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Article

Development of an Auxiliary Indicator for Improving the Rationality and Reliability of the National-Level Carbon Productivity Indicator

by
Jong Hyo Lee
1,
Hong Yoon Kang
1,* and
Yong Woo Hwang
2
1
Program in Circular Economy Environmental System, Inha University, 100, Inha-ro, Michuhol-gu, Incheon 22212, Republic of Korea
2
Department of Environmental Engineering, Inha University, 100, Inha-ro, Michuhol-gu, Incheon 22212, Republic of Korea
*
Author to whom correspondence should be addressed.
Energies 2024, 17(15), 3831; https://doi.org/10.3390/en17153831
Submission received: 15 July 2024 / Revised: 28 July 2024 / Accepted: 29 July 2024 / Published: 3 August 2024
(This article belongs to the Collection Energy Use Efficiency)

Abstract

:
Global attention to climate change has surged since the advent of the Paris Agreement, intensifying the importance of measuring and managing carbon productivity indicators on a national level. Nevertheless, concerns persist regarding the reliability of such measurements because of inherent discrepancies in implementing and operating national-level carbon productivity indicators, coupled with their inherent uncertainty. This study proposes a multiple regression model to address these issues aimed at refining national-level carbon productivity indicator metrics, accounting for factors such as the gross domestic product and total greenhouse gas emissions by sectors. The objective was to offer insights into enhancing and effectively utilizing current indicators, enabling a more nuanced interpretation of the variation in the carbon productivity indicators across diverse industrial landscapes. This study showed that adjustments of the carbon productivity metrics reflect disparities in emissions across industrial structures, with countries characterized by high emissions from non-service industries showing improving trends. In addition, this paper proposes an auxiliary indicator estimating method for carbon productivity that, when utilized with current methodologies, is more usable to interpret productivity indicators within the context of varying industrial compositions across OECD countries. Moreover, by elucidating the nuances of industrial structures, this study advocates for more sophisticated approaches to interpreting and managing the productivity indicators tailored to the unique economic landscape of each country. Nevertheless, the limitations stemming from data availability underscore the need for further research, particularly in refining the national-level carbon resource productivity indicators analyses and exploring the thematic productivity variations in greater depth. By addressing these gaps, future studies will contribute to a more comprehensive understanding of national-level carbon resource productivity indicators dynamics and reveal targeted strategies for sustainable development.

1. Introduction

Human civilization has developed at the expense of the global environment, leading to widespread destruction and negative impacts. Governments and international organizations are exploring various strategies for sustainable development in response to rapid population growth and increasing issues of environmental pollution and resource depletion. Two prominent international strategies are the transitions to a circular economy and a green economy [1,2]. These strategies are focused on how the changes in global environmental management and economic strategies affect regional economies and, ultimately, the achievement of sustainable development goals. This topic is a crucial agenda for policymakers worldwide [3,4].
In particular, global interest in climate change has surged since the signing of the Paris Agreement in 2015, emphasizing the importance of calculating and managing carbon productivity indicators at the national level. Monitoring and evaluating the value-added generated relative to the greenhouse gas emissions of a country provides crucial insights for policymakers, aiding in setting the priorities from macroeconomic and microeconomic perspectives [5,6,7].
The Republic of Korea also strives to enhance the usability of carbon productivity indicators in line with global trends. Significant capital is being invested in R&D for technology and process innovations at the business level, in facility construction to increase the value-added relative to greenhouse gas emissions, and in businesses within the circular economy or those promoting carbon neutrality, such as remanufacturing [8]. Efforts are being made to calculate carbon productivity indicators more precisely at the national and regional levels, facilitating more rational comparisons and analyses between countries.
Generally, the national-level carbon productivity is calculated as the gross domestic product (GDP) divided by the total greenhouse gas emissions (TGEs). The result expresses the value-added generated per ton of CO2-equivalent greenhouse gas emissions, measured in USD/ton CO2-eq. On the other hand, this method cannot account for the characteristics of the industries that comprise the economy of a country in detail, potentially distorting the interpretation of the carbon productivity indicator of that country. For example, although the TGEs vary according to the primary, secondary, and tertiary industries, GDP measures the final products and the total value-added of services. Thus, the carbon productivity indicator can be structurally biased, either advantageous or disadvantageous, depending on the industrial structure of each country.
Given the broad nature of the GDP and TGEs indicators, the current carbon productivity indicator cannot consider the detailed properties of greenhouse gas emission sources according to industry. For example, the concrete industry in Canada [9], the metal industry in China [10], and the industrial growth trends in Pakistan [11] cannot be efficient in terms of carbon productivity compared to other industries. The impact of specific industries on carbon productivity varies significantly according to country or region, with high greenhouse gas-emitting industries lowering carbon productivity at the national or regional levels [12].
In light of these issues, this study designed an auxiliary indicator to complement the current national carbon productivity indicator by considering industry-specific greenhouse gas emissions. This will provide a more reasonable interpretation of carbon productivity, reflecting the differences in the industrial structure of each country. This paper proposes ways to improve and utilize the current national carbon productivity indicator and suggests using auxiliary indicators that consider the industrial structure of each country to enhance the interpretation and management of carbon productivity indicators.

2. Research Background

Previous studies reported that national-level productivity indicators related to the environment, such as GDP and the domestic material consumption (DMC), can lead to incorrect interpretations because of the failure to account for the industrial structure of each country and the role of energy and resource use in greenhouse gas emissions. The current indicator, calculated by simply dividing the GDP by total greenhouse gas emissions, has limitations in reflecting the productivity of a country in environmental terms [13,14,15,16]. Furthermore, although TGEs statistics are useful for understanding economic drivers and predicting future trends, they cannot adequately explain the value-added generated within the external economy because of the TGEs in a specific country [13,17,18,19,20,21].
Furthermore, the national-level carbon productivity results using these statistics can be distorted if greenhouse gas emissions are outside the calculation scope. For example, when a developed country relocates a greenhouse-gas-intensive industry to a developing country, the TGEs of the developed country decrease, which should be reflected in the carbon productivity calculation of the developed country through a separate adjustment process [22].

