Tabea Beck
University of Stuttgart
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International Journal of Life Cycle Assessment | 2013
Thomas Koellner; Laura de Baan; Tabea Beck; Miguel Brandão; Bárbara María Civit; Manuele Margni; Llorenç Milà i Canals; Rosie Saad; Danielle Maia de Souza; Ruedi Müller-Wenk
PurposeAs a consequence of the multi-functionality of land, the impact assessment of land use in Life Cycle Impact Assessment requires the modelling of several impact pathways covering biodiversity and ecosystem services. To provide consistency amongst these separate impact pathways, general principles for their modelling are provided in this paper. These are refinements to the principles that have already been proposed in publications by the UNEP-SETAC Life Cycle Initiative. In particular, this paper addresses the calculation of land use interventions and land use impacts, the issue of impact reversibility, the spatial and temporal distribution of such impacts and the assessment of absolute or relative ecosystem quality changes. Based on this, we propose a guideline to build methods for land use impact assessment in Life Cycle Assessment (LCA).ResultsRecommendations are given for the development of new characterization models and for which a series of key elements should explicitly be stated, such as the modelled land use impact pathways, the land use/cover typology covered, the level of biogeographical differentiation used for the characterization factors, the reference land use situation used and if relative or absolute quality changes are used to calculate land use impacts. Moreover, for an application of the characterisation factors (CFs) in an LCA study, data collection should be transparent with respect to the data input required from the land use inventory and the regeneration times. Indications on how generic CFs can be used for the background system as well as how spatial-based CFs can be calculated for the foreground system in a specific LCA study and how land use change is to be allocated should be detailed. Finally, it becomes necessary to justify the modelling period for which land use impacts of land transformation and occupation are calculated and how uncertainty is accounted for.DiscussionThe presented guideline is based on a number of assumptions: Discrete land use types are sufficient for an assessment of land use impacts; ecosystem quality remains constant over time of occupation; time and area of occupation are substitutable; transformation time is negligible; regeneration is linear and independent from land use history and landscape configuration; biodiversity and multiple ecosystem services are independent; the ecological impact is linearly increasing with the intervention; and there is no interaction between land use and other drivers such as climate change. These assumptions might influence the results of land use Life Cycle Impact Assessment and need to be critically reflected.Conclusions and recommendationsIn this and the other papers of the special issue, we presented the principles and recommendations for the calculation of land use impacts on biodiversity and ecosystem services on a global scale. In the framework of LCA, they are mainly used for the assessment of land use impacts in the background system. The main areas for further development are the link to regional ecological models running in the foreground system, relative weighting of the ecosystem services midpoints and indirect land use.
International Journal of Life Cycle Assessment | 2013
Thomas Koellner; Laura de Baan; Tabea Beck; Miguel Brandão; Bárbara María Civit; Mark Goedkoop; Manuele Margni; Llorenç Milà i Canals; Ruedi Müller-Wenk; Bo Pedersen Weidema; Bastian Wittstock
PurposeTo assess the diverse environmental impacts of land use, a standardization of quantifying land use elementary flows is needed in life cycle assessment (LCA). The purpose of this paper is to propose how to standardize the land use classification and how to regionalize land use elementary flows.Materials and methodsIn life cycle inventories, land occupation and transformation are elementary flows providing relevant information on the type and location of land use for land use impact assessment. To find a suitable land use classification system for LCA, existing global land cover classification systems and global approaches to define biogeographical regions are reviewed.Results and discussionA new multi-level classification of land use is presented. It consists of four levels of detail ranging from very general global land cover classes to more refined categories and very specific categories indicating land use intensities. Regionalization is built on five levels, first distinguishing between terrestrial, freshwater, and marine biomes and further specifying climatic regions, specific biomes, ecoregions and finally indicating the exact geo-referenced information of land use. Current land use inventories and impact assessment methods do not always match and hinder a comprehensive assessment of land use impact. A standardized definition of land use types and geographic location helps to overcome this gap and provides the opportunity to test the optimal resolution of land cover types and regionalization for each impact pathway.Conclusions and recommendationThe presented approach provides the necessary flexibility to providers of inventories and developers of impact assessment methods. To simplify inventories and impact assessment methods of land use, we need to find archetypical situations across impact pathways, land use types and regions, and aggregate inventory entries and methods accordingly.
