Background, aim, and scopeThe development of robust and up-to-date generic life cycle inventory data for materials is absolutely crucial for the LCA
community since many LCA studies rely on these generic data about materials. LCA databases and software usually include within
their package such generic LCI datasets. However, in many cases, the quality of these data is poor while the methodology and
the models used for their development are rarely accessible or transparent. This paper presents the development of robust
European LCI datasets for the production of primary and recycled aluminium ingots and for the transformation of aluminium
ingot into semi-finished products, i.e. sheet, foil and extrusion.
Materials and methodsThe environmental data have been collected through an extensive environmental survey, organised among the European aluminium
industry, focusing on the year 2005 and covering EU27 countries as well as EFTA countries (Norway, Iceland and Switzerland).
From this survey, European averages, i.e. foreground data, have been calculated for the direct inputs and outputs of the various
aluminium processes. Using the GaBi software, the foreground data have been combined within LCI models integrating background
LCI data on energy supply systems, ancillary processes and materials. For the primary aluminium production (smelters), a specific
model for the electricity production has been developed. The methodology for the data consolidation and for the development
of the various models is explained as well as the main differences between the new modelling approach and LCI models used
in the past. An independent expert has critically reviewed the entire LCI project including data collection, models development,
calculation of LCI data and associated environmental indicators.
ResultsAs confirmed by the critical review, the new LCI datasets for aluminium ingot production and transformation into semi-finished
products have been developed though a robust methodology in full accordance with ISO 14040 and 14044. Most significant environmental
data and LCI results are reported in this paper with an emphasis on energy use and the major emissions to air. The full environmental
report, including the critical review report and the calculation of environmental indicators for a pre-set of impact categories,
is available on the website of the European Aluminium Association (EAA 2008). Whenever possible, the updated European averages and the new LCI data are compared with previous results developed from
two past European surveys covering respectively the years 2002 and 1998. For the aluminium processes related to primary production,
European averages are also benchmarked against global averages calculated from two worldwide surveys covering the years 2000
and 2005.
DiscussionWhile some data evolutions are directly attributed to the variation of foreground data, e.g. raw materials consumption or
energy use within the aluminium processes, modifications related to the system boundaries, the background data and the modelling
hypotheses can also influence significantly the LCI results. For primary aluminium production, the evolution of the foreground
data is dominated by the strong decrease of PFC (perfluorocarbon) emissions (about 70% since 1998). In addition, the electricity
structure calculated from the refined electricity model shows significant differences compared to previous models. In the
2005 electricity model, the hydropower share reaches 58% while coal contributes to 15% only of the electricity production.
In 1998, the respective share of coal-based and hydro-electricity were respectively calculated to 25% and 52%. As a result,
the electricity background LCI data are then significantly affected and influence also positively the environmental profile
of primary aluminium in Europe. For the semi-production processes, the reduction of process scrap production, especially for
extrusion and foil, demonstrates the increase of process efficiency from 1998. In parallel, a significant reduction of energy
use is observed between 1998 and 2005. However, this positive trend is not fully reflected within LCI data due to the significant
contribution of the background electricity data. The choice of the electricity model plays also a critical role for these
transformation processes since electricity production contributes to about 2/3 of the consumption of the non-renewable energy
and to about the same level of the air emissions. In such a case, the move from the UCPTE electricity model used in the past
towards the EU25 electricity model used for the development of the updated LCI data has a detrimental effect on the environmental
profile of the three LCI datasets respectively related to sheet, foil and extrusion. In addition to energy and process scrap
reduction, the reduction of the VOC (volatile organic compounds) emission is also a major trend in foil production. Finally,
for old aluminium scrap recycling, the new LCI data show a dramatic improvement regarding energy efficiency, reinforcing the
environmental soundness of promoting and supporting aluminium recycling within the aluminium product life cycles.
ConclusionsThis paper shows the development of generic LCI data about aluminium production and transformation processes which are based
on robust data, methodologies and models in full accordance with ISO 14040 and 14044 standards, as confirmed by the critical
review. The publishing of these LCI datasets definitely shows the commitment of the European aluminium industry to contribute
in a transparent, fair and scientifically sound manner to product sustainability in a life cycle thinking perspective.
Recommendations and perspectivesSoftware houses and LCA practitioners are invited to update their generic European data on aluminium with the herewith datasets.
Even if the quality and the completeness of these LCI data reach a high standard, some areas for data improvements have been
identified, as described within the review report. Land use, water use and solid waste treatment appear as three priority
areas for data refining and improvement. The land use dimension, particularly meaningful for bauxite mining, is not covered
in the current LCI data while it is now integrated within many LCA studies. Up to now, the reporting of meaningful and robust
data on water origins and use have not been possible due to the huge discrepancies between the surveyed sites combined with
the difficulty to report coherent input and output water mass flows. The development of water data, only focussing on water-stressed
areas, will most probably make more sense in the future. Finally, collecting more qualitative information about solid waste
processing and treatment will help to include such operations within the system boundaries and to model their associated air,
water and soil emissions.