Regional Sustainability ›› 2022, Vol. 3 ›› Issue (4): 356-372.doi: 10.1016/j.regsus.2022.11.006cstr: 32279.14.j.regsus.2022.11.006
• Full Length Article • Previous Articles Next Articles
LIU Weia,*(), JIA Zhijiea, DU Menga, DONG Zhanfengb, PAN Jieyua, LI Qinruia, PAN Linyana, Chris UMOLEa
Received:
2022-07-20
Revised:
2022-11-21
Accepted:
2022-11-29
Published:
2022-12-30
Online:
2023-01-31
Contact:
LIU Wei
E-mail:weling9@163.com
LIU Wei, JIA Zhijie, DU Meng, DONG Zhanfeng, PAN Jieyu, LI Qinrui, PAN Linyan, Chris UMOLE. Influencing factors and contribution analysis of CO2 emissions originating from final energy consumption in Sichuan Province, China[J]. Regional Sustainability, 2022, 3(4): 356-372.
Table 1
Various reference coefficients for the different fuel types."
Fuel type | B | S | A | R |
---|---|---|---|---|
Raw coal | 20,934 kJ/kg | 0.7143 kgce/kg | 26.37 t C/TJ | 94.00% |
Coal washed and dressed | 26,377 kJ/kg | 0.9000 kgce/kg | 25.41 t C/TJ | 93.00% |
Coke | 28,470 kJ/kg | 0.9714 kgce/kg | 29.50 t C/TJ | 93.00% |
Crude oil | 41,868 kJ/kg | 1.4286 kgce/kg | 20.10 t C/TJ | 98.00% |
Gasoline | 43,124 kJ/kg | 1.4714 kgce/kg | 18.90 t C/TJ | 98.00% |
Kerosene | 43,124 kJ/kg | 1.4714 kgce/kg | 19.60 t C/TJ | 98.00% |
Diesel oil | 42,705 kJ/kg | 1.4571 kgce/kg | 20.20 t C/TJ | 98.00% |
Fuel oil | 41,868 kJ/kg | 1.4286 kgce/kg | 21.10 t C/TJ | 98.00% |
Liquefied petroleum gas (LPG) | 50,242 kJ/kg | 1.7143 kgce/kg | 17.20 t C/TJ | 98.00% |
Natural gas | 32,238 kJ/m3 | 1.3300 kgce/m3 | 15.30 t C/TJ | 99.00% |
Table 2
Definition of variables in Equations 3-10."
Variable | Definition | Unit | Variable | Definition | Unit |
---|---|---|---|---|---|
i | Industrial structure. i=1, agriculture, forestry, animal husbandry and fishery sector; i=2, industry sector; i=3, construction sector; i=4, transportation, storage and post sector; i=5, wholesale, retail trade, hotels and catering service sector; i=6, other service sectors. | - | ΔC | CO2 emission variation (ΔC=ΔCt-ΔC0, where 0 indicates the base year and t denotes the target year) | 104 t |
P | Resident population | 104 | ΔCP | Contribution of the population size to CO2 emission variation | 104 t |
G | Gross regional product (GDP) | 100 million CNY | ΔCA | Contribution of the economic development to CO2 emission variation ( | 104 t |
Gi | Output value of sector i | 100 million CNY | ΔCS | Contribution of the industrial structure to CO2 emission variation ( | 104 t |
Ei | Energy consumption of sector i | 104 t of standard coal | ΔCI | Contribution of the energy consumption intensity to CO2 emission variation ( | 104 t |
Fij | Consumption of energy source j in industrial structure i, and energy sources include raw coal, coal washed and dressed, coke, crude oil, gasoline, kerosene, diesel oil, fuel oil, liquefied natural gas, and natural gas | 104 t or 100 million m3 | ΔCES | Contribution of the energy consumption structure to CO2 emission variation ( | 104 t |
Cij | CO2 emissions stemming from the consumption of energy source j in industrial structure i | 104 t | ΔCEF | Contribution of the CO2 emission factor to CO2 emission variation ( | 104 t |
Table 3
Influencing factors of CO2 emissions originating from final energy consumption (abbreviated as CO2 emissions) in Sichuan Province."