3. Disparity between the National-Level Carbon Productivity Indicators and Per Capita Greenhouse Gas Emissions

According to OECD Data Explorer (https://data-explorer.oecd.org/, accessed on 31 July 2024) on GDP and TGEs [23], Korea’s average per capita greenhouse gas emissions in 2019 was 13.5 tons CO2-eq., the sixth highest among 38 OECD countries and over 40% higher than the OECD average of 9.5 tons CO2-eq. Australia had the highest per capita emissions at 21.9 tons CO2-eq., approximately 1.6 times more than Korea. The United States and Canada followed, with 20.0 and 19.2 tons CO2-eq. per capita emissions, respectively. In contrast, Japan, with a high manufacturing sector similar to Korea, had per capita emissions of 9.6 tons, ranking 14th among OECD countries and approximately 70% of Korea’s emissions. Costa Rica had the lowest per capita emissions at 1.6 tons CO2-eq., followed by Colombia with 3.6 tons CO2-eq. and Sweden with 4.9 tons CO2-eq.
By contrast, the carbon productivity indicator (GDP/TGEs) showed different results from per capita emissions. In 2019, Korea generated an average value-added of 2355.1 USD/ton CO2-eq., approximately half of the OECD average of 4490.0 USD/ton CO2-eq., ranking 32nd out of 38 OECD countries. Switzerland had the highest carbon productivity, producing 15,524.2 USD/ton CO2-eq., approximately 6.6 times higher than Korea. Sweden and Norway followed, with 10,549.5 and 8021.1 USD/ton CO2-eq., respectively. Japan ranked 19th with 4234.3 USD/ton CO2-eq., approximately 1.8 times higher than Korea. Turkey had the lowest carbon productivity at 1493.8 USD/ton CO2-eq., approximately one-tenth of Switzerland, followed by Poland with 1542.6 USD/ton CO2-eq. and Mexico with 1722.7 USD/ton CO2-eq.
These disparities highlight the need to improve the rationality and validity of the current carbon productivity indicator through additional formula design or to use auxiliary indicators for relative comparison. The GDP/TGEs indicator tends to overestimate or underestimate certain countries by not considering their industrial and geographical characteristics. For example, Luxembourg’s average per capita greenhouse gas emissions were 17.3 tons CO2-eq., approximately three times higher than Turkey’s. On the other hand, Luxembourg’s value-added creation per unit of greenhouse gas emissions was 6501.5 USD/ton CO2-eq., approximately 4.4 times higher than Turkey’s. Despite the higher per capita emissions, Luxembourg, with a service industry focus and relatively high indirect greenhouse gas emissions, generates significantly more value-added than greenhouse gas emissions (Table 1).
These trends and limitations indicate that it is necessary to improve the current indicator to ensure its rationality and validity through additional formula design or using auxiliary indicators for relative comparison. This study suggests developing auxiliary indicators that consider the industrial structure and resource value differences of each country by closely analyzing the trends and relationships between the value-added generated and the sources of value-added creation or the factors accompanying it.

4. Research Methods

The existing national carbon productivity indicator is calculated by dividing the GDP by total greenhouse gas emissions (GDP/TGEs), indicating the economic value-added generated per ton of greenhouse gas emitted. This study examined the extent of the advantages or disadvantages of this calculation due to differences in industrial and economic structures and other factors among countries.
This study conducted multiple regression analyses to identify these disparities, considering the value-added generated from greenhouse gas emissions by the service and non-service sectors. The OECD countries’ GDP and TGEs statistics from 2017 to 2019 were used as the data sources.
The scope of research ensures data integrity and an appropriate sample size. Although the GDP data are available for all timeseries data until 2022, the TGEs data lack completeness beyond 2019. Therefore, the most recent complete data set available from 2019, along with the data from 2017 and 2018, provided 114 samples for analysis, meeting the requirements for multiple regression analysis.
Previous studies and the data presented in this research show that the value-added compared to greenhouse gas emissions is lower in non-service industries than in service industries.
Cross-analysis between GDP and TGEs statistics according to the industries revealed Spearman correlation coefficients of 0.444 for the non-service industry and 0.714 for the service industry, respectively. Hence, a moderate positive correlation exists between GDP and TGEs for the non-service industry and a very strong positive correlation exists for the service industry. The significance probabilities were all p < 0.001, indicating a clear statistical basis for the interaction between the variables (Table 2).
Therefore, this study used the OECD real GDP (base year 2015) and TGEs statistics (excluding LULUCF) by country and industry to design a regression model. This model derives the adjusted carbon productivity (adjCP) as a dependent variable and uses the value-added created by industry—where GDP1st+2nd represents the non-service industry GDP and GDP3rd represents the service industry GDP—versus greenhouse gas emissions by industry—where GHGs1st+2nd represents the non-service industry greenhouse gas emissions and GHGs3rd represents the service industry greenhouse gas emissions—as independent variables ( G D P 1 s t + 2 n d G H G s 1 s t + 2 n d and G D P 3 r d G H G s 3 r d , respectively). Multiple regression analysis was then performed based on this model.
The carbon productivity is the value-added created per 1 kg CO2-eq. of greenhouse gas emissions. The mathematical structure of the regression model is expressed as Equation (1).
a d j C P = β n s e v G H G s G D P 1 s t + 2 n d G H G s 1 s t + 2 n d + β s e v G H G s G D P 3 r d G H G s 3 r d + c G H G s
GDP1st+2ndthe sum of the GDP from the primary and secondary industriesGDP3rdthe GDP of the tertiary industry
GHGs1st+2ndthe sum of total greenhouse gas emissions from the primary and secondary industriesGHGs3rdthe total greenhouse gas emissions from the tertiary industry
βnsevGHGsthe carbon productivity determination coefficient of the non-service industryβsevGHGsthe carbon productivity determination coefficient of the service industry
adjCPadjusted carbon productivitycGHGsthe carbon productivity constant

