Working Paper 43 - ETH Zurich - Natural and Social Science ...
Working Paper 43 - ETH Zurich - Natural and Social Science ... Working Paper 43 - ETH Zurich - Natural and Social Science ...
Working Paper 43 (Re-) Structuring the Field of Non- Energy Mineral Resource Scarcity Umweltnatur- und Umweltsozialwissenschaften Natural and Social Science Interface Sciences naturelles et sociales de l'environnement Maya Wolfensberger, Daniel J. Lang & Roland W. Scholz March 2008
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<strong>Working</strong> <strong>Paper</strong> <strong>43</strong><br />
(Re-) Structuring<br />
the Field of Non-<br />
Energy Mineral<br />
Resource Scarcity<br />
Umweltnatur- und Umweltsozialwissenschaften<br />
<strong>Natural</strong> <strong>and</strong> <strong>Social</strong> <strong>Science</strong> Interface<br />
<strong>Science</strong>s naturelles et sociales de l'environnement<br />
Maya Wolfensberger,<br />
Daniel J. Lang &<br />
Rol<strong>and</strong> W. Scholz<br />
March 2008
Publisher:<br />
Prof. Dr. Rol<strong>and</strong> W. Scholz<br />
Institute for Environmental Decisions (IED)<br />
<strong>Natural</strong> <strong>and</strong> <strong>Social</strong> <strong>Science</strong> Interface (NSSI)<br />
<strong>ETH</strong> Zürich CHN J74.2<br />
Universitätsstrasse 20<br />
CH-8092 Zürich<br />
Tel. +41 44 632 5892<br />
Fax +41 44 632 10 29<br />
E-mail: rol<strong>and</strong>.scholz@env.ethz.ch<br />
Authors:<br />
Maya Wolfensberger<br />
Institute for Environmental Decisions (IED)<br />
<strong>Natural</strong> <strong>and</strong> <strong>Social</strong> <strong>Science</strong> Interface (NSSI)<br />
<strong>ETH</strong> Zürich<br />
CH-8092 Zürich<br />
Prof. Dr. Rol<strong>and</strong> W. Scholz<br />
Institute for Environmental Decisions (IED)<br />
<strong>Natural</strong> <strong>and</strong> <strong>Social</strong> <strong>Science</strong> Interface (NSSI)<br />
<strong>ETH</strong> Zürich CHN J74.2<br />
Universitätsstrasse 20<br />
CH-8092 Zürich<br />
Tel. +41 44 632 58 92<br />
E-mail: rol<strong>and</strong>.scholz@env.ethz.ch<br />
Dr. Daniel J. Lang<br />
Institute for Environmental Decisions (IED)<br />
<strong>Natural</strong> <strong>and</strong> <strong>Social</strong> <strong>Science</strong> Interface (NSSI)<br />
<strong>ETH</strong> Zürich CHN J72.2<br />
Universitätsstrasse 20<br />
CH-8092 Zürich<br />
Tel. +41 44 632 60 37<br />
E-mail: daniel.lang@env.ethz.ch
(Re-) Structuring the Field of<br />
Non-Energy Mineral Resource Scarcity<br />
Summary of the Workshop “Scarce Raw Materials”<br />
August 31-September 2, 2007 – Davos, Switzerl<strong>and</strong><br />
This document is intended to summarize the discussions of the workshop<br />
“Scarce Raw Materials” <strong>and</strong> is targeted at the participants, involved institutions,<br />
<strong>and</strong> further interested parties.<br />
Maya Wolfensberger, Daniel J. Lang & Rol<strong>and</strong> W. Scholz<br />
Contents<br />
Contents ......................................................................................................................................................................................... 1<br />
Setting ............................................................................................................................................................................................ 2<br />
Workshop goals <strong>and</strong> topics ............................................................................................................................................ 3<br />
Preparation <strong>and</strong> Follow-up Phase .............................................................................................................................. 4<br />
Organization .......................................................................................................................................................................... 4<br />
Participants ............................................................................................................................................................................ 5<br />
Program ................................................................................................................................................................................... 6<br />
Summary of the Workshop Discussions ...................................................................................................................... 7<br />
Topic A: The Role of Scarcity in Society ................................................................................................................... 7<br />
Topic B: Causes of Scarcity ........................................................................................................................................... 10<br />
Topic C: Sustainable Coping Strategies ............................................................................................................... 14<br />
Topic D: The »Red List of Scarce Raw Materials« ............................................................................................. 17<br />
Summary .................................................................................................................................................................................... 20<br />
Concluding Remarks ............................................................................................................................................................. 22<br />
References ................................................................................................................................................................................. 22<br />
Glossary ....................................................................................................................................................................................... 24<br />
Annex ............................................................................................................................................................................................ 26
Maya Wolfensberger, Daniel J. Lang & Rol<strong>and</strong> W. Scholz<br />
Setting<br />
Mineral raw materials exhibit an ever-increasing importance <strong>and</strong> indispensability in<br />
various products. The rapid development of electronic industrial products requires a growing<br />
diversity of mineral raw materials for specific functions, especially engineering metals. Some<br />
cycles of materials such as copper are today mainly dominated by human action (Klee &<br />
Graedel, 2004). The dissipative use of a number of metals has increased in a variety of applications<br />
(Ayres, 1997) <strong>and</strong> could represent a cause for concern as it st<strong>and</strong>s for an irreversible loss of<br />
material. Concerns arose, among others, because the viability of recycling at end-of-life seems<br />
to be hindered by the materials concentration in products (Johnson, Harper, Lifset, & Graedel,<br />
2007). Gordon et al. (2006) estimated the quantities of metals residing in ore in the lithosphere,<br />
in use in products <strong>and</strong> in waste deposits. In the case of copper, the results suggest that a sustained<br />
supply at today’s consumption rates require measures such as near-complete recycling.<br />
Although others, such as Tilton & Lagos (2007), have argued against these results, the awareness<br />
that the scarcity of certain mineral raw materials may be a future challenge to society has<br />
recently increased. The enormous increases in prices of some specialty metals used for emerging<br />
technologies have endorsed these concerns <strong>and</strong> finally brought the notion of scarcity back<br />
to the forefront of scientific research <strong>and</strong> public discussion (Wäger & Classen, 2006). Industrialized<br />
countries are now largely dependent on imported ores of many metals from a shrinking<br />
list of potential mineral exporters. For instance, the emerging economies of India <strong>and</strong> China<br />
require enormous amounts of material, are growing rapidly, <strong>and</strong> will increase the competition<br />
among importers (Ayres, 1997). Hence, a nation’s or an industrial branch’s access to the relevant<br />
mineral raw materials might become increasingly important in ensuring a functioning market<br />
economy <strong>and</strong> securing national interests. Growing scarcity might increase the conflict potential<br />
between nations <strong>and</strong>/or continents <strong>and</strong> favor strategic decisions or market interventions.<br />
The regional distribution of those non-renewable resources <strong>and</strong> the different purchasing<br />
power of nations are critical issues to be considered, particularly when addressing intragenerational<br />
equity issues. The globally widespread <strong>and</strong> unequally distributed material flows of mineral<br />
raw materials matter with respect to societal <strong>and</strong> political development 1 <strong>and</strong> need further<br />
consideration.<br />
1 Finally, most economic resource models depart from the basic assumption of a market economy as the prevailing<br />
economic system. However, discussing resource scarcity should also imply considering long-term developments (i.e.,<br />
>100 years). Within these time scales, new economic <strong>and</strong> societal systems might emerge which are based on regulatory<br />
mechanisms that differ from a market economy.<br />
2 March 2008
(Re-) Structuring the field of Non-Energy Mineral Resource Scarcity<br />
Workshop goals <strong>and</strong> topics<br />
During a two-day workshop, a group of the world’s leading experts in the field of resource<br />
availability, management, economy, <strong>and</strong> material sciences discussed the incidence of<br />
<strong>and</strong> evidence for potential raw material scarcity <strong>and</strong> possible ways to create an anticipatory<br />
<strong>and</strong> preventive resource management. The focus was on non-renewable resources not used as<br />
fuels. Among these, special emphasis was placed on mineral raw materials such as Platinum<br />
Group Elements (PGEs, see Glossary), Rare Earth Elements (REEs, see Glossary), more conventional<br />
elements like zinc, copper, or titanium, <strong>and</strong> minerals used as fertilizers, such as phosphorus<br />
or potassium.<br />
The subject was analyzed under four topic areas that structure <strong>and</strong> address important issues<br />
in the field, aiming to elicit the relevant foci with regard to the dynamics <strong>and</strong> significance<br />
of scarcity both at present <strong>and</strong> in the future. The topics were, at the same time, chosen as being<br />
conducive to building mankind’s capacity to estimate future societal vulnerabilities emerging<br />
from raw material scarcity:<br />
• The Role of Scarcity in Society (Topic A): What is meant by scarcity <strong>and</strong> what role does it play<br />
in society?<br />
• The Causes of Scarcity (Topic B): What are the potential causes of scarcity in the future?<br />
• Sustainable Coping Strategies: (Topic C): What can a society committed to Sustainable<br />
Development do to alleviate scarcity?<br />
• The »Red List of Scarce Raw Materials« (Topic D): Would a Red List be a suitable instrument<br />
to prevent scarcity?<br />
The aim of topic D was to provide evidence for the relevance of preventive resource management<br />
<strong>and</strong> to set the stage for the future course of action. Such management should help to<br />
avoid unexpected scarcities that have the potential to endanger human welfare by indicating<br />
priorities of actions with respect to Research <strong>and</strong> Development (R&D), policy making or<br />
lifestyle changes. During the workshop, a half-day session was dedicated to each topic.<br />
<strong>ETH</strong>-UNS <strong>Working</strong> <strong>Paper</strong> <strong>43</strong> 3
Maya Wolfensberger, Daniel J. Lang & Rol<strong>and</strong> W. Scholz<br />
Preparation <strong>and</strong> Follow-up Phase<br />
The workshop was embedded in an in-depth preparation phase (April to August 2007)<br />
<strong>and</strong> follow-up phase (ongoing since October 2007). The preparation phase <strong>and</strong> the initial postprocessing<br />
phase of the workshop were coordinated within the scope of a Master’s thesis completed<br />
by Maya Wolfensberger Malo <strong>and</strong> supervised by Dr. Daniel J. Lang <strong>and</strong> Prof. Rol<strong>and</strong> W.<br />
Scholz.<br />
The results of both phases are documented in a final report available on request (daniel.lang@env.ethz.ch).<br />
Within the scope of the preparation phase, a framework consisting of the four mentioned<br />
topics was constructed with the intention of initiating <strong>and</strong> sustaining the workshop discussions,<br />
compiling the fundamental knowledge base, <strong>and</strong> proposing possible foci for the discussion.<br />
The data collection was carried out via literature research <strong>and</strong> a Delphi-like inquiry process<br />
among the invited experts. Based on these data, hypotheses were extracted <strong>and</strong> formulated.<br />
The relevant information was provided to the experts in the form of a booklet, which<br />
provided a basis for the workshop discussions. Within the scope of the follow-up process, it is<br />
planned to merge the data collected into a joint publication.<br />
Organization<br />
The workshop was financed by the Swiss Federal Office for the Environment (FOEN). It<br />
was organized by the Institute for Environmental Decisions – <strong>Natural</strong> <strong>Science</strong> <strong>Social</strong> Interface<br />
at <strong>ETH</strong> <strong>Zurich</strong> (IED/NSSI). The workshop is part of a cooperation project between IED/NSSI, the<br />
Swiss Federal Office for the Environment (FOEN) - Waste <strong>and</strong> Raw Materials Division, the Environmental<br />