Influencing factor | Unit | Influencing factor | Unit |
---|---|---|---|
Resident population (X1) | 104 | Coal washed and dressed consumption (X11) | 104 t |
GDP (X2) | 100 million CNY | Coke consumption (X12) | 104 t |
Output value of agriculture, forestry, animal husbandry and fishery sector (X3) | 100 million CNY | Crude oil consumption (X13) | 104 t |
Output value of the industry sector (X4) | 100 million CNY | Gasoline consumption (X14) | 104 t |
Output value of construction sector (X5) | 100 million CNY | Kerosene consumption (X15) | 104 t |
Output value of transportation, storage and post sector (X6) | 100 million CNY | Diesel oil consumption (X16) | 104 t |
Output value of wholesale, retail trade, hotels and catering service sector (X7) | 100 million CNY | Fuel oil consumption (X17) | 104 t |
Output value of other service sectors (X8) | 100 million CNY | LPG consumption (X18) | 104 t |
Energy consumption of standard coal (X9) | 104 t of standard coal | Natural gas consumption (X19) | 100 million m3 |
Raw coal consumption (X10) | 104 t | Electricity consumption (X20) | 100 million kWh |
Table 4
Grey relation analysis results for the correlation degree between CO2 emissions and the selected 20 influencing factors in Sichuan Province."
Grey relation | Rank | Correlation degree | Grey relation | Rank | Correlation degree |
---|---|---|---|---|---|
?(X0, X1) | 2 | 0.9940 | ?(X0, X11) | 18 | 0.9365 |
?(X0, X2) | 13 | 0.9683 | ?(X0, X12) | 4 | 0.9924 |
?(X0, X3) | 11 | 0.9807 | ?(X0, X13) | 12 | 0.9720 |
?(X0, X4) | 9 | 0.9826 | ?(X0, X14) | 3 | 0.9938 |
?(X0, X5) | 16 | 0.9597 | ?(X0, X15) | 7 | 0.9871 |
?(X0, X6) | 14 | 0.9656 | ?(X0, X16) | 8 | 0.9858 |
?(X0, X7) | 15 | 0.9610 | ?(X0, X17) | 20 | 0.6533 |
?(X0, X8) | 17 | 0.9455 | ?(X0, X18) | 19 | 0.7847 |
?(X0, X9) | 1 | 0.9990 | ?(X0, X9) | 6 | 0.9885 |
?(X0, X10) | 10 | 0.9809 | ?(X0, X20) | 5 | 0.9891 |
Fig. 3.
Variation in CO2 emissions caused by the decomposed influencing factors (population size, economic development, industrial structure, energy consumption intensity, and energy consumption structure) as well as the annual difference of CO2 emissions in Sichuan Province from 2011 to 2019. The values of the left axis refer to the difference of CO2 emissions between the adjacent two years, while the values of the right axis refer to the difference between positive and negative values in the current year."
Table 5
Contribution amount and degree of economic development to CO2 emissions."
Year | Contribution amount of economic development to CO2 emissions (×104 t) | Contribution degree of economic development to CO2 emissions (%) |
---|---|---|
2011 | 4706.05 | 224.42 |
2012 | 3252.04 | 110.30 |
2013 | 2708.56 | -494.20 |
2014 | 2196.70 | -1093.42 |
2015 | 1082.13 | -97.44 |
2016 | 2005.78 | -97.03 |
2017 | 3149.78 | 273.68 |
2018 | 3044.98 | 216.09 |
2019 | 2109.94 | 212.25 |
Table 6
Kaya-logarithmic mean Divisia index (LMDI) decomposition model results of industrial structure effect on the variation of CO2 emissions."
Year | Cumulative CO2 emission variation (×104 t) | |||||
---|---|---|---|---|---|---|
AFAHF | I | C | TSP | WRTHCS | O | |
2011 | -11.36 | -302.76 | 9.02 | -230.45 | -34.59 | 50.33 |
2012 | -16.68 | -447.40 | 12.71 | -89.13 | 0.50 | 42.64 |
2013 | -38.58 | -252.64 | 16.69 | -107.10 | 5.34 | 57.04 |
2014 | -3.76 | -1012.36 | 12.12 | 468.52 | 41.18 | 39.13 |
2015 | -5.61 | -937.32 | -9.67 | 78.44 | 93.90 | 56.51 |
2016 | -15.16 | -1508.89 | -5.49 | 211.62 | 72.72 | 112.98 |
2017 | -26.76 | -1298.51 | 13.81 | -181.40 | 82.68 | 105.69 |
2018 | -44.03 | -833.64 | 24.06 | 83.74 | -19.52 | 96.57 |
2019 | 0.00 | -91.07 | -2.63 | -118.07 | 12.00 | 9.89 |
Total | -161.93 | -6684.59 | 70.60 | 116.18 | 254.21 | 570.80 |
Table 7
LMDI decomposition model results of energy consumption intensity effect on the variation of CO2 emission."
