Erik Persson
What is Wrong with
Extinction?
The Answer from Anthropocentric
Instrumentalism
Contents
1. INTRODUCTION ..................................................................................................................................................3
1.1. BACKGROUND AND PURPOSE OF THE INVESTIGATION .....................................................................................3
1.2. THE PART OF THE INVESTIGATION PRESENTED IN THIS BOOK..........................................................................5
1.3. THE DISPOSITION OF THE REST OF THE INVESTIGATION ...................................................................................6
1.4. ACKNOWLEDGEMENTS ......................................................................................................................................7
2. ANTHROPOCENTRIC INSTRUMENTALISM..............................................................................................8
2.1. THE STANDARD ANSWER ...................................................................................................................................8
2.2. THE RIGHT ANSWER?...................................................................................................................................... 11
2.3. SOME KINDS OF INSTRUMENTAL VALUE OF NON-HUMAN SPECIES FOR HUMAN BEINGS ............................. 12
2.3.1. Food........................................................................................................................................................ 12
2.3.2. Medicine ................................................................................................................................................. 15
2.3.3. Materials and fuel.................................................................................................................................. 17
2.3.4. Indicator species.................................................................................................................................... 24
2.3.5. Some non-destructive uses of other species ......................................................................................... 25
2.3.6. Tourism................................................................................................................................................... 27
2.4. TRADE OFF ...................................................................................................................................................... 30
2.5. CHOICE VALUE ............................................................................................................................................... 36
2.6. TRANSFORMATIVE VALUE.............................................................................................................................. 40
2.7. ECOSYSTEM SERVICES .................................................................................................................................... 43
3. UNCERTAINTY.................................................................................................................................................. 53
3.1. BIODIVERSITY AND UNCERTAINTY ................................................................................................................ 53
3.2. DEALING WITH UNCERTAINTY ....................................................................................................................... 58
3.3. THE PRECAUTIONARY PRINCIPLE .................................................................................................................. 61
3.3.1. Promoting the positive versus avoiding the negative.......................................................................... 63
3.3.2. Irreversibility ......................................................................................................................................... 65
3.3.3. The value of human health .................................................................................................................... 70
3.3.4. The cost of being late............................................................................................................................. 72
3.3.5. False positives versus false negatives .................................................................................................. 74
3.3.6. Conclusions............................................................................................................................................ 77
3.4. PROBLEMS WITH THE PRECAUTIONARY PRINCIPLE ....................................................................................... 78
3.4.1. Is the precautionary principle ill-defined? .......................................................................................... 79
3.4.2. Is the precautionary principle anti-science? ....................................................................................... 80
3.4.3. Values instead of science ...................................................................................................................... 83
3.4.4. Favouring the status quo....................................................................................................................... 85
3.4.5. Ignoring other risks ............................................................................................................................... 87
3.4.6. Does the precautionary principle lure us into a paradox?................................................................. 91
3.4.7. How do we prove a negative?............................................................................................................... 92
3.5. WHAT CAN THE PRECAUTIONARY PRINCIPLE DO FOR US? ............................................................................ 93
4. FUTURE GENERATIONS................................................................................................................................ 96
4.1. DO WE HAVE ANY DUTIES TO FUTURE GENERATIONS? ................................................................................. 97
4.1.1. The asymmetry problem ........................................................................................................................ 97
4.1.2. The non-identity problem .................................................................................................................... 106
4.1.3. The problem of overwhelming sacrifice ............................................................................................. 114
4.1.4. Mental impossibility ............................................................................................................................ 118
4.1.5. Uncertainty........................................................................................................................................... 119
4.1.6. Democracy ........................................................................................................................................... 122
4.1.7. Opportunity loss................................................................................................................................... 123
4.1.8. Distance................................................................................................................................................ 126
4.1.9. Will they need our sacrifices?............................................................................................................. 128
4.2. CONCLUSIONS ............................................................................................................................................... 133
5. SOMETHING IS LACKING........................................................................................................................... 134
1
6. SUMMARY AND CONCLUSIONS ............................................................................................................... 137
REFERENCES ....................................................................................................................................................... 139
2
1. Introduction
1.1. Background and purpose of the investigation
No one really knows the rate by which species go extinct by the hands of human
beings. The estimations differ,1 but they seem to agree that it is a matter of extreme
proportions. According to the Worldwatch Institute, we are now experiencing the worst case
of mass extinction since the dinosaurs disappeared 65 million years ago.2 For most of us, this
is a depressing insight and many people seem to agree that to knowingly cause or
significantly contribute to the extinction of entire species is (at least prima facie) not only
bad, but morally wrong.
For someone with a philosophic curiosity, the question that immediately arises is:
‘Why is it wrong’?
Intuitively it seems obviously true that it is wrong, but why is it wrong, and how does
it fit with formal ethical theories? These questions are more complicated than they may seem
at the first glance and they have been the object of a heated debate among both ethicists and
environmentalists. This fact alone should be reason enough to pursue the question, but there
are other reasons too. The clearness of and the wide agreement about the intuition that what
we are doing is at least prima facie wrong, makes the extinction problem an excellent test
case that any theory should be able to deal with in order to be taken seriously as a moral
theory.
Another quite obvious motivation for studying the question of why it is prima facie
wrong to cause extinction, is that a better understanding of the ethical aspects of the
extinction problem would increase our chances of dealing with the problem. Bryan G.
Norton points out that environmentalists often put much effort in trying to explain why a
species is instrumentally important for human beings, and they often use different
approaches. This is a ‘strategy’ that usually gives a bad impression however. It also makes it
1
For some estimations, see: Aniansson 1990 pp.21,25,65, Bennett et al 2003 p.136, Callicott 1986 p.138, Daily
2000 p.333, Ehrlich et al 1990 p.96,97,99, Heinzman 1990 p.5, James 2002 p.55, Kellert 1986 p.51, Lovejoy
1986 p.14, Millennium Ecosystem Assessment 2005 pp.v,2,3,4f,42ff, Niklasson & Nilsson 2001 p.19, Norton
1986:1 p.120, Norton 1986:2 pp.3,10, Norton 1987 p.65, Palmer 1995 p.31, Ricklefs 1997 p.597, Wramner
1990 p.5
2
http://www.worldwatch.org/topics/nature 2004-06-04. Bennett et al (Bennett et al 2003 p.136) seems to
reason along the same lines.
3
harder to reach the common goal of saving the species. 3 Failures of the environmental
movement that can be traced back to the difficulties in agreeing on why different species and
ecosystems are important enough for us humans to be worth saving, leads Bryan G. Norton
to conclude that we need what he labels “a coherent rationale for environmental protection.”4
This is underlined by Lori Gruen and Dale Jamieson who declare that:
It is ironic that the destruction of biodiversity, which may be the greatest of human
crimes against nature, is also one of the least understood. We do not have a good
philosophical account of why biodiversity matters, and the steps that would have to
be taken to protect it are, in the present climate, politically impossible.5
Both Norton’s and Gruen/Jamieson’s remarks, tell us that there is quite a great deal of
work to be done in the field, and they also tell us that the work is very important.
Finally, the problem of human-caused extinction also seems to be a good battleground
for the more general question of what should count as criteria for moral standing. Actually,
most of the ethical debate surrounding the extinction problem is concerned with this
question, and this will also be salient in this investigation.
The present debate around this question is mostly performed in polemic between
advocates of holistic theories on the one hand, and advocates of individualistic theories on
the other.
The advocates of the holistic approach claim that we have moral duties directly to the
species. They are primarily concerned that without a direct moral standing for the species,
we will have to depend on its the instrumental value for us humans.
The individualists on the other hand claim that only individuals can be moral objects.
They are sceptical to the holistic approach, and to the possibility of ascribing moral standing
to species. They especially find it difficult to comprehend how species can have morally
relevant interests for us to consider. This book is the first part of an investigation that will
scrutinise both the holistic approach and the individualistic approaches.
3
Norton 1982 pp.18f
Norton 1982 p.20
5
Gruen & Jamieson 1994 p.334
4
4
1.2. The part of the investigation presented in this book
In this book, I will examine the most common answer to why it is wrong to cause a
species to go extinct, viz. because (and only because) the species is – directly or indirectly –
instrumentally valuable to us human beings.
I will start with a general account of the idea. Then I will take a closer look at some of
the ways in which other species can have instrumental value for us human beings, and at
how these values can be expected to stand up in a trade off situation with other human
values. I will then go on and investigate two special types of instrumental value that are
suggested to be important in our relation with other species. It is also important not to forget
that the species do not just supply us with value individually, but also in virtue of being a
part of an ecosystem (or rather several ecosystems) and of the general biodiversity. I will
therefore assign a part of the investigation to that kind of values.
Due to the large degree of uncertainty surrounding both the value and the function of
species, I will assign one chapter especially to the issue of uncertainty. I will then both
discuss the uncertainties as such, and how to deal with them. I will pay special attention to
the so-called precautionary principle that has become increasingly popular as a tool for
decision under uncertainty, but that is also subject to some serious criticism.
An important part of the problem of extinction is that typically, it is now living human
beings who benefit while future generations of human beings have to live with the problems.
I will therefore assign a chapter to the question of whether we have a moral duty to preserve
species for the sake of future human beings.
As we shall see, many species as well as a generally high degree of biodiversity are
quite important for us human beings – both present and future generations. This seems to
account for some part of why it is morally problematic to cause extinction, but it will
probably not give us the whole answer. Even though the instrumental value of many species
for us humans seems to give us quite strong moral reasons to be restrictive in contributing to
their extinction, it does not seem to be enough to motivate our strong feelings of moral
indignation. We seem to need something more to explain why we should refrain from doing
things that are e.g. economically lucrative only on the basis that these activities cause
extinction of other species.
5
It is therefore necessary to continue the investigation in order to gain a complete
answer to our question. This will be done in a coming extended publication containing the
entire investigation.
In order to be as clear as possible as to how the investigation presented in this book fits
with the whole, I will give a short account of the disposition of the rest of the investigation.
The reader who is only interested in moral duties generated by the instrumental value of
other species for human beings, can skip this part and go directly to chapter 2.
1.3. The disposition of the rest of the investigation
The rest of the investigation will consider the suggested answers to the question of
“what is wrong with extinction” that are not based on the instrumental value of the species
for human beings.
I will start with another of the major contestants, viz. the idea that we have moral
obligations to the species themselves. This approach has some great advantages, but also its
fair share of problems. I will start by presenting the idea, and then go through the problems
one by one to see if they are real, and if so, how serious they are and whether they can be
solved.
When analysing the idea of how species can have intrinsic value, we will find that this
view might not be best expressed in terms of moral standing for the species, but in terms of
final value of the species for human beings. We will thus turn back to the human-centred
approach, but this time no longer just in an instrumental setting. By considering the final
value of other species for human beings, we seem to be able to account for most of the
intuitions referred to by the holistic approach without having to claim that the species have
moral standing on their own. At the same time we will get a much more complete
understanding of why it is wrong to cause extinction compared to what we could get by just
referring to the instrumental value of the species for human beings.
Even this will not give us the full answer however. There will still be conflicts that
cannot be fully explained in terms of human interests whether instrumental or final. In the
last part of the investigation, I will widen the individualistic approach further by taking it
beyond anthropocentrism. The case for moral standing for many non-human individual
6
animals is much easier to defend than both the idea that entire species have moral standing,
and the idea that only human beings have moral standing. Nevertheless, this extended
individualistic approach also has its share of problems. These problems will be scrutinised,
and hopefully the combined results of the entire investigation will give a solid account of
what is wrong with extinction.
1.4. Acknowledgements
Before I start presenting the investigation however, I wish to thank everyone who has
been involved in the process. Not least my supervisor Dan Egonsson who has read my text
several times and bestowed me with much useful feedback. I also wish to thank Agneta Åhs,
Jonathan Linné, Wlodek Rabinowicz, Johannes Persson and Dennis Brice who have all read
the whole or parts of the manuscript and provided me with many useful comments. A special
thanks goes to the members of the PhD study group at the Lund University Centre for
Sustainability Studies, and the philosophy seminar at the Royal Institute of Technology to
whom I have presented parts of the text, and who’s comments have been very useful. Finally
a want to express my gratitude to Stiftelsen Oscar och Lilli Lamms minne, who has financed
part of the work.
7
2. Anthropocentric Instrumentalism
2.1. The standard answer
I have chosen to call the first and most common answer to our question
‘anthropocentric instrumentalism’. ‘Anthropocentric’ because it only considers the value
other species have for us human beings, and ‘instrumentalism’ because it does not conceive
of other species as having value as ends in themselves, but only as a means to something
else.6
This answer has historically been viewed as the most important reason for
conservation,7 and if we scrutinise official national and international policy documents that
discuss the issue of species loss, we can see that anthropocentric instrumentalism clearly
dominates – when the question of a reason is at all discussed. In most documents, it is not
discussed at all, or just barely. In some cases, the documents explicitly state other reasons
than anthropocentric instrumentalism.8 It is however quite clear from the reasoning in the
documents that anthropocentric instrumentalism is almost always assumed to be the sole
basis for their concern about other species. When reasons are mentioned, they are with few
exceptions only just that – mentioned – nothing more. The discussion, agreements,
recommendations etc. (depending on the purpose of the document) are imbued with the
attitude that other species only have value as a means for other things valued intrinsically or
instrumentally by human beings.9
In scientific, educational or advisory articles or textbooks discussing species loss
and/or giving advice on species preservation, the question of why we should protect
threatened species is in general not discussed. When it is, it is common to talk about
6
Many authors do not acknowledge the possibility that other species can have intrinsic value for human beings
and therefore use the term ‘anthropocentrism’ as equivalent to the way I use the term ‘anthropocentric
instrumentalism’.
7
Melin 2001 passim, Rundlöf 1999 p.12
8
Melin 2001 passim
9
For a more extensive investigation surrounding this, see Stenmark 2000 passim. Stenmark has studied several
national and international policy documents and has reached the same conclusion as I have. See also Aniansson
1990 p.123. For a historical outlook from a Swedish perspective, see Melin 2001 Passim
For examples, see e.g. The Bern convention 1979 pp.2f, Cal/EPA 2003, Interview with EU commissionaire
Margot Wallström in Sydsvenska Dagbladet February 9th 2004
(http://w1.sydsvenskan.se//print/printarticle.jsp?article=10074604,), Johansson 2003 pp.3,8,28, Millennium
Ecosystem Assessment 2005 passim, Various statement by MA board members on the official website of the
Millennium Ecosystem Assessment, The Rio Convention 1992 §1 and passim, World Commission on
Environment and Development 1987 p.6:1ff and passim, Johansson 2006 p.10,15
8
“scientific”, “biological” or “ecological” reasons. What this means is seldom discussed, but
it seems quite clear that these reasons are not conceived of as moral ones. In fact, most
authors of this kind of texts do not recognise them as value judgements at all. Obviously,
they are value judgements, but disguised as scientific statements. The reason judgements
disguised as scientific statements are sometimes anthropocentric instrumental (“we need to
study the species to determine how we can utilise them in the most effective way”, “ecology
tells us that we need the species in order to survive” etc.). Sometimes the reasons are based
on an anthropocentrically intrinsic attitude towards the species (“the species is fascinating in
its own right and therefore intrinsically worthy of our attention”), and quite often ecocentric
(“we must respect the species for its own sake”). Sometimes the authors contrast their
“scientific”(etc.) reasons for preservation with what they call “moral” or “ethical” reasons.
Why their own reasons are not moral, and what they mean by “moral” and “ethical” reasons,
is not however clear. When they use these terms, they most often seem to refer to the kind of
reasons for preservation that I will call anthropocentric intrinsic reasons. Sometimes they
seem to be thinking of a certain type of anthropocentric instrumental reasons, according to
which nature or certain species are important for aesthetic, cultural or religious reasons. It is
not clear though why these values are seen as moral while the so-called “scientific” (or
“biological” etc.) reasons for preservation are not. Sometimes the authors also contrast their
“scientific”(etc.) reasons with what they call “economic” or “utilitarian”10 reasons. The latter
seems to be identical with what I have labelled anthropocentric instrumental reasons.
Authors of scientific, advisory or educational texts that discuss the question of why species
preservation is important, are often very eager to find this kind of “economic” or “utilitarian”
motive to justify their work, but it is in general also clear that this is seldom their own
motives – at least not primarily.11
Finding clear statements from non-governmental organisations (NGOs) concerning
why preservation is important has proved to be surprisingly difficult.12 Most NGOs are of
10
They clearly do not use the term ‘utilitarian’ the way it is normally used within ethics, but rather as a
synonym to ‘instrumental’.
11
For examples of how this kind of texts reason around the value of species preservation, see e.g. Aniansson
1990 p.31, Elmqvist et al 2005:2 pp.44ff, Farber 2000 pp.s492f, passim, From & Delin (ed.) 1997 p.5,
Gärdenfors 2005 p.120,126, Ihse 2005 pp.62,66f,72, Johansson, Birgitta 2005:1p.39, Johansson Maria 2005
p.100, Niklasson & Nilsson 2001 pp.19f, Norton 1987 pp.6f, Ricklefs 1997 p.597, Spellerberg14ff, Sörlin 1991
p.175.
12
I have studied the official internet sites of the following organisations: BirdLife International
(http://www.birdlife.org), BirdLife Malta (http://www.birdlifemalta.org), Defenders of Wildlife
(http://www.defenders.org), Danmarks Naturfredningsforening (http://www.dn.dk/), Estonian Fund for Nature
(http://www.elfond.ee/index.php?keel=inglise), European Centre for Nature Conservation (http://www.ecnc.nl),
Friends of the Earth International (http://www.foei.org), Greenpeace
9
course focused on the means of protection, not the reasons, but it is still rather surprising that
they do not spend more energy justifying their work. When they do, the reasons are typically
anthropocentric instrumental,13 but just like in the scientific texts, they also mention
“scientific”/”ecological” etc. reasons for species protection, and now and then they appeal to
e.g. “ethical”, “aesthetical” or “cultural” reasons, or the “intrinsic value” of nature,
ecosystems or species.14
Personal experience tells me however that many people active in NGOs have reasons
for their work that go beyond the anthropocentric instrumental ones that are expressed in
official national and international policy documents. Both anthropocentric intrinsic,
ecocentric and individualistic non-anthropocentric (i.e. sentientistic,15 zoocentric16 or
biocentric17) reasons are common.
To summarize: The question of why extinction is a problem is not very deeply
discussed among policymakers, or among scientists and NGOs dealing with preservation
issues. From what I have found, it seems that both the NGOs and the scientific authors seem
to be willing to admit a wider range of reasons for protecting biodiversity compared with the
official national and international policy documents, even though the authors of scientific
texts are more prone to hiding their own value judgements behind pretended scientific
statements. Both NGOs and scientific authors tend ultimately to justify their commitment to
saving endangered species by anthropocentric instrumental arguments. I guess that the main
reason for this is that this type of argument is supposed to have a greater impact among both
the public and the decision makers. That anthropocentric instrumentalism is more commonly
accepted among decision makers – at least among the most influential ones – seems to be
confirmed by the official national and international policy documents referred to above.
(http://www.greenpeace.org/international/), Greenpeace Sweden (http://www.greenpeace.org/sweden),
Miljöförbundet Jordens Vänner (http://www.mjv.se), Natur och Miljö – Riksorganisation för miljövård
(http://www.naturochmiljo.fi), Norges Naturvernforbund (http://www.naturvern.no), Plantlife
(http://www.plantlife.org.uk), Rainforest Action Network (http://www.ran.org), Svenska
Naturskyddsföreningen (http://www.snf.se), Svenska Rovdjursföreningen (http://www.rovdjur.se), Sveriges
Ornitologiska Förening (http://www.sofnet.org), Taiga Rescue Network (http://www.taigarescue.org), The
World Conservation Union (http://www.iucn.org/), Wildlife Trust (http://www.wildlifetrust.org), World Wide
Fund For Nature (http://www.panda.org/),
13
See e.g. Aniansson 1990 passim, Johansson, Birgitta 2005 2 p.106f Lindén p.72ff, Olsson 2004 p.43,
Plantlife (http://www.plantlife.org.uk), Taiga Rescue Network (http://www.taigarescue.org), Wramner 1990
pp.4,7
14
See e.g. Aniansson 1990 pp.16f,58,80,108, BirdLife International (http://www.birdlife.org), Johansson,
Birgitta 2005 1p.13, Johansson, Birgitta 2005 2 p106f, Olsson 2004 p.43, Wramner 1990 pp.4,7
15
Sentientistic ethics assigns moral standing to all and only sentient beings.
16
Zoocentric ethics assigns moral standing to all and only animals.
10
2.2. The right answer?
Sverker Sörlin, who has studied our attitudes towards the environment from a
historical perspective, claims that the best reason to believe that we will establish what he
calls “a contract with nature” is that the arrogance we have shown towards nature will
eventually be detrimental also to our own species and our culture.18 Sörlin thus seems to
consider anthropocentric instrumentalism the correct – and the most instrumentally useful –
answer to our question. He is apparently not alone in this. Steven Luper-Foy and Bryan
Norton e.g. believe that anthropocentrism does give us strong reasons for becoming better at
protecting nature.19
Is this judgement correct, and if so, is it sufficient to account for our moral intuitions
concerning extinction? I.e.: To what degree can anthropocentric instrumentalism account for
our moral intuitions against species extinction?
The rest of this book will be concerned with this question.
In order to answer it, we have to answer three sub-questions:
1. How important are other species to us human beings?
2. If other species are important to us, are they important enough in comparison to the
values they have to compete with?
3. If so, can this be a complete explanation of why it is at least in general morally
wrong to contribute to the extinction of a species?
I will start by trying to answer the first two questions by discussing different ways in
which other species can have instrumental value for human beings, and by looking at some
particular forms of instrumental value that are especially relevant for our investigation.
When I have done that, I will approach the third question by investigating whether our moral
intuitions concerning extinction can be completely satisfied with anthropocentric
instrumentalism as the sole answer.
Let us however begin with the first of the sub-questions by looking at some ways in
which other species can have instrumental value for human beings.
17
Biocentric ethics assigns moral standing to all and only living beings.
Sörlin 1991 p.273f
19
Luper-Foy 1995 p.91, Melin 2001 p.15 Just like Stenmark, Melin and many others, Luper-Foy does not
distinguish between anthropocentric instrumental and anthropocentric intrinsic attitudes towards nature in the
way I do in this investigation. Since I believe the two versions are relevantly different and because of a history
of misunderstandings, I will be careful in keeping them separate.
18
11
2.3. Some kinds of instrumental value of non-human species for
human beings
2.3.1. Food
All our nutrients come from other species directly and indirectly. Most of the species
used directly for food are domesticated, but even wild species contribute to our food supply,
especially in developing regions but even the most technologically advanced countries
depend in many ways on wild species for their food.20 All our domesticated species today
originate from wild species, and some of today’s wild species will probably be the basis for
domesticated species in the future.21 Since it is assumed by anthropocentrism that only
human beings have moral standing, the fact that we are killing the proximate source of our
nutrients (including killing and eating sentient animals) is not in itself a problem according
to anthropocentrism as long as the species continues to exist and supplies us with new
individuals to eat. This will give us a strong incentive for conserving the species even
without involving ethics. Rational selfishness alone is an incentive for conservation. If we
also admit the moral responsibility not to deplete the food sources for other human beings,
the argument will be even stronger. It also makes the argument more inclusive since we
probably need more species to supply the whole of humanity with food. A species that is
well suited for being farmed/hunted/gathered etc. in Sweden may not be equally well suited
for the same activities in e.g. India.22
This looks promising, but the case is not as simple as it looks above. That a species is
found suitable as food for human beings has not always been good news from a preservation
perspective. We have literally eaten a large number of species to extinction.23 This is
probably quite often a result of imprudence or irrationality rather than as something that
necessarily follows from anthropocentric instrumentalism, but maybe we do not need to save
all the sources of a particular nutrient to secure the supply of that nutrient? Maybe we do not
20
Almered Olsson 2005 p. 53, Aniansson 1990 pp.57,59,68, Gärdenfors 2005 p.119, Ihse 2005 p.62, Lindén
1990 pp.73,77, Millennium Ecosystem Assessment 2005 pp.30f, Myers, 1990 pp.16,21f, Söderqvist 2005 p.74
21
Ehrlich et al 1990 p.102, Myers, 1990 p.16, Norton 1987 p.27
22
It has to be pointed out however that in the same way and for the same reasons that anthropocentrism
provides a stronger incentive for preservation than egocentrism, an even wider account of who has moral
standing – ecocentrism or non-anthropocentric individualistic theories – would provide an even stronger
incentive for preservation but it would complicate the question of whether it is ethically acceptable to eat the
source of the nutrition.
23
For some examples see e.g. Ricklefs 1997 p.606
12
need to save all species that supply us with protein in order to secure our supply of protein
e.g.? Economically, it may well be rational in many cases to replace natural species with
bred or cultivated ones that are more productive and easier to manage (as long as the wild
species are not important for other reasons).24 This means that if we find one species that is a
good provider of different nutrients and is easy to breed etc. we have a tendency to
domesticate that species and breed large numbers of it. At the same time other species that
play the same role but less effectively lose their importance.
It is also argued from an economic perspective that it can sometimes be perfectly
rational to deplete a non-renewable resource if we know or at least have good reasons to
believe that we can replace it with another resource. It may even be economically required to
do so if extensive use of the first resource is necessary to drive the economical and
technological development that is needed for us to develop the means of utilizing the other
resource. If this is right, it substantially weakens the argument that we need to preserve any
given species as sources of nutrients for human beings as long as there exist other species
that can supply us with the same nutrients.
There is another reason why it might be a problem from a preservation perspective that
a species turns out to be a valuable nutrient source for human beings: If we domesticate a
species, we will probably change its genetic make up. The properties that make it more
suitable for human utilization may well make the domesticated form less suited for a life in
nature. If this is combined with the usual human fear of competition, the result can be that
other species including the non-domesticated relatives of the species are eradicated in order
to protect or give room for the domesticated version. This behaviour is quite common and
has e.g. resulted in destruction of forests and wetlands to gain land for different types of
agriculture, as well as to fierce eradication campaigns against everything from plants and
animals competing for nutrients, via plants and animals competing for space, to all kinds of
predators that see domesticated animals as easy prey.25 Domesticated forms of different
plants, grasses and animals have taken over large areas of the planet. This has contributed
substantially to the extinction of wild species. One illustrative example is when rain forests
are cut down to grow soy used as fodder to cattle in order to provide us with meat and milk.26
Because of problems like those listed above, Robert Ricklefs concludes that the
economic value of different species for agriculture is not a good basis for protecting natural
24
Luper-Foy 1995 p.97
Almered Olsson 2005 p.57, Ihse 2005 p.67, Williams 1996 p.169
26
Almered Olsson 2005 p.57
25
13
biodiversity.27 Since different species inevitably have different degrees of instrumental value
for us, an anthropocentric instrumental approach will mean that some species will be
favoured at the expense of others. Even if this does not mean that the less valuable species
are turned into oblivion, they will be strongly repressed and diminished. The genetic
diversity of the species will decrease and the repressed species will risk extinction in the
long run.
One good reason for conservation based on our need for food, is that a larger degree of
biodiversity among species used for food (both wild and cultivated) increases the food
security. If one species is hit by e.g. a disease, we can get the nutrients from another
species.28
Two other important aspects of the “nutrient-track” deserve to be pointed out: As we
said in the beginning of this sub-section, all our cultivated species originate from wild
species. This means that the larger the biodiversity, the larger the probability that we will
find new species that can be useful for us. 29 It also means that in order to find new species to
cultivate or to cross breed with our cultivated breeds, or just to transfer genes from, we need
a supply of wild species.30 As an illustration, Norman Myers mentions the great corn blight
in the U.S. that destroyed half of their 1970 corn crop. The problem was dealt with by
interbreeding the cultivated corn with corn from its original growing place in Mexico.31
This seems to be a good reason from the point of view of anthropocentric
instrumentalism not to do things that might lead to the extinction of wild species, and may to
some degree counterbalance the benefits we get from getting rid of competing species.
Another thing we have to consider is that we really do not have any way of knowing today
which genetic material will be useful in the future. This can be seen as an argument to
conserve species “just in case”. I will however return to this strategy in chapter 3.
We should also consider the fact that natural evolution goes on all the time, and
“invents” new properties in both plants and animals, properties that can turn out to be very
useful for us. In order for this evolutionary process to continue, we need to protect not only
the species that are potentially useful, but also the ecosystems in which they live and evolve,
27
Ricklefs 1997 p.598
Almered Olsson 2005 p.54
29
Norton 1986:1 p.117f
30
Almered Olsson 2005 p.54, Aniansson 1990 pp.59,68f,124, Johansson 2003 p.8, Myers 1990 pp.16f,
Williams 1996 p.169
31
Myers 1990 p.16
28
14
and other species that may evolve useful traits in the future or just contribute to the selective
pressure that drives the evolutionary process.32
These last points are of course not just relevant when it comes to food, but also in other
cases where nature contributes to human wellbeing. They are examples of so-called
ecosystem services. The ecosystem services are important for our supply of food in several
different ways. Most pollinators are e.g. wild insects and bats etc.33 Wild species improve the
quality of the soil or help to spread the seeds of plants.34 A substantial degree of biodiversity
is needed to keep the surrounding ecosystems working, to prevent our cultivated species
succumbing to deceases and “pests” etc.35 Monocultures can be very productive but they
cannot sustain themselves for very long without human assistance. They need input of
fertilisers and human intervention – generally powered by fossil fuels.36 The “input”
independently of how it is substantiated must come from somewhere and it is very often
depends on some kind of ecosystem service.
The ecosystem services are also important for other things than food, and I will
therefore discuss them separately and in more detail later.
Before that, I will discuss a couple of other specific uses of other species that might
make it important for us to conserve the species from an anthropocentric instrumental
perspective.
2.3.2. Medicine
Medical benefits are sometimes put forth as an important reason for preservation of
species.37 Many of the medical drugs we use today originate from plants.38 In the future,
these numbers are believed to increase. Most plants have never been checked for medically
32
Norton 1986:1 p.117f
Ehrlich et al 1990 p.102, Millennium Ecosystem Assessment 2005 pp.25f, Johansson 2003 p.2, Myers 1990
p.21f, Prance 1990 p.57, Söderqvist 2005 p.75
34
Johansson 2003 p.27, Johansson, Birgitta 2005:1 pp.8,12, Söderqvist 2005 p.75
35
Almered Olsson 2005 p.55f
36
Norton 1986:1 pp.129f
37
Johansson, Birgitta 2005 2 p 107, Kellert 1986 p.53, Rundlöf 2000 p.13, Sober 1986 p.173
38
Aniansson 1990 p.59, Daily 2000 pp.333f, Ehrlich et al 1990 p.101, Lovejoy 1986 p.17, Ricklefs 1997 p.598
33
15
useful substances,39 and we will probably find many new medical drugs among wild
species.40
Can this account for at least part of why it is seen as morally problematic to contribute
to the extinction of species? The situation seems to be very similar to the one we just
discussed regarding food, and most of the aspects discussed in relation to food are also
applicable here. One difference is that even though the human demand for medicine is large,
it is probably not as large as the demand for food, which means that both the pros and the
cons of referring to medical value are smaller in scope compared to when we refer to the
value of species as sources of food as an explanation for why the causing of extinction is
morally problematic from an anthropocentric instrumental point of view. Another difference
is that even though many medical drugs originate in wild plants, the plants are in general not
utilised in the manufacturing of drugs.41 This diminishes some aspects, but not others. The
domestication and competition aspects as well as the depletion aspect that we brought up in
the previous sub-section are much less of a problem when we talk about medicine. Wild
species are said to be at least as important as future sources of medical drugs as they are as
future sources of food. This means that protecting the basis of future evolution will also be at
least as important in the medical case as in the food case.
I pointed out in the introduction that our intuitions tell us that it is prima facie wrong to
contribute to extermination all things considered. This leaves room for saying that there may
be cases when it is acceptable or even required to contribute to extermination. This is most
salient when we deal with species that carry human diseases, like for instance the black rat
(Rattus rattus), the malaria carrying mosquito (Anopheles maculipennis and other species in
the Anopheles genus), and of course the malaria parasites themselves (a number of species
of the genus Plasmodium) – not to mention several kinds of bacteria.