Protection Agency of Canton <strong>Zurich</strong> (AWEL) <strong>and</strong> the University of <strong>Zurich</strong> – Chair of<br />
<strong>Social</strong> <strong>and</strong> Industrial Ecology (SIE).<br />
The workshop took place Aug. 31-Sept. 2, 2007 in Davos, Switzerl<strong>and</strong>, antecedent to <strong>and</strong> in<br />
collaboration with the conference R07, »Recovery of Materials <strong>and</strong> Energy for Resource Efficiency»<br />
organized by the Swiss Federal Laboratories for Materials Testing <strong>and</strong> Research (EMPA)<br />
<strong>and</strong> the Swiss Academy of Engineering <strong>Science</strong>s.<br />
4 March 2008
(Re-) Structuring the field of Non-Energy Mineral Resource Scarcity<br />
Participants<br />
Experts from different disciplines, such as resource economy, material sciences, geology,<br />
<strong>and</strong> industrial ecology were invited to participate. The ten experts in those fields listed bellow<br />
were selected based on Internet research <strong>and</strong> a “snowball inquiry process”.<br />
Inhee Chung<br />
Dr. John H. DeYoung, Jr.<br />
Juerg Gerber<br />
Prof. Thomas E. Graedel<br />
Prof. Chris T. Hendrickson<br />
Prof. Jacqueline A. Isaacs<br />
Prof. R<strong>and</strong>olph E. Kirchain<br />
Prof. Armin Reller<br />
Prof. John E. Tilton<br />
Prof. Friedrich-W. Wellmer<br />
UNEP, Division of Technology, Industry <strong>and</strong> Economics (DTIE), France<br />
U.S. Geological Survey, USA<br />
World Business Council of Sustainable Development (WBSCD) <strong>and</strong> Alcan<br />
Switzerl<strong>and</strong><br />
Yale School of Forestry & Environmental Studies, USA<br />
Carnegie Mellon University, USA<br />
Northeastern University Boston, USA<br />
Massachusetts Institute of Technology, USA<br />
University of Augsburg, Germany<br />
Colorado School of Mines, USA <strong>and</strong> Pontificia Universidad Católica de<br />
Chile<br />
(Formerly) Federal Institute for Geosciences <strong>and</strong> <strong>Natural</strong> Resources<br />
(BGR), Germany<br />
Dr. Patrick Wäger of the Swiss Federal Laboratories for Materials Testing <strong>and</strong> Research<br />
(EMPA) acted as a liaison officer for the World Conference “R07, Recovery of Materials <strong>and</strong> Energy<br />
for Resource Efficiency“<br />
The Steering Committee included 10 consultants representing the Swiss entities involved,<br />
including the <strong>ETH</strong> <strong>Zurich</strong> (Prof. Scholz’s Chair, <strong>Natural</strong> <strong>Social</strong> <strong>Science</strong> Interface at the<br />
Institute for Environmental Decision (NSSI/IED)), the Swiss Federal Office for the Environment<br />
(FOEN), the Environmental Protection Agency of Canton <strong>Zurich</strong> <strong>and</strong> the University of <strong>Zurich</strong>.<br />
Prof. Rol<strong>and</strong> W. Scholz<br />
Dr. Daniel J. Lang<br />
Andy Spörri<br />
Maya Wolfensberger Malo<br />
Prof. Claudia R. Binder<br />
Dr. Hans-Peter Fahrni<br />
Susan Glättli<br />
Dr. Elmar Kuhn<br />
Dr. Stefan Schwager<br />
Dr. Beat Stäubli<br />
<strong>ETH</strong> <strong>Zurich</strong>, NSSI/IED, Principal Organizer<br />
<strong>ETH</strong> <strong>Zurich</strong>, NSSI/IED, Principal Organizer<br />
<strong>ETH</strong> <strong>Zurich</strong>, NSSI /IED, Junior Organizer<br />
<strong>ETH</strong> <strong>Zurich</strong>, NSSI /IED, Junior Organizer<br />
University of Zürich, <strong>Social</strong> <strong>and</strong> Industrial Ecology (UZH-SIE), Switzerl<strong>and</strong><br />
FOEN – Waste <strong>and</strong> Raw Materials Division, Switzerl<strong>and</strong><br />
FOEN – Waste <strong>and</strong> Raw Materials Division, Switzerl<strong>and</strong><br />
Environmental Protection Agency of Canton <strong>Zurich</strong><br />
FOEN – Waste <strong>and</strong> Raw Materials Division, Switzerl<strong>and</strong><br />
Environmental Protection Agency of Canton <strong>Zurich</strong><br />
<strong>ETH</strong>-UNS <strong>Working</strong> <strong>Paper</strong> <strong>43</strong> 5
Maya Wolfensberger, Daniel J. Lang & Rol<strong>and</strong> W. Scholz<br />
Program<br />
FRIDAY, AUGUST 31, 2007<br />
Optional program (14:30): Short hiking trip <strong>and</strong> guided visit to the Kirchner Museum<br />
Reception (18:00) <strong>and</strong> Welcoming Speech (Prof. R.W. Scholz)<br />
Welcome Dinner (18:30)<br />
SATURDAY, SEPTEMBER 1, 2007<br />
Outline of the ideas <strong>and</strong> the goal of the workshop (Prof. R.W. Scholz)<br />
Introduction to the organization of the workshop (Dr. Daniel J. Lang) <strong>and</strong> introduction round<br />
Introductory Presentations: Topic A (Morning)<br />
Prof. F.W. Wellmer The “Scarcity-Problem” in the Field of Commodities<br />
Prof. A. Reller<br />
Geography of Strategic Non-Energy Minerals<br />
Introductory Presentations: Topic B (Afternoon)<br />
Prof. T. Graedel Determining the Criticality of Materials<br />
Prof. R. Kirchain The Role of Materials in Sustainable Mobility<br />
Prof. J. Isaacs<br />
Scarcity Issues Associated with Nanoscale Electronics<br />
SUNDAY, SEPTEMBER 2, 2007<br />
Introductory Presentations: Topic C (Morning)<br />
Prof. J.E. Tilton Sustainable Coping Strategies, Part A<br />
Prof. C.T. Hendrickson Sustainable Coping Strategies, Part B<br />
Introductory Presentations: Topic D (Afternoon)<br />
Dr. J.H. DeYoung Jr. Content, Updating, <strong>and</strong> Critical Points of the Red List<br />
Juerg Gerber<br />
The Red List from a Business Perspective<br />
Inhee Chung<br />
Aspects in Reference to the Scientific Panel for Sustainable Resource<br />
Management<br />
6 March 2008
(Re-) Structuring the field of Non-Energy Mineral Resource Scarcity<br />
Summary of the Workshop Discussions<br />
In the following, the main messages of the workshop discussions are briefly summarized.<br />
The topics discussed evoked many different opinions. After each section, the general conclusions<br />
are indicated by either one of the two following symbols:<br />
Indicating<br />
consensuses<br />
Indicating<br />
dissenting views<br />
Consensuses have been inferred, but they may not entirely reflect the opinion of<br />
all experts. Therefore, they only indicate that there seemed to be a main tendency<br />
toward agreement.<br />
The dissenting views may either reflect an expert’s opinion that was not advanced<br />
by others or different points of view considering a certain issue. In the latter case,<br />
the dissenting views mentioned are sequentially named.<br />
Topic A: The Role of Scarcity in Society<br />
What is meant by scarcity <strong>and</strong> what role does it play in society?<br />
<br />
<br />
Debating about resource scarcity requires initially defining what is actually meant by<br />
“scarcity”. Resource analysts attribute different meanings to the term. Absolute scarcity (also<br />
called physical scarcity) happens when satisfaction of an elementary need is no longer possible<br />
<strong>and</strong> cannot be met by additional production (Baumgartner, Becker, Faber, & Manstetten, 2006),<br />
while relative scarcity (also called economic scarcity) refers to a shortage of supply relative to<br />
the mineral’s dem<strong>and</strong> (adapted from DeYoung et al., 1987, p. 517). Brooks (1966, pp. 22-24) attributed<br />
the term scarcity to what is referred to as economic scarcity <strong>and</strong> the term rarity to what is<br />
referred to as physical scarcity. Baumgartner et al. (2006) proposed that discussion of these<br />
terms is important as the distinction between both types of scarcity has immediate implications<br />
for the distinction between what has been called ‘weak’ <strong>and</strong> ‘strong’ sustainability (see<br />
Glossary). During the workshop, there was general agreement that absolute or physical scarcity<br />
is too narrow as a concept because the availability of mineral raw materials is constantly<br />
influenced by societal, technological <strong>and</strong> economic development, besides geologic abundance.<br />
It is inappropriate to talk only about absolute scarcity as this concept fails to take into account<br />
the dynamics of society, technology, <strong>and</strong> economics.<br />
Prof. Wellmer introduced the feedback control system which proposes that higher prices<br />
will give incentives to offset emerging scarcities through technological improvements (more<br />
efficient products or substitutes) or the discovery of new reserves (see Glossary). He argued that<br />
as long as this feedback control system works efficiently <strong>and</strong> effectively, scarcity would not be<br />
an issue of concern to human welfare. By <strong>and</strong> large, the experts have agreed with the feedback<br />
control system, but no consensus was found on the time frame within which this system would<br />
work in the future.<br />
In the next 20 years, if prices of mineral commodities rise, scarcities of raw materials will be<br />
offset through technological improvements by (i) substitution, (ii) recycling, <strong>and</strong> (iii) the finding<br />
of new reserves. Within this time frame, scarcity will act as a trigger for technology improvements<br />
<strong>and</strong> product development.<br />
<strong>ETH</strong>-UNS <strong>Working</strong> <strong>Paper</strong> <strong>43</strong> 7
Maya Wolfensberger, Daniel J. Lang & Rol<strong>and</strong> W. Scholz<br />
The disagreement with respect to the time frame was mostly rooted in different assumptions<br />
on the question whether the limitedness of resources (see Glossary) will constrain<br />
economic growth. To the resource optimists, resources are unlikely to exercise significant constraints<br />
over human action, as rises in extraction costs would induce an array of scarcityoffsetting<br />
activities such as new cost-saving technologies, more efficient products, the substitution<br />
with less costly <strong>and</strong> more abundant resources, recycling <strong>and</strong> the discovery of new deposits<br />
(Tilton, 1996). The resource base (see Glossary) is seen as practically unlimited source of mineral<br />
raw materials. The numbers suggested by the resource base would thus prove that society<br />
has more pressing problems than the mineral depletion, because some estimates would last<br />
for millions of years (Tilton, 2003, pp. 23, table 3-2). Limits to growth due to resource constraints<br />
would thus be a non-problem. Early authors defending this view are Stiglitz (1974), Dasgupta &<br />
Heal (1974) or Solow (1974a, 1974b), for instance.<br />
Resource pessimists in turn, assume that incessant extraction of primary deposits will<br />
eventually exhaust deposits. Hence, they assume that the geologic limits will sooner or later<br />
exercise constraints on human action. Concerns about absolute scarcity have been expressed<br />
by Barnett <strong>and</strong> Morse (1963), Meadows et al. (1971) or Daly (1977), for instance. They tend to stick<br />
to the numbers suggested by the reserves <strong>and</strong> the reserve base (see Glossary), which are considerably<br />
lower than those suggested by the resource base.<br />
According to Prof. Tilton’s work (1996, 2003) the outlined debate is based on two different<br />
paradigms: the “fixed stock paradigm” (defended by resource pessimists) <strong>and</strong> the “opportunity<br />
cost paradigm” (defended by resource optimists).<br />
The incessant extraction of primary deposits will eventually exhaust them. Thus, the geologic<br />
limits will sooner or later exercise constraints on human action.<br />
Resources are unlikely to exercise significant constraints over human action, as rises in<br />
extraction costs would eventually induce an array of offsetting activities.<br />
Which role scarcity finally plays in society depends on many assumptions <strong>and</strong> the time<br />
frames considered. Whether we should think in years, decades, centuries or even millennia was<br />
a focus of interest. The uncertainties lying ahead might require a departure from thinking in<br />
short time frames, but the longer-term context of these issues should not be neglected.<br />
<br />
Mineral raw material scarcity <strong>and</strong> material cycles are often related to north-south conflicts.<br />
Prof. Reller illustrated the contexts revealed by the spatial <strong>and</strong> temporal trajectories of<br />
metals used in advanced technologies by taking their whole life cycle into account. He illustrated<br />
the geographical distribution of those metals of mining, consumption, <strong>and</strong> recycling,<br />
pointing out that the value-producing processes are often conducted in developed countries,<br />
while the processes associated with hazardous impacts, such as mining <strong>and</strong> disposals, often<br />
take place in developing countries. The latter are primarily used as a source <strong>and</strong> a sink of materials<br />
needed in the industrialized world.<br />
The geographical distribution of raw material processing phases matters with respect to the<br />
interaction of politics, economics, <strong>and</strong> social well-being.<br />
8 March 2008
(Re-) Structuring the field of Non-Energy Mineral Resource Scarcity<br />
The significance of the real price (see Glossary) in reflecting trends in scarcity uncovered<br />
a number of dissenting views. Some experts argued that the real price could not be a suitable<br />
indicator in some cases because external social <strong>and</strong> environmental costs were not included.<br />
Others defended it as the best indicator available despite its limitations.<br />
Real price trends are useful indicators of trends in scarcity over time even though external<br />
costs <strong>and</strong> benefits complicate their use.<br />
<br />
<br />
Apparently, a consensus was found on the significance of the reserve-to-consumption ratio<br />
(R/C ratio, defined as the reserves (see Glossary) divided by current annual consumption),<br />
