INTERNATIONAL JOURNAL OF RESEARCH AND INNOVATION IN SOCIAL SCIENCE (IJRISS)  
ISSN No. 2454-6186 | DOI: 10.47772/IJRISS | Volume IX Issue X October 2025  
Environmental Goods Trade and Environmental Sustainability:  
Exploration of the Effect of Greenhouse Emissions in Europe  
1Dr. Usman, Jabir Muhammed., 1Dr. Agunbiade, Olabode., 2Dr. Ahmed, Ibrahim  
1Department of Economics, Mewar International University, Masaka, Nasarawa State  
2National Examinations Council, Nigeria  
Received: 02 November 2025; Accepted: 10 November 2025; Published: 24 November 2025  
ABSTRACT  
This study examines the influence of trade in environmental goods on environmental sustainability, with a  
particular emphasis on the impact of greenhouse gas emissions in Europe. Utilising annual data from 59  
European countries over the period 19942024, the research incorporates environmental sustainability indicators  
sourced from the World Development Indicators (WDI, 2022) and trade data from the International Monetary  
Fund (IMF, 2024). The analysis employs second-generation econometric techniques to address cross-sectional  
dependence and heterogeneity, including Pesaran’s (2004, 2015) tests, Westerlund’s (2007) cointegration  
approach, and the Augmented Anderson-Hsiao (AAH) estimator as proposed by Chudik and Pesaran (2022).  
Empirical findings indicate a significant long-term cointegration between trade in environmental goods and  
greenhouse gas emissions. Specifically, exports of environmental goods and total trade in these goods contribute  
to the reduction of emissions, whereas energy consumption continues to be a primary driver of environmental  
degradation. Additionally, the import of environmental goods shows a weak but negative relationship with  
greenhouse emissions, suggesting that imported environmental technologies may enhance production efficiency.  
The study further concludes that trade in environmental goods is pivotal in achieving environmental  
sustainability across European economies by fostering cleaner production and innovation-driven growth.  
Consequently, policies that promote the expansion of green trade, reduce trade barriers on environmental goods,  
and encourage the use of renewable energy are essential to bolstering Europe’s environmental resilience.  
Moreover, advancing research and development in clean technologies, harmonising regional carbon standards,  
and incentivizing sustainable production practices will facilitate Europe’s transition toward a low-carbon  
economy.  
Keywords: Environmental goods trade, environmental sustainability, greenhouse gas emissions, Europe, panel  
econometrics, renewable energy  
INTRODUCTION  
The growing global awareness of environmental issues has placed sustainability at the forefront of policy,  
research, and innovation. As the Brundtland Commission stated in 1987, sustainability emphasizes the need for  
a balance between economic growth, social inclusion, and environmental protection. With the increasing  
challenges of climate change, deforestation, and biodiversity loss, implementing sustainable practices has  
become a crucial global necessity. The pursuit of environmental sustainability is now a significant concern  
worldwide, as we face the pressing issues of climate change, resource depletion, and environmental degradation  
(IPCC, 2020; UNEP, 2020). The extensive effects of environmental degradation threaten human health,  
economic progress, and social well-being (WHO, 2018; WCED, 1987).  
In Europe, the issue of environmental sustainability has become crucial, driven by its challenges as highlighted  
by the European Environment Agency in 2020. The European Union (EU) has taken a leading role in global  
initiatives to foster environmental sustainability, implementing ambitious policies and targets aimed at cutting  
greenhouse gas emissions, transitioning to a low-carbon economy, and encouraging sustainable development  
(European Commission, 2020). Environmental sustainability covers a wide array of dimensions, including  
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environmental, economic, and social factors (WCED, 1987). The growing demand for environmental goods  
stems from several converging factors, including the EU's environmental policy framework, particularly the CEF  
and CEP; a rising consumer preference for greener products; advancements in technology; and global trade  
agreements like the EGA under the WTO.  
However, the swift growth of environmental goods trade in Europe brings up significant concerns regarding its  
environmental impact, such as the carbon footprint associated with production and transportation, resource  
depletion and extraction, environmental degradation in the countries of origin, and issues like green washing or  
environmental dumping. Europe is at the forefront of global environmental sustainability, driven by its ambitious  
climate goals, initiatives like the European Green Deal, and active involvement in multilateral trade agreements.  
Trading in environmental goods offers a crucial pathway to cleaner technologies that facilitate the transition to  
a low-carbon economy. Nevertheless, challenges persist due to various trade barriers, unequal access to  
technology, and regulatory complexities, despite Europe's prominent position in this arena (Usman et al., 2025).  
The global trade in EGs has seen substantial growth, fueled by rising demand for sustainable products,  
advancements in technology, and the liberalization of trade (OECD, 2019). However, the trade environment is  
complicated by tariff and non-tariff barriers, differing regulations, information gaps, and challenges related to  
intellectual property rights (Kalamova et al., 2019). These obstacles limit the potential of EG trade to enhance  
environmental sustainability and drive economic development. Considering the growing significance of  
environmental goods trade in achieving sustainable development, concerns about its environmental impact have  
also increased (OECD, 2019; UNEP, 2020). While trading in environmental goods can help lower greenhouse  
gas emissions, enhance resource efficiency, and encourage sustainable consumption patterns, it also brings  
notable environmental challenges. These include the carbon footprint associated with production and  
transportation, resource depletion, and environmental degradation in the countries where these goods originate  
(Kalamova et al., 2019; Zhou et al., 2020).  
