Quantification of $ CO_{2} $ emissions of macro-infrastructure in China with simplified life cycle assessment
Abstract The main policies of China have promoted the development of the urbanization and the industrialization. The rise of infrastructure energy consumption shows the process of modernization in our country; however, despite there are a lot of researches about the energy consumption in the field o...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Yang, Weining [verfasserIn] Qi, Zhongying [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2016 |
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| Schlagwörter: |
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| Übergeordnetes Werk: |
Enthalten in: Natural hazards - Dordrecht [u.a.] : Springer Science + Business Media B.V., 1988, 82(2016), 1 vom: 08. Feb., Seite 545-569 |
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| Übergeordnetes Werk: |
volume:82 ; year:2016 ; number:1 ; day:08 ; month:02 ; pages:545-569 |
| Links: |
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| DOI / URN: |
10.1007/s11069-016-2197-0 |
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| Katalog-ID: |
SPR016328116 |
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| 520 | |a Abstract The main policies of China have promoted the development of the urbanization and the industrialization. The rise of infrastructure energy consumption shows the process of modernization in our country; however, despite there are a lot of researches about the energy consumption in the field of construction, transportation and other infrastructure, in academia, there are less statistics about energy consumption for the infrastructure as a whole, and its proportion in total energy consumption in the whole country. Thus, this paper tries to characterize infrastructures of China, which include construction, transportation, energy, water supply and drainage, post and telecommunication system by establishing an estimation model of infrastructure system $ CO_{2} $ emissions through national official macro-level statistical data. We employ the simplified $ LCCO_{2} $A method to analyze the activities in each stage and calculate associated $ CO_{2} $ emissions throughout infrastructures’ whole life cycle in China from 1993 to 2012. The results show that $ CO_{2} $ emissions from the infrastructure have rapidly grown over the past decades. The total emissions of the standard coal were 888.16 million tons in 1993, up to about 7.76 billion tons in 2012. The operation stage emissions dominate over the infrastructure emissions, accounting for 80–90 % of the impact. In this paper, on the one hand, from the perspective of the overall environmental benefits, we provide a more comprehensive environmental assessment analysis method for the policy makers. On the other hand, the infrastructure construction of China has periodic characteristic. We analyze the specific features of the infrastructure $ CO_{2} $ emissions in different stages, and put forward emission-reduction measures in consideration of the current conditions, which reflects that the key of balancing the relationship between modernization and environment is adjusting emission reduction policy according to different stages to adapt to the “new normal”. In addition, the method development is also important for future quantifications of $ CO_{2} $ emissions of other sectors in China and beyond. | ||
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10.1007/s11069-016-2197-0 doi (DE-627)SPR016328116 (SPR)s11069-016-2197-0-e DE-627 ger DE-627 rakwb eng 550 ASE 31.00 bkl 43.48 bkl Yang, Weining verfasserin aut Quantification of $ CO_{2} $ emissions of macro-infrastructure in China with simplified life cycle assessment 2016 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The main policies of China have promoted the development of the urbanization and the industrialization. The rise of infrastructure energy consumption shows the process of modernization in our country; however, despite there are a lot of researches about the energy consumption in the field of construction, transportation and other infrastructure, in academia, there are less statistics about energy consumption for the infrastructure as a whole, and its proportion in total energy consumption in the whole country. Thus, this paper tries to characterize infrastructures of China, which include construction, transportation, energy, water supply and drainage, post and telecommunication system by establishing an estimation model of infrastructure system $ CO_{2} $ emissions through national official macro-level statistical data. We employ the simplified $ LCCO_{2} $A method to analyze the activities in each stage and calculate associated $ CO_{2} $ emissions throughout infrastructures’ whole life cycle in China from 1993 to 2012. The results show that $ CO_{2} $ emissions from the infrastructure have rapidly grown over the past decades. The total emissions of the standard coal were 888.16 million tons in 1993, up to about 7.76 billion tons in 2012. The operation stage emissions dominate over the infrastructure emissions, accounting for 80–90 % of the impact. In this paper, on the one hand, from the perspective of the overall environmental benefits, we provide a more comprehensive environmental assessment analysis method for the policy makers. On the other hand, the infrastructure construction of China