Energy Consumption on CO2 Emissions across the European Union (EU) Member Countries. Sustainability 2021, 13, 656. [Google Scholar] [CrossRef]
  67. Petruška, I.; Litavcová, E.; Chovancová, J. Impact of Renewable Energy Sources and Nuclear Energy on CO2 Emissions Reductions—The Case of the EU Countries. Energies 2022, 15, 9563. [Google Scholar] [CrossRef]
  68. Apergis, N.; Payne, J.E.; Menyah, K.; Wolde-Rufael, Y. On the Causal Dynamics between Emissions, Nuclear Energy, Renewable Energy, and Economic Growth. Ecol. Econ. 2010, 69, 2255–2260. [Google Scholar] [CrossRef]
  69. Jaforullah, M.; King, A. Does the Use of Renewable Energy Sources Mitigate CO2 Emissions? A Reassessment of the US Evidence. Energy Econ. 2015, 49, 711–717. [Google Scholar] [CrossRef]
  70. Ben Jebli, M.; Youssef, B.S. Renewable Energy Consumption and Agriculture: Evidence for Cointegration and Granger Causality for Tunisian Economy. Int. J. Sustain. Dev. World Ecol. 2016, 24, 149–158. [Google Scholar] [CrossRef]
  71. Khoshnevis Yazdi, S.; Beygi, E.G. The Dynamic Impact of Renewable Energy Consumption and Financial Development on CO2 Emissions: For Selected African countries. Energy Sources Part B Econ. Plan. Policy 2018, 13, 13–20. [Google Scholar] [CrossRef]
  72. Hasnisah, A.; Azlina, A.A.; Taib, C.M.I.C. The Impact of Renewable Energy Consumption on Carbon Dioxide Emissions: Empirical Evidence from Developing Countries in Asia. Int. J. Energy Econ. Policy 2019, 9, 135–143. [Google Scholar] [CrossRef]
  73. Saidi, K.; Omri, A. The Impact of Renewable Energy on Carbon Emissions and Economic Growth in 15 Major Renewable Energy-consuming Countries. Environ. Res. 2020, 186, 109567. [Google Scholar] [CrossRef]
  74. Szetela, B.; Majewska, A.; Jamroz, P.; Djalilov, B.; Salahodjaev, R. Renewable Energy and CO2 Emissions in Top Natural Resource Rents Depending Countries: The Role of Governance. Front. Energy Res. 2022, 10, 872941. [Google Scholar] [CrossRef]
  75. Nan, Y.; Sun, R.; Mei, H.; Yue, S.; Yuliang, L. Does Renewable Energy Consumption Reduce Energy Ecological Footprint: Evidence from China. Environ. Res. Ecol. 2023, 2, 015003. [Google Scholar] [CrossRef]
  76. Li, P.; Ouyang, Y. The dynamic impacts of financial development and human capital on CO2 emission intensity in China: An ARDL approach. J. Bus. Econ. Manag. 2019, 20, 939–957. [Google Scholar] [CrossRef]
  77. Ahmed, Z.; Zafar, M.W.; Ali, S.; Danish. Linking urbanization, human capital, and the ecological footprint in G7 countries: An empirical analysis. Sustain. Cities Soc. 2020, 55, 102064. [Google Scholar] [CrossRef]
  78. Sharma, G.D.; Shah, M.I.; Shahzad, U.; Jain, M.; Chopra, R. Exploring the nexus between agriculture and greenhouse gas emissions in BIMSTEC region: The role of renewable energy and human capital as moderators. J. Environ. Manag. 2021, 297, 113316. [Google Scholar] [CrossRef] [PubMed]
  79. Iqbal, M.A.; Majeed, M.T.; Luni, T. Human capital, trade openness and CO2 emissions: Evidence from heterogeneous income groups. Pak. J. Commer. Soc. Sci. 2021, 15, 559–585. [Google Scholar]
  80. Mentel, G.; Tarczyński, W.; Azadi, H.; Abdurakmanov, K.; Zakirova, E.; Salahodjaev, R. R&D human capital, renewable energy and CO2 emissions: Evidence from 26 Countries. Energies 2022, 15, 9205. [Google Scholar] [CrossRef]
  81. Khan, M.; Rana, A.T.; Ghardallou, W. FDI and CO2 emissions in developing countries: The role of human capital. Nat. Hazards 2023, 17, 1125–1155. [Google Scholar] [CrossRef]
  82. Pata, U.K.; Caglar, A.E.; Kartal, M.T.; Kılıç Depren, S. Evaluation of the role of clean energy technologies, human capital, urbanization, and income on the environmental quality in the United States. J. Clean. Prod. 2023, 402, 136802. [Google Scholar] [CrossRef]
  83. Xiao, J.; Shen, L.; Du, X. Exploring the effect of human capital on carbon emissions: Evidences from 125 countries. Environ. Sci. Pollut. Res. 2023, 30, 85429–85445. [Google Scholar] [CrossRef]
  84. Ullah, A.; Altay Topcu, B.; Dogan, M.; Imran, M. Exploring the nexus among hydroelectric power generation, financial development, and economic growth: Evidence from the largest 10 hydroelectric power-generating countries. Energy Strategy Rev. 2024, 52, 101339. [Google Scholar] [CrossRef]
  85. Ali, N.; Phoungthong, K.; Khan, A.; Abbas, S.; Dilanchiev, A.; Tariq, S.; Sadiq, M.N. Does FDI foster technological innovations? Empirical evidence from BRICS economies. PLoS ONE 2023, 18, e0282498. [Google Scholar] [CrossRef] [PubMed]
  86. World Bank. CO2 Emissions (Metric Tons Per Capita). 2023. Available online: https://data.worldbank.org/indicator/EN.ATM.CO2E.PC (accessed on 17 July 2023).