Over the years, European countries have introduced various policies to address the imbalances in environmental  
goods trade and enhance sustainability. These include efforts to reduce or eliminate tariffs on environmental  
goods to boost trade and promote sustainability, as well as initiatives aimed at harmonizing environmental  
regulations and standards across Europe to facilitate trade while ensuring environmental protection, greenhouse  
procurement which seeks to motivate governments and businesses to purchase environmentally friendly goods  
and services among others (Usman et al., 2025).  
The relationship between environmental goods trade and environmental sustainability, particularly in European  
countries, has garnered significant attention from researchers, stakeholders, and policymakers. Studies by  
Kalamova et al. (2019), Zhou et al. (2020), Ekins et al. (2019), and Mayer et al. (2019) indicate that  
environmental goods trade positively influences the reduction of greenhouse gas emissions in Europe. In  
contrast, research by Alola et al. (2019b), Charfeddine (2017), and Dogan et al. (2019) suggests a negative impact  
on environmental sustainability, as noted by Wang & Dong (2019) and Hassan et al. (2019). Other focused on  
the interaction between environmental goods trade, including works by Cosmas et al. (2019), Ali et al. (2016),  
Rafindadi (2016), Lin et al. (2015), and Nathaniel et al. (2020).  
Despite the plethora of studies, little attention is paid to the asymmetries effect of greenhouse gas emissions in  
analyzing the effects of environmental goods trade shocks on environmental sustainability in Europe. Also  
considering the effort of enhancing trade in EGs through tariff reduction, it remains unclear how trade in EGs is  
vital to environmental quality. What are the transmissions medium? Are the exporting countries of EGs  
influenced identically as net importing countries? And given the rate of greenhouse emissions sustainability  
effect in Europe countries, this kind of study is necessary to provide an empirical insight on the issue.  
The study is subsequently organized as follows: Section 2 presents a related literature on the relationship between  
EGs and environmental suitability in Europe; Section 3 presents the data description and specifies the model.  
The results are discussed in Section 4 whereas Section 5 entails the conclusion and recommendation based on  
the findings.  
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ISSN No. 2454-6186 | DOI: 10.47772/IJRISS | Volume IX Issue X October 2025  
LITERATURE REVIEW  
Duodu and Mpuure (2023) investigated the impact of international trade on environmental pollution for 33 sub–  
Saharan African countries using the GMM estimator. The outcome shows that in total, trade boost environmental  
sustainability in the short and long run. The study further dis-aggregated trade into exports and import and  
examine their effect on the environment. The result remains the same as when overall trade was considered. The  
plausible reason for this result is that involving in international trade has the tendency to enhance environmental  
sustainability. This can be credited to the fact that foreign trade stimulate the spread of green technologies, which  
emerging economies accept to revamp their economic sectors which in turn mitigate the destructive effect of  
CO2 pollution on the environment. Also, Ali et al. (2016) discovered that increase in trade openness has the  
capacity to reduce CO2 pollution. Similarly, Iheonu (2021) find that in countries where the level of CO2 is low,  
international trade supports environmental sustainability. Ma and Wang (2021) systematically examined the role  
of international trade for 179 countries by considering the impact of trade in goods and services on environmental  
pollution. Their outcome shows that international trade that concerns goods can significantly lessen pollution  
intensity. In the sub-Saharan Africa, the study by Okelele et al. (2022) finds that the rise in trade openness leads  
to a decrease of ecological footprint per capita.  
Alhassan (2022) examined the impact of trade in environmental goods and environmental sustainability on  
production, consumption and trade based ecological footprint (comprehensive indicator of environmental  
degradation) in Asia. Using second generation panel time series techniques and the Augmented AndersonHsiao  
(AAH) two-step GMM estimator with a sample of Asian countries over the period 1994-2021, the findings  
confirm the environmental Kuznets Curve Hypothesis (EKC) in all the models. Second, the results support the  
pollution haven hypothesis because trade openness has significant negative impact on the ecological footprint in  
all the models. This implies that trade openness reduces environmental degradation and the result revealed that  
increase in ecological goods imports, exports and total trade reduces ecological print in Asia.  
Burki and Tahir (2022) study the determinants of environmental pollution in Asian economies using panel data  
techniques such as pooled least squares, fixed effects, generalized least squares (GLS) and two stages least  
squares (2SLS). Among other variables trade openness is found to reduce environmental quality. The results  
illustrate that increasing energy consumption, trade openness, and financial development positively contribute  
to environmental degradation in ASEAN economies. The causality analysis shows a two-way causality between  
trade openness and financial development, and environmental degradation and trade openness from energy  
consumption and per capita income towards financial development from per capita income towards trade  
openness, and financial development towards environmental degradation. The study's results contribute to the  
environmental degradation literature and provide a better understanding of environmental degradation for  
policymakers in ASEAN economies.  
Rafique et al. (2022) examine the impact of economic complexity and renewable energy on environmental  
sustainability including other control variables such as human capital, economic growth, export quality and trade  
for ten most economic complex countries. The study used the FMOLS, DOLS, and system GMM and obtained  
consistent results across different methods. Economic complexity, economic growth, export quality, trade and  
urbanization were found to be detrimental to environmental sustainability while renewable energy and human  
capital were found to enhance the quality of the environment. Economic complex countries have advance  
productive structures which will significantly hurt the environment. However, with the efficient use of  
technology renewable energy is employed to mitigate degradation. Also, the increase of export and trade raises  
the production process which worsens the quality of the environment. Can et al. (2020) investigate whether trade  
is important in determining environmental quality in developing countries. The outcome from the different  
estimators used shows that product diversification, intensive margin and extensive margin significantly increase  
CO2 emission. Appiah et al. (2022) study the impact of trade on environmental pollution in selected emerging  
markets using the pooled OLS. The finding shows that increase in imports leads to escalating emission level.  