On the other hand, according to the Millennium report, a larger diversity of wildlife
probably decreases the spread of many wildlife pathogens to human beings.42 If this is
correct, it means that even though the battle against diseases can in some circumstances be
an argument in favour of exterminating certain species, it can also be an argument in favour
of preserving a generally high level of biodiversity.
39
Aniansson 1990 p.59
Aniansson 1990 pp.59,68f, Myers 1990 p.17, Norton 1987 p.27, Regan 1986 p.195
41
Lovejoy 1986 p.17
42
Millennium Ecosystem Assessment 2005 p.31, Myers 1990 p.17
40
16
2.3.3. Materials and fuel
Many of the materials we use in our daily lives come from living organisms.43 Most
notably wood that is used in everything from paper towels to houses, but also plenty of other
materials.44
Wood and other organic products are also important as fuel. 45 More than half of the
fuel used in developing countries comes from wood. In some countries like Tanzania and
Uganda, wood comprises four fifths of the fuel. Even in industrialised countries, wood is an
important source of energy. In the relatively densely forested Sweden, it makes up 17% of
the energy consumption.46 Bio fuel is a renewable energy source that many people see as an
important alternative to the present non-renewables.
In many respects, the harvesting of other species for material is similar to harvesting
them for food. One difference is that once the material is extracted, it can be used for a
longer period of time. Once food is eaten, it is gone and we need a new harvest. One might
think that this makes the pressure on the supplying species smaller when it comes to
material, but unfortunately it is not so. The demand for materials that we find valuable is
often close to insatiable, and our use of material resources is usually very wasteful. Many
species have disappeared and even more are threatened as a result of our “hunger” for
materials. The use of wood as fuel, paper pulp, timber, etc. has e.g. led to the cutting down
of a large portion of the world’s forests. The rainforest in particular. The latter is the world’s
riches ecosystem, and many other species have been brought down in the fall. Cutting down
the rain forest, both in order to exploit the trees, and in order to make room for agriculture,
might even be the most important cause of extinction today.
Apart from wood, a number of animal and plant species are directly threatened because
we value some material they supply. The use of wild animal products is in fact the primary
factor behind the endangerment of many vertebrate species.47 Ivory and rhinoceros horns e.g.
have been very popular among human beings. This popularity has nearly caused the
43
Ehrlich et al 1990 p.101, Ihse 2005 p. 62, Myers 1990 p.17, Norton 1987 p.27
Aniansson 1990 pp.59,68, Daily 2000 pp.333ff, Gerstin 1990 p. 87, Myers 1990 p.17, Söderqvist 2005 p.74,
Tucker 1990 pp.46f
45
Norton 1987 p.27
46
Millennium Ecosystem Assessment 2005 p.31
47
Kellert 1986 p.68
44
17
extinction of both elephants and rhinoceroses.48 Some other species have already disappeared
because they have turned out to give us useful materials.49
Maybe this can be explained as an effect of irrationality rather than as something that
follows from anthropocentric instrumentalism? We are quite often very irrational in our use
of resources, but I am not sure all cases of extinction due to our utilisation of the species can
be explained this way. We discussed this problem briefly in the last sub-chapter when we
talked about food and pointed out that there are probably cases where it is in fact rational
from a strict anthropocentric point of view to use our sources of nutrient in such a way that
some species go extinct. This is probably, at least sometimes, also the case with material and
fuel.
There is another aspect of the use of other species as material or fuel that we have to
take a closer look at. When discussing food, I mentioned that it might not always be
irrational from an anthropocentric point of view to exploit a species to such a degree that it
goes extinct. This may also be the case when we talk about material and fuel. This
conclusion is difficult to establish however. Marian Radetzki believes that there are some
identifiable cases where extinction has had negative economic effects. One such case is the
over-fishing of cod in the north Atlantic. He does not believe that this is always the case
however.50 As we saw, some sources of nutrient can e.g. be substituted by other sources of
nutrient. This is also the case with other resources such as materials of different kinds: One
material can often be substituted by another that does the same job – maybe even better than
the original.51
The possibility of substituting a resource is an important issue in this discussion. The
possibility of substituting one material for another is usually overrated by economists due to
the fact that in economic terms, everything is per definition replaceable by the right amount
of anything else. This is of course not the case in the real world. None the less, materials are
constantly replaced by other materials and this is something that has to be accounted for
when we decide whether a certain species is expendable. This argument goes both ways
however: It is also possible to substitute material and fuel from non-living nature with
material and fuel from living organisms.52 If we try to consider also future generations,
48
Ricklefs 1997 p.599
Prance 1990 p.59
50
Radetzki 2001 p.72f
51
Farber 2000 p.s495f, passim, Luper-Foy 1995 p.97, Radetzki 1990 p.51ff, Radetzki 2001 p.75, SLU 2006:1,
SLU 2006:2, SLU 2006:3
52
SLU 2006:1, SLU 2006:2, SLU 2006:3
49
18
things become more complicated. It is very difficult – not to say impossible – to foresee
what material will in the future be substituted by what other material. We can therefore never
know if a species that does not seem very valuable at the moment will not turn out to be very
valuable in the future.53 To this one might of course answer that it does not matter as long as
there are other materials we can use instead. In fact, since we have the ability to use
materials from the non-living nature, we can always use that to substitute a species.54 We
have e.g. already substituted a lot of the wood used before with metal and various polymers.
It might also be possible to genetically modify species to produce special materials more
effectively than the natural species.55 On the other hand, nature is very “inventive” and as
with medical drugs, it sometimes produces materials that we would not have thought of
ourselves or which would be very expensive to imitate. The economic value of these
materials can probably not motivate a general ban of activities that might lead to extinction
however even though it can motivate preservation of some very important species.
Maybe we can single out some important species and grow them in large
monocultures. Would not that be a more effective and profitable way of getting hold of the
material we need? The economist Marian Radetzki is very optimistic about this possibility.56
After all, this is exactly what we have done with food, and it is in fact utilised in large scale
with trees. This suggestion is very ecologically naïve however. Species do not work on their
own but as parts of a system. A few monocultures clearly work, but only as long as there are
natural environments in the vicinity. To substitute all natural environments with
monocultures and to let all but the directly useful species go extinct would not work. The
question that remains is how much of the natural environment can we turn into monocultures
and how many species apart from the species we harvest do we need? The most probable
answer is that we will not know that until we reach the limit.
If we take the point of view of particular individual human agents, it may be even more
common that extinction follows as an effect of a completely rational behaviour than if we try
to consider the interests of all human beings. Take a look at a simple cost-benefit analysis for
a project. Suppose it turns out when everything is taken into account that the project will
generate an income of $10 000, while the costs will amount to $1 000 000. Is this a good
deal? The way I have described it here, it is obviously not a good deal, but let us make a
53
Lovejoy 1986 p.17
Radetzki 1990 p.51ff
55
Radetzki 1990 p.51ff, Radetzki 2001 p.75
56
Radetzki 2001 pp.74f
54
19
specification: Assume that the income from the project will fall on the decision maker while
the costs will fall on the society as whole. Then the part of the costs that falls on the decision
maker will be very small in comparison to the gain, and instead of making a great personal
loss she will make a personal profit. An act that would look preposterous if all costs were
taken into account may well look like a very good deal for the decision maker(s) if the profit
falls on the latter while someone else has to pay the price.57 Unfortunately, this way of
making decisions is very common. The Millennium Assessment report on biodiversity for
instance points out that many people have gained quite a lot from activities that have
contributed to the disappearance of species, including for example forestry and agriculture.58
It also points out however, that the gain often comes with a cost that has to be paid by
someone else – often poor people – and which is not always factored into the decision.59 This
way of making decisions is in fact very common,60 and the costs are paid both by other
contemporary human beings, by future generations of human beings, and by other species.
Effects that fall upon someone other than the decision maker are usually referred to by
economists as external effects. 61 That they are seen as external is of course a result of the
perspective we assume when we make the decision – viz. an egocentric perspective: Effects
only count to the extent that they fall on the decision maker. As long as decisions are made
along these lines, it does not really matter whether it would in many or even in most cases of
harvesting material, food, medical drugs etc. from other species be more rational from an
anthropocentric point of view to preserve the species. The result will still be destruction if
that is what gives the largest payoff for the individual who makes the decision, i.e. if it is the
most rational thing to do from a strictly egocentric point of view. This may be an important
explanation of many environmental problems. For our investigation, it means that many of
the problems we have found in this and the preceding (as well as the following) sub-sections
may be rooted not in anthropocentrism but in egocentrism. According to anthropocentrism
(the way I use the term in this work), we do have moral duties to our fellow humans, and that
is the basic idea behind using anthropocentric instrumentalism as an explanation of why
causing extinction is a moral problem. Is it possible that the problems that have been
imputed on anthropocentrism are in fact a result of egocentric and not anthropocentric
thinking? Egocentrism and anthropocentrism are in my experience often unrightfully
57
Millennium Ecosystem Assessment 2005 p.38
Millennium Ecosystem Assessment 2005 pp.5f,30,40
59
Millennium Ecosystem Assessment 2005 pp.5,30,40,80 See also Clarke 1995 p.43
60
Luper-Foy 1995 pp.96f
61
Lovejoy 1986 p.21, Radetzki 1990 p.13, Radetzki 2001 p.22
58
20
conflated in discussions about environmental ethics and the distinction between them
deserves to be pointed out. In this case, it is especially important since it means that some of
the problems we have found may actually be the result of egocentric rather than
anthropocentric considerations, and should therefore not necessarily count against
anthropocentric instrumentalism as the answer to our main question.
It is sometimes proposed that the problem of external effects could be dealt with within
a system of rational egoism by constructing a system of property rights. 62 I.e. all resources
should be owned by different legal persons. Usually, it is conceived of as ownership of land
(and water) including animals, plants etc. that inhabits the area, though the resources can of
course also be divided in other ways.
The idea that the problem can be solved by property rights is not universally agreed
upon however – even among economists.63 Even the most ardent advocates of strict property
rights as a solution to the problem of external effects admit that such a system has
limitations.64 One of the problems is that individuals of many species migrate between
different areas and different countries. This means that if one individual property owner
preserves the individuals while they are on her land, someone else might harvest them when
they reach his land.65 Other problems include for instance that it would be very impractical to
distribute property rights over things like species, and that it would probably be considered
too unconventional to gain enough support.66 To come to terms with these problems through
a system of property rights would need a system of ownership of individual animals that
trumps property rights connected to land ownership.
Specialisation may also be one explanation why privatisation has not been able to deal
with the problem of external effects. When a resource is owned by someone with a particular
interest, it is used in a way that best suits that interest while other goods and services from
the species do not count. This may lead to a higher degree of exploitation compared to a
system where many different interests have to co-exist.
There are also other suggestions of how to internalise externalities: Laws, taxes, fees,
etc.67 The best method for internalising external does not concern us here. What is interesting
given our investigation, is whether any such measure can be motivated from a purely
62
Eliasson 2000 p.128,135, Radetzki 1990 p.27ff, Radetzki 2001 p.47, Randall 1986 p.90
Randall 1986 pp.80
64
Radetzki 2001 p.49ff
65
Lovejoy 1986 p.24
66
Randall 1986 p.90
67
Hermele 2002 p.177,183,187f
63
21
egocentric point of view and still comply with the wider anthropocentric perspective. It is
sometimes claimed that restrictions on our selfish behaviour can be rationally agreed on (at
least hypothetically) for purely egocentric reasons.68 As long as I am the only one making
decisions in the way I outlined above it will be rational for me from an egocentric point of
view. If everyone (or at least a substantial number) makes their decisions along these lines
however, the total sum of costs imposed on me by them will be larger than the profit I will
get from making decisions that way. Therefore, it seems to be in everyone’s interest to agree
on a system that does not allow for this kind of decision making.
If this claim is correct, the distinction between egocentrism and anthropocentrism is
not important – at least when we deal solely with intra-generational relations.69
Whether such a system really works, and whether it always or even in general makes it
irrational from an egocentric point of view to cause extinction, remains to be shown
however. The idea of rational egoism as a basis for moral principles as such is also very
controversial. I will not go any deeper into this debate here since it would take us too far
from the main purpose of the investigation. I will just point out some problems that are
particularly relevant in connection to our investigation. One such problem is that the way of
making decisions illustrated above is very common, and it is hard to believe that it would be
that common if it were irrational from an egoistic viewpoint. Another difficult problem is
that even though in the above example it would be more rational to adopt a system that
everyone follows as compared to a situation with no agreement at all, it would be even better
for each individual to break the agreement: A system where no one generates personal profit
in a way that also generates large costs for the rest of society is better for everyone compared
to a system where everyone does it. It is however even better for each individual to continue
making a profit this way while everyone else does not. If everyone else goes on making a
profit on other’s expense, it is even more important for each individual to go on and make
profit any way they can even when it imposes a great cost on others. I.e., we are in a
prisoner’s dilemma type of situation.
A very important problem surrounding the notion of a contract between selfish
individuals is that it presupposes a situation with equal bargaining power. Such an
assumption is far from realistic – if nothing else, it is effectively frustrated by evolution. The
lack of such equality in the real world is probably an important explanation of why in so
many situations it is in fact rational for the egocentric to make decisions that imposes the
68
See e.g. Luper-Foy 1995 p.97
22
costs on others. This ought to be the case both for those with much power and for those with
very limited power. Those with much power can get away with quite a lot without the risk of
being subjected to the same treatment. Those with limited power do in some situations have
to disregard the effects on others just in order to survive in the short term. As we will see
later, it is also quite clear that this aspect is particularly severe when we deal with intergenerational relations – where the now living have all the power while future generations
have absolutely no power.
What all of this has shown us is that it is probably after all often rational from the
perspective of a rational egocentric agent with a limited lifespan to engage in projects where
the cots are larger than the profit as long as the costs are external while the profit falls on the
agent. This in turn shows us that at least some of the problems we have found should
probably be imputed to egocentrism instead of anthropocentrism. This is good news for the
advocates of anthropocentric instrumentalism as an explanation to why it is morally
problematic to contribute to the extinction of other species.
We also have to remember that even if some external effects could be dealt with within
an egoistic framework, the case for conservation would be even stronger if we also admitted
that we have a duty to consider the interests of other human beings. We therefore have to
admit that independently of the problems pointed out above, it is always – for purely
numerical reasons – the case that anthropocentrism gives us a stronger reason for
conservation than egocentrism. If we allow for duties to other people, he scope will also be
wider as I pointed out when discussing other species as source of food, since people have
different tastes and live in different environments with different conditions etc. This means
that we need a larger selection of species for our consumption.
I do not believe that all problems we have found – and will find – can be pinned on
egocentrism however. It would probably be naïve to believe that we could blame
egocentrism or irrational behaviour (from the point of view of anthropocentrism) for all
cases of depletion of material resources that cause extinction of species even though they
could probably be blamed for many.
We also have to remember that if we would accept that not just human beings, but also
non-human species and individuals have moral status, the case against the type of decisionmaking seen above would be even stronger. We showed above that even if extinction would
be bad from the point of view of egocentrism, it would be even worse from the point of view
69
I will return to the question of inter-generational issues in a later chapter.
23
of anthropocentrism. In the same vein, if we take one more step and accept a nonanthropocentric answer to the question of who has moral standing, then we have to admit
that even more “payers” are paying even larger costs for our profits (often much larger costs
since other species and individuals of other species are more strongly affected). This means
that analogously we would find that even in cases where anthropocentrism favours
conservation, non-anthropocentrism provides an even stronger argument for conservation.
Therefore, if the scenario I have depicted above gives support to anthropocentrism rather
than egoism as an answer to why extinction is wrong, it clearly gives an even stronger
support to non-anthropocentrism rather than anthropocentrism as an answer to this question.
2.3.4. Indicator species
Some species are important as indicator.70 I.e. they are particularly sensitive to some
type of environmental change which if allowed to continue will affect us as well – directly or
indirectly via other species or via a dramatic change of the ecosystem.71 These species can
therefore be used as a kind of early warning system (in a way like canary birds were used in
mines as indicators of a low oxygen level). This use gives certain species an extra dose of
instrumental value for us.
This may look rather cynical, and seen in a broader (non-anthropocentric) perspective,
it is. It is nothing we need to worry about for the moment, since we are investigating how far
we can get with a purely anthropocentric approach. The conclusion must be that the
“indicator-track” is a clear case – although of a limited scope – of value that can be a part of
an explanation of why extermination is a problem from an anthropocentric instrumental
point of view: It is a foretaste of what will happen to us, and if we do not want that to happen
to us, we need to do something about the cause of the extinction of the indicator species. If
we do not do that, it will harm us and is therefore immoral.
70
71
Aniansson 1990 pp.59,116f, Ricklefs 1997 p.600
Johansson, Birgitta 2005 2 p.106
24
2.3.5. Some non-destructive uses of other species
Not all ways of using nature to promote human values are destructive. Non-human
species also have instrumental values for us in ways that are best utilised by letting them be.
I am thinking of values like recreation, inspiration, aesthetic experiences, silence, solitude,
psychological amendment, knowledge of how the world around us works, a sense of history,
identity, national or regional pride etc.72
One could also mention things like religious worship, but I will not include that kind of
value in the investigation since I want to avoid grounding the value of species on
cosmologies or views of nature that are not supported by science.
Someone might be tempted to argue that some of the values mentioned above – such
as aesthetic value – are in fact intrinsic and not instrumental. We could take time from the
investigation discussing whether for instance aesthetic values are instrumental or intrinsic,
and whether the value is in the object or in the experience. I will cut that discussion short
here however simply because I do not think it is essential for our purpose. It is reasonable to
assume that other species can have intrinsic value for human beings in many different ways,
and I will investigate that possibility elsewhere.73 Here when I talk about aesthetics and other
values of the type listed above, what I have in mind is the instrumental value of the species
as a means to aesthetic, recreational or other values. A tree as a motive for a painting or
inspiration for a poem e.g. or an ant as an object of study that leads to increased knowledge.
The knowledge, the painting and the poem may in their turn have intrinsic value and/or
instrumental value in relation to something else that has intrinsic value etc. Either way, the
value of the species is purely instrumental in relation to knowledge, aesthetic value etc. that
we might gain from it. When the Millennium report talks about spiritual and cultural values,
these types of value are not considered intrinsic values, but are seen as instrumental in
relation to for instance social stability.74 (It is not clear whether social stability in turn is seen
as an intrinsic value.) This means that the species have instrumental value in relation to some
other instrumental value, which in turn is instrumental in relation to something else, and
maybe the chain continues even further.
72
See e.g. Aniansson 1990 p.57, Daily 2000 pp 333f, Farber 2000 p.s494, Gärdenfors 2005 p.119, Johansson
2003 p.24, Kellert 1986 pp.52f, Luper-Foy 1995 p.97, Millennium Ecosystem Assessment 2005 pp.31f, Melin
2001 pp.59f, Norton 1987 pp.15,18,27, Regan 1986 p.195, Sober 1986 p.173Stenmark 2000 p.34, Söderqvist
2005 p.75
73
To be published in the next book containing the whole investigation.
74
Ihse 2005 p.65ff, Millennium Ecosystem Assessment 2005 p.31,32, Nordlund 2000 Passim
25
Can these types of non-destructive utilisation of other species be a part of an answer to
our question? It seems quite clear that the values mentioned above are important to people,
and it also seems quite clear that nature or different objects in nature can produce these
values. Natural environments with much variation seem to improve the quality of human
life,75 and it is well known within environmental psychology that many people prefer
environments with elements of nature.76 In an investigation of attitudes regarding
biodiversity among the inhabitants of Kristianstad in southern Sweden, non-destructive
values turned out to be among the most widely held reasons for protecting biodiversity.77
That the values are non-destructive gives them a much stronger position as potential
bases for preservation. On the other hand, there is less demand for these values compared to
other values we have discussed (food, medical drugs, material and fuel). This means that in a
trade-off situation, they risk ending up quite far from the top of the priority-list. You can
hear from time to time that it is impossible to enjoy a beautiful landscape with an empty
stomach. In other words, in order to appreciate more subtle values, you need to first fulfil
your more basic needs. This is probably not universally true, but it probably contains at least
a large element of truth. At least, willingness to pay for this kind of values seems to increase
with higher income. This in turn has fuelled a debate about protecting species. It happens
e.g. that a preservation project with a good intention ends up as a conflict between the welloff who can afford the “luxury” of protecting aesthetic, historical etc. values, and the less
well-off who want to harvest the species for food or fuel etc. This is particularly salient when
the preservationists are Westerners whereas the species they want to preserve are located in
the third world.78 In this situation, the values we are discussing will not easily counterbalance
the exploitative interests from a purely anthropocentric instrumental point of view.
Another problem with the kind of values we are discussing here is that they have a
tendency to get downplayed or even neglected in trade-offs. Anders Melin distinguishes
between two types of anthropocentrism. One that accepts this kind of values (which he calls
“non-material values”) and one that does not. He calls the former kind “ideal
anthropocentrism”, and the latter kind “material anthropocentrism”.79
75
Norton 1986:1 p.129
Johansson, Maria 2005 p.96
77
Johansson, Maria 2005 p.99
78
Andersson 2005 p.91, Sober 1986 p.191
79
Melin 2001 p.23
76
26
One reason for why the non-material values tend to get downplayed is probably that
they are difficult to assess in monetary terms. 80 This in turn is probably partly due to their
relative abstractness: Food or timber is easier to see as a real commodity compared to
inspiration or relaxation. I believe there is also another explanation: Things like food and
timber are easier to trade since they represent roughly the same value for most people, while
the values we are discussing here are more personal.
One way in which the non-destructive values can have economically measurable value
and which is receiving more and more attention is in the form of tourism. It has become
increasingly clear in most societies that the type of value we are talking about here
represents a large economic value through its ability to attract tourists. In the next subsection, we shall take a closer look at this special case of combined experiencevalue/economic-value that might help tipping the scale in favour of preservation in at least
some cases.
2.3.6. Tourism
Tourism is often put forward as an important instrumental reason for protecting
species.81 A species can provide instrumental value for us humans both because it provides
us as tourists with inspiration, recreation and the other non-destructive values discussed
above, and because it generates income by attracting others as tourists to our area. The
tourist and travel business is the world’s third largest branch of business.82 Nature tourism in
turn is one of the fastest growing branches of tourism and is a large source of income in
many countries – not least in poor countries or areas.83 The income from tourism tends to
provide a very strong and very direct incentive for protection even for people who would not
otherwise care for nature preservation, or would even be against protection of at least some
species.84 This goes for instance for big predators that might be a threat to human beings or
their life stock, but that are also very attractive to tourists. In many cases, both these and
80
Ihse 2005 p.70
Andersson 2005 p.93, Hellmark 2004:1 pp.133f, Johansson, Birgitta 2005 1p.8, Walsh 2004 p.65
82
Olsson 2004 p.35, Prosser 1995 p.118
83
Charter for Sustainable Tourism1995, Hanneberg 2004 p.59,63, Hellmark 2004:5 p.51, Lindén 1990 p.73,
Ricklefs 1997 p.599
84
Doole 2005, Hanneberg 2004 p.64,71, Hellmark 2004:6 p.75, Olsson 2004 p.43
81
27
other animals are actually more economically valuable alive as tourist attractions, then they
are dead.85
Another gain from a protection perspective is that nature tourism might – hopefully –
also influence the tourists by increasing their interest in the animals or plants they see
(maybe even in species they did not come to see but as a bonus get to see anyway). It might
also increase their understanding of the communities in which the species live and make
them more sympathetic towards conservation in general.86
There is a risk that tourism also contributes to the destruction however,87 which is why
some initiatives have been developed to counter the environmental impact of tourism. Both
the UN and other organisations have held conferences and compiled policy documents
aiming at sustainable tourism.88 The World Tourism Organization (WTO) discusses the
matter actively, and there are several different types of labelling of environmentally friendly
tourism – often referred to as “eco-tourism”.89 Obviously, the big bulk tourism can never be
in the form of eco-tourism, and even eco-tourism is not without negative impact. Just getting
to the destination often requires using plenty of energy, mostly in the form of fossil fuels.
This in turn means plenty of pollution including carbon dioxide that increases the
greenhouse effect with a tremendous impact on the environment, including other species.90
Setting the standards for what is to count as eco-tourism is not easy, and there will
certainly turn up borderline cases where it is difficult to say how much encroachment is
acceptable in order to stay in business.91 It is easy to fall victim to the “salami-principle” –
i.e. finishing off the habitat one slice at a time, where every single slice is not in itself a
cause of concern, and where it is impossible to say precisely at which slice we have gone too
far.
85
Doole 2005, Hanneberg 2004 p.64, Johansson 2005:2 p.110
Hellmark 2004:5 p.48, Hellmark 2004:6 pp.75,76
87
Delin 1997 p.9, Hanneberg 2004 p.69, Doole 2005, Hellmark 2004:2 p.25, Hellmark 2004:3 p.22, Hellmark
2004:6 p.74, Karlsson 2004 p.7, Olsson 2004 p.35,38,42, Prosser 1995 p.119, World Conference on
Sustainable Tourism1995, World Ecotourism summit 2002 p.2
88
Europarc Federation 2002, Prosser 1995 p.119, World Conference on Sustainable Tourism1995, World
Ecotourism summit 2002
89
Helllmark 2004:3 pp.15ff, Hellmark 2004:6 passim,
http://www.ecotourism.org/index2.php?ecotourism_associations, http://www.gdrc.org/uem/eco-tour/ecotour.html, Karlsson 2004 p.7, Olsson 2004 p.41f
90
Hellmark 2004:1 p.134, Hellmark 2004:6 p.77, Olsson 2004 pp.39f
The Québec convention on ecotourism in fact calls for regulatory mechanisms regarding transport in
connection with ecotourism: World Ecotourism summit 2002
91
Doole 2005, Fall, Carl-Axel 2004 passim, Hanneberg 2004 pp.59,69f, Hellmark 2004:6 p.76, Olsson 2004
p.43
86
28
An inherent problem with eco-tourism is that it can never be allowed to be too
successful measured in number of tourists. With too many tourists, the wildlife experience
will inevitably be lost even if the impact on the environment can be held at a low level. It
will therefore never be able to include the large masses of tourists.92 It may, however, be able
to influence mass-tourism by showing that it is possible to pursue tourism in a nondevastating form, and by influencing mass-tourism to raise their standards of consideration
for the environment, even if their standards cannot be as high as that of the certified ecotourism. Some believe that this might be the most important gain from eco-tourism.93
One problem with tourism as an incentive for protection is that it is selective. Only
some species are attractive enough for people to spend money and time to see them.94 This
means that tourism can only account for the instrumental value of a limited number of
species, but, as pointed out above, one spin-off may be that tourists widen their interest to
include a larger number of species. Therefore, in order to entice the customers to come back,
the enterprises must consider a larger number of species than the original “target species”. It
is also obvious that the popular species cannot survive in the wild in a vacuum. They need a
habitable environment, which includes a large array of other species that thereby indirectly
also becomes instrumentally valuable to us.
One risk we have to consider regarding both eco-tourism and other forms of tourism is
that the tourists get an oversimplified or maybe romanticised view of the area they visit. 95
The opposite is of course also a risk: That the inhabitants of the area get an overly
romanticised view of life in the west by continually seeing rich westerners on vacation.
Apparently, tourism too has pros and cons as a reason for preservation. Like many of
the previously suggested instrumental values, it is partly self-defeating in that it will destroy
its own basis if it becomes too popular. This is a strong argument for proceeding with
caution, but it might not be strong enough in a trade off between non-exploiting (or more
correct “less-exploiting”) eco-tourism and more exploiting mass-tourism.
The effect on people’s minds may be the most important contribution of tourism. This
change of mind can however as we saw go in both directions. Things and events that have
the effect of changing people’s minds concerning what they value have been labelled
“transformative value” by Bryan G. Norton, and it might play an important role of its own
92
Doole 2005, Fall 2004 p.155, Helllmark 2004:1 p. 134, Hellmark 2004:3 p.23, Hellmark 2004:5 p.48,
Hellmark 2004:6 p.77, Olsson 2004 pp.38f,45
93
Hanneberg 2004 pp.70f, Hellmark 2004:1 p.134, Hellmark 2004:6 p.75
94
Ricklefs 1997 p.600
95
Doole 2005, Hellmark 2004:3 pp.22f, Olsson 2004 p.42
29
when it comes to accounting for our intuitions concerning extinction. We will therefore
devote a section of its own to that kind of value later in the book.
2.4. Trade off96
We have seen that many species do have instrumental value for human beings, but we
have also seen that it is not always easy to tell whether this value is strong enough to explain
the moral indignation when our encroachments in nature cause species to go extinct.
Encroachments that contribute to the extinction of other species are done for a reason, and
the instrumental value of the threatened species has to be weighed against the value of the
things we will have to abstain from if we are to protect the species. I.e. the instrumental
value of a species has to compete with other instrumental values.97 To preserve species can
also be quite expensive, 98 and it is at least not inconceivable that in a number of such
situations the instrumental value of the destructive alternative may be greater for us than the
instrumental value of the destructed species. Even though this in many cases may be a matter
of short-sightedness,99 we cannot assume that it is always so. It might be that the alternative
that contributes to extinction is sometimes more instrumentally valuable even if we consider
the long-term effects.
Alan Randall is conservatively optimistic regarding the outcome of trade-offs between
human values that favour preservation and human values that favour exploitation. He argues
that cost-benefit analyses100 often turn out in favour of the “pro-environment” alternative.101
He does not (understandably) attempt to estimate how often this happens, but he draws the
96
I am aware of the immense problems of finding a common unit in which to compare different goods. To
transform all values into monetary value is something that many economists are working on not least when it
comes to different kinds of value in nature. The problems involved are great and I do not take stand here on
whether it is possible to solve them. In this section as well as in all other cases of comparison between different
values I will just assume that it is possible to compare the intrinsic value of different goods on an intuitive
level.
97
Johansson, Birgitta 2005:1 pp.8,14,17, Melin 2001 p.114
98
Bodegård 2005 p.22, passim, Johansson, Birgitta 2005 1p.8,9, Melin 2001 p.15,114
99
As pointed out by e.g. Ricklefs 1997 p.598
100
In the cases Randall discuss, benefits are stated in terms of “willingness-to-pay” and costs are stated in terms
of “willingness-to-accept”.
101
Randall 1986 p.95. “Pro-environment” can of course mean different things, but since the paper is about
preservation, I assume that the meaning of the term in the context it appears is not totally irrelevant to our
question.
30
relatively modest though very important conclusion that “… commercial interests do not
hold a monopoly on economic arguments.”102
Norman Myers supplies us with a real life example of a fruit called ‘durian’. It is
native to Southeast Asia, and is said to be most exquisite. It contributes (1990) with $100
million a year to the local economies. The problem is that it is pollinated by one particular
species of bat, which is threatened by different kinds of human encroachment. The swamps
where the bats find most of their food (apart from the nectar from the durian tree), is claimed
for human buildings. Human constructions also threaten the caves where the bats live since
the caves are exploited for limestone used to make concrete.103
In order then to find out whether the disappearance of the tree and the bats is a bad
thing according to anthropocentric instrumentalism, we have to weigh the positive effects of
the buildings against the negative effects of losing the durian fruit. The negative effects for
human beings are that many people will no longer be able to enjoy this exquisite fruit, and
that the local economies will lose about $100 million a year. The positive effects for human
beings are not clearly spelled out by Myers, but there ought to be a non-negligible economic
gain. People in the area will get access to new apartments, and there will be quite a few jobs
on the line. Given the information we have got, it is not possible to say what the total result
will be. It illustrates however that it is seldom quite obvious whether conservation or
exploitation is the most rational option in a particular situation from the point of view of
anthropocentric instrumentalism. This is obviously a problem for the usefulness of this
theory when it comes to explaining why extinction is generally seen as morally problematic
– especially since this intuition often appears as very clear.
Some of those who have thought about the subject of trade-offs between preservation
and other values are quite pessimistic:
Thomas Lovejoy believes that a choice between the economic value of a particular
species and the economic value of an encroachment turning out to favour the species does
not happen very often.104
Petra Andersson considers it “not unbelievable” that if we cut down the forest of the
Parc des volcans national park in Rwanda, and have it cultivated by human beings, the total
sum of happiness would be larger than if we keep it protected.105
102
Randall 1986 p.95. By ‘commercial’ I assume the author in this context means something like
“exploitative”.