5. Results

This study performed multiple regression analyses with GDP and TGEs statistics from OECD data [23] to adjust the carbon productivity of 38 OECD countries, using carbon productivity by industry as the independent variable. The explanatory power of the model was very high, with R2 = 0.909 and adjusted R2 = 0.907. In addition, the difference between R2 and adjusted R2 was less than 0.1%, indicating sufficient validity (Table 3).
The regression equation derived based on the explanatory power of the model was a d j C P = 0.732 · G D P 1 s t + 2 n d G H G s 1 s t + 2 n d + 0.367 · G D P 3 r d G H G s 3 r d 0.368 , and the variance inflation factor (VIF) was 1.362, indicating no multicollinearity issues among the variables (Table 4).
The sample distribution was normal (Figure 1). The normal P–P plot of the regression standardized residuals also showed significant convergence to the regression line (Figure 2). Similarly, the partial regression plots for the variables G D P 1 s t + 2 n d G H G s 1 s t + 2 n d and G D P 3 r d G H G s 3 r d indicated that the samples of the variables that make up the regression equation were linear at a significant level (Figure 3 and Figure 4).
As a result of re-estimating carbon productivity using the coefficients derived from regression analysis, the countries with the greatest improvement in carbon productivity were Korea, Estonia, Israel, and Australia. Korea’s carbon productivity increased from 2337.5 USD/ton CO2-eq., ranking 31 out of 38 OECD countries, to 3996.0 USD/ton CO2-eq., approximately a 71.0% improvement, moving up 13 places to 18th. Similarly, Estonia’s carbon productivity increased from 1651.8 USD/ton CO2-eq., ranking 35, to 2525.3 USD/ton CO2-eq., approximately a 52.9% improvement, moving up seven places to 28th. Israel’s carbon productivity increased from 4832.7 USD/ton CO2-eq., ranking 13, to 6460.1 USD/ton CO2-eq., approximately a 33.7% improvement, moving up to sixth. Australia’s carbon productivity increased from 2531.8 USD/ton CO2-eq., ranking 27, to 3360.7 USD/ton CO2-eq., approximately a 32.7% improvement, moving up five places to 22nd.
On the other hand, the countries with the greatest decline in carbon productivity were Luxembourg, Latvia, France, and the United Kingdom. Luxembourg’s carbon productivity decreased from 6542.6 USD/ton CO2-eq., ranking 6, to 4543.5 USD/ton CO2-eq., approximately a 30.6% decrease, falling 10 places to 16th. Latvia’s carbon productivity decreased from 2989.4 USD/ton CO2-eq., ranking 22, to 2443.9 USD/ton CO2-eq., a decrease of approximately 18.2%, falling eight places. France’s carbon productivity decreased from 6018.6 USD/ton CO2-eq., ranking eight, to 5006.6 USD/ton CO2-eq., approximately a 16.8% decrease, falling three places. The carbon productivity of the UK decreased from 6027.7 USD/ton CO2-eq. to 5047.0 USD/ton CO2-eq., approximately a 16.3% decrease, also falling three places (Table 5).
Regarding a carbon productivity correction, an improvement or decline in carbon productivity reflects the adjustments in the current estimation method. The adjusted carbon productivity in this study does not mean the actual carbon productivity but rather the current carbon productivity indicator. The adjusted carbon productivity indicator designed in this study highlights the discrepancies and adjusts for factors that might underestimate the carbon productivity of a country.
The carbon productivity adjustment results can be summarized as follows.
Korea, Estonia, Israel, and Australia, where the carbon productivity improved the most, were three representative countries where the carbon productivity in non-service industries significantly reduced the overall carbon productivity of the country. The change could be identified more clearly when the existing carbon productivity was exponentiated.
In this study, when industrial productivity is exponentiated based on country-level carbon productivity, a positive number can be interpreted as an industry group that increases the carbon productivity of a country, a negative number can be interpreted as an industry group that decreases carbon productivity, and the size of the absolute value represents the degree of impact on the carbon productivity of the entire country.
Comparative analysis was conducted on exponentiating the carbon productivity of the service and non-service industries in 38 OECD countries (2017 to 2019). The country group with the lowest non-service industry carbon productivity and the highest service industry carbon productivity was the country group with the largest change rate in the adjusted carbon productivity estimation results. The carbon productivity of non-service industries in Korea, Estonia, Israel, and Australia was only 50.9% (Korea), 27.2% (Estonia), 65.9% (Israel), and 45.7% (Australia) of the OECD average non-service industry carbon productivity of 1925.3 USD/ton CO2-eq. In the case of Korea, the carbon productivity in the service industry was 9936.1 USD/ton CO2-eq. (13th), which was approximately 12% higher than the OECD average service industry carbon productivity of 8909.1 USD/ton CO2-eq. The carbon productivity auxiliary indicator designed in this study can be appropriately utilized to adjust the size of the corresponding deviation because the carbon productivity in the non-service industry was very low.
Korea is a representative manufacturing-centered country, but it relies on overseas imports for most of its resources, such as oil, bituminous coal, and gas, because it lacks natural resources. Nevertheless, Korea is one of the most energy-consuming countries, accounting for approximately 2% of global energy consumption. In particular, the proportion of energy consumption in the industrial sector is relatively high. The reason for the high proportion of greenhouse gas emissions in the industrial sector is due to the characteristics of the domestic industrial structure centered on energy-intensive manufacturing. The greenhouse gas emissions from manufacturing are approximately 150 million tons CO2-eq. from the steel industry, approximately 40 million tons CO2-eq. from petrochemicals, approximately 35 million tons CO2-eq. from cement, and approximately 15 million tons CO2-eq. from oil refining. These four industries account for approximately 75% of the greenhouse gas emissions of the entire industrial sector. Looking at the proportion of each industry within the OECD industrial sector, Korea has the highest proportion of manufacturing among the 38 OECD countries, and the proportion of the steel and metal industry, which is the industry that emits the most greenhouse gas, is much higher than that of major countries [24].
Estonia has significant greenhouse gas emissions. The average annual greenhouse gas emissions per capita in the European Union from 2005 to 2019 was 8.4 tons CO2-eq. In 2005, however, Estonia’s average annual greenhouse gas emissions per capita reached 14.1 tons CO2-eq. Afterward, it showed a steadily decreasing trend. In 2019, it emitted 11.5 tons CO2-eq. of greenhouse gas. Even based on the average annual greenhouse gas emissions per person in 2019, this was approximately 37% higher than the 15-year average for the European Union. Estonia’s greenhouse gas is emitted mainly from the energy industry, which comes from shale oil processing, which is abundant in Estonia. Shale oil, which is used as a raw material for power generation and diesel production, emits significant amounts of greenhouse gas during extraction and processing. Estonia aims to phase out shale oil power production by 2035 and shale oil use in the entire energy sector by 2040. Nevertheless, shale oil remains a major source of power that Estonia relies on locally [25].
Australia is a global exporter of fossil fuels and a representative country of energy demands from fossil fuels. According to Australia’s 2019 Greenhouse Gas National Inventory Report, the TGEs from Australia was 530 million tons CO2-eq., with per capita emissions at 21 tons CO2-eq., approximately three times the world average, and emissions from coal accounted for approximately 30% of the TGEs [26]. As of 2020, 66% and 7.5% of Australia’s total energy production came from coal and natural gas, respectively [27]. In addition to these resource characteristics, Australia’s TGEs is influenced by its geographical and economic landscape. The agricultural and livestock sectors, which utilize the country’s vast territory, produce significant amounts of methane. In addition, a relatively large number of people use cars and airplanes for intercity travel [28].
Israel is a service-industry-centered country, with the service sector accounting for more than 80% of the national economy. Although most industries are not major greenhouse gas emitters, high greenhouse gas emissions sectors, such as paper, petrochemicals, and cement, contribute 28% of the total industrial economy, leading to relatively more greenhouse gas emissions from the manufacturing field than other OECD countries [29].
These industrial and geographical factors, such as the industrial structure and resource types, can adversely affect carbon productivity calculations. The carbon productivity auxiliary indicator proposed in this study is adjusted by the service and non-service industrial character to calibrate discrepancies. By classifying carbon productivity by industries and applying specific coefficients, the study provides an upward adjustment for countries that inherently emit significant greenhouse gases because of their industrial and geographical characteristics.
Among the countries where the carbon productivity decreased the most, Luxembourg, France, and the United Kingdom had the highest average tertiary industry GDP share over the three years (2017 to 2019) among 38 OECD countries. Hence, the current carbon productivity estimation method, which can estimate high carbon productivity from value-added creation in service industries, tends to skew the national carbon productivity of service-industry-based countries favorably. Therefore, countries with a high proportion of the service industry in their economy are calculated relatively favorably when assessing carbon productivity.
Figure 5 presents a graph comparing current carbon productivity with adjusted carbon productivity. The adjusted carbon productivity bulges outward, centered around the current carbon productivity, represented by the blue line. Upward bulges indicate countries whose carbon productivity has been adjusted upward. These countries exhibit high greenhouse gas emissions relative to created value-added in their non-service industries and have a relatively low proportion of the service industry in their overall economy. Conversely, downward bulges signify countries with a downward adjustment in carbon productivity. These countries typically have a very high proportion of the service industry in their overall economy or very low direct greenhouse gas emissions from their non-service industries.