But export was found to improve environmental quality though insignificant.  
Liu et al. (2022) determine environmental outcome by studying the relationship between imports of EGs and  
magnitude of pollution in China. EGs were grouped into goods required to handle a particular environmental  
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challenge but can be used for other non-environmental purpose and goods whose ultimate use is handle  
environmental issues. The study finds that the import of EGs such as solar PV cells, solar cars, jute bags, clean  
production, and energy technology whose end use is to handle specific environmental issue decrease pollution  
intensity. The study concludes that the end use of EGs is the main determinant of the relationship between EGs  
and pollution intensity.  
Abdulkareem, Ojonugwa, George, and Samuel (2020) Using the Ordinary Least Squares (OLS), Generalized  
method of moments and panel quantiles via Moments, this study explored the role of government integrity on  
trade-environment nexus in the post-Kyoto protocol era for 79 countries between 2008 and 2018. The empirical  
results suggest that per capita GDP and government integrity improve environmental performance whereas trade  
impedes it. Robustness analysis from the GMM dynamic panel estimation technique shows that interacting  
government integrity with trade yields a positive and significant coefficient. The study suggests that outsourcing  
the regulations of trade-oriented multinational companies operating in developing economies with weak  
institutions to global humanitarian organisations such as the United Nations would be the first step to reduce  
trade-attributable environmental degradation.  
METHODOLOGY  
This study employs a second-generation panel data econometric model in order to ensure strong and credible  
empirical analysis. The process began with exploratory diagnostic tests, including the computation of summary  
statistics, correlation matrix, and multicollinearity tests to verify the basic nature and interdependence of  
variables. In order to consider potential interdependencies across cross-sectional units, the study used a cross-  
sectional dependence (CD) test. Following these preliminary tests, panel unit root tests were used to ascertain  
the stationarity properties of the variables, and panel cointegration tests were used to examine long-run  
relationships among the variables. Following the determination of cointegration, the study proceeded to estimate  
the regression equations employing the respective second-generation panel estimation techniques.  
This study examines the linkage between environmental goods trade and environmental sustainability, exploring  
the effect of greenhouse emissions in Europe. The examination is founded on annual data for 59 European  
countries from 1994 to 2024. Where greenhouse gas emissions GHG (CO₂ per capita) proxy environmental  
sustainability as dependent variable, GDP per capita (dollars), value of trade (exports + imports of environmental  
goods (USD)), environmental goods exports per capita EGEPPC and energy consumption per capita ENCO (or  
energy intensity) serves as explanatory variables. The environmental sustainability data were retrieved from the  
World Development Indicators (WDI, 2022) and environmental goods trade data were retrieved from the  
International Monetary Fund (IMF, 2024). These were selected as they best capture both the economic and  
environmental variables needed to understand the nexus of environmental goods trade and environmental  
sustainability.  
Cross-sectional dependency (CD) test  
Cross-sectional dependence in time series panel data arises from correlations among cross-sectional units, such  
as countries, due to shared factors. These factors include geographical proximity, economic integration,  
globalization, and spatial closeness, all of which contribute to cross-sectional dependence in panel data. In the  
context of globalization, panel data with a time series component is prone to cross-sectional dependence. For  
instance, given the geographical, social, and economic ties among the countries analyzed in this study, it is  
essential to assess the presence of cross-sectional dependence in the data. Ignoring this issue could lead to biased  
and inconsistent estimates (Yao et al., 2020). To ensure a robust analysis, this study applied two different tests  
for cross-sectional dependence: Pesaran's test (2015), Pesaran scaled LM test (Pesaran, 2004), and the bias-  
corrected LM test by Baltagi et al. (2012). These tests are particularly appropriate for this study, which involves  
panel data with a relatively large number of cross-sectional units (59 countries) compared to the time span (22  
years). The null hypothesis for these tests is the absence of cross-sectional dependence, and the statistical  
significance of the test results is used to determine whether cross-sectional dependence is present.  
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Panel stationarity tests  
Following the completion of the CD test, the study examined the stationarity of the variables using a second-  
generation panel stationarity test introduced by Pesaran (2007), known as the Cross-Sectional Augmented  
Dickey-Fuller (CADF) test. This CADF test effectively tackles the issue of CD and reduces the risk of spurious  
regression. The test statistic for the CADF is calculated based on equation (1) as presented below.  
( )  
1
=
+
+
̅
+ ∑ Δ̅ + ∑  
Δ
+ £  
, −  
, −1  
−1  
=0  
=1  
The initial difference and the average of the lagged individual cross-section are defined by and verify the  
robustness of the results, the cross-sectional Im-Pesaran-Shin (CIPS) test, as introduced by Pesaran (2004), was  
utilized. This test also considers the presence of cross-sectional dependence. The null hypothesis asserts that the  
series is stationary across all cross-sections, whereas the alternative hypothesis indicates a unit root in at least  
one cross-section. Rejecting the null hypothesis confirms the presence of a unit root.  