  87. World Bank. Renewable Energy Consumption (% of Total Final Energy Consumption). 2023. Available online: https://data.worldbank.org/indicator/EG.FEC.RNEW.ZS (accessed on 17 July 2023).
  88. Breusch, T.S.; Pagan, A.R. The lagrange multiplier test and its applications to model specification tests in econometrics. Rev. Econ. Stud. 1980, 47, 239–253. [Google Scholar] [CrossRef]
  89. Pesaran, M.H.; Ullah, A.; Yamagata, T. A bias-adjusted LM test of error cross-section independence. Econom. J. 2008, 11, 105–127. [Google Scholar] [CrossRef]
  90. Pesaran, M.H. General Diagnostic Tests for Cross Section Dependence in Panels. CESifo Working Paper Series. 2004. No. 1229. Available online: http://ssrn.com/abstract=572504 (accessed on 16 July 2023).
  91. Pesaran, M.H.; Yamagata, T. Testing slope homogeneity in large panels. J. Econom. 2008, 142, 50–93. [Google Scholar] [CrossRef]
  92. Pesaran, M.H. A Simple Panel Unit Root Test in the Presence of Cross-Section Dependence. J. Appl. Econom. 2007, 22, 265–312. [Google Scholar] [CrossRef]
  93. Eberhardt, M.; Bond, S. Cross-Section Dependence in Nonstationary Panel Models: A Novel Estimator, MPRA (Munich Personal RePEc Archive). 2009. Paper No: 17692. Available online: https://mpra.ub.uni-muenchen.de/17692/ (accessed on 27 July 2023).
  94. Granger, C.W.J. Investigating causal relations by econometric models and cross-spectral methods. Econometrica 1969, 37, 424–438. [Google Scholar] [CrossRef]
  95. Dhaene, G.; Jochmans, K. Split-panel Jackknife Estimation of Fixed-effect Models. Rev. Econ. Stud. 2015, 82, 991–1030. [Google Scholar] [CrossRef]
  96. Gujarati, D.N.; Porter, D.C. Basic Econometrics, 5th ed.; McGraw-Hill/Irwin: New York, NY, USA, 2009. [Google Scholar]
  97. Xiao, J.; Juodis, A.; Karavias, Y.; Sarafidis, V.; Ditzen, J. Improved tests for Granger noncausality in panel data. Stata 2023, 23, 230–242. [Google Scholar] [CrossRef]
  98. Mehmood, K.; Hassan, S.T.; Qiu, X.; Ali, S. Comparative analysis of CO2 emissions and economic performance in the United States and China: Navigating sustainable development in the climate change era. Geosci. Front. 2024, 15, 101843. [Google Scholar] [CrossRef]
  99. OECD. Environmental Policy Stringency Index. 2023. Available online: https://stats.oecd.org/Index.aspx?DataSetCode=EPS (accessed on 2 August 2023).
  100. Imran, M.; Alam, M.S.; Jijian, Z.; Ozturk, I.; Wahab, S.; Dogan, M. From resource curse to green growth: Exploring the role of energy utilization and natural resource abundance in economic development. Nat. Resour. Forum 2024. [Google Scholar] [CrossRef]
Figure 1. The methodology for investigating the interaction among renewable energy, business climate, human capital, and CO2 emissions.