6. Proposal and Utilization

The national-level carbon productivity auxiliary indicator designed in this study identifies countries that require additional interpretation of productivity indicators because of their industrial and geographical characteristics. In addition, it adjusts the national-level carbon productivity to an appropriate level, making it a useful auxiliary tool in utilizing the current national carbon productivity indicator.
The carbon productivity auxiliary indicator is based on the adjusted carbon productivity results of OECD countries, derived from multiple regression analysis. This indicator considers the tendency of countries to show large deviations from the current carbon productivity results and the productivity distribution by the service and non-service industries. The indicator uses a non-service industry carbon productivity coefficient of 0.732, a service industry carbon productivity coefficient of 0.367, and a carbon productivity constant of −0.368, rounding to the second decimal place for ease of application.
Figure 6 presents the formula for the carbon productivity auxiliary indicator. This indicator appropriately compensates for the blind spots not addressed by the current carbon productivity measure because it considers the explanatory power (R2 = 0.909, adjR2 = 0.907) of the multiple regression model and the country-specific classifications based on the industrial structure characteristics and carbon productivity by the service and non-service classification. The indicator considers the greenhouse gas emissions according to the industries of OECD member countries and reflects the added value created according to the level of emissions in the service and non-service industries of each country.
On the other hand, while the industrial structure characteristics by country can be categorized, the detailed industrial and geographical characteristics, as well as the social and cultural factors, differ even within the same category. Thus, using the multiple regression model correction value directly based on simple statistics may seem unreasonable. Therefore, this study proposes the following. First, the carbon productivity was compared by dividing the countries into service and non-service industry categories based on the proportion of the tertiary industry. The share of the tertiary industry was a major factor in determining the direction of productivity adjustment. Thus, the share of the tertiary industry can serve as a reference point for distinguishing countries where a simple comparison of carbon productivity is possible.
Significant variations among countries were evident when estimating the carbon productivity of OECD member countries based on the current carbon productivity calculation system. For example, Switzerland’s carbon productivity in 2019 was 15,143.7 USD/ton CO2-eq., approximately 3.5 times the OECD average of 4290.9 USD/ton CO2-eq. In contrast, Poland’s carbon productivity was 1419.4 USD/ton CO2-eq., approximately one-third of the OECD average. This statistical deviation can be stabilized by clustering countries with similar industrial characteristics (Table 6 and Figure 7).
This study set the tertiary industry share of 74% as the criterion for distinguishing service and non-service industry countries. Countries where the tertiary industry accounts for more than 74% of the total economy are classified as service-centered, whereas those below 74% are classified as non-service-centered. This threshold approximates the median tertiary industry share of the 38 OECD countries chosen for the convenience of application. In addition, the carbon productivity auxiliary indicator calculated in this study will be used alongside the current carbon productivity indicator to show the relative gap.
The carbon productivity auxiliary indicator calculated in this study will be used alongside the current carbon productivity indicator to show the relative gap. The comparison and analysis confirmed that the auxiliary indicator reduced the deviation for service-industry-centered countries and increased the deviation for non-service-industry-centered countries.
For example, Switzerland recorded the highest carbon productivity among service-industry-centered countries at 13,760.8 USD/ton CO2-eq., approximately 2.5 times the average of 5371.5 USD/ton CO2-eq. among 16 OECD service-industry-centered countries. In contrast, Canada, which had the lowest ranking among service-industry-centered countries, had a carbon productivity of 2176.6 USD/ton CO2-eq., which was less than half the OECD average for service-industry-centered countries. This reduction in deviation can be interpreted as homogeneity in carbon productivity, driven largely by the tertiary industry.
In contrast, the gap in carbon productivity actually increased for non-service-industry-centered countries. Norway recorded the highest carbon productivity among non-service-industry-centered countries at 9218.0 USD/ton CO2-eq., approximately 2.5 times the average of 3651.2 USD/ton CO2-eq. among 19 non-service-industry-centered countries. Poland, with the lowest ranking among non-service-industry-centered countries, had a carbon productivity of 1339.5 USD/ton CO2-eq., approximately one-third of the OECD average. This increased gap was attributed to the varying forms and structures of primary and secondary industries and their economic dependence.
For example, Korea and Australia, which showed the greatest improvement, have a high dependence on greenhouse-gas-emitting industries, resulting in significant adjustments to their carbon productivity. In contrast, Hungary and Slovenia, which showed the largest decrease, have relatively high shares of the secondary industry, but a significant proportion of their economy is in assembly industries [30], which import parts or intermediate goods and produce finished products [31,32]. This resulted in a decrease in carbon productivity (Table 7 and Table 8, Figure 8 and Figure 9).
Thus, the auxiliary indicator of this study for carbon productivity can be seen as compensating for the gaps not considered by the current carbon productivity measures, especially those related to industrial and geographical characteristics. This study sets the tertiary industry share of 74% as the criterion for distinguishing service and non-service industry countries. Countries where the tertiary industry accounts for more than 74% of the total economy are classified as service-centered, and those below 74% are classified as non-service-centered. This threshold approximates the median tertiary industry share of the 38 OECD countries chosen for the convenience of application. In addition, the carbon productivity auxiliary indicator calculated in this study will be used alongside the current carbon productivity indicator to show the relative gap.

7. Conclusions

This study designed a multiple regression model using GDP and industry-specific greenhouse gas emissions statistics and corrected the GDP/TGEs, the current national carbon productivity calculation method. In addition, the carbon productivity in the service and non-service industry sectors, which was the criterion for variable division in the regression model, was calculated separately, the carbon productivity and ranking fluctuation ranges were compared and analyzed, and auxiliary indicators and utilization methods that can be used with the current carbon productivity indicator were proposed.
The research results for each productivity indicator can be summarized as follows.
For carbon productivity, countries with high greenhouse gas emissions in non-service industries because of their industrial structures (e.g., Korea, Estonia, and Australia) were appropriately selected and corrected. On the other hand, some countries (e.g., Luxembourg and Costa Rica) with low carbon productivity in the service industry but evaluated as having high overall carbon productivity because of the small absolute amount of greenhouse gas emitted by the service industry were corrected downward. The carbon productivity auxiliary indicator was designed using a non-service industry carbon productivity coefficient of 0.732, a service industry carbon productivity coefficient of 0.367, and a carbon productivity constant of −0.368, rounded to the second decimal place for convenience ((0.7 × non-service industry productivity) + (0.3 × service industry productivity) − 0.4). A comparative analysis was conducted using the current carbon productivity and the carbon productivity auxiliary indicators by dividing service and non-service industry countries based on the proportion of the service industry in the economy of that country.
The analysis showed that the carbon productivity auxiliary indicator designed in this study reduced the deviation for service-industry-centered countries compared to the current carbon productivity indicator while increasing the deviation for non-service-industry-centered countries. For service-industry-centered countries, despite differences in the form and structure of primary and secondary industries, the tertiary industry essentially drives GDP, suggesting homogeneity in carbon productivity. For non-service-industry-centered countries, the main differences in the form and structure of the primary and secondary industries, as well as the large difference in economic dependence by each industrial group, mean that the auxiliary indicator can appropriately quantify the gaps difficult to consider using the current carbon productivity indicator.
For example, Korea and Luxembourg, which have large upward and downward ranges of carbon productivity adjustments, can be compared through their carbon-intensive steel industries. According to the ESG report of company P, the largest steel company in Korea, the greenhouse gas emitted per ton of steel products is approximately 2 tons CO2-eq. [33]. Similarly, company A, a leading steel company in Luxembourg, reports very similar emissions per ton of steel products (2 tons CO2-eq.) [34]. This means that greenhouse gas emissions per unit weight are similar regardless of the country, with absolute emissions increasing with production volume. Luxembourg has a high proportion of the service industry in its national economy. Therefore, it is likely to be calculated favorably under the current method, whereas Korea, with a high proportion of manufacturing, is likely to be calculated unfavorably.
The carbon productivity auxiliary indicator designed in this study provides insight into which areas may be advantageous or disadvantageous in terms of the carbon productivity because of the industrial structure of each country and the extent of these advantages and disadvantages.
In summary, the carbon productivity adjustment multiple regression model designed in this study, the comparative analysis of carbon productivity by the service and non-service industries, and the results of applying the carbon productivity auxiliary indicator highlight the limitations of the current national carbon productivity indicator. This paper also provided insights into improving the productivity indicators by considering each country’s industrial structure. The proposed carbon productivity auxiliary indicator is expected to enhance the rationality of the current indicator by being used alongside the existing national carbon productivity calculation.
For example, the proposed auxiliary indicator can be useful for comparing and analyzing carbon productivity between service- and non-service-industry-centered countries or among countries with similar export structures by sector. The auxiliary indicator directly reflects the value-added created from greenhouse gas emissions. Therefore, it is a valuable supplement to the existing GDP/TGEs indicator, which overlooks the industrial structure characteristics. Nevertheless, implications are derived at the level of descriptive statistics analysis regarding the differences in rankings by category (service and non-service) and the results of the carbon productivity changes by adjustments. These results suggest conducting a more sophisticated and detailed national-level carbon productivity analysis.