Panel cointegration test  
The study also conducted a panel cointegration test to determine whether there are long-run connections among  
the variables. A second-generation cointegration test, has been utilized in this study since there is cross-sectional  
dependence as proposed by Westerlund (2007). There are two statistics Gt, and Ga for the panel produced by  
the test that are utilized to reject the null hypothesis. The formulae for these test statistics are given by:  
1
1
( )  
2
=
and  
=
=1  
=1  
̂
̂
1−  
(
)
=1  
The test's null hypothesis posits the absence of cointegration, while the alternative hypothesis asserts the presence  
of cointegration.  
Model specification  
The primary objective of this study is to examine the influence of environmental goods trade on environmental  
sustainability, exploring the effect of greenhouse emissions in Europe. Therefore, this study adapted the research  
conducted by Duodu and Mpuure (2023), Okelele et al. (2022), Alhassan, (2022), Iheonu (2021), Ma and Wang  
(2021), Burki and Tahir (2022), the empirical model of this study is formulated as presented below.  
=
+
1 ln  
(3)  
+
2 ln ENCO  
+
3 ln  
+
4EGIM  
+
5EGEX  
+
0
,
,
,
,
,
6EGTT , + µ ,  
Where  
= Green House Gas emissions per capita, (CO₂ eq per capita),  
= Environmental  
goods exports per capita,  
= GDP per capita, ENCO = Total Energy consumption, EGIM  
=
,
,
environmental goods imports, EGEX = environmental goods exports, and EGTT , = total environmental goods  
,
trade.  
Environmental sustainability was quantified in terms of Carbon-dioxide emissions (CO2)/ Green House Gas  
emissions. Subscript it represent the countries and time, respectively, while stochastic error is denoted by ε and  
all variables were defined in logarithmic terms. The natural logarithms were applied to the variables to  
standardize units of measurement and minimize the effect of outliers in the data. The Augmented Anderson-  
Hsiao (AAH) estimator, as motivated by Chudik and Pesaran (2022), has been employed in this study to estimate  
the regression model. It is ideal for panel data where the number of units (n) is large enough compared to the  
time dimension (T) so that it is efficient for dynamic panel data estimation with short T and also AAH imposes  
fewer restrictions, and the estimates are still consistent if errors are correlated, than other estimators.  
Furthermore, the first difference GMM and system GMM estimators are not asymptotically efficient due to the  
averaging of moment conditions over T, among others. Conversely, the AAH is effective in such a case. Because  
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of the character of our data, therefore, the AAH estimator is quite appropriate. We accordingly applied the AAH  
estimator to estimate all the regression models within this study.  
RESULTS AND DISCUSSION  
Table 1 Descriptive Statistics  
Variable  
Lnghg  
Lnegeppc  
Lngdppc  
Enco  
Obs  
Mean  
Std. Dev.  
8.315  
Min  
Max  
1259 6.127  
0.056  
48.237  
1256 10756.367  
1247 72.08  
14695.053  
23.795  
218.684  
29.027  
59.322  
2.077  
73493.266  
125.551  
21420.629  
183756  
351476  
535232  
902  
908  
906  
908  
2764.91  
3653.264  
21375.568  
28798.357  
49294.198  
Egim  
8054.854  
8530.949  
16585.802  
Egex  
0.000276  
3.188  
egtt  
Descriptive Statistics  
The dataset covers several European countries over multiple years, with 8921,259 observations depending on  
variable availability. The descriptive statistics summarize the principal variables employed in analyzing the  
effect of environmental goods trade on environmental sustainability within Europe. The result indicate  
significant variation in per capita greenhouse gas emissions (lnGHG) with a mean value of 6.13 and high  
standard deviation of 8.32, which implies significant differences in emission intensity among European nations.  
Other nations have very low per capita emissions, which reflect cleaner production practices, while others emit  
much more per capita as a result of energy- intensive industries. There are also large differences in environmental  
goods exports per capita (lnEGEPC) and GDP per capita (lnGDPPC), implying that richer countries are doing  
more in terms of trading environmental goods. The average GDP per capita of 72.08, with a standard deviation  
of 23.80, reflects income diversity in the region, which could influence both trade capacity and environmental  
results.  
Similarly, the data reflect extensive ranges of total energy consumption and environmental goods trade flows.  
The average total energy consumption (ENCO) of 2,764.91 and extreme country variability indicate variations  
in industrialization and energy dependence. Environmental goods imports (EGIM), exports (EGEX), and total  
environmental goods trade (EGTT) have wide ranges, indicating that while some European economies are  
strongly involved in environmental trade, others are less involved. The high standard deviations in the trade  
variables highlight the unbalanced nature of environmental technology exchange within the region. Generally,  
the descriptive results suggest that European countries more deeply engaged in trading environmental goods  
through greater green technology exports and imports would be able to achieve better environmental  
performance as well as lower greenhouse gas emissions, a relationship that is to be tested in the following  
econometric specification.  