also called static lifetimes. These have been criticized for failing to take into account the dynamic<br />
nature of reserves (Tilton, 1996, p. 93) <strong>and</strong> the different choices of criteria that lead to<br />
divergent resource estimates by different investigators (Gordon, et al., 2006, p. 1211). Wellmer &<br />
Becker Platen (2002, p. 730) propose that the ratio can be regarded as an indication of the need<br />
for innovation, signifying the available time buffer during which functionally equivalent substitutes<br />
must be found. In any case, the ratio could give an idea as to which mineral raw materials<br />
should be considered in view of a preventive resource management.<br />
The remaining lifetimes suggested by the R/C ratio do not provide an adequate indicator of<br />
upcoming scarcity, but they might indicate whether there is a need for innovation.<br />
The panel agreed that it is important to focus primarily on the function which can be fulfilled<br />
by a raw material’s material properties, as proposed by Wellmer & Becker-Platen (2002,<br />
p. 725). This view is apparent as other chemical elements or other materials usually replace<br />
metals used for electronic devices if they become scarce (<strong>and</strong> thus expensive).<br />
The function that is fulfilled by a mineral raw material’s material properties is a decisive<br />
criterion when addressing issues of scarcity.<br />
Scarcity might oblige society to weigh up certain functions or differing objectives. Should<br />
indium be used in thin film photovoltaics or Liquid Crystal Displays? However, the hypothesis<br />
that trade-offs between competitive applications may hinder the implementation of sustainable<br />
technologies (in this case the solar cells) was not advanced by all experts to the same extent.<br />
Trade-offs between competitive applications may hinder the implementation of sustainable<br />
technologies.<br />
There were different assumptions considering the essentiality of raw materials for specific<br />
functions. It was undisputed that phosphorus <strong>and</strong> potassium are essential in fulfilling<br />
functions of vital importance, but opinions diverged on the view that other raw materials also<br />
have essential properties <strong>and</strong> are thus irreplaceable over the long run in certain applications.<br />
Substitution is not possible for a variety of mineral raw materials in certain applications.<br />
Substitution is, as a matter of principle, feasible for all mineral raw materials (excluding the<br />
essential elements for plant growth, P <strong>and</strong> K).<br />
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<br />
A consensus was reached on the proposition that substitution must receive special attention<br />
in research <strong>and</strong> development. The time lags to implement new technologies based on<br />
alternative (more abundant) raw materials might be a critical factor inhibiting the functionality<br />
of certain services.<br />
Substitution possibilities are a key aspect to be addressed by R&D.<br />
It was proposed to differentiate among certain categories of mineral raw materials, distinguishing<br />
them by the relevant features determining the attention they should receive in<br />
terms of insecurity of supply. The following categories were differentiated: human <strong>and</strong> natural<br />
system-sensitive, technological system-sensitive, geopolitical system-sensitive, <strong>and</strong> market/economic<br />
system-sensitive. These categories are not mutually exclusive. More information<br />
about these categories <strong>and</strong> some examples can be found in Table 1 (see annex).<br />
Open Questions<br />
• What functions are vital for life or essential for technical applications? Will we be able to<br />
provide sufficient amounts of the raw materials needed to fulfill these functions?<br />
• Will sink problems (the limited capacity to absorb the hazardous impacts of material cycles<br />
for human health <strong>and</strong> the natural environment) be more urgent than source problems (limited<br />
supply of mineral raw materials)?<br />
Topic B: Causes of Scarcity<br />
What are the potential causes of scarcity in the future?<br />
Analyzing <strong>and</strong> detecting the causes of scarcity are indispensable preparatory steps before<br />
creating problem-solving strategies. Mineral raw material scarcities emerge for various<br />
reasons. In most cases, they arise from the interplay of different drivers. Supply- <strong>and</strong> dem<strong>and</strong>related<br />
drivers were distinguished <strong>and</strong> allocated to different areas (geological, technological,<br />
societal, economic, <strong>and</strong> functional). The drivers of scarcity that were mentioned in the workshop<br />
were merged <strong>and</strong> illustrated in Figure 1.<br />
They were, also grouped into different potential time frames (permanent, mid-term (25<br />
to 100 years), <strong>and</strong> short-term 0–25 years)). These times frames should indicate the potential<br />
duration of scarcity caused by the corresponding drivers.<br />
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(Re-) Structuring the field of Non-Energy Mineral Resource Scarcity<br />
Figure 1:<br />
Supply- <strong>and</strong> dem<strong>and</strong>-related drivers of scarcity<br />
The workshop placed emphasis on scarcities emerging from insufficient primary production.<br />
Nevertheless, factors inhibiting secondary production were discussed as well. It was argued<br />
that the recovery of raw materials from anthropogenic stocks is mainly restricted by their<br />
increasing statistical entropy (see Glossary), either in products or the environment. According<br />
to Prof. Reller, losses of materials due to spatial dilution into the environment <strong>and</strong> the anthroposphere<br />
occurring through societal mobilization processes are one of the biggest issues. He<br />
stressed that not only the mineral raw materials used in small amounts, but also conventional<br />
<strong>and</strong> highly available elements like zinc or titanium are subject to dissipation. Entropy reversal is<br />
in theory feasible using enough energy. However, the scarcity of energy resources reveals the<br />
irretrievability of dissipated mineral raw materials <strong>and</strong> the importance of anticipatory measures<br />
to prevent high entropy states (Rechberger & Graedel, 2002).<br />
<br />
Another problem is revealed by the unidentified outflows occurring through uncontrolled<br />
exports of residuals. A great number of used cars, for instance, are exported to regions without<br />
an appropriate recycling infrastructure or awareness, which in the end leads to great losses of<br />
many mineral raw materials.<br />
The recovery of mineral raw materials from anthropogenic stocks is limited by their high<br />
entropy states <strong>and</strong> out-of-reach disposal because of unidentified outflows.<br />
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Prof. Graedel illustrated the two dimensions that reveal the criticality of materials.<br />
These are the importance in use <strong>and</strong> availability. Illustrating these dimensions as axes reaching<br />
from high to low in a two-dimensional graph indicates the region of danger (high risk in<br />
both dimensions). Also, Prof. Graedel pointed out that there are data challenges on a variety of<br />
points <strong>and</strong> a potential temporary mismatch between the quantity supplied <strong>and</strong> quantity dem<strong>and</strong>ed<br />
of certain mineral raw materials due to a lack of highly qualified researchers <strong>and</strong><br />
skilled workers in the mining area. All experts did however not defend this. Some argued that<br />
we have enough information to quantify the mineral raw materials in deposits successfully<br />
with current knowledge. Skinner (1976) postulated a bimodal distribution of geochemical<br />
scarce metals (less than 0.1 percent of crust by weight) that are concentrated as a result of<br />
leaching, transport, <strong>and</strong> deposition by ore-forming solutions. This means that after the highgrade<br />
ores are exhausted, energy requirements for mineral production from common rocks<br />
would increase considerably. This switch from the extraction of ores to the extraction of common<br />
rocks has been named the ‘mineralogical barrier’. However, whether ores must be extrapolated<br />
by assuming the Skinner hypothesis remains unclear <strong>and</strong> disputed.<br />
<br />
Prof. Scholz stressed that resource availability by no means corresponds to resource accessibility.<br />
The differences in global capital among nations <strong>and</strong> geopolitical causes may provoke<br />
scarcity rather than mineral depletion. It has been argued that the location of deposits in a<br />
few countries <strong>and</strong> the low numbers of companies controlling the mineral commodity’s production<br />
might substantially increase the potential for geopolitically or strategically induced scarcities.<br />
Some experts countered that the likelihood of coalitions of sellers to provoke longer-term<br />
scarcities seems to be low, because more suppliers would enter the market immediately.<br />
The availability of mineral raw materials is not the most critical issue. Accessibility is more<br />
difficult to manage due to changing values in society <strong>and</strong> the uneven distribution between supply<br />
<strong>and</strong> dem<strong>and</strong> geographies <strong>and</strong> markets.<br />
The discussion about the likelihood of the network production system between potential<br />
joint products (see Glossary) <strong>and</strong> principal wanted element(s) to induce scarcities revealed a<br />
polarized field of debate. Potential joint products are by-products (see Glossary) of primary<br />
products, co-products (see Glossary) <strong>and</strong> coupled elements (see Glossary). Elements currently<br />
produced as joint products are, for instance, indium, germanium, <strong>and</strong> those PGEs or REEs, which<br />
are not produced as principal wanted elements. For the PGEs, the principal wanted elements<br />
are platinum <strong>and</strong> palladium, for the REE this is at present neodymium, formerly due to market<br />
circumstances europium, samarium, or cerium. Currently, there are no mines from which only<br />
by-products <strong>and</strong> coupled products are economically extracted; their extraction always depends<br />
on the extraction of a main product. The so-called “metal wheel” illustrates this interconnection<br />
(Reuter et al., 2005; Verhoef, Dijkema, & Reuter, 2004). As proposed by the same authors<br />
(Reuter, Verhoef, Dijkema, & Villeneuve, 2005), by reducing the capacity for the production of<br />
main products, the input <strong>and</strong> recovery capacity of the dependent potential joint products in the<br />
networked production system are removed. Also, if potential joint products experience sharp<br />
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(Re-) Structuring the field of Non-Energy Mineral Resource Scarcity<br />
increases in dem<strong>and</strong> without a relative increase in dem<strong>and</strong> of corresponding main products,<br />
there will be an insufficient supply of potential joint products. It has been proposed that the low<br />
resilience of this system could lead to a so-called “structural scarcity” (Christian Hagelücken,<br />
presentation at the workshop “Closing the material cycle” at EMPA, 12.4.2007). This opinion<br />
relies on the assumption that potential joint products cannot be produced economically as<br />
main products. However, opinions diverged on this assumption. It was argued that it would be<br />
possible to produce potential joint products as main products because high dem<strong>and</strong> (<strong>and</strong> thus a<br />
high price) would unleash efforts to do so. The fact that no exploration has been undertaken for<br />
deposits from which potential joint products can be economically produced as main products<br />
was cited as an indication for a probable solution. It was argued that, as in the case of main<br />
products, the previously postulated feedback control system would offset the scarcity of potential<br />
joint products as well, as higher prices would induce a quest for cost-reducing effects.<br />
Hence, it was not concluded whether the network production system is likely to cause longerterm<br />
scarcity if potential joint products experience sharp increases in dem<strong>and</strong> or if the capacity<br />
for production of the main products is reduced.<br />
Potential joint products cannot be produced economically as main products. Without a relative<br />
increase in production of the corresponding main products, they become “structurally scarce”.<br />
Potential joint products can be produced economically as main products. If a potential joint<br />
product must be produced as a main product, the feedback control system will regulate its<br />
production <strong>and</strong> longer-term scarcities will not occur.<br />
It was proposed that nanotechnology offers a potential for material-saving technologies<br />
due to the lower amounts of mineral raw materials required. However, nanotechnology might<br />
even increase the potential for dissipation of mineral raw materials <strong>and</strong> thus lead to a scarcity<br />
situation. It was also argued that nanotechnology would neither provoke nor ease scarcity, <strong>and</strong><br />
thus is essentially unrelated to scarcity. Prof. Isaacs showed that nanotechnology couldn’t be<br />
considered as just one technology. It should thus be discussed carefully with respect to generalization<br />
about its impacts.<br />
Nanotechnology has the potential to ease scarcity due to the reduced amounts of materials<br />
needed.<br />