Figure 1. The methodology for investigating the interaction among renewable energy, business climate, human capital, and CO2 emissions.
Energies 17 03625 g001
Table 1. A summary of the literature on business climate and CO2 emissions.
Table 1. A summary of the literature on business climate and CO2 emissions.
StudySample; PeriodMethodEffect of Business Climate Indicators on CO2 Emissions
Gani and Sharma [32]A total of 87 developing economies and 20 developed economies; 2003RegressionA negative relationship between the procedures to start a job and CO2 emissions
Rieger [33]A total of 104 developing countries; 2005–2014RegressionPositive
Omri and Afi [34]A total of 32 developing countries; 2001–2015RegressionPositive
Table 2. A summary of the literature on renewable energy CO2 emissions.
Table 2. A summary of the literature on renewable energy CO2 emissions.
StudySample; PeriodMethodEffect of Renewable Energy on Greenhouse Gases/CO2 Emissions
Abbas et al. [15]BRICS countries; 1990–2020MG and PMG estimatorsNegative
Imran et al. [19]US, Japan, Australia, and India; 1991–2021Method of
moments quantile regression
Negative
Justice et al. [62]Ghana; 1990–2020Correlation analysisNegative
Dogan and Seker [63]40 countries with highest renewable energy; 1985–2011Pedroni and LM bootstrap cointegration tests.Negative
Koengkan and Fuinhas [64]10 South American countries; 1980–2012RegressionNegative
Ben Jebli et al. [65]22 Central and South American economies; 1995–2010Pedroni cointegration test and Granger causality testNegative and unidirectional causality from renewable energy to CO2
emissions
Bayar et al. [66]EU countries; 2004–2017Cointegration and causality analysesNegative
Petruška et al. [67]22 European countries;
1992–2019
Cointegration analysisNegative
Apergis, et al. [68]19 developed and developing economies; 1984–2007Vector error correction modelInsignificant
Jaforullah and King [69]USA; 1960–2007VARNegative
Ben Jebli and Youssef [70]Tunisia; 1980–2011Vector error correction modelNegative
Khoshnevis Yazdi and Beygi [71]25 African
countries; 1985–2015
PMG estimator and Granger causality testNegative, but causality differs among the countries
Hasnisah et al. [72]13 Asian developing economies; 1980–2014Pedroni cointegration testInsignificant
Saidi and Omri [73]15 major renewable-energy-consuming countries; 1990–2014Pedroni cointegrations testNegative and bidirectional causality between renewable energy and CO2 emissions
Szetela et al. [74]Top natural-resource-dependant countries; 2000–2015RegressionNegative
Nan et al. [75]China; 2000–2020VAR and quantile regressionNegative
Table 3. A summary of the literature on human capital and CO2 emissions.
Table 3. A summary of the literature on human capital and CO2 emissions.
StudySample; PeriodMethodInfluence of Human Capital on CO2 Emissions
Zafar et al. [38]US; 1970–2015ARDLNegative
Yao et al. [39]20 OECD members; 1870–2014Cointegration and regression analysesNegative
Rahman et al. [40]Newly industrialized economies; 1979–2017CointegrationNegative
Hao et al. [41]G7 economies; 1991–2017CS-ARDLNegative
Jahanger et al. [42] 78 developing countries; 1990–2016RegressionNegative
Adikari et al. [43] Sri Lanka; 1978–2019ARDLNegative
Zhang et al. [44]Top ten global carbon emitters; 1990–2019CointegrationNegative
Haini [45]ASEAN members; 1996–2019RegressionPositive
Zhang et al. [46]Pakistan; 1985–2018ARDLNegative for CO2 emissions but positive for ecological footprint
Sarkodie et al. [47]China; 1961–2016RegressionPositive
Bano et al. [48]Pakistan; 1971–2014Causality analysisBilateral causality between human capital and CO2 emissions.
Abdouli and Omri [49]Mediterranean statesCausality analysisBilateral causality between human capital and CO2 emissions.
Joof and Zhakanova Isiksal [50]MINT states; 1976–2010Causality analysisBilateral causality between human capital and CO2 emissions.
Li and Ouyang [76] China; 1978–2018ARDLPositive in the short-term and negative in the long-term
Ahmed et al. [77] G7 economies; 1971–2014Cointegration and causality analysesNegative and a unilateral causal relationship between human capital and ecological footprint.