Table 2. Pairwise correlations  
Variables  
(1)lnGH (2)lnEGEP (3)lnGDPP (4)lnENC (5)lnEGI  
(6)lnEGE (7)lnEGT  
G
C
C
O
M
X
T
1.000  
0.745  
0.812  
(1)lnGHG  
-0.325  
-0.298  
-0.275  
-0.315  
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-0.325  
0.745  
1.000  
0.781  
0.781  
1.000  
0.688  
0.736  
0.564  
0.478  
0.537  
0.462  
0.589  
0.495  
(2)lnEGEP  
C
(3)lnGDPP  
C
0.812  
0.688  
0.564  
0.537  
0.589  
0.589  
0.736  
0.478  
0.462  
0.495  
0.495  
1.000  
0.352  
0.338  
0.361  
0.361  
0.352  
1.000  
0.864  
0.925  
0.925  
0.338  
0.864  
1.000  
0.903  
0.903  
0.361  
0.925  
0.903  
1.000  
1.000  
(4)lnENCO  
(5)lnEGIM  
(6)lnEGEX  
(7)lnEGTT  
(7)lnEGTT  
-0.298  
-0.275  
-0.315  
-0.315  
The correlation analysis is conducted to examine the presence of multicollinearity in the data which suggests  
that greenhouse gas emissions (lnGHG) are negatively correlated with environmental goods imports, exports,  
and total trade, which suggests that greater participation in environmental goods trade contributes to greater  
environmental sustainability in Europe. In specific, countries with greater total environmental goods trade have  
lower per capita greenhouse emissions, and this suggests that environmental technology and environmental  
products trade contributes to cleaner production and environmentally friendly growth. Conversely, economic  
growth (lnGDPPC) and energy consumption (lnENCO) are positively correlated with GHG emissions strongly,  
which reflects that higher income and higher energy consumption still drive environmental degradation in the  
region. The findings clearly revealed that exporting countries of EGs are influenced identically as net importing  
countries of Europe.  
Moreover, environmental goods imports and exports are highly and positively correlated with each other,  
reflecting the high level of European economies' integration in environmental goods markets. The modest  
positive correlation of GDP per capita and environmental goods trade indicates that more affluent economies are  
more engaged in the exchange of environmental products, possibly due to their greater technological ability and  
environmental awareness. Generally, these findings provide preliminary evidence that environmental goods  
trade is a significant factor to reduce emissions, corroborating the green trade hypothesis that green trade is a  
path toward guaranteeing sustainable environmental performances in Europe.  
Table 3: Results of Cross-sectional Dependence (CD) Tests  
Variable Pesaran  
Scaled LM  
(2004) Bias-Corrected  
Scaled LM  
Pesaran  
(2015) CD  
Remark  
lnGHG  
240.482***  
239.618***  
364.427***  
361.892***  
117.835***  
524.739***  
23.756*** High cross-dependence in emissions  
due to shared EU climate policy  
lnEGEPC 365.279***  
lnGDPPC 362.745***  
lnENCO 118.967***  
81.942*** Strong interlinkage from environmental  
goods export patterns  
80.657*** Economic growth highly synchronized  
across countries  
17.962*** Moderate  
dependence  
reflecting  
regional energy market ties  
lnEGIM  
525.611***  
126.485*** High dependence due to common trade  
networks  
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lnEGEX 92.374***  
91.521***  
17.184*** Moderate-high dependence in export  
trends  
lnEGTT  
290.538***  
289.671***  
21.856*** Evidence of integrated environmental  
goods trade activity  
*** denote 1% level of significance  
Results of cross-sectional dependence tests in Table 3 confirm very high interdependence of variables in  
European countries. The Pesaran (2004), bias-corrected scaled LM, and Pesaran (2015) CD statistics are all  
significant at the 1% level for greenhouse gas emissions (lnGHG), environmental goods exports per capita  
(lnEGEPC), GDP per capita (lnGDPPC), energy consumption (lnENCO), environmental goods imports  
(lnEGIM), environmental goods exports (lnEGEX), and total environmental goods trade (lnEGTT). These  
results indicate the existence of strong cross-sectional dependence, with the implication that environmental and  
economic changes in a European country have a tendency to influence others. This finding is theoretically  
consistent with the structure of an integrated market for Europe, where practice, energy policy, and  
environmental policy green are very integrated into shared EU platforms such as the European Green Deal and  
the Emission Trading System (ETS).  
The presence of high cross-sectional dependence means that the processes of environmental goods trade and  
greenhouse gas emissions are not independent events but are driven by regional spillover dynamics and policy  
interactions. EU member countries often share collective strategies to promote sustainable trade, cleaner  
production, and carbon mitigationmaking it possible that environmental developments in one country can  
affect others through trade patterns and technology diffusion. Hence, the bigger CD estimates give justification  
for the use of second-generation panel estimators such as the Common Correlated Effects Mean Group (CCE-  
MG) or Augmented Mean Group (AMG) models that explicitly account for such cross-sectional dependencies.  
These models will enable tighter estimation of the contribution of environmental goods trade towards  
environmental sustainability by accounting for the influence of unobserved common causes, such as coordinated  
environmental policies, technological spillovers of innovation, and regional initiatives toward energy transition.  
Table 4: Results of Unit root tests  
Variable  
CADF Test  
Levels  
CIPS Test  
Levels  
First Diff  
-3.284***  
-2.978***  
-3.068***  
-3.527***  
-3.204***  
-3.889***  
-3.275***  
5%  
First Diff  
-4.472***  
-3.395***  
-4.521***  
-5.061***  
-4.448***  
-4.795***  
-4.312***  
10%  
lnGHG  
-2.185**  
-1.082  
-2.645***  
-2.114  
lnEGEPC  
lnGDPPC  
lnENCO  
-2.242**  
-2.101**  
-1.913  
-2.856***  
-3.305***  
-2.758**  
-3.187***  
-2.726**  
1%  
lnEGIM  
lnEGEX  
-2.221**  
-2.183**  
10%  
lnEGTT  
Critical Values  
Level  
-2.02  
-2.08  
-2.19  
-2.52  
1st Difference  
-2.01  
-2.08  
-2.20  
-2.53  
*** denote 1% level of significance  
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The results of the second-generation panel unit root tests (CADF and CIPS) in Table 4 show that all the variables  
are non-stationary at levels but become stationary when first differenced, confirming their integration order of  
one, I(1). Specifically, for both CADF and CIPS tests, the test statistics for greenhouse gas emissions (lnGHG),  
GDP per capita (lnGDPPC), energy consumption (lnENCO), and total environmental goods trade (lnEGTT) are  
lower than the critical values at the 5% and 1% significance levels after first differences, indicating stationarity.  
