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21 pages, 4198 KiB  
Article
Decomposition of Intensity and Sustainable Use Countermeasures for the Energy Resources of the Northwestern Five Provinces of China Using the Logarithmic Mean Divisia Index (LMDI) Method and Three Convergence Models
by Zhenxu Zhang, Junsong Jia, Chenglin Zhong, Chengfang Lu and Min Ju
Energies 2025, 18(6), 1330; https://doi.org/10.3390/en18061330 (registering DOI) - 8 Mar 2025
Viewed by 12
Abstract
Energy resources are a material basis for regional sustainable development and ecological security. However, this issue has not been adequately studied in Northwest China. Here, we consider the five northwestern provinces of China and break down the change in energy use intensity. Results [...] Read more.
Energy resources are a material basis for regional sustainable development and ecological security. However, this issue has not been adequately studied in Northwest China. Here, we consider the five northwestern provinces of China and break down the change in energy use intensity. Results show that the total energy intensity in the five northwestern provinces decreased from 2.389 tons/104 Chinese yuan (CNY) in 2000 to 0.92 tons/104 CNY in 2021. The main influencing factors for the decline in energy intensity are the industrial energy intensity followed by the industrial structure and the energy structure. There are eight industrial sub-sectors that contributed to the decrease in industrial energy intensity. Conversely, there are seven sub-sectors that increased industrial energy intensity. In addition, there are six sub-sectors with an energy intensity of more than 1 ton/104 CNY. The convergence parameters demonstrate that the energy intensities of the five northwestern provinces did not converge to the same steady-state level, and their gap did not narrow in the short term. While the region’s overall energy intensity has shown a consistent downward trajectory, sectors heavily reliant on traditional fossil fuels—such as coal chemical processing, petroleum refining, and coking—have experienced a paradoxical upward trend in energy consumption. To address this, governments must implement targeted sector-specific measures, including upgrading technical capabilities through advanced coal gasification technologies, optimizing heat integration systems in petroleum refining processes, and streamlining intermediate production stages to minimize energy waste. Full article
(This article belongs to the Special Issue Energy Planning from the Perspective of Sustainability)
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<p>Location of the five northwestern provinces of China.</p>
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<p>(<b>a</b>) The growth trend of energy consumption and GDP in the five northwestern provinces of China; (<b>b</b>) the average energy intensity of the five northwestern provinces and China.</p>
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<p>Change in energy intensity in the five northwestern provinces of China.</p>
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<p>(<b>a</b>) The decomposition results of energy intensity in the five northwestern provinces of China. (<b>b</b>) (inset) The cumulative effect of each effect. <math display="inline"><semantics> <mrow> <mo>Δ</mo> <msub> <mi>S</mi> <mrow> <mi>i</mi> <mo>,</mo> <mi>t</mi> </mrow> </msub> </mrow> </semantics></math>, <math display="inline"><semantics> <mrow> <mo>Δ</mo> <msub> <mi>I</mi> <mrow> <mi>i</mi> <mo>,</mo> <mi>t</mi> </mrow> </msub> </mrow> </semantics></math>, <math display="inline"><semantics> <mrow> <mo>Δ</mo> <msub> <mi>F</mi> <mrow> <mi>i</mi> <mi>m</mi> <mo>,</mo> <mi>t</mi> </mrow> </msub> </mrow> </semantics></math>, and <math display="inline"><semantics> <mrow> <mo>Δ</mo> <msub> <mi>e</mi> <mrow> <mi>t</mi> <mi>o</mi> <mi>t</mi> </mrow> </msub> </mrow> </semantics></math> are the industrial structure effect, industrial energy intensity effect, energy structure effect, and total effect, respectively. (<math display="inline"><semantics> <mrow> <mo>Δ</mo> <msub> <mi>e</mi> <mrow> <mi>t</mi> <mi>o</mi> <mi>t</mi> </mrow> </msub> <mo>=</mo> <mo>Δ</mo> <msub> <mi>S</mi> <mrow> <mi>i</mi> <mo>,</mo> <mi>t</mi> </mrow> </msub> <mo>+</mo> <mo>Δ</mo> <msub> <mi>I</mi> <mrow> <mi>i</mi> <mo>,</mo> <mi>t</mi> </mrow> </msub> <mo>+</mo> <mo>Δ</mo> <msub> <mi>F</mi> <mrow> <mi>i</mi> <mi>m</mi> <mo>,</mo> <mi>t</mi> </mrow> </msub> </mrow> </semantics></math>).</p>
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<p>(<b>a</b>) Decomposition results of industrial structure effects. (<b>b</b>) (inset) The cumulative effects of each industrial structure. (<b>c</b>) The trends and shares of changes in each industrial structure. <span class="html-italic">S</span><sub>1</sub>, <span class="html-italic">S</span><sub>2</sub>, <span class="html-italic">S</span><sub>3</sub>, and <math display="inline"><semantics> <mrow> <mo>Δ</mo> <msub> <mi>S</mi> <mrow> <mi>i</mi> <mo>,</mo> <mi>t</mi> </mrow> </msub> </mrow> </semantics></math> denote the primary industry structure effect, secondary industry structure effect, tertiary industry structure effect, and total industry structure effect, respectively. (<math display="inline"><semantics> <mrow> <mo>Δ</mo> <msub> <mi>S</mi> <mrow> <mi>i</mi> <mo>,</mo> <mi>t</mi> </mrow> </msub> </mrow> </semantics></math> = <span class="html-italic">S</span><sub>1</sub> + <span class="html-italic">S</span><sub>2</sub> + <span class="html-italic">S</span><sub>3</sub>).</p>
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<p>(<b>a</b>) Decomposition results of the energy intensity effect of industries. (<b>b</b>) (inset) The cumulative effect of energy intensity by industry (tons/10<sup>4</sup> CNY). <span class="html-italic">I</span><sub>1</sub>, <span class="html-italic">I</span><sub>2</sub>, <span class="html-italic">I</span><sub>3</sub>, and <math display="inline"><semantics> <mrow> <mo>Δ</mo> <msub> <mi>I</mi> <mrow> <mi>i</mi> <mo>,</mo> <mi>t</mi> </mrow> </msub> </mrow> </semantics></math> denote the primary industry energy intensity effect, the secondary industry energy intensity effect, the tertiary industry energy intensity effect, and the total effect of industrial energy intensity, respectively. (<math display="inline"><semantics> <mrow> <mo>Δ</mo> <msub> <mi>I</mi> <mrow> <mi>i</mi> <mo>,</mo> <mi>t</mi> </mrow> </msub> </mrow> </semantics></math> = <span class="html-italic">I</span><sub>1</sub> <span class="html-italic">+ I</span><sub>2</sub> <span class="html-italic">+ I</span><sub>3</sub>).</p>
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<p>(<b>a</b>) Decomposition results of the energy structure effect. Insets: (<b>b</b>) The cumulative effect of each type of energy. (<b>c</b>) The share of each type of energy use. (<math display="inline"><semantics> <mrow> <mo>Δ</mo> <msub> <mi>F</mi> <mrow> <mi>i</mi> <mi>m</mi> <mo>,</mo> <mi>t</mi> </mrow> </msub> </mrow> </semantics></math> denotes the total energy structure effect, which is the sum of effects from coal, oil, natural gas, and electricity).</p>
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<p>The cumulative contribution of the energy intensity of each sub-sector in five provinces. (I5 is missing in Shaanxi; I8, I9, I17, and I33 are missing in Gansu; I17, I31, and I33 are missing in Qinghai; I4, I17, I21, and I35 are missing in Ningxia; and I5, I17, I32, and I33 are missing in Xinjiang).</p>
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<p>(<b>a</b>) Cumulative contribution of sub-sectors to energy intensity in the five northwestern provinces of China. (<b>b</b>) Energy intensity of sub-sectors.</p>
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<p>Energy intensity <span class="html-italic">σ</span> convergence. (<span class="html-italic">CV</span>, <span class="html-italic">σ</span>, and <span class="html-italic">G</span> denote the coefficient of variation, <span class="html-italic">σ</span> coefficient, and Gini coefficient, respectively).</p>
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<p>Energy intensity convergence in the five northwestern provinces of China.</p>
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21 pages, 5290 KiB  
Article
Historical Drivers and Reduction Paths of CO2 Emissions in Jiangsu’s Cement Industry
by Kuanghan Sun, Jian Sun, Changsheng Bu, Long Jiang and Chuanwen Zhao
C 2025, 11(1), 20; https://doi.org/10.3390/c11010020 - 5 Mar 2025
Viewed by 313
Abstract
With global climate challenges intensifying, the cement industry, as a major CO2 emitter, has attracted significant attention regarding its emission reduction potential and strategies. Advanced economies like the European Union use carbon pricing to spur innovation, while emerging countries focus on incremental [...] Read more.