Nanotechnology increases the dissipation of mineral raw materials <strong>and</strong> thus potentially causes<br />
scarcity.<br />
Nanotechnology is essentially unrelated to scarcity. It neither provokes nor eases scarcity.<br />
Prof. Kirchain presented the results of a study on the role of materials in sustainable mobility<br />
completed by his group for WBCSD. Projected global automotive materials consumption<br />
has shown that sufficient material resources are available for the production of transport vehicles<br />
over the next 50 years, given that resource dem<strong>and</strong>s from other sectors do not change<br />
dramatically. Results have shown that even with maximized recycling rates, there will be a<br />
growing need for primary material resources. This is because the projected increase in vehicle<br />
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Maya Wolfensberger, Daniel J. Lang & Rol<strong>and</strong> W. Scholz<br />
production <strong>and</strong> material dem<strong>and</strong> will outstrip the rate at which secondary material can be recycled<br />
from de-registered vehicles. Such extrapolations might be interesting with respect to<br />
emerging technologies promoted as sustainable technologies. One task of an early warning<br />
system as addressed in topic D could be to prevent emerging technologies based on insufficiently<br />
existing mineral raw materials.<br />
Open Questions<br />
• Which mineral commodities are most likely to encounter much higher production costs in<br />
the future? To what extent <strong>and</strong> how reliably can we extrapolate the future dem<strong>and</strong> of mineral<br />
raw materials?<br />
• Should we focus on those commodities currently recovered as joint products but whose<br />
consumption may increase rapidly, requiring production as main products? What will be the<br />
associated rises in costs of production?<br />
• Do we have to worry about the Skinner hypothesis, <strong>and</strong> if so, which mineral commodities<br />
are likely to be most vulnerable?<br />
• How might geopolitics affect the economic regulatory systems of dem<strong>and</strong> <strong>and</strong> supply?<br />
Topic C: Sustainable Coping Strategies<br />
What can a society committed to Sustainable Development do to alleviate scarcity?<br />
Mutually defining a sustainable strategy to confront scarcity is not easy, as resource optimists<br />
<strong>and</strong> resource pessimists rely upon different assumptions. However, the proposition of<br />
intergenerational equity provides common ground to move towards Sustainable Development.<br />
This was clear <strong>and</strong> defended by all experts, but opinions on what actually must be conserved<br />
for future generations could be grouped under the two concepts ‘weak’ <strong>and</strong> ‘strong’ sustainability.<br />
Thus, it was a matter of controversy whether we should conserve the function that a raw<br />
material fulfills <strong>and</strong> allow depletion if the raw material has a suitable substitute, or whether<br />
we should h<strong>and</strong> down a reasonable stock of mineral raw materials for future generations.<br />
We must ensure that the functions of the mineral raw materials will be fulfilled in the future.<br />
We must h<strong>and</strong> down a reasonable stock of all mineral raw materials to future generations <strong>and</strong><br />
allow them to detect new functions.<br />
Closing the materials loop is by many seen as an imperative for achieving SD. This however<br />
poses a challenge for a variety of reasons. Reusing anthropogenic stocks to a much greater<br />
extent requires installing an appropriate infrastructure for product design <strong>and</strong> recycling, avoiding<br />
dissipative losses or material losses through out-of-reach disposals. There seems to be a<br />
great need for improving life cycle thinking in business models which until now often see the<br />
primary <strong>and</strong> secondary metal’s market as a completely separate activities (Petrie, 2007). The<br />
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(Re-) Structuring the field of Non-Energy Mineral Resource Scarcity<br />
paramount need is to integrate these coping strategies into political agendas <strong>and</strong> to ensure<br />
that case-oriented strategies will be preemptively steered. As outlined by Prof Reller integrative<br />
precautionary measures are central to avoid dissipation. Approaches such as the “designing<br />
for disassembly” described by Johnson et al. (2007) are potential measures to preventively<br />
avoid the losses occurring through spatial dilution.<br />
<br />
With decreasing primary deposits of mineral raw materials, the recovery from secondary feeds<br />
such as products or l<strong>and</strong>fills will become more important. Preventive strategies to “Close the<br />
Loop” are recommended to address this situation.<br />
Problem-solving strategies were collected by mutual discussion. The Closed-Loop-<br />
System approach was analyzed, <strong>and</strong> coping strategies to achieve this system were merged <strong>and</strong><br />
are illustrated in Figure 2. The coping strategies named in the discussions were allocated to<br />
three different repositories, roughly divided into: “Lithosphere”, “in-use”, <strong>and</strong> “waste deposits”.<br />
It is assumed that the main losses occur through dissipation <strong>and</strong> out-of-reach disposal.<br />
The seven groups of coping strategies<br />
are:<br />
1. Find new deposits<br />
2. Make identified mineral resources<br />
economic to exploit<br />
3. Avoid dissipative losses 2<br />
4. Retard growth in consumption<br />
5. Increase efficiency<br />
6. Avoid out-of-reach disposals<br />
7. Encourage recycling<br />
Figure 2:<br />
Material cycle of mineral raw materials <strong>and</strong> coping strategies allocated to the three repositories<br />
“lithosphere”, in-use” <strong>and</strong> “waste deposits”.<br />
As outlined by Prof. Tilton, long-run availability of the mineral commodities can be either<br />
achieved by reducing the cost-increasing effects of mineral depletion (i.e., by altering the speed<br />
at which society extracts <strong>and</strong> uses its primary mineral resources) or by promoting the costreducing<br />
effects of new technology. Prof. Tilton stressed that new technologies have more than<br />
offset the cost-increasing effects of depletion over the past century, but that this does not<br />
guarantee that this situation will continue indefinitely in the future. He argued that most of the<br />
coping strategies applied today (e.g., more recycling, new technologies that allow the substitution<br />
of abundant resources for scarce resources, etc.) only slow the speed at which society extracts<br />
<strong>and</strong> uses primary mineral resources. Hence, such efforts slow the pace at which mineral<br />
2 The anthropogenic extent of dissipation can be quantified by means of a reference value reflecting the statistical<br />
entropy of a MRM in processes compared with the statistical entropy in the original ore. The characterization of the<br />
statistical entropy by a single metric per substance offers a useful decision support <strong>and</strong> design tool (Rechberger &<br />
Graedel, 2002).<br />
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depletion promotes scarcities, but for the most part do not reverse the tendency. What can reverse<br />
the tendency for depletion to produce scarcities are new technologies that reduce the<br />
costs of producing mineral raw materials <strong>and</strong> that allow society to extract metals from previously<br />
infeasible sources.<br />
Prof. Hendrickson also stressed the difficulties revealed by the unpredictability of future<br />
supply of mineral raw materials. He argued that companies could react over different time<br />
periods to make new investments, with profits discounted over a relatively short planning horizon.<br />
This allows estimating the amount of a mineral raw material available in the next few<br />
years. However, the shifts in dem<strong>and</strong> <strong>and</strong> supply functions over a long period of time remain<br />
difficult to predict.<br />
<br />
There are mineral raw materials whose extraction is significantly limited by other scarce<br />
resources such as energy, water, l<strong>and</strong>, or pristine ecosystems <strong>and</strong> thus may potentially induce<br />
trade-offs between these natural goods. For instance, as mining <strong>and</strong> processing of ore requires<br />
enormous amounts of water with current technologies, <strong>and</strong> much of the activity takes place in<br />
water-scarce regions, trade-offs between different uses might occur. If regulations are set up<br />
to control these interfering uses, scarcity might emerge in spite of sufficient resources remaining<br />
in the ground. It has been argued that the low practicability of environmental regulations in<br />
developing countries permitted the continuous supply of low-cost mineral raw materials in the<br />
past. Should these circumstances change, which is certainly desirable from a socio-political<br />
point of view, production costs of mineral raw materials might increase considerably. Pressure<br />
from industrialized nations to keep the prices low might however extend the point in time<br />
when this will happen. Hence, there are trade-offs between the security of supply <strong>and</strong> social or<br />
environmental issues. As outlined by Prof. Hendrickson, a paramount policy issue in coping with<br />
scarcity is the extent to which market intervention may be desirable for purposes such as preventing<br />
disruptions of supply or improving inter- <strong>and</strong> intragenerational equity.<br />
Solutions to scarcity entail a certain trade-off between security of supply <strong>and</strong> intra-<strong>and</strong><br />
intergenerational issues. Public policy plays a key role in undertaking the socially optimal action.<br />
Open Questions<br />
• What should public policy undertake to cope with potential scarcity caused by mineral depletion,<br />
<strong>and</strong> to what extent should it try to alter the behavior of markets?<br />
• What are the trade-offs between the two coping options (i.e., the conservation of the function<br />
vs. the conservation of the mineral stocks for the next generation)? What are the relative<br />
roles of public policy <strong>and</strong> the marketplace in determining how these trade-offs will be<br />
effected?<br />
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(Re-) Structuring the field of Non-Energy Mineral Resource Scarcity<br />
Topic D: The »Red List of Scarce Raw Materials«<br />
Would a Red List be a suitable instrument to prevent or h<strong>and</strong>le scarcities sustainably?<br />
The term “Red List” was adopted from the official “Red List of Threatened Species” designed<br />
to determine the relative risk of species extinction (IUCN, 2006). The »Red List of Scarce<br />
Raw Materials« was proposed to serve as an early warning system, encouraging proactive action<br />
according to the precautionary principle by helping to anticipate, <strong>and</strong> thus avoid, scarcities<br />
that could endanger human welfare. The surveys in the run-up to the workshop already revealed<br />
that the idea of the »Red List of Scarce Raw Materials« met with different opinions as to<br />
its significance. Some experts thought that it is rather irrelevant <strong>and</strong> even has the potential to<br />
negatively affect the market. Others thought it could be a useful instrument for policy makers<br />
or product designers <strong>and</strong> that it could steer research <strong>and</strong> pre-emptive actions of industry in the<br />
right direction. As a result of discussion during the workshop, more ideas <strong>and</strong> suggestions were<br />
integrated in the initial idea. The panel concluded that more aspects in addition to mere physical<br />
scarcity must be considered in such an early warning system.<br />
A “Green List” or ”Scenario-Based Preventive Resource Management“ was proposed to<br />
replace the “old” idea of the Red List by including the new approaches dealt with in the last topics.<br />
Resources whose availability <strong>and</strong> accessibility is of concern in the realms of environment,<br />
society <strong>and</strong> economy should be the focus of interest, not necessarily those which are claimed to<br />
be exhausted soon. The basic approach is to address crucial questions from the viewpoint of<br />
the “Scenario-based Preventive Resource Management“, considering the following key issues:<br />
Relevant functions in natural <strong>and</strong> human systems<br />
The relevant functions fulfilled by a mineral’s material properties in natural <strong>and</strong> human<br />
systems are a decisive criterion to be considered.<br />
• What are the material properties needed to ensure the provision of the relevant functions<br />
in the future?<br />
Trends of dem<strong>and</strong><br />
The trends of dem<strong>and</strong> of relevant technologies must be kept in view in order to anticipate<br />
erroneous developments. Short-term <strong>and</strong> long-term trends must be equally considered on<br />
the basis of different scenarios.<br />
• Which emerging technologies based on critical mineral raw materials might experience a<br />
considerable increase in dem<strong>and</strong> in the near-term <strong>and</strong> long-term future?<br />
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Eco-political criteria<br />
As has been demonstrated, environmental regulations might induce scarcity. A social optimum<br />
between security of supply <strong>and</strong> intra-<strong>and</strong> intergenerational issues must be aspired.<br />
• What are the negative side effects for environment <strong>and</strong> social issues? Is the usage of these<br />