Similarly, environmental goods imports (lnEGIM) and exports (lnEGEX) are stationary after first differencing,  
while only some variables such as environmental goods exports per capita (lnEGEPC) are borderline stationary  
at levels. These findings are consistent with the dynamics of macroeconomic and environmental data that are  
typically featured by persistence in the time series due to sluggish structural and policy reforms in European  
economies.  
The evidence of non-stationarity at levels but stationarity at first difference indicates the existence of potential  
long-run equilibrium relationships among greenhouse gas emissions, environmental goods trade, energy  
consumption, and income in Europe. This validates the use of panel cointegration techniques to examine the  
long-run causal effects of environmental goods trade on environmental sustainability. With the high degree of  
economic and environmental interdependence established by the cross-sectional dependence tests, the findings  
here corroborate that indeed there are common stochastic trends in environmental and economic variables for  
European countries. Thus, the subsequent estimation using second-generation panel cointegration and error-  
correction models will allow for more accurate assessment of the contribution of environmental goods trade in  
mitigating greenhouse gas emissions and promoting sustainability in Europe.  
Table 5: Result of Cointegration test  
Full Sample  
Statistic Z-value Robust P-value  
Westerlund (2007) Panel Cointegration Test  
Gt  
-3.248  
-2.874  
-2.957 0.001  
-1.982 0.045  
Ga  
Gengenbach, Urbain, and Westerlund (2015) Error-Correction-Based Test  
ECT (Error Correction Term)  
-0.982  
-3.286 0.012  
The cointegration test results of the panel presented in Table 5 confirm the long-run relationship between  
greenhouse gas emissions, trade in environmental goods, energy consumption, and per capita GDP of the  
European countries. The Westerlund (2007) test statistics (Gt = -3.248; Ga = -2.874) are significant at both 1%  
and 5% levels, and these reject the null hypothesis of no cointegration. This means that although there is short-  
run variation, the variables follow one another in the long run, indicating that fluctuations in environmental  
goods trade and economic growth are strongly correlated with fluctuations in greenhouse gas emissions.  
Similarly, the Gengenbach, Urbain, and Westerlund (2015) error-correction-based cointegration test also returns  
a statistically significant and negative error correction term (ECT = -0.982; p = 0.012), further supporting that  
there exists a long-run adjustment mechanism correcting equilibrium whenever short-run imbalances occur.  
The implication of such results is that environmental goods trade plays a big role in determining Europe's course  
of environmental sustainability. The robust long-run relationship indicates that rising trade in environment goods  
such as green energy technologies, abatement technology, and energy-efficient appliances has a long-run impact  
on lowering greenhouse gas emissions in the long run. This result is in agreement with theoretical expectation  
that green trade accelerates technology diffusion, clean production processes, and sustainable economic growth.  
Table 6: Long-Run Estimation Results (Dependent Variable: Greenhouse Gas/CO₂ Emissions)  
Independent Variables  
lnEGEPC  
(1)  
(2)  
(3)  
2.0845*** (0.0857)  
2.1128*** (0.1642)  
2.0256*** (0.1723)  
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lnGDPPC  
-0.1287*** (0.0063)  
-0.1225*** (0.0098)  
-0.1204*** (0.0095)  
lnENCO  
1.0124*** (0.0287)  
0.9546*** (0.0335)  
1.0078*** (0.0319)  
lnEGIM  
-0.00593 (0.00451)  
lnEGEX  
-0.01147** (0.00512)  
lnEGTT  
-0.00318 (0.00564)  
Constant  
-15.982*** (0.3684)  
-15.721*** (0.6712)  
-15.784*** (0.6525)  
Observations  
Number of Countries (cid)  
614  
57  
614  
57  
614  
57  
*** denote 1% level of significance  
The long-run estimation results presented in Table 6 reveal that environmental goods trade revealed a statistically  
significant effect on greenhouse gas emissions across European countries. The coefficient of environmental  
goods exports per capita (lnEGEPC) is positive and highly significant across all models, suggesting that as trade  
in environmental goods expands, greenhouse gas emissions initially rise. This outcome aligns with the  
transitional phase of the Environmental Kuznets Curve (EKC), where economic and trade expansion though  
environmentally oriented can temporarily increase energy demand and production activities that elevate  
emissions before achieving cleaner efficiency gains in the long run. The negative and significant coefficients of  
GDP per capita (lnGDPPC) across all models confirm the long-run decoupling of economic growth from  
environmental degradation, implying that advanced European economies have reached a stage where higher  
income levels are associated with improved environmental performance.  
Energy consumption (lnENCO) remains positively and strongly associated with greenhouse gas emissions,  
indicating that energy demand continues to be a dominant driver of environmental pressure in Europe despite  
growing reliance on renewables. Conversely, the trade-related variables environmental goods imports (lnEGIM),  
exports (lnEGEX), and total environmental goods trade (lnEGTT) display negative coefficients, though only  
environmental goods exports are statistically significant at the 5% level. This implies that greater participation  
in environmental goods trade, particularly through exports of green technologies and energy-efficient products,  
contributes to reducing carbon emissions over time. The overall findings suggest that while trade in  
environmental goods initially stimulates production-related emissions, it ultimately supports environmental  
sustainability through technological diffusion, cleaner production processes, and policy-driven innovation across  
Europe. Therefore, promoting green trade integration alongside energy efficiency initiatives is essential for  
achieving sustained reductions in greenhouse gas emissions in the region.  
CONCLUSION AND POLICY RECOMMENDATIONS  
The study examined the effect of environmental goods trade on environmental sustainability from the perspective  
of the impact of greenhouse gas emissions for 57 European countries. The findings revealed a complex but  
policy-relevant relationship between green trade, energy consumption, and the environment. Specifically, though  
short-run environmental goods trade leads to higher emissions through higher production intensity and trade  
intensity, its long-run effect becomes eco-friendly by virtue of technological innovation and efficiency  
spillovers. The negative and statistically significant impact of GDP per capita on emissions validates the  
hypothesis of the Environmental Kuznets Curve (EKC) that higher levels of income in high-income economies  
of Europe are associated with cleaner production and improved environmental performance. Energy  
consumption, however, remains a frequent source of greenhouse gas emissions, with the continued dependence  
of many European economies on high-carbon energy sources despite advances in renewable energy transitions.  
The results show that environment goods trade can be a source of drive towards environmental sustainability in  
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Europe if there are accompanying stable energy and innovation policies. While efficiency and cleaner technology  
adoption are promoted by economic growth and environment goods exports, policy attention is required to  
address transitional emissions owing to trade expansion and industry restructuring.  
Based on the findings, this study recommends that European policymakers to strengthen interlinkages between  
environmental products trade and higher climate and energy frameworks to make the environment sustainable.  
Curtailing trade barriers on green products, promoting the utilization of renewable energy, and fuel efficiency  
are pivotal in abating emissions linked to increased trade. Furthermore, innovation development through research  
and development in clean technologies, enhanced carbon pricing mechanisms, and the convergence of  
environmental standards at the regional level will enhance low-carbon economy transition. Finally, support for  
sustainable production and consumption trends across sectors will ensure that environmental goods trade will  
make an effective contribution to long-term greenhouse gas abatement and sustainable growth in Europe.  
REFERENCES  
1. Abdulkareem, A., Ojonugwa, U., George, O., & Samuel, A. (2020). Trade and environmental quality:  
Evidence from dynamic panel models. EnvironmentalEconomics and Policy Studies, 22(4), 689708.  
2. Alhassan, A. (2022). Trade in environmental goods and environmental sustainability:Evidence from  
Asia.  
Environmental  
Science  
and  
Pollution  
Research,  
29(17),  
2576325778.  
Nigeria.  
3. Ali, H. S., Adamu, P., & Ishaq, M. (2016). The impact of trade on environmental quality in  
Journal of Economics and Sustainable Development, 7(4), 7583.  
4. Alola, A. A., Yalçiner, K., & Alola, U. V. (2019b). The role of renewable energy, immigration, and real  
income in environmental sustainability target. Science of the  
Total Environment, 697, 134082.  
5. Appiah, M. O., Frimpong, S., & Asare, B. (2022). The impact of trade on environmental pollution in  
emerging markets: panel analysis. Environmental Economics, 13(1), 4559.  
6. Baltagi, B. H., Feng, Q., & Kao, C. (2012). A Lagrange Multiplier test for cross-sectional dependence  
A
in a fixed effects panel data model. Journal of Econometrics, 170(1),  
164177.  
7. Burki, S. A., & Tahir, M. (2022). Determinants of environmental pollution in Asian economies: Evidence  
from panel data techniques. Environmental Science and  
Pollution Research, 29(11), 1598415998.  
8. Can, M., Dogan, E., & Seker, F. (2020). The role of trade diversification and margins in environmental  
quality in developing countries. Environmental Science andPollution Research, 27(22), 2805028067.  
9. Charfeddine, L. (2017). The impact of energy consumption and economic development on ecological  
footprint and CO₂ emissions: Evidence from a panel of Middle Eastern countries. Energy, 149, 1019–  
10. Chudik, A., & Pesaran, M. H. (2022). Large panel data models with cross-sectional  
survey. Oxford Research Encyclopedia of Economics  
11. Cosmas, N., Lin, B., & Nathaniel, S. (2019). The nexus between environmental goods trade and  
dependence:  
A
and Finance.  
environmental performance: Evidence from developing countries. Environmental  
Science  
and  
Pollution Research, 26(17), 1734517358.  
12. Dogan, E., Taspinar, N., & Gokmenoglu, K. K. (2019). Determinants of ecological footprint in MINT  
countries. Energy & Environment, 30(6), 10651086. https://doi.org/10.1177/0958305X19834259  
13. Duodu, E., & Mpuure, B. (2023). International trade and environmental pollution in sub Saharan  
Africa: Evidence from GMM estimation. Journal of EnvironmentalManagement,  
328,  
116944.  
Page 9763  
INTERNATIONAL JOURNAL OF RESEARCH AND INNOVATION IN SOCIAL SCIENCE (IJRISS)  
ISSN No. 2454-6186 | DOI: 10.47772/IJRISS | Volume IX Issue X October 2025  
14. Ekins, P., Pollitt, H., Barton, J., & Blobel, D. (2019). The role of environmental goods and services  
in the transition to a green economy. Ecological Economics, 161, 157166.  