With global climate challenges intensifying, the cement industry, as a major CO2 emitter, has attracted significant attention regarding its emission reduction potential and strategies. Advanced economies like the European Union use carbon pricing to spur innovation, while emerging countries focus on incremental solutions, such as fuel substitution. Combining LMDI decomposition and the LEAP model, this study examines Jiangsu Province as a test bed for China’s decarbonization strategy, a highly efficient region with carbon intensity 8% lower than the national average. Historical analysis identifies carbon intensity, energy mix, energy intensity, output scale, and economic effects as key drivers of emission changes. Specifically, the reduction in cement production, real estate contraction, lower housing construction, and reduced production capacity are the main factors curbing emissions. Under an integrated technology strategy—including energy efficiency, fuel and clinker substitution, and CCS—CO2 emissions from Jiangsu’s cement sector are projected to decrease to 17.28 million tons and 10.9 million tons by 2060 under high- and low-demand scenarios, respectively. Clinker substitution is the most significant CO2 reduction technology, contributing about 60%, while energy efficiency gains contribute only 3.4%. Despite the full deployment of existing reduction methods, Jiangsu’s cement industry is expected to face an emissions gap of approximately 10 million tons to achieve carbon neutrality by 2060, highlighting the need for innovative emission reduction technologies or carbon trading to meet carbon neutrality goals. Full article
(This article belongs to the Section Carbon Cycle, Capture and Storage)
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Graphical abstract

Graphical abstract
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<p>Geographical area map of Jiangsu Province.</p>
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<p>LMDI-LEAP composite model logic diagram.</p>
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<p>The energy consumption and CO<sub>2</sub> emissions of Jiangsu’s cement industry (2012–2022).</p>
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<p>Effects of driving forces for CO<sub>2</sub> emissions increment in Jiangsu’s cement industry (the definition of the relevant parameters can be found in the nomenclature).</p>
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<p>Cement yield and related factors analyzed by (<b>a</b>) FAI and (<b>b</b>) Gompertz models.</p>
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<p>Changes in cement CO<sub>2</sub> emissions trends in high-demand setting: (<b>a</b>) technology freezing (<b>b</b>) energy efficiency improvement; (<b>c</b>) fuel substitution; (<b>d</b>) clinker substitution; (<b>e</b>) CCS technology application; (<b>f</b>) technology integration.</p>
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<p>Changes in cement CO<sub>2</sub> emissions trends under low-demand setting: (<b>a</b>) technology freezing; (<b>b</b>) energy efficiency improvement; (<b>c</b>) fuel substitution; (<b>d</b>) clinker substitution; (<b>e</b>) CCS technology application; (<b>f</b>) technology integration.</p>
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<p>Different technology-related CO<sub>2</sub> emissions reduction scenarios of cement industry, (<b>a</b>) High-demand setting and (<b>b</b>) Low-demand setting.</p>
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<p>Influence of technology variables on emission reduction potential under integrated-technology scenario: (<b>a</b>) fuel substitution, (<b>b</b>) clinker substitution, (<b>c</b>) CCS diffusivity, and (<b>d</b>) high technical level.</p>
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21 pages, 6979 KiB  
Article
Nitrogen and Gray Water Footprints of Various Cropping Systems in Irrigation Districts: A Case from Ningxia, China
by Huan Liu, Xiaotong Liu, Tianpeng Zhang, Xinzhong Du, Ying Zhao, Jiafa Luo, Weiwen Qiu, Shuxia Wu and Hongbin Liu
Water 2025, 17(5), 717; https://doi.org/10.3390/w17050717 - 1 Mar 2025
Viewed by 266
Abstract
Under the influence of water resource conservation policies, the annual water diversion volumes in irrigation areas have been steadily decreasing, leading to substantial changes in regional cropping systems. These shifts have profoundly impacted agricultural reactive nitrogen (Nr) emissions and surface water quality. This [...] Read more.
Under the influence of water resource conservation policies, the annual water diversion volumes in irrigation areas have been steadily decreasing, leading to substantial changes in regional cropping systems. These shifts have profoundly impacted agricultural reactive nitrogen (Nr) emissions and surface water quality. This study focuses on the Yellow River Irrigation area of Ningxia, China, and employs a life cycle assessment method to quantitatively analyze fluctuations in the nitrogen footprint (NF) and gray water footprint (GWF) across three cropping systems—rice-maize intercropping, rice monoculture, and maize monoculture—during 2021–2023. The results indicate that rice monoculture exhibited significant variability in NF values (197.89–497.57 kg Neq·ha−1), with NO₃ leaching identified as the primary loss pathway (102.33–269.48 kg Neq·ha−1). The GWF analysis revealed that in 2021, the region’s GWF peaked at 23.18 × 104 m3·ha−1, with water pollution predominantly concentrated in Pingluo County (8 × 104 m3·ha−1). LMDI analysis identified nitrogen fertilizer application as the main contributor to variations in NF, while surface water pollution was indirectly influenced by crop yield. Furthermore, gray correlation analysis highlighted a significant coupling relationship between NF and GWF, with nitrogen fertilizer application having the most pronounced impact on GWF. Therefore, in the face of the gradual tightening of water resources in the irrigation areas, the current situation of reduced water diversion should be adopted as early as possible, and initiatives such as the reduction of nitrogen fertilizer application and the adjustment of the planting area of dryland crops should be accelerated to cope with the problem of nitrogen pollution brought about by changes in the cropping system. Full article
(This article belongs to the Special Issue Basin Non-Point Source Pollution)
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<p>Yellow River Irrigation area of Ningxia and sampling points.</p>
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<p>Three planting patterns and irrigation and drainage systems in the Yellow River Irrigation area of Ningxia.</p>
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<p>System boundaries and structure for the life cycle assessment of the N footprint and gray water footprint in the Yellow River Irrigation area of Ningxia. Note: Type of agricultural material in the figure are categorized by type of agricultural consumption, and N inputs correspond to type of agricultural material.</p>
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<p>Dynamics changes of gray water footprint under different tillage practices in the Yellow River Irrigation area of Ningxia.</p>
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<p>The impact of changes in factors on reactive nitrogen emissions.</p>
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<p>The impact of changes in factors on gray water footprint.</p>
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<p>Gray correlation analysis between nitrogen footprint compositions: N fertilizer, P fertilizer, pesticide, fuel, and electricity.</p>
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23 pages, 3924 KiB  
Article
Estimation of Greenhouse Gas Emissions and Analysis of Driving Factors in Jiangxi Province’s Livestock Industry from a Life Cycle Perspective
by Xingyue Chen, Qifeng Che, Guoxiong Chen, Tingting Hu, Jing Zhang and Qihong Tu
Sustainability 2025, 17(5), 2108; https://doi.org/10.3390/su17052108 - 28 Feb 2025
Viewed by 213
Abstract
As a significant source of greenhouse gas emissions, objectively understanding the quantity of emissions from the livestock industry and their spatiotemporal evolution is crucial for advancing low-carbon and green development in regional livestock industries. Therefore, based on the Life Cycle Assessment (LCA) method, [...] Read more.
As a significant source of greenhouse gas emissions, objectively understanding the quantity of emissions from the livestock industry and their spatiotemporal evolution is crucial for advancing low-carbon and green development in regional livestock industries. Therefore, based on the Life Cycle Assessment (LCA) method, this study estimated greenhouse gas emissions from the livestock industry across 11 municipal regions in Jiangxi Province from 2002 to 2022, revealing the spatiotemporal characteristics of these emissions. The study also employed the Logarithmic Mean Divisia Index (LMDI) model to analyze the influencing factors. The results showed that (1) between 2002 and 2022, total greenhouse gas emissions from Jiangxi Province’s livestock industry exhibited an upward trend, increasing from 13.52 million tons to 21.27 million tons, with an average annual growth rate of 2.36%. (2) During the study period, the spatial patterns of super-high-emission and light-emission zones remained relatively stable, while medium and heavy emission zones showed dynamic evolution. (3) Intensity effects, agricultural structural effects, and rural population size played a suppressive role in livestock greenhouse gas emissions, while regional development levels and urbanization levels were key drivers of increased emissions. Therefore, governments should accelerate the implementation of clean production models, enhance technological innovation, promote pollution reduction at the source, and develop differentiated livestock development strategies based on regional resource endowments and demographic–economic characteristics. Full article
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<p>Overview of the study area.</p>
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<p>System boundary.</p>
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<p>Proportion of GHG emissions from each segment.</p>
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<p>Proportion of total emissions from different livestock.</p>
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<p>Spatial distribution of greenhouse gas emissions from animal husbandry in Jiangxi Province. (<b>a</b>) 2002; (<b>b</b>) 2006; (<b>c</b>) 2010; (<b>d</b>) 2014; (<b>e</b>) 2018; (<b>f</b>) 2022.</p>
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<p>Proportion of GHG emissions from each segment in Jiangxi Province of emissions from each city in 2022.</p>
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<p>Proportion of emissions from different livestock and poultry in Jiangxi Province in 2022 as a percentage of emissions in each municipality.</p>
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21 pages, 1817 KiB  
Article
Driving Effects and Differences of Transportation Carbon Emissions in the Yangtze River Economic Belt
by Haichang Guan and Chengfeng Huang
Sustainability 2025, 17(4), 1636; https://doi.org/10.3390/su17041636 - 16 Feb 2025
Viewed by 390
Abstract
Identifying the driving effects and differentiated characteristics of transportation carbon emissions is crucial for developing targeted and differentiated emission reduction strategies and providing a scientific basis for the Yangtze River Economic Belt. This study adopted a “top-down” approach to account for the transportation [...] Read more.
Identifying the driving effects and differentiated characteristics of transportation carbon emissions is crucial for developing targeted and differentiated emission reduction strategies and providing a scientific basis for the Yangtze River Economic Belt. This study adopted a “top-down” approach to account for the transportation carbon emissions of the Yangtze River Economic Belt from 2000 to 2019 and constructed LMDI models and quantile regression models to estimate the driving effects and heterogeneity of influencing factors. The research results indicate the following: (1) The level of economic development is a key driving factor for transportation carbon emissions in the Yangtze River Economic Belt, with a cumulative effect of 160%. Upon inspection, the relationship between economic and transportation carbon emissions conforms to the environmental Kuznets curve. When the per capita transportation production value reaches CNY 7500, there is a “turning point” in transportation carbon emissions. (2) The population size has a driving effect on transportation carbon emissions, but as carbon emissions continue to increase, their marginal effects gradually diminish. (3) The energy structure and transportation structure have a significant inhibitory effect on transportation carbon emissions. The driving effect of the energy structure shows an “N” shape with quantile changes, while the transportation structure gradually converges. (4) Both energy intensity and transportation intensity show inhibitory effects, indicating that innovative energy substitution, optimization of transportation structure, and improvement of organizational efficiency are key ways to achieve carbon reduction in transportation. It is suggested that the Yangtze River Economic Belt should develop differentiated emission reduction paths in different regions, effectively balance economic development and carbon emission control, and promote the green and low-carbon transformation of the transportation system. Full article
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<p>Trends in the proportion of emissions derived from fossil energy consumption.</p>
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<p>Spatial distribution of transportation carbon emissions in the Yangtze River Economic Belt (2000/2010/2019).</p>
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<p>Changes in contribution rates of factors influencing transportation carbon emissions in the Yangtze River Economic Belt.</p>
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<p>Changes in quantile regression coefficients.</p>
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22 pages, 1819 KiB  
Article
Carbon Abatement Technology Transformation and Correlated Risks in the Airline Industry
by Lei Xu, Han Yin, Min Sun, Mengyu Wang, Kaiwen Shen and Jie Ji
Sustainability 2025, 17(4), 1399; https://doi.org/10.3390/su17041399 - 8 Feb 2025
Viewed by 534
Abstract
The airline industry is currently navigating a pivotal period characterized by rapid development and increasing global pressure to reduce carbon emissions. Airlines, as the first to be significantly impacted, must actively manage their carbon footprints, adopt carbon abatement technologies, and address the inherent [...] Read more.
The airline industry is currently navigating a pivotal period characterized by rapid development and increasing global pressure to reduce carbon emissions. Airlines, as the first to be significantly impacted, must actively manage their carbon footprints, adopt carbon abatement technologies, and address the inherent risks in this transformation. This paper examines the risk factors correlated with the technology transformation of carbon abatement and proposes effective abatement strategies. Using panel data of China Southern Airlines from 2009 to 2023 and applying the Logarithmic Mean Divisia Index (LMDI) method based on the Kaya identity, we analyze the differential impacts of various factors on unit carbon emissions. Multiple scenarios, derived from the influences of these factors, are constructed, and the Monte Carlo algorithm is employed to simulate the impact and volatility of correlated risks in the technology transformation for the abatement of carbon emissions. The findings are as follows: on the one hand, carbon emissions are strongly driven by energy consumption (0.99), flight volume (0.941), flight hours (0.931), transportation turnover (0.923), and take-off frequency (0.833). On the other hand, technology (56%) and scale (54.74%) significantly reduce unit carbon emissions, while take-off frequency negatively impacts emissions (−35.19%). Technology-related risks are controllable and relatively stable, whereas scale-related risks are highly uncertain. Additionally, operation-related risks can be partially hedged to ensure a certain level of risk controllability. Full article
(This article belongs to the Special Issue Green Supply Chain and Sustainable Operation Management)
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<p>Carbon abatement technology transformation and correlated risks.</p>
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<p>Annual trends in Southern Air operating effects.</p>
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<p>Annual changes in Southern Air transport turnover.</p>
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<p>Possible scenarios of carbon emissions of Southern Air in 2050.</p>
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26 pages, 6690 KiB  
Article
Key Determinants of Energy Intensity and Greenhouse Gas Emission Savings in Commercial and Public Services in the Baltic States
by Vaclovas Miskinis, Arvydas Galinis, Inga Konstantinaviciute, Viktorija Bobinaite, Jarek Niewierowicz, Eimantas Neniskis, Egidijus Norvaisa and Dalius Tarvydas
Energies 2025, 18(3), 735; https://doi.org/10.3390/en18030735 - 5 Feb 2025
Viewed by 565
Abstract
The improvement of energy efficiency (EE) and growing consumption of renewable energy sources (RES) in the commercial and public services sector are playing important roles in seeking to pursue sustainable development in the Baltic States and contributing to the transition to a low-carbon [...] Read more.
The improvement of energy efficiency (EE) and growing consumption of renewable energy sources (RES) in the commercial and public services sector are playing important roles in seeking to pursue sustainable development in the Baltic States and contributing to the transition to a low-carbon economy. This paper provides findings from a detailed analysis of energy intensity trends in economic sectors from 2005 to 2022 in three countries, considering the role of transformations in the energy and climate framework of the European Union (EU). Based on the Fisher Ideal Index application, the different contributions from improving EE and structural changes are revealed. The dominant role of EE improvements in energy savings is identified in Estonia and Lithuania, and structural changes are dominant in Latvia. Changes in energy-related greenhouse gas (GHG) emissions in the commercial and public services sector and the main determinants of their reduction are examined. Based on applying the Kaya identity and the logarithmic mean Divisia index (LMDI) method, decreasing energy intensity is the most important determinant in all three countries. Due to the different extents of RES deployment, their role was very important in Estonia and Latia but was less effective in Lithuania. Reduction in emission intensity has the largest impact in Latvia. The GHG emissions decreased by 34.1% in Estonia, 17.5% in Latvia, and 16.7% in Lithuania. The results confirm the need for new policies, implementation of relevant EE measures, and the growing contribution from RES in Latvia and Lithuania. Full article
(This article belongs to the Special Issue Energy Efficiency Assessments and Improvements)
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<p>The logical research scheme (made by the authors).</p>
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<p>Index of GDP growth in the EU-27 and in the Baltic States [<a href="#B56-energies-18-00735" class="html-bibr">56</a>].</p>
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<p>Changes in final energy intensity in economic sectors (own estimations).</p>
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<p>Changes in final energy intensity in sectors of economies (own estimations).</p>
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<p>Changes in final energy intensity in sectors of economies (own estimations).</p>
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<p>Saving of final energy use in sectors of national economies (own estimations).</p>
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<p>Saving of final energy use in sectors of national economies (own estimations).</p>
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<p>Changes in energy-related GHG emissions in the commercial and public services sector and their determinants in the Baltic States (own estimations).</p>
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<p>Changes in energy-related GHG emissions in the commercial and public services sector and their determinants in the Baltic States (own estimations).</p>
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<p>Decomposition dynamics and changes in GHG emissions in the commercial and public services sector of the Baltic States (own estimation).</p>
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<p>Decomposition dynamics and changes in GHG emissions in the commercial and public services sector of the Baltic States (own estimation).</p>
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<p>Changes in GHG emissions per employee in the commercial and public services sector (own estimation).</p>
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23 pages, 7013 KiB  
Article
Spatiotemporal Characteristics of Carbon Emissions from Construction Land and Their Decoupling Effects in the Yellow River Basin, China
by Zhaoli Du, Xiaoyu Ren, Weijun Zhao and Chenfei Zhang
Land 2025, 14(2), 320; https://doi.org/10.3390/land14020320 - 5 Feb 2025
Viewed by 454
Abstract
Carbon emissions (CE) from expanding construction land (CL), a vital territory for human production and habitation, have contributed to climate change worldwide. The Yellow River Basin (YRB), an essential economic region and energy supply base in China, is experiencing rapid urbanization, and the [...] Read more.