materials environmentally <strong>and</strong> socially justifiable? How can those negative side effects be<br />
preemptively recognized <strong>and</strong> avoided?<br />
• If more than one material can fulfill the defined functions, which has the least negative<br />
environmental, social, economic, <strong>and</strong> political consequences?<br />
Geopolitical criteria<br />
Geopolitics has the potential to induce scarcity. The country <strong>and</strong> company concentration<br />
(see Glossary) of mineral commodities <strong>and</strong> other critical factors should be observed <strong>and</strong> registered<br />
as a precautionary measure.<br />
• Is or will there be a high country or company concentration respectively of the mineral raw<br />
materials in focus?<br />
• Will mineral raw materials be available <strong>and</strong> accessible in the required amounts <strong>and</strong> from<br />
reliable sources?<br />
Such a tool entails several crucial challenges due to existing uncertainties. It is unsure<br />
how far we are capable of predicting the future course of research <strong>and</strong> technology. As pointed<br />
out by Dr. DeYoung, the updates <strong>and</strong> maintenance of such a list are likely to take as much effort<br />
as the initial set-up. Monitoring seems to be the most crucial <strong>and</strong> critical issue at the same<br />
time. Dr. DeYoung presented a list of attributes for measuring a mineral commodity’s criticality<br />
that was used for planning purposes for the upcoming USGS national mineral resource assessment,<br />
with measures <strong>and</strong> criteria for each mineral commodity.<br />
Many experts stressed the environmental concerns associated with resource management.<br />
It remained unclear which indicators could be used in considering them <strong>and</strong> how an environmental<br />
impact (of mining, for instance) should become allocated to a certain mineral commodity.<br />
It was also discussed on what level (organizational, national, or international) such an<br />
early warning system would be most usefully implemented. An international level would require<br />
involving many stakeholders <strong>and</strong> ensuring that value judgments do not influence the results.<br />
It was argued that it might be more effective to complete several lists for each nation<br />
(national) or even for each industrial sector (organizational). However, in the latter two cases,<br />
there might be many conflicting interests competing with each other, so the usefulness of the<br />
venture might be compromised. The implementation of a list offers advantages <strong>and</strong> disadvantages<br />
for each level considered. The experts agreed that the implementation of such an in-<br />
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(Re-) Structuring the field of Non-Energy Mineral Resource Scarcity<br />
strument as the ”Scenario-Based Preventive Resource Management“, on any level, would require<br />
a multi-stakeholder approach. In order to ensure its implementation, the relevant industry<br />
<strong>and</strong> science stakeholders need to be asked to participate <strong>and</strong> provide information in a corresponding<br />
network.<br />
Mr. Gerber illustrated the role of raw materials from a business perspective. He stressed<br />
the significance of a systematic application of life cycle thinking in modern business practice to<br />
provide society with more sustainable goods <strong>and</strong> services by managing the total life cycle of an<br />
organization’s product portfolio. He proposed working more on the basis of scenarios <strong>and</strong> emphasized<br />
that for this purpose, stakeholder management is needed, as forecasts would not be<br />
good enough for the topics addressed. He pointed out that we should have an idea today of<br />
what a sustainable product will look like in 2050 because of the long investment cycles for base<br />
industries <strong>and</strong> lead times in R&D.<br />
Ms. Chung presented the idea of the Scientific Panel on Sustainable Resource Management<br />
whose aim is to provide independent scientific advice to national governments <strong>and</strong> relevant<br />
international organizations on use intensity, security of supplies <strong>and</strong> the environmental<br />
impacts of selected products <strong>and</strong> services on a global level. Furthermore, it should support the<br />
enhancement of scientific knowledge, <strong>and</strong> capacity building in developing countries <strong>and</strong> furthermore<br />
contribute to sustainable consumption <strong>and</strong> production. Ms. Chung’s presentation<br />
showed that many of the concerns addressed are in the focus of international organizations<br />
such as UNEP. After the workshop, the Scientific Panel was actually launched in November<br />
2007. More information on the panel can be found at http://www.unep.fr/pc/sustain/initiati<br />
ves/resourcepanel/.<br />
The two-dimensional graph presented by Prof. Graedel <strong>and</strong> described in a recent release<br />
of the Committee on Critical Mineral Impacts of the U.S. Economy, Committee on Earth Resources<br />
<strong>and</strong> the National Research Council (2008) provides significant information for deciding<br />
on a mineral’s criticality <strong>and</strong> is a suitable baseline for the pre-selection of minerals that ought<br />
to receive special attention in a Preventive Resource Management. During the workshop, critical<br />
raw materials potentially falling under that category were listed in a first draft (Table 2, see<br />
annex). The table gives information about the mineral raw materials that were named in the<br />
discussion <strong>and</strong> is to be seen as a first, incomplete collection.<br />
Open Questions<br />
• How do we know if the materials required today to fulfill society’s needs, will continue to<br />
be required in the future?<br />
• How can appropriate consideration be given to environmental <strong>and</strong> social concerns?<br />
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Summary<br />
The ambitious two-day workshop “Scarce Raw Materials” with leading international experts<br />
in the relevant areas was set up in order to analyze potential future risks emerging from<br />
resource scarcity. An appropriate way to build an early warning system was envisioned. The<br />
latter system should facilitate an anticipatory <strong>and</strong> preventive (sustainable) resource management<br />
which helps avoid unexpected scarcities that have the potential to endanger human welfare<br />
by indicating priorities of actions with respect to R&D, policy making, or lifestyle changes.<br />
The workshop process included an in-depth preparation <strong>and</strong> post-processing phase which was<br />
carried out in collaboration with the workshop participants. The experts were chosen based on<br />
their outst<strong>and</strong>ing expertise in the fields of resource management, resource economy, geology,<br />
<strong>and</strong> material sciences.<br />
The workshop was structured in four topic areas. Each half-day was dedicated tone of the<br />
four topics respectively. Some crucial outcomes of the workshop with respect to each topic are<br />
briefly summarized below:<br />
Topic A: The Role of Scarcity in Society<br />
In many cases, scarcity is not permanent but rather constantly influenced by societal,<br />
technological, <strong>and</strong> economic developments. The feedback control system proposes that scarcity<br />
acts as a trigger for technology improvements <strong>and</strong> product development. The system indicates<br />
that higher prices provide incentives to offset emerging scarcities through technological<br />
improvements. The panel did not agree on the time frame of its validity (years, decades, centuries<br />
or even millennia). The disagreement was rooted in the different assumptions considering<br />
the questions whether the limitedness of resources will exercise constraints on human action<br />
<strong>and</strong> the extent to which it will be possible to explore the resource base. This debate is led by<br />
two camps; “resource pessimists” following the “fixed stock paradigm” <strong>and</strong> “resource optimists”<br />
arguing according to the “opportunity cost paradigm” (Tilton, 1996, 2003; Tilton & Lagos,<br />
2007). Further disagreements involved the essentiality of mineral raw materials. All experts<br />
agreed that phosphorus <strong>and</strong> potassium are considered essential, but no agreement was<br />
achieved on whether further mineral raw materials are irreplaceable in certain technical applications.<br />
Different categories of mineral raw materials were perceived. The categories distinguish<br />
the mineral raw materials according to relevant features that determine the attention<br />
they should receive when insecurity of supply is analyzed. The following categories were distinguished:<br />
Human <strong>and</strong> natural system-sensitive, technological system-sensitive, geopolitical<br />
system-sensitive <strong>and</strong> market/ economic system-sensitive (see further information in Table 1 in<br />
the annex).<br />
20 March 2008
(Re-) Structuring the field of Non-Energy Mineral Resource Scarcity<br />
Topic B: The Causes of Scarcity<br />
Potential drivers of scarcity were identified. By <strong>and</strong> large, experts agreed that counterproductive<br />
geopolitics, dissipation, high statistical entropy states in products, or societal barriers<br />
will presumably be equally or even more decisive in producing scarcities than the depletion<br />
of primary deposits. The role of nanotechnology was perceived differently. Some considered<br />
that it would ease scarcity; others that it would increase scarcity due to dissipation <strong>and</strong> the<br />
potential dependence on scarce mineral raw materials, <strong>and</strong> still others argued that it is unrelated<br />
to scarcity.<br />
The likelihood of so-called “structural scarcities” of potential joint products was discussed.<br />
Whether the potential joint products are likely to suffer from long-term scarcity under<br />
sharp increases in dem<strong>and</strong> was assessed differently.<br />
A very critical issue seems to be the irreversible loss of materials through dissipation,<br />
which is still increasing in a variety of applications. Dissipative flows into the environment finally<br />
inhibit a closed loop system <strong>and</strong> thus sustainable action.<br />
Topic C: Sustainable Coping Strategies<br />
It was evident that coping strategies to alleviate scarcity may force trade-offs between<br />
the security of supply <strong>and</strong> intra- <strong>and</strong> intergenerational equity issues. It was argued that more<br />
efforts to should be made to “Close the Loop”. The key role of public policy in fostering “life cycle<br />
thinking” was stressed.<br />
The hazardous impacts on the environment <strong>and</strong> human health associated with production,<br />
recovery, <strong>and</strong> disposal, are rather alarming <strong>and</strong> could further increase in case of scarcity.<br />
The fact that the processing phases involved mainly take place in developing countries is a<br />
paramount policy issue of intragenerational equity.<br />
Topic D: The »Red List of Scarce Raw Materials«<br />
The idea of the Red List was replaced by a more dynamic approach considering new aspects.<br />
Rather than only scarcity, other risks in supply security should be considered as well. It<br />
emphasized that system dynamics, the significance of a raw material’s function, <strong>and</strong> environmental<br />
as well as social criteria should become integrated. Such a “Scenario-based Preventive<br />
Resource Management” would have to be set up in a challenging multi-stakeholder process<br />
with critical issues to be considered. It was not concluded on what level (organizational, national,<br />
or international) it would be most effective. Also, maintenance <strong>and</strong> updating were identified<br />
as complex challenges. The “Scenario-based Preventive Resource Management” must be<br />
promoted by implementing a national or international resource network to exchange data <strong>and</strong><br />
increase data security. The involvement of the relevant stakeholders of industry <strong>and</strong> science is<br />
a key aspect in establishing such an early warning system.<br />
<strong>ETH</strong>-UNS <strong>Working</strong> <strong>Paper</strong> <strong>43</strong> 21
Maya Wolfensberger, Daniel J. Lang & Rol<strong>and</strong> W. Scholz<br />
Concluding Remarks<br />
Neither the fixed stock paradigm postulated by the resource pessimists, nor the opportunity<br />
cost paradigm defended by the resource optimists alone seems to fulfill the overall requirements<br />
for a future-oriented policy of sustainable management of mineral raw materials.<br />
The goal of going beyond these paradigms to the idea of a preventive anticipatory resource<br />
management is a major challenge. However, integrating key aspects of both paradigms might<br />
provide a basis for eliciting a common strategy for the formulation of the desired early warning<br />
system.<br />
Today’s resource use <strong>and</strong> management have long-term impacts for future political, social,<br />
<strong>and</strong> economic systems. Comparing the current rather short-term oriented comprehension<br />
<strong>and</strong> partly sketchy information about resource availability <strong>and</strong> accessibility with the longlasting<br />
effects of today’s resource management reveals telling discrepancies.<br />
Upcoming publications will address <strong>and</strong> further evolve case-oriented approaches to sustainably<br />
plan <strong>and</strong> steer the future use of mineral raw materials. The network of people created<br />
during the workshop sets the stage for pursuing the goal of further projects <strong>and</strong> cooperation<br />
