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Natural materials life cycle assessment

For a full life cycle assessment, the basic principle is that each material and energy input into the system should be traced back to natural resources obtained from the environment, or to releases into the environment. These are termed elementary flows , and they represent inputs into or outputs from the system being analysed. In an analysis of this type, it may be relatively straightforward to assign a material value to a flow of (for example) water effluent into the environment, but what may be less certain is the environmental impact of such a flow in a quantitative sense. [Pg.192]

Products and processes all have a natural life cycle. For example, the life cycle of a product starts from the extraction of raw materials for its production and ends when the product is finally disposed. In the production, use and disposal of this product, energy is consumed and wastes and emissions are generated. A life-cycle assessment is an analysis in which the use of energy and materials are quantified and the potential environmental and societal impacts are predicted. Life-cycle thinking is progressively being adopted by industry as an... [Pg.254]

Environmental life-cycle assessment (LCA) provides a mechanism for systematically evaluating the environmental impacts linked to a product or process and in guiding process or product improvement efforts. LCA-based information also provides insights into the environmental impacts of raw material and product choices, and maintenance and end-of-product-life strategies. Because of the systematic nature of LCA and its power as an evaluative tool, the use of LCA is increasing as environmental performance becomes more and more important in society. It is likely that LCA will soon become widely used within U.S. industry and by those involved in crafting national and regional environmental policy. [Pg.184]

Murphy, Norton, 2008. Life Cycle Assessment of Natural Fibre Insulation Materials. Final report Imperial College London, Prepared for the NNFCC. http //eiha.org/media/attach/ 372/lca fibre. pdf. [Pg.252]

For consumers, natural fibre composites in automobiles provide better thermal and acoustic insulation than fibre glass and reduce irritation of the skin and respiratory system. The low density of plant fibres also reduces vehicle weight, which cuts fuel consumption [72]. Alves et al. [73] studied the life cycle assessment (LCA) analysis of the replacement of glass fibres by jute fibres as reinforcement of composite materials to produce automotive structural components in the structural frontal bonnet of an off-road vehicle (Buggy). [Pg.25]

The chapter demonstrates that in spite of the incompatibility between hydrophilic natural fibres and hydrophobic polymeric matrices, the properties of natural fibre composites can be enhanced through chemical modifications. The chemical treatments have therefore played a key role in the increased applications of natural fibre composites in the automotive sector. Recent work has also shown that if some of the drawbacks of natural fibres can be adequately addressed, these materials can easily replace glass fibres in many applications. The chapter has also shown that there have been attempts to use natural fibre composites in structural applications, an area which has been hitherto the reserve of synthetic fibres like glass and aramid. The use of polymer nanocomposites in applications of natural fibre-reinforced composites, though at infancy, may provide means to address these efficiencies. Evidence-based life-cycle assessment of natural fibre-reinforced composites is required to build confidence in the green composites applications in automotive sector. [Pg.696]

This book on natural rubber presents a summary of the present state-of-the-art in the study of these versatile materials. The two volumes cover all the areas related to natural rubber, from its production to composite preparation, the various characterization techniques and life cycle assessment. Chapters in this book deal with both the science of natural rubber - its chemistry, production, engineering properties, and the wide-ranging applications of natural rubber in the modern world, from the manufacture of car tyres to the construction of earthquake protection systems for large buildings. Although there are a number of research publications in this field, to date, no systematic scientific reference book has been published specifically in the area of natural rubber as the main component in systems. We have developed the two volumes by focusing on the important areas of natural rubber materials, the blends, IPNs of natural rubber and natural rubber based composites and nanocomposites their preparation and characterization techniques. The books have also profoundly reviewed various classes of fillers like macro, micro and nano (ID, 2D and 3D) used in natural rubber industries. The applications and the life cycle analysis of these rubber based materials are also highlighted. [Pg.6]

The relatively new field of industrial ecology provides a useful organizing framework for DEE (Lowe, 1993). Design for Environment (DEE) is the terminology for the third component of the LCA life-cycle improvement assessment. The principle of sustainable development suggests that companies or individuals should try both to minimize the consumption of virgin natural resources and to minimize the generation of waste material that has no productive use. [Pg.108]

Opportunities for P2 at the macroscale can be identified from three distinct perspectives. First, waste-generation audits identify flow rates and compositions of materials in the industrial economy, which are potential P2 targets, from natural resource extraction to consumer product disposal. Second, industrial ecology studies examine the uses and the wastes associated with a particular material. Third, life-cycle analyses (LCA) assess the environmental impacts due to the life cycles of individual products/processes by determining waste generation rates, energy consumption, and raw material usage. [Pg.108]

Determining the impact assessment requires classification of each impact into one of these categories, characterization of the impact to establish some kind of relationship between the energy or materials input/output and a corresponding natural resource/human health/ecological impact, and finally the evaluation of the actual environmental effects. Many life cycle analyses admit that this last phase involves social, political, ethical, administrative, and financial judgments and that the quantitative analyses obtained in the characterization phase are only instruments by which to justify policy. A truly scientific life cycle analysis would end at the characterization phase, as many of the decisions made beyond that point are qualitative and subjective in nature. [Pg.23]


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See also in sourсe #XX -- [ Pg.84 ]




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