Abstract
PurposeThe assessment of potential environmental impacts associated to mineral resource use in LCA is a highly debated topic. Most current impact assessment methods consider the extraction of resources as the issue of concern, while their dissipation is an emerging concept. This article proposes an approach to account for mineral resource dissipation in life cycle inventories (LCIs), with application to a case study.MethodsThe definition of mineral resources is first discussed considering both current main LCA practice and the context of resource dissipation. Secondly, the approach is described: considering a short-term perspective (25 years), any flow of resources to (i) environment, (ii) final waste disposal facilities, and (iii) products-in-use in the technosphere, with the resources not providing any significant function anymore (including due to non-functional recycling), is suggested to be reported as dissipative at the level of unit processes. This approach first requires to map the flows of mineral resources into and out of the unit processes under study (“resource flow analysis”), before identifying the dissipative flows and reporting them in LCI datasets.Results and discussionThe approach is applied to analyze the direct dissipation of mineral resources along the primary production of copper, using Ecoinvent (v3.5) datasets. The production of 1 kg of copper cathode generates 0.88 kg of direct dissipative flows of resources (primarily calcium carbonate, copper, and to a lower extent iron), with important contributions of “tailings disposal,” “pyrometallurgy,” and “mining and concentration.” Moreover, this article discusses (i) how the developed approach would change the interpretation of results regarding mineral resources in LCA, (ii) how far some key methodological aspects of this approach (e.g., the temporal perspective) can affect the inventory results (e.g., in the case of the primary production of copper, considering a long-term perspective implies a significant shift in main contributions regarding both unit processes and resource flows), and finally (iii) the issue of new data requirements, in terms of availability and adequacy.ConclusionsAs demonstrated in the case study, existing LCI datasets and supporting documentation contain at least part of the data and information required to consistently compile the dissipative flows of resources at the unit process level, yet with the need for some complementary data and assessments. This approach may be particularly relevant to better support the development of more resource-efficient techniques or product designs. It is still open how to adapt characterization approaches to account for the impact induced by these resource dissipative flows.
Highlights
In 2011, the International Reference Life Cycle Data System (ILCD) handbook, published by the Joint Research Centre of the European Commission (EC-JRC), provided recommendations on models and characterization factors that should be used for impact assessment in life cycle assessment (LCA; EC-JRC, 2011)
The approach consists in reporting the dissipative flows, in mass units, at the unit process level
This approach is in line with most of the studies which have dealt so far with resource dissipation in material flow analysis (MFA) and SFA, in which a set of dissipative flows is usually predefined before the corresponding masses are calculated based on different types of data (Beylot et al 2020)
Summary
In 2011, the International Reference Life Cycle Data System (ILCD) handbook, published by the Joint Research Centre of the European Commission (EC-JRC), provided recommendations on models and characterization factors that should be used for impact assessment in life cycle assessment (LCA; EC-JRC, 2011) This created the basis for the Product and Organization Environmental Footprint. The ADP is based on the concept of resource depletion: the extraction of a resource from the Earth’s crust is considered to contribute to this resource depletion (exhaustion of the natural stock) This recommendation is in line with that of the “task force mineral resources” of the United Nations Environment Life Cycle Initiative with respect to the LCA studies which aim at quantifying the relative contribution of a product system to the depletion of mineral resources (Berger et al 2020)
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