Abstract:The environmental benefi ts and trade-offs of automotive biofuels are well known, but less is known about aviation biofuels. We modeled the environmental impacts of three pathways for aviation biofuel in Australia (from microalgae, pongamia, and sugarcane molasses) using attributional life cycle assessments (LCAs), applying both economic allocation and system expansion. Based on economic allocation, sugarcane molasses has the better fossil energy ratio FER (1.7 MJ out/MJ in) and GHG abatement (73% less than av… Show more
“…Microalgal biofuels, known as third‐generation biofuels, are treated as a technically viable alternative energy solution that overcomes the major drawbacks related to the first and second generations. Compared to the first‐ and second‐generation biofuels, microalgal biofuels offer many more advantages, such as a high growth rate, high‐efficiency CO 2 mitigation, non‐competition for farmland, less water demand than land crops, toleration of wastewaters during cultivation, and more cost‐effective farming …”
“…Microalgal biofuels, known as third‐generation biofuels, are treated as a technically viable alternative energy solution that overcomes the major drawbacks related to the first and second generations. Compared to the first‐ and second‐generation biofuels, microalgal biofuels offer many more advantages, such as a high growth rate, high‐efficiency CO 2 mitigation, non‐competition for farmland, less water demand than land crops, toleration of wastewaters during cultivation, and more cost‐effective farming …”
“…The aim of this production step was the separation of lipids from the remainder of the biomass. In all the cases considered, the extraction is assisted with the use of solvents (hexane, methanol, and ethanol), in some case with additional steps such as a drill pressing or dry de‐gumming . None of the studies take into consideration more advanced approaches currently under exploration, such as the innovative use of switchable hydrophilicity solvents (SHS) at room temperature that use CO 2 for separation and no required a drying of the solvent prior to use, or the CO 2 expanded methanol approach (adopted from Paudel et al …”
“…Cox et al [25] evaluated the STJ from sugarcane molasses, and estimated its GHG emissions at 80 g CO 2 e/MJ, using a system expansion method. On the other hand, Moreira et al [26] estimated the GHG emissions of STJ from sugarcane at 8.5 g CO 2 e/MJ, using a system expansion method.…”
Section: Introductionmentioning
confidence: 99%
“…The large difference in the GHG emissions between these two studies stemmed from differing approaches to estimating indirect effects. Cox et al [25] assumed that sorghum production will increase as sugarcane is used as a jet fuel feedstock, resulting in LUC GHG emissions of over 100 g CO 2 e/MJ from the increased sorghum production. Moreira et al [26], on the other hand, used the Global Trade Analysis Project model to estimate the LUC, and reported subsequent LUC GHG emissions of 12 g CO 2 e/MJ.…”
Section: Introductionmentioning
confidence: 99%
“…Cox et al [25] and Moreira et al [26], however, examined only STJ produced via biological conversion from sugarcane, which is not widely available for fuel production outside Brazil. Staples et al [27] included corn and corn stover, which are more relevant to the US biofuel industry.…”
BackgroundTo reduce the environmental impacts of the aviation sector as air traffic grows steadily, the aviation industry has paid increasing attention to bio-based alternative jet fuels (AJFs), which may provide lower life-cycle petroleum consumption and greenhouse gas (GHG) emissions than petroleum jet fuel. This study presents well-to-wake (WTWa) results for four emerging AJFs: ethanol-to-jet (ETJ) from corn and corn stover, and sugar-to-jet (STJ) from corn stover via both biological and catalytic conversion. For the ETJ pathways, two plant designs were examined: integrated (processing corn or corn stover as feedstock) and distributed (processing ethanol as feedstock). Also, three H2 options for STJ via catalytic conversion are investigated: external H2 from natural gas (NG) steam methane reforming (SMR), in situ H2, and H2 from biomass gasification.ResultsResults demonstrate that the feedstock is a key factor in the WTWa GHG emissions of ETJ: corn- and corn stover-based ETJ are estimated to produce WTWa GHG emissions that are 16 and 73%, respectively, less than those of petroleum jet. As for the STJ pathways, this study shows that STJ via biological conversion could generate WTWa GHG emissions 59% below those of petroleum jet. STJ via catalytic conversion could reduce the WTWa GHG emissions by 28% with H2 from NG SMR or 71% with H2 from biomass gasification than those of petroleum jet. This study also examines the impacts of co-product handling methods, and shows that the WTWa GHG emissions of corn stover-based ETJ, when estimated with a displacement method, are lower by 11 g CO2e/MJ than those estimated with an energy allocation method.ConclusionCorn- and corn stover-based ETJ as well as corn stover-based STJ show potentials to reduce WTWa GHG emissions compared to petroleum jet. Particularly, WTWa GHG emissions of STJ via catalytic conversion depend highly on the hydrogen source. On the other hand, ETJ offers unique opportunities to exploit extensive existing corn ethanol plants and infrastructure, and to provide a boost to staggering ethanol demand, which is largely being used as gasoline blendstock.Electronic supplementary materialThe online version of this article (doi:10.1186/s13068-017-0698-z) contains supplementary material, which is available to authorized users.
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