between the institutions involved in the challenging <strong>and</strong> societal relevant field of mineral raw<br />
material scarcity.<br />
References<br />
Andersson, B. A. (2001). Material Constraints on Technology Evolution: The Case of Scarce Metals<br />
<strong>and</strong> Emerging Energy Technologies,. Chalmers University of Technology <strong>and</strong> Göteborg<br />
University, Göteborg, Sweden.<br />
Ayres, R. U. (1997). Metals recycling: economic <strong>and</strong> environmental implications. Resources, Conservation<br />
<strong>and</strong> Recycling, 21(3), 145-173.<br />
Barnett, H. J., & Morse, C. (1963). Scarcity <strong>and</strong> growth the economics of natural resource availability.<br />
Baltimore: Resources for the future; Johns Hopkins Press.<br />
Baumgartner, S., Becker, C., Faber, M., & Manstetten, R. (2006). Relative <strong>and</strong> absolute scarcity of<br />
nature. Assessing the roles of economics <strong>and</strong> ecology for biodiversity conservation. Ecological<br />
Economics, 59(4), 487-498.<br />
Brooks, D. B. (1966). Supply <strong>and</strong> Competition in Minor Metals. Baltimore, MD: Resources for the<br />
Future Press.<br />
Brooks, D. B. (1976). Mineral supply as a stock, chapter 2.5A. In W. A. Vogely (Ed.), Economics of the<br />
mineral industries, 3rd ed. (pp. 127-207). New York: American Institute of Mining, Metallurgical,<br />
<strong>and</strong> Petroleum Engineers.<br />
Committee on Critical Mineral Impacts of the U.S. Economy, Committee on Earth Resources, &<br />
National Research Council. (2007). Minerals, Critical Minerals, <strong>and</strong> the U.S. Economy.<br />
Daly, H. E. (1977). Steady-State Economics. San Francisco: W.H. Freeman <strong>and</strong> Company.<br />
Daly, H. E. (1994). Operationalizing sustainable development by investing in natural capital. In A.<br />
Jannsson, H. Hammer, C. Folke & R. Costanza (Eds.), Investing in <strong>Natural</strong> Capital: The Ecological<br />
Economics Approach to Sustainability (pp. 21-37). Washington, DC: Isl<strong>and</strong> Press.<br />
Dasgupta, P., & Heal, G. (1974). Optimal Depletion of Exhaustible Resources. Review of Economic<br />
Studies, 3-28.<br />
DeYoung, J. H., Jr., Barton, P. B., Boulege, J., Dahmen, P., Gocht, W. R. A., Kürsten, M. O. C., et al.<br />
(1987). Assessment of Non-energy Mineral Resources- Group Report. In D. J. McLaren &<br />
B. J. Skinner (Eds.), In: Resources <strong>and</strong> world development report of the Dahlem Workshop<br />
on Resources <strong>and</strong> World Development (pp. 509-523). Chichester: Wiley.<br />
22 March 2008
(Re-) Structuring the field of Non-Energy Mineral Resource Scarcity<br />
DeYoung Jr., J. H., Sutphin, D. M., & Cannon, W. F. (1984). International Strategic Minerals Inventory<br />
summary report—Manganese. U.S. Geological Survey Circular 930-A, 22.<br />
Gordon, R. B., Bertram, M., & Graedel, T. E. (2006). Metal stocks <strong>and</strong> sustainability. Proceedings of<br />
the National Academy of <strong>Science</strong>s of the United States of America, 103(5), 1209-1214.<br />
Hartwick, J. M. (1977). Intergenerational Equity <strong>and</strong> the Investment of Rents from Exhaustible<br />
Resources. American Economic Review, 67, pp. 972-974.<br />
IUCN. (2006). Red List of threatened species. from http://www.iucnredlist.org/:<br />
Johnson, J., Harper, E. M., Lifset, R., & Graedel, T. E. (2007). Dining at the Periodic Table: Metals<br />
Concentrations as They Relate to Recycling. Environ. Sci. Technol., 41(5), 1759-1765.<br />
Klee, R. J., & Graedel, T. E. (2004). Elemental cycles: A status report on human or natural dominance.<br />
Annual Review of Environment <strong>and</strong> Resources, 29, 69-107.<br />
Meadows, D. H., Meadows, D. L., R<strong>and</strong>ers, J., & Behrens, W. W. (1971). The Limits to growth. New<br />
York: Universe Books.<br />
National Research Council. (2008). Minerals, Critical Minerals, <strong>and</strong> the U.S. Economy. Washington,<br />
DC: The National Academic Press.<br />
Petrie, J. (2007). New models of sustainability for the resources sector - A focus on minerals <strong>and</strong><br />
metals. Process Safety <strong>and</strong> Environmental Protection, 85(B1), 88-98.<br />
Rechberger, H., & Graedel, T. E. (2002). The contemporary European copper cycle: statistical<br />
entropy analysis. Ecological Economics, 42(1-2), 59-72.<br />
Reuter, M. A., Heiskanen, K., Boin, U., Van Schaik, A., Verhoef, E. V., Yang, Y., et al. (2005). The metrics<br />
of material <strong>and</strong> metal ecology harmonizing the resource, technology <strong>and</strong> environmental<br />
cycles. Amsterdam: Elsevier.<br />
Reuter, M. A., Verhoef, E., Dijkema, G. P. J., & Villeneuve, J. (2005). Life cycle assessment (LCA) for<br />
the metals cycle in the context of waste policy. Géosciences, numéro 1.<br />
Scherer, F. M. ( 1970). Industrial Market Structure <strong>and</strong> Economic Performance. Chicago, IL: R<strong>and</strong><br />
McNally College Publishing Co.<br />
Skinner, B. J. (1976). Second iron age ahead? American Scientist, 64(3), 258-269.<br />
Solow, R. M. (1974a). The economics of resources or the resources of economics. American Economic<br />
Review, 64, 1-14.<br />
Solow, R. M. (1974b). Intergenerational equity <strong>and</strong> exhaustible resources. [Symposium]. Review<br />
of Economic Studies, 29-46.<br />
Solow, R. M. (1992). An almost practical step towards sustainability. Washington DC: Resources<br />
for the Future.<br />
Stiglitz, J. (1974). Growth with exhaustible natural resources: efficient <strong>and</strong> optimal growth<br />
paths. [Symposium]. Review of Economic Studies, 123-137.<br />
Tilton, J. E. (1996). Exhaustible resources <strong>and</strong> sustainable development: Two different paradigms.<br />
Resources Policy, 22(1-2), 91-97.<br />
Tilton, J. E. (2003). On borrowed time? Assessing the Threat of Mineral Depletion. Washington DC:<br />
Resources for the Future.<br />
Tilton, J. E., & Lagos, G. (2007). Assessing the long-run availability of copper. Resources Policy,<br />
32(1-2), 19-23.<br />
USGS, & U.S. Bureau of Mines. (1980). Principles of a Resource/Reserve Classification for Minerals<br />
(U.S. Geological Survey Circular 831).<br />
Verhoef, E. V., Dijkema, G. P. J., & Reuter, M. A. (2004). Process Knowledge, System Dynamics,<br />
<strong>and</strong> Metal Ecology. Journal of Industrial Ecology, 8(1-2), 23-<strong>43</strong>.<br />
Wäger, P., & Classen, M. (2006). Metal availability <strong>and</strong> supply: the many facets of scarcity. Proceedings<br />
of MMME’06. <strong>Paper</strong> presented at the 1st International Symposium on Material,<br />
Minerals &Metal Ecology (MMME 06), November 14-15, Cape Town, South Africa.<br />
Wellmer, F.-W., & Becker-Platen, J. D. (2002). Sustainable development <strong>and</strong> the exploitation of<br />
mineral <strong>and</strong> energy resources: a review. International Journal of Earth <strong>Science</strong>s, 91(5),<br />
723-745.<br />
Wellmer, F.-W., Hannak, W., Krauß, U., & Thormann, A. (1989). Deposits of Rare Metals. In M. Kürsten<br />
(Ed.), 5th International Symposium on Mineral Resources: Raw Materials for New<br />
Technologies, (pp. 71-122). Hannover, 19.-21. Oct. 1988: Stuttgart (Schweizerbart).<br />
<strong>ETH</strong>-UNS <strong>Working</strong> <strong>Paper</strong> <strong>43</strong> 23
Maya Wolfensberger, Daniel J. Lang & Rol<strong>and</strong> W. Scholz<br />
Glossary<br />
By-products<br />
Company concentration<br />
Co-product<br />
Country concentration<br />
Coupled elements<br />
Resource base<br />
By-products are elements that can be produced from concentrates<br />
or slags of principal wanted elements due to market circumstances<br />
(like indium or germanium from zinc concentrates).<br />
Prof. Wellmer (personal communication, January 14, 2008) <strong>and</strong><br />
Dr. DeYoung (personal communication, February 3, 2008).<br />
The distribution of production of a mineral commodity within an<br />
industry, which can be measured by a company concentration ratio<br />
(or industry concentration ratio) showing the percentage of<br />
total production (physical output or value) contributed by the<br />
largest few firms, ranked in order of shares of production. Related<br />
to the concept of market concentration, which concerns the<br />
distribution of sales within a market, as opposed to the distribution<br />
of production within an industry. (Scherer, 1970, pp. 50-57)<br />
Co-products are elements that must be produced together from<br />
a mineral deposit because market circumstances require the<br />
revenue from all of the co-products in order to be profitable Dr.<br />
DeYoung (personal communication, February 3, 2008).<br />
The global distribution of production of a mineral commodity<br />
among producing countries, which can be measured by a country<br />
concentration ratio, showing the percentage of total production<br />
(physical output or value) contributed by the largest few countries,<br />
ranked in order of shares of production. (Adapted from the<br />
concepts of market concentration <strong>and</strong> industry concentration,<br />
DeYoung Jr., Sutphin, & Cannon, 1984, pp. 8-9, 11)<br />
Coupled elements are such elements that must be produced at<br />
the same time as a principal wanted element, at least to the intermediate<br />
product stage, regardless of market circumstances<br />
because the elements are chemically very similar <strong>and</strong> occur together<br />
in ore deposits (like rare-earth elements in REE deposits<br />
or platinum, palladium, <strong>and</strong> other platinum-group elements in<br />
PGE deposits). Adopted from Wellmer et al. (1989) <strong>and</strong> amended<br />
by Dr. DeYoung (personal communication, February 3, 2008).<br />
An approach to the universe of resource availability in which<br />
technologic <strong>and</strong> economic limitations are largely ignored. Geologic<br />
limitations derive from natural abundance <strong>and</strong> are not ignored,<br />
for they are the essence of the resource base.” The resource<br />
base encompasses all of a given material (e.g., copper)<br />
within some portion of the earth’s crust. (D.B. Brooks, 1976, pp.<br />
148-149, 152-158)<br />
24 March 2008
(Re-) Structuring the field of Non-Energy Mineral Resource Scarcity<br />
PGEs<br />
Potential joint products<br />
Real price<br />
REEs<br />
Reserve base<br />
Reserves<br />
Resources<br />
Statistical entropy<br />
Strong sustainability<br />
Weak sustainability<br />
Platinum Group Elements include iridium, osmium, palladium,<br />
platinum, rhodium, <strong>and</strong> ruthenium.<br />
Potential joint products include potential by-products (of primary<br />
products), co-products, <strong>and</strong> coupled elements. They either can or<br />
must be produced when producing the principal wanted element(s).<br />
Prof. Wellmer (personal communication, January 14,<br />
2008) <strong>and</strong> Dr. DeYoung (personal communication, February 3,<br />
2008)<br />
Price of a commodity that has been adjusted for inflation (Tilton,<br />
2003, p. 141).<br />
The Rare Earth Elements include the element lanthanum (La) <strong>and</strong><br />
the fourteen elements that follow La in the periodic table (Lanthanides).<br />
“That part of an identified resource that meets specified minimum<br />
physical <strong>and</strong> chemical criteria related to current mining<br />
<strong>and</strong> production practices, including those for grade, quality, thickness,<br />
<strong>and</strong> depth. The reserve base is the in-place demonstrated<br />
(measured plus indicated) resource from which reserves are estimated.”<br />
(USGS & U.S. Bureau of Mines, 1980, p. 5)<br />
“That part of the reserve base which could be economically extracted<br />
or produced at the time of determination. The term reserves<br />
need not signify that extraction facilities are in place <strong>and</strong><br />
operative.” (USGS & U.S. Bureau of Mines, 1980, p. 5)<br />
“A concentration of naturally occurring solid, liquid, or gaseous<br />
material in or on the earth’s crust in such form <strong>and</strong> amount that<br />
economic extraction of a commodity from the concentration is<br />
currently or potentially feasible.” (USGS & U.S. Bureau of Mines,<br />
1980, p. 5)<br />
Entropy is a measure of the disorder or r<strong>and</strong>omness in a closed<br />
system. Statistical entropy is used to measure the variance of a<br />
probability distribution (Rechberger & Graedel, 2002).<br />
Strong sustainability, as supported by Daly (1994) claims that<br />
natural capital <strong>and</strong> man-made capital are only complementary<br />
at best. In order for Sustainable Development to be achieved,<br />
natural capital has to be kept constant independently from manmade<br />
capital.<br />
The use of natural resources is consistent with weak sustainability<br />
so long as the diminishing natural capital is being substituted<br />
by gains through human capital (e.g., buildings) (Hartwick, 1977;<br />
Solow, 1992).<br />
<strong>ETH</strong>-UNS <strong>Working</strong> <strong>Paper</strong> <strong>43</strong> 25
Maya Wolfensberger, Daniel J. Lang & Rol<strong>and</strong> W. Scholz<br />
Table 1:<br />
Annex<br />
Proposed categories of mineral raw materials<br />
Category Explanation Examples<br />
Human <strong>and</strong> natural<br />
system-sensitive<br />
Technological<br />
system-sensitive<br />
Geopolitical systemsensitive<br />
Market-/ economic systemsensitive<br />
Mineral raw materials that are essential for vital<br />
functions. Their scarcity represents a threat for<br />
human beings.<br />
Mineral raw materials whose extraction is<br />
significantly limited by other scarce<br />
environmental goods such as energy, water, l<strong>and</strong>,<br />
or pristine ecosystems. Scarcities might emerge<br />
from these trade-offs between environmental<br />
goods.<br />
Mineral raw materials used for emerging<br />
technologies with global potential of widespread<br />
market diffusion.<br />
Mineral raw materials that are essential for<br />
technical applications. Suitable substitutes might<br />
be found but currently no alternative solutions<br />
are on h<strong>and</strong>.<br />
Mineral raw materials produced in only a few<br />
countries or extracted by only a few companies<br />
may have a higher risk of seller coalitions<br />
increasing market prices.<br />
Which elements are considered to be<br />
geopolitically critical depends finally on the<br />
strategic purposes of the nation <strong>and</strong> their import<br />
dependence.<br />
The thorough market penetration of many<br />
products relying on the supply of certain bulk<br />
mineral raw materials might lead to severe<br />
impacts on market structures if the accessibility of<br />
the materials changes temporarily. Furthermore,<br />
the supply of these materials might respond<br />
sensitively to economic interventions. For<br />
instance, the high volatility of the market price<br />
might be an investment barrier <strong>and</strong> induce<br />
economic scarcity.<br />
Phosphorus <strong>and</strong> potassium<br />
Several (e.g. water scarcity<br />
constraining mining activities)<br />
Indium, rhodium, bismuth, selenium,<br />
tellurium, etc.<br />
REEs such as gadolinium for energy<br />
efficient light systems<br />
Rhenium for high-temperature<br />
combustors<br />
PGEs mainly extracted from South<br />
African mines, etc.<br />
Copper, etc.<br />
26 March 2008
(Re-) Structuring the field of Non-Energy Mineral Resource Scarcity<br />
Table 2:<br />
Draft list of mineral raw materials that might deserve special attention (to be extended)<br />
Mineral raw<br />
material<br />
Copper<br />
Gold<br />
Hafnium<br />
Indium<br />
Criticality<br />
Divided into the importance in use <strong>and</strong> availability according to the<br />
Committee on Critical Mineral Impacts of the U.S. Economy <strong>and</strong> others<br />
(2007)<br />
Importance in use<br />
Essential properties such as<br />
low electrical resistance.<br />
Outst<strong>and</strong>ing resistance to<br />
corrosion <strong>and</strong> electrical<br />
conductivity. Important for<br />
information technology,<br />
other high performance<br />
applications <strong>and</strong> jewelry.<br />
Increases in dem<strong>and</strong><br />
expected (new computer<br />
chips).<br />
Limited potential for<br />
substitution (in the<br />
production of low-cost<br />
electricity for instance).<br />
Availability<br />
Need for innovation due to low R/C ratio.<br />
By-product to copper <strong>and</strong> zinc, two<br />
metals with short reserve lives<br />
(Andersson, 2001).<br />
Need for innovation due to low R/C ratio.<br />
Phosphorus Essential for vital functions. No unlimited source as in the case of<br />
potassium (seawater).<br />
Platinum<br />
REEs such as<br />
Gadolinium<br />
Rhenium<br />
Rhodium<br />
Tellurium<br />
Titanium<br />
Uranium<br />
Zinc<br />
Exceptionally promising for<br />
nanostructural applications.<br />
Essential <strong>and</strong> indispensable<br />
for new <strong>and</strong> energy efficient<br />
light systems.<br />
No substitutes in hightemperature<br />
combustors<br />
(airplane engines, etc.).<br />
No substitutes in catalytic<br />
converters of cars.<br />
Limited potential for<br />
substitution (production of<br />
low-cost electricity).<br />
Used as titan oxide in white<br />
colour pigments.<br />
Unique properties for energy<br />
production.<br />
Electrochemical properties<br />
make zinc a good<br />
anticorrosion protection<br />
material.<br />
High degree of dissipation through<br />
losses from vehicle’s catalytic converters.<br />
By-product of copper <strong>and</strong> zinc, two<br />
metals with low R/C ratios.<br />
As<br />
mentioned<br />
in<br />
Workshop,<br />
surveys<br />
Surveys<br />
Workshop<br />
Workshop,<br />
surveys<br />
Workshop,<br />
surveys<br />
Workshop,<br />
surveys<br />
Workshop<br />
Workshop<br />
Workshop,<br />
surveys<br />
(Andersson,<br />
2001)<br />
High degree of dissipation. Survey 1<br />
High degree of dissipation in corrosive<br />
environments <strong>and</strong> from other uses.<br />
Survey 1<br />
Workshop,<br />
survey<br />
<strong>ETH</strong>-UNS <strong>Working</strong> <strong>Paper</strong> <strong>43</strong> 27
<strong>ETH</strong>-UNS <strong>Working</strong> <strong>Paper</strong>s<br />
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(Published as: Scholz, R.W. (1998). Umweltforschung<br />
zwischen Formalwissenschaft und Verständnis:<br />
Muss man den Formalismus beherrschen,<br />
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research between formal science <strong>and</strong><br />
comprehension: is comm<strong>and</strong> of the formalism<br />
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& W. Schröder (Eds.), Umweltforschung quergedacht:<br />
Perspektiven integrativer Umweltforschung<br />
und -lehre [Environmental research<br />
thought laterally: perspectives on integrating<br />
environmental research <strong>and</strong> teaching] (pp. 309–<br />
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UNS (1994). Lehrstuhlbeschreibung Umweltnaturund<br />
Umweltsozialwissenschaften (UNS). Fallstudie,<br />
Forschung und Berufspraxis. Zürich: <strong>ETH</strong> Zürich,<br />
Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 3<br />
Mieg, H.A. (1994). Die Expertenrolle. Zürich: <strong>ETH</strong><br />
Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 4<br />
Heitzer, A. & Scholz, R.W. (1994). Monitoring <strong>and</strong><br />
evaluating the efficacy of bioremediation – a conceptual<br />
framework. Zürich: <strong>ETH</strong> Zürich, Umweltnatur-<br />
und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 5 (Out of Print)<br />
Scholz, R.W., Weber, O., & Michalik, G. (1995). Ökologische<br />
Risiken im Firmenkreditgeschäft. Zürich:<br />
<strong>ETH</strong>-Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
(Published as: Scholz, R.W., Weber, O., & Michalik,<br />
G. (1995). Ökologische Risiken im Firmenkreditgeschäft.<br />
[Ecological risks in loans to enterprises] In<br />
Overlack-Kosel, D., Scholz, R.W., Erichsen, S.,<br />
Schmitz, K. W., <strong>and</strong> Urban, G. (Eds.), Kreditrisiken<br />
aus Umweltrisiken [Loan risks due to environmental<br />
risks (pp. 1–49). Bonn: Economica.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 6 (Out of Print)<br />
Scholz, R.W., Heitzer, A., May, T., Nothbaum, N.,<br />
Stünzi, J., & Tietje, O. (1995). Datenqualität und<br />
Risikoanalysen – Das Risikoh<strong>and</strong>lungsmodell zur<br />
Altlastenbearbeitung. Zürich: <strong>ETH</strong> Zürich, Umweltnatur-<br />
und Umweltsozialwissenschaften.<br />
(Published as: Scholz, R.W., Heitzer, A., May, T. W.,<br />
Nothbaum, N. Stünzi, J., & Tietje, O. (1996). Datenqualität<br />
und Risikoanalysen: Das Risikoh<strong>and</strong>lungsmodell<br />
zur Altlastenbearbeitung. [Data<br />
quality <strong>and</strong> risk analyses. The Risk Action Model<br />
of soil remediation] In S. Schulte-Hostede, R.<br />
Freitag, A. Kettrup, <strong>and</strong> W. Fresenius (Eds.), Altlasten-Bewertung:<br />
Datenanalyse und Gefahrenbewertung<br />
[Evaluation of soil remediation cases:<br />
analysis of data <strong>and</strong> evaluation of risks] (pp. 1–29).<br />
L<strong>and</strong>sberg: Ecomed.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 7 (Out of Print)<br />
Scholz, R.W., Mieg, A.H., & Weber, O. (1995). Mastering<br />
the complexity of environmental problem<br />
solving by case study approach. Zürich: <strong>ETH</strong> Zürich,<br />
Umweltnatur- und Umweltsozialwissenschaften.<br />
(Published as: Scholz, R.W., Mieg, H.A., & Weber, O.<br />
(1997). Mastering the complexity of environmental<br />
problem solving with the case study approach.<br />
Psychologische Beiträge, [Contributions<br />
to Psychology] 39, 169–186.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 8 (Out of Print)<br />
Tietje, O. & Scholz, R.W. (1995). Wahrscheinlichkeitskonzepte<br />
und Umweltsysteme. Zürich: <strong>ETH</strong><br />
Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
(Published as: Tietje, O. & Scholz, R.W. (1996).<br />
Wahrscheinlichkeitskonzepte und Umweltsysteme.<br />
[Concepts of probability <strong>and</strong> environmental<br />
systems] In A. Gheorghe & H. Seiler (Eds.),<br />
Was ist Wahrscheinlichkeit? Die Bedeutung der<br />
Wahrscheinlichkeit beim Umgang mit technischen<br />
Risiken [What is probability? The<br />
meaning of probability in the case of technical<br />
risks] (pp. 31–49). Zürich: vdf.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 9 (Out of Print)<br />
Scholz, R.W. (1995). Grenzwert und Risiko: Probleme<br />
der Wahrnehmung und des H<strong>and</strong>elns. Zürich: <strong>ETH</strong><br />
Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
(Published as: Scholz, R.W. (1996). Grenzwerte und<br />
Risiko: Probleme der Wahrnehmung und des<br />
H<strong>and</strong>elns. [St<strong>and</strong>ards <strong>and</strong> risks: Problems of<br />
cognition <strong>and</strong> of action] In A. Grohmann & G.<br />
Reinicke (Eds.), Transparenz und Akzeptanz von<br />
Grenzwerten am Beispiel des Trinkwassers<br />
[Transparency in the setting of st<strong>and</strong>ards <strong>and</strong><br />
their acceptance in the case of drinking water]<br />
(pp. 5–19). Berlin: Erich Schmidt Verlag.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 10 (Out of Print)<br />
Weber, O. (1995). Vom kognitiven Ungetüm bis zur<br />
Unverständlichkeit: Zwei Beispiele für Schwierigkeiten<br />
im Umgang mit Grenzwerten. Zürich: <strong>ETH</strong><br />
Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
(Published as: Weber, O. (1996). Vom kognitiven<br />
Ungetüm bis zur Unverständlichkeit: zwei Beispiele<br />
für Schwierigkeiten im Umgang mit Grenzwerten.<br />
[From cognitive monsters to incomprehensibility:<br />
two examples of difficulties in managing<br />
st<strong>and</strong>ards] In Umweltbundesamt (Ed.),<br />
Transparenz und Akzeptanz von Grenzwerten am<br />
Beispiel des Trinkwassers. Berichtsb<strong>and</strong> zur Tagung<br />
vom 10. und 11. Oktober 1995 (mit Ergänzungen),<br />
[Transparency in <strong>and</strong> acceptance of st<strong>and</strong>ards.<br />
The case of drinking water] (pp. 133–150).<br />
Berlin: Erich Schmidt Verlag.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 11<br />
Oberle, B.M., Meyer, S.B., & Gessler, R.D. (1995).<br />
Übungsfälle 1994: Ökologie als Best<strong>and</strong>teil von<br />
Unternehmens- strategien am Beispiel der Swissair.<br />
Zürich: <strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 12 (Out of Print)<br />
Mieg, H.A. (1996). Managing the Interfaces between<br />
<strong>Science</strong>, Industry, <strong>and</strong> Society. Zürich: <strong>ETH</strong> Zürich,<br />
Umweltnatur- und Umweltsozialwissenschaften.<br />
(Published as: Mieg, H.A. (1996). Managing the<br />
interfaces between science, industry, <strong>and</strong> society.<br />
In: UNESCO (Ed.), World Congress of Engineering<br />
Educators <strong>and</strong> Industry Leaders (Vol. I, pp. 529-533).<br />
Paris: UNESCO.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 13 (Out of Print)<br />
Scholz, R.W. (1996). Effektivität, Effizienz und Verhältnismässigkeit<br />
als Kriterien der Altlastenbearbeitung.<br />
Zürich: <strong>ETH</strong> Zürich, Umweltnatur- und<br />
Umweltsozialwissenschaften.<br />
(Published as: Scholz, R.W. (1996). Effektivität, Effizienz<br />
und Verhältnismässigkeit als Kriterien der<br />
Altlastenbearbeitung. [Efficacy, efficiency <strong>and</strong><br />
appropriateness as criteria for evaluating soil<br />
remediation cases] In: Baudirektion des Kantons<br />
Zürich in Zusammenarbeit mit <strong>ETH</strong>-UNS (Eds.).<br />
Grundsätze, Modelle und Praxis der Altlastenbearbeitung<br />
im Kanton Zürich: Referate zur<br />
Altlastentagung 1996 [Principles, models <strong>and</strong> the<br />
administrative practice of soil remediation in the<br />
Canton of <strong>Zurich</strong>] (pp. 1–22) Zürich: AGW Hauptabteilung<br />
Abfallwirtschaft und Betriebe.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 14 (Out of Print)<br />
Tietje, O., Scholz, R.W., Heitzer, A., & Weber, O.<br />
(1996). Mathematical evaluation criteria. Zürich:<br />
<strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
(Published as: Tietje, O., Scholz, R.W., Heitzer, A.,<br />
<strong>and</strong> Weber, O. (1998). Mathematical evaluation<br />
criteria. In H.-P. Blume, H. Eger, E. Fleischhauer, A.<br />
Hebel, C. Reij, & G. Steiner (Eds.), Towards<br />
sustainable l<strong>and</strong> use (pp. 53–61). Reiskirchen:<br />
Catena.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 15<br />
Steiner, R. (1997). Evaluationsbericht: Bewertung<br />
der obligatorischen Berufspraxis im Studiengang<br />
Umweltnaturwissenschaften durch Betriebe und<br />
Studierende. Zürich: <strong>ETH</strong> Zürich, Umweltnaturund<br />
Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 16 (Out of Print)<br />
Jungbluth, N. (1997). Life-cycle-assessment for<br />
stoves <strong>and</strong> ovens. Zürich: <strong>ETH</strong> Zürich, Umweltnatur-<br />
und Umweltsozialwissenschaften.<br />
(Published as: Jungbluth, N. (1997). Life-Cycle-Assessment<br />
for stoves <strong>and</strong> ovens. 5th SETAC-Europe<br />
LCAS Case Studies Symposium, (pp. 121–130), Brussels.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 17<br />
Tietje, O., Scholz, R.W., Schaerli, M.A., Heitzer, A., &<br />
Hesske, S. (1997). Mathematische Bewertung von<br />
Risiken durch Schwermetalle im Boden: Zusammenfassung<br />
des gleichnamigen Posters auf der<br />
Tagung der Deutschen Bodenkundlichen Gesellschaft<br />
in Konstanz. Zürich: <strong>ETH</strong> Zürich, Umweltnatur-<br />
und Umweltsozialwissenschaften.