Author Contributions

J.H.L. devised the research, the main conceptual ideas, and the proof outline. In addition, he worked out almost all of the technical details and conducted the current and adjusted national-level carbon productivity estimation by multiple regression analysis. H.Y.K. and Y.W.H. supervised and reviewed the research. All authors discussed the results and commented on the manuscript. All authors have read and agreed to the published version of the manuscript.

Funding

This work was supported by a Korea Institute of Energy Technology Evaluation and Planning (KETEP) grant funded by the Korean government (Ministry of Trade, Industry and Energy) (No. 20214000000520, Human Resource Development Project in Circular Remanufacturing Industry).

Data Availability Statement

The original contributions presented in the study are included in the article. Further inquiries can be directed to the corresponding author.

Conflicts of Interest

The authors have no conflicts of interest to declare that are relevant to the content of this study.

References

  1. European Commission. An EU Action Plan for the Circular Economy. Communication from the Commission to the European Parliament, the Council, the European Economic and Social Commitee and the Commitee of Regions. 2015. Available online: https://eur-lex.europa.eu/resource.html?uri=cellar:8a8ef5e8-99a0-11e5-b3b7-01aa75ed71a1.0012.02/DOC_1&format=PDF (accessed on 31 July 2024).
  2. United Nations Environment Programme. Towards a Green Economy: Pathways to Sustainable Development and Poverty Eradication: A Synthesis for Policy Makers. 2011. Available online: https://sustainabledevelopment.un.org/content/documents/126GER_synthesis_en.pdf (accessed on 31 July 2024).
  3. Bachtler, J.; Martins, J.O.; Wostner, P.; Zuber, P. Towards Cohesion Policy 4.0: Structural Transformation and Inclusive Growth; Taylor & Francis: Oxfordshire, UK, 2017. [Google Scholar] [CrossRef]
  4. Fratini, C.F.; Georg, S.; Jørgensen, M.S. Exploring circular economy imaginaries in European cities: A research agenda for the governance of urbansustainability transitions. J. Clean. Prod. 2017, 228, 974–989. [Google Scholar] [CrossRef]
  5. Corvellec, H.; Campos, M.J.Z.; Zapata, P. Infrastructures, lock-in, and sustainable urban development: The case of waste incineration in the Göte-borg Metropolitan Area. J. Clean. Prod. 2013, 50, 32–39. [Google Scholar] [CrossRef]
  6. Mayer, A.; Haas, W.; Wiedenhofer, D.; Krausmann, F.; Nuss, P.; Blengini, G.A. Measuring progress towards a circular economy: A monitoring framework for economy-wide material loop closing in the EU28. J. Ind. Ecol. 2019, 23, 62–76. [Google Scholar] [CrossRef] [PubMed]
  7. Van Buren, N.; Demmers, M.; van der Heijden, R.; Witlox, F. Towards a circular economy: The role of Dutch logistics industries and governments. Sustainability 2016, 8, 647. [Google Scholar] [CrossRef]
  8. Lee, J.H.; Kang, H.Y.; Kim, Y.W.; Hwang, Y.W.; Kwon, S.G.; Park, H.W.; Choi, J.W.; Choi, H.H. Analysis of the life cycle environmental impact reductions of remanufactured turbochargers. J. Remanuf. 2023, 13, 187–206. [Google Scholar] [CrossRef]
  9. Adesina, A. Recent advances in the concrete industry to reduce its carbon dioxide emissions. Environ. Chall. 2020, 1, 100004. [Google Scholar] [CrossRef]
  10. Benjamin, N.I.; Lin, B. Quantile analysis of carbon emissions in China metallurgy industry. J. Clean. Prod. 2020, 243, 118534. [Google Scholar] [CrossRef]
  11. Ullah, S.; Ozturk, I.; Usman, A.; Majeed, M.T.; Akhtar, P. On the asymmetric effects of premature deindustrialization on CO2 emissions: Evidence from Pakistan. Environ. Sci. Pollut. Res. Int. 2020, 27, 13692–13702. [Google Scholar] [CrossRef] [PubMed]
  12. Qi, W.; Song, C.; Sun, M.; Wang, L.; Han, Y. Sustainable Growth Drivers: Unveiling the Role Played by Carbon Productivity. Int. J. Environ. Res. Public Health 2020, 19, 1374. [Google Scholar] [CrossRef] [PubMed]
  13. Wiedmann, T.O.; Schandl, H.; Lenzen, M.; Moran, D.; Suh, S.; West, J.; Kanemoto, K. The material footprint of nations. Proc. Natl. Acad. Sci. USA 2015, 112, 6271–6276. [Google Scholar] [CrossRef] [PubMed]
  14. Mancini, L.; Benini, L.; Sala, S. Resource footprint of Europe: Complementarity of material flow analysis and life cycle assessment for policy support. Environ. Sci. Policy 2015, 54, 367–376. [Google Scholar] [CrossRef]
  15. Pothen, F.; Welsch, H. Economic development and material use. Evidence from international panel data. World Dev. 2019, 115, 107–119. [Google Scholar] [CrossRef]
  16. Lee, J.H.; Kang, H.Y.; Hwang, Y.W.; Kwon, S.G. Development of Sub-indicator for Enhancing the Reliability of National-level Resource Productivity Estimation. Clean Technol. 2022, 28, 258–266. [Google Scholar] [CrossRef]
  17. Baynes, T.M.; Musango, J.K. Estimating current and future global urban domestic material consumption. Environ. Res. Lett. 2018, 13, 065012. [Google Scholar] [CrossRef]
  18. Dong, L.; Dai, M.; Liang, H.; Zhang, N.; Mancheri, N.; Ren, J.; Dou, Y.; Hu, M. Material flows and resource productivity in China, South Korea and Japan from 1970 to 2008: A transitional perspective. J. Clean. Prod. 2017, 141, 1164–1177. [Google Scholar] [CrossRef]
  19. Krausmann, F.; Gingrich, S.; Eisenmenger, N.; Erb, K.H.; Haberl, H.; Fischer-Kowalski, M. Growth in global materials use, GDP and population during the 20th century. Ecol. Econ. 2009, 68, 2696–2705. [Google Scholar] [CrossRef]
  20. Steinberger, J.K.; Krausmann, F.; Getzner, M.; Schandl, H.; West, J. Development and dematerialization: An international study. PLoS ONE 2013, 8, e70385. [Google Scholar] [CrossRef] [PubMed]
  21. Giljum, S.; Dittrich, M.; Lieber, M.; Lutter, S. Global patterns of material flows and their socio-economic and environmental implications: A MFA study on all countries worldwide from 1980 to 2009. Resources 2014, 3, 319–339. [Google Scholar] [CrossRef]
  22. Talmon-Gros, L. Material Productivity Measurement. In Development Patterns of Material Productivity; Springer: Cham, Switzerland, 2014. [Google Scholar] [CrossRef]
  23. OECD. OECD Data Explorer. Available online: https://data-explorer.oecd.org/ (accessed on 31 July 2024).
  24. Lee, S.W.; Lee, J.W. 2050 carbon neutrality and the way ahead for manufacturing. KIET Mon. Ind. Econ. Rev. 2021, 275, 20–31. [Google Scholar]
  25. European Parliament. Climate Action in Estonia. 2021. Available online: https://www.europarl.europa.eu/RegData/etudes/BRIE/2021/690684/EPRS_BRI(2021)690684_EN.pdf (accessed on 31 July 2024).
  26. Australia Gorvernment. National Inventory Report 2017. 2019. Available online: https://unfccc.int/sites/default/files/resource/aus-2019-nir-24May19.zip (accessed on 31 July 2024).
  27. McConnell, D.; Holmes, S.; Tan, S.; Cubrilovic, N. An Open Platform for National Electricity Market Data. OpenNEM. Available online: https://opennem.org.au/energy/nem/?range=all&interval=1y&view=discrete-time (accessed on 31 July 2024).
  28. Climate Council. Agriculture’s Contribution to Australia’s Greenhouse Gas Emissions. 2021. Available online: https://web.archive.org/web/20210828170749/https://www.climatecouncil.org.au/resources/australia-agriculture-climate-change-emissions-methane/ (accessed on 31 July 2024).
  29. The Israel Democracy Institute. Carbon Pricing in Israel. 2022. Available online: https://en.idi.org.il/media/18866/carbon-pricing-in-israel-israel-2050-a-thriving-economy-in-a-sustainable-environment.pdf (accessed on 31 July 2024).
  30. doopedia. Assembly Industry. Available online: https://terms.naver.com/entry.naver?docId=1141663&cid=40942&categoryId=31898 (accessed on 31 July 2024).
  31. Boda, G. To what extent is Hungary a knowledge-based economy? Theory Methodol. Pr.—Rev. Bus. Manag. 2017, 13, 69–84. [Google Scholar] [CrossRef]
  32. Briški, M.; Verbič, B. Remote Sessions of the National Assembly of the Republic of Slovenia and its Working Bodies. Int. J. Parliam. Stud. 2021, 1, 199–206. [Google Scholar] [CrossRef]
  33. POSCO. ESG Factbook. 2022. Available online: https://www.posco.co.kr/homepage/servlet/FileDown?file=/hfiles/enboard/6915f96b18aa6772235a61a30ebdc510.pdf&filename=POSCO%20ESG%20Factbook%202022.pdf (accessed on 31 July 2024).
  34. ArcelorMittal. Annual Report 2021. 2022. Available online: https://www.vernimmen.net/ftp/ArcelorMittal_2021.pdf (accessed on 31 July 2024).
Figure 1. Normal distribution histogram of a multiple regression model for adjusting the GDP using carbon productivity by service and non-service sectors. (Note. adjCP: adjusted carbon productivity).
Figure 1. Normal distribution histogram of a multiple regression model for adjusting the GDP using carbon productivity by service and non-service sectors. (Note. adjCP: adjusted carbon productivity).
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Figure 2. Normal P–P plots of the regression standardized residual of a multiple regression model for adjusting the GDP using carbon productivity by the service and non-service sectors. (Note. adjCP: adjusted carbon productivity).
Figure 2. Normal P–P plots of the regression standardized residual of a multiple regression model for adjusting the GDP using carbon productivity by the service and non-service sectors. (Note. adjCP: adjusted carbon productivity).
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Figure 3. Partial regression plots of a multiple regression model for adjusting the GDP using carbon productivity of the non-service sector. (Note. adjCP: adjusted carbon productivity).
Figure 3. Partial regression plots of a multiple regression model for adjusting the GDP using carbon productivity of the non-service sector. (Note. adjCP: adjusted carbon productivity).
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Figure 4. Partial regression plots of a multiple regression model for adjusting the GDP using carbon productivity of the service sector. (Note. adjCP: adjusted carbon productivity).
Figure 4. Partial regression plots of a multiple regression model for adjusting the GDP using carbon productivity of the service sector. (Note. adjCP: adjusted carbon productivity).
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Figure 5. Comparison graph between the current carbon productivity and the adjusted carbon productivity.
Figure 5. Comparison graph between the current carbon productivity and the adjusted carbon productivity.
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Figure 6. Auxiliary indicator estimating formula of national-level carbon productivity.
Figure 6. Auxiliary indicator estimating formula of national-level carbon productivity.
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Figure 7. The current national-level carbon productivity ranking graph of OECD countries (average of 2017 to 2019). (Note. The red color is below the average and the blue color is above the average).
Figure 7. The current national-level carbon productivity ranking graph of OECD countries (average of 2017 to 2019). (Note. The red color is below the average and the blue color is above the average).
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Figure 8. Current and adjusted carbon productivity rankings of service-sector-based countries in the OECD list (average of 2017 to 2019). (Note. The red color is below the average and the blue color is above the average).
Figure 8. Current and adjusted carbon productivity rankings of service-sector-based countries in the OECD list (average of 2017 to 2019). (Note. The red color is below the average and the blue color is above the average).
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Figure 9. Current and adjusted carbon productivity rankings of non-service-sector-based countries in the OECD list (average of 2017 to 2019). (Note. The red color is below the average and the blue color is above the average).
Figure 9. Current and adjusted carbon productivity rankings of non-service-sector-based countries in the OECD list (average of 2017 to 2019). (Note. The red color is below the average and the blue color is above the average).
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Table 1. Greenhouse gas emission per capita and carbon productivity ranking of OECD countries (as of 2019).
Table 1. Greenhouse gas emission per capita and carbon productivity ranking of OECD countries (as of 2019).
CountriesGreenhouse Gas Emission
(per Capita, ton CO2-eq.)
RankingCountriesCarbon Productivity
(USD/ton CO2-eq.)
Ranking
Australia21.91Switzerland15,524.21
United States20.02Sweden10,549.52
Canada19.23Norway8021.13
Luxembourg17.34Costa Rica7901.34
New Zealand16.05Denmark7381.55
Korea13.56Ireland6545.66
Iceland13.17Luxembourg6501.57
Ireland12.48United Kingdom6303.78
Czech Republic11.69France6235.39
Estonia11.010Austria5558.210
Netherlands10.411Iceland5221.011
Belgium10.112Finland5092.612
Poland10.113Israel5083.513
Japan9.614Netherlands5030.514
Germany9.615Germany4893.115
Finland9.516Italy4763.016
Norway9.517Belgium4601.117
Austria9.018Spain4500.518
Israel8.719Japan4234.319
Slovenia8.220Portugal3743.020
Denmark8.121United States3230.821
Greece8.022Slovenia3157.922
Slovak Republic7.323Latvia3085.223
Lithuania7.224Lithuania2704.924
Italy7.125New Zealand2664.025
United Kingdom6.826Slovak Republic2645.726
Hungary6.627Hungary2532.327
Spain6.628Chile2508.328
France6.529Australia2478.329
Portugal6.230Canada2409.530
Turkiye6.231Greece2382.531
Mexico5.932Korea2355.132
Latvia5.833Estonia2138.033
Chile5.834Czech Republic2045.734
Switzerland5.435Colombia1836.635
Sweden4.936Mexico1722.736
Colombia3.637Poland1542.637
Costa Rica1.638Turkiye1493.838
Note. Bolded and backgrounded countries have clear disparities between greenhouse gas emissions and carbon productivity. Details are described in the manuscript.
Table 2. Results of correlation analysis between GDP and TGEs and the service and non-service industrial sectors.
Table 2. Results of correlation analysis between GDP and TGEs and the service and non-service industrial sectors.
ValueAsymptotic Standards Error aApproximate T bApproximate Significance
Spearman correlationOrdinal by ordinalNon-service industry (GDP × TGEs)0.4440.0673.690<0.001 c
Service industry (GDP × TGEs)0.7140.05410.784<0.001 c
a Not assuming the null hypothesis. b Using the asymptotic standard error assuming the null hypothesis. c Based on normal approximation. (Note. GDP: Gross Domestic Product, TGEs: Total Greenhouse gas Emissions).
Table 3. Summary of a multiple regression model for adjusting the GDP using carbon productivity by the service and non-service sectors.
Table 3. Summary of a multiple regression model for adjusting the GDP using carbon productivity by the service and non-service sectors.
adjCP bRR2Adjusted R2Std. Error of the EstimateR2 Change
0.953 a0.9090.9070.8346973760.909
Change Statistics
F Changedf1df2Sig.f Change
552.68221110
a Predictors: (Constant), carbon productivity of non-service industry (primary industry + secondary industry), carbon productivity of service industry (tertiary industry). b Dependent Variable: adjCP.
Table 4. Result of a multiple regression model for adjusting GDP using carbon productivity by the service and non-service sectors.
Table 4. Result of a multiple regression model for adjusting GDP using carbon productivity by the service and non-service sectors.
adjCP a Unstandardized
Coefficients
Standardized
Coefficients Beta
Collinearity Statistics
BStd. ErrortSig.ToleranceVIF
(Constant)−0.3680.18 −2.040.044
G D P 1 s t + 2 n d G H G s 1 s t + 2 n d 0.7320.0470.51815.48200.7341.362
G D P 3 r d G H G s 3 r d 0.3670.0210.57617.2240
a Dependent Variable: adjCP.
Table 5. Summary of the multiple regression results for adjusting national-level carbon productivity considering greenhouse gas emissions by the service and non-service sectors.
Table 5. Summary of the multiple regression results for adjusting national-level carbon productivity considering greenhouse gas emissions by the service and non-service sectors.
CountriesThe Current
Carbon Productivity
The Adjusted
Carbon Productivity
DifferenceRelative ChangeNon-Service-Based Industry’s Carbon Productivity
(Exponentiated)
Service Based
Industry’s Carbon Productivity
(Exponentiated)
Service Based
Industry Share
USD/tCO2-eq.RankUSD/tCO2-eq.Rank%RankValueRankValueRank%Rank
Korea2337.5313996.018 (△ 13)1658.571.01−0.3775170.6285164.437
Estonia1651.8352525.328 (△ 7)873.552.92−0.4994330.6171274.118
Israel4832.7136460.16 (△ 7)1627.433.73−0.5808370.5220380.18
Australia2531.8273360.722 (△ 5)828.932.74−0.4586290.5210472.823
Costa Rica6551.458224.74 (△ 1)1673.225.550.095310.03733876.216
New Zealand2661.6243267.923 (△ 1)606.322.86−0.4615310.4819673.920
Greece2248.5322686.026 (△ 6)437.619.57−0.6326380.5100582.72
Colombia1836.4342126.032 (△ 2)289.515.88−0.3656150.4535767.133
Japan4041.0194582.914 (△ 5)541.813.49−0.3811180.39951170.027
Finland4888.7125521.78 (△ 4)633.112.910−0.4293250.40491073.621
Mexico1616.7361807.536 (—)190.811.811−0.3459120.4420865.735
Norway7997.438797.73 (—)800.310.012−0.323070.33742067.232
Czech Republic1880.9332061.734 (▼ 1)180.89.613−0.3432110.4174966.034
Chile2588.5252762.025 (—)173.56.714−0.3563140.38321368.531
Ireland5960.896158.07 (△ 2)197.23.315−0.253130.27172763.038
Iceland5255.0115346.39 (△ 2)91.31.716−0.4462260.35201676.415
Portugal3473.0203528.421 (▼ 1)55.41.617−0.5036340.38591278.89
Germany4592.2164571.915 (△ 1)−20.3−0.418−0.3673160.31702172.024
Slovak Republic2470.4282455.629 (▼ 1)−14.8−0.619−0.3427100.34411868.829
Netherlands4756.0144721.513 (△ 1)−34.5−0.720−0.5272360.36611480.66
Sweden10,522.9210,320.62 (—)−202.3−1.921−0.4226230.30402376.614
Denmark6985.846748.05 (▼ 1)−237.8−3.422−0.4529280.31652278.010
Turkiye1535.7371439.637 (—)−96.1−6.323−0.309150.34791765.336
Austria5469.5104983.112 (▼ 2)−486.4−8.924−0.342490.24533173.522
United States3079.6212796.424 (▼ 3)−283.2−9.225−0.5138350.34021980.75
Poland1421.6381285.238 (—)−136.4−9.626−0.3480130.35671568.630
Spain4248.9183831.320 (▼ 2)−417.5−9.827−0.4236240.28802577.312
Lithuania2579.4262303.231 (▼ 5)−276.2−10.728−0.338180.28012671.226
Switzerland15,152.3113,4301 (—)−1722.4−11.429−0.227520.11393674.917
Canada2368.7302083.933 (▼ 3)−284.9−12.030−0.3838200.30022474.019
Slovenia2979.9232620.427 (▼ 4)−359.4−12.131−0.287440.23143569.528