Sharma et al. [78]India, Bangladesh, Nepal, Myanmar, Sri Lanka, Thailand; 1985–2019Panel cointegration and quantile regressionNegative
Iqbal et al. [79]126 countries; 1971–2020RegressionNegative
Mentel et al. [80]26 countries; 1995–2015CointegrationNegative
Khan et al. [81]108 developing economies; 2000–2016Panel cointegration and vector error correction modelNegative
Pata et al. [82]US; 1974–2019ARDLNegative
Xiao et al. [83]125 countries; 2000–2019RegressionInverted U-shaped interplay between human capital and CO2 emissions for upper-middle- and high-income countries.
Table 4. Description of variables.
Table 4. Description of variables.
Variable Abbreviation Data DefinitionData Source
CO2CO2 emissions (metric tons per capita)World Bank [86]
BUSCLIMPrivate sector indexUNCTADSTAT [29]
RNWENRenewable energy use (percentage of total final energy use)World Bank [87]
HCAPHuman capital indexUNCTADSTAT [29]
Table 5. Summary indicators of CO2, BUSCLIM, RNWEN, and HCAP.
Table 5. Summary indicators of CO2, BUSCLIM, RNWEN, and HCAP.
CharacteristicCO2BUSCLMRNWENHCAP
Mean5.58951.51722.73945.663
Median6.07749.65314.81048.548
Maximum11.88579.79650.05061.202
Minimum0.88431.5753.18026.861
Std. Dev.3.78311.08116.8809.163
Skewness0.2480.61940.299−0.307
Kurtosis1.5963.0731.417 1.783
Table 6. Results of LM, LMadj, and LM CD tests.
Table 6. Results of LM, LMadj, and LM CD tests.
Cross-Section Dependence TestsTest StatisticsProbability Values
LM17.2890.004
LMadj.19.5370.000
LM CD18.1020.015
Table 7. Delta tilde tests’ results.
Table 7. Delta tilde tests’ results.
TestTest StatisticProbability Values
~ 26.1930.002
~ a d j . 28.5050.011
Table 8. Results of panel CIPS test.
Table 8. Results of panel CIPS test.
VariableLevel1. Level
ConstantConstant + TrendConstantConstant + Trend
CO2−1.167−1.214−5.782 ***−6.731 ***
BUSCLM−1.092−1.188−6.921 ***−7.832 ***
RNWEN−0.947−1.036−8.117 ***−9.104 ***
HCAP−0.884−0.972−7.479 ***−8.693 ***
*** significant at 1%.
Table 9. Westerlund and Edgerton cointegration test results.
Table 9. Westerlund and Edgerton cointegration test results.
ConstantConstant and Trend
LM StatisticAsymptotic p ValueBootstrap p ValueLM StatisticAsymptotic
p Value
Bootstrap
p Value
5.8850.3180.4097.1020.3915.885
Table 10. Cointegration coefficients.
Table 10. Cointegration coefficients.
CountriesBUSCLIMRNWENHCAP
Brazil0.037−0.317 ***−0.103 **
China0.041 ***−0.428 ***−0.093 ***
India0.028−0.297 ***−0.086 ***
Russian Federation0.025 **−0.414 ***−0.097
South Africa0.017 **−0.469 **−0.075 **
Panel0.036 **−0.413 ***−0.084 ***
*** and ** indicate significance at 1% and 5% levels, respectively.
Table 11. JKS Granger non-causality test.
Table 11. JKS Granger non-causality test.
H0HPJ Wald TestProbability Values
BUSCLIM CO219.27550.0000
CO2 BUSCLIM49.06750.0000
RNWEN CO217.41320.0000
CO2 RNWEN34.26130.0000
HCAP CO211.97840.0005
CO2 HCAP3.92190.0477
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Sezgin, F.H.; Bayar, Y.; Sart, G.; Danilina, M. Impact of Renewable Energy, Business Climate, and Human Capital on CO2 Emissions: Empirical Evidence from BRICS Countries. Energies 2024, 17, 3625. https://doi.org/10.3390/en17153625

AMA Style

Sezgin FH, Bayar Y, Sart G, Danilina M. Impact of Renewable Energy, Business Climate, and Human Capital on CO2 Emissions: Empirical Evidence from BRICS Countries. Energies. 2024; 17(15):3625. https://doi.org/10.3390/en17153625

Chicago/Turabian Style

Sezgin, Funda H., Yilmaz Bayar, Gamze Sart, and Marina Danilina. 2024. "Impact of Renewable Energy, Business Climate, and Human Capital on CO2 Emissions: Empirical Evidence from BRICS Countries" Energies 17, no. 15: 3625. https://doi.org/10.3390/en17153625

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop