Current limits of life cycle assessment framework in evaluating environmental sustainability – case of two evolving biofuel technologies
Introduction
In order to mitigate climate change and reduce dependency on fossil fuels, ambitious targets have been set for the use of renewable energy in transportation. For example, the European Union (EU) has set a 10% target for renewable energy in transport by 2020 in the EU Directive (28/2009/EC) on the promotion of the use of energy from renewable sources (RED). Also, the United States and many other countries have set ambitious targets for biofuel production (EISA, 2007; IEA, 2010). Along with growing global population, changing dietary preferences, and increasing use of biomass for other industrial applications, the use of biomass is expected to increase and cause competition for biomass resources (Berndes and Hansson, 2007). To produce biofuels, a wide range of biomass sources with various conversion routes can be utilised. Some biomass production systems are almost natural, such as forests, and some are to a large extent anthropogenic, such as microalgae production. In general, the anthropogenic systems use more inputs (fertilisers, pesticides, energy and water), but the productivity per hectare is high (Lardon et al., 2009).
The ambitious targets to increase biofuel production have created pressure to assess the environmental and social impacts of the expanding bioenergy production. Many studies have shown that first generation biofuels can cause even more environmental impacts than their fossil counterparts, and often second generation biofuels based on lignocellulosic or waste biomass are considered a potential solution to more sustainable biofuels production (e.g. Fargione et al., 2008; Gonzalez-Garcia et al., 2009). However, there can be significant problems in the sustainability of second generation biofuels as well (Melamu and Von Blottniz, 2011). These challenges of the input flows can be mitigated by various eco-design strategies using recycled materials from industrial sources (Soratana and Landis, 2011; Kadam, 2002), by aiming at reducing output fluxes to the environment, and/or by recycling them in system loops.
The studies on the environmental sustainability of biofuels are often based on life cycle assessment (LCA) (ISO, 2006) or an application of it. To ensure the sustainability of the biofuels, the EU has established a set of sustainability criteria for transportation biofuels and other bioliquids in the RED. The RED methodology for GHG impacts assessment is an application of LCA, as it aims to consider the impacts during the whole life cycle of biofuels. However, several problems of bioenergy LCA studies related to the use of input data, functional units, allocation methods, reference systems and other assumptions have been identified (Cherubini and Strømman, 2011). In addition, uncertainties and use of specific local factors for indirect effects (such as land-use change) may result in significant variation in final results (Cherubini and Strømman, 2011; Soimakallio and Koponen, 2011; Soimakallio et al., 2009). Due to the lack of input data and the immature state of the assessment methodologies for some of the impact categories, environmental impacts other than climate change are not usually assessed (Cherubini and Strømman, 2011). These challenges make the comparisons of the LCA bioenergy studies complicated.
Despite the methodological difficulties in producing reliable and unbiased estimates of the impacts of alternative production systems, biofuel production is a rapidly increasing field due to pressures of climate change mitigation. Therefore, an important viewpoint is to consider the available sustainability assessments as an input to make as optimal decisions as possible, taking potential biases and uncertainties of the available information into account. Techniques developed to support LCA-based decision-making with respect to multiple criteria (e.g. Myllyviita et al., 2012) and uncertainty assessments (e.g. Mattila et al., 2012) can be utilised in this context.
The aim of this study is to evaluate how the environmental sustainability issues concerning forest and algae biodiesel production can be estimated by using the framework of life cycle assessment. The forest biodiesel system is based on a “natural” feedstock production, while the algae production is an entirely anthropogenic system using an artificial infrastructure and inputs. These two biofuel chains were chosen because they are contrasting systems, and therefore exemplify the current limits of the life cycle assessment framework effectively. A short review of the limitations of the current LCA methodology is performed, and the challenges related to the environmental assessment of the two systems are discussed. An example of the complexity of quantitative assessment is given concerning the GHG emissions. By assessing the two very different biofuel chains, the study illustrates the challenges related to decision-making, while the best possible biofuel products should be selected for future development.
Section snippets
Materials and methods
For assessing the environmental burdens, the conceptual framework used is the LCA as defined in the international standards ISO 14040 and 14044. The impact categories assessed include climate impacts (GHG emissions), impacts on land use and land use change, resource depletion, water use, soil quality impacts and changes in biodiversity. These categories were chosen as they were identified as being important for both cultivation systems, and they are still immature in their methodological
Climate impacts
The climate impacts of biofuel chains are generally assessed by calculating the GHG emissions (CO2, CH4, and N2O) related to the whole life cycle of the product, and by comparing them to the emissions of fossil fuels. Even though the climate impacts are the most studied environmental impact category in LCA studies of biofuels (Cherubini and Strømman, 2011), there is no single, widely accepted methodology to assess them. The studies use varying allocation methods, spatial and temporal system
Example of climate impact assessment using the RED methodology
The RED methodology for calculating GHG emissions was followed in order to give an example of an LCA-based tool currently being used for decision-making (EU, 2009). According to the RED methodology, the functional unit was one MJ of biofuel, and energy allocation (based on LHVs) was used to attribute the emissions among the products. In forest residue FT-diesel production, no co-products were created so no allocation took place. In the algae oil production, allocation was needed, as biogas was
Discussion and conclusions
The LCA-based assessment methods have developed remarkably in recent years. However, there is no commonly accepted methodology capable of comprehensively estimating the chosen environmental impacts (climate impacts, land use and land use change, resource depletion, water use, soil quality impacts, and changes in biodiversity) of forest residue and microalgae biofuel production chains. The impacts discussed in this study are highly complex and an accurate assessment of the environmental impacts
Acknowledgements
This work is supported by the Marie Curie's International Research Staff Exchange Scheme (ECO-TOOL Project – Grant Agreement Number: PIRSES-GA-2008-230851), the PEER partnership (Partnership of seven of the largest European environmental centres) and the SUBICHOE-project (Sustainability of biomass utilisation in changing operational environment), which was funded by TEKES – the Finnish Funding Agency for Technology and Innovation, the Finnish Ministry of Employment and the Economy and the
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