Carbon emissions (CE) from expanding construction land (CL), a vital territory for human production and habitation, have contributed to climate change worldwide. The Yellow River Basin (YRB), an essential economic region and energy supply base in China, is experiencing rapid urbanization, and the contradiction between economic development and ecological protection is increasingly acute. Consequently, a thorough examination of the spatial and temporal change features of carbon emissions from construction land (CECL) and its decoupling from economic growth (EG) is crucial for the maintaining development of the region. This study adopts the IPCC carbon emission coefficient approach for measuring the CECL in the YRB from 2010 to 2021. The temporal and spatial variation features of CECL in the YRB were revealed using ArcGIS software and the standard deviation ellipse (SDE) model. The decoupling effect between CECL and EG was analyzed using the Tapio decoupling model and innovatively combined with the Logarithmic Mean Divisia Index (LMDI) method to explore the influence of five main drivers on the decoupling effect. This study found that: (1) The CECL rose from 2.463 billion tons in 2010 to 3.329 billion tons in 2021. The spatial layout of CECL is “high in the east and low in the west”. (2) The SDE of CECL is distributed in the direction of “northeast to southwest”, and the gravity center’s moving path is “northwest to northeast to northwest”; (3) weak decoupling (WD) is the main decoupling state between CECL and EG; (4) the economic output effect and the construction land (CL) scale effect are the two main factors inhibiting the decoupling of CECL, while the energy intensity effect, the population density effect, and the energy structure effect are the main elements motivating the decoupling of CECL. This study provides specific references and bases for the YRB in China and other countries and regions with similar levels of development in promoting green and ecologically friendly initiatives and achieving low-carbon utilization of regional land and sustainable development. Full article
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<p>Study location overview map.</p>
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<p>Research framework of this paper.</p>
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<p>Trends in CL area (<b>a</b>), CECL and annual growth rate (<b>b</b>) (between 2010 and 2021).</p>
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<p>CL area (<b>a</b>), and CECL in the nine provinces of the YRB (<b>b</b>) (between 2010 and 2021).</p>
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<p>Spatial distribution pattern of CECL in the YRB (between 2010 and 2021).</p>
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<p>Changes in the CL area in the YRB (between 2010 and 2021).</p>
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<p>SDE and its central migration of CECL in YRB (between 2010 and 2021).</p>
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<p>Trend of decoupling index in the YRB.</p>
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<p>Decoupling status in the nine provinces of the YRB (between 2010 and 2021).</p>
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<p>Decoupling status percentage in nine provinces of the YRB (between 2010 and 2021).</p>
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<p>Spatial pattern evolution of decoupling status of CECL in the YRB (between 2010 and 2021).</p>
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<p>LMDI decomposition results of the decoupling index of the YRB.</p>
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<p>LMDI decomposition results of the decoupling index in 9 provinces of the YRB.</p>
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20 pages, 5594 KiB  
Article
System Dynamics-Based Integrated Benefit Analysis of Low-Carbon Management Process of Municipal Solid Waste
by Genping Zhang, Gang Lu, Kaili Liu and Hongbo Liu
Sustainability 2025, 17(3), 1193; https://doi.org/10.3390/su17031193 - 1 Feb 2025
Viewed by 976
Abstract
With rapid economic development, the amount of the municipal solid waste (MSW) generated has increased dramatically. To improve the socio-economic benefits and environmental impacts of the low-carbon management of MSW, it is crucial to identify the drivers of Greenhouse Gas (GHG) emissions from [...] Read more.
With rapid economic development, the amount of the municipal solid waste (MSW) generated has increased dramatically. To improve the socio-economic benefits and environmental impacts of the low-carbon management of MSW, it is crucial to identify the drivers of Greenhouse Gas (GHG) emissions from MSW treatment and assess their systematic and comprehensive benefits. The factor decomposition method is one of the most commonly used methods focused on identifying GHG emission-influencing factors, while the system dynamics (SD) method is commonly used to analyze the causal relationships between linear and nonlinear variables in complex dynamic systems. Unlike existing studies that account for and evaluate MSW from a static perspective, this paper innovatively combines the LMDI-SD model to identify and quantify the GHG emission drivers of MSW and evaluate the benefits of decarbonizing the MSW management in China from a comprehensive and systematic perspective. The results show that the dominant factor driving MSW GHG emissions from 2010 to 2022 is the economic development factor, ∆EED, while the intensity of MSW generation ∆EGI and the structure of MSW treatment ∆ETS play a stronger inhibiting role. Based on this, the SD model is constructed to simulate different scenarios, and the analysis shows that increasing the waste separation rate (S3) is the most effective measure to improve the socio-economic benefits and environmental impacts of the system. Compared with the base scenario, the socio-economic benefits and environmental impacts in 2050, for example, are increased by 82.8% and 43.4%, respectively. Improving the utilization rate of landfill gas (S1), reducing the per capita amount of MSW generated (S4) and increasing the incineration rate of MSW (S2) also have significant advantages for the improvement of benefits. Finally, some policy recommendations for the improvement of the comprehensive benefits of low-carbon MSW management systems are proposed to help policymakers make appropriate decisions. Full article
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<p>Components related to the assessment of the benefits of the low-carbon MSW management process.</p>
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<p>MSW generation and GHG emission accounting subsystem.</p>
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<p>Socio-economic benefits assessment subsystem.</p>
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<p>Environmental impact assessment subsystem.</p>
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<p>2010–2022 China’s MSW treatment process GHG emissions value changes and the contribution of each driving factor.</p>
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<p>Socio-economic benefits of China’s MSW low-carbon management process under different scenarios in 2020–2050.</p>
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<p>Cumulative socio-economic benefits of China’s MSW low-carbon management process under different in 2020–2025.</p>
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<p>Environmental impacts of China’s MSW low-carbon management process under different scenarios in 2020–2050.</p>
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<p>Cumulative environmental impacts of China’s MSW low-carbon management process under different scenarios in 2020–2050.</p>
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<p>Composition of environmental impacts of MSW treatment processes under different scenarios in 2020, 2030, 2040 and 2050.</p>
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27 pages, 4768 KiB  
Article
Analysis of Spatial Differences and Influencing Factors of Carbon-Emission Reduction Efficiency of New-Energy Vehicles in China
by Lingyao Wang, Taofeng Wu and Fangrong Ren
Energies 2025, 18(3), 635; https://doi.org/10.3390/en18030635 - 30 Jan 2025
Viewed by 429
Abstract
As new-energy vehicles (NEVs) gradually gain public attention, their carbon-reduction issues have become a focal point in academia. This study evaluates the carbon-reduction efficiency of NEVs in 21 Chinese provinces using an improved three-stage DEA model, analyzes spatial disparities with the Dagum Gini [...] Read more.
As new-energy vehicles (NEVs) gradually gain public attention, their carbon-reduction issues have become a focal point in academia. This study evaluates the carbon-reduction efficiency of NEVs in 21 Chinese provinces using an improved three-stage DEA model, analyzes spatial disparities with the Dagum Gini coefficient, and decomposes carbon-emission factors using the LMDI method. Results show that the overall carbon-reduction efficiency is low, with an average value of only 0.266. Significant differences exist in production- and consumption-stage efficiencies across regions. Shanxi Province performed the best, with efficiency scores of 1 in both stages, while the carbon-reduction stage showed the lowest efficiency, ranging between 0.2 and 0.3 in most regions. The central region exhibited the highest carbon-reduction efficiency, followed by the western and eastern regions, primarily influenced by intra-regional disparities. Energy intensity significantly suppresses carbon emissions, followed by energy structure, while economic development and population size positively contribute to carbon emissions. This study provides theoretical support for regional governments to formulate policies related to the NEV industry and offers practical guidance for its further development. Full article
(This article belongs to the Special Issue CO2 Emissions from Vehicles (Volume II))
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<p>Structure of the research methodology.</p>
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<p>Carbon-reduction efficiency of NEVs in various provinces.</p>
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<p>Annual average of three stages of efficiency of new-energy vehicles.</p>
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<p>Average value of the three stages of efficiency in the provinces.</p>
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<p>Key indicator efficiency: (<b>a</b>) Carbon Emissions; (<b>b</b>) Number of active patents; (<b>c</b>) Number of new-energy vehicles produced.</p>
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<p>Regional efficiency of city clusters.</p>
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<p>Inter-regional trends in the Gini coefficient.</p>
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<p>Decomposition of the contribution of factors influencing carbon emissions (%).</p>
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<p>Changes in consumption of selected energy sources (10,000 tons of standard coal).</p>
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<p>Share of energy consumption by province.</p>
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29 pages, 5916 KiB  
Article
The Coordinated Development and Identification of Obstacles in the Manufacturing Industry Based on Economy–Society–Resource–Environment Goals
by Jiaojiao Yang, Ting Wang, Min Zhang, Yujie Hu and Xinran Liu
Systems 2025, 13(2), 78; https://doi.org/10.3390/systems13020078 - 26 Jan 2025
Viewed by 514
Abstract
Given the deficiencies in the definition of connotation, the construction of index systems, and the coordination of targets within the research on sustainable development in the manufacturing industry, an evaluation index system for sustainable development has been established. This system includes economic benefits, [...] Read more.
