Page 94 - Materials Chemistry, Second Edition
P. 94

80                                           A.-S. Nizami and I. M. Ismail

            1 Introduction

            1.1 Lignocellulosic Biofuels, Renewable Directive,
                and Sustainability

            Large-scale replacement of fossil fuels with renewable energy sources is necessary
            due to energy security and climate change in the form of greenhouse gas (GHG)
            emissions (Farrell et al. 2006). Thus, there is an emerging utilization of ligno-
            cellulosic biomass, which is the largest source of renewable carbohydrates for
            bioenergy production (Jørgensen et al. 2007). The lignocellulosic biomass is an
            attractive feedstock for anaerobic digestion (AD) that produces biomethane to be
            used as a biofuel. However, according to the EU renewable directive of 2009,
            ‘‘… the GHG emission saving from the use of biofuels and bioliquids taken into
            account… shall be at least 35 %, whereas from 2017, GHG emission savings shall
            be at least 50 %’’ (EC 2009). Thus, the renewable directive (EC 2009) promotes
            nonfood feedstocks including perennial grasses, forest, and agricultural residues,
            energy crops, organic fraction of municipal solid waste (OFMSW), and other like
            substrates for biofuel production. Grasses are one of the lignocellulosic biomass
            for producing enriched biomethane as a transport fuel (Peeters 2009; Eisentraut
            2010; Singh et al. 2010a). Biomethane from lignocellulosic biomass has a better
            energy balance when compared to first-generation liquid transport biofuels (Korres
            et al. 2011). Many European countries are seeking biofuels to meet sustainability
            criteria and to achieve GHG emission savings targets (Korres et al. 2010).



            1.2 Significance of LCA Studies for Biofuels


            The generation of biofuels is facing the challenges of becoming full commer-
            cialization (Singh et al. 2010b), which is expected in near future due to improved
            process technologies and value-added products (IEA 2009). Thus, to ascertain
            optimal biofuel strategies, it is necessary to take into account environmental
            impacts of biofuel and bioproducts (by-products) from cradle to grave. The indi-
            rect input in the biofuel production process, related emissions and wastes as well
            as the fate of downstream products are all included in life-cycle assessment (LCA)
            studies. Thus, the overall assessment and impact evaluation of biofuels is carried
            out in a systematic manner. Nevertheless, LCA can also bring inaccurate and
            unsuitable actions for the industry, policy-making sectors, and people’s perception
            if not exercised correctly (Korres et al. 2011).
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