International Journal of Life Cycle Assessment | 2013
Stefan Albrecht; Peter Brandstetter; Tabea Beck; Pere Fullana-i-Palmer; Kaisa Grönman; Martin Baitz; Sabine Deimling; Julie Sandilands; Matthias Fischer
PurposeThe year-round supply of fresh fruit and vegetables in Europe requires a complex logistics system. In this study, the most common European fruit and vegetable transport packaging systems, namely single-use wooden and cardboard boxes and re-useable plastic crates, are analyzed and compared considering environmental, economic, and social impacts.MethodsThe environmental, economic, and social potentials of the three transport packaging systems are examined and compared from a life cycle perspective using Life Cycle Assessment (LCA), Life Cycle Costing (LCC) and Life Cycle Working Environment (LCWE) methodologies. Relevant parameters influencing the results are analyzed in different scenarios, and their impacts are quantified. The underlying environmental analysis is an ISO 14040 and 14044 comparative Life Cycle Assessment that was critically reviewed by an independent expert panel.Results and discussionThe results show that wooden boxes and plastic crates perform very similarly in the Global Warming Potential, Acidification Potential, and Photochemical Ozone Creation Potential categories; while plastic crates have a lower impact in the Eutrophication Potential and Abiotic Resource Depletion Potential categories. Cardboard boxes show the highest impacts in all assessed categories. The analysis of the life cycle costs show that the re-usable system is the most cost effective over its entire life cycle. For the production of a single crate, the plastic crates require the most human labor. The share of female employment for the cardboard boxes is the lowest. All three systems require a relatively large share of low-qualified employees. The plastic crate system shows a much lower lethal accident rate. The higher rate for the wooden and cardboard boxes arises mainly from wood logging. In addition, the sustainability consequences due to the influence of packaging in preventing food losses are discussed, and future research combining aspects both from food LCAs and transport packing/packaging LCAs is recommended.ConclusionsFor all three systems, optimization potentials regarding their environmental life cycle performance were identified. Wooden boxes (single use) and plastic crates (re-usable) show preferable environmental performance. The calibration of the system parameters, such as end-of-life treatment, showed environmental optimization potentials in all transport packaging systems. The assessment of the economic and the social dimensions in parallel is important in order to avoid trade-offs between the three sustainability dimensions. Merging economic and social aspects into a Life Cycle Assessment is becoming more and more important, and their integration into one model ensures a consistent modeling approach for a manageable effort.
International Journal of Life Cycle Assessment | 2010
Catherine Benoît; Gregory A. Norris; Sonia Valdivia; Andreas Ciroth; Åsa Moberg; Ulrike Bos; Siddharth Prakash; Cássia Maria Lie Ugaya; Tabea Beck
Stahlbau | 2011
Ulrike Kuhlmann; Philippa Maier; Heinz Friedrich; Rolf Kaschner; Martin Mensinger; Marjolaine Pfaffinger; Klaus Sedlbauer; Matthias Fischer; Tabea Beck; Thomas Ummenhofer; Tim Zinke
Stahlbau | 2013
Ulrike Kuhlmann; Philippa Maier; Heinz Friedrich; Rolf Kaschner; Martin Mensinger; Marjolaine Pfaffinger; Klaus Sedlbauer; Matthias Fischer; Katrin Lenz; Tabea Beck; Thomas Ummenhofer; Tim Zinke
Stahlbau | 2017
Tim Zinke; Thomas Ummenhofer; Sarah Schneider; Tabea Beck; Katrin Lenz; Michael Neudeck; Eckart Koch
Stahlbau | 2014
Ulrike Kuhlmann; Philippa Maier; Tim Zinke; Thomas Ummenhofer; Marjolaine Pfaffinger; Martin Mensinger; Sarah Schneider; Katrin Lenz; Tabea Beck; Heinz Friedrich
Mauerwerk | 2012
Tristan Herbst; Sarah Schneider; Tabea Beck; Georg Flassenberg
Stahlbau-Kalender 2016. Eurocode 3 - Grundnorm, Werkstoffe und Nachhaltigkeit. Hrsg.: U. Kuhlmann | 2016
Ulrike Kuhlmann; Philippa Maier; Tim Zinke; Thomas Ummenhofer; Heinz Friedrich; Ralph Holst; Cyrus Schmellekamp; Katrin Lenz; Tabea Beck; Sarah Schneider; Matthias Fischer