Given the deficiencies in the definition of connotation, the construction of index systems, and the coordination of targets within the research on sustainable development in the manufacturing industry, an evaluation index system for sustainable development has been established. This system includes economic benefits, social benefits, resource management, and environmental goals and is built upon a clear definition of the concept’s connotation. The CRITIC–entropy–TOPSIS–CCDM approach is employed for the computation of the coordinated development level of the manufacturing industry. To identify the main factors influencing the coupling coordination degree (CCD) from a mechanistic and compositional point of view, a logarithmic mean divisia index (LMDI) is used. Furthermore, the obstacle degree model analyzes the factors that restrict subsystem development. The results show the following. (1) The coordinated development level of the Chinese manufacturing industry has been maintained at 0.6–0.7, while the CCD of Hainan, Qinghai, and Xinjiang remains to be enhanced. (2) The key factor affecting the CCD is the coupling degree. The evaluation value of the economy and employment system determines the trend of coordinated development in the regional manufacturing industry. (3) The economic and employment scenarios in most provinces (cities) led to a significant decrease in the CCD compared to the baseline scenario, with average growth rates of −10.55% and −12.69%. This suggests that policymakers’ priorities significantly influence the CCD. The research presents a theoretical framework for assessing the sustainability of the manufacturing industry, offering valuable insights to guide the industry towards more sustainable practices. Full article
(This article belongs to the Special Issue Data Analytics for Social, Economic and Environmental Issues)
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<p>Research flowchart.</p>
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<p>Study area.</p>
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<p>The development level of subsystems in four regions over the years. (<b>A</b>) Economic subsystem; (<b>B</b>) employment subsystem; (<b>C</b>) energy subsystem; (<b>D</b>) water subsystem; (<b>E</b>) carbon emission subsystem.</p>
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<p>Spatial distribution of subsystem development levels: ((<b>A</b>) economic subsystem in 2003; (<b>B</b>) economic subsystem in 2009; (<b>C</b>):economic subsystem in 2015; (<b>D</b>) economic subsystem in 2020; (<b>E</b>) employment system in 2003; (<b>F</b>) employment system in 2009; (<b>G</b>) employment system in 2015; (<b>H</b>) employment system in 2020; (<b>I</b>) energy subsystem in 2003; (<b>J</b>) energy subsystem in 2009; (<b>K</b>) energy subsystem in 2015; (<b>L</b>) energy subsystem in 2020; (<b>M</b>) water subsystem in 2003; (<b>N</b>) water subsystem in 2009; (<b>O</b>) water subsystem in 2015; (<b>P</b>) water subsystem in 2020; (<b>Q</b>) carbon subsystem in 2003; (<b>R</b>) carbon subsystem in 2009; (<b>S</b>) carbon subsystem in 2015; (<b>T</b>) carbon subsystem in 2020).</p>
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<p>Coupling coordination degree and coefficient of variation of four regions over the years.</p>
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<p>Spatial distribution of the coupling coordination degree in (<b>A</b>) 2003, (<b>B</b>) 2009, (<b>C</b>) 2015, and (<b>D</b>) 2020.</p>
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<p>Decomposition of the coupling coordination degree: (<b>A</b>) from the mechanistic perspective; (<b>B</b>) from the composition perspective.</p>
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<p>Cumulative obstacle index of 30 provinces regarding subsystems.</p>
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18 pages, 4422 KiB  
Article
Spatial–Temporal Dynamics and Drivers of Crop Water Footprint in Xinjiang, China
by Xiaoyu Zhang, Zhenhua Wang, Jian Liu, Wenhao Li, Haixia Lin, Tehseen Javed, Xuehui Gao, Guopeng Qin, Huadong Liu, Hengzhi Wang, Yifan Liu and Hanchun Ye
Agronomy 2025, 15(2), 296; https://doi.org/10.3390/agronomy15020296 - 25 Jan 2025
Viewed by 538
Abstract
Efficient allocation and utilization of water resources are critical for the sustainable development of agriculture in arid regions, particularly those heavily reliant on irrigation. Xinjiang, one of China’s major agricultural regions, faces significant challenges in managing water resources due to its arid climate [...] Read more.