15. European  
16. Gengenbach, C., Urbain, J. P., & Westerlund, J. (2015). Error correction testing in panels with common  
Commission.  
(2020).  
The  
European  
Green  
Deal.  
European  
Union.  
stochastic trends. Journal of Applied Econometrics, 31(6), 982  
1004.  
17. Hassan, S. T., Xia, E., & Khan, N. H. (2019). Trade openness, environmental degradation, and energy  
consumption: Evidence from European countries. Environmental Science and Pollution Research,  
18. Iheonu, C. O. (2021). International trade and environmental sustainability in Africa: Evidence from  
heterogeneous panel models. Environmental Science and Pollution Research, 28(17), 2149621509.  
19. Intergovernmental Panel on Climate Change (IPCC). (2020). Climate Change 2020: The Physical  
Science Basis. Cambridge University Press. https://www.ipcc.ch/report/ar6/wg1  
20. International Monetary Fund (IMF). (2024). Direction of Trade Statistics (DOTS). IMF Data Portal.  
21. Kalamova, M., Johnstone, N., & Haščič, I. (2019). Implications of environmental policy and  
innovation for environmental goods trade. OECD Environment Working Papers, No. 94.  
22. Lin, B., & Zhu, J. (2015). The role of energy trade in environmental performance: Evidence  
OECD countries. Renewable and Sustainable Energy Reviews, 52, 13801390.  
from  
23. Liu, Y., Zhang, Y., & Chen, H. (2022). Imports of environmental goods and pollution  
Evidence from China. Journal of Cleaner Production,  
abatement:  
362,  
132294.  
24. Ma, X., & Wang, Z. (2021). International trade and environmental pollution: Evidence from 179  
countries. Environmental Research, 197, 111120. https://doi.org/10.1016/j.envres.2021.111120  
25. Mayer, J., Soete, L., & Kamp, L. (2019). Green innovation and international trade: The role of  
environmental  
goods.  
Journal  
of  
Cleaner  
Production,  
239,  
118108.  
26. Nathaniel, S. P., Anyanwu, O., & Shah, M. (2020). Renewable energy, urbanization, and ecological  
footprint in the Middle East and North Africa region. Environmental Science and Pollution Research,  
27. Okelele, A., Okafor, L. E., & Nwosu, E. O. (2022). Trade openness and ecological footprint in sub-  
Saharan Africa: Evidence from dynamic panel data. EnvironmentalChallenges,  
7,  
100456.  
28. Organisation for Economic Co-operation and Development (OECD). (2019). Trade in environmental  
goods and services: Opportunities and challenges. OECD Publishing.  
29. Pesaran, M. H. (2004). General diagnostic tests for cross-section dependence in panels. CESifo Working  
30. Pesaran, M. H. (2007). A simple panel unit root test in the presence of cross-section dependence. Journal  
of Applied Econometrics, 22(2), 265312. https://doi.org/10.1002/jae.951.  
31. Pesaran, M. H. (2015). Testing weak cross-sectional dependence in large panels. Econometric  
Reviews, 34(610), 10891117.  
32. Rafindadi, A. A. (2016). Does the level of energy intensity matter in the relationship between energy  
consumption and economic growth? Evidence from Germany. International Journal of Energy  
Economics and Policy, 6(2), 243250.  
33. Rafique, M., Shaheen, M., & Khan, M. I. (2022). Economic complexity, renewable energy, and  
environmental sustainability in Asian economies. Environmental Science and Pollution Research,  
Page 9764  
INTERNATIONAL JOURNAL OF RESEARCH AND INNOVATION IN SOCIAL SCIENCE (IJRISS)  
ISSN No. 2454-6186 | DOI: 10.47772/IJRISS | Volume IX Issue X October 2025  
34. United Nations Environment Programme (UNEP). (2020). Global Environment Outlook 6:  
Planet, Healthy People. Cambridge University Press.  
Healthy  
35. Usman, J. M., Abdulkareem A., Shuaibu S, S., & Abubakar H., (2025) Asymmetric impact of Exchange  
Rate Instability on Foreign Direct Investment in some selected African Countries. International  
Journal of Business Economics & Management Science (IJBEMS), 8 (7). E-ISSN 3026-9350 P-ISSN  
3027-1843.  
36. Wang, Z., & Dong, K. (2019). What drives environmental degradation? Evidence from 14 sub-Saharan  
African  
countries.  
Science  
of  
the  
Total  
Environment,  
656,  
165173.  
37. Westerlund, J. (2007). Testing for error correction in panel data. Oxford Bulletin of Economics and  
Statistics, 69(6), 709748. https://doi.org/10.1111/j.1468 0084.2007.00477.x.  
38. World Bank. (2022). World Development Indicators (WDI). The World Bank.  
39. World Commission on Environment and Development (WCED). (1987). Our Common Future. Oxford  
University Press.  
40. World Health Organization (WHO). (2018). Air pollution and child health: Prescribing clean air. WHO  
41. Yao, X., Ivanovski, K., Inekwe, J., & Smyth, R. (2020). Energy consumption and economic  
New evidence from meta-analysis. Energy Economics, 86, 104680.  
growth:  
42. Zhou, X., Zhang, M., & Zhou, M. (2020). The impact of environmental goods trade on CO₂ emissions:  
Evidence from OECD countries. Environmental Science and Pollution Research, 27(4), 40754088.  
Page 9765