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76                      4. Life cycle sustainability assessment: An ongoing journey

                 stakeholder profiles are: egalitarian (social, environmental, economic), hierarchist (environ-
                 mental, economic, social) and individualist (economic, environmental, social).
                   The LCA results show that the total environmental impact (from lower to higher impact) of
                 the transportation fuels considering “well-to-tank” are in the order, ethanol-sugarcane < pet-
                 rol < ethanol-corn. The reason for the high environmental impact of biofuel from corn is at-
                 tributed to the large land requirement and the perceived consumption of fossil fuel in the
                 production chain in the United States. But when considering “tank-to-wheel,” the biofuels
                 had lower environmental impacts compared to fossil fuels. The petrol from Nigerian oil
                 and biofuel from Brazilian sugarcane showed more severe negative social impacts than petrol
                 from Russian oil and biofuel from US corn. The positive social impacts were in the order: fos-
                 sil fuels (lower positive impacts), biofuels from US corn (medium positive impacts), and
                 biofuels from Brazilian sugarcane (high positive impacts). The total LCC was highest
                 (0.0203 €/MJ) for ethanol from US corn but lowest (0.0111 €/MJ) for ethanol from Brazilian
                 sugarcane. The total LCC for the petrol fell in between the biofuels (0.0132 €/MJ for Nigeria
                 and 0.0126 €/MJ for Russia). The results were confirmed by the values of performance levels
                 of the different transportation fuels for the different sustainability dimensions, as presented
                 in Table 4.2.
                   The results of the relative sustainability ranking of the transportation fuels differed among
                 the different stakeholder profiles (Fig. 4.11). This implies that different stakeholders will have
                 different transportation fuel preferences. According to the authors, the dataset in the
                 Ecoinvent database used for their study are about two decades old (2000–18) casting doubt
                 on the current applicability of the sustainability performance results for the transportation
                 fuels assessed.


                 4.4.4 Reinforced concrete buildings in seismic regions
                   Gencturk et al. (2016) developed an LCSA framework and used it to assess the impact of
                 earthquake actions on lifetime structural performance of reinforced concrete buildings. The
                 case study was applied to a reinforced concrete building (four-story three-bay RC moment
                 resisting frame) located in San Francisco, California. The system boundary for the assessment
                 covered the structural components of the entire building and the functional unit was from cra-
                 dle to grave butexcluded operation, maintenance, and nonseismic repair not directlyrelatedto

                 TABLE 4.2 Performance levels for different transportation fuels (Ekener et al., 2018).
                                               LCA                       SLCA
                                                              Negative impacts
                 Fuel                     Ecovalue   EPS     SHDB       SDG      Jobs created  LCC
                 Petrol-Nigerian oil      0.693      0.558   0.152      0.113    0             0.652
                 Petrol-Russian oil       0.478      0.225   0          0        0             0.859
                 Ethanol-Brazilian sugarcane  1      1       0.728      0.699    1             1
                 Ethanol-US corn          0          0       1          1        0.333         0
                 EPS, Environmental Priority Strategies; SDG, Sustainable Development Goal; SHDB, Social Hotspot Database.
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