LCA
and Metals
Environment
Group at CANMET-MMSL |
ICMM
International
Council on Mining and Metals
International Workshop
on Life-Cycle Assessment and Metals
Sponsored by: UNEP/SETAC/APEC-GEMEED/International
Council on Mining and Metals (ICMM)/NRCan
THE ISSUES
Life-cycle assessment (LCA) has proven to be a valuable tool to
evaluate the potential environmental impact of products and materials.
It is increasingly used by industry for guidance in decision-making
on products and materials. LCA information also influences environmental
policy-making and government regulators.
Recently, the growing global interest in LCA has led a number
of government and industry sectors, including the metals industry,
to develop life-cycle inventory (LCI) databases. Furthermore, a
need has been identified to discuss knowledge that has been obtained
with respect to the mining, production, use and disposal of base
metals, and to compare it with current LCA methodologies. As well,
over the last few years, a major science program has helped better
document the environmental and health interactions of metals and
can be used to enrich LCA.
From April 15 to 17, 2002, a workshop was held in Montréal
to discuss issues related to LCA and metals.
Sixty technical experts, from 15 countries with different perspectives
(LCA, life-cycle impact assessment (LCIA), risk assessment (RA),
economy, geology) and from diverse sectors (industry, academia,
consultant, government) attended the workshop.
It was sponsored by the United Nations Environment Programme (UNEP),
the Society of Environmental Toxicology and Chemistry (SETAC), the
Asia Pacific Economic Cooperation (APEC), the International Council
on Mining and Minerals (ICMM), and Natural Resources Canada. The
workshop was also supported by the International Copper Association,
the International Zinc Association and the Nickel Development Institute.
The aluminum and steel sectors also sent representatives.
The purposes of the workshop were:
- to build bridges between the LCA community and scientists interested
in toxicological and environmental considerations related to metals,
and
- to support the UNEP/SETAC Life-Cycle Initiative by proposing
metal-related areas for future work aimed at improving the quality
of LCA results for decision-making.
The discussions were focussed around three themes: life-cycle inventory,
metal mining, and human and environmental toxicity.
LIFE-CYCLE INVENTORY
The objectives of Theme 1 were:
- to discuss industry- and government-sponsored LCI databases
for metal production and recycling;
- in compliance with ISO 14041, to assess the consistency of data
by examining system boundaries, allocation rules and emission
criteria; and
- to examine data gaps and how to address those issues.
Recycling is an important feature for the metal sector and it
has been a dominant issue with respect to data gaps and how to allocate
the environmental burden. Three conclusions were reached for that
theme.
Review information on metals recycling
A working group can be established (within the Life-Cycle Initiative
or ICMM) to review available information on metals recycling and
techniques for its improvement.
For the primary production, good-quality data exist for the LCI
of steel and base metals. But the data related to emissions associated
with the recycling activities need to be compiled for various commodities.
Furthermore, the knowledge of the recycling rate for various products
can be improved.
Guidance document on recycling
A guidance document entitled "Inherent properties, loop closure
and recycling modeling in LCI in the context of metals" can be developed.
This should be done under the Life-Cycle Initiative and within ISO
standards. It could be expanded to include other materials.
The ISO International Standard 14041 and the ISO Technical Document
1049 describe allocation procedures for recycling based on the "inherent
properties" of the material and how to apply it. The understanding
of the "inherent property" is a function of the background of the
participants. For some, it was the function that defined the properties
and for others it was the atomic structure that determined the properties.
Guidance document on LCI databases
A guidance document can be developed that deals with how LCI databases
should be presented and used (i.e., organized for easy access and
understanding for practitioners; used in transparent and consistent
ways).
This recommendation reflects the tension between practitioners
desiring open access to all data all the time, and the generators/owners
of that data concerned about how that data will be used. It might
be misused out of ignorance or abused for competitive marketing
purposes. Put another way, it is easier to see what practitioners
get out of open databases, and easier to imagine how the generators
of those databases could be affected by the misuse or abuse of those
databases. Moreover, a number of national and regional databases
are being developed that may or may not resemble each other, let
alone databases that are currently found in proprietary software
packages. The process of developing a guidance document could assist
in bringing the interests of the different stakeholders together.
METAL
MINING
The objectives for Theme 2 were to review current information
with respect to mining and to compare it to LCA practices in order
to evaluate gaps and enhance relevancy. Discussions were structured
around the applicability of the concept of resource depletion, the
direct impact of mining, and how to improve the collaboration between
LCA and mining experts.
Resource depletion/availability
A consensus emerged that, as a result of the availability, recyclability
and substitutability of metals, the depletion of resources is not
an issue that requires high-priority consideration; it need not
be a priority issue in the assessment of metals, particularly when
compared to other themes. Since the word "depletion" suggests
scarcity in the minds of many, the expression "resource availability"
or "access to resources" may be more helpful. The word
"access" points to the socio-economic issues that, in practice,
are the most likely to place limits on access to resources. It is,
however, unclear how this aspect would fit into the life-cycle impact
assessment (LCIA) framework, as impact categories with a "positive"
meaning are not used in accepted methodologies.
Physical impact and land use
There is a danger to use some oversimplification in modeling the
environmental impact of mining. Approaches that propose to quantify
the impact of mining strictly as a function of the volume are not
appropriate in LCA. Surface use and other impact categories such
as acidification (acid mine drainage) and salinization are much
more relevant and site specific. Environmental issues related to
tailings stability, mine closure and abandoned mines were discussed.
Case studies
As the impact of mining depends on the site and the management
practices, it has been concluded that case studies could be used
to make generic impact assessment factors for different mining types.
That information would be useful information on uncertainty determination.
In order to increase the reliability of LCA, it has been recommended:
a) to develop a number of case studies that span the range of mining
conditions, management practices and age of the mine; b) to develop
a set of generic applicable factors for the different archetypal
cases and a general average for background databases, and to document
uncertainty ranges; and c) to use the case studies to define criteria
or indicators to measure mining impacts.
HUMAN
AND ENVIRONMENTAL TOXICITY
The objective of Theme 3 was to characterize the methods and technical
limitations, for the incorporation into LCA, of ecological and human
health impacts of metals.
Exploration of this objective was an exercise in establishing
an interface between practitioners of two disciplines: metals life-cycle
assessment and risk assessment (RA). Participants searched for common
ground, defined terms, explored differences of opinion, and discussed
the applications and limitations of each discipline. Since the objective
was one of incorporating ecological and health impacts into LCA,
the emphasis was squarely on how the biology could inform and comply
with the methods and metrics of LCA, and not the reverse. Throughout
the presentations and discussion, topics shifted among metals toxicity,
health and ecological impacts, and risk assessment. Three major
conclusions were reached for that theme.
Definitions on LCA and RA
There is a conflict of jargon as used in LCA and RA. A dictionary
of definitions as used by each and a common ground for definitions
need to be developed.
Metals-specific research issues
Metals-specific research issues need to be investigated to improve
current approaches for addressing toxicological impacts in LCA.
These issues include: transformation/speciation, fate and transport,
bioavailability, background conditions and effects.
How should the form of the metal and its speciation be considered?
For each metal, how many and which species should be considered?
How should the bioavailable fractions in different waters (fresh,
marine, estuarine and laboratory) be considered? How should metals
speciation be considered expressly for terrestrial ecotoxicity separate
from aquatic ecotoxicity? Research, similar to that now under way
in aquatic environments, is needed for terrestrial ecosystems. In
the long term, fate and transport models (e.g., biotic ligand model,
speciation models) need to be adapted for use in LCA. Meanwhile,
in the short term, appropriate components of models can be used
in LCA.
How should uptake from water (including uptake of particulate
matter) and food be considered in general, but also specifically
for metals? Analyses of sources of metals to biota must consider
uptake from food versus uptake from the media (e.g., water, sediment),
the type of diet and the specific organisms being considered for
impact. Consideration of bioavailability is vital in both risk and
life-cycle assessments when insights beyond screening-level assessments
are required. In this process it is important to distinguish between
bioaccumulation (Bioconcentration Factor, or BCF) and bioavailability.
What are the ranges of media and environments that should be considered
in LCAs (e.g., soil types, water types, air compartments)? It would
be interesting to study how this could be dealt with in LCA, by
considering different classes of generic site information (e.g.,
three classes of background conditions). Which benchmark of toxicity
should be used in a comparative assessment? Dose-response measures
that best characterize the dose and shape of the dose-response curve
(Benchmark Dose, or BMD) should be used, if available and where
background concentrations can be taken into consideration. The most
representative species or the median response among species, rather
than the most sensitive species, should be used as the indicator
species for both risk and life-cycle assessment.
Advance integration between RA and LCA
In order to increase the relevance of life-cycle impact assessment
(LCIA), a white paper on the difference and similarities between
LCA and RA and workshops in integrating RA and LCA are recommended.
An instructive case study that includes: (1) both RA and LCA (separate
analyses on the same product, followed by comparison and then an
attempt to integrate), (2) both organic chemical(s) and metals to
ensure uniformity of methods, and (3) one site-specific and one
generalized scenario is suggested.
LCA
AND DEVELOPING COUNTRIES
Developing countries are characterized by a large informal economy,
including artisan mining and recycling activities. Those activities
are having an impact on the environment and human health but are
a source of employment. The life-cycle approach has been applied
successfully in the Philippines to restructure the secondary lead-acid
battery industry, including the informal sector.
Generally, the concept of LCA is new and not well understood by
the mining and metallurgical industry and government in developing
countries, but one of the Life-Cycle Initiative objectives includes
the development and the dissemination of practical tools with the
involvement of developing countries.
NEXT STEPS
The proceedings of the workshop will be co-published by UNEP and
SETAC. Some of the proposed activities will be discussed by ICMM
and by the Life-Cycle Initiative.
CONCLUSIONS
This workshop provided a good opportunity to build bridges among
specialists from different disciplines with a common concern regarding
metals. It permitted identification of issues in the application
of LCA and the proposal of areas for future work in order to increase
the reliability of LCA results. Those results will feed into the
Life-Cycle Initiative.
Steering Committee:
Co-chairmen
Alain Dubreuil (Natural Resources Canada)
Antoon Franckaerts (International Council on Mining and Metals)
Members
Atsushi Inaba (Agency of Industrial Science and Technology - Japan)
Olivier Jolliet (Swiss Federal Institute of Technology - Lausanne)
Gregory Schiefer (Society of Environmental Toxicology and Chemistry)
Guido Sonnemann (United Nations Environment Programme)
Scientific Committee:
Chairman
Alain Dubreuil (National Resources Canada)
Members
Scott Baker (International Copper Association)
Alain Dubreuil (Natural Resources Canada)
Mark Goedkoop (PRé Consultants)
Atsushi Inaba (Agency of Industrial Science and Technology - Japan)
Olivier Jolliet (Swiss Federal Institute of Technology - Lausanne)
Bruce McKean (Nickel Development Institute)
For more information, contact:
Dr. Alain Dubreuil
Tel.: (613) 995-5844
Fax: (613) 996-9041
E-mail: dubreuil@nrcan.gc.ca
Life-Cycle Inventory
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All documents are in PDF format.
Abstracts
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Human and Environmental Toxicity
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Abstracts List
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LCA and Developing Countries
All documents
are in PDF format.
Abstract:
Bordia
- Abstract - Relevance of Life-Cycle Assessment in Developing
Countries
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