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Comparison of egg packages: package from polystyrene or recycled paper?

Comparison of egg packages: package from polystyrene or recycled paper?. Kertu-Liisa Terk. Introduction. The application of life cycle assessment for the comparison The input and output streams of mass and energy are examined The environmental impacts

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Comparison of egg packages: package from polystyrene or recycled paper?

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  1. Comparison of egg packages: package from polystyrene or recycled paper? Kertu-Liisa Terk

  2. Introduction • The application of life cycle assessment for the comparison • The input and output streams of mass and energy are examined • The environmental impacts • Use of EcoIndicator 95 for the Impact Assessment step

  3. Polystyrene package: • Sanitary and protects food against bacteria and spoilage. • Light weighted packages • Unknown is styrene penetration into the edible part of egg

  4. Recycled paper: • Does not protect from moisture, spoilage and can damage its shape as well. • Lightweight material, but its wet strength is so low that it cannot qualify for many food packaging applications unless it is reinforced and waterproofed.

  5. Purpose of this study • Evaluate, via the tool of LCA, the environmental burdens associated with the egg packaging products, polystyrene and recycled paper, by identifying and quantifying energy and material uses and releases • To assess impacts on the environment throughout the entire life of the product including extracting and processing raw materials, manufacturing, transportation and distribution, use, reuse, maintenance, recycling and final disposal.

  6. Methodology • Boundary of the system • Functional unit: quantity of 300 000 eggs which need 50 000 eggcups of six eggs each. • Weight of PS eggcup 15 g, recycled paper 22 g. 50 000 eggcups require for their production a quantity of 0,75 tn of PS and 1,1 tn recycled paper. • Does’nt include transportation, distribution and utilization stages of the product • It is assumed that both egg-packaged products are disposed in landfills.The waste treatment stage was not taken into account because of the different behaviour of the two materials in landfill. • Capital equipment and minor ancillary materials have been excluded. • Depicting of mechanical injures and maintenance has not been considered • Geographically localized in Greece, PS is imported to Greece. • Due lack of data an energy model that represents European situation has been used.

  7. Methodology • Data collectionFor each egg-package the following environmental impact indicators were calculated: • Energy demand: electric power and heat; • Non-renewable fuel demand: coals, fuels, natural gas; • Raw materials demands: common raw materials; • Consumption of primary energy sources: coal seam, crude oil, hydropower, nuclear fuel, crude natural gas, and biomass of trees; • Air emissions: CH4, SO2, NOx, CO and CO2; • Water emissions: total suspended solids (TSS), biological oxygen demand (BOD), chemical oxygen demand (COD), and chlorinated organic compounds (AOXs); • Solid emissions: municipal wastes from life cycle and in landfills.

  8. Methodology • Impact Assessment • Classification and characterization – the data from the inventory analysis are grouped together into a number of impact categories (greenhouse effect, ozone depletion...). • Normalization – to normalize the aggregated data per impact category in relation to the actual magnitude of the impacts within this category in some given area. The reason is to increase the comparability of the data from the different impact categories and thus provide a basis for the next step, the evaluation. Therefore each impact calculated for the life cycle of a product is benchmarked against the known total effect for this impact category. Reveals which effects are larger or smaller. • Evaluation –different specific impact categories are weighted so that they can be compared among themselves. The normalized impact scores are multiplied by a weighting factor representing the relative importance of the effect. • Eco-Indicator’95 method

  9. Description of the process • Production of polystyrene egg cups

  10. Description of the process • Production of recycled paperegg cups

  11. Results • No final judgements can be made as not all impacts are considered to be of equal importance. • Necessary is to set a hierarchy of relative importance of the different impacts. • Raw materials – no direct comparison can be made since they need different raw materials.

  12. Polystyrene eggcup contributes: Greenhouse effect Acidification Winter smog Summer smog Recycled paper eggcup contributes Heavy metals Winter smog Results

  13. Evaluation results and comparison GWP – greenhouse warming potential ODP – ozone depletion potential AP – acidification potential NP – nutrient enrichment SS – summer smog WS – winter smog CS – carcinogenic substances HM – heavy metals

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