has periodic characteristic. We analyze the specific features of the infrastructure $ CO_{2} $ emissions in different stages, and put forward emission-reduction measures in consideration of the current conditions, which reflects that the key of balancing the relationship between modernization and environment is adjusting emission reduction policy according to different stages to adapt to the “new normal”. In addition, the method development is also important for future quantifications of $ CO_{2} $ emissions of other sectors in China and beyond. Macro-infrastructure (dpeaa)DE-He213 CO (dpeaa)DE-He213 emissions (dpeaa)DE-He213 Simplified life cycle assessment (dpeaa)DE-He213 China (dpeaa)DE-He213 Qi, Zhongying verfasserin aut Enthalten in Natural hazards Dordrecht [u.a.] : Springer Science + Business Media B.V., 1988 82(2016), 1 vom: 08. Feb., Seite 545-569 (DE-627)315621729 (DE-600)2017806-2 1573-0840 nnns volume:82 year:2016 number:1 day:08 month:02 pages:545-569 https://dx.doi.org/10.1007/s11069-016-2197-0 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-MAT SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 31.00 ASE 43.48 ASE AR 82 2016 1 08 02 545-569 |
| spelling |
10.1007/s11069-016-2197-0 doi (DE-627)SPR016328116 (SPR)s11069-016-2197-0-e DE-627 ger DE-627 rakwb eng 550 ASE 31.00 bkl 43.48 bkl Yang, Weining verfasserin aut Quantification of $ CO_{2} $ emissions of macro-infrastructure in China with simplified life cycle assessment 2016 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The main policies of China have promoted the development of the urbanization and the industrialization. The rise of infrastructure energy consumption shows the process of modernization in our country; however, despite there are a lot of researches about the energy consumption in the field of construction, transportation and other infrastructure, in academia, there are less statistics about energy consumption for the infrastructure as a whole, and its proportion in total energy consumption in the whole country. Thus, this paper tries to characterize infrastructures of China, which include construction, transportation, energy, water supply and drainage, post and telecommunication system by establishing an estimation model of infrastructure system $ CO_{2} $ emissions through national official macro-level statistical data. We employ the simplified $ LCCO_{2} $A method to analyze the activities in each stage and calculate associated $ CO_{2} $ emissions throughout infrastructures’ whole life cycle in China from 1993 to 2012. The results show that $ CO_{2} $ emissions from the infrastructure have rapidly grown over the past decades. The total emissions of the standard coal were 888.16 million tons in 1993, up to about 7.76 billion tons in 2012. The operation stage emissions dominate over the infrastructure emissions, accounting for 80–90 % of the impact. In this paper, on the one hand, from the perspective of the overall environmental benefits, we provide a more comprehensive environmental assessment analysis method for the policy makers. On the other hand, the infrastructure construction of China has periodic characteristic. We analyze the specific features of the infrastructure $ CO_{2} $ emissions in different stages, and put forward emission-reduction measures in consideration of the current conditions, which reflects that the key of balancing the relationship between modernization and environment is adjusting emission reduction policy according to different stages to adapt to the “new normal”. In addition, the method development is also important for future quantifications of $ CO_{2} $ emissions of other sectors in China and beyond. Macro-infrastructure (dpeaa)DE-He213 CO (dpeaa)DE-He213 emissions (dpeaa)DE-He213 Simplified life cycle assessment (dpeaa)DE-He213 China (dpeaa)DE-He213 Qi, Zhongying verfasserin aut Enthalten in Natural hazards Dordrecht [u.a.] : Springer Science + Business Media B.V., 1988 82(2016), 1 vom: 08. Feb., Seite 545-569 (DE-627)315621729 (DE-600)2017806-2 1573-0840 nnns volume:82 year:2016 number:1 day:08 month:02 pages:545-569 https://dx.doi.org/10.1007/s11069-016-2197-0 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-MAT SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 31.00 ASE 43.48 ASE AR 82 2016 1 08 02 545-569 |
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10.1007/s11069-016-2197-0 doi (DE-627)SPR016328116 (SPR)s11069-016-2197-0-e DE-627 ger DE-627 rakwb eng 550 ASE 31.00 bkl 43.48 bkl Yang, Weining verfasserin aut Quantification of $ CO_{2} $ emissions of macro-infrastructure in China with simplified life cycle assessment 2016 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The main policies of China have promoted the development of the urbanization and the industrialization. The rise of infrastructure energy consumption shows the process of modernization in our country; however, despite there are a lot of researches about the energy consumption in the field of construction, transportation and other infrastructure, in academia, there are less statistics about energy consumption for the infrastructure as a whole, and its proportion in total energy consumption in the whole country. Thus, this paper tries to characterize infrastructures of China, which include construction, transportation, energy, water supply and drainage, post and telecommunication system by establishing an estimation model