Efficient allocation and utilization of water resources are critical for the sustainable development of agriculture in arid regions, particularly those heavily reliant on irrigation. Xinjiang, one of China’s major agricultural regions, faces significant challenges in managing water resources due to its arid climate and dependence on irrigation. This study investigates the spatial–temporal dynamics of crop water footprint (CWF) and its driving factors in Xinjiang. Unlike previous studies on Xinjiang that primarily focus on total water footprint, this research emphasizes the crop blue water footprint (CWFB) to provide a more precise assessment of agricultural water allocation and consumption. Using the CROPWAT 8.0 model, the CWF of 14 prefectures in Xinjiang were analyzed for the period 2000–2020. Focusing primarily on the crop blue water footprint (CWFB), the study employed the Logarithmic Mean Divisia Index (LMDI) model to identify key drivers and their mechanisms. Results reveal that Xinjiang’s average annual CWF is 179.02 Gm3, with CWFB contributing 90.22% and the crop green water footprint (CWFG) accounting for. 10.05%. The CWFB showed an initial increase followed by stabilization, with Southern Xinjiang being the largest contributor, trailed by Northern and Eastern Xinjiang. Among the 14 prefectures, the top seven accounted for 90.46% of CWFB. Cotton, wheat, and maize were the major crops, comprising 47.80%, 23.14%, and 21.45% of the total blue water footprint, respectively. This study identifies the dominant role of economic effect and water use efficiency effect in driving changes in CWFB through its analysis of the driving factors. Understanding the spatial–temporal changes and key drivers of blue water consumption helps regions adjust cropping structures and agricultural water resource allocation patterns to ensure sustainable agricultural development. The findings not only offer valuable implications for policymakers and stakeholders in Xinjiang but also provide references for other arid and semiarid regions facing similar challenges in agricultural water resource management. Full article
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<p>Map of the study areas.</p>
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<p>Diagram of the steps of the analysis process.</p>
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<p>Yearly crop water footprint of Xinjiang (2000–2020). The blue bar representing (<span class="html-italic">CWFT</span>) indicates the total crop water footprint, with the scale on the left <span class="html-italic">Y</span>-axis. The red square line representing (<span class="html-italic">CWFB</span>) and the red triangular line representing (<span class="html-italic">CWFG</span>) indicate the crop blue water footprint and the crop green water footprint, respectively, with the scale on the right <span class="html-italic">Y</span>-axis. The units are Gm<sup>3</sup>.</p>
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<p>Mann–Kendall statistical test analysis of crop blue water footprint from 2000–2020. The blue line with square markers represents UF, the black line with circle markers represents UB, and the two dashed lines above and below the Y = 0 axis represent the ±1.96 significance level lines.</p>
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<p>Crop blue water footprint of major crops from 2000 to 2020. The bars, colored differently from left to right, represent the <span class="html-italic">CWFB</span> in Gm<sup>3</sup> for cotton, wheat, corn, alfalfa, and rice for each year, respectively.</p>
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<p>Spatial distribution of <span class="html-italic">CWFB</span> for 2000, 2008, 2014, and 2020, along with the 2000–2020 annual average crop blue water footprint. The <span class="html-italic">CWFB</span> is classified into five levels, with different colors ranging from lighter to darker. The letters a, b, c, and d denote Urumqi, Changji, Karamay, and Kizilsu, respectively.</p>
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<p>Annual average <span class="html-italic">CWFB</span> for the three major regions, fourteen prefectures, and major crops in Xinjiang from 2000 to 2020. Values in parentheses represent the corresponding annual average crop blue water footprint in Gm<sup>3</sup>.</p>
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<p>Contributions of the five drivers of <span class="html-italic">CWFB</span> from 2000 to 2020. Total indicates the amount of change in <span class="html-italic">CWFB</span>, PF indicates the amount of change in <span class="html-italic">CWFB</span> due to changes in the population effect, WUEF indicates the amount of change in <span class="html-italic">CWFB</span> due to changes in the water use efficiency effect, EF indicates the amount of change in <span class="html-italic">CWFB</span> due to changes in the economic effect, WSF indicates the amount of change in <span class="html-italic">CWFB</span> due to changes in the water use structure effect, and TF indicates the amount of change in <span class="html-italic">CWFB</span> due to changes in technology effect. WSF denotes the change in <span class="html-italic">CWFB</span> caused by the change in water use structure effect, and TF denotes the change in <span class="html-italic">CWFB</span> caused by the change in technology effect.</p>
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<p>Average contribution of drivers, 2000–2020. The value for each factor indicates the average amount of change in <span class="html-italic">CWFB</span> caused by its change.</p>
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28 pages, 22057 KiB  
Article
Quantifying Socio-Regional Variability via Factor Analysis over China: Optimizing Residential Sector Emission Reduction Pathways
by Yu Zhao and Prasanna Divigalpitiya
Environments 2025, 12(2), 37; https://doi.org/10.3390/environments12020037 - 22 Jan 2025
Viewed by 732
Abstract
Policy synergy, the evidence-based coordination of public policies, can aid in more rapidly achieving air pollutant and carbon dioxide (CO2) emission reduction targets. Using logarithmic mean Divisia index (LMDI) decomposition, coupling coordination degree (CCD), and geographically and temporally weighted regression (GTWR) [...] Read more.
Policy synergy, the evidence-based coordination of public policies, can aid in more rapidly achieving air pollutant and carbon dioxide (CO2) emission reduction targets. Using logarithmic mean Divisia index (LMDI) decomposition, coupling coordination degree (CCD), and geographically and temporally weighted regression (GTWR) models, we analyzed the emission characteristics, drivers, and reduction pathways of residential air pollution across 30 Chinese provinces from 2001 to 2020. The southern provinces produced more air pollution than the northern provinces, with the gap widening after 2015. In the residential sector, energy emission factors (LMDI decomposition result, 686,681.9) and population size (14,331) had greater impacts on air pollutant emissions than the energy structure, energy intensity, synergies, or GDP per capita. The GTWR analysis of the CCD mechanism indicated that hydroelectricity and urbanization enhanced coupling coordination in the southeast. Meanwhile, in the west, coupling coordination was improved by R&D investment, government spending on industrial pollution control, electricity consumption, per capita cropland, temperature, and urbanization. This analysis provides a valuable reference for optimizing emission reduction strategies. Full article
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<p>Analysis steps and processes.</p>
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<p>Geographic divisions for the purpose of this study.</p>
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<p>Rates of change in pollutant emissions. Note: vertical dotted lines indicate 2013.</p>
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<p>Changes in the relative contribution of sources and types of pollutants. Note: The subfigures (<b>a</b>–<b>c</b>) show the variations in the contribution of emission sources from the residential sector, while (<b>d</b>) presents the changes in the proportion of different pollutants.</p>
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<p>North–South comparison of North–South emissions. Note: T1, 2001–2005; T2, 2006–2010; T3, 2011–2015; and T4, 2016–2020. The subfigures (<b>a</b>–<b>j</b>) show sources of PM2.5, PM10, SO<sub>2</sub>, NOx, VOC, OC, BC, NH<sub>3</sub>, CO, CO<sub>2</sub>, separately.</p>
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<p>North–South comparison of pollution sources. Note: Subfigures (<b>a</b>–<b>c</b>) illustrate the proportion of pollution sources in northern regions in 2020, southern regions in 2020, and a comparison of the average values between the north and south, respectively.</p>
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<p>Emissions of provinces and cities in 2020. Note: areas in the north are colored blue and those in the south pink. The petals of the rose chart represent the combined emissions of air pollutants and CO<sub>2</sub>, with different petal colors indicating the emission levels of various provinces and cities.</p>
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<p>North-–south emission driving factors: H, AP emissions per unit of CO<sub>2</sub>; R, CO<sub>2</sub> emissions per unit of AP; P, emission factor; Z, population. Numbers indicate the role of the H, R, P, and Z factors in emissions. South and north represent the averages of the north and south provinces, respectively. Subfigures (<b>a</b>–<b>d</b>) illustrate the contribution of the four factors to PM2.5, PM₁₀, BC, and OC emissions in northern regions, while subfigures (<b>e</b>–<b>h</b>) present the contributions of these factors to the same pollutants in southern regions.</p>
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<p>Contribution of seven factors to PM<sub>2.5</sub> emissions in 30 provinces. Note: This visually represents the contribution of seven factors to PM<sub>2.5</sub> emissions across 30 provinces, with each province’s contributions depicted by specific numerical values within concentric circles. For instance, Beijing’s contributions are indicated by the second concentric circle with a value of 4 × 10<sup>2</sup> and the fourth circle with 8 × 10<sup>2</sup>. This graphical representation allows for a clear distinction between the northern provinces, labeled (1)–(15), and the southern provinces, labeled (16)–(30). For detailed data, please refer to <a href="#environments-12-00037-t003" class="html-table">Table 3</a>, <a href="#environments-12-00037-t004" class="html-table">Table 4</a>, <a href="#environments-12-00037-t005" class="html-table">Table 5</a> and <a href="#environments-12-00037-t006" class="html-table">Table 6</a>.</p>
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<p>Distribution diagram of factors driving the degree of coupling based on averages in the period of 2001–2020. Regression coefficients with <span class="html-italic">p</span>-values &gt; 0.1 are excluded. The legend illustrates each factor’s coefficient of influence on the coupling degree, where positive values indicate a promoting effect and negative values suggest a weakening impact. Subfigures (<b>a</b>–<b>i</b>) respectively depict the spatial distribution of the impact coefficients of R&amp;D investment, environmental regulation, average years of education, energy structure, GDP per capita, per capita cropland, hydroelectricity generation, temperature, and urbanization on CCD.</p>
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13 pages, 5590 KiB  
Article
An LMDI-Based Analysis of Carbon Emission Changes in China’s Waterway Transportation Sector
by Shanshan Zheng, Cheng Chen and Sikai Xie
Sustainability 2025, 17(1), 325; https://doi.org/10.3390/su17010325 - 4 Jan 2025
Viewed by 679
Abstract
The waterway transportation industry, recognized for its high capacity, cost-effectiveness, and energy efficiency, plays a vital role in global freight transport and trade. In China, it serves as a key pillar supporting the national economy and foreign trade. However, its heavy dependence on [...] Read more.
