Abstract
Resource-based cities are important strategic bases for securing resources in China and have made great contributions to the country’s economic development. Long-term extensive resource development has made resource-based cities an important region constraining China from achieving comprehensive low-carbon development. Therefore, it is of great significance to explore the low-carbon transition path of resource-based cities for their energy greening, industrial transformation, and high-quality economic development. This study compiled the CO2 emission inventory of resource-based cities in China from 2005 to 2017, explored the contribution to CO2 emissions from three perspectives (driver, industry, and city), and predicted the peak of CO2 emissions in resource-based cities. The results show that resource-based cities contribute 18.4% of the country’s GDP and emit 44.4% of the country’s CO2 and that economic growth and CO2 emissions have not yet been decoupled. The per capita CO2 emissions and emission intensity of resource-based cities are 1.8 times and 2.4 times higher than the national average, respectively. Economic growth and energy intensity are the biggest drivers and main inhibitors of CO2 emissions growth. Industrial restructuring has become the biggest inhibitor of CO2 emissions growth. Based on the different resource endowments, industrial structures, and socio-economic development levels of resource-based cities, we propose differentiated low-carbon transition pathways. This study can provide references for cities to develop differentiated low-carbon development paths under the “double carbon” target.
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Data availability
The 84 resource-based cities are listed in Table 1. The types of fossil fuels and industrial processes are presented in Tables 2 and 3, respectively. The 47 socioeconomic sectors are listed in Table 4. The CO2 emission inventories of resource-based cities are available from the corresponding author on reasonable request.
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Funding
This work was supported by the Guangdong Basic and Applied Basic Research Foundation (2020A1515011230) and the Humanities and Social Science Foundation of the Ministry of Education of China (16YJCZH162).
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Kejun Li: Formal analysis, methodology, validation, visualization, writing—original draft preparation. Ya Zhou: Conceptualization, supervision, funding acquisition, methodology, formal analysis, resources, validation, writing—review and editing. Xuanhao Huang: Formal analysis, writing—review and editing. Huijuan Xiao: Formal analysis, writing—review and editing. Yuli Shan: writing—review and editing.
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Appendix
Appendix
Appendix 1. GM(1,1) model construction and accuracy test
The modeling process for the GM(1,1) model is as follows.
For a sequence X(0)
its Accumulating Generation Operational Sequence (AGO Sequence) is
where \({X}^{(1)}(k)={\sum}_1^k{X}^{(0)}(t),\kern0.5em k=1,2,3,\cdot \cdot \cdot, \kern0.5em n\)
Establish the first-order linear differential equation of X(1)(k), i.e., GM(1,1) model:
Its differential equation can be written as:
The matrix form is:
Solve by least squares method \(\hat{a}\),
Substituting \(\hat{a}\) into \(\frac{dx^{(1)}}{dt}+a{x}^{(1)}=u\) (GM(1,1) model) and solving for it, we get:
Model accuracy test:
Relative residual Q-test:
Variance ratio C-test:
Where \(\overline{X}=\frac{1}{n}{\sum}_{k=1}^n{X}^{(0)}(k)\),\(\overline{e}=\frac{1}{n}{\sum}_{k=1}^ne(k)\)
Small error probability P-test
Accuracy prediction level
Prediction accuracy | Excellent | Qualified | Barely qualified | Unqualified |
---|---|---|---|---|
Q | <0.01 | <0.05 | <0. 1 | <0.2 |
C | <0.35 | <0.5 | <0.65 | ≥ 0.65 |
P | >0.95 | >0.8 | >0.7 | ≤ 0.7 |
Appendix 2. Supplementary table
Appendix 3. Supplementary figure
See Fig. 10
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Li, K., Zhou, Y., Huang, X. et al. Low-carbon development pathways for resource-based cities in China under the carbon peaking and carbon neutrality goals. Environ Sci Pollut Res 31, 10213–10233 (2024). https://doi.org/10.1007/s11356-023-28349-4
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DOI: https://doi.org/10.1007/s11356-023-28349-4