Year | Cumulative CO2 emission variation (×104 t) | |||||
---|---|---|---|---|---|---|
AFAHF | I | C | TSP | WRTHCS | O | |
2011 | -94.15 | -2424.57 | -51.40 | -419.48 | 102.82 | -43.53 |
2012 | 15.56 | 651.01 | -112.86 | -21.51 | -117.41 | -152.93 |
2013 | -2.92 | -2648.93 | -202.90 | -569.47 | -174.60 | 1151.15 |
2014 | -45.07 | -1303.81 | -44.32 | 40.67 | 121.18 | -1226.49 |
2015 | -2.88 | -1133.23 | 24.89 | -251.82 | -169.91 | -20.78 |
2016 | -81.93 | -3450.44 | 127.36 | 413.86 | -123.03 | -231.85 |
2017 | -69.16 | -249.64 | -42.24 | -54.17 | -126.43 | -198.18 |
2018 | -157.48 | 353.76 | 4.10 | -531.97 | -330.80 | -80.28 |
2019 | -2.97 | -954.34 | -43.00 | 10.38 | -94.60 | -190.26 |
Total | -441.01 | -11,160.20 | -340.37 | -1383.50 | -912.79 | -993.15 |
[1] |
Alajmi, R.G., 2021. Factors that impact greenhouse gas emissions in Saudi Arabia: Decomposition analysis using LMDI. Energy Policy. 156, doi: 10.1016/j.enpol.2021.112454.
doi: 10.1016/j.enpol.2021.112454 |
[2] |
Ang, B.W., 2005. The LMDI approach to decomposition analysis: a practical guide. Energy policy. 33(7), 867-871.
doi: 10.1016/j.enpol.2003.10.010 |
[3] | Chai, N., Zhao, T., Lin, T., 2012. Grey relation analysis of carbon dioxide emissions from energy consumption of industries in China. Ecological Economy. 105-107. (in Chinese) |
[4] | Chen, F.P., 2017. Impact of population and industrial structure on carbon emissions and mission. Beijing: Beijing University of Chemical Technology. (in Chinese) |
[5] | Chen, J.H., Li, Q.C., 2021. Research on the influencing factors of energy consumption carbon Emission in Sichuan Province under the background of the construction of Chengdu-Chongqing double city economic circle:from the perspective of LMDI method. Ecological Economy. 37(12), 30-36. (in Chinese) |
[6] |
Chen, L., Xu, L.Y., Xu, Q., et al., 2016. Optimization of urban industrial structure under the low-carbon goal and the water constraints: a case in Dalian, China. Cleaner Prod. 114, doi: 10.1016/j.jclepro.2015.09.056.