The waterway transportation industry, recognized for its high capacity, cost-effectiveness, and energy efficiency, plays a vital role in global freight transport and trade. In China, it serves as a key pillar supporting the national economy and foreign trade. However, its heavy dependence on fossil fuels has intensified carbon emission challenges, creating significant barriers to achieving sustainable development goals. This study employs Input-Output Analysis and the Logarithmic Mean Divisia Index model to examine the changes in carbon emissions and their driving factors in China’s waterway transportation industry from 2002 to 2020, while also exploring potential pathways for emission reduction. The findings reveal the following: (1) From 2002 to 2020, despite a substantial rise in total carbon emissions, the industry has been progressively transitioning towards a low-carbon trajectory through the adoption of clean energy technologies and optimization of its energy structure. (2) Economic scale effects have been the primary drivers of carbon emission growth, with population-scale effects playing a lesser role. Since 2011, the implementation of green technologies and low-carbon management strategies has effectively stabilized emission growth rates. (3) Improvements in energy carbon intensity and transportation energy intensity have significantly reduced carbon emissions. Moreover, the promotion of clean energy technologies and energy-saving measures has substantially lowered the industry’s carbon emission intensity. Full article
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<p>Carbon Emissions by Energy Type in China’s Waterway Transportation Industry.</p>
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<p>Decomposition of Carbon Emission Factors in China’s Waterway Transportation Industry (2002–2020).</p>
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<p>Contribution of Energy Carbon Intensity in China’s Waterway Transportation Industry (2002–2020).</p>
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<p>Contribution of Energy Intensity in China’s Waterway Transportation Industry (2002–2020).</p>
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<p>Contribution of Industry Scale in China’s Waterway Transportation Industry (2002–2020).</p>
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<p>Contribution of Economic Scale in China’s Waterway Transportation Industry (2002–2020).</p>
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<p>Contribution of Population Scale Effect in China’s Waterway Transportation Industry (2002–2020).</p>
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18 pages, 20230 KiB  
Article
Understanding Emission Trends, Regional Distribution Differences, and Synergistic Emission Effects in the Transportation Sector in Terms of Social Factors and Energy Consumption
by Yu Zhao and Prasanna Divigalpitiya
Sustainability 2024, 16(24), 10971; https://doi.org/10.3390/su162410971 - 13 Dec 2024
Viewed by 842
Abstract
China’s transportation sector plays a significant role in reducing carbon dioxide (CO2) and air pollution. Previous studies have predominantly utilized scenario analysis to forecast emissions for the next 30 to 50 years based on coefficients from a base year. To elucidate [...] Read more.
China’s transportation sector plays a significant role in reducing carbon dioxide (CO2) and air pollution. Previous studies have predominantly utilized scenario analysis to forecast emissions for the next 30 to 50 years based on coefficients from a base year. To elucidate the current state of gas emissions in the transportation sector, this study employed panel data for 10 types of gas emissions from 2001 to 2020, analyzing their emission characteristics, tendencies, and synergistic effects. Utilizing the Kaya equation and the logarithmic mean division index (LMDI) decomposition method, we developed a model of pollutant emissions that considers the synergistic effects, pollution emission intensity, energy mix, energy consumption intensity, and population. The results show that all pollutants in the transportation sector decreased except for NH3 and CO2. There was a synergistic effect between air pollutants and CO2 emissions, but the reduction was not significant. From 2013 to 2020, the transportation sector shifted from a high emission intensity with low synergy to a low emission intensity with high synergy. The results indicate that off-road mobile vehicles, on-road diesel vehicles, and motorcycles became the main source of emissions from transportation in certain provinces, and a key area requiring attention in policy development. Gasoline consumption was identified as the primary contributor to the significant increase in synergistic emission variability in the transportation sector. These results provide policymakers with practical ways to optimize emission reduction pathways. Full article
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<p>Analysis structure. Note: this study analyzed 10 types of emissions from four pollution sources. On the left side is the sequence of research steps, while the corresponding research methods are presented on the right side (source: created by the authors).</p>
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<p>Sources of pollutant emissions in 2020.</p>
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<p>Sources of pollutants and changes in emissions. Note: The subfigures (<b>a</b>–<b>j</b>) show sources of CO<sub>2</sub>, CO, PM<sub>2.5</sub>, PM<sub>10</sub>, BC, OC, VOC, NOx, SO<sub>2</sub>, NH<sub>3</sub>, separately.</p>
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<p>Changes relative to the previous year.</p>
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<p>Emission intensity and synergistic effects in 2013 and 2020. Note: The subfigures (<b>a</b>–<b>f</b>) show synergistic effect of the pollutant with CO<sub>2</sub>. The red dots mark the average of the 30 provinces and cities.</p>
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<p>Variations in emission origins across four provinces and cities. Note: The subfigures (<b>a</b>–<b>f</b>) show sources of PM<sub>2.5</sub>, PM<sub>10</sub>, NOx, VOC, SO<sub>2</sub>, CO<sub>2</sub>, separately.</p>
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<p>Theil index with population and gasoline as the base.</p>
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<p>Province categories.</p>
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<p>Emission origins of the seven major regions.</p>
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