Italy4691.0154089.617 (▼ 2)−601.4−12.832−0.3838190.24673076.613
Belgium4507.4173859.419 (▼ 2)−648.0−14.433−0.4590300.27002880.27
Hungary2400.2292021.635 (▼ 6)−378.5−15.834−0.317660.24383371.525
United Kingdom6027.775047.010 (▼ 3)−980.7−16.335−0.4684320.24792981.73
France6018.685007.311 (▼ 3)−1011.3−16.836−0.4478270.23613481.14
Latvia2989.4222443.930 (▼ 8)−545.5−18.237−0.3929220.24453277.411
Luxembourg6542.664543.516 (▼10)−1999.1−30.638−0.3870210.08903788.61
Note. △: Increase in rank, ▼: decreade in rank.
Table 6. The current national-level carbon productivity ranking of OECD countries (average of 2017 to 2019).
Table 6. The current national-level carbon productivity ranking of OECD countries (average of 2017 to 2019).
CountriesGross Domestic Product
(Million USD)
Total Greenhouse Gas Emission
(ton CO2-eq.)
Carbon Productivity (GDP/TGEs,
USD/ton CO2-eq.)
RankingDeviation from the MeanComparing to Average
Switzerland714,060.047,152.315,143.7110,852.8352.93%
Sweden543,451.251,651.410,521.526230.6245.21%
Norway416,758.952,113.37997.233706.3186.37%
Denmark345,153.749,480.56975.542684.6162.57%
Luxembourg68,846.010,521.06543.752252.8152.50%
Costa Rica62,451.310,291.06068.661777.6141.43%
United Kingdom2,806,296.1465,992.66022.271731.3140.35%
France2,704,992.9449,992.96011.281720.3140.09%
Ireland373,757.062,774.65954.091663.1138.76%
Austria438,957.780,327.05464.6101173.7127.35%
Iceland25,217.64798.05255.911965.0122.49%
Finland266,623.654,568.94886.012595.1113.87%
Israel379,135.878,429.54834.113543.2112.66%
Netherlands886,035.6186,562.64749.314458.4110.68%
Italy2,021,676.4431,082.74689.815398.9109.30%
Germany3,851,172.0840,795.94580.416289.5106.75%
Belgium527,309.7116,986.04507.517216.6105.05%
Spain1,376,422.4324,474.34242.018−48.998.86%
Japan5,028,745.11,245,731.54036.819−254.194.08%
Portugal234,552.667,761.53461.420−829.580.67%
United States20,463,790.06,644,857.73079.621−1211.371.77%
Latvia33,085.611,060.12991.422−1299.569.72%
Slovenia52,366.217,588.12977.423−1313.569.39%
New Zealand210,512.679,092.52661.624−1629.362.03%
Chile283,420.3109,504.02588.225−1702.760.32%
Lithuania52,090.220,201.02578.626−1712.360.09%
Australia1,414,240.6558,551.22532.027−1758.959.01%
Slovak Republic102,499.341,550.52466.928−1824.057.49%
Hungary155,899.464,959.42400.029−1891.055.93%
Canada1,706,096.8720,176.32369.030−1921.955.21%
Korea1,666,623.5712,945.62337.731−1953.254.48%
Greece205,716.991,706.92243.232−2047.752.28%
Czech Republic240,059.2127,861.11877.533−2413.443.76%
Colombia323,032.3175,881.41836.634−2454.342.80%
Mexico1,216,775.7753,112.21615.735−2675.237.65%
Estonia29,543.718,488.01598.036−2692.937.24%
Turkiye799,133.4520,133.31536.437−2754.535.81%
Poland569,826.5401,464.51419.438−2871.533.08%
Average 4290.9
Table 7. Current and adjusted carbon productivity rankings of service-sector-based countries in the OECD list (average of 2017 to 2019).
Table 7. Current and adjusted carbon productivity rankings of service-sector-based countries in the OECD list (average of 2017 to 2019).
CountriesThe Current Carbon Productivity
($/tCO2-eq.)
The Adjusted Carbon Productivity
($/tCO2-eq.)
Relative Change
ValueRankValueRank
Switzerland15,143.7113,760.81 (—)9.1%
Sweden10,521.5210,860.72 (—)3.2%
Costa Rica6068.658167.23 (△2)34.6%
Denmark6975.5371154 (▼1)2.0%
Israel4834.196917.95 (△4)43.1%
Iceland5255.985644.16 (△2)7.4%
United Kingdom6022.265301.47 (▼1)−12.0%
France6011.275248.78 (▼1)−12.7%
Netherlands4749.3105009.09 (△1)5.5%
Luxembourg6543.744690.610 (▼6)−28.3%
Italy4689.8114268.811 (—)−9.0%
Belgium4507.5124054.212 (—)−10.1%
Spain4242.0134020.213 (—)−5.2%
Portugal3461.4143740.214 (—)8.1%
United States3079.6152956.715 (—)−4.0%
Greece2243.2182877.416 (△2)28.3%
Estonia1598.0192702.317 (△2)69.1%
Latvia2991.4162546.418 (▼2)−14.9%
Canada2369.0172176.619 (▼2)−8.1%
Average5332.0 5371.5
Note. △: Increase in rank, ▼: decreade in rank.
Table 8. Current and adjusted carbon productivity rankings of non-service-sector-based countries in the OECD list (average of 2017 to 2019).
Table 8. Current and adjusted carbon productivity rankings of non-service-sector-based countries in the OECD list (average of 2017 to 2019).
CountriesThe current Carbon Productivity
($/tCO2-eq.)
The adjusted Carbon Productivity
($/tCO2-eq.)
Relative Change
ValueRankValueRank
Norway7997.219218.01 (—)15.3%
Ireland5954.026387.32 (—)7.3%
Finland4886.045841.43 (△1)19.6%
Austria5464.635189.14 (▼1)−5.0%
Japan4036.864831.75 (△1)19.7%
Germany4580.454791.26 (▼1)4.6%
Korea2337.7144260.57 (△7)82.3%
Australia2532.0113577.88 (△3)41.3%
New Zealand2661.683472.89 (▼1)30.5%
Chile2588.292899.910 (▼1)12.0%
Slovenia2977.472706.811 (▼4)−9.1%
Slovak Republic2466.9122567.712 (—)4.1%
Lithuania2578.6102395.613 (▼3)−7.1%
Colombia1836.6162240.814 (△2)22.0%
Czech Republic1877.5152164.715 (—)15.3%
Hungary2400.0132091.516 (▼3)−12.9%
Mexico1615.7171899.817 (—)17.6%
Turkiye1536.4181496.418 (—)−2.6%
Poland1419.4191339.519 (—)−5.6%
Average3249.8 3651.2
Note. △: Increase in rank, ▼: decreade in rank. Bolded and backgrounded countries show clear difference between the current carbon productivity and the adjusted carbon productivity. Details are described in the manuscript.
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Lee, J.H.; Kang, H.Y.; Hwang, Y.W. Development of an Auxiliary Indicator for Improving the Rationality and Reliability of the National-Level Carbon Productivity Indicator. Energies 2024, 17, 3831. https://doi.org/10.3390/en17153831

AMA Style

Lee JH, Kang HY, Hwang YW. Development of an Auxiliary Indicator for Improving the Rationality and Reliability of the National-Level Carbon Productivity Indicator. Energies. 2024; 17(15):3831. https://doi.org/10.3390/en17153831

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Lee, Jong Hyo, Hong Yoon Kang, and Yong Woo Hwang. 2024. "Development of an Auxiliary Indicator for Improving the Rationality and Reliability of the National-Level Carbon Productivity Indicator" Energies 17, no. 15: 3831. https://doi.org/10.3390/en17153831

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