103
Myers 1990 p.21f
104
Lovejoy 1986 p.22
105
Andersson 2005 p.91
31
The economist Kenneth Hermele believes that there is an opposition between
economic growth and species preservation, at least in a short perspective, but he indicates
some pessimism even in the long turn.106
On top of that, Bryan G. Norton – who in general is positive towards the idea that
anthropocentrism favours species preservation – points out that in a future with more
humans, the negative instrumental value of a species that e.g. competes with human beings
for food or habitat, will increase and maybe even override its positive instrumental value.
Therefore, anthropocentric instrumentalism will according to Norton be a continuously
weaker reason for preservation.107
The scenarios of the Millennium Assessment report on biodiversity show that many of
the things we need to do in order to counter human poverty and enhance development, are
likely to further impoverish biodiversity.108 The report indicates that the development paths
for relieving today’s poverty, hunger and health problems for human beings during the next
50 years also mean continued loss of biodiversity (even though the worst scenario in terms
of achieving the human welfare goals is also worst in terms of for instance species loss).109
This means that in at least some situations where we have to choose between preservation
and extinction, the alternative that implies extinction will from an anthropocentric
instrumental point of view actually be preferable.
The Millennium assessment group also points out that even though it is often possible
for a community to make money through preservation by e.g. ecotourism or a sustainable use
of forest products, the communities would in general make more money by exploiting the
area in a way that can lead to a loss of species.110 They also believe that if we only consider
what they call “utilitarian”111 reasons for protecting biodiversity, we will actually get by with
a lower diversity than we have today.112 This means that even though we will need some
species, we will apparently not need all of them.
The millennium assessors conclude that win-win situations may not be as common as
has been hoped in situations where both conservation and development is at stake. They also
106
Hermele 2002 p.153
Norton 1982 pp.18,21f
108
Millennium Ecosystem Assessment 2005 p.77
109
Millennium Ecosystem Assessment 2005 p.15
110
Millennium Ecosystem Assessment 2005 p.12,90 The same thing is indicated by Doole 2005 describing a
visit to a Chinese village where the inhabitants have exchanged logging for ecotourism. They manage to make
a living from ecotourism but their income had fallen as a result of the change. The number of tourists where
growing and the village leader believed that they would gain income in a longer perspective.
111
‘Utilitarian’ in reports like these generally means ‘instrumental’, and should not be confused with the normal
meaning of the term ‘utilitarian’ in ethics.
107
32
tell us that conflict between the two is more common than interplay, and they finally claim
that it would be naïve to believe that we can always have both. The Millennium assessors
therefore advice us to think more of how to make trade-offs between development and
species protection.113
This list of pessimistic assessments concerning the outcomes of trade off-situations
shows that we may do well in being careful in what we can expect from anthropocentric
instrumentalism as a basis for preservation.
Norman Myers writes that our lifestyle with “cheap supplies of hamburger beef,
hardwood timber, and other tropical forest products” is a large threat to the rain forest.114
This goes not just for the rain forest, but for many other habitats and their species as well.
Since our demands for food and other utilities from nature historically have been the main
cause of human induced extinction, maybe references to these demands are not the best basis
for a defence of biodiversity?
On the other hand, Myers also claims that
the continuing decline of tropical forests [and we might add other ecosystems and
species] will eventually levy a heavy price on our temperate-zone lifestyles, through
the loss of many potential sources of new foods, drugs, industrial raw materials,
even sources of energy.115
This is also an important point that seems to be right in line with the statements by
Sörlin in the beginning of this chapter. It also underlines the point we have made earlier that
it is not necessarily always the case that our wasteful use of natural resources follows from
anthropocentric instrumentalism. On the other hand, we could not exclude that what looks
like short-sighted and wasteful use may in some cases actually be the most rational from a
strictly anthropocentric instrumental viewpoint. In order to be able to continue to utilise
other species we have to be aware not to use them faster than they can reproduce themselves.
If we demand large quantities at a low cost of whatever it is that a certain species supplies,
and the species cannot sustain that demand in the long term, we have to ask another
question: Is it better to satisfy the demand to a high degree for a short time, or to satisfy it to
a lower degree for a longer time? The answer is not as obvious as proponents of a “wise use”
112
Millennium Ecosystem Assessment 2005 p.7
Millennium Ecosystem Assessment 2005 p.74
114
Myers 1990 p.22
113
33
of natural resources often assume. It looks quite obvious that the latter option is the best one
in the long term especially if the total amount of good we can get from the species in the
long term is much larger than what we can get if we choose the more “short-sighted”
alternative. If we take the actual behaviour by consumers and suppliers as an indicator of
their interests however, the answer seems to be that they quite often prefer a high degree of
satisfaction of a demand for a short time rather than a low degree of satisfaction for a long
time. This could of course be explained by saying that people are irrational, but it might also
be explained by the instability of people’s preferences – at least of their instrumental
preferences. There may be different ways of satisfying our intrinsic preferences, and if the
favoured ways of satisfying the consumers’ preferences shift – as we know they do – then
our case for conservation will turn out to be weak. The durian fruit mentioned by Myers may
be exquisite, but there are many delicious fruits, as well as other means of pleasing our taste
buds, and human taste tends to shift. So maybe in some situations it is best from an
anthropocentric instrumental point of view to get as much as possible out of a species while
it is in fashion even if it means that it will disappear eventually.
One aspect that may be important is that the less common something is the higher is
usually the price. This in turn means that it is often in fact more economically worthwhile to
exploit threatened species. 116 On the other hand, the exploitation also often means a larger
cost since it takes more effort to collect the last specimens of a species. This is not always
true however. Lovejoy uses whales as an example of this phenomenon, but not all species
are scattered over the world’s oceans. Technological improvement should not be
underestimated either when it comes to increasing our capacity to exploit smaller and more
scattered resources.
It seems that the answer to whether sustainable use or fast exploitation of a species is
the best option from an anthropocentric instrumental point of view depend to a large degree
on the nature the instrumental value of the species – and especially on whether it is
exchangeable. Some demands can only be satisfied in one way. We should therefore
distinguish between exchangeable and non-exchangeable instrumental value. Exchangeable
instrumental value comes in degrees. The size of an instrumental value is in part determined
by the size of the intrinsic value it serves as a means to, and in part of how effective a means
it is to promote this value, but it is also determined by the availability and effectiveness of
alternative means to promote the same intrinsic value. Non-exchangeable instrumental value
115
Myers 1990 p.22
34
has only the first dimension: Its value is decided by the size of the intrinsic value it is a
means to.
Some things of course have both instrumental and intrinsic value, and many things
have instrumental value in relation to more than one intrinsic value. Often we are also
dealing with chains of instrumental value. Finally, some (or most) things seem to have both
positive and negative values that have to be weighed together.
The fact that there are non-exchangeable functions does not necessarily mean that
there are non-exchangeable species, but it is not implausible that there are. To identify them
will however probably be quite difficult and it will certainly not apply to all species.
One thing that has to be remembered when we talk about exchangeability is that it
excludes the possibility of assigning a monetary value to non-exchangeable entities. To
assign monetary value to something implies that we have also decided how many or how
much of some other entity it takes to achieve the same value. If we put a monetary value on
breathable air, no matter how high, it is always possible to accumulate enough of something
with a lower value that can outweigh the value of the air. This would be absurd. If we assign
the value of $1 000 000 000 to breathable air we would in fact be able to say that we could
substitute the breathable air if we instead manufacture one billion copies of a $1 pen. That
would obviously be absurd since if we do not have any air to breath, we cannot utilise the
things we have manufactured anyway. The only thing that could replace breathable air would
be something that can produce the same benefit, not something that just produces something
else of equal economic value, and it is very unlikely that we could find something that can
give us the same benefits as clean air.
This complicates further the already complex process of making a rational trade-off
according to the principles of anthropocentric instrumentalism. My points are that it is hard
to know the outcome of all trade-offs between acts that preserve and acts that contributes to
extinction, and in some instances it might not even be practically possible. When it is
possible, we can however expect that a number of trade-offs might favour encroachments
that contributes to extinction if we look at them from a purely anthropocentric instrumental
perspective even though they intuitively seem at least morally problematic, and often as
clearly wrong. This in turn seems to weaken the usefulness of anthropocentric
instrumentalism as a way of answering our question.
116
Lovejoy 1986 p.21
35
One thing we have to consider though is that there is no consensus in ethics that the
rather utilitarian way of calculating we have used in this chapter is the correct way of making
ethical decisions. If we accept a more deontological approach to ethics, we have to consider
the fact that sometimes the best total trade-off can imply unacceptable costs to certain
individuals. It might for instance at some occasions be the case that a project that leads to the
extinction of a species turns out to give the best total outcome, but also turns out to be a
death blow to a small rain forest tribe whose life is dependent on the species. In that case, it
might still be the case that extinction is deemed to be immoral. On the other hand, this
argument can sometimes also go in the opposite direction. It might e.g. turn out that a certain
insect species supplies humanity on the whole with more positive than negative effects, but
at the same time causes great havoc for the local populations of humans. In cases like that a
deontological ethic may conclude that the best thing to do after all would be to exterminate
the species.
2.5. Choice value
The Millennium report points out that the stability of ecosystems is apart from its other
values, also important for what they call “freedom of choice and action”, defined as
“opportunity to be able to achieve what an individual values doing and being”.117 We can call
this type of value ‘choice value’ since it gives us a larger array of choices. The definition of
‘choice value’ will thus be: ‘The instrumental value something has because it increases the
array of choices for human beings.’ Having a large array of choices can have both
instrumental and intrinsic value. For many it seems to have a quite high degree of intrinsic
value.118
Bryan Norton reasons along the same lines as the millennium assessors, but focuses
more directly on the choice value of species. He points out that if we sacrifice a species for
short-term gains, we also sacrifice what he calls “future options of the human race”.119
The value – both intrinsic and instrumental – of having a large array of choices may be
an important reason for why it is seen as immoral to contribute to the extinction of species.
117
118
Millennium Ecosystem Assessment 2005 pp.19,25,30
See e.g. Daily 2000 p.335
36
Losing biodiversity tends to imply a loss of choices.120 In agriculture, larger biodiversity
gives the farmers a wider array of choices with regard to future crops. Thereby the farmers
also become less vulnerable to changes, and gain a sense of control. We could argue in the
same way concerning most of the usages of other species. A larger selection of species gives
us more options to choose from. This is interesting since it gives us a way of dealing with
one of the more tricky problems we have encountered in the previous chapters, viz.
exchangeability. We noted that there might be non-exchangeable species, and there certainly
are non-exchangeable functions, but we have also noted that some goods can be supplied by
more than one species, and even that some things like for instance many materials can be
substituted by non-living substances. We can call this ‘the redundancy problem’ since it
indicates that some species may be redundant. If a large array of choices has a value
however, the redundancy problem will be much smaller. A species that has an instrumental
value and is exchangeable will thereby automatically also have a choice value through its
contribution to our array of choices. It will therefore never be really redundant even if there
are several other ways of getting hold of the same good. If we lose the species, we have still
lost choice value. The service can be upheld even if one of the species that supplies it
disappears, but our array of choices between different suppliers of the service is diminished.
Redundancy will therefore be something positive by giving us a larger array of choices.
On the other hand, in many cases we lose species because of a process that generates
something else that increases our array of choices in another way or another area. Money is a
kind of universal instrumental value. Money can be transformed into many kinds of
instrumental or intrinsic values. This means that money is in a way the “ultimate choice
value”. This makes money a very difficult competitor in all cases of trade-off when we strive
for a large array of choices. In today’s society it seems like this particular quality in money –
its exchangeability into most other values – has made it the most sought after commodity.
We spend most of our lives giving other people what they want in order for us to get – not
things we value intrinsically – but money.121 We can then exchange the money for the things
we want. This looks like a detour, but instead of aiming directly for what we want, we go via
money not only because we know that we can get more of what we value by earning more
money (we could achieve that without going via money), but because the money represents
119
Norton 1987 p.63
Millennium Ecosystem Assessment 2005 p.32
121
Money can of course be valued intrinsically, but here we will only talk about its instrumental value, and in
particular its choice value.
120
37
many different values. If we exchange a horse for a cow we have got a cow, but if we
exchange a horse for money we can chose what to buy for the money. By exchanging a
service or a commodity for money instead of another service or commodity, we gain choice
value. Exchanging goods or services for money has been a manifestly successful way for
individuals to increase their array of choices. So successful even that it has a tendency to
make people forget about the areas where our choices get diminished by the process.
Sometimes it seems that we are so eager in our hunt for “the ultimate choice value” that we
do not notice the intrinsic or instrumental values we lose along the way.
The question we have to answer is if the loss of choice value in the form of lost species
is so bad from an anthropocentric instrumental perspective that encroachments that
contribute to the extinction of species can be seen as morally problematic for that particular
reason. In the light of what I just said about money as the ultimate choice value, it can be
difficult to maintain that we all in all lose more choice value than we gain by so to speak
“transferring species into money”.
One thing that talks in favour of our case is the quite obvious fact that in order for
money to keep its choice value, the things we like to buy for the money have to exist. The
choice value of money is only as large as the number of things you can buy with the money.
That is why printing more money leads to a decrease of the value of the currency. In the
same way, the more things we can buy with the money, the larger the money’s choice value.
We therefore have to distinguish between (A) situations where I get money from you
in exchange for giving you my work or some existing goods or goods that have been
transformed in a reversible way – and (B) situations where I get money through an act that
leads to depletion of something else (like a species). In both cases, I increase the number of
options for my own part by getting more money to choose how to spend. The difference is
that in (B), I decrease the choice value of money as well as the total choice value for
everyone (including me). I take away one thing from the world permanently and thereby
make it impossible for everyone to utilise it.122
When you make money in a way that causes a species to go extinct, you may gain in
net choice value for your own part since the choice value of the money may be larger for you
personally than the choice value of the species would have been. You are however also
decreasing the number of things that the money represents (in the form of choices of food,
material, aesthetic experiences etc.) for everyone. You therefore in one way decrease the
122
Adapted from Williams 1969 p.173
38
general choice value of money by taking away a species. It is my impression that this aspect
is often neglected in trade-off situations even when choice value is considered.
Furthermore, when you take away a species you take it away forever. It is sometimes
argued that encroachments that destroy nature but increase economic growth may not be a
big problem since it is always possible to use the money we gain to repair the damage.123
This is not possible when we talk about extinction – at least not yet and it might never be.124
There are attempts to resurrect extinct species by cloning, but there has not yet been
any success. Even if it will eventually work, there are other problems however. One
important limiting factor is that cloning is only possible if there are preserved DNA. Another
problem is that some species are so to speak “more than their genes”. I.e., some of the
information that govern their behaviour (and thereby among other things constitute their role
in the ecosystem) is stored not in their genes but in their brains, and is passed on from
generation to generation by the older animals showing the young. This information will
inevitably be lost even if the information in the genes can be retrieved. An additional
problem is that the environment might have changed while the species was gone. This means
that it may not be possible to reintroduce it. Even reintroductions of species that are gone
from one area but still exist in other areas has a low success rate and are very costly.125
Reintroduction of species that have been extinct, and have therefore not had the chance to
evolve during this time must reasonably be even more difficult and may even cause new
problems since it in practice means that we are introducing a species that is not adapted to
the system and the system is not adapted to.126 If the species on the other hand had existed in
the environment during the changes, it might have been able to adapt (unless of course the
changes go too fast).
Because of these and probably also other hitherto unknown problems, reviving species
through cloning may never be a real alternative on a larger scale even if it is technically
possible. The irreversibility of extinction is thus something we must consider a reality. There
is (in general) no such thing involved when we lose money. If we miss an opportunity to
make money, we can probably make money some other time and some other way. If we
destroy a species, we can probably never get it back no matter how much money we have.
123
See e.g. Radetzki 2001 p.87
Ulf Gärdenfors at “Artdatabanken” that compiles the red list for Sweden, clearly denies the possibility of
ever getting back a species once it is gone: Gärdenfors 2005 p.120
125
Norton 1986:1 p.121
126
See Crichton 1991 for a thought provoking fictional illustration of this.
124
39
That a loss is forever seems to be a very important psychological factor when we deal
with species extinction.127 The discussion we have seen here many be one possible
explanation.
There is one more thing we have to keep in mind when we talk about choice value:
Choice value for human beings is clearly important, but “choice value” for evolution is even
more important. If we diminish biodiversity, the evolutionary process will have fewer
genomes to “choose” from. This in turn means that we decrease the probability that the
particular species with the particular property we need for food or medicine or any of the
other uses we have discussed earlier, will turn up. It also means that possibilities for the
biological communities to adapt to future changes – human induced or not – will be smaller.
Some species obviously do not have any choice at all. They are totally dependent on one
type of food, host, pollen distributor, etc. Other species however do have a choice. When one
or more of the species they utilise disappear, they have less of a choice. This in turn can
make things more difficult for them in the long run. The species might be less abundant and
they may eventually disappear. If this species is important for us, it means it is also
important for us not to diminish the number of choices for the members of the species. We
will discuss the matter of ecosystem stability and adaptation soon but before that, we will
discuss another type of value other species can have for human beings.
2.6. Transformative value
Bryan Norton distinguishes between strong and weak anthropocentrism. Both are
instances of what I would call anthropocentric instrumentalism, but they differ from each
other in that the weak version includes a type of value not included by the strong version.
Strong anthropocentrism the way it is defined by Norton, only sees nature as valuable
to the extent that it satisfies demand values. Weak anthropocentrism also admit for nature to
have value for us by providing transformative value. A demand value is something that can
provide satisfaction for a felt preference. Transformative value on the other hand is a type of
value that makes us examine, and possibly alter a felt preference.128
127
128
See e.g. Elmqvist et al 2005:2 p.46
Norton 1987 p.9ff
40
To illustrate the concept of transformative value, he gives us two examples:
The first example features a teenager who really wants to go to a rock concert, but
instead of a ticket to the rock concert, she receives a ticket to a concert with a symphony
orchestra. As a result, she becomes very disappointed. The ticket does not represent a
demand value for her – i.e. it does not satisfy any of her preferences – and she wants to give
the ticket away. After having been persuaded by her parents to attend the classical concert,
she acquires a taste for classical music, which continues to give her much pleasure. Thanks
to the ticket, she alters her set of felt preferences concerning music, from only including rock
music to also including classical music. The ticket therefore represented a transformative
value for her.
Norton also uses an example of a child whose friends are bad for him. The time spent
with these people ultimately changes the demand values of the child in a direction that
relative to some other basic value129 is negative for him. It is therefore an example of a
negative transformative value.130
I interpret Norton’s use of the term ‘weak anthropocentrism’ based on these examples
as a kind of anthropocentric instrumentalism according to which nature, other species etc.
has instrumental value for us not just as a means for achieving what we already value, but
also as having the potential to change these values. Thereby giving us the opportunity to
value different things (that hopefully are more worthy of our preferences), or to value more
things. Nature or different species therefore has instrumental value according to Norton not
just for satisfying existing intrinsic values but also for supplying us with new ones.
By including transformative value in the realm of anthropocentric values, Norton
hopes to be able to increase the use of anthropocentric arguments in favour of preservation.
Others seem to believe the opposite. The economist Marian Radetzki does not use the
terminology introduced by Norton, and he does not go trough the more intricate
philosophical aspects of it, but he still seems to be thinking of something very similar to the
transformative values identified by Norton. Radetzki believes that lack of the things we
value in nature might transform our preferences so that we in the end will not miss them but
rather be glad that they are gone and replaced by whatever we have got instead. Future
generations might e.g. according to Radetzki acquire a taste for the barren artificial
129
Norton discusses the nature of what distinguishes a positive transformative value from a negative
transformative value. I do not believe that he manages to fully answer the question, but I will not go into that
question here since it would take us too far away from our own question.
130
Norton 1987 p.10f
41
environments they may have to live in and eventually even come to prefer that type of
environment to the natural environment. In order to support his assumption, he points out
that many people today prefer swimming pools to the ocean even at seaside resorts despite
the water in the ocean being as clean as the water in the pool.131 One might also add that the
number of people who spend their time off at the mall is much larger than the number of
people who spend it at the nearest public wilderness area.
I am not convinced that this really grants Radetzki’s conclusion however. The facts
seem undisputable but the logic is not convincing. Even if many people today actually prefer
the barren monocultures of a modern city, they might in the same way learn to appreciate a
richer environment with larger biodiversity if they became exposed to it in a proper way and
were provided with the basic understanding of biology that makes it possible to get more
pleasure from the experience. This is in fact parallel to Norton’s example: Most young
people today would not freely go to a classical music concert, but if they where exposed to it
and got to learn about it at least a good part might acquire a taste for this kind of music and
as a result have a wider selection of music to enjoy. The transformative value of a ticket to a
concert does therefore not necessarily consist just in changing the taste of the concertgoer. It
might well – as it did in Norton’s example – consist in adding to the tastes she already has,
and therefore increasing choice value. 132 The thing is that if you start appreciating
experiencing other species you do not have to stop experiencing the pleasures of modern
civilisation. In the same way, by getting access to the latter, you do not have to give up the
former. By learning to appreciate both, you will rather have more things to appreciate
(increased choice value). Radetzki’s argument seems to rest on the assumption that we can
transform away preferences and so to speak “get over” things we do not have access to
anymore, while Norton’s seem to rest on the idea that we through transformation can both
increase and refine our set of preferences. Both directions are probably possible, but
Norton’s direction (towards an increase of demand values) clearly seems more enriching
while Radetzki’s seems to make our lives less rich. Even if we learn to appreciate what we
131
Radetzki 1990 p.55, Radetzki 2001 p.79
Maybe we can describe the relation between transformative value and other types of value thus: ‘Something
has transformative value if it enhances something’s value – not by transforming the object of value but by
transforming the valuer’. The relation between the two types of value discussed in this and the previous chapter
will thus be: ‘One way in which something can have transformative value is by enhancing something’s choice
value – not by transforming the object of value but by transforming the valuer’. It may also be a good idea to
distinguish between positive and negative transformative value, where the former transforms the valuer into
valuing something she did not value before (or valuing it more than she did before), while the latter transforms
the valuer into not valuing something (or valuing it less). This means that choice value is only increased by
positive transformative value.
132
42
have got, it seems quite clear that it would be even better if we got more to appreciate. All in
all it seems clear that the existence of transformative values talks clearly in favour of
diversity: With more diversity we can learn to appreciate more things and therefore have a
richer life, as with the teenage girl in Norton’s example who learned to appreciate both rock
and classical music. Radetzki’s reasoning might be of some comfort if we lose diversity, but
Norton’s reasoning shows us that more diversity is still better. This ought reasonably to go
for biological diversity as well as for diversity in musical styles.
I think the distinction between demand values and transformative values is quite
interesting, and it seems very reasonable to include transformative values among our reasons
to preserve other species from an anthropocentric perspective.
2.7. Ecosystem services
In this section, I will take a closer look not at the instrumental value of individual
species, but at the systems that the species are part of. The ecosystems too supply us with a
substantial set of services. These services are often referred to as “ecosystem services” and
some of them are extremely important.133 The ecosystem services include regulation of the
oxygen content in the atmosphere, running the water, coal, nutrient, and other cycles,
photosynthesis, pollination, seed dispersal, pest control, regulation of the climate, keeping
the soil productive, taking care of waste products, etc.134 It is quite clear that we as human
beings to a large degree are dependant on biodiversity in general, and on some species in
particular, to uphold the ecosystem services. The coral reefs alone are said to provide
ecosystem services amounting to hundreds of millions of dollars by providing habitats for
fish, cycling nutrients, protecting human settlements against waves etc.135 Some calculations
indicate that the economic value of ecosystem services is twice the size of the worlds total
133
The term ‘ecosystem services’ is sometimes used in a way that covers all services we get from nature. I
think however that it is useful to distinguish between the services and goods we get directly from the species
and the services we get from the system – even though there is a large grey zone between them.
134
Daily 2000 pp.333ff, Ehrlich et al 1990 p.99,102f, Elmqvist 2005:1 p. 32, Farber 2000 pp.s494f, Gärdenfors
2005 p.119, Johansson 2003 pp.2,24, Johansson, Birgitta 2005:1 pp.8,236, Kellert 1986 p.53, Lovejoy 1986
pp.17f, Luper-Foy 1995 0.97, Millennium Ecosystem Assessment 2005 passim, Norton 1986:1 p.128,
Söderqvist 2005 p.75, Prance 1990 p.64
135
Millennium Ecosystem Assessment 2005 p.25 See also Lindén 1990 p.73
43
GNP.136 The climate is affected in many ways by biodiversity, especially by trees. Many
trees are very “thirsty” organisms, which means they play an important role in the water
cycle. Through their roots, the trees draw a lot of water from the ground – water that is then
evaporated into the atmosphere.137 Cutting down trees can mean drought in some places, and
flooding in others.138 Ehrlich and Ehrlich mention drought in Rwanda and Egypt, and
flooding in India and Bangladesh as results of deforestation.139 Trees also bind large amounts
of carbon, which means that they play an important part in regulating the amount of carbon
dioxide in the atmosphere. This in turn means that trees are important in regulating the
greenhouse effect and thereby the climate. 140 They also contribute to climate control in other
ways. The leaf surface for instance affects the amount of sunlight that is reflected back from
earth.
We could go on for quite a long time listing ecosystem services from trees, but to sum
it up, we can without any doubt conclude that trees are important for the ecosystem services,
and thereby for human life as we know it.
The same type of reasoning can in different degrees be applied to organism after
organism. The ecosystem services are in general as basic and as important as food, and are
probably more important than many of the other uses we have discussed. Among the
ecosystem services are the basic life enabling services like photosynthesis and the circulation
of nutrients without which our kind of life would be impossible.
In fact, our wellbeing is more dependent on the biotic community than many people
are aware.141 Some authors in fact recommend that we consider the value of biodiversity
primarily in terms of ecosystem services rather than as suppliers of different kinds of
goods.142 For instance, Bryan G. Norton suggests that the goal of species preservation should
be “conceived as the goal of protecting total diversity”.143 He even argues that the value all
species have by being part of the total diversity, is sufficient for seeing them as worthy of
protection.144
He is not thereby denying that the different species also have instrumental value for us
because of their particular features, but he sees this almost as a bonus – a value that can be
136
Gärdenfors 2005 p.119
Millennium Ecosystem Assessment 2005 p.29, Myers 1990 pp.17ff
138
Ehrlich et al 1990 p.103, Lovejoy 1986 p.15, Myer 1990 p.19
139
Ehrlich et al 1990 p.103
140
Walsh 2004 p.65
141
Lovejoy 1986 p.24
142
Bandyopadhyay et al. 1990 pp.68ff, Prance 1990 p. 64
143
Norton 1987 p.34
137
44
added on top of the general value the species has as being a part of biodiversity.145
Apparently, by taking departure in total biodiversity, Norton wants to lay a ground ensuring
that all species have at least a basic equal value that we can mount towards the value of other
human projects that might be detrimental to one or more species. The “bonus” value that
many species have on top of that just strengthens its position in relation to other human
values, even further.
When we talk about ecosystem services, we should not forget that evolution itself is a
kind of ecosystem service. The natural evolution goes on all the time, and “invents” new
properties in both plants and animals, properties that can turn out to be very useful for us.
More species also increase the chance of finding new useful species. 146 This means that all
species contribute to biodiversity in two ways: By being a part of the diversity, and by
interacting with other species and thereby contributing to their survival and evolution.147
When a species goes extinct, it therefore also means a change in the evolutionary process
since it affects the selection pressure on the remaining species.148 In order for this
evolutionary process to continue, we need to protect not only the species that are potentially
useful, but also the ecosystems in which they live and evolve, and other species that may
evolve useful traits in the future or that just contribute to the selective pressure that drives the
evolutionary process. As Alan Randall points out, we could talk about preservation of
evolutionary processes just as we talk of preservation of species.149 This kind of ecosystem
service is seldom mentioned, but should not be underestimated.
Norton reasons along these lines when he points out that species with no direct
instrumental value may still be indirectly useful by just contributing to the evolution and
thereby to the emergence of new species that may be useful in a more direct way. His idea is
that diversity contributes to diversity, and at least some yet to be evolved species will be
useful for us. Therefore, all species are important by merely being part of the competition
that drives evolution and contributes to future diversity.150
One important conclusion one might draw from this reasoning is that it is therefore not
enough to preserve a species in one of the areas where it occurs, or in a zoo or a national
144
Norton 1986:1 p.111
Norton 1987 p.35
146
Norton 1986:1 p.128
147
Norton 1986:1 p.127
148
Vermeij 1986 p.40
149
Randall 1986 p.100
150
Norton 1987 pp.61,63
145
45
park. It is important to preserve it in every ecosystem in which it plays a part.151 Even if a
species is not globally extinct but only locally, the humans living in the area where it is gone
still suffer the consequences of living in an environment with lower biodiversity.152 Ulf
Gärdenfors from “Artdatabanken”153 makes an analogy with human professions. It is good
that we have physicians but is not enough that they exist somewhere in the world. We need
physicians in the area where we live.154
It has been suggested that we might be able to replace some ecosystem services by
artificial means just as we can replace e.g. some materials with materials from non-living
nature.155 This is probably not the case with most ecosystem services. It seems in fact to be
an important feature of ecosystem services that they are typically non-exchangeable.156
Lovejoy contends the weaker but probably sufficiently strong idea that to artificially
maintain the ecosystem services by a human design would take a planning effort that is
totally overwhelming both scientifically and socially, and that it will not be possible in the
near future.157
The exchangeability was one of the things that posed a problem for the anthropocentric
instrumental approach when we discussed the use of other species as resources in some of
the previous sections. The fact that this does not apply to the same degree to ecosystem
services makes them a stronger basis for preservation according to anthropocentric
instrumentalism, than is the case with many of the other areas of use. To take away an
irreplaceable service ought in short to be more wrong from an anthropocentric instrumental
perspective than to take away something that can be substituted.
However, even though the ecosystems services are in general not exchangeable, some
of the species that make the ecosystems work might be exchangeable. Let us return to the
trees for a moment: Trees are important, but there are many tree species, and there is a lot of
overlapping in their ability to provide different ecosystem services. This means that even
though we need trees to regulate for instance the climate, we probably do not need all
existing tree species for this purpose. In fact, since some species are better at this than others,
this particular ecosystem service could provide an argument to cut down trees of less
effective species and substitute them with trees from the more effective species. Things are
151
Lovejoy 1986 p.23
Gärdenfors 2005 p.116,118, Norton 1986:1 p.121
153
The Species Information Centre at the Swedish University of Agricultural Sciences.
