Page 15 - Materials Chemistry, Second Edition
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Life Cycle Assessment: Principles, Practice and Prospects
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                 perhaps most topically, what are the implications for climate change of different energy scenar-
                 ios, and how can we identify optimal services from ‘sustainable’ levels of impact?
                    In the post-World War 2 era, a new generation of energy technologies – nuclear, geother-
                 mal, modern wind and other ‘renewables’ – tested the energy balance question. Energy analysis
                 became increasingly complex, systemic and sophisticated through successive empirical devel-
                 opments. At first, the technique was typically used to assess production of a given unit of
                 energy in a given form, examining immediate inputs on site in the production system. Inevita-
                 bly, as more complex generation technologies were examined, so the analysis was extended.
                 For example, the question of whether a given nuclear generation technology produced more
                 energy than it consumed led researchers to look beyond the generation facilities themselves to
                 ‘yellow cake’ production and uranium mining, long-term waste management, and even to the
                 impacts of transport (of personnel, materials and equipment) and associated research, devel-
                 opment, marketing and management services. This was a precursor to what became known as
                 ‘life cycle analysis’, a systematic process-oriented approach to identifying energy inputs in the
                 production of energy services.
                    In the late 1960s, the first Resource Environmental Profile Analyses (REPAs) were under-
                 taken and these became the forerunners of modern LCA. Notably, Coca Cola Amatil commis-
                 sioned work by a group of researchers (later to become Franklin Associates) in the United
                 States of America (USA) to investigate the resources and environmental profile of different
                 packaging materials for their products (Hunt et al. 1974). Oil shortages in the early 1970s led to
                 a focus back on energy analysis. However, by the mid-1980s, multi-criteria systematic inquiry
                 had spread to include nappies, appliances, automobiles and housing. Interchangeable terms
                 were used to describe these studies including eco-balances, cradle-to-grave analysis, and life
                 cycle analysis. In 1990, the term ‘life cycle assessment’ was proposed and agreed upon by those
                 attending a workshop in Vermont, USA, held by the Society of Environmental Toxicology and
                 Chemistry (SETAC).
                    Rapid development followed, as LCA grew into a body of systematic, inclusive, analytical
                 approaches to environmental impact assessment. SETAC then embarked on the development
                 and extension of LCA, publishing various ‘best-practice’ guides (e.g. Barnthouse et al. 1997;
                 Kotaji et al. 2002; Udo de Haes et al. 2002) and advice on LCA simplification and methods (e.g.
                 Udo de Haes 1996; Christiansen 1997). Applications to public policy (Allen et al. 1997) and
                 particular sectors, such as building and construction (Kotaji et al. 2003), were also examined
                 as well as the application of LCA to more embedded management modes within organisations
                 (Hunkeler et al. 2004).
                    In 2002, the United Nations Environment Programme (UNEP) and SETAC formed the
                 UNEP/SETAC Life Cycle Initiative to assist development and uptake of LCA. Building upon a
                 base of practice in several European countries, the USA and Japan, this initiative seeks to
                 enable users to put life cycle thinking into practice. This has generated focus on the ‘new’
                 manufacturing centres in Asia (including the subcontinent and eastern Asia), Africa and South
                 America. Hence, as the production centres of modern manufacturing shifted through the
                 effects of globalisation, so LCA practitioners followed, further developing methods and tech-
                 niques for calculating the environmental impacts of production and consumption systems.
                 The apparent interdependence of evolving LCA practice and demand across geographic regions
                 has specific implications in Australia.


                 1.2  LCA definition, standards and process
                 Although many definitions exist, LCA essentially comprises a systematic evaluation of envi-
                 ronmental impacts arising from the provision of a product or service. The original Interna-








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