of infrastructure system $ CO_{2} $ emissions through national official macro-level statistical data. We employ the simplified $ LCCO_{2} $A method to analyze the activities in each stage and calculate associated $ CO_{2} $ emissions throughout infrastructures’ whole life cycle in China from 1993 to 2012. The results show that $ CO_{2} $ emissions from the infrastructure have rapidly grown over the past decades. The total emissions of the standard coal were 888.16 million tons in 1993, up to about 7.76 billion tons in 2012. The operation stage emissions dominate over the infrastructure emissions, accounting for 80–90 % of the impact. In this paper, on the one hand, from the perspective of the overall environmental benefits, we provide a more comprehensive environmental assessment analysis method for the policy makers. On the other hand, the infrastructure construction of China has periodic characteristic. We analyze the specific features of the infrastructure $ CO_{2} $ emissions in different stages, and put forward emission-reduction measures in consideration of the current conditions, which reflects that the key of balancing the relationship between modernization and environment is adjusting emission reduction policy according to different stages to adapt to the “new normal”. In addition, the method development is also important for future quantifications of $ CO_{2} $ emissions of other sectors in China and beyond. Macro-infrastructure (dpeaa)DE-He213 CO (dpeaa)DE-He213 emissions (dpeaa)DE-He213 Simplified life cycle assessment (dpeaa)DE-He213 China (dpeaa)DE-He213 Qi, Zhongying verfasserin aut Enthalten in Natural hazards Dordrecht [u.a.] : Springer Science + Business Media B.V., 1988 82(2016), 1 vom: 08. Feb., Seite 545-569 (DE-627)315621729 (DE-600)2017806-2 1573-0840 nnns volume:82 year:2016 number:1 day:08 month:02 pages:545-569 https://dx.doi.org/10.1007/s11069-016-2197-0 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-MAT SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 31.00 ASE 43.48 ASE AR 82 2016 1 08 02 545-569 |
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10.1007/s11069-016-2197-0 doi (DE-627)SPR016328116 (SPR)s11069-016-2197-0-e DE-627 ger DE-627 rakwb eng 550 ASE 31.00 bkl 43.48 bkl Yang, Weining verfasserin aut Quantification of $ CO_{2} $ emissions of macro-infrastructure in China with simplified life cycle assessment 2016 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The main policies of China have promoted the development of the urbanization and the industrialization. The rise of infrastructure energy consumption shows the process of modernization in our country; however, despite there are a lot of researches about the energy consumption in the field of construction, transportation and other infrastructure, in academia, there are less statistics about energy consumption for the infrastructure as a whole, and its proportion in total energy consumption in the whole country. Thus, this paper tries to characterize infrastructures of China, which include construction, transportation, energy, water supply and drainage, post and telecommunication system by establishing an estimation model of infrastructure system $ CO_{2} $ emissions through national official macro-level statistical data. We employ the simplified $ LCCO_{2} $A method to analyze the activities in each stage and calculate associated $ CO_{2} $ emissions throughout infrastructures’ whole life cycle in China from 1993 to 2012. The results show that $ CO_{2} $ emissions from the infrastructure have rapidly grown over the past decades. The total emissions of the standard coal were 888.16 million tons in 1993, up to about 7.76 billion tons in 2012. The operation stage emissions dominate over the infrastructure emissions, accounting for 80–90 % of the impact. In this paper, on the one hand, from the perspective of the overall environmental benefits, we provide a more comprehensive environmental assessment analysis method for the policy makers. On the other hand, the infrastructure construction of China has periodic characteristic. We analyze the specific features of the infrastructure $ CO_{2} $ emissions in different stages, and put forward emission-reduction measures in consideration of the current conditions, which reflects that the key of balancing the relationship between modernization and environment is adjusting emission reduction policy according to different stages to adapt to the “new normal”. In addition, the method development is also important for future quantifications of $ CO_{2} $ emissions of other sectors in China and beyond. Macro-infrastructure (dpeaa)DE-He213 CO (dpeaa)DE-He213 emissions (dpeaa)DE-He213 Simplified life cycle assessment (dpeaa)DE-He213 China (dpeaa)DE-He213 Qi, Zhongying verfasserin aut Enthalten in Natural hazards Dordrecht [u.a.] : Springer Science + Business Media B.V., 1988 82(2016), 1 vom: 08. Feb., Seite 545-569 (DE-627)315621729 (DE-600)2017806-2 1573-0840 nnns volume:82 year:2016 number:1 day:08 month:02 pages:545-569 https://dx.doi.org/10.1007/s11069-016-2197-0 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-MAT SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 31.00 ASE 43.48 ASE AR 82 2016 1 08 02 545-569 |
