Working Paper 43 - ETH Zurich - Natural and Social Science ...

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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

<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 />

<strong>ETH</strong>-UNS <strong>Working</strong> <strong>Paper</strong> <strong>43</strong> 9


Maya Wolfensberger, Daniel J. Lang & Rol<strong>and</strong> W. Scholz<br />

<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 />

10 March 2008


(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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Maya Wolfensberger, Daniel J. Lang & Rol<strong>and</strong> W. Scholz<br />

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 />

12 March 2008


(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 />

<strong>ETH</strong>-UNS <strong>Working</strong> <strong>Paper</strong> <strong>43</strong> 13


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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Maya Wolfensberger, Daniel J. Lang & Rol<strong>and</strong> W. Scholz<br />

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 />

<strong>ETH</strong>-UNS <strong>Working</strong> <strong>Paper</strong> <strong>43</strong> 17


Maya Wolfensberger, Daniel J. Lang & Rol<strong>and</strong> W. Scholz<br />

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 />

<strong>ETH</strong>-UNS <strong>Working</strong> <strong>Paper</strong> <strong>43</strong> 19


Maya Wolfensberger, Daniel J. Lang & Rol<strong>and</strong> W. Scholz<br />

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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Scholz, R.W. (1994). Muss man den Formalismus beherrschen,<br />

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<strong>ETH</strong> Zürich, Umweltnatur- und Umweltsozialwissenschaften.<br />

(Published as: Scholz, R.W. (1998). Umweltforschung<br />

zwischen Formalwissenschaft und Verständnis:<br />

Muss man den Formalismus beherrschen,<br />

um die Formalisten zu schlagen? [Environmental<br />

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 />

328). Berlin: Springer.)<br />

■ UNS-<strong>Working</strong> <strong>Paper</strong> 2 (Out of Print)<br />

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 />

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■ UNS-<strong>Working</strong> <strong>Paper</strong> 4<br />

Heitzer, A. & Scholz, R.W. (1994). Monitoring <strong>and</strong><br />

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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.

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