doi: 10.1016/j.jclepro.2015.09.056 |
[7] | Chen, R.X., 2018. Research on optimization of energy consumption structure of Sichuan Province under carbon reduction. Chengdu University of Technology. (in Chinese) |
[8] | China National Institute of Standardization, China Quality Mark Certification Group, Guangzhou Institute of Energy Testing, et al., 2020. General rules for calculation of the comprehensive energy consumption. Beijing: State Administration for Market Regulation. |
[9] | Energy Statistics Division, National Bureau of Statistics, 2012. China Energy Statistical Yearbook 2011. Beijing: China Statistics Press. (in Chinese) |
[10] | Energy Statistics Division, National Bureau of Statistics, 2013. China Energy Statistical Yearbook 2012. Beijing: China Statistics Press. (in Chinese) |
[11] | Energy Statistics Division, National Bureau of Statistics, 2014. China Energy Statistical Yearbook 2013. Beijing: China Statistics Press. (in Chinese) |
[12] | Energy Statistics Division, National Bureau of Statistics, 2015. China Energy Statistical Yearbook 2014. Beijing: China Statistics Press. (in Chinese) |
[13] | Energy Statistics Division, National Bureau of Statistics, 2016. China Energy Statistical Yearbook 2015. Beijing: China Statistics Press. (in Chinese) |
[14] | Energy Statistics Division, National Bureau of Statistics, 2017. China Energy Statistical Yearbook 2016. Beijing: China Statistics Press. (in Chinese) |
[15] | Energy Statistics Division, National Bureau of Statistics, 2018. China Energy Statistical Yearbook 2017. Beijing: China Statistics Press. (in Chinese) |
[16] | Energy Statistics Division, National Bureau of Statistics, 2019. China Energy Statistical Yearbook 2018. Beijing: China Statistics Press. (in Chinese) |
[17] | Energy Statistics Division, National Bureau of Statistics, 2020. China Energy Statistical Yearbook 2019. Beijing: China Statistics Press. (in Chinese) |
[18] | Energy Statistics Division, National Bureau of Statistics, 2021. China Energy Statistical Yearbook 2020. Beijing: China Statistics Press. (in Chinese) |
[19] |
Fan, Y., Wu, G., Wei, Y.M., 2007. Using LMDI method to analyze the change of China’s industrial CO2 emissions from final fuel use: An empirical analysis. Energy Policy. 35(11), 5892-5900.
doi: 10.1016/j.enpol.2007.07.010 |
[20] |
Gu, S., Fu, B., Thriveni, T., et al., 2019. Coupled LMDI and system dynamics model for estimating urban CO2 emission mitigation potential in Shanghai, China. J. Cleaner Prod. 240, 118034, doi: 10.1016/j.jclepro.2019.118034.
doi: 10.1016/j.jclepro.2019.118034 |
[21] |
Huang, Y.S., Shen, L., Liu, H., 2019. Grey relational analysis, principal component analysis and forecasting of carbon emissions based on long short-term memory in China. J. Cleaner Prod. 209, 415-423.
doi: 10.1016/j.jclepro.2018.10.128 |
[22] | IPCC (Intergovernmental Panel on Climate Change), 2019. 2019 Refinement to the 2006 IPCC Guidelines for National Greenhouse Gas Inventory. [2022-11-28]. https://www.ipcc.ch/report/2019-refinement-to-the-2006-ipcc-guidelines-for-national-greenhouse-gas-inventories/. |
[23] |
Jiang, S., Zhu, Y.N., He, G.H., et al., 2020. Factors influencing China’s non-residential power consumption: Estimation using the Kaya-LMDI methods. Energy. 201, 117719, doi: 10.1016/j.energy.2020.117719.
doi: 10.1016/j.energy.2020.117719 |
[24] | Li, X., 2019. Ppreliminary study on energy saving and emission reduction in Sichuan province based on the relationship among energy consumption, carbon emission and economic growth. PhD Dissertation. Chengdu: Southwest Jiaotong University. (in Chinese) |
[25] |
Lin, B.Q., Ahmad, I., 2016. Analysis of energy related carbon dioxide emission and reduction potential in Pakistan. J. Cleaner Prod. 143, 278-287.
doi: 10.1016/j.jclepro.2016.12.113 |
[26] |
Liu, M.Z., Zhang, X.X., Zhang, M.Y., et al., 2021. Influencing factors of carbon emissions in transportation industry based on CD function and LMDI decomposition model: China as an example. Environmental Impact Assessment Review. 90(1), 106623, doi: 10.1016/j.eiar.2021.106623.
doi: 10.1016/j.eiar.2021.106623 |
[27] |
Liu, J., Yang, Q.S., Zhang, Y., et al., 2019. Analysis of CO2 emissions in China’s manufacturing industry based on extended logarithmic mean division index decomposition. Sustainability. 11(1), doi: https://doi.org/10.3390/su11010226.
doi: https://doi.org/10.3390/su11010226 |
[28] | Liu, Y., Guo, J.J., Liu, C.Y., 2012. The effect of demographic factors on carbon dioxide emissions: panel quantile regression analysis. Population & Economics. 3, 13-18. (in Chinese) |
[29] |
Ma, L.W., Chong, C.H., Zhang, X., et al., 2018. LMDI decomposition of energy-related CO2 emissions based on energy and CO2 allocation sankey diagrams: The method and an application to China. Sustainability. 10(2), doi: 10.3390/su10020344.