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10.1007/s11069-016-2197-0 doi (DE-627)SPR016328116 (SPR)s11069-016-2197-0-e DE-627 ger DE-627 rakwb eng 550 ASE 31.00 bkl 43.48 bkl Yang, Weining verfasserin aut Quantification of $ CO_{2} $ emissions of macro-infrastructure in China with simplified life cycle assessment 2016 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The main policies of China have promoted the development of the urbanization and the industrialization. The rise of infrastructure energy consumption shows the process of modernization in our country; however, despite there are a lot of researches about the energy consumption in the field of construction, transportation and other infrastructure, in academia, there are less statistics about energy consumption for the infrastructure as a whole, and its proportion in total energy consumption in the whole country. Thus, this paper tries to characterize infrastructures of China, which include construction, transportation, energy, water supply and drainage, post and telecommunication system by establishing an estimation model of infrastructure system $ CO_{2} $ emissions through national official macro-level statistical data. We employ the simplified $ LCCO_{2} $A method to analyze the activities in each stage and calculate associated $ CO_{2} $ emissions throughout infrastructures’ whole life cycle in China from 1993 to 2012. The results show that $ CO_{2} $ emissions from the infrastructure have rapidly grown over the past decades. The total emissions of the standard coal were 888.16 million tons in 1993, up to about 7.76 billion tons in 2012. The operation stage emissions dominate over the infrastructure emissions, accounting for 80–90 % of the impact. In this paper, on the one hand, from the perspective of the overall environmental benefits, we provide a more comprehensive environmental assessment analysis method for the policy makers. On the other hand, the infrastructure construction of China has periodic characteristic. We analyze the specific features of the infrastructure $ CO_{2} $ emissions in different stages, and put forward emission-reduction measures in consideration of the current conditions, which reflects that the key of balancing the relationship between modernization and environment is adjusting emission reduction policy according to different stages to adapt to the “new normal”. In addition, the method development is also important for future quantifications of $ CO_{2} $ emissions of other sectors in China and beyond. Macro-infrastructure (dpeaa)DE-He213 CO (dpeaa)DE-He213 emissions (dpeaa)DE-He213 Simplified life cycle assessment (dpeaa)DE-He213 China (dpeaa)DE-He213 Qi, Zhongying verfasserin aut Enthalten in Natural hazards Dordrecht [u.a.] : Springer Science + Business Media B.V., 1988 82(2016), 1 vom: 08. Feb., Seite 545-569 (DE-627)315621729 (DE-600)2017806-2 1573-0840 nnns volume:82 year:2016 number:1 day:08 month:02 pages:545-569 https://dx.doi.org/10.1007/s11069-016-2197-0 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-MAT SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 31.00 ASE 43.48 ASE AR 82 2016 1 08 02 545-569 |
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<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000caa a22002652 4500</leader><controlfield tag="001">SPR016328116</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20220111031052.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">201006s2016 xx |||||o 00| ||eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1007/s11069-016-2197-0</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)SPR016328116</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(SPR)s11069-016-2197-0-e</subfield></datafield><datafield tag="040" ind1=" " ind2=" "><subfield code="a">DE-627</subfield><subfield code="b">ger</subfield><subfield code="c">DE-627</subfield><subfield code="e">rakwb</subfield></datafield><datafield tag="041" ind1=" " ind2=" "><subfield code="a">eng</subfield></datafield><datafield tag="082" ind1="0" ind2="4"><subfield code="a">550</subfield><subfield code="q">ASE</subfield></datafield><datafield tag="084" ind1=" " ind2=" "><subfield code="a">31.00</subfield><subfield code="2">bkl</subfield></datafield><datafield tag="084" ind1=" " ind2=" "><subfield code="a">43.48</subfield><subfield code="2">bkl</subfield></datafield><datafield tag="100" ind1="1" ind2=" "><subfield code="a">Yang, Weining</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Quantification of $ CO_{2} $ emissions of macro-infrastructure in China with simplified life cycle assessment</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2016</subfield></datafield><datafield tag="336" ind1=" " ind2=" "><subfield code="a">Text</subfield><subfield code="b">txt</subfield><subfield code="2">rdacontent</subfield></datafield><datafield tag="337" ind1=" " ind2=" "><subfield code="a">Computermedien</subfield><subfield code="b">c</subfield><subfield code="2">rdamedia</subfield></datafield><datafield tag="338" ind1=" " ind2=" "><subfield code="a">Online-Ressource</subfield><subfield code="b">cr</subfield><subfield code="2">rdacarrier</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Abstract The main policies of China have promoted the development of the urbanization and the industrialization. The rise of infrastructure energy consumption shows the process of modernization in our country; however, despite there are a lot of researches about the energy consumption in the field of construction, transportation and other infrastructure, in academia, there are less statistics about