154
Gärdenfors 2005 p.118
155
Farber 2000 p.s495f, passim, Radetzki 2001 pp.43,75,77f
156
Daily 2000 p.334, Ehrlich et al 1990 p.102
152
46
not that simple however. There are many different types of environments on the planet and
not all tree species thrive in all types of environment or play exactly the same roles in all
types of environment. This means that even if we do not need all presently existing tree
species for climate regulation, we definitely need a fair number of them. To this we should
also add that species depend on other species for their continued existence,158 and some tree
species on other tree species. In Sweden, Pedunculate oak (Quercus robur) e.g. depends on
Norway Spruce (Picea abies) to be able to propagate: The oak propagates by acorns that
grow after they have been hidden by the Eurasian jay (Garrulur glandarius) who use them as
winter food but sometimes forget where they have hidden the acorns. If the acorn is not
buried, it will probably be eaten by squirrels (Sciurus vulgaris), deer (different species of
Cervidae) or mice (different species of Muridae) before they get the chance to grow. The
jays in turn do not nest in oak trees but need thick spruce forests to nest, so therefore the
spruce is important for the oak.159
We also have to remember that trees play a role in many ecosystem services – not just
climate regulation – and they played a large role in many of the previous discussions, (see
the sub-sections Food, Material and fuel, Medicine, and Tourism, not to mention Some nondestructive uses of other species above). The tree species that have the highest instrumental
value for one particular service are not necessarily the same species that best performs
another particular service. Some species are very important in some ecosystems but not in
others.160 We will therefore still need quite a large selection of species to fulfil the different
roles. It has also turned out that monocultures are not very sustainable, which means that we
need more than one species for each type of ecosystem. Actually, we need quite a lot of
species to get a working ecosystem – and not just tree species. Trees are heavily dependent
on pollination, seed dispersal (see the example above that not only tells us that oak depends
on spruce, but also that oak depends on jays), micro fauna in the soil, fungus that live in
symbioses with many trees, etc. In short, to secure the ecosystems services, we need species
that are not directly involved in the services in question, but that are necessary for the system
to work. Agriculture has showed us that even though monocultures can be very productive,
they cannot sustain themselves for very long without human help. They in fact depend on the
ecosystem services they are replacing.161 Thus, the function of things in nature tends to
157
Lovejoy 1986 pp.20f
Gärdenfors 2005 p.116
159
Johansson 2003 p.27, Johansson, Birgitta 2005:1 pp.8,12, Söderqvist 2005 p.80
160
Daily 2000 p.336
161
Norton 1986:1 pp.129f
158
47
depend on there being other things functioning in a certain way.162 This should not be a
surprise since the properties of different species have evolved as a result of interplay with the
environment in which they live. There seems in short to be a very intricate web of
dependency relations. This means that we also have the problem of what we might call
“domino effects”. One extinction can lead to another and then to a third and so on.163 The
disappearance of one species can have quite large effects and a small change of the
ecosystem might lead to a bigger change in the long term. This means that even if the species
that goes extinct as a result of our actions is not useful for us per se, it can lead to another
species that is important for us going extinct further down the line as a result of the first
extinction.164 Something that complicates it further,is that we do not have enough knowledge
about the connections in nature to say that the extinction of a certain species will not lead to
a downward spiral of extinction.165
Norton also argues that even though most cases of dependence is not absolute, loss of
species makes the system less stable, and often involves a decrease in the population of the
dependant species, which makes it more vulnerable to environmental changes.166 This in turn
can affect other species and may eventually push some species over the edge.167 For instance,
when deforestation affects the water cycle this may lead to further extinctions.168 In a
simulation performed by Plotnick & McKunney 1993, the result was even worse. It turned
out that an ecosystem could, depending on the relative rates of speciation and extinction, fall
into a situation where the death of a single species could lead to a mass extinction.169
According to many biologists and environmentalists, a larger biodiversity in general
tends to increase the stability of the ecosystems, while a lower biodiversity in the same vein
decreases the stability.170 According to one study by David Tilman and J.A. Downing
published 1994, spots with a larger number of species had a higher resilience against
drought.171 Another study by Tilman from 1996 indicates the same thing.172 Marine biologists
Thomas Elmqvist and Kerstin Johannesson claim in a paper from 2005 that it is becoming
162
Bandyopadhyay et al. 1990 pp.77, Myers 1990 p.22ff, Prance 1990 p.64
Norton 1986:1 pp.114ff, Vermeij 1986 p.40
164
Norton 1986:1 p.118
165
Norton 1987 p.62
166
See the reasoning on choice value for other species above.
167
Norton 1987 pp.62f
168
Lovejoy 1986 p.16
169
Kaufman et al 1998 p.522
170
See e.g. Aoki et al 2001 p.65, Elmqvist et al 2005:2 p.47, Ihse 2005 p.64, Johansson, Birgitta 2005 1p.41,
Norton 1986:1 pp.122f
171
Referred to by Ricklefs 1997 p.599
172
Tilman 1996 pp.254ff
163
48
increasingly clear that the loss of biodiversity is a threat to the production of food and
different materials but also to the supply of ecosystem services.173 They refer to reports from
several European studies that indicate that larger biodiversity means increased biomass
production (and thereby to a larger amount of coal bound by the trees which is important for
counteracting the increasing greenhouse effect), smaller leakage of nutrients from the
system, smaller risk of invasion by alien species, and larger stability over time.174 They are
not sure however if the results can be generalised to the majority of the earth’s ecosystems.175
They also mention the existence of several cases where ecosystems have “flipped” (changed
dramatically), and where decreasing biodiversity has been part of the cause.176 It is
considered beyond doubt that biodiversity is important for the marine ecosystems but
biologists are not sure precisely how.177 Elmqvist and Johannesson claim that more species
makes the ecosystem more stable,178 though Johannesson believes that far from all existing
species are necessary for the ecosystems to work.179 In an investigation of aquatic trophic
systems, Ichiro Aoki and Takahisa Hamamatsu show that an increase of biomass diversity
(which is not strictly the same as species diversity although they often coincide) in aquatic
ecosystems increases the whole systemic stability,180 but point out that most investigations
regarding the relation between diversity and stability only deal with one trophic level (in
general herbivorous societies), and that we still need more thorough investigations of the
relation between diversity and stability in whole systems involving different trophic levels.181
In a simulation study performed by Kaufman et al, the authors conclude that the best strategy
to optimise the chances of survival for all species is to preserve a high degree of diversity.182
The greatest importance of species richness when it comes to ecosystem services, are
according to some sources to be found in its contribution to the long time stability and
resilience of the ecosystems.183 Other sources deny any connection between species richness
and stability, while some even claim that there is a negative connection – for instance that
the high degree of specialisation in ecosystems with many species means that the species are
173
Elmqvist et al 2005:2 pp.49f
Elmqvist et al 2005:2 pp.47f
175
Elmqvist et al 2005:2 p.48
176
Elmqvist et al 2005:2 pp.48f
177
Johannson 2003 p.22
178
Johansson, Birgitta 2005:1 p.10
179
Johansson, Birgitta 2005:1 p.17
180
Aoki et al 2001 passim
181
Aoki et al 2001 p.65
182
Kaufman et al 1998 p.531
183
Millennium Ecosystem Assessment 2005 pp.25,64
174
49
extra sensitive to changes – which ought to make systems with a higher degree of
biodiversity less instead of more stable, and less instead of more resilient.184
David Tilman presents a list of investigations with very differing conclusions. Some
support the idea that larger diversity means a higher degree of stability. Some point in the
opposite direction, and some have found no connection. It should also be remembered that
relatively few investigations have been done in this field.185
The Biodiversity syntheses from the Millennium Assessment Report, concludes that
there is what they call “established but incomplete” evidence that a lower biodiversity means
a lower resilience to, and ability to recover from, disturbances.186 They also acknowledge
that some species are much more important than others, and that the composition of species
has turned out to be at least as important as the sheer number of species.187 The latter point
has also been made by Norton who none the less sees the number as the important question
to concentrate on when we discuss preservation.188
To sum up before we slide too far away from ethics and too deep into ecology: In
order to secure the ecosystem services we need working ecosystems, and in order to secure
working ecosystems in the long term, we inevitably need at least some degree of
biodiversity.189 However, we cannot say for sure that the larger the biodiversity, the better for
a steady delivery of ecosystem services, and we can probably not say that we need all
species for this purpose. We can say with great confidence about some particular species that
they are very important in this respect, while the confidence is much lower regarding other
species, and there is a great uncertainty concerning many species. There is also a great
uncertainty concerning how many species it takes to make a certain system work.
Norton believes that the contribution of each species is in most cases very small. There
are many species and the systems contain much redundancy. Therefore, the probability for
each particular species to be the one that causes the system to break is extremely small.190 On
top of that, many threatened species are naturally rare, which means that their contribution
184
Aniansson 1990 pp.37f,64, Sober 1986 p.176. See also Aoki et al 2001 p.70 who lists some examples. The
authors are however critical to their conclusions that are based on what they label “mathematical toy models”.
185
Tilman 1996 p.350
186
Millennium Ecosystem Assessment 2005 p.5f
187
Millennium Ecosystem Assessment 2005 p.22
188
Norton 1986:1 p.112
189
McGarvin 2001 p.25, Millennium Ecosystem Assessment 2005 pp.2,22,28,30
190
Norton 1986:1 p.122
50
ought to be even lower.191 Norton does not believe that these problems are devastating
however. He presents three reasons for that:
1. Even though there is much redundancy in most ecosystems, this is not a reason to be
less cautious. In fact, it is the redundancy that drives the competition, which in turn drives
evolution. Redundancy is therefore very important, and even if a species is rare, it may still
be an important participant in the evolutionary process. Naturally rare species are often
naturally rare because of their far-reaching specialisation. If a species is extremely
specialised, the niche it inhabits is bound to be very small. A far-reaching specialisation can
however be a strong evolutionary force in relation to other species that partly compete within
the same niche, even though they are not limited to that niche. Even the extinction of rare
species is therefore significant in terms of decreasing competition in relation to the
characteristics for which it is specialised.
2. Our knowledge of the evolutionary process is in general not good enough to specify
the importance of every species, and therefore we cannot say that a certain species is
redundant.
3. As we saw above, even if the disappearance of a particular species does not lead to
the extinction of other species, it may well lead to a weakening of some populations. This in
turn may contribute to a process that eventually pushes these species over the edge.192 In
other words: When we are dealing with extinctions, it is probably a good idea to consider
that even extinctions that have very small, or even no discernible effects, may have the effect
of taking us closer to the point where the ecosystem breaks down, and when we reach that
point (the “threshold”) an extinction that otherwise would go virtually unnoticed, can have a
tremendous effect on the ecosystem and thereby on us.
I believe that Norton’s answers are correct and to the point, and that they show that
even though the probability that the disappearance of a particular species will be devastating
is quite low, this cannot be used as an argument to disregard the species.
There is one salient problem with the argument from ecosystem services however, viz.
that many species are in fact already gone and we seem to live on and prosper. Is this not an
argument that we did not need all these species after all, and that it might not be such a big
catastrophe if we lose some more?193
To this one can answer
191
Norton 1987 p.61, Sober 1986 p.176
Norton 1986:1 p.121, Norton 1987 p.62
193
This problem is pointed out by e.g. Ricklefs 1997 p.597
192
51
(1) that we do not know what we could have gained from the species if they had not
disappeared. We are obviously alive without them, but we may have had better lives with
them, and some humans that have succumbed might have survived if some of the species
that have disappeared still existed.
One might also answer
(2) that there may be a time lag so that the effects do not show until later.
Finally
(3), we may find an answer in the threshold that Norton mentions. We may be fine so
far, but we do not know for how long we can go on like this. There might be a threshold
somewhere, and the warning signals may come too late.194 In the worst case, we might not
even know where the threshold is, which looks like an argument to be extra careful. I will
however come back to this problem in chapter 3 where I take a closer look at this and other
uncertainties we have encountered.
Both answers (2) and (3) means that even if we have not been seriously affected by the
loss of a species, future generations might be affected by the loss that we have caused. I will
discuss the moral implications of this in chapter 4.
The conclusions of this section is that ecosystem services are important from an
anthropocentric instrumental perspective – at least as important as any of the other goods
that different species contribute with. Some of the services are necessary for our future
existence. Many of the services also seem to be irreplaceable. In order for these services to
work, we need a certain – probably quite high – degree of biodiversity. We cannot say
however how many and which species that are necessary for a steady supply of ecosystem
services.
194
The concept of and problems related to threshold effects and other non-linear changes will be discussed
more thoroughly in the next chapter.
52
3. Uncertainty
3.1. Biodiversity and uncertainty
Our knowledge and understanding of most species, interactions between species,
ecosystems functioning and what roles different species play, is still highly incomplete and
full of uncertainties.195 There is also much uncertainty about the anthropocentric value of
different products and services from nature.196 What complicates it even further is that many
species are not even discovered yet. How can we value the services or goods they may
supply?197 In previous chapters we have encountered situations where our attempts to assess
the value of other species have been hampered by uncertainty. We will hopefully be able
remove some of the uncertainty by more thorough investigations, but we can probably not
remove it completely without substantial costs,198 or maybe even at all. To get a perfect
prediction of what will happen in an ecosystem in the long term when we make as
fundamental changes as removing a species might not even be possible.199 The old view of
nature as a machine – a clockwork with mechanic precision where a particular intervention
necessarily leads to a particular, foreseeable effect – is replaced by a more modern
conception of nature as something dynamic and complex, or even uncertain and chaotic.200
We have in other words started to realise that the way nature reacts to our treatment is not
completely predictable.
Donna Maher talks about a change of science from a situation where
… prediction of system behaviour was a matter of having enough data, to a 'science
of surprise', where chaos and unpredictability are endemic, with stability and
predictability the exception.201
Sverker Sörlin makes a similar point by referring to chaos theory and catastrophe
theory when he tells us that the old fashioned linear models will not help us find out at which
195
Aniansson 1990 p.38,42, Farber 2000 p.s492, Ihse 2005 p.71, Söderqvist 2005 p.78
Farber 2000 p.s495
197
Randall 1986 p.85
198
Farber 2000 p.s496, McGarvin 2001 p.25
199
McGarvin 2001 p.25
200
Beltrán 2001 p.4, Herremoës et al 2001 p.193, Sörlin 1991 p.18
201
Maher 1999-2000
196
53
point the decreasing ozone layer, or the greenhouse effect etc. will take an uncontrollable
catastrophic turn.202 He does not mention loss of biodiversity, but the same reasoning can
probably be used here.
One of these nonlinear phenomena that we have to consider when we are dealing with
complex things like living beings or ecosystems is (as we have noted earlier), the existence
of threshold values.203 Normally we assume that cause and effect are proportional, and can be
described by some linear equation, i.e. that a certain change in the cause leads to a
corresponding proportional change in the effect. However, in some situations all or most of
the effect takes place when the causation power has reached a certain value – the threshold
value. In this type of situation, most changes in the causation power do not have any visible
effect at all, but still have the important indirect effect of taking us closer to the threshold
value. This climbing closer to the threshold value is in many cases something that takes
place invisibly.204 When the threshold is reached, the next change in the causing power –
however small – will mean all the difference in the world. Then the up to now only latent
effect will suddenly occur all at once.
In our case, it would mean that the disappearance of a single species, or two or three,
from an ecosystem might not result in any discernible effects on e.g. the ecosystem services.
This might go on for a while but when a threshold is reached, the results could be dramatic.
Anne and Paul Ehrlich use an analogy about a person who pops rivets from the wings
of airplanes. He sells the rivets for 50 cents each and he defends himself by pointing out that:
I’ve already taken 200 rivets out of this wing, and nothing has happened yet. Lots of
planes fly with missing rivets. They build a lot of redundancy into jet aircraft, partly
because they don’t completely understand the materials and stresses involved, so
nobody can prove that taking another rivet out will weaken the wing too much.205
As we saw in the previous chapter, decreasing redundancy might have unwanted
consequences. One consequence that we touched upon was that we might be approaching a
threshold. Both the story about the water filler and the story about the rivet popper are
illustrations of this.
202
Sörlin 1991 p.255
Daily 2000 p.335. Clarke 1995 p.41, Herremoës et al 2001 p.193, McGarvin 2001 p.25, Norton 1986:1
p.123 (Clarke talks about them as “jump effects”.)
204
This is not always the case though. Sometimes it is indicated by something else than the effect we are
worried about (and do not see any trace of yet).
203
54
As Bryan Norton points out, the assumption of the ‘rivet popper’ that the absence of
any accident so far is an indicator that the risk of an accident in the future is very low, would
be true if we were talking about a series of independent events. The problem is that we are
not. For every rivet he pops, there are fewer rivets left, which means that the constitution of
the plane is constantly getting weaker. The same goes for species: For every species that
goes extinct above the speciation rate, there are fewer species left, and the ecosystem – even
the global system – is weakened.206
This is typical for threshold effects. Every change in the input takes the system closer
to the threshold even though the effect is not noticeable until we reach the threshold.
Margareta Ihse extends the collection of “threshold-analogies” with an analogy about a
hammock where the species are the threads of the fabric that will hold us up for a while, but
bursts when the fabric gets too thin.207
This is a very good analogy of ecosystems as well as of the circulation of nutrients etc.
in nature. They can be described as a web with many intertwined threads. This gives the
system a certain amount of stability but we do not know when the web gets too thin to
uphold its function. It also illustrates that the resisting power of nature that is due to the
redundancy in the systems is never a guarantee against severe changes. It holds back – and
hides – the changes for a while and lulls into a false sense of security, but it does not stop the
change forever and when it occurs all the change occurs at once.
The Ehrlich analogy points at an important difference between the natural
disappearance of species and the high extinction rate we are facing at the moment due to
anthropogenic interventions: Normally the species that go extinct are replaced by other
species just like lost rivets in an airplane are replaced by new rivets.208 At the pace by which
species are disappearing today, the species cannot be replaced fast enough however and we
face a net loss.
There is one important difference between the analogy with the rivets and the loss of
species however, and unfortunately, this difference makes the species loss much more
problematic than the loss of rivets. New rivets can be taken from the storeroom and the old
ones can be replaced by human maintenance personnel. Species on the other hand are
replaced by evolution. Instead of being taken from a storeroom, they evolve from the genetic
205
Ehrlich et al 1990 p.95
Norton 1986:1 p.122, Norton 1987 p.68
207
Ihse 2005 pp.70f
208
Ehrlich et al 1990 p.96
206
55
basis that already exists in the existing species. This tells us that in order to replace lost
species with new species that have a better chance of survival, we need above all a large
selection of genes. I.e., we need a large biodiversity, and that is precisely what we are losing.
The non-linear aspect can be brought one step further and form another argument to
consider: Sometimes a very small change in the input can have a very large effect on the
output. If there are effects like this in ecosystems, it must be a very strong argument indeed
for extra caution about all interventions in the ecological systems – including interventions
that contribute to the extinction of species.
Furthermore, if we take a closer look on the evolutionary process, we will find that one
of its inherent features is that it has no predetermined direction. It is not the case that the
individuals of a species always get bigger or faster or more intelligent. The direction in
which the evolution takes a certain species depends on its environment and on chance. The
environment changes all the time, and what “remedy” that evolves in a certain species as an
“answer” to a particular change in the environment depends on what its gene pool happens to
have in store, and on which re-combinations and mutations that happen to take place. Which
of these “remedies” in turn that eventually are favoured by natural selection, depends not just
on one single aspect of the environment in which the species live, but on the total selective
pressure that the environment puts on the species. If rabbits (Oryctolagus cuniculus) become
faster, foxes (Vulpes vulpes) have to evolve too, but not just in relation to the rabbits. If they
evolve a quality that makes them better rabbit hunters but also makes them less resistant to
cold or easier prey for the lynx (Felis lynx), they will loose out in the evolutionary game
anyway. All species are in fact at any given moment subjected to pressure of many different
types from a large number of different directions, and the sources of the pressure are also in
their turn subjected to pressure of many different types from a large number of different
directions – including from the species they are exerting pressure on. If we were going to
calculate the direction of evolution for the fox, we would have to consider the selection
pressure that is placed on the fox by both the lynx and the rabbit, as well as all other species
that interact with the fox as well as all the non-living forces of nature. The rabbit and the
lynx and the other species evolve too however, and that has to be taken into account. The fox
is putting both the rabbit and the lynx under selective pressure just as they do with the fox,
but that is not all. The lynx not only eat foxes but also rabbits so we have to look at the
pressure they exert on each other. The lynx also eat other prey though and the rabbit is not
just hunted by the fox and the lynx. It therefore does not just evolve in a way that helps the
56
rabbits cope with the threat from these predators, but also as a result of how the golden eagle
(Aquila chrysaetos) evolve since they eat rabbits too, etc. The pressure from the lynx and the
golden eagle will inevitably also affect what options the genes of the rabbit has when it
comes to “dealing” with the threat from the fox and so on. Then we have to put the result we
get for the rabbit back into our equation for the fox together with the results from other prey
species for the fox, and so on and so forth – and while we have done that the whole scenario
has already changed. In short, we would have a problem that is infinitely more difficult to
solve than the “three body-problem” in physics.
What this tells us is that we simply cannot know for sure what will happen in an
ecosystem in the long run when we make such a radical alteration as changing the species
composition.
Changing the species composition can be done in different ways. It can be done e.g. by
causing a species to go extinct as we are discussing here, or by putting in a new species that
was not there before (but that may well have the result in other species disappearing).
The best literary description of the latter is probably Michael Crichton’s book “Jurassic
Park”.209 In this book, species of animals and plants that lived more than 65 million years ago
are resurrected and placed in a present day environment. As we know, it did not work out
very well in spite of the guarantees from John Hammond and his bio-engineers. This was of
course just fiction. We do not know what will happen in a situation like this, but the point of
the story was just that: We do not know, because we cannot know. It is impossible to predict
the results from such a project, and therefore we should be more cautious. To recreate prehistoric organisms is quite extreme, but many of the interventions we make are almost as
extreme, and as we saw above, our possibilities of foreseeing the results are limited. The best
and most frightening illustration in the book is probably the absolute confidence by which
Mr Hammond and his staff guarantee the safety of the arrangement. (What is particularly
frightening is how easy it is to recognise this unshakable confidence in many people in the
real world.)
There are many real-life examples of how we have intervened in nature and ended up
very surprised over the results. The rabbit explosion in Australia and the drought catastrophe
in Sahel in Africa are both described as examples of catastrophic situations caused by our
ignorance about ecology.210 A well-known example of how human beings have deliberately
tried to engineer nature to suit our purpose by taking away a species from the system, is the
209
Crichton 1991 passim
57
wolves that where hunted virtually to oblivion in North America in order to protect both
farm animals and game animals (or to be more precise, to protect human farmers and hunters
from the competition). This resulted in an explosive increase in the number of deer, which in
turn caused a lot of damage to the ecosystems. It also had a negative economic effect on the
human population since it destroyed the grazing for domesticated animals such as sheep.211
All the examples above confirm the problem of predicting what will happen in an
ecosystem as a result of human encroachment. The lesson that seems to emerge from this
section is that we will probably never reach a situation where we have enough information to
make a fully informed decision as to which course of action is the most rational from an
anthropocentric instrumental point of view. We therefore need some kind of strategy for how
to handle the uncertainties that we cannot get rid of. In the coming sections we will try to
find such a strategy, and we will in particular take a closer look at one that has recently
become very popular.
3.2. Dealing with uncertainty
There is as we noted in the previous section – and have seen many examples of in the
previous chapter – much uncertainty surrounding the things we have to consider in order to
answer our main question. It might not even be possible to totally get rid of all the
uncertainty, or even to reduce it to a reasonable level. We therefore need a strategy of how to
behave in situations of uncertainty. Åsa Mattsson identifies four different strategies:212
I. One strategy is not to change anything until we have a better understanding. At first
sight, this looks like the only rational strategy: If we lack sufficient knowledge to make a
good decision, it must be better not to make any decision at all – at least until we have
sufficient knowledge.
It has also been suggested that lack of knowledge as such cannot be an argument in
favour of acting in a certain way.
213
If that is correct, it is a strong argument for this
210
Palmer 1995 p.26f
Ricklefs 1997 p. 598
212
Mattsson 2006 pp.10f
213
Sober 1986 pp.175f
211
58
approach. It would also be very important for our investigation. Lack of knowledge
regarding the future value of a species is sometimes used as an argument for preservation.214
That argument would be refuted if we find that lack of knowledge cannot be an argument for
any particular strategy. 215
There are problems with this idea however. The most important problem is probably
that deciding to wait is also a decision, and in bi-polar decisions like preserving or not
preserving, waiting must mean something. The question is: Does it mean that we preserve
the species until we know more or that we exploit the species until we know more? The
answer to the question “what do we do while we wait” is often very important. In situations
where we deal with irreversible changes it is extremely important, and that the “wait and
see” strategy do not have an answer to this question (it cannot have one – that is the very
point of the strategy) is very problematic.
It is also possible that we will never reach an understanding that is much better than
the one we have. In the previous section, we saw that this is a quite plausible option when we
deal with some changes in nature.
Finally, we have to be aware that there is a risk in waiting. It is in general true that
waiting for more information before we make a decision increases the probability that the
decision will be better when it comes. On the other hand, there is a risk that it will then be
too late. The time factor can in some situations make waiting a very dangerous strategy.
II. A slightly different strategy is to wait for a better understanding, but monitor what
is happening while we wait and prepare for the possibility of problems materialising along
the way. This strategy has the same advantages and drawbacks as the previous one, with the
difference that we are better prepared to deal with problems as they appear. This does not
seem like a good solution when dealing with nonlinear or irreversible changes though since
we will not be able to act until the problem has already appeared.
III. Another strategy is to act immediately on the best available information, and hope
it is correct. By doing that we will not lose any time, but we run the risk of the information
not being correct. There is also the drawback that since we are treating our inadequate
information as adequate, we leave no room for precautionary measures in case it turns out to
be wrong.
214
See previous chapter. See also Gärdenfors 2005 p.119
59
IV. Finally, we have the strategy of making a decision based on the information we
have but adapting it to the uncertainties, and building in some precautionary measures in
case events turn out differently than predicted. There are different versions of this strategy
but the version that has received the most attention recently is the so-called precautionary
principle. This strategy is recommended or even prescribed by many official sources,
including international declarations and treaties such as the Rio declaration, Agenda 21 and
the constitution of the European Union, but also by national as well as regional and local
legislation in many countries.216 If we can show that the precautionary principle is ethically
and rationally in accordance with anthropocentric instrumentalism, or even required by
anthropocentric instrumentalism, and if we can show that it is applicable to our situation,
then we may have a method for dealing with some of our problems.
In the next section, I will try to produce an interpretation of the precautionary principle
that is in accordance with basic moral intuitions. In the section after that, I will go on and
take a look at some proposed problems with the principle. Finally, I will try to apply it on the
species problem and see first of all whether it is possible, and in that case, what the result
would be.
215
Sober 1986 pp.175f
Herremoës et al 2001 p.14 contains a list of international treaties that contain the precautionary principle.
See also Beltrán 2001 p.3, Case, David 2005, Environmental commons, Gollier & Treich 2003 p.81, Grandjean
2004 p.206, Grandjean et al 2004 p.482, Lin 2001 p.129, Melin 2001 p.98, Rio Declaration §15, Sandin 2004:2
pp.2f, Sandin 2004:3 p.8, San Francisco Adopts the Precautionary Principle, SF Precautionary Principle
Ordinance, Turner & Hartzell 2004 p.450, Walsh 2004 p.69. See also
http://www.institute.redlands.edu/p3/tthome.htm for an extensive list of treaties containing references to the
precautionary principle.
216
60
3.3. The Precautionary Principle
The precautionary principle has been formulated in several different ways. The most
common formulation is from the Rio Declaration: 217
Where there are threats of serious or irreversible damage, lack of full scientific
certainty shall not be used as a reason for postponing cost-effective measures to
prevent environmental degradation.218
The Rio declaration in general leaves much room for interpretation, and the
precautionary principle is no exception.219 There is a large flora of interpretations, and there
is still no real consensus. 220 The Rio formulation has also been criticised for being too weak,
and for not really telling us what to do, but only what not to do (i.e. not to use lack of
scientific certainty as an excuse for not acting).221 Nonetheless, it can be used as a good
starting point for our investigation. It seems that the basic idea expressed by this formulation
that “business as usual” is at least in some situations – viz. in situations where we risk
serious or irreversible environmental degradation – not the best strategy as a response to
uncertainty.
Another often referred to formulation of the precautionary principle is the so-called
Wingspread formulation.222 It was formulated six years after the Rio formulation at a
conference with a number of scientists, activists, etc. from different countries (though mostly
from North America).
It states the principle as follows:
217
See e.g. Barrett 2005, Case 2005, Cussio 2005, Gee 2006, Gollier & Treich 2003 p.81 Grandjean 2004
p.206, Lin 2001 p.129, Melin 2001 p.101, Stijkel et al 1999 pp.304f, Sandin 1999 pp.895,903, Sandin et al
2002 p.289, Sandin 2004:1 p.4, Sandin 2004:2 p.5, Walsh 2004 p.69
218
Rio Declaration §15
219
For a discussion of the Rio formulation, see Sandin 1999 p.895, Sandin et al 2002 p.289, Sandin 2004:2
p.15, Sandin 2004:3 pp.10f
220
Sandin 1999 p.889, Sandin 2004:2 p.2
221
Sandin 2004:1 p.4
222
Grandjean 2004 p.206, Sandin 1999 p.891,905, Sandin 2004:1 p.4, Sandin 2004:3 p.8, Turner & Hartzell
2004 pp.449,251f, passim
61
When an activity raises threats of harm to human health or the environment,
precautionary measures should be taken even if some cause and effect relationships
are not fully established scientifically.223
Contrary to the Rio formulation, the Wingspread formulation is stated as a positive
prescription. It is also somewhat more specific than the Rio formulation regarding what
counts as scientific certainty. Finally, it widens the scope of the principle by being more
general regarding the kinds of threat, and also by including human health among the relevant
considerations for application. It seems clear, though, that the two formulations are built
upon the same basic intuitions.
Other formulations point clearly in the same direction.224 Grandjean et al interpret the
Precautionary principle as:
… a tool for avoiding possible future harm associated with suspected, but not
conclusive, environmental risks. 225
Per Sandin defines the basic idea of the precautionary principle as follows:
… on some occasions, measures against a possible hazard should be taken even if
the available evidence does not suffice to treat the existence of that hazard as a
scientifically established fact.226
The formulations differ, but the basic theme is the same: If we suspect that something
is a threat to some important values – in particular to human health or the environment – we
should do something about it even when we are not totally sure that it is a threat.
I believe it can be a good idea to get some understanding of the intuitions behind the
principle in order to gain a better understanding of how to use it. It is also important for our
investigation to find out whether the precautionary principle is justifiable from the position
of anthropocentric instrumentalism. The formulations we have seen so far seem to be
consonant with a number of basic moral intuitions that would justify the precautionary
223
Wingspread Conference 1998
See e.g. Gollier & Treich 2003 p.77
225
Grandjean et al 2004 p.282
226
Sandin 2004:2 p.3 This interpretation is stated more or less similarly at many places. E.g. in Sandin et al
2002 p.288, Sandin 2004:3 p.2
224
62
principle, and help us specify what it means and how it should be applied. I will take a closer
look at some of these intuitions.
3.3.1. Promoting the positive versus avoiding the negative
It might be argued as a basis for the precautionary principle, that it is more important
to avoid things that are negative than to promote things that are positive.227 This intuition
could explain expressions like “err on the side of caution”, and “better safe than sorry”. It
seems that the precautionary principle could be interpreted along these lines, 228 but is it a
reasonable position to hold?
Kuntz-Duriseti reasons from an economic perspective and claims that the damage from
a negative economic shock is larger than the value of a positive economic “shock” of the
same size. 229 Ingar Brinck on the other hand attempts to give an evolutionary account of the
intuition. She believes that it has been more important for our survival to concentrate on
negative events than on positive events.230
Kuntz-Duriseti does not provide any argument for his claim other than his intuitions,
but let us take a closer look at Brinck’s idea: If we are in a situation where we can make a
decision we are obviously alive and we have at least some degree of influence over our own
lives. In such cases, it might be correct that we from a “survival perspective” are in a
situation where we have more to lose than to gain. On the other hand, in order to improve
our evolutionary fitness, there seems to be quite a lot more to desire. In order to propagate
our genes – and thereby the inclination to be more negative towards harm than positive
towards improvements – we need to mate, something we might have to be risk-taking in
order to be successful at. In the evolutionary game, risk-taking individuals often lose, but
when they win, the return is high. Therefore, it is not always an evolutionary advantage to be
more negative towards harm than positive towards improvements – just as it is not always an
advantage to be more negative towards harm than positive towards improvements.
227
Holtug 2002, Munthe 1997
see e.g. Munthe 1997
229
Kuntz-Duriseti 2004 pp.293,296
230
Brinck 2005 p.53
228
63
Therefore, from an evolutionary perspective there is probably room for both attitudes in a
population (a mix of “strategies”).
Either way, an evolutionary investigation cannot on its own tell us whether the
intuition is morally justified.
One problem we have to face is that it is not totally clear what it means to say that it is
more important to avoid negative values than to promote positive values. In one
interpretation, going from where we are to a worse position, is a less acceptable option than
not going (the same distance) from where we are to a better position – other things being
equal but independent of where we are on the positive-negative scale. If we e.g. talk in terms
of happiness, this interpretation would mean that it is always worse to make someone less
happy than to abstain from making someone more happy to the same degree no matter how
happy they are to begin with. If we have to choose between an option (A) that will prevent a
decrease in the level happiness for someone who is already in a bliss by 5 “units”, and an
option (B) will that increase the level of happiness for someone in great misery also by 5
“units”, we are obliged to chose (A).