doi: 10.3390/su10020344 |
[30] |
Mahony, T.O., 2013. Decomposition of Ireland’s carbon emissions from 1990 to 2010: An extended Kaya identity. Energy Policy. 59, 573-581.
doi: 10.1016/j.enpol.2013.04.013 |
[31] |
Mao, X.Q., Hu, T., Zeng, A., et al., 2016. Implications of the 11th and 12th Five-Year Plans for energy conservation and CO2 and air pollutants reduction: a case study from the city of Urumqi, China. J. Cleaner Prod. 112, 1767-1777.
doi: 10.1016/j.jclepro.2015.08.015 |
[32] |
Nam, K.M., Waugh, C.J., Paltsev, S., et al., 2013. Carbon co-benefits of tighter SO2 and NOx regulations in China. Global Environmental Change. 23(6), 1648-1661.
doi: 10.1016/j.gloenvcha.2013.09.003 |
[33] | NCSC (National Center for Climate Change Strategy and International Cooperation), 2011. Guidelines for the Preparation of Provincial GHG Inventories (Trial). [2022-11-28]. http://www.ncsc.org.cn/SY/tjkhybg/202003/t20200319_769763.shtml. |
[34] | NDRC (National Development and Reform Commission), 2021. In the 14th Five-Year Plan, the proportion of clean energy in Sichuan will reach 88%. [2022-11-28]. http://www.cfgw.net.cn/epaper/content/202111/30/content_45172.htm |
[35] | Ning, Y.D., Zhang, Y.H., Ding, T., et al., 2012. Empirical Study of Decomposition of CO2 Emission Factors in China. China Population,Resources and Environment. 22(S2), 9-14. (in Chinese) |
[36] |
Ortega-Ruiz, G., Mena-Nieto, A., García-Ramos, J., 2020. Is India on the right pathway to reduce CO2 emissions? Decomposing an enlarged Kaya identity using the LMDI method for the period 1990-2016. Sci. Total Environ. 737, 139638, doi: 10.1016/j.scitotenv.2020.139638.
doi: 10.1016/j.scitotenv.2020.139638 |
[37] |
Pan, L., Sun, B., Wei, W., 2011. City air quality forecasting and impact factors analysis based on grey model. Procedia Engineering. 12, 74-79. (in Chinese)
doi: 10.1016/j.proeng.2011.05.013 |
[38] | Sichuan Provincial Bureau of Statistics, 2021. Sichuan Statistical Yearbook 2020. Beijing: China Statistics Press. (in Chinese) |
[39] | State Grid Sichuan Electric Power Company, 2018. Greenhouse Gas Emission Report of the State Grid Sichuan Electric Power Company. [2022-11-28]. https://max.book118.com/html/2018/0428/163624780.shtm. |
[40] | The People’s Government of Sichuan Province, 2021. Overview of Sichuan. [2022-11-28]. https://www.sc.gov.cn/. |
[41] |
Tursun, H., Li, Z., Liu, R., et al., 2015. Contribution weight of engineering technology on pollutant emission reduction based on IPAT and LMDI methods. Clean Technol. Environ. Policy. 17(1), 225-235.
doi: 10.1007/s10098-014-0780-1 |
[42] |
Yang, H.H., Ma, L.W., Li, Z., 2020. A method for analyzing energy-related carbon emissions and the structural changes: A case study of china from 2005 to 2015. Energies. 13(8), 2076, doi: 10.3390/en13082076.
doi: 10.3390/en13082076 |
[43] |
Yang, J., Cai, W., Ma, M.D., et al., 2019. Driving forces of China’s CO2 emissions from energy consumption based on Kaya-LMDI methods. Sci. Total Environ. 711, doi: 10.1016/j.scitotenv.2019.134569.
doi: 10.1016/j.scitotenv.2019.134569 |
[44] | Zhang, J., Cai, J.F., 2014. Impacts of household structure and household consumption on carbon dioxide, emission in China. Future and Development. 38(10), 53-57. (in Chinese) |
[45] | Zheng, Y., Lu, F., Liu, J.R., et al., 2020. comparative study on CO2 emissions from fossil energy consumption and its influencing factors in typical cities of China. Acta Ecological Sinica. 40(10), 3315-3327. (in Chinese) |
No related articles found! |
Viewed | ||||||
Full text |
|
|||||
Abstract |
|
|||||