energy consumption for the infrastructure as a whole, and its proportion in total energy consumption in the whole country. Thus, this paper tries to characterize infrastructures of China, which include construction, transportation, energy, water supply and drainage, post and telecommunication system by establishing an estimation model of infrastructure system $ CO_{2} $ emissions through national official macro-level statistical data. We employ the simplified $ LCCO_{2} $A method to analyze the activities in each stage and calculate associated $ CO_{2} $ emissions throughout infrastructures’ whole life cycle in China from 1993 to 2012. The results show that $ CO_{2} $ emissions from the infrastructure have rapidly grown over the past decades. The total emissions of the standard coal were 888.16 million tons in 1993, up to about 7.76 billion tons in 2012. The operation stage emissions dominate over the infrastructure emissions, accounting for 80–90 % of the impact. In this paper, on the one hand, from the perspective of the overall environmental benefits, we provide a more comprehensive environmental assessment analysis method for the policy makers. On the other hand, the infrastructure construction of China has periodic characteristic. We analyze the specific features of the infrastructure $ CO_{2} $ emissions in different stages, and put forward emission-reduction measures in consideration of the current conditions, which reflects that the key of balancing the relationship between modernization and environment is adjusting emission reduction policy according to different stages to adapt to the “new normal”. In addition, the method development is also important for future quantifications of $ CO_{2} $ emissions of other sectors in China and beyond.</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Macro-infrastructure</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">CO</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">emissions</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Simplified life cycle assessment</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">China</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Qi, Zhongying</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="773" ind1="0" ind2="8"><subfield code="i">Enthalten in</subfield><subfield code="t">Natural hazards</subfield><subfield code="d">Dordrecht [u.a.] : Springer Science + Business Media B.V., 1988</subfield><subfield code="g">82(2016), 1 vom: 08. 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Yang, Weining |
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Yang, Weining ddc 550 bkl 31.00 bkl 43.48 misc Macro-infrastructure misc CO misc emissions misc Simplified life cycle assessment misc China Quantification of $ CO_{2} $ emissions of macro-infrastructure in China with simplified life cycle assessment |
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550 ASE 31.00 bkl 43.48 bkl Quantification of $ CO_{2} $ emissions of macro-infrastructure in China with simplified life cycle assessment Macro-infrastructure (dpeaa)DE-He213 CO (dpeaa)DE-He213 emissions (dpeaa)DE-He213 Simplified life cycle assessment (dpeaa)DE-He213 China (dpeaa)DE-He213 |
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ddc 550 bkl 31.00 bkl 43.48 misc Macro-infrastructure misc CO misc emissions misc Simplified life cycle assessment misc China |
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quantification of $ co_{2} $ emissions of macro-infrastructure in china with simplified life cycle assessment |
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Quantification of $ CO_{2} $ emissions of macro-infrastructure in China with simplified life cycle assessment |
| abstract |
Abstract The main policies of China have promoted the development of the urbanization and the industrialization. The rise of infrastructure energy consumption shows the process of modernization in our country; however, despite there are a lot of researches about the energy consumption in the field of construction, transportation and other infrastructure, in academia, there are less statistics about energy consumption for the infrastructure as a whole, and its proportion in total energy consumption in the whole country. Thus, this paper tries to characterize infrastructures of China, which include construction, transportation, energy, water supply and drainage, post and telecommunication system by establishing an estimation model of infrastructure system $ CO_{2} $ emissions through national official macro-level statistical data. We employ the simplified $ LCCO_{2} $A method to analyze the activities in each stage and calculate associated $ CO_{2} $ emissions throughout infrastructures’ whole life cycle in China from 1993 to 2012. The results show that $ CO_{2} $ emissions from the infrastructure have rapidly grown over the past decades. The total emissions of the standard coal were 888.16 million tons in 1993, up to about 7.76 billion tons in 2012. The operation stage emissions dominate over the infrastructure emissions, accounting for 80–90 % of the impact. In this paper, on the one hand, from the perspective of the overall environmental benefits, we provide a more comprehensive environmental assessment analysis method for the policy makers. On the other hand, the infrastructure construction of China has periodic characteristic. We analyze the specific features of the infrastructure $ CO_{2} $ emissions in different stages, and put forward emission-reduction measures in consideration of the current conditions, which reflects that the key of balancing the relationship between modernization and environment is adjusting emission reduction policy according to different stages to adapt to the “new normal”. In addition, the method development is also important for future quantifications of $ CO_{2} $ emissions of other sectors in China and beyond. |