Another – and stronger – interpretation says that all changes for the worse are more
important than any change for the better. If we use the happiness-example above and adapt it
to this interpretation it would tell us that in a choice between an option (C) that will prevent a
small decrease in happiness for someone who is really happy (with say 1 “unit”), and an
option (D) that would largely increase the happiness of someone who is really miserable
(with say 100 “units”), we are obliged to chose (C).
Neither is it clear how to distinguish harm from lack of improvement. When we talk
about harm versus improvement we have to ask “in relation to what?”. Are we talking about
a harm/improvement in relation to the situation in which the affected person is, or are we
talking about harm/improvement in relation to some fixed baseline, and how, if that is the
case, should the baseline be fixed?231 There are also other complications: If we fail to prevent
a pain, would that be an example of a harm or of a lack of improvement? The situation is
getting worse than it is now and could therefore be seen as a harm. On the other hand, it is a
matter of something that would have been in a better state if we had intervened, which
sounds like something we have failed to improve.232 We can even question whether an
intervention that increases someone’s pleasure is just a matter of improvement or if it is also
a matter of preventing a lack of enjoyment that she would otherwise suffer – i.e. of
231
Holtug 2002 pp.268f
64
preventing a harm.233 Apparently, it makes a great difference if we look upon a state of the
world or upon an ongoing process.
Another problem is that it is not quite clear what it means to say that avoiding negative
values are more important than promoting positive values. Important in what sense? Are we
talking of the same scale when we talk of the importance as when we talk about the positive
and negative values in the phrase we are investigating? It might be that we have a meta-scale
according to which moves on the lower scale get different values depending on which way
they move or where on the scale they are. An alternative interpretation would be that the
question about whether negative values are more important than positive values is a moral
question, while the values we are comparing (the positive and the negative values) are about
personal experiences. Such a move is not easy to justify. Why should negative experiences
carry a larger weight than positive experiences of the same size from a moral perspective?
We need independent justification in order to make such a controversial statement.
The intuition saying that it is more important to avoid negative values than to promote
positive values may well be an important explanation for the popularity of the precautionary
principle. However, because it is so controversial, and because it is in itself in need of
justification, I will abstain from using it as a justification or interpretation of the
precautionary principle.
3.3.2. Irreversibility
One common intuition that might help us justify and understand the precautionary
principle, is that some outcomes are unacceptable and should therefore never be risked no
matter what we could gain by risking them – or at least we need extraordinary security
against them.234 In this section, I will discuss this intuition, and I will concentrate on one
particular outcome that looks like a good candidate for being of this particular kind –
irreversibility. Irreversibility is mentioned explicitly by some formulations of the
232
Holtug 2002 pp.268f
Holtug 2002 p.370
234
Munthe 1997
233
65
precautionary principle,235 and is also, as we have seen, particularly relevant in relation to
our investigation.
When Per Sandin discusses irreversibility as an aspect of precaution, he follows
Fleming in viewing it as one of three aspects of ‘threat’ that are relevant for our
understanding of the precautionary principle. The three aspects are: Severity, irreversibility
and preventability.236 If the threat is not preventable, it is meaningless to take precautionary
measures even if it is irreversible (it would not even be possible to identify any measures as
precautionary).
That severity is relevant seems intuitively plausible as well. The more severe an
outcome is, the more important it must be to take precautionary measures against it. It is also
intuitively plausible that some degree of severity is a necessary prerequisite for invoking the
precautionary principle. An event that is irreversible but not negative hardly calls for
precaution, and an event that is only slightly negative but can quite easily be
counterbalanced by the positive effects you get from the process in question (or from
abolishing a process), should reasonably be treated as one value among others and be dealt
with in a normal cost/benefit-analysis. Sandin illustrates the importance of severity by an
example of a boulder that is crushed in order to get gravel.237 This is clearly an irreversible
act, but it is not very severe (or in general bad).
In fact, irreversibility might even on some occasions be a good thing. If we manage to
get permanently rid of some great evil, that is surely positive.
It thus seems that irreversibility cannot be a sufficient reason for invoking an extra
precautious decision procedure. It has to occur in combination with preventability and some
degree of severity. Perhaps it is not that simple though. Cannot irreversibility be considered
as something that is negative in its own right, and thereby automatically fulfil the severity
criterion just by being irreversible? Obviously, irreversibility can have a negative intrinsic
value for some people, but probably not a great enough negative intrinsic value to fulfil the
severity criteria in its own right.
Another alternative is that something else has a very high intrinsic value, and that
irreversible changes by necessity destroy this value. That way, irreversibility would not have
a negative intrinsic value, but by being inherently destructive in relation to something that
has a positive intrinsic value, the effect would be very similar in that irreversibility would be
235
Most notably the Rio formulation (see above). See also Herremoës et al 2001 p.13
Sandin 1999 p.892
237
Ibid
236
66
necessarily negative. I can imagine two widely held values in relation to which irreversibility
is necessarily negative, namely choice value and democracy. The reason why irreversibility
is necessarily negative in relation to these two values is the same in both cases: An inherent
feature of irreversibility is that it limits our future range of choices. This means that
irreversibility always has a negative choice value. This in turn means that we take decisions
on behalf of all future generations – decisions that they will never be able to change.
Therefore, it is a democratic problem as well. In relation to both these values – choice value
and democracy – irreversibility seems to be necessarily negative. This means that if we value
freedom of choice or democracy, the fact that a certain decision is irreversible, is by
necessity an argument against it.
Is this a sufficient reason for removing irreversible decisions from the realm of
acceptable choices or at least to grant it extra ordinary treatment? I do not believe it is.
Choice value and democracy are two of many values that might be affected by, and therefore
should be considered, in a decision. Even if they are important values, we may assume that
they can be overridden by other values. It does not justify that we give irreversibility any
extraordinary standing in the decision process. That something is a problem by necessity
does not tell us anything about how severe the problem is. The problems we have discussed
do not seem to be severe enough to grant irreversible changes the special status we are
looking for.
I do not believe we need to claim that irreversibility is a sufficient prerequisite for
invoking the precautionary principle however. When we are dealing with a problem that is
severe in its own right or for some independent reason, and it turns out to be irreversible as
well, the irreversibility can be a factor that enhances the problem to such a degree that it
gives the problem a special status. Clearly, a decision that might lead to a severe problem,
and that is also irreversible, must be treated with extra care. This could be handled by
following the precautionary principle and demand that the burden of proof (in the form of
showing that the suspicions are unfounded) should rest on those in favour of the irreversible
alternative.
For instance, it seems reasonable that in a situation where we suspect that a certain
resource might become very important in the future, we should be extra careful not to
irreversibly destroy it even if we lack strong evidence about its future importance. It even
looks reasonable to say that if we suspect that something will be more important in the future
than the gain we will get from destroying or depleting it today, we need extra strong proof
67
against this suspicion if the destruction or depletion would be irreversible. This means that
apart from being a problem due to its special relation to choice value and democracy,
irreversibility is also a problem when combined with something that may turn out to be
problematic for some other reason. This brings us back to the discussion about the boulder:
If we suspect that the boulder might turn out to be more important in the future than the
gravel is today and in the future, then we must not destroy it unless we have good arguments
against this suspicion. Generally, if we suspect that something after being irreversibly
changed may turn out to be more important than the goods or services we get now and in the
future from changing it, then we should not change it in an irreversible way unless we have
very good arguments against this suspicion.
Irreversibility can therefore in many cases of uncertainty – for instance about the future
value of different resources – justify a change in where we place the burden of proof.
Irreversibility does not just have a tendency to complicate decisions about resources. It
seems to have effects that go even deeper. Per Sandin compares the precautionary principle
with a decision principle used by insurance companies: When making business decisions, the
insurance companies try to “…maximize expected monetary value, but only if bankruptcy is
not one of the possible outcomes.”238
This seems like a sensible decision principle: Use cost/benefit-analyses but make no
decisions that if they fail will result in bankruptcy.
The question is: What makes bankruptcy so special? I believe that a substantial part of
the explanation lies in its irreversibility: It is bad if we lose money on a deal, but we can
come back and make money on another deal. It is also a pity if we stay out of a deal that
would have rendered us a great profit, but we can in general make money on another deal
(even though we have lost some opportunity value). If we go bankrupt on the other hand, it
is over.239 Ordinary cost-benefit analysis may well be the most rational decision method
when we talk about “ordinary” events such as recurring economic deals. In these cases, the
expected value is probably a good account of the long-term gain or loss, and extremes that
happen quite seldom are in general outweighed in the long term by the sum of the smaller
but more common events. On the other hand, if we are talking about bankruptcy or about the
irreversible loss of irreplaceable life-supporting systems (the “ultimate bankruptcy”), the
238
Sandin 2004:2 p.8
There is of course an important difference: A bankruptcy is obviously not irreversible in the same way as is
loss of irreplaceable life support systems. A company can go bankrupt but the people involved can live on and
eventually start a new business – which might explain why some aggressive actors on the market are after all
prepared to risk bankruptcy to get a chance at the really big harvest. It illustrates the main idea nevertheless.
239
68
situation is extra tricky in that this particular type of effect cannot be allowed to happen even
once. In situations like these, it seems rational to adopt an alternative strategy for decisionmaking. If we go for the reversible alternative instead of the irreversible, we have an option
to choose the irreversible alternative later if further investigations show that it is safe.240
This brings us back to the discussion we had in section 2.5 when we noted that the
irreversibility of extinction is probably an important reason why extinction is seen as morally
problematic. As we saw in Sandin’s example, it might also be a paradigm example of a
widely held intuition that plays an important role, not just when we talk about extinction, but
also in other decision situations where “game over” is among the possible outcomes.
The conclusion has to be that apart from being inherently bad in relation to choice
value and democracy, irreversibility also has the property of making bad things worse in a
way that is particularly significant for both the general understanding of the precautionary
principle and for our investigation. This goes especially for – for lack of better terminology –
“game over” situations, that is, for situations that are not even allowed to occur once.
Is irreversibility then a necessary prerequisite for applying the precautionary principle?
Suppose we substitute the smashed boulder in Sandin’s example with a species that is
pushed to extinction, and add the assumption that we could recreate it exactly as it was (and
at the same time assume that the environment in which it lived has not changed etc.). The
intuitions go apart here. On the one hand, irreversibility does seem to be relevant. On the
other hand, if a certain state of the world is bad, then it is bad even if it is just temporary. Let
us assume that we are dealing with a species that is instrumentally important for us. Is not
then the state of the world worse for us during the time the species is gone even if we know
that we can get it back? We would in any case lose what the economists call opportunity
value, that is to say, opportunities for utilisation of the species. Some people with a disease
that could have been cured by a medical drug from the species would die. This is bad even
though we will be able to cure future people once we have revived the species.
Imagine that we exterminate a species that could – but will not – be revived. It seems
to me that this cannot be accepted at the same time as we maintain that the effects of an
irreversible extermination are unacceptable. I therefore believe that it would be unreasonable
to consider irreversibility as a necessary prerequisite.
Our conclusion is that irreversibility is not sufficient and not necessary for the
precautionary principle to be justified. Its inherently negative impact on choice value and the
240
Gollier & Treich 2003 pp.83,88
69
democratic rights of future generations is an argument against making irreversible decisions.
It is not strong enough though to give it the special status we need to support our intuition.
However: When the irreversible change is problematic also in some other way, the
irreversibility greatly enhances the severity, and it seems very reasonable to assume that it
can push it over the threshold for what is unacceptable. This goes especially when a “game
over” situation is among the suspected outcomes.
This will provide a strong justification for the precautionary principle: When we
suspect that an act may lead to a severe effect that would also be irreversible, we need strong
evidence against this suspicion before accepting the act as an acceptable choice.
Furthermore, some irreversible changes are such that they are not even allowed to
happen once – so called “game over” situations. The burden of proof on someone who
proposes what might have such an effect has to be extra strong.
Since both severity and suspicion come in degrees, the evidence we need against the
suspicion should also come in degrees depending on how strong our suspicion is and on the
severity of the problem.241
3.3.3. The value of human health
It is sometimes claimed that human health and the environment tend to be downplayed
in traditional decision procedures.242 It is also explicitly stated in many formulations of, and
discussions around, the precautionary principle that it should come into play in situations
where there is a threat against human health or the environment.243
This indicates that one of the intuitions behind the principle is that human health and
the environment need to be better protected than has been the case in traditional decision
procedures.
If this is correct, it means that the precautionary principle indicates a change of value.
Not, like in 3.3.1, a change in how we weigh positive and negative value, but a change in
what we find most important.
241
Gee 2006 and Grandjean 2004 p.208 reason along the same lines even though they do not discuss
irreversibility in particular but severity in general.
242
Turner & Hartzell 2004 p.453, Lin 2001 p.129, Wingspread Conference 1998
243
Gollier & Treich 2003 p.81, passim, Sandin 1999 p.889,892, Sandin 2004:1 p.1, Turner & Hartzell 2004
p.449, Wandall 2004 p.270
70
That human health should be highly valued from an anthropocentric vantage point
seems obvious, but it is not obvious how it should be valued in relation to economic value.
Especially since economic value can be transformed into human health (by using economic
growth to improve health care), and the other way around. There are also attempts to
conflate the two by measuring human health in monetary terms. Maybe the solution is to be
found at least in part in the way the latter is done. It may be a general intuition that when
economists and decision makers make comparisons between human health and other human
values (whether these comparisons are expressed in monetary terms or not), health is
assigned a value that is too low. It seems that the value people place on human life and
human health is ascending. If this is correct, shifting the burden of proof could be one way of
accounting for the change in the decision procedure.
The question that immediately arises is whether this change in value cannot be dealt
with simply by assigning a higher value to human health in an ordinary cost/benefit-analysis.
The answer is that the problem goes deeper than that. The entire decision procedure seems to
be biased to the disadvantage of values like human health.
Traditionally, the burden of proof has been placed on those who want to decide against
the use of a substance or a process that is – or has a good chance of being – economically
profitable. It seems to be consciously or unconsciously assumed that economic gain is the
default reason for acting or not acting in a certain way and that very good reasons are needed
for those who want to change or abolish a money generating practice.244 A particular way of
valuing outcomes is in other words built into the process. One important intuition behind the
precautionary principle seems to be that this needs to be changed. It is very common to
interpret the precautionary principle as consisting of, or at least implying, a change of the
burden of proof.245 As we have seen, changing the burden of proof may be one way of
dealing with the intuition that irreversibility has a tendency to worsen bad outcomes. Where
we place the burden of proof also seems to be the result of how we prioritise between the
alternatives we are deliberating about. The precautionary principle may thus be justified by
the intuition that when human health is at stake, that should be the default value instead of
economic profit. That also means that we can interpret the principle as telling us that
someone who wants to make a decision that may be detrimental to human health should be
244
Herremoës et al 2001 p.180, McGarvin 2001 p.25
See e.g. Grandjean et al 2004 p282, Kuntz-Duriseti 2004 p.291, Lin 2001 p.131, McGarvin 2001 p.23 note
3, Munthe 1997, Turner & Hartzell 2004 p.453, Wandall 2004 p.270, Wingspread Conference 1998. See also
the section on irreversibility above.
245
71
assigned a burden of proof at least as heavy as those who want to ban or regulate an act that
is potentially profitable.
3.3.4. The cost of being late
We have seen that traditionally it has been necessary to present strong evidence for a
ban or even regulation of a useful or economically profitable substance or process. Gathering
the necessary evidence may take some time and much can happen during this time.246 In
recent history, both people and the environment have often suffered (and in many cases still
suffers) unnecessary harm because the decision makers have waited for more conclusive
evidence before dealing with the problem. The ozone depleting CFC is one example. If we
had not waited so long for conclusive proof that CFC destroys the ozone layer, we could
have banned it earlier and avoided some of its long-term effects.247 Benzene, asbestos, and
lead additives in petrol are some other well-known examples,
248
and there are probably
many more.249
The time factor is especially important when dealing with complex things like
ecosystems or the human body. The effects often do not show until the substance or process
has been in use for a while (for instance because of the threshold effects we discussed
earlier).250 This means we will in general not have conclusive evidence that a substance is
dangerous until it is already in the system – maybe in large quantities – and we may have to
live with the problem for a long time. When we deal with non-linear relations, it is also very
difficult to establish a clear cause-effect relationship, and we may have to wait even longer
than normal for conclusive evidence.
Therefore, taking action before we have conclusive evidence is in fact something that
in certain cases is required by anthropocentric instrumentalism (as it would be by any moral
theory).
246
Gee 2006, Herremoës et al 2001 passim, McGarvin 2001 p.20, Sandin 1999 p.906 note 10
Gee 2006
248
Beltrán 2001 p.3, Gee 2006, Gee & Greenberg 2001 p.59, Grandjean et al 2004 p.283, Infante 2001 pp.41f
249
For more examples, see Grandjean et al 2004 pp.282f, Herremoës et al 2001 p.173,176, Ibarreta & Swan
2001 p.86, Koppe & Keys 2001 pp.64f,71, Lambert 2001 pp.32,34
250
Farman 2001 pp.76f, Gee & Greenberg 2001 p.55, Gollier & Treich 2003 p.79, Ibarreta & Swan 2001 p.87,
von Keauss & Herremoës p.117
247
72
The title as well as the content of the EEA report on the precautionary principle Late
lessons from early warnings, states very clearly that the editors consider the cost of time loss
as a very important motivation for the precautionary principle.251 The idea that we under
certain circumstances should not wait for conclusive evidence before taking action is as we
saw in the beginning of this chapter, very central in all formulations of the precautionary
principle.
I believe the problems connected with time loss is probably an important justification
for the precautionary principle – maybe the most important of all. All “real world” decisionmakers worthy of the epithet – from stock traders to military commanders – know that even
though it is important to have accurate information, it is at least as important to act in time.
Maybe the tendency to give an unreasonably high priority to accurateness over acting
in time, has been uncritically adopted from the realm of science and philosophy? In our
“world”, the search for knowledge and understanding is the ultimate goal. In society in
general, there are many other goals and the relative cost of losing time in relation to being
wrong is sometimes much higher. Decision makers in society need information, and the best
way of getting reliable information is to turn to those who have the formation of knowledge
and understanding as their ultimate goal. However, since the goal of the decision makers is
not precisely the same as the goal of those who provide them with information, we need a
transformation rule. I believe it is very important that this is not done by changing the rules
or the aims of science. Instead, we need an adaptor between the two realms – the realm of
science and the realm of practical decision-making. It seems that the precautionary principle
could be such an adaptor. The traditional formulations of the precautionary principle like the
Rio formulation and the Wingspread formulation are not sufficiently clear. They talk about
the importance of not waiting for conclusive evidence before taking measures, and they
mention the importance of considering the value of what we might lose if we do not. That it
is important to consider the values at stake can however just as well be an argument for
taking the extra time needed to make sure that an intervention does not worsen the situation.
In order to get to the conclusion they promote, we need an additional argument stressing the
importance of timing when it comes to securing the values in question. As we have seen in
this sub-section, timing is important and has shown to be important in many situations,
which means that this premise is very well underpinned. Earlier in this section, we have seen
251
Herremoës et al 2001 p.1
73
that the value aspect must be decisive when we make decisions under uncertainty, and that
the decision procedures must be adapted to account for that.
I conclude that when timing is essential we have to move further towards the “beingin-time” end of the “being-in-time/being-right” scale. The stronger the suspicion that timing
is essential and the more essential we suspect it to be, the closer ought we to be to the
“being-in-time” end.
The opposite is also true. The stronger the suspicion that correct information is
essential and the more essential we suspect it to be, the closer ought we to be the “beingright” end of the scale. Where the cut off point lies, i.e. when it is – to put it crudely – time
to “stop thinking and start acting”, will then have to be decided in each particular case based
on the relative importance of these two factors for the value at stake.
Since there have been quite a few cases where a lot of damage has been caused
because regulators have waited too long before taking action, extra attention probably has to
be given to the timing aspect for pure pedagogic reasons – in order to increase the awareness
that timing does play an important role.
3.3.5. False positives versus false negatives
Scientists do not like to be wrong. In the scientific world, being wrong is in general
worse than not being right. This does not only mean that scientists prefer to postpone their
judgement until they have more evidence. It also means that they are biased to err in favour
of false negatives over false positives. It is worse for a scientist’s career to be exposed as
having claimed something that turns out not to be the case (a false positive), than to be
exposed as having denied something that turns out to be the case (a false negative). 252
Birgitte Wandall calls the bias towards false negatives the “conservative burden of
proof”, since it confers the burden of proof on those who make a positive claim.253 She also
points out that the reason for this tendency is probably that one of the main values guiding
science is to keep the scientific corpus (the body of statements accepted by science) as free
252
Gee 2006, Gee & Greenberg 2001 p.60, Grandjean 2004 p.217,384, Herremoës et al 2001 p.184, Mattsson
2005 p.9, Wandall 2004 p.267 note 6
253
Wandall 2004 pp.267,269, Wandall 2005
74
as possible from false statements.254 This is the scientific community’s own version of
“erring on the side of caution”, and it is doubtlessly a good reason to trust science: If
something is claimed by the scientific society to be true, it probably is true. This also means
however that if the scientific community does not want to exclaim something as true, it does
not necessarily mean that it is false. To believe that it is, seems to be an all too common
mistake that in some situations can cause a good deal of harm.255 It is after all not obvious
that the goal of avoiding false positives is always a superordinate goal in society at large. In
many cases where other values are at stake (values – like human health – that may not be
basic epistemic values but are important in anthropocentric instrumentalism as well as other
moral theories), false negatives can have at least as severe effects as false positives. The
effects of not regulating or banning something that is dangerous can be at least as bad from a
moral point of view as the effects of regulating or banning something that is harmless. If we
accept the intuition from section 3.3.3 that human health needs to be assigned a higher value
than has traditionally been the case, it is probably in many cases more important to avoid
false negatives than to avoid false positives. 256 We therefore have a case that is parallel to the
intuition discussed above regarding the value of acting in time. The conclusion must also be
the same: We need a decision rule that can compensate for the difference in goals between
science and practical decision making,257 and the precautionary principle seems to be
precisely cut out for that job. The cost of false negatives for a host of human values,
including human health, seems just like the cost of time loss to be a strong argument in
favour of the precautionary principle: Just as it is sometimes more important to act in time
than being exactly right, it is sometimes more important to avoid false negatives than to
avoid false positives – depending on the values at stake.
It is therefore reasonable to handle this intuition in a similar way: When we make
decisions in matters where some important value is at stake (e.g. human health), and when
we suspect that a certain decision may result in serious damage to this value, and when we
suspect that a false negative is a more substantial threat to the protection or promotion of this
value than a false positive, then we should move our priorities from being biased towards
avoiding false positives in the direction of avoiding false negatives.
254
Wandall 2004 pp.267,269
Gee 2006
256
Mattsson 2005 p.9, Wandall 2004 pp.269f, Wandall 2005
257
For a discussion on the goals of science, see Wandall 2004 p.267
255
75
It is important to see that it is not a matter of going from a system that is totally
immune to false positives to one that is totally immune against false negatives. A system
immune to false positives would not produce any statements about the world at all (only
analytical statements would pass the test), while a system that is immune to false negatives
would not be able to exclude anything other than pure contradictions. Everything would be
considered as possible, and no possibility could ever be excluded from our considerations.
Changing priorities from being right in the direction of acting in time can be done
simply by taking action sooner instead of waiting for more reliable information, but how do
we in practice move our priorities from avoiding false positives to avoiding false negatives?
One way would be to transfer the burden of proof from those who claim that the
practice or substance is dangerous to those who claim that it is safe in relation to the values
in question. Instead of asking, “is this dangerous?”, we ask “is this safe?”. This is the
solution Wandall suggests based on her categorisation of the scientific urge to avoid false
positives as a “conservative burden of proof”.258
The idea of shifting the burden of proof can be interpreted as an “either/or-solution”.
Either we place the burden of proof on one side, or we place it on the other. I think it would
be more fruitful to go for a successive solution – as in the previous three subsections. Just as
something can be more or less valuable, a threat can be more or less severe, and timing can
be more or less important, avoiding false negatives can be more or less important. What we
need is a method that allows us to change focus in proportion to the importance of avoiding
false negatives relative to the importance of avoiding false positives. We need to be able to
increase or decrease the burden of proof successively on the different sides. This could be
dealt with for instance by moving the confidence level. The scientist can supply the decision
makers with a set of answers based on different confidence levels. This would allow them to
choose a confidence level that fits the distribution of the burden of proof that is appropriate
given the importance of avoiding false negatives in relation to false positives. At the same
time, the scientific community can choose to include only the answers based on the most
conservative confidence level in the scientific corpus. It would also make the procedure
more transparent and reduce the power scientists have over deciding the relative importance
of avoiding false positives versus avoiding false negatives – on behalf of the entire society.
A weakness in this suggestion is that people lacking insight in how science works and
what it is about, could point at the discrepancy in confidence level between the assertion
258
Wandall 2004 p.270
76
incorporated in the scientific corpus and the assertion on which policy/legislation is based,
and claim that the latter is not based on sound science or at least does not fulfil the most
rigorous scientific demands. It is my humble hope, however, that it is possible to explain the
process to these people, and especially to point out both the distinction between the scientific
method and the choice of confidence level, and the difference in goals between science and
society, which is keeping the scientific corpus clean one the one hand and
protecting/promoting a host of other important values on the other. It would thus hopefully
be possible for the public to understand that making decisions based on a confidence level
that is less biased in favour of avoiding false positives is not the same as making decisions
based on a less scientific method. Instead, it is a matter of making the scientific results more
useful in relation the different but just as legitimate goals of society in general.
3.3.6. Conclusions
One important result from this section is that the precautionary principle seems to be
acceptable, and probably required, from the point of view of moral anthropocentrism.
Furthermore, the precautionary principle is based on a number of different intuitions. What
we call the precautionary principle is therefore a conglomerate of several principles that has
precaution as a common denominator.259
The precautionary principle should be used in order to deal with things that traditional
decision procedures are unable to deal with, such as the scientific bias towards false
negatives, loss of precious time, severe harms – especially irreversible ones – and certain
important values like human health, that are systematically downplayed by the traditional
decision methods.
Much more needs to be said in order to find out how exactly to apply the precautionary
principle. For instance, we have to specify the degree of suspicion needed in order to ban a
useful substance with reference to the principle. We also need to specify what kinds of harm
that justifies such acts.
Based on what we have seen in this section we can make some conclusions however:
259
I will for simplicity go on using the term ‘the precautionary principle’.
77
* When we suspect that a process might result in unacceptable harm, we need extra
strong evidence against this suspicion.
* The stronger the suspicion and the more unacceptable the harm, the stronger
evidence we need in order to accept the process in question.
* When we suspect that a process may result in a severe and irreversible change, we
need extra strong evidence against this suspicion in order to accept the process as a viable
option.
* This goes especially when the change may result in a “game over” situation.
* Those who want to carry out a decision that is suspected to be detrimental to human
health should be assigned a burden of proof that is at least as heavy as those who want to ban
or regulate an act that is potentially profitable.
* When we suspect that timing is important in order to protect or promote an important
value, we need to move towards the “being-in-time” end on the “being-in-time/being-right”
scale.
* The more important we suspect the timing to be and the stronger our suspicion, the
closer to the “being-in-time” end do we have to move.
* We also need to be able to successively change the burden of proof between positive
and negative claims in proportion to the importance of avoiding false negatives relative to
the importance of avoiding false positives (e.g. by adjusting the confidence level).
3.4. Problems with the precautionary principle
There are some frequently occurring objections to the precautionary principle.260 It has
been described as being ill-defined, un-scientific or even anti-science, hindering progress,
increasing the total risk instead of decreasing it, and trying to substitute science-based
decision-making by value-based or ideology-based decision-making. In order to come to a
reliable conclusion of whether the precautionary principle really is in accordance with the
basic intuitions of anthropocentric instrumentalism, we have to take a closer look at these
objections. I will start the question of whether the precautionary principle is too poorly
defined to be of any use.
78
3.4.1. Is the precautionary principle ill-defined?
Many observers have pointed out that the meaning of the principle is unclear.261 Some
authors believe that this is an inherent trait in the principle,262 while others are confident that
it is possible to come to terms with the obscurities.263
In the previous section, we too noticed that much work needs to be done in order to
clarify the precautionary principle. On the other hand, we did manage to identify some basic
intuitions behind the principle. Based on these intuitions in turn we also managed to sketch
out some ideas of how the precautionary principle should be interpreted and implemented.
The fact that there is more than one intuition behind the principle, and that the
intuitions need to be accounted for in different ways, shows that what we call the
precautionary principle is better thought of as several principles brought together under one
heading. This may remove some of the confusion.
Are the remaining obscurities a terminal defect in the principle? I do not believe it is.
First of all, it seems clear that much more can be done in terms of clarification than we have
done here. What is even more important is that the obscurities of the precautionary principle
are not more serious than in most ethical norms. Even if ethical norms present us with
difficulties when it comes to interpretation and implementation, it would not be advisable to
stop using them.
We also have to be aware that to compare the precautionary principle to the more
simplified traditional decision methods only in terms of clarity would not be fair. The
precautionary principle is invented in order to handle situations where the simpler solutions
do not work. It is therefore only to be expected (though it is not a necessary truth) that it is
more difficult to formulate in a clear and simple manner. To the extent that the traditional
decision methods are clearer and simpler than the precautionary principle, it is so to a large
degree because they ignore the intuitions that the precautionary principle accounts for.
In the good tradition of Ockham’s razor, simplicity makes a solution better than the
alternatives only if the solution in question is also as good as, and as comprehensive as, the
alternatives. A cost/benefit-analysis is not satisfying in those situations the precautionary
principle is cut out to deal with, which means that its simplicity will be of no help.
260
Sandin et al 2002 pp.287f, Sandin 2004:3 p.8
Gollier & Treich 2003 p.99, Munthe 1997, Sandin 1999 p.894, Sandin et al 2002 p.289, Turner & Hartzell
2004 passim
262
see e.g. Turner & Hartzell 2004 p.451
263
See e.g. Sandin et al 2002 p.289
261
79
Our conclusion is that the precautionary principle is ill-defined and needs much
improvement, but the problem does not seem to be fatal, and can probably be improved quite
a lot. The precautionary principle is also better than the simpler alternatives when it comes to
accounting for many basic moral intuitions – in spite of its obscurities.
3.4.2. Is the precautionary principle anti-science?
The precautionary principle has been criticised for being unscientific and of
marginalising the roll of science.264 It has even been accused of being “anti-science”.265
The Precautionary Principle tells us not to wait for incontestable scientific proof of the
dangerousness of a process before we take action against it. This clearly looks like the
principle urges us to pay less attention to science – at least when we are short of time. Is not
this an unscientific – not to say anti-scientific – way of making decisions compared to the
more traditional method of scientifically analysing the risks and putting the probabilities into
a cost/benefit-analysis? Not necessarily. The latter method works best when we have
virtually the knowledge we need.266 The question we have to answer is what to do when we
do not have the information we need.
As we saw in section 3.2, there are different strategies for dealing with insufficient
knowledge. Two of the strategies involve that we do not intervene until we know more. This
may well be the most prudent choice in some situations of imperfect knowledge, for instance
if we are in an acceptable situation and suspect that any change can cause serious damage if
it is not properly thought through. However, not all situations are like that. As we saw
before, it is not uncommon that quite severe problems have been allowed to go on and in
some cases to become even worse because we have waited for better evidence. In situations
like that, the strategy of waiting for better knowledge does not seem like a good idea.
An alternative strategy presented in section 3.2 was to act from the best available
information and hope it is correct. We saw then however that there are serious drawbacks in
the form of risks that we do not do anything to protect us from.
264
Sandin et al 2002 p.295
Grandjean 2004 pp.209,214
266
Grandjean 2004 p.203
265
80
The fourth alternative was to use the precautionary principle. The way we have
interpreted the principle, it tells us to be aware that sometimes being too late is at least as
problematic as being wrong, and therefore we need to adjust our decisions along the “beingright/being-in-time” scale. The adjusting should be made according to how important it is to
be in time relative to how important it is to be right in relation to the values at stake, in the
situation we are dealing with.
This is obviously not an easy judgement to make, but it is none the less routinely done
by various decision makers. It is quite obvious that this kind of judgement cannot always be
correct. However, if we abstain from making a decision and assume that being right is the
only important thing, then we have deliberately excluded an indisputably important
dimension of the decision, and it is hard to see how that could be an improvement.
What is important as well is that the precautionary principle does not belittle the
importance of being right. It claims that it is sometimes even more important to be in time. It
is so to speak better to be approximately right and in time than being absolutely right but too
late. 267
It is also important to note that the precautionary principle does not tell us to stop
searching for a better understanding.268 An important implication of the concept of
precaution is that decisions should be reviewed periodically in the light of new scientific
findings.269 This may even lead to more – not less – research being done.270 It could therefore
be argued that in this respect, the precautionary principle is promoting science rather than
opposing it. Without the precautionary principle, we have the opposite situation: As long as
we lack sufficient knowledge things go on as usual. This gives an advantage to those who do
not produce sufficient data to make a risk analysis,271 which in turn seems to be a tempting
incentive to block scientific progress. More research might find out that what we are doing is
dangerous. As long as we do not know, we can go on as usual. This is especially tempting in
the frequently occurring cases where those who benefit from the practice are not the same as
those who run the risks if the practice turns out to be dangerous.
The precautionary principle does not stand in the way of science but advices us on
what to do about a problem while we wait for the new information and the better
267
Grandjean 2004 p.211
In fact in the EU interpretation it is explicitly stated that “scientific research shall be continued”. See
Grandjean 2004 p.206
269
Grandjean 2004 pp.210,214, Lin 2001 p.131, Sandin 2004:1 p.10
270
Grandjean 2004 pp.210,214
271
Grandjean 2004 p.208
268
81
understanding. There must reasonably be a policy for that – apart from the policy about
improving knowledge. The time we have to wait for better knowledge is sometimes quite
long, and what happens during that time may have rather far reaching consequences. I cannot
see that it is more rational to have decision makers sitting down in inertia than to have them
act in the most rational manner possible during the time it takes the scientists to form a better
understanding of the situation. If we see someone drowning and wait until we are absolutely
sure that she will in fact drown if we do not help her, then we will probably not get there in
time to save her. If our criteria are really strict, we may not even be convinced until we have
seen her drown – and then it is definitely too late. I believe that in good decision-making we
always have to weigh the advantages of high certainty of the decision against the advantages
of acting fast. True, acting on incomplete knowledge can worsen the situation, but so can
inertia as we have seen. Therefore, we return to the question: Which aspect – the being-right
aspect or the being-in-time aspect – is the most important one in the situation given the
values at stake? The precautionary principle lets the being-in-time aspect enter the procedure
without excluding the being-right aspect.
It could be argued that just by letting in the “being-in-time” aspect we do in fact
marginalise science by allowing for the possibility of moving our priorities at least to some
extent away from the “being-right” aspect. It is also quite reasonable to believe that the
quality of the decision will decrease if we base it on less scientific evidence.272 It can
therefore not be denied that the precautionary principle to some extent diminishes the role of
science and that this is bad. We have to remember however that not using the precautionary
principle diminishes the time aspect and that this is bad. We are therefore back to the
conclusion in 3.3.4: Both being-right, and being-in-time is instrumentally valuable.
Sandin et al also point out that the term ‘unscientific’ can be interpreted in a weak way
and in a strong way. A decision is according to this distinction unscientific in the weak way
if it does not build on scientific evidence, while it is unscientific in the strong sense if it
disregards scientific evidence. Since the precautionary principle tells us what to do in
situations where there is insufficient scientific evidence to build on or disregard, it is
unscientific in the weak sense of the word, but not in the strong sense.273
We should also point out that not using the precautionary principle and doing nothing
until we are totally sure, would in fact also be unscientific in the weak sense. It tells us to
272
273
Sandin et al 2002 p.295
Sandin et al 2002 pp.295f
82
make a certain decision (in this case to wait) that is not based on science (remember that the
reason for the suggested inertia is that we lack scientific evidence).
3.4.3. Values instead of science
The precautionary principle is sometimes seen as an attempt to substitute science with
values, which is considered as a strong objection against the principle.274
I think it is quite clear that the precautionary principle contains value statements and
that much of the motives behind the principle is a matter of values (see section 3.3).
However, the precautionary principle is not supposed to be a description of the world, but a
decision method. All decisions are valuations. If we have no values, we cannot make any
decision. To say that we should do A rather than not-A is to say that A is better than not-A.
I.e. we have made a value judgement. Any alternative decision procedure must also be based
on values, and as a matter of fact, the existing alternative decision procedures – like risk
analysis – are based on values as well.275
One important motivation behind the precautionary principle is to promote certain
values like human health, but – again – decision procedures that do not tell us to be
particularly careful when human health or other important values are at stake are equally
evaluative. In section 3.3.3 we saw that the traditional decision methods are biased in favour
of economic profit. We may also remember that the criteria for what statements to
incorporate in the scientific corpus are in fact based on values (so called epistemic values).276
In section 3.3.5 we saw an example, in the form of the evaluation that false positives are
worse than false negatives. The scientific community even evaluates how much worse a false
positive is when they chose a certain confidence level. I believe that one of the major virtues
of the precautionary principle is that it brings out the evaluative aspect into the open and
makes it a subject of discussion and deliberation.
To base decisions on sound science is excellent and should always be strived for, and
there is nothing in the precautionary principle that tells not to use the best available scientific
evidence, or to look for better scientific evidence. To hide evaluative considerations behind a
274
Sandin et al 2002 pp.287f,294
Grandjean 2004 p.209, Sandin et al 2002 p.294
276
Wandall 2004 p.267
275
83
veil of quasi objectivity on the other hand is not an acceptable way of making decisions, and
it does not make the decision more scientific. It only makes it look that way and is thus just
less honest. It has been, and still is, very easy to brand decision criteria and decision methods
that favour the environment or human health as being evaluative while promoting economic
profit is seen as the default value or even as no value at all. This is a way of making
decisions that is worrying, and if the precautionary principle can contribute to bringing the
hidden values out in the open, it must reasonable be an argument in favour of the principle –
not against it.
The precautionary principle is thus not a matter of substituting science with values but
of substituting values with values – and of making the values more clearly visible.
There is still one aspect of the precautionary principle that may be interpreted as
substituting science with values. We have seen that when important values are at stake and
the uncertainty is large, we should be extra careful not to jeopardise the values. This can be
interpreted as saying that if the uncertainty regarding the probability part of a risk assessment
is large, then we should give less weight to the probability part of the equation, and more to
the value of the possible outcome.
Strictly speaking, this is not a matter of substituting science with values since the
precautionary principle does not tell us to stop looking for better predictions – or to disregard
the evidence we do have. What it tells us to do is to distrust uncertain results (which seems
like a sound scientific approach), and to adjust our decision method in light of the
uncertainties in the predictions. Uncertainties concerning a scientific result must be a part of
the scientific result and therefore accounted for by the researcher and used in the decision
procedure. If the uncertainty is such that an error in one direction would be worse than an
error in the other direction in relation to the values we want to promote or protect, it would
no doubt be irrational not to account for that in the decision.
84
3.4.4. Favouring the status quo
It is often claimed that the precautionary principle demands an unreasonably high
degree of certainty from new methods and technologies, and therefore is biased in favour of
the status quo and against progress and innovation.277 It is even claimed that if the
precautionary principle were consistently applied, it would in effect lead to a halt for all
innovation.278
One part of the explanation as to why many people have made this interpretation might
be that they associate ‘precaution’ with ‘caution’ and ‘caution’ with ‘inertia’.279 The
precautionary principle has probably also been used in that way by political decision makers.
I do not believe that this is the proper way of using the principle however. In fact, none of
the classical formulations even indicate such an interpretation. For instance, the Rio
formulation explicitly urges us to “take measures”. That is difficult to interpret as favouring
inertia.
What might make the precautionary principle biased towards the status quo would be
if it told us to take precautionary measures only when it comes to new ideas, or demanded a
higher degree of security for new ideas.280 Nothing in the classical formulations – or in my
conclusions – points in that direction however.281
Consider the intuitions we discussed in the previous section. Only the first of the
investigated intuitions seems to indicate a bias towards status quo. If the main motivation
behind the principle were the intuition that avoiding the negative is more important than
promoting the positive, it would probably – depending on how we interpret the idea (see
section 3.3.1) – make sense to be more cautious against new ideas than against old ones.282
However, as Munthe points out, it would not always make sense, since we may, by a new
invention or idea, in some cases stop a change for the worse that is on its way. This means
that even the intuition that the negative carries larger weight than the positive can in some
cases favour innovation (depending on how the intuition should be interpreted). However, in
277
Cuccio 2005, Miller et al 2001
Gollier & Treich 2003 p.98, Grandjean 2004 p.208
279
Donna Maher (Maher 1999-2000) clearly points out the difference between ‘caution’ and ‘inertia’. It is
probably also important to distinguish between ‘caution’ and ‘precaution’ since a shift between these two terms
seems to be quite common in the debate concerning the precautionary principle.
280
Lin 2001 p.129
281
Even if the precautionary principle has often been applied in a way that favours the status quo, we can at
least see a tendency in the other direction in the new EU-regulation of chemical substances (REACH). One of
the most important principles in REACH is that not only new chemicals but also chemicals already in use are to
be tested.
278
85
most cases a precautionary principle based on the intuition that it is more important to avoid
the negative than to promote the positive, would be biased towards the status quo.283
The intuition that it is more important to avoid the negative than to promote the
positive is very controversial however, and it suffers from problems concerning both how it
should be understood, and how it should be justified. I therefore choose not to use that
intuition in my conclusions of how the principle should be interpreted and applied. I can
imagine though that those who embrace that intuition might end up in an interpretation of the
principle that favours the status quo.
This emphasises the conclusion that the general – undifferentiated –precautionary
principle we meet in the classical formulations and in the general debate, seems to be
motivated by various intuitions yielding different conclusions. It also shows again why an
investigation of the intuitions behind the principle is important and why it is important to
distinguish between the different “sub-principles” that follow from the different intuitions.
Another reason why the precautionary principle has been seen as a threat to progress
and innovation might be found in the way we define ‘progress’ or ‘innovation’. There is a
considerable difference between stopping progress or innovation, and redirecting it.284 The
precautionary principle will probably stop some innovations that are deemed less safe. On
the other hand, it ought also to give a competitive advantage to those who develop safer
alternatives, and thereby in fact encourage some types of innovation.285
People who profit from a particular development probably tend to see it as a progress
even if other people suffer from it or would gain much more if the development took another
direction.
This reminds us of the problem that decisions are often based on an egocentric
definition of ‘profit’ and ‘loss’. The definitions of ‘progress’ and ‘innovation’ may suffer
from the same problem.286 If so, it may be that at least some of the worries regarding the
precautionary principle are due to some people’s worries that technology will develop in a
direction that is less profitable from their own perspective and not from the general
anthropocentric perspective that we are investigating here.
282
Munthe 1997
Munthe 1997
284
Herremoës et al 2001 p.182
285
Herremoës et al 2001 p.182
286
I.e. ‘problem’ from a general anthropocentric basis as we use in this investigation. From an egocentric view
point, it would not be a problem.
283
86
3.4.5. Ignoring other risks
One argument that has been launched against the precautionary principle is that it
neglects the fact that by focusing too much on one risk we may increase another risk or even
the total sum of risks.287 It may e.g. urge us to spend so much money on avoiding one risk
that we do not have enough money left to deal with other – maybe even larger – risks.288 It
might also be that putting too much effort into avoiding a certain risk means that we will
have to abstain from doing other more valuable things. I.e. we risk losing opportunity
value.289 It might even be that by banning one particular substance or process we will end up
in a situation that is actually worse.290 If for precautionary reasons we stop using a certain
pesticide, it may increase the risk for crop failure and as a result cause famine.291 If we say
no to a certain genetically modified crop, it might lead to a continued use of pesticides and
fertilisers that we could have avoided by genetic modification,292 and if we abstain from
using a certain chemical because of its neurotoxicity the result may be that we instead use
another chemical that is carcinogenic.293
Sandin’s way of dealing with this problem is simply to be very clear that the
precautionary principle is precautionary in relation to a particular risk.294 By being clear
about this, we avoid a situation where people are mislead to think that we have attacked all
potential risks while we in fact have discussed one particular potential risk.
Sandin’s suggestion would make the shortcomings of the principle clearer and
therefore the principle more honest, but it does not – as Sandin admits295 – help us get rid of
the shortcomings. If the precautionary principle persistently tends to increase the total risk, it
does not help to point out that it is not meant to deal with the total risk. The principle will
still be worthless and should not be used. What we would rather need is a formulation of the
principle that acknowledges and handles the fact that some ways of dealing with some risks
may increase other risks. That does not seem like an impossible task. What we have to do is
to formulate the principle in such a way that it is applicable to the whole situation.
287
Grandjean et al 2004 p.383, Sandin 2004:1 pp.3f, Sandin 2004:3 pp.8f
Sandin 1999 p.894, Sandin et al 2002 p.293
289
Herremoës et al p.175, 194, Kuntz-Duriseti 2004 p.291, Munthe 1997, Sandin 1999 p.894, Turner &
Hartzell 2004 p.454
290
Kuntz-Duriseti 2004 p.291
291
Sandin et al 2002 p.293
292
Munthe 1997
293
Sandin et al 2002 p.293
294
Sandin 2004:1 pp.7f, Sandin 2004:3 p.9
295
Sandin 2004:3 p.9
288
87
I therefore prefer Sandin’s et al earlier analysis in which they point out that if we stress
one risk too strongly and therefore neglect another risk, we have a too narrow horizon. They
also point out that this is not just a problem for the precautionary principle. It is in fact
something that has to be dealt with by all decision principles.296 We have the same problem
if we base our decisions on the strategy “always try to maximise utility”: If we concentrate
too much on maximising utility in one situation, we may fail to maximise utility in total.297
This is not an argument against trying to maximize utility however. It is only an argument
against being too narrow in our considerations. The solution in this case is to include as
many factors as we can in the decision.
We can reason in the same way regarding the precautionary principle, with the
exception that finding a useful solution is a little more complicated. The precautionary
principle is intended to be used in situations where we have incomplete information about
the risks involved. This in turn makes it difficult to include more factors in the decision.
There are other factors that can be included however, and that would help to make a more
rational decision regarding the total risk. If we look at the interpretations in 3.3, the
precautionary principle tells us to consider things like the values at stake, the importance of
being in time, the degree of suspicion, etc. All these considerations can be applied to the
whole situation. We can compare the values at stake and we can compare the importance of
being in time for different values, etc. It makes the decision more complicated, but not more
unfeasible than a traditional utilitarian calculation.
Consider the example of genetic modification versus pesticides and fertilisers: If we
say no to a certain genetically modified crop, it might lead to a continued use of pesticides
and fertilisers that we could have avoided by genetic modification. If we apply the
precautionary principle to the situation as a whole, we would have to compare the risks we
run in the different situations. Say, that we know approximately what risks we run by
continuing the use of pesticides and fertilisers, but that we only have some unconfirmed
suspicions about the risks we would run as a result of genetic modification. If we do not
apply the precautionary principle the solution is simple: We do not know for certain that
there are any risks involved in genetic modification, so we have no reason to avoid it.
What, then, if we apply the precautionary principle? The principle does not tell us
always to avoid the uncertain risk and run for the known risk. At least that does not follow
from the conclusions in this work, and I have found nothing in the classical formulations
296
This is also pointed out by Östberg 1993 p.27
88
pointing in that direction. Neither should we just wait and see while continuing with
“business as usual”, or be satisfied with just making our decisions based on the present state
of knowledge regarding the probabilities. Instead, the principle exhorts us to make a decision
involving all relevant factors that were identified in section 3.3. We have to look at the
values involved, and at how the different values can be threatened by the use of pesticides
and fertilisers, and by genetic modification respectively. We would also have to factor in the
uncertainties regarding our suspicion against genetic modification. We would of course have
to look at the expected benefits of the different approaches – and at the uncertainties
regarding our expectations of the benefits. We would have to consider whether any of the
potential harms would be irreversible, and we would have to consider whether time is
particularly important somewhere in the process, etc. All these considerations would need a
lot of research and deliberation, and it would certainly not be possible to be correct all the
time. It still seems like a more rational alternative though compared to disregarding these
aspects and only look at how well identified the risks for the respective alternatives are.
In the previous sub-section as well as in the sub-section on irreversibility, we pointed
out that an important aspect of precaution is that we have to be prepared to re-evaluate our
decision in the light of better knowledge. This is also relevant in relation to the present
problem.298 If we chose an attitude of precaution, we should be able to re-evaluate and if
necessary reverse the decision if better knowledge shows that it has increased the total risk.
This is not always feasible, which only shows – again – that irreversibility is an important
aspect to consider when we make decisions that are potentially harmful. We should make
sure that it is possible to change a decision in the light of better knowledge by avoiding
irreversible effects – at least when we suspect that the irreversible effects can be
unacceptably harmful, and the more severe and the stronger the suspicion, the more careful
we should be in avoiding irreversible effects.
Let us finally take a look at the claim that the principle pays too much attention to
potential harm and forgets the potential benefits.299 The principle has doubtlessly been used
in that way in some cases, but it does not follow from my interpretation that it should be
used that way. If we accept the intuition that it is more important to avoid negative events, it
would be perfectly rational. Since we have chosen not to accept that intuition, there seem to
297
Sandin et al 2002 p.293
Wandall 2004 p.271
299
Herremoës et al p.175
298
89
be no reason why the principle should pay more attention to potential harm than to potential
benefits.
One alternative – or complementing – explanation as to why the precautionary
principle has been perceived as giving more weight to potential harm than to potential
benefits might be found in what is considered a ‘harm’ and what is considered a ‘benefit’.
We saw above (sub-section 3.3.3) that the value of the environment and human health has
often been downplayed in traditional decision methods. The precautionary principle is often
evoked in situations where the potential benefit from a decision is economic while the
potential harm concerns human health or the environment. It may therefore look like harm
gets more attention than benefit by the precautionary principle. Though what actually
happens is that the values that have been notoriously subjected to harm get upgraded and
better protected – not as a result of changing the way we weigh positive and negative effects,
but as a result of how we value human health and the environment.
Herremoës et al also point out that claims to the effect that a process has certain
benefits actually do need more attention. Not in the way of being assigned more weight, but
by being subject of more thorough investigation.300 They argue that there should be a burden
of proof placed on those who point out potential benefits and not just on those who point out
the potential harms.
Such a demand seems reasonable and does not presuppose a shift in how we weigh
positive and negative effects. On the contrary, if we put equal weight to positive and
negative effects, it is very reasonable that the burden of proof should not fall on one side.
Instead, claims of potential harm and claims of potential benefit should be subject of equally
hard scrutinising. Since the burden of proof up to now has been almost exclusively placed on
those who express worries regarding human health and the environment and since much of
the harm that has resulted from different projects has fallen upon human health and the
environment. A more equal distribution of the burden of proof necessarily means a larger
weight on those pointing out economic benefits. That does not mean that the distribution was
fair before and is now askew however. On the contrary, the precautionary principle used
correctly corrects the prevalent distortions.
300
Herremoës et al p.175
90
3.4.6. Does the precautionary principle lure us into a paradox?
It has been argued that the precautionary principle demands that we forbid everything,
301
and that it leads to a paradox by demanding that we ban every action as well as every non-
action.302
One of the basic features of the precautionary principle is that we take the burden of
proof from those who want a ban and place it on those who do not want a ban. Instead of
demanding proof that something is dangerous before forbidding it, we demand proof that it
is safe before allowing it. However, abstaining from an act – any act – will also be risky,
which means that we end up with a ban on both the performance the non-performance of all
acts. 303
Sandin considers this an argument against formulating the precautionary principle in
global terms, and in favour of formulating it in terms of precaution against some particular
potential harm.304 This will not help us though. Even if we concentrate on one particular
harm, the decision we are considering will still carry some very small probability of bringing
about this harm. Every act – and non-act – can by some weird chain of coincidences result in
just about anything. For instance, we may follow Sandin’s advice and use the precautionary
principle only for some particular risk, say the possible extinction of mankind. Me putting on
the right shoe first instead of the left may under some extreme circumstances by some weird
coincidence lead to the actualisation of this risk. We would therefore have to prohibit me
from putting on the right shoe first. In fact, we would also have to prohibit me from putting
on the left shoe first – and from not putting on any shoe at all. Since all these alternatives
have some minute probability of causing the extinction of mankind. We would thus be left in
the dilemma we started with.
Maybe we can adapt Sandin’s proposal to limiting the scope of the precautionary
principle, not to one particular outcome, but to one particular decision. The decision can be
in the form of performing a particular act or of not performing that act, but it cannot be
applicable to both alternatives. We might then say that “prohibiting me from putting on the
right shoe first or not putting on the shoes at all can have negative effects, but this does not
301
Munthe 1997, Sandin et al 2002 pp.290f, Sandin 2004:1 pp.3f
Munthe 1997, Sandin 2004:1 pp.1,3f
303
Sandin et al 2002 p.291, Sandin 2004:3 p.10. Turner & Hartzell 2004 pp.450f has compared this paradox to
Pascal’s wager.
304
Sandin 2004:3 p.10
302
91
have to concern us since we are only discussing precaution in relation to putting on the left
shoe first”. This would, however, make the principle rather uninteresting.
Sandin et al do point towards an important fact: None of the authoritative formulations
of the precautionary principle in fact require absolute proof of safety.305 This is important,
since the opponents of the principle have to assume that it does. In order to end up in the
situations described above, we must have an extreme epistemic threshold, at least when it
comes to convincing us that something is safe. To assume that the degree of certainty we
demand will lead to a ban of everything and ultimately end up in a paradox, therefore looks
like a “straw man-argument”. The classical formulations of the principle do not assume such
a high epistemic threshold, and neither do my interpretation from section 3.3. We must also
remember that the precautionary principle is intended to come into play in situations where
we have some indication that the act in question is a threat to some important value. Just as
there must be a correlation between the importance of a value and the proof we demand that
a process is not a threat to this value, we also need some correlation between these things
and the strength of the indication that the process in question might be harmful.306
Sandin et al suggest that we apply a de minimis principle, i.e. a limit on how small
probabilities that should count.307 The question is what would be a reasonable limit. My
suggestion is that we use a flexible system in which the level is decided by the value at stake,
the severity of the potential harm, and the degree of suspicion against the process we discuss.
3.4.7. How do we prove a negative?
Shifting the burden of proof is one of the main features of the precautionary principle.
There is one seemingly important problem however. The problem is that we have an
asymmetry in the very nature of “showing something to be the case”. It only takes one
incident to show that a certain process can harm a particular value, while we can never be
absolutely sure that a process is safe in relation to that particular value.
305
Sandin et al 2002 p.291
Herremoës et al (ed.) 2001 p.170, Sandin et al 2002 pp.290,291, and Turner & Hartzell 2004 p.456 bring up
the question of correlation between degree of suspicion and demand of proof.
307
Sandin et al 2002 pp.291f
306
92
The question is therefore: How do you prove that something is safe? In other words,
how many negative results does it take to prove that there are no negative effects?308
My answer is once again that this is a problem only if we have an extremely high
epistemic threshold, e.g. if we demand absolute certainty. We have seen that none of the
classic formulations of the principle urge us to adopt such an extreme threshold, and the
same goes for my interpretation of the principle. In my interpretation it is a matter of a
gradual change of the burden of proof in relation to the values, threats etc. that are at stake.
The more valuable, the larger our suspicion, and the larger the suspected threat, the higher
ought the threshold to be. Absolute certainty is not possible and cannot be demanded.
3.5. What can the precautionary principle do for us?
Is the precautionary principle applicable to the subject of extinction? It has been
applied to this question by some official statements. The UN FAO Code of Conduct for
Responsible Fisheries urges a precautionary approach in relation to fish stocks.309 In order to
motivate the precautionary principle, the Wingspread document explicitly mentions
extinction as one of the areas where traditional decision methods have failed.310 The Rio
declaration does not explicitly talk about extinction, but claims that the precautionary
principle should be used in situations of a) serious damage, b) irreversible damage, and c)
lack of full scientific certainty. These are all salient aspects of species extinction: The
extinction of species is typically irreversible. There are many uncertainties concerning the
species issue. There are suspicions that extinction will harm some very important values.
There are non-linear effects that both increase the uncertainties and make the question of
timing extra important. If the species loss results in a loss of an ecosystem service, that too is
typically irreversible and the nonlinear reaction of ecosystems to encroachments makes the
uncertainties great.311 In the worst case, loss of important ecosystem services can lead to
what I called “game over-situations”. All of the things mentioned here turned out in section
3.3 to be precisely the kind of things that the precautionary principle is meant to deal with.
308
Gee 2006
McGarvin 2001 p.23
310
Wingspread Conference 1998
311
Daily 2000 p.336
309
93
Bryan G. Norton compares the rivet popping analogy by Ehrlich and Ehrlich (see
section 2.7 above), to a phenomenon called “zero-infinity dilemmas”.312 A zero-infinity
dilemma is a situation in which the probability for something to go wrong is very small,
while the effects if it does is catastrophic.313 If too many species disappear from an
ecosystem, the ecosystem may break down. The same would be the case with the entire
biosphere. For each single species, the probability that its extinction would cause the
breakdown is “quite low”, but if it does, the consequences would be very serious indeed.314
This too looks like a good reason for applying the precautionary principle to the
question of extinction. The question is what probability is low enough and what gain is high
enough to take the risk. The important thing to note is that the principle tells us not to be
satisfied with an ordinary risk analysis. It urges us to take into account the uncertainty
concerning the probability (there is no way we can know in advance whether the species in
question will be the one that causes the break down). It also urges us to consider both the
value of the ecosystem at risk, the harm that may be caused to this value, the uncertainties
concerning these aspects, and the aspect of irreversibility. It finally tells us that as a result of
these considerations we must adjust and quite possibly increase the burden of proof for those
who want to take the risk.
Norton is not alone in concentrating on the possible breakdown of ecosystems and the
loss of ecosystem services. The UN Millennium Ecosystem Assessment group belongs to
this category. They reason in three steps:
1. They first argue that working ecosystems provide us with many important
ecosystem services.
2. Then they stress the importance of biodiversity for properly working ecosystems.
3. Finally, they suggest that since so much is at stake, and since we have good
reasons to believe that biodiversity is important for the ecosystems to work, but do
not know exactly how, we ought to apply the precautionary principle.
In our case, since the ecosystem services are very valuable and since there is a strong
suspicion that loss of biodiversity may eventually be detrimental to this value, we should
demand very strong evidence that the species under consideration will not be the one that
breaks the neck of an ecosystem service. However, since we cannot ever know that in
312
Norton 1986:1 p.121, Norton 1987 pp.67ff
This is the standard definition. Norton adds a list of other criteria that are characteristic of the extinction in
particular. I believe however that the simpler standard definition is sufficient for the point I am going to make.
314
Norton 1986:1 p.121, Norton 1987 pp.67ff
313
94
advance, we ought instead to demand good evidence that a certain practice will not cause
extinction.
Protection of ecosystems and ecosystem services is not the only reason to apply the
precautionary principle to the species issue however. Other species also supply us with a
host of different instrumental values. In some cases the exploitation of these values risk
causing extinction of the species. As we have seen, exploiting a species to the degree that it
goes extinct may in fact be economically rational from an anthropocentric viewpoint. This is
however something we do not always know for sure. In 3.3.2 I noted that when an act might
result in an irreversible change, we need extra strong evidence against any suspicion that the
change will result in serious problems – e.g. by destroying or depleting a resource that would
afterwards turn out to be more valuable in its original state. This is clearly applicable to the
situation we discuss here. Extinction is as we have seen irreversible, and we cannot know
now what the value of the species will be for future generations of human beings. What we
can know on the other hand is that historically species have time and again turned out to be
valuable in ways we had not expected.315 It therefore seems quite clear that the precautionary
principle tells us not to drive species to extinction, and that if we still contemplate on doing
it, a heavy burden of proof should be placed on the shoulders of those in favour of the
exploitation.
315
Gärdenfors 2005 p.119
95
4. Future Generations
Ghillean Prance believes that we would manage the rainforests very differently
(presumably better) if we thought more about our “great-great-great-great-greatgrandchildren”.316 That might be true, but do we have a moral duty to change our
management of the rainforests out of concern for our great-great-great-great-greatgrandchildren? Do we – to put the question in terms more suitable for our investigation –
have a moral duty to preserve species for the benefit of future generations of human beings?
Political and legislative documents sometimes express such a duty. Both the Brundtland
report and the Rio declaration for instance explicitly tell us that we do have such a duty.317 In
his survey of official governmental and inter governmental policy texts, Mikael Stenmark
has identified a general idea of what he calls ‘intergenerational justice’, meaning that we
have a moral obligation to consider the needs of future generations of human beings.318
It is not totally clear what this means. The official policy documents seldom state very
precisely how they conceive of our duties to future generations.319 I think it is quite clear
though that most people do recognise some kind of moral duties towards future generations.
It also seems quite clear that for many people this is a strong argument for nature
conservation. It is not uncommon to hear people argue that we need to preserve nature,
ecosystems or species for the sake of future generations.
According to Stenmark, the idea that we have duties not just to our children and
grandchildren, but also further into the future, is a genuinely new idea in international policy.
He believes that the change is induced by necessity trough the new insights of our
dependence on nature, of the possibility that some natural resources will eventually run out,
and of the fact that there are limits to what nature can absorb in terms of human
interference.320 He also puts his finger on the question of how far into the future our concerns
should reach, and the question of whether our concern for future generations should decrease
with time.321
Our concern is whether a duty towards future human generations can explain at least a
part of why extinction is conceived of as a moral problem. In order to answer that question
316
Prance 1990 p.64
Melin 2001 passim, Stenmark 2000 pp.29f,34,49ff
318
Stenmark 2000 p.37
319
Melin 2001 p.104, Stenmark 2000 pp.8,52f,56f,62ff
320
Stenmark 2000 pp.8,49ff
321
Stenmark 2000 pp.67f
317
96
we have to investigate whether we have such a duty at all, and also its possible scope and
demands.
4.1. Do we have any duties to future generations?
The first thing we have to investigate is whether we at all have any moral duties to
consider the interests of future generations. This question has been the subject of an
intensive debate and I will here discuss what I believe are the most serious objections.
4.1.1. The asymmetry problem
One salient feature in most of our relations with future generations is that they work
only one way: Much of what we do will affect them, but almost nothing they do can affect
us.322
Parfit illustrates our relations to future generations with ‘the auditorium dilemma’.323 In
some auditoriums, the first row can gain a better view by standing. Standing up is less
comfortable than sitting down, but in some situations it might be worth the discomfort to get
a better view. This presents a problem for the second row. They originally had a view that
was good enough and they had no reason to endure the discomfort of standing. It was
therefore in their interest to remain seated. If the first row stands up, however, the second
row will not see anything. Therefore, they also have to stand up in order to regain their view.
This will make their situation worse compared to how it was from the beginning. By
standing up, they will have the same view as before but they will be less comfortable. The
same goes for the row behind it and so on for the rest of the rows. When all rows are
standing up, all but the first row will have the same view as before but be less comfortable.
The first row will be less comfortable but have a better view. The result is that the first row
will be better off while all other rows will be worse off.
We can see this as an analogy to intergenerational relations, where the first row is the
present generation and the second row the generation after that etc. What the first row does
322
Barry 1996 p.209, Narveson 1996 pp.39f
97
will have effects on the next generation and so on but what a later generation does will not
affect the generation before it.
The ‘auditorium dilemma’ differs from e.g. the ‘prisoner’s dilemma’ in having one
group that is untouchable by the others (being the “outsiders” as Parfit calls it).324 This means
that there is no way we can make a deal that will be acceptable to everyone based on strict
rational egoism.
Another salient feature is that the luxury of being untouchable is transferred from row
to row together with the bad effects of the acts done by the first row. This means that there is
always a very strong temptation for every row to deal with the problem created with the row
in front of them in a way that makes the situation worse for the row behind them. Even
though it is worse to stand and have a good view than to sit and have a good view, it is even
worse to sit and have a bad view. Analogously, it is always a tempting alternative for every
new generation to soften the impact from the things done by the previous generation by
passing on as much as they can of the bad effects to the next generation.