<strong>ETH</strong>-UNS <strong>Working</strong> <strong>Paper</strong>s (continued from previous page)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 18<br />
Jungbluth, N. (1998). Ökologische Beurteilung des<br />
Bedürfnisfeldes Ernährung: Arbeitsgruppen, Methoden,<br />
St<strong>and</strong> der Forschung, Folgerungen. Zürich:<br />
<strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 19 (Out of Print)<br />
Weber, O., Scholz, R.W., Bühlmann, R., & Grasmück,<br />
D. (1999). Risk Perception of Heavy Metal Soil Contamination<br />
<strong>and</strong> Attitudes to Decontamination<br />
Strategies. Zürich: <strong>ETH</strong> Zürich, Umweltnatur- und<br />
Umweltsozialwissenschaften.<br />
(Published as: Weber, O., Scholz, R.W., Bühlmann,<br />
R., & Grasmück, D. (2001). Risk Perception of Heavy<br />
Metal Soil Contamination <strong>and</strong> Attitudes to<br />
Decontamination Strategies. Risk Analysis, Vol. 21,<br />
Issue 5, pp. 967–967.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 20 (Out of Print)<br />
Mieg, H.A. (1999). Expert Roles <strong>and</strong> Collective Reasoning<br />
in <strong>ETH</strong>-UNS Case Studies. Zürich: <strong>ETH</strong><br />
Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
(Published as: Mieg, H.A. (2000). University-based<br />
projects for local sustainable development –<br />
Expert Roles <strong>and</strong> Collective Reasoning in <strong>ETH</strong>-<br />
UNS Case Studies. International Journal of<br />
Sustainability in Higher Education, Vol. 1, No. 1, pp.<br />
67–82.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 21<br />
Scholz, R.W. (1999). «Mutual Learning» und Probabilistischer<br />
Funktionalismus – Was Hochschule und<br />
Gesellschaft von ein<strong>and</strong>er und von Egon Brunswik<br />
lernen können. Zürich: <strong>ETH</strong> Zürich, Umweltnaturund<br />
Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 22 (Out of Print)<br />
Semadeni M. (1999). Moving from Risk to Action: A<br />
conceptual risk h<strong>and</strong>ling model. Zürich: <strong>ETH</strong> Zürich,<br />
Umweltnatur- und Umweltsozialwissenschaften.<br />
(Published as: Semadeni, M. (2000). Moving from<br />
risk to action: A conceptual risk h<strong>and</strong>ling model.<br />
In R. Häberli, R. Scholz, A. Bill, & M. Welti (Eds.),<br />
Proceedings of the International Transdisciplinarity<br />
2000 Conference: Transdisiplinarity – Joint<br />
Problem-Solving among <strong>Science</strong>, Technology <strong>and</strong><br />
Society. <strong>ETH</strong> <strong>Zurich</strong>. Workbook I: Dialogue<br />
Sessions <strong>and</strong> Idea Market (pp. 239-234). Zürich:<br />
Haffmanns Sachbuch Verlag.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 23 (Out of Print)<br />
Güldenzoph, W. & Scholz, R.W. (2000). Umgang<br />
mit Altlasten während dem Transformationsprozess<br />
im Areal Zentrum Zürich Nord (ZZN). Zürich:<br />
<strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften<br />
(Published as: Güldenzoph, W., Baracchi, C., Fagetti,<br />
R., & Scholz, R.W. (2000). Chancen und<br />
Dilemmata des Industriebrachenrecyclings:<br />
Fallbetrachtung Zentrum Zürich Nord [Opportunities<br />
<strong>and</strong> dilemmas in the recycling of industrial<br />
"brownfields": Case study city center <strong>Zurich</strong><br />
North]. DISP 1<strong>43</strong> [Documents <strong>and</strong> Information on<br />
Local, Regional, <strong>and</strong> Country Planning in Switzerl<strong>and</strong>],<br />
36, 10-17.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 24<br />
Semadeni M. (2000). Soil <strong>and</strong> Sustainable L<strong>and</strong>-<br />
Use. Zürich: <strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 25<br />
Sell J., Weber, O., & Scholz, R.W. (2001). Liegenschaftsschatzungen<br />
und Bodenbelastungen. Zürich:<br />
<strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 26 (Out of Print)<br />
Hansmann, R., Hesske, S., Tietje, O., & Scholz, R.W.<br />
(2001). Internet-unterstützte Umweltbildung: Eine<br />
experimentelle Studie zur Anwendung des Online-<br />
Simulationsspiels SimUlme im Schulunterricht.<br />
Zürich: <strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
(Published as: Hansmann, R., Hesske, S., Tietje, O.,<br />
& Scholz, R.W. (2002). Internet-unterstützte Umweltbildung:<br />
Eine experimentelle Studie zur<br />
Anwendung des Online-Simulationsspiels Sim-<br />
Ulme im Schulunterricht. Schweizerische Zeitschrift<br />
für Bildungswissenschaften, Nr. 1/2002.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 27<br />
Scholz, R.W. & Weber, O. (2001). Judgments on<br />
Health Hazards to Soil Contamination by Exposed<br />
<strong>and</strong> Not-exposed Residents. Zürich: <strong>ETH</strong> Zürich,<br />
Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 28<br />
Scholz, R.W., Steiner, R., & Hansmann, R. (2001).<br />
Practical Training as Part of Higher Environmental<br />
Education. Zürich: <strong>ETH</strong> Zürich, Umweltnatur- und<br />
Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 29<br />
Hansmann, R., Scholz, R.W., Crott, H.W., & Mieg,<br />
H.A. (2001). Education in Environmental Planning:<br />
Effects of Group Discussions, Expert Information,<br />
<strong>and</strong> Case Study Participation on Judgment Accuracy.<br />
Zürich: <strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 30<br />
Laws, D., Scholz, R.W., Shiroyama, H., Susskind, L.,<br />
Suzuki, T., & Weber, O. (2002). Expert Views on<br />
Sustainability <strong>and</strong> Technology Implementation.<br />
Zürich: <strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 31<br />
Flüeler, T. (2002). Robust Radioactive Waste Management:<br />
Decision Making in Complex Socio-technical<br />
Systems. Part1 = Options in Radioactive Waste<br />
Management Revisited: A Proposed Framework for<br />
Robust Decision Making; Part 2 = Robustness in<br />
Radioactive Waste Management. A Contribution to<br />
Decision Making in Complex Socio-technical Systems.<br />
Zürich: <strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
(Part 1 published as: Flüeler, T. (2001a): Options in<br />
Radioactive Waste Management Revisited: A<br />
Framework for Robust Decision Making. Journal of<br />
Risk Analysis. Vol. 21. No. 4. Aug. 2001:787-799.<br />
Part 2 published as: Flüeler, T. (2001b): Robustness<br />
in Radioactive Waste Management. A Contribution<br />
to Decision-Making in Complex Sociotechnical<br />
Systems. In: E. Zio, M. Demichela & N.<br />
Piccinini (eds.): Safety & Reliability. Towards a<br />
Safer World. Proceedings of the European Conference<br />
on Safety <strong>and</strong> Reliability. ESREL 2001.<br />
Torino (I), 16-20 Sep. Vol. 1. Politecnico di Torino,<br />
Torino, Italy:317-325.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 32<br />
Hansmann, R., Mieg, H.A., Crott, H.W., & Scholz,<br />
R.W. (2002). Models in Environmental Planning:<br />
Selection of Impact Variables <strong>and</strong> Estimation of<br />
Impacts. Zürich: <strong>ETH</strong> Zürich, Umweltnatur- und<br />
Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 33<br />
Schnabel, U., Tietje, O., & Scholz, R.W. (2002). Using<br />
the Power of Information of Sparse Data for Soil<br />
Improvement Management. Zürich: <strong>ETH</strong> Zürich,<br />
Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 34<br />
Weber, O., Reil<strong>and</strong>, R., & Weber, B. (2002). Sustainability<br />
Benchmarking of European Banks <strong>and</strong><br />
Financial Service Organizations . Zürich: <strong>ETH</strong><br />
Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 35<br />
Kammerer, D., Sell, J., & Weber, O. (2002). Evaluation<br />
of AIJ Project Proposals – Potential Contribution<br />
to Sustainable Development. Zürich: <strong>ETH</strong><br />
Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 36<br />
Scholz, R.W., Mieg, H.A., & Weber, O. (2003). Wirtschaftliche<br />
und organisationale Entscheidungen.<br />
Zürich: <strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
(Published as: Scholz, R.W., Mieg, H.A., & Weber O.<br />
(2003). Wirtschaftliche und organisationale Entscheidungen,<br />
In: Auhagen & Bierhoff. Wirtschaftsund<br />
Organisationspsychologie.)<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 37<br />
Scholz, R.W. & Binder, C. (2003). The Paradigm of<br />
Human-Environment Systems. Zürich: <strong>ETH</strong> Zürich,<br />
Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 38<br />
Hansmann, R., Crott, H.W., Mieg, H.A., & Scholz,<br />
R.W. (2003). Is Group Performance Improved by<br />
Evaluating Task Difficulty <strong>and</strong> by Knowing about<br />
the Differential Effects of Conformity?. Zürich: <strong>ETH</strong><br />
Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 39<br />
Binder, C., Hofer, C., Wiek, A., & Scholz, R.W. (2003).<br />
Transition process towards regional wood flows by<br />
integrating material flux analysis <strong>and</strong> agent analysis:<br />
The case of Appenzell Ausserrhoden, Switzerl<strong>and</strong>.<br />
Zürich: <strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 40<br />
Loukopoulos, P. & Scholz, R.W. (2003). Future Urban<br />
Sustainable Mobility: Using ‘Area Development<br />
Negotiations’ for Scenario Assessment <strong>and</strong> for<br />
Assisting the Democratic Policy Process. Zürich:<br />
<strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 41<br />
Fenchel, M., Scholz, R.W., & Weber, O. (2003). Does<br />
Good Environmental Performance reduce Credit<br />
Risk? – Empirical Evidence from Europe`s Banking<br />
Sector. Zürich: <strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> 42<br />
Grasmück, D. & Scholz, R.W. (2003). Risk perception<br />
of heavy metal soil contamination by high-exposed<br />
<strong>and</strong> low-exposed inhabitants. Zürich: <strong>ETH</strong> Zürich,<br />
Umweltnatur- und Umweltsozialwissenschaften.<br />
■ UNS-<strong>Working</strong> <strong>Paper</strong> <strong>43</strong><br />
Wolfensberger, M., Lang, D., & Scholz, R.W. (2008).<br />
(Re-) Structuring the field of Non-Energy Mineral<br />
Resource Scarcity. Summary of the Workshop<br />
“Scarce Raw Materials” August 31–September 2,<br />
2007 – Davos, Switzerl<strong>and</strong>. Zürich: <strong>ETH</strong> Zürich,<br />
Umweltnatur- und Umweltsozialwissenschaften.