| abstractGer |
Abstract The main policies of China have promoted the development of the urbanization and the industrialization. The rise of infrastructure energy consumption shows the process of modernization in our country; however, despite there are a lot of researches about the energy consumption in the field of construction, transportation and other infrastructure, in academia, there are less statistics about energy consumption for the infrastructure as a whole, and its proportion in total energy consumption in the whole country. Thus, this paper tries to characterize infrastructures of China, which include construction, transportation, energy, water supply and drainage, post and telecommunication system by establishing an estimation model of infrastructure system $ CO_{2} $ emissions through national official macro-level statistical data. We employ the simplified $ LCCO_{2} $A method to analyze the activities in each stage and calculate associated $ CO_{2} $ emissions throughout infrastructures’ whole life cycle in China from 1993 to 2012. The results show that $ CO_{2} $ emissions from the infrastructure have rapidly grown over the past decades. The total emissions of the standard coal were 888.16 million tons in 1993, up to about 7.76 billion tons in 2012. The operation stage emissions dominate over the infrastructure emissions, accounting for 80–90 % of the impact. In this paper, on the one hand, from the perspective of the overall environmental benefits, we provide a more comprehensive environmental assessment analysis method for the policy makers. On the other hand, the infrastructure construction of China has periodic characteristic. We analyze the specific features of the infrastructure $ CO_{2} $ emissions in different stages, and put forward emission-reduction measures in consideration of the current conditions, which reflects that the key of balancing the relationship between modernization and environment is adjusting emission reduction policy according to different stages to adapt to the “new normal”. In addition, the method development is also important for future quantifications of $ CO_{2} $ emissions of other sectors in China and beyond. |
| abstract_unstemmed |
Abstract The main policies of China have promoted the development of the urbanization and the industrialization. The rise of infrastructure energy consumption shows the process of modernization in our country; however, despite there are a lot of researches about the energy consumption in the field of construction, transportation and other infrastructure, in academia, there are less statistics about energy consumption for the infrastructure as a whole, and its proportion in total energy consumption in the whole country. Thus, this paper tries to characterize infrastructures of China, which include construction, transportation, energy, water supply and drainage, post and telecommunication system by establishing an estimation model of infrastructure system $ CO_{2} $ emissions through national official macro-level statistical data. We employ the simplified $ LCCO_{2} $A method to analyze the activities in each stage and calculate associated $ CO_{2} $ emissions throughout infrastructures’ whole life cycle in China from 1993 to 2012. The results show that $ CO_{2} $ emissions from the infrastructure have rapidly grown over the past decades. The total emissions of the standard coal were 888.16 million tons in 1993, up to about 7.76 billion tons in 2012. The operation stage emissions dominate over the infrastructure emissions, accounting for 80–90 % of the impact. In this paper, on the one hand, from the perspective of the overall environmental benefits, we provide a more comprehensive environmental assessment analysis method for the policy makers. On the other hand, the infrastructure construction of China has periodic characteristic. We analyze the specific features of the infrastructure $ CO_{2} $ emissions in different stages, and put forward emission-reduction measures in consideration of the current conditions, which reflects that the key of balancing the relationship between modernization and environment is adjusting emission reduction policy according to different stages to adapt to the “new normal”. In addition, the method development is also important for future quantifications of $ CO_{2} $ emissions of other sectors in China and beyond. |
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| title_short |
Quantification of $ CO_{2} $ emissions of macro-infrastructure in China with simplified life cycle assessment |
| url |
https://dx.doi.org/10.1007/s11069-016-2197-0 |
| remote_bool |
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| author2 |
Qi, Zhongying |
| author2Str |
Qi, Zhongying |
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| doi_str |
10.1007/s11069-016-2197-0 |
| up_date |
2024-07-03T22:24:59.537Z |
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| score |
7.4018965 |