The auditorium dilemma is a good analogy to the case of future generations and
natural resources, ecosystem services, etc. We can improve our lives by over consuming
resources in a way that will affect future generations. The only thing they can do to deal with
the situation is to continue consuming resources as long as there are any left, and thereby
pass the problem on to future generations. In fact, the intergenerational problem is worse
than the auditorium dilemma, since by consuming resources in a pace that exceeds the
regeneration rate or by consuming non-renewable resources, the problem will not just be
passed on, but also be worsened. If we add a growing human population it will become even
worse.
The asymmetry problem does not present an obstacle for including future generations
in the realm of moral objects as long as our criteria for being a moral object do not
presuppose a reciprocal relation between the object and the agent. For theories that do that –
like contractualism and communitarianism – it is problematic however.
Both Derek Parfit,325 and Brian Barry,326 concludes that the asymmetry problem in fact
shows that, contractualism does not admit of duties to future generations, since they are not
able to enter into mutual contracts with us. (Parfit bases his conclusion on Barry).327
323
Parfit 1987 p.383 note 19b
Parfit 1987 p.383 note 19b
325
Parfit 1987 p.357
326
Barry 1996 passim
327
Parfit 1987 p.357 note 7.
324
98
Christian Munthe and Anders Melin are of the same mind when it comes to contractualism
in general.328 Both claim however that John Rawls' version in fact allows for moral duties to
future persons. The reason for that is that it is possible to deny the people behind the veil of
ignorance329 the knowledge of what generation they will belong to. They will therefore prefer
an equitable distribution of resources between generations as well as within generations.330
This seems plausible given the idea of a veil of ignorance. There is one problem that is
not mentioned however but which I believe is of crucial importance if we are to establish a
just distribution of resources. The people in the original position do not know what
generation they will belong to, but do they know how many generations the resources are
supposed to be distributed among and how large each generation will be? Rawls does not
mention anything about this and to assume such knowledge would be utterly unrealistic. If
the people in the original position do not know these things however, how can they decide
what will be a just distribution? Luper-Foy believe that the people behind the veil will adopt
a policy regarding e.g. consumption and pollution that can be indefinitely sustainable.331
Such a policy would take care of this problem even though it would be sub-optimal for the
rational egoists that the people in the original position are according to Rawls’ model. It is
not optimal since it puts harder restrictions on people than would be necessary if they know
how many generations there would be, but given that they do not know and given that no
one would like to be born in generation X+1 after having agreed to base the calculations on
X generations, this principle still seems rational given the original position.332
Luper-Foy’s suggestion would not take care of the problem regarding the number of
people per generation however. We could of course quite simply transform the idea of
infinite sustainability into a policy that assumes an infinite number of people. The problem is
that such a policy would not allow for any consumption at al. I believe however that the
problem could be solved by approaching the question of population size from a prescriptive
rather than a predictive angle. I.e. by adopting a policy for how large a generation is allowed
to be.
328
Melin 2001 p.124, Munthe 1997
The “veil of ignorance”-model is described in Rawls 1973 pp.136ff.
330
Rawls 1973 pp.137, 287f. Commented by e.g. Luper-Foy 1995 pp.95f,100, Melin 2001 p.124, Munthe 1997
331
Luper-Foy 1995 pp.95f,100
332
It still assumes a rather high aversion towards risk, just like many other decisions Rawls assumes that the
people in the original position would take. In Rawls description of the veil of ignorance he specifies that the
people behind do not know their aversion to risk (Rawls 1973 p.137), but they obviously have one and it has to
be quite strong – much stronger in fact than would be granted by the precautionary principle.
329
99
A simple solution to both problems would be to assume that everyone that will ever
live takes part in the decision behind the veil. This is forbidden by Rawls in his restrictions
for the veil of ignorance however. He presents different reasons, but the strongest reason
seems to be that it is important for his theory that any randomly selected person should be
able to go behind the veil and reach the same conclusion.333
A possible solution to the problem concerning the number of generations would be to
let all generations be represented behind the veil. This alternative is also ruled out by Rawls
– apparently for the same reasons.334 Instead he assumes that everyone behind the veil belong
to the same generation. This assumption does not just exclude a simple solution to the
problem presented above. In fact, it also threatens to bring down the whole motivation for
considering the interests of future generations at al. It is true that they still do not know when
in history they will live so they would initially be in favour of a fair distribution but only up
to the point when they enter the picture whenever that will be. They cannot affect the policy
of previous generations (who do not take part in the decision process), and since they do not
have to care about future generations (they all know that they will belong to the same
generation). The veil of ignorance can therefore not given the original set-up produce any
agreement to consider future generations.335
Rawls himself is aware of this, and he infers a special amendment to deal with the
problem. Two of the most basic rules of the original position are that none are allowed to
have any moral inclinations and that none are allowed to know their preferences. Rawls
makes an exception to the second of these basic rules however by allowing the people
behind the veil to care for their future relatives.336
This is a very strong concession by Rawls and it means in effect that care for future
generations does not follow from his theory but is added to the theory from the outside in
order to save the theory. In his later writings, he therefore chose another solution. Instead of
allowing the people behind the veil of ignorance to have emotions towards their offspring, he
infers a rule that their agreements must be such that they would want everyone to follow it
independently of what generation they belong to.337 This means that instead of making an
exception to the restriction against knowing their interests, Rawls chose to make an
exception to the restriction against having any moral inclinations. I do not know if this is a
333
Rawls 1973 p.139
Rawls 1973 pp.140,291f
335
Rawls 1973 pp.140,291f, Rawls 1993 pp.273f
336
Melin 2001 p.125, Rawls 1973 pp.140,292
337
Melin 2001 p.125, Rawls 1993 p.274
334
100
smaller concession for Rawls. The new solution means that he introduces a certain moral
intuition explicitly in order for his theory to include a duty to care for future generations
instead of letting such a duty emerge from behind the veil of ignorance. He uses the moral
relevance of future generations as a basic moral principle needed to make his theory
justifiable, which in turn means that we cannot use his model to justify concern for future
generations.
There is also a general problem with the idea of the veil of ignorance that affects the
question of future generations. It does not give us any hint on how to implement the idea in a
world where we do not make decisions behind a veil of ignorance. I.e. even though
intergenerational equity would be a rational conclusion from an egocentric perspective given
the veil of ignorance, this does not tell us anything of what is rational from an egocentric
perspective in the real world. The only way of making use of the idea of a veil of ignorance
in a world that is as a matter of fact not constructed like that would be to adopt the veil of
ignorance as a basic moral principle overruling any selfish inclinations. That would in
practice be equivalent with adopting a moral principle that tells us to be totally impartial. If
we do that however we have left both reciprocity and rational selfishness.
Is there any way a true reciprocal theory can deal with the asymmetry problem?
Barry Gower thinks that it is possible to have a reciprocal arrangement between overlapping generations, but not between non-overlapping ones. He therefore concludes that
there cannot, according to formal theories of justice, be such a thing as justice or injustice in
our relations with generations further into the future.338
Jan Narveson has a different opinion. According to him, the overlapping can be used to
solve the problem also in the general case. There is always overlapping between generations
(since one generation is born by the previous one), and just as one generation takes care of
the next one during the latter’s childhood, the latter takes care of the former during their old
age. Therefore, he claims, it is not really true that the intergenerational relations only work
one way.339
This would not be a general solution however, since it cannot deal with situations
where the time lap between the act and the effect is so long that there will be no overlapping
between the generation that causes the problem and the generation that experience it.
Situations like that are probably not that uncommon when dealing with environmental
changes.
338
Gower 1995 pp.51f
101
There are also other problems that seems to show that Narveson’s solution might not
even work in the particular case where generations overlap. The relation between
generations that Narveson points out does in fact not make the relation totally symmetrical.
The parent’s care of the child takes place before the child’s care of the parent. There is thus
still a time asymmetry. Time asymmetries always present a problem for theories based on
reciprocity since it puts a heavy pressure on the trust of the first agent in the second
(potential) agent, and also puts a heavy burden on the sense of duty of the latter to fulfil her
part of the deal even though she has already got what she wanted. Basing the argument on
this sense of duty would however make contractualism superfluous.
There is also another problem. If children are not well taken care of the effect is shown
immediately or within the lifetime of the parent. This is not always the case when we deal
with environmental problems. When it is the case, it tends to make the intergenerational
aspect less interesting. If the consequences are immediate, they will also affect us and other
contemporary people, and we do not need to involve duties to future generations in order to
establish that there is a moral problem.
There might be a certain degree of interesting overlapping though, since it is possible
that the bad consequences begin to show in the later years of the inflicting generation
without outweighing the earlier benefits they have already got, while the younger generation
will have to live with the negative consequences for a long time. In these cases,
contractualism would give us a reason to constrain ourselves in our dealings with nature,
since the members of the future generation still have time to retaliate if we break the
hypothetical contract.
Often the negative effects do not turn up until after the inflictors are dead however, and
if they turn up earlier, they generally do not yet overshadow the positive effects. This is
probably the most common setup in cases of human inflicted extinction. It normally takes a
while for a species to disappear completely after a fatal blow, and the disappearance of one
species will not always have any perceptible effect (consider the threshold effects discussed
earlier).340 In these situations, we lack the overlapping that Narveson’s argument hinges on.
Brenda Almond suggests – inspired by Dworkins and Rawls – that justice demands us
to repay future generations for what we got from past generations.341
339
Narveson 1996 p.56
See also Ihse 2005 p.70
341
Almond 1995 p.18
340
102
I am not convinced that this can help us solve the problem. We live in a world with an
increasing greenhouse effect as a result of what our parents and grandparents did. Would that
make it all right for us increase the greenhouse effect further – or are we even obliged to do
it and punish future generations for the acts of previous generations in order for justice to
have its course? Previous generations have driven a large number of species to extinction.
This could if we follow Almond’s idea be a reason for us to do the same.
One could say that we should do to future generations what we wish that previous
generations had done for us but this cannot be defended from the point of view of rational
selfishness. We are back where we started: We need an account of moral standing for future
generations that does not depend on what we can actually get from them in terms of benefits
or retaliation.
There is also another problem with Almond’s asymmetrical idea of justice: How can
justice demand that we pay back not to the one we received the benefit from, but to someone
else?
The question of future generations is apparently a devastating problem from a
contractarian point of view. Other contractarians have offered different solutions but none of
them have been able to deal with the asymmetry problem.342
I believe we have to conclude that contractualism does not supply us with any rational
reason to preserve species for the benefit of future generations.
Anver de-Shalit tries to solve the asymmetry problem from a communitarian vantage
point, which he thinks gives the best account of our duties to future generations.343 He claims
that even though we live at different times we are part of the same community. For example,
parts of us survive in the form of our achievements and in the form of other people’s
memories of us.344 This is a kind of cultural interaction between the generations: We interact
with them by creating and inventing ideas and things that will live on during their lifetimes.
They interact with us by upholding the memory of us and by using and refining the things
and ideas we have passed on to them.345 This also goes for ethical norms. We pass on ethical
norms to them. They share, apply, and reflect on the norms.346 This means that we are part of
the same community.
342
See e.g. David Gauthier (Gauthier 1986 passim). His suggestion is a very clear example of this shortcoming,
as is shown in de-Shalit 1990 p.226 and Melin 2001 pp.122ff.
343
de-Shalit 1995 p.13ff
344
de-Shalit 1995 p.38f
345
de-Shalit 1995 p.43
346
de-Shalit 1995 p.45ff. See also Melin 2001 pp.125f
103
Eventually this will fade off however. Their reflecting on the common values together
with external influences means that after a number of generations we will no longer be
members of the same moral community.347 From this de-Shalit concludes that we do have
duties to consider the interests of future generations, but that these duties gradually fade
away as we gradually become members of different communities.348
This will give us three degrees of duties:
To contemporary people we have far-reaching positive duties.
To those who will live in the near future we have almost as strong positive duties.
To those living further off into the future we have much weaker and only negative
duties. Moreover, if it is not a matter of very strong remote future interests competing with
very weak present-day interests, the remote future interests will not outweigh the interests of
contemporary people.349
I find de-Shalit’s solution problematic. We are not part of the same community on the
same premises. We can pass on norms to them, but they cannot pass on norms to us. No
matter how much and how well they reflect on our norms they can still not impose them on
us. The asymmetry problem therefore does not disappear.
In addition, it is not obvious to me that sharing the same ethical norms could tell us
anything about what the norms should imply. It does not seem to exclude for instance that
we share the norm that there are no duties to future generations. It is odd to claim that moral
standing is decided not by the content of our ethics, but with whom we share it. Furthermore,
de-Shalit’s communitarianism is hit by the argument from marginal cases. Some
contemporary human beings are not able to reflect on moral values or fulfil any of the other
criteria de-Shalit has placed for being part of the same community. They will therefore fall
outside the community and have no standing.
De-Shalit also argues that we want future generations to conclude that our values are
good.350 Why? It is probably not because we fear their reactions. The explanation cannot be
that we care for them, since that would beg the question. If we do not care about future
generations to begin with, we are not likely to care about what they think about our values.
He refers to the existence of guilt feelings and to our interests in the welfare of future
generations as arguments for his idea of a trans-generational community.351 However, these
347
de-Shalit 1995 p.47
de-Shalit 1995 p.53f
349
de-Shalit 1995 p.54f. See also Melin 2001 pp.125f
350
de-Shalit 1995 p.48
351
de-Shalit 1995 p.18f
348
104
feelings do not show that we regard future generations as moral objects. It may be that we
have these feeling towards them because they are valuable to us. We can have an interest in
just about anyone and anything from stalagmites to extraterrestrials. If we weaken the
criteria for what it takes to be a part of a common community that much, the term would lose
all meaning.
It is also a problematic fact that all duties in the trans-generational community are
aimed in one direction. De-Shalit uses our upholding of traditions as an argument for the fact
that we identify ourselves as being part of a trans-generational community together with past
generations of practitioners of the same traditions.352 If anything, however, this illustrates
how interactions between generations move only in one direction. By upholding the
traditions of our forefathers, we clearly see that we are influenced by those before us in a
way that they can never be influenced by us. De-Shalit talks about a cultural interaction in
the form of discussions aiming at finding “a common set of ideas which determine a
common good”.353 It is difficult to see how such a discussion can take place between
individuals living in different generations however. Melin also points out that since de-Shalit
demand shared values in order to be part of the same community, it must be difficult to
perform the kind of critical debate he talks about as something that binds us together.354
I have found nothing in de-Shalit’s arguments that helps us in our dealings with the
asymmetry problem. The general result in this sub-section is that neither communitarianism,
nor contractualism can demand from us that we care for future generations. The failure of
contractualism also underlines our previous conclusion that rational egoism does not seem to
give us much reason for avoiding extinction.
Since the asymmetry problem only is a problem for theories that demand some kind of
symmetric relation between the moral agent and the moral object however, it is not a
devastating drawback to the idea of moral duties to future generations.
352
de-Shalit 1995 p.20
de-Shalit 1995 p.25
354
Melin 2001 pp.127f
353
105
4.1.2. The non-identity problem
One problem that has been widely discussed in relation to future generations, is the socalled non-identity problem pointed out by Thomas Schwartz and Derek Parfit among others.
Thomas Schwartz argues that because of this problem, we can not have moral
obligations to posterity other than to our “near posterity”.355 He uses the question of
population size to illustrate the problem, but claims that his point can be generalised to cover
all kinds of duties to future generations. His reasoning goes as follows: Assume that we do
not limit the size of the population and as an effect of that, the lives of future generations of
human beings will be less enjoyable. If we take any future person X, it would be very
probable that X would not have existed had we adopted a more restrictive population policy
not only because there would be fewer people, but also because the events leading up to the
birth of X would be significantly different. This in turn means that X would probably not be
identical to anyone of those who would be born if we were to live according to the stricter
policy.356 The people that would have benefited from the stricter policy will not be the same
as those who actually get to live. Therefore, we have not failed to do our duty to those people
by not adapting the stricter policy.357
He believes that in the first generations after our own, there will still be people who
would be identical independently of our choice. We should therefore assume some duties to
our immediate posterity. However, these duties will fade very fast since the differences
between the populations will increase exponentially.358
This reasoning is then generalised, and Schwartz claims to have shown that it covers
all alleged duties to future generations – not just duties concerning population size.359
Schwartz is not satisfied with having shown that we do not have any duties to make
sacrifices on behalf of future generations other than possibly the immediately following
generations. He also claims that to put restrictions on now living human beings in order to
benefit future humans cannot even be morally permissible, since it would mean that we put
restrictions on now living individuals, although there is no one to whom we owe these
restrictions.360
355
Schwartz 1996 (first published 1978) p.3
Schwartz 1996 pp.4ff
357
Schwartz 1996 pp.7ff
358
Schwartz 1996 p.6
359
Schwartz 1996 pp.10f
360
Schwartz 1996 pp.11f
356
106
It could be argued against Schwartz that even though no individual member will be the
same under the different policies, the society will be the same. One could therefore object
that even if no particular member of the society is better off than she would be had we
adopted a more restrictive policy, the society would be better off.
This idea differs from the communitarianism discussed in the previous section, since
here we are not talking about duties to particular individuals based on their belonging to the
same community but about duties to the communities as such.
One thing that speaks in favour of this approach is that when we talk about future
generations, we spontaneously tend to talk about them not as individuals but as a group.
Stenmark explains this habit by pointing out that future humans do not yet have an identity,
which makes it easier to conceive of them as a group than as individuals.361
Schwartz does not believe it can solve the non-identity problem however. His
argument is that it does not matter morally if the society is better off when no individual is.362
This objection seems reasonable although not everyone would agree. We do not have to go
into that question here however. In this book, we investigate whether anthropocentrism, can
answer the question of why it is morally problematic to cause extinction. Anthropocentrism
does not admit moral standing for anyone or anything but human beings. That excludes the
possibility of accepting moral duties to societies. This means that we cannot find any help in
the idea of moral duties to societies in order to support anthropocentrism even if it would
turn out to be valid.
Schwartz concludes that we do not have any moral duties to future humans. Instead, he
suggests that we presently living humans have a moral duty to each other to adopt policies
that contribute to a better life for future generations. Most now living human beings wish
that future generations should prosper far into the future. In order to secure this wish, we
need to make sacrifices. In order to secure a fair distribution of these sacrifices, we all have a
moral obligation – not to future generations but to each other – to contribute.363
We would in other words have no duties towards future generations of human beings,
but only duties regarding them, just as we according to anthropocentrism have no duties
towards other species but might have duties regarding them. The difference is that our
valuing of a good life for future generations of human beings is probably intrinsic rather than
361
Stenmark 2000 pp.60f,64,67
Schwartz 1996 p.6f
363
Schwartz 1996 pp.12f
362
107
instrumental (although Schwartz does not discuss this question). It is not very probable that
people, who are unable to affect us, would have instrumental value for us.364
For our investigation, this means that we have a duty to other now living human beings
to share the burden of considering the wellbeing of future human beings to which we have
no moral duties, but who have intrinsic value for us. This might among other things imply a
duty to preserve species that have instrumental value for future generations of human beings.
Derek Parfit’s conclusion is radically different. The basic story is the same: If someone
had not been conceived at the time she was actually conceived, she would not exist at all. If
the conception had taken place earlier or later, it would have involved two other gametes,
and therefore the resulting foetus would have a perhaps slightly but still different genetic
makeup.365 Parfit sets the time limit at a month (obviously to be on the safe side, but he also
hints that the real time interval after or before which we would not have existed had we not
been conceived within it, may actually be much shorter).366
If we try to benefit a future individual by doing what will change the time of his
conception, we have not benefited him at all – we have benefited someone else who is born
instead. This in turn means that if we neglect to take this step, no one is made worse off,
since he would not have been born at all if we had acted in the less depleting way.367
We can complicate the situation further by adding that if we choose different lifestyles,
it will also effect who we meet and have children with. This means that different lifestyles
will lead to different identities of future individuals. If we then choose to consider the
interests of future generations by living a less destructive life, the future people who will
benefit from this will not be the same as if we instead had chosen a more wasteful lifestyle.
If we choose the wasteful lifestyle, this will not be worse for future humans as long as their
lives will be worth living.368 If we assume that it is possible to benefit someone by bringing
her into existence, we could even claim that we have benefited her by living a wasteful
life.369
364
Anthropocentric instrumentalism the way I have defined it in this investigation does not exclude the
possibility that future generations of human beings may have intrinsic value for us. It only excludes that other
species can have intrinsic value for us. Schwartz’s solution therefore seems to be allowed by anthropocentric
instrumentalism. It does not take us all the way however since future generations still do not have any moral
standing of their own.
365
Parfit 1987 pp.351ff
366
Parfit 1987 p.352
367
Parfit 1987 p.358ff
368
Parfit 1987 p.361ff
369
Parfit 1987 p.363
108
Should we therefore follow Schwartz and conclude that we have no moral duty – other
than a duty to other contemporary humans, and possibly to the immediately following
generations – to make any sacrifices for the sake of coming generations? Not according to
Parfit. He regards the intuition that we have a moral duty to consider future generations as
too basic. He illustrates this by the following imagined situation:
There are two different conditions – K and J – that give the same handicap to the child
of a woman who is the bearer of either K or J. The difference between them is that J is
curable, while K is not curable but disappears by itself within two months. A programme (let
us call it J) is set up to cure women with condition J. Another programme (let us call it K) is
set up to test women for condition K, and if they have it, advice them to wait for two months
before getting pregnant. Both programmes will if performed have the result that 1000 more
healthy children and 1000 fewer severely handicapped children will be born. Unfortunately,
there is not enough funding to go through with both programmes, so one of them has to be
cancelled. If we chose to carry out programme J, the same children will be born, only they
will not suffer from the handicap. If we chose to carry out programme K, different children
will be born and thereby benefit from the programme. We could therefore say that we have a
duty to these individuals to perform programme J but we have no duty to anyone to perform
programme K.
The question is: What does our intuitions tell us? Is there any moral reason to prefer
one programme rather than the other? 370 Parfit’s intuition is that there is not. If we disregard
the obvious fact that there are more risks involved for the prospective mother in having an
operation, compared to just waiting two months before becoming pregnant, I share this
intuition. I suppose most people would agree, in spite of the fact that alternative K is
vulnerable to the non-identity-problem, while alternative J is not. The fact that our intuitions
do not distinguish between the two programmes indicates just as Parfit points out, that what
matters intuitively in this example is that independently of which programme we chose,
1000 more healthy children and 1000 fewer handicapped children will be born. The identity
of the children does not seem to be relevant. 371
Parfit’s conclusion is that we must reject the idea that “what is bad must be bad for
someone”.372
370
Parfit 1987 p.367f
Parfit 1987 p.368f
372
Parfit 1987 p. 363
371
109
I am not sure that making this sacrifice is an improvement however – or even that it is
necessary. What Parfit needs is to reject the idea that identity is morally relevant, not the idea
that what is bad must be bad for someone.
That what is bad must be bad for someone is also a very basic moral intuition, and
maybe even more so than the intuition that we should show concern for future generations. If
we reject the idea that what is bad must be bad for someone, the answer to the question
“what is bad?” would be up for grabs – and I cannot figure out a plausible answer to this
question that does not assume that what is bad is bad for someone.
It seems that Parfit has missed an important distinction. We can – and should –
distinguish between the questions of what is bad and what is wrong. The question of what is
bad and the principles for answering this question are indeed very important for the question
of what is wrong, but they are not the same thing. The question of what is bad concerns
necessarily what is bad for someone in order to be meaningful, and analogously, in order to
be meaningful, the question of what is good has to be about what is good for someone. There
must be a subjective perspective from which something is good or bad in order for it to be
so. The question of right and wrong in turn has to relate to good and bad – and thereby to
what is good and bad for someone. Of course, we can say that a certain act should not be
performed because it is taboo even though it does not relate to the question of what is good
or bad for any moral object. This is not what is normally meant when we condemn
something for moral reasons however, and it is not the way I am using the terms ‘moral’ and
‘ethical’ here.
Gustaf Arrhenius investigates the possibility of solving some other dilemmas involving
different populations by discussing them on the normative (right/wrong) level instead of on
the axiological (good/bad) level.373 He is not satisfied with the result however and therefore
abandons the idea. He does not discuss the implications for the non-identity problem though
but I believe that much could be gained by doing so. I also believe that by doing so we
would avoid some confusion. When Arrhenius discusses what he calls “The Person Affecting
Restriction” (sometimes also called “the slogan”) – i.e. the intuition that for something to be
good it must be good for someone – he states it as follows:
(a) If outcome A is better (worse, equally as good) than (as) B, then A is better
(worse, equally as good) than (as) B for at least one individual.
373
Arrhenius 2000 pp.196ff
110
(b) If outcome A is better (worse) than B for someone but worse (better) for no
one, and B is better (worse) than A for no one, then A is better (worse) than B.374
Formulated in this way, the person affecting restriction seems unproblematic but at the
same time uninteresting from an ethical perspective since it is totally axiological and
contains no normative statement. I.e. if we assume that the terms ‘better’, ‘worse’ etc. keep
their meaning through the entire statement. It would be possible to interpret the formulation
in prescriptive terms but then we have to use the terms ‘better’, ‘worse’ etc. in two different
ways: Normatively in the first part of (a) and the last part of (b) and axiological in the other
parts. To shift the meaning of a term in the middle of a definition is rather confusing
however. I would instead suggest that we reserve the words ‘good’ and ‘bad’, ‘better’ and
‘worse’, and the like for axiological discussions and instead use terms like ‘right’, ‘wrong’
etc. for normative discussions. By doing so we will avoid much confusion, and we can avoid
the ‘good without being good for someone’, and ‘bad without being bad for someone’ to
sneak their way back into the discussion. If we follow my reasoning, we would be able to
reformulate (a) by replacing the axiological formulation (including the use of the words
‘better’, ‘worse’, and ‘equally as good as’) in the part before the comma with a normative
formulation (and thus use terms like ‘right’, ‘wrong’ or ‘morally neutral’).
In statement (b), the axiological formulation (with the words ‘better’ and ‘worse’) in
the last third of the sentence should be replaced by a normative formulation (and terms like
‘right’ or ‘wrong’ – or maybe ‘more right’ and ‘more wrong’ depending on the view one
wants to express).
We would then have a normative statement looking like this:
(a) If it is right (wrong, morally neutral) to chose A over B, then A is better (worse,
equally as good) for someone than (as) B for is for someone.
(b) If outcome A is better (worse) for someone than B is for someone but worse
(better) for no one, and B is better (worse) than A for no one, then it is right
(wrong) to chose A over B.
In this reformulation, we do not use words like ‘good’ and ‘bad’ in two different
senses. It is therefore my belief that even though discussing the particular problems
Arrhenius is concerned with in terms of right/wrong instead of good/bad, does not help him
374
See e.g. Arrhenius 2000 p.125
111
deal with the particular problems he is investigating, the shift is still an improvement. It is an
improvement since it stresses the correct question. If we discuss how we ought morally to
behave, it is a matter of right or wrong, not just about good and bad. When we discuss the
non-identity problem, we are as a matter of fact discussing how we ought morally to behave,
considering the fact that what we do will not be better for the particular members of a
particular population, even though it will be good for some other individuals.
To shift our attention from good/bad to right/wrong, will also help us deal with the
non-identity problem without having to jump from the frying pan into the fire so to speak.
I.e. we can save the intuition that we have a moral duty to consider future generations
without having to sacrifice the even more basic intuition that what is bad must be bad for
someone. If we distinguish between good/bad and right/wrong, we will be able to keep the
sentence Parfit rejected (i.e.: “what is bad must be bad for someone”), and instead reject the
sentence: “what is wrong must be wrong to someone”. It seems reasonable to say that what is
wrong does not have to be expressed in terms of ‘wrong to someone’. In fact, it seems
intuitively more correct to say about an act that ‘it is wrong’ than to say ‘it is wrong to
someone’ (or ‘it is wronging someone’), even though it concerns what is good or bad for
someone. That is, an act can be considered as right or wrong without being right or wrong to
someone, but for it to be considered as right or wrong, it has to affect (the quality or quantity
of) things that are good or bad for someone even though the identity of the ‘someone’ does
not matter.
The problem in Parfit’s example was that by choosing the less wasteful life we would
not increase the amount of good for a particular person, but we would still increase the
amount of experienced good in the world. By increasing the amount of good in the world,
we would not make the situation better since it would be better for no one, but we would do
the right thing. There is nothing deeply counter-intuitive in saying that we can do the right
thing even if it does not increase the amount of good or decrease the amount of bad for a
given individual. It also seems reasonable that we can do something wrong even if it does
not increase the amount of bad or decrease the amount of good for a given individual – as
long as there is in fact someone experiencing some amount of good or bad, and the amount
of experienced good or bad will be larger or smaller depending on our behaviour. It just does
not have to be an intrapersonal improvement or impairment. An interpersonal comparison
seems to work just as well.
112
If we apply this to Parfit’s example, we could say that choosing a depleting lifestyle
would be wrong because it would mean that some people would experience less good than
some people would if we choose a less depleting lifestyle, where ‘some people’ may or may
not be the same individuals. The important thing is that we are still talking about things
(food, energy, clean air, wellbeing, happiness, fulfilment of preferences, etc.) that are good
because they are good for someone, and our behaviour is wrong because it means less of
something that is good because it is good for someone (or more of something that is bad
because it is bad for someone). We do not have to infer some kind of objective good that
exists independently of a perspective that experiences it as good. We reserve the term ‘good’
for things that are good for someone, and talk about ‘right’ when we talk about how we
should act.
The conclusion is that the situation which arises in the future if we chose a more
depleting lifestyle today is not bad as long as the population will at least have a life worth
living (since it in that case is not bad for anyone), but to make this choice would be wrong
because it results in a situation that is less good for the people affected than the alternative
would have been for the people that would have been affected had we chosen differently –
independently of the identity of those affected.
Jan Narveson seems to have missed the distinction between good/bad and right/wrong
just as Parfit has, but from another direction so to speak. He claims that: “Duties that are not
owed to anybody stick in the conceptual throat”.375 I believe the reason why they stick in
Narveson’s conceptual throat is that when he is uttering them, he is not distinguishing
between ‘right/wrong’ on the one hand and ‘good/bad’ on the other. If doing one’s duty is to
do what is right, then it has to be about what is good or bad for someone, but it does not has
to be expressed as a duty to someone. To talk about things as being good or bad without
them being good or bad for someone would stick in my conceptual throat too. However, this
is not the same as talking about duties that are not owed to anybody.
Note that the only thing we have to accept in order to avoid the non-identity problem is
that it is possible and meaningful to make interpersonal comparisons. We do not have to
assume the full load of utilitarianism. We do not for instance have to assume any particular
way of comparing good or bad. We do not have to accept that we can or should add the good
or bad of different people. We do not even have to accept that we are always obliged to
make interpersonal comparisons, or that we have to aim for the maximum quote of good
375
Narveson 1996 p.43
113
over bad in order to accept this solution. The solution ought therefore to be acceptable even
for those who have a more deontological view of right and wrong – as long as they accept
that interpersonal comparisons are possible, meaningful and at least in situations involving
different possible future populations also morally relevant.
Therefore, as long as we do not have a very strong aversion towards interpersonal
comparisons, the non-identity problem does not relieve us from having duties to consider the
good of future generations – whoever they will be.
4.1.3. The problem of overwhelming sacrifice
For those who have a utilitarian approach to ethics there is another possible problem to
consider. If our aim is to maximise happiness (or well-being or preference satisfaction etc.),
we
get
into
a
problem
if
we
count
all
happiness/suffering
or
preference
satisfaction/preference frustration independently of when it occurs. If we show equal
consideration to future generations and avoid messing things up terribly by for example
destroying essential ecosystem services in the near future or start an atomic war, there will
be a multitude of generations ahead of us. This means that almost any sacrifice we can make
that will benefit future generations is morally required no matter how small the benefit, since
there will be many more to enjoy the benefits than who makes the sacrifice.376 Therefore, it
seems that we have a duty to live very modestly indeed, and save almost everything to future
generations – and so should the next generation, and the one after that and so on. This in turn
means that as long as people can expect several generations ahead of them, every future
generation would have to abstain from harvesting what was saved by the previous
generation, and just hand it over to the next generation.377
This seems like an unreasonably large sacrifice, and it has therefore been suggested
that we discount the interests of future generations,378 or even disregard them totally.
Derek Parfit does not agree with this solution, and claims instead that our problem
calls for a general limit on how great sacrifices someone can be asked to make for someone
else – independently of whether we talk about inter- or intragenerational issues. He also
376
Almond 1995 p.6, Melin 2001 pp.128f, Narveson 1996 p.38,40, Parfit 1987 p.484, Rawls 1973 pp.286f
Narveson 1996 p.59
378
Melin 2001 p.129, Parfit 1987 p.484
377
114
thinks that if we believe that trying to maximise the total sum of good leads to inequality
between generations and if we find this problematic, we should not solve the problem by
discounting but by adopting a principle of fair distribution.379 If we discount, we may
occasionally end up in situations where we could avoid a larger catastrophe in the future by a
relatively modest sacrifice today but find that it is not worth it since the bad effects in the
future carry less weight.380
I believe that Parfit is right when he points out that the problem of overwhelming
sacrifices is a general problem of distribution and that is not particularly related to
intergenerational matters. We have a similar problem in intragenerational ethics: There is an
almost endless amount of poverty in the world, and almost any krona I make would generate
a larger benefit if I give it to charity than if I spend it myself. Do I have to give up
everything? This is a difficult question for utilitarianism, but no utilitarian would seriously
propose that we solve it by not counting or by discounting the interests of our
contemporaries. If it is not justifiable to use such a method in intragenerational dealings, it
cannot reasonably be justifiable when we are dealing with the same problem only on an
intergenerational level. Luper-Foy in fact goes as far as stating that we have to deal with the
issue of distributing resources justly between different generations before we can take on the
task of distributing the resources among contemporaries in a just way.381
The point is that if we accept the overwhelming sacrifices in intragenerational relations
then we have no excuse for not accepting them in intergenerational relations. If we do not
accept such large sacrifices then that is a problem for both inter- and intragenerational ethics
and it has to be dealt with in a way that would work both within and between generations.
Discounting does not seem to be considered acceptable within generations and should
therefore not be used between generations.
If we want to take on Parfit’s challenge of finding a solution in the form of a system
for fair distribution, we would have to step away from basic utilitarianism. If we accept that
then what kind of solution should we chose? I will look at two different suggestions, and as
we will see, the large number of future people is not just a problem for utilitarians.
Anver de-Shalit especially looks at the problem that we already today have people who
have less than a fair chare of resources, and it would not be reasonable to demand from them
that they further decrease their use of resources for the benefit of future generations. Anver
379
Parfit 1987 p.184f. According to Melin 2001 p.129, others too have reasoned in the same way.
Parfit 1987 p.184f
381
Luper-Foy 1995 p.100
380
115
de-Shalit has aimed for a compromise. He suggests that when duties to future generations
conflict with “a genuine need to improve the welfare of contemporaries”, we should look for
what he calls “a middle way”.382
When our
obligations to very remote future generations do not contradict obligations to
contemporaries, we have no excuse not to fulfil them. If these obligations to very
remote future generations clash with certain obligations to contemporaries, and
especially to the worst off among our contemporaries, it is reasonable to argue that
in some cases our obligations to contemporaries have some priority (although this
difference by no means cancels out our obligations to very remote future
generations). 383
It is not easy to draw any conclusions from this and it is even harder to find any useful
advice on how we should actually behave.
Gregory Kavka suggests that we use Locke’s principles of just acquisition, and adapt
them to an intergenerational setting. This means that it would be acceptable for us to use
resources as long as we do not waste them and as long as there is “enough and as good” left
for others.384 This in turn implies that we should leave the next generation at least as well off
regarding resources as we were.385
What does it mean to leave enough and as good of a non-renewable resource? One way
of doing so could be to limit the number of people – i.e. to limit the number of competitors
for resources – in the future, and thereby decreasing the pressure on the resources.386 That is
probably not what Locke had in mind. In addition, for non-renewable resources this would
not be enough if we want to uphold Locke’s proviso. Even if we use the resources very
sparingly, there will be less and less, and sooner or later, it will be totally depleted. Before
that happens, there will be less left than each of us has used and therefore Locke’s proviso
will no longer hold.
One way of dealing with this would be to decrease the number of people in each
generation and eventually let the species disappear when the resources are exhausted.
382
de-Shalit 1995 p.11
de-Shalit 1995 p.11
384
Kavka 1996 p.200
385
Kavka 1996 p.200 Robert Nozick and Robert Elliot are reasoning along the same lines (Melin 2001 p.130).
386
Stenmark 2000 pp.53ff
383
116
Kavka is opposed to exterminating humanity,387 but what other alternatives are there?
Kavka talks about recycling and using technology to increase the output of resources,388 but
that is probably not enough. Even if we get better at extracting a non-renewable resource, it
will disappear eventually and we cannot recycle everything. Some resources are destroyed
when we use them. In fact, even for the resources we can recycle, the second law of
thermodynamics will eventually claim its due.
An alternative would be to widen the interpretation of Locke’s proviso and allow for
substitutes.389 This approach is often advocated by economists (see chapter 2 above), and
would be in accordance with e.g. the Brundtland report, which tells us that we may use or
even deplete a resource as long as we compensate for the loss.390
Take for example fuel. One way of leaving enough fuel to future generations is to see
to it that all future generations will have as much fossil fuel at their disposal as we have had
at our disposal. However, since we cannot produce fossil fuel, and since it takes nature
millions of years to do so, it means that given a stabile population, we will not be allowed to
use any fossil fuel at all. However, if we allow for substitutes, we can use all the fossil fuel
there is, given that we find an alternative that will do the same job to the same extent and just
as good. This modification of Locke’s proviso seems more reasonable, and would just take a
small amendment. We only need to shift focus from the resource to what we can get from it.
What would this shift mean for our investigation? The answer is that it would reaffirm
a suspicion that has been brought up before: That it might be acceptable from an
anthropocentric instrumental perspective to drive a species to extinction as long as the
service or goods we get from it can be substituted by another species or by a non-living
source. This means that if we allow for substitution and concentrate our concern on the
goods or service rather than on the resource as such even in an intergenerational setting, our
theory will be a weaker defence against extinction, and may not be able to entirely account
for the intuition we aim to explain.
387
Kavka 1996 pp.192ff
Kavka 1996 pp.200f
389
This alternative is apparently suggested by Elliot and Nozick. See Melin 2001 p.130
390
Stenmark 2000 p.56,62f
388
117
4.1.4. Mental impossibility
It is not easy to imagine or to reason about things that will take place very far in to the
future. It is probably even more difficult to mobilise really emotions towards events that are
far into the future even if it is possible to reason around them in an abstract way. This
problem has been pointed by Anver de-Shalit and Jan Narveson among others. According to
both of them, it means that we cannot in practice demand from now living humans that they
make sacrifices on behalf of future generations that are comparable to the sacrifices we can
demand on behalf of their contemporaries.
Anver de-Shalit argues that we should discount the interests of future generations (by
not adjudging them with positive duties more than a few generations into the future) because
duties that reach too far into the future would demand what is for most people
inconceivable.391
Narveson tells us that a principle that gives future generations the right to an equal
share of resources that are basic for life, would be “impossibly abstract or obscure or
both”.392 He also claims that this principle will be “self-extinguishing”. The reason for that is
that we are deciding the size of the next generation. Narveson asks us to consider a scenario
where we cut the next generation by one half. The question will then be: What does that
mean for our resource use? Does it mean that the members of the next generation will be
able to enjoy twice as many resources, or does it mean that we will be able to spend more of
the resources?393
Parfit and Melin do not agree with this however. Parfit claims that the fact that future
individuals cannot be identified is no more relevant than that we might have difficulties
identifying individuals who are geographically far away.394
Melin points out that to take departure in the question of whether presently living
people think we should care about future generations is to beg the question that it is the
values of now living people that count while the future only counts if we think it should
count.395
The question is undoubtedly interesting: Does our limited imaginative faculties justify
a discounting or even non-counting of the interests of future generations?
391
de-Shalit 1995 p.14
Narveson 1996 p.60
393
Narveson 1996 p.60
394
Parfit 1987 p.357
395
Melin 2001 p.11
392
118
I do not believe it does. Both Melin’s and Parfit’s objections seem valid, and in
addition, one can point out another thing that I believe is crucial. I believe that as long as it is
mentally possible to rationally understand that even future people will have interests and that
the future realisation or frustration of these interests can be affected by what we are doing
now, we have a duty to consider this in our decisions even if it is a difficult intellectual
process and even if it is not possible to fully take in emotionally.
4.1.5. Uncertainty
According to the Brundtland report, sustainable development is a development that
“ensures that it meets the needs of the present without compromising the ability of future
generations to meet their own needs.” To be able to live up to that, we need to know what
the needs of future generations are. Even if we follow the terminology already in practice in
this book and use the wider term ‘interests’, this is a task that seems very difficult. There is a
large degree of uncertainty regarding the interests of future generations,396 and this problem
is also accompanied with some other problems. Anver de-Shalit for instance points out that
even if it were possible to foresee the interests of future generations – which he does not
believe it is – it would be complicated to compare and weigh their interests against the
interests of our contemporaries.397
Another problem is that we do not know for sure what life will be like in the future,
how the technology will develop, or even for how long the human species will survive.
Our inability to make reliable forecasts not just about the preferences of future
generations, but also about the future in large, makes I.G. Simmons question the entire idea
of caring for future generations:
There is time for caution here: if we define justice to include future generations, but
cannot forecast the nature of that future at all accurately, then how do we know
what to avoid?398
396
Farber 2000 p.s495
de-Shalit 1995 p.5, Melin 2001 p.128
398
Simmons 1995 p.71
397
119
Simmons does not want to see this as an excuse for a laissez-fair attitude in relation to
future generations, but how do we avoid such an attitude? When we look at the problems
presented here, one might be tempted to limit our concerns to the present, and possibly to the
immediately following generations while leaving the rest to their destiny. Another approach
would be to discount our concern for the future at a rate representing the degree of
uncertainty. This last approach is used by many economists and some philosophers.399 One
fact in favour of discounting rather than a more abrupt cut off-point is that we are dealing
with predictions that tend to get more uncertain the further into the future we stretch them.
Discounting would make it possible to lessen our concern successively in proportion to the
increasing uncertainty.
Another possibility is put forward by Jan Narveson who suggests that our almost total
lack of knowledge of the future can be seen as an argument for confining our concern for the
future to approximately the next 50 years.400 His argument is that since we are next to totally
ignorant, “no rational consideration of the problem is possible …”.401
One might point out here that if “no rational consideration of the problem is possible”
how can he then conclude that confining our concerns to a special length of time is a better
solution than any other solution? I think Narveson is too pessimistic however. In the
previous chapter we noted that inertia is not always the best way of handling uncertainty. We
found that in situations where for instance important values are at stake, it is more rational to
take precautionary measures such as demanding extra high degrees of certainty in order to go
through with a project that might threaten the value in question. If we have a situation where
our decision may threaten important future interests although we do not know if they will,
the conclusion must be the opposite of what Narveson recommends. I.e. in order to be
justified to ignore future generations, we should demand a high degree of certainty that
future generations will not hold the interest in question. Lack of knowledge should count
against ignoring them, not the other way around. The degree of certainty we demand should
of course as we saw earlier stand in proportion to how important we suspect the interest to
be. This is complicated since that is one of the things we do not know, but which also seems
to talk in favour of being extra careful with what we subject them to.
399
See Gower 1995 p.57, Kavka 1996 p.190,202 note8 Kavka also mentions Martin Golding (“Obligations to
Future Generations” Monist 56 1972 pp.97-98), Parfit 1987 p.481
400
Narveson 1996 p.40f
401
Narveson 1996 p.41
120
Parfit is in general negative to discounting and he makes no exception when it comes
to uncertainty. He follows the same strategy as before and points out that we have to
distinguish between (1) the fact that our predictions get less certain over time, and (2)
whether, given the assumption that a prediction is correct, we are entitled to discount the
weight of the effect just because it takes place in the distant future. He admits that (1) is
often the case, but does not believe that this can answer (2).402
According to Parfit, this is important for two reasons. Both because we should be
careful not to “miss-state our moral view”, and because there are situations when predictions
do not get less certain over time.403
I agree with the first reason: We should be more cautious about the terminology we
use and not claim that we discount on the basis of time as such when we are actually
discounting on the basis of diminishing certainty.
How about Parfit’s second reason? Even if he is correct and there actually are such
cases, we still have to admit that most prognoses do get less certain over time. On the other
hand, it might be that the things we can predict with a higher degree of certainty are
important enough to make a difference even if the uncertainty is great in the general case.
Several authors point out cases where our knowledge about future generations is not so
bad,404 Kavka e.g. points out that we can know about future generations that they will need
“enough food to eat, air to breathe, space to move in, and fuel to run machines”.405 This
looks correct, but what does it tell us? Even if we agree that they will need fuel for their
machines, we don’t know what kind of fuel. When I write this a large amount of alternatives
are being developed, and I would not like to put much money on a bet about which of these
will be the fuel of the future. Maybe a combination? Maybe something completely different
that no one has yet thought of? Our need for things like food, air and water on the other hand
is biologically determined and we can assume that these things will not change substantially
in the future. All life forms on the planet need water and nutrients, and all “higher” life
forms need oxygen. This may not seem like much information to base our concern on, but
for this investigation, it is very central. This means that we have to apply our concern for
future generations on our previous food discussion, and the same goes for ecosystem
services. In order to have a working water cycle, sufficient levels of oxygen, suitable climate
402
Parfit 1987 p.481f
Parfit 1987 p.482,486
404
See e.g. Kavka 1996 p.189, Melin 2001 p.129, Munthe 1997
405
Kavka 1996 p.189
403
121
etc. we need working ecosystems. This means that the few things we do know about the
needs of future generations are still very important for our investigation. It is true that it only
takes away some of the uncertainty and therefore only deals with the argument from
uncertainty for some particular interests. On the other hand, these interests are very basic and
they are directly related to some of the ways where other species are the most important for
us.
The conclusion seems to be that we are not justified in using the lack of certainty
concerning future generations as an excuse for discounting their interests. We only have
some knowledge about a few things but these things are on the other hand very important –
and directly relevant for our investigation since they imply that species that have a high
instrumental value for us will also have a high instrumental value for future generations of
human beings. When it comes to the things we do not know, it seems most reasonable to
invoke the precautionary principle. That means that since we do not know whether a
particular species will be important for future generations, but have a strong suspicion based
on historical evidence that many species will turn out to be important for future generations
probably in ways we can not yet imagine,406 we should be very restrictive when it comes to
doing things that risk leading to extinction, and the burden of proof should lay on the
shoulders of those in favour of exploitation.
4.1.6. Democracy
A possible argument for discounting is that most people living today seem to be less
concerned with the further future compared to the immediate future. We could claim that we
for democratic reasons have to respect this and discount the future.407
However, Parfit points out that this argument only exhorts us to follow the majority
view concerning whether we should discount the future. It does not tell us what this view
morally ought to be – and this is the question we are concerned with.408 I agree with Parfit
that there is a distinction and that it is relevant. Since we are performing a moral
investigation, the relevant question is whether it is right to count the interests of future
406
Gärdenfors 2005 p.119
Parfit 1987 p.480
408
Parfit 1987 p.480
407
122
generations for less than the interests of contemporary people. This question cannot be
answered by an election.
There is also another problem with the argument from democracy. It begs the question
of whose interests should be considered. A basic assumption of the argument is that most
now living people are less concerned with the further future. If we base our decision solely
on the interests of the concerns of now living people, we have excluded the interests of
future generations already in the decision process.
It is in fact a serious problem for present versions of democracy that they seem
incapable of dealing with this kind of questions: They are not democratic over time. We do
many things today that have been decided by “democratic” methods by now living human
beings, but where most of the people who will be affected by the decisions are not
represented in the decision process simply because they are not yet born. Since the normal
democratic process is inherently biased in favour of the present population, we cannot rely
on the normal democratic process in intergenerational issues. If we want a reason to exclude
the interests of future generations, it has to be an independent argument why their interests
should not count. It cannot be based on a process where the interests of future generations
are excluded already in the process.
4.1.7. Opportunity loss
A common reason for discounting the future is based on the issue of opportunity loss.
A thing that (like money) represents an instrumental value has value because of what you
can get out of it (in the form of intrinsic value or of another instrumental value – like more
money). The earlier you get something, the more utility you can extract from it. If you get it
later, you will not be able to use it while you wait, and you will therefore lose
opportunities.409 This is an important reason for economic discounting, but is it applicable to
the question of whether and to what extent we should consider the interests of future
generations?
Alan Randall does not think so. He points out that market economy has a tendency to
handle questions of resource use over time as investment problems, but he is not convinced
409
Parfit 1987 p.482f
123
that this is a possible approach in situations like extinction that has effects for a very long
time and are irreversible.410
Parfit points out in the same way as we have seen above that it is important to keep in
mind the reason for discounting. If we think it reasonable to discount for opportunity losses,
we should be clear that it really is a matter of opportunity discounting, not temporal
discounting as such. Parfit stresses the importance of being clear about this both in order for
us not to be led astray in our moral reasoning and because he does not believe that
opportunities always decrease over time. For instance, some investments do not bring any
return, and things we consume do not decrease in opportunity value if we receive them later
(we still only consume them once). Furthermore, when we deal with trade-off-situations, we
will continue to get value out of what we started with until we trade it in. This will
compensate for the value we should have extracted from the thing we are going to trade it
for. Assume that we are going to exploit a beautiful landscape in order to build an airport,
but the exploitation is delayed. We will then lose opportunity value because we cannot use
the airport but we will also gain opportunity value because the landscape will be intact and
can be used for other things like recreation.411
Parfit’s reasoning seems reasonable up to a certain degree, and I think his last point is
well worth pointing out since it is often forgotten. We also have to admit however that if we
find the trade-off worth doing in the first place, i.e. if we value the airport higher than the
unspoiled landscape, we have presumably decided that there is more value in the airport than
in the unspoiled landscape. We will therefore lose net-opportunity-value by delaying the
exploitation even if we can get some value from the unspoiled landscape while we wait.
What does it mean for our investigation? Let us assume that building the airport in the
example above will lead to the extinction of a species that has its last refuge in the area. Let
us also assume that the species supplies some kind of good but that the airport will be more
valuable for us than the species. Let us finally assume that by the time the last contemporary
human has died, the airport has become obsolete but that the species would have continued
to produce the good had it been allowed to survive. That would mean that even though its
value for us is smaller than the value for the airport, its value for future generations will be
larger than that of the airport. These are the assumptions. The reason for the last assumption
is to create an intergenerational conflict. The question would then be: Does opportunity
value in cases like this tell us to build the airport?
410
Randall 1986 p.83,96
124
An aspect that seems to be important when we apply the question of opportunity value
on intergenerational relations is that the receivers of the value will change during the
process. If we build the airport, we will receive a higher opportunity value. Future
generations will not get anything and since they will not have the species either, they will
lose out on the deal. It therefore looks like discounting on the basis of opportunity value
assumes that future generations do not have any moral standing or at least a lower moral
standing.412 There might be another explanation however. It may be that we do count future
generations but realise that we will get more out of the airport if we build it than they would
get from the species. I.e. we will win more than they will lose. In that case, we do not have
to assume that future generations are without moral status in order get the result that it is
better all things considered to build the airport. In fact, we have not even reached the
conclusion that the interests of future generations do not count. We have considered their
interests but concluded that it will be more in our interest to drive the species extinct than it
is in their interest that we preserve it. That way, opportunity value is not really a basis for
discounting the interests of future generations, but in practice it will at least in some cases
still make references to the interests of future generations less useful for those who claim
that we should protect species for anthropocentric instrumental reasons.
The reasoning above presupposes a strictly utilitarian outlook. It might be that we hold
a moral conviction about what is to count as a just distribution of harms and benefits
between moral object, or any type of principle with the effect that there are limits to what we
can subject a moral objects to in order to benefit someone else. Then we cannot dismiss the
fact that we will get the benefits of the higher opportunity value while future generations will
not get anything, as easily as we did above. I.e. we cannot get rid of the problem that we get
all the benefits from the airport and they get none of the benefits (since they have no use for
the airport and the species is gone), by referring to the fact (when it is a fact) that the total
sum of good will be larger that way.
In cases like this, it therefore seems that a deontological approach would mean larger
consideration of future generations, and also a stronger reason to avoid extinction.
Even from a utilitarian perspective however we have to remember that it is not
necessarily always the case that the total value will be higher from decisions like the one
above. Not even the opportunity value would always be higher that way, and even when it is
higher, it can in many cases be outweighed by a higher total value over time if we utilise the
411
Parfit 1987 p.483f
125
species in a sustainable way. The important point here is however that there will probably be
some cases where a utilitarian anthropocentric instrumental approach – even if we accept
moral standing for future generations – will accept that we drive a species to extinction even
when the moral intuition we are investigating in this book tell us that it would be wrong. I do
not know how often this will happen in reality, but it still weakens the position for
anthropocentric instrumentalism in our investigation.
4.1.8. Distance
Parfit is very careful to point out that we should not claim to be discounting because of
time when our reason for discounting is in fact something else. In this sub-section, we shall
ask whether it is reasonable to discount because of the distance as such between the
decision-maker and the affected person. We can imagine different kinds of distance. One
type is temporal distance. Another is genetic distance (distance of kinship).
Parfit claims that discounting because of kinship is not strictly the same as discounting
because of temporal distance though in practice they always coincide, since degree of
kinship does decrease from generation to generation.413
However, temporal discounting may well play a role of its own independently of
kinship or other distance discounting. If one believes that the distance between the agent and
the object is important for moral considerations, why should genetic distance be more
important than temporal distance? I guess we should rather say that temporal discounting is a
sub-category of distance discounting just like genetic discounting (or kinship discounting) is.
Even if these two sub-categories in general co-inside, they do not always co-inside and have
to be handled separately.
The most interesting question is whether discounting for distance is morally acceptable
(or even obliged) – and whether it is a matter of temporal distance or of genetic distance.
Parfit compares time discounting and spatial discounting. He claims that no one
accepts spatial discounting, and believes that temporal discounting is equally
unacceptable.414 Mary Warren, Kristin Shrader-Frechette, L.W. Sumner, Gregory Kavka and
412
This seems to be Munthes conclusion (Munthe 1997).
Parfit 1987 p.485
414
Parfit 1987 p.486, 357
413
126
Jan Narveson reason along the same lines. Warren makes an analogy with different kinds of
non-acceptable discrimination forms of now living people. She claims that “the historical
period in which they exist” is no more relevant as a basis for moral standing than is other
“accidental properties” such as age, race or sex.415 Shrader-Frechette makes the same
analogy with irrelevant properties but from a contractual perspective.416 Sumner points out
that to favour someone just because of her location in time is to count someone for more
than one, which cannot be acceptable according to utilitarianism.417 Kavka notes that spatial
location is not morally relevant, so why should location in time be? He also considers it part
of rational prudence to put equal weight on one’s own present and future, and thinks that
analogously rational morality should put equal weight on present and future generations.418
Narveson argues that the fact that people differ by their location on the planet does not grant
that we should treat them differently and the same should apply to future people who differ
from us when it comes to their location in time. The same rules that guide our dealings with
contemporary people should thus apply to our dealings with future generations just as the
same principles apply to all presently living people even though some live quite far from us
in geographical terms.419
Kavka’s comparison with rational prudence does not seem relevant here since in his
example we are talking about one and the same person, not about our duties to consider other
people’s interests.
How about the general comparison with spatial distance made by all of the
abovementioned authors? It seems reasonable that if we are not allowed to discriminate
because of spatial distance as such, we should not be allowed to discriminate because of
temporal distance as such, and I cannot think of any relevant difference between the two
cases that would make it acceptable to treat the cases differently.
How about kinship distance then? Can we apply the same reasoning there? Intuitively,
it does not seem unreasonable to treat one’s own family different than others, at least in
some respects. I believe very few people would find it immoral if someone feeds her own
children rather than sending food to distant children if we have to choose between the two
options. In fact, many people are inclined to find it morally questionable not to take special
care of their own family. This does not seem to be a matter of strict proportional discounting
415
Warren 1996 p.29
Shrader-Frechette 2000 p.772
417
Sumner 1996 p.103
418
Kavka 1996 p.188
419
Narveson 1996 p.39
416
127
however, and it apparently does not apply to all situations. Even if it is morally required to
give certain benefits to your closest kin or to give priority to your closest kin in some
situations, you may not do so generally and you are not allowed to harm others in order to
benefit your closest kin, at least not if the harm done exceeds a certain magnitude. Parfit
suggests that the kinship discounting in analogy with spatial discounting (which he now
surprisingly seems to accept) should not apply to inflicting of great harm. I.e., even if it is
acceptable to give larger benefits to your closer kin, this way of reasoning is not acceptable
when we talk about large degrees of harm. To cause great harm to anyone is never
acceptable according to Parfit independently of how distantly related the victim is.420 This
should obviously be more specified since we need to establish where to draw the borderline.
It might also have to be widened since it is not always acceptable to give larger benefits to
your closer kin either. Parfit’s solution does seem to be generally acceptable however.
Another thing we have to add which is also pointed out by Parfit is that the discounting
should probably only apply up to a certain distance.421 Even if it is reasonable to treat your
own child differently than a much more distantly related child, it is not acceptable to treat
that child differently than an even further related child. Discounting is therefore reasonable
only up to a point. The alternative would be a discounting that decrease exponentially with
decreasing degree of kinship. This alternative could be made to coincide closely with the
exponentially decreasing degree of genetic kinship.
Our conclusion is that discounting based on distance is reasonable when it comes to
kinship distance but only up to a certain point, and only in some situations, and never when
we are talking about great harm. No discounting is acceptable on the basis of temporal
distance as such.
4.1.9. Will they need our sacrifices?
Another thing to consider is that although many natural resources decrease and are
eventually depleted, other types of good actually increase. Knowledge is e.g. typically
increasing. By the help of knowledge, we can find substitutes for some of the depleted
resources. We also invent new technologies that utilise other – and possibly less – resources
420
Parfit 1987 p.486
128
than the old technologies. This means that we could make up for at least some of the demise
we have caused by accumulating knowledge and improving science and technology that
benefits the lives of future generations.422 Since new knowledge is constantly created and
since knowledge can be transferred from the present to the future but not the other way
around, it is highly probable that future people will have more knowledge than we do. That
way, they may figure out remedies to the problems we have already caused.423 Some
economists even claim that the increase of human knowledge might be more important than
natural resources for the economy.424
This is sometimes seen as an argument not to restrict our selves for the sake of future
generations,425 or at least to discount the negative effects of our actions. Parfit identifies two
principles that support this reasoning:
1. Diminishing marginal utility. They will be better off than we are. Because of that, a
certain resource or other benefit would be relatively less important for them than for us. It is
therefore reasonable that we use the resource instead of saving it for future generations.
2. Distributive justice. If they will be better off than we are, we cannot be morally
required to redistribute our more limited resources to benefit them.426
By now, we know Partfit's position. First, to discount because of (1) and (2) is not the
same as discounting for temporal reasons and we should be careful to state the correct reason
for our discounting. Second, the overlapping is probably not perfect. Some future humans
are likely to be less well equipped than some present day humans.427
An interesting problem with (1) as an argument against making sacrifices is pointed
out by Anver de-Shalit. Thanks to technological progress, the resources we leave to future
generations may well be worth more to them than to us.428 This means that from a utilitarian
perspective, the accumulation of knowledge and improvement of technology can be an
argument in favour of preservation.
Another author who is not satisfied with the appeal to knowledge accumulation is
Shrader-Frechette. She is not explicitly talking about species extinction, but attacks the
assumption that future generations might be better equipped to deal with nuclear waste than
421
Parfit 1987 p.485f
Narveson 1996 pp.39f, Rawls p.288, de-Shalit 1995 p.2
423
Narveson 1996 p.40,57,59
424
Radetzki 1990 p.48,51, Radetzki 2001s.72
425
Narveson 1996 p.60, Rawls 1973 p.287
426
Parfit 1987 p.484
427
Parfit 1987 p.484
428
de-Shalit 1995 p.4f
422
129
we are.429 Her arguments could be useful also in a discussion about species extinctions
however.
She launches four arguments:
The first one resembles Parfit’s second objection above: We cannot know that future
generations will be better equipped than we are to deal with a certain problem. She mentions
that things like overpopulation and depletion of resources as well as the possibility that the
problem as such get worse over time, may actually make it harder for them to deal with the
problem.
Secondly, she invokes an argument from justice: Even though another person is better
equipped to deal with a problem than I am, I have no right to expose this person to the
problem.
Her third argument is that the appeal to increasing knowledge is self-serving by being
clearly in the interest of those who make the decision.
The fourth argument says that we are dealing with a case of misplaced priorities. She
argues that it is more important to protect someone from harm than to promote welfare and if
a person is harmed, she cannot be compensated by enhancing the welfare of someone else.430
Let us take a look at these arguments: In her first argument, Shrader-Frechette
questions the assumption. I find it very difficult to assess it the probability of the assumption
in the long term but so far the accumulated knowledge of humanity has increased
tremendously and seems to increase exponentially. As a result, our technological capacity
has skyrocketed (not just literally). If this continues, there seems to be almost no limit to
what future humans may be capable of. Not everyone is convinced that this will be enough
however. Luper-Foy for instance is rather pessimistic about the possibility of solving the
problems we have caused by improved technology. He claims e.g. that there is not much
room for improvement of the food production.431 We also have to remember that the
assumption that the capacity of future generations to solve all problems we may throw at
them is based on simple extrapolation and we ought to be careful about what we impose on
posterity with reference to such an unsophisticated forecasting method. There have been
periods of stagnation in the history of human thought. During the middle ages, the Catholic
Church put a very strong lid on human thinking, which in effect meant that intellectual
progress in many areas was made virtually impossible. We cannot be totally sure that this
429
Shrader-Frechette 2000 p.773
Ibid
431
Luper-Foy 1995 p.99
430
130
will not happen again, even though it seems unlikely. Had for instance Nazi-Germany been
victorious in World War II we might well have ended up in a situation where new thinking
would have been impossible in many areas and old knowledge would have ended up in the
flames. We can also imagine that catastrophes like atomic war or extensive climate change
may be at least as effective lids on human progress in the future. The very behaviour we are
trying to defend by the argument from increasing knowledge may eventually undermine the
argument by prohibiting the progress. It might be a good idea to apply the precautionary
principle again. Since we do not know what capacities future generations will hold, and since
large values are at stake, we should not use this uncertainty as an excuse for not taking the
necessary measures to avoid imposing the problems on them.
Let us now have a look at Shrader-Frechette’s second objection: It does indeed seem
unacceptable in intragenerational relations to go around and cause problems for other people
and excuse oneself by pointing out that they have the ability to handle it. It is one thing that
someone is capable of dealing with a problem. It is another to say that it is acceptable to
expose him to the problem (whether I too have this capacity or not) – at least as long as it
actually is a problem. If future generations would have such powers that problems that seem
overwhelming to us are not even problems to them, then maybe it would be justified to say
that we have done nothing wrong by exposing them to these “problems” simply because they
would not be problems. What then if they are still problems but so insignificant that future
generations will be able to deal with them in a few seconds by a simple and cheap operation,
or that their society or technology will be so different from ours that what would be very
large problems for us are only very small problems for them, and that they would be able to
live with them with only a small inconvenience? Then I suppose we would be justified in
saying that what we did was a little selfish, but not that bad. What if the problem would take
a little more effort to solve or make their lives somewhat more inconvenient? Then one
should probably say that what we did was not very nice, but no serious crime. So we could
go on. My point here is that we are dealing with a matter of degree. The question is: Where
should we draw the line?
A utilitarian will clearly draw the line where the total expense for future generations
will be larger than the gain for us.
From a deontological perspective, this is not acceptable. According to ShraderFrechette, it is intuitively obvious that we have to consider basic rights before we try to
131
maximise the total welfare.432 This is her fourth objection. I will not enter the debate of
deontological versus consequentialist ethics here. I just note that if we assume a
deontological position, our answer would not so much depend on how much we can gain
from imposing this problem on future generations. Instead, we would have to accept that
imposing problems on future generations for our own gain is not a just behaviour even if the
problems we cause are relatively small. Exactly where the limit should be placed is however
a question that remains to be answered.
Let us turn to the third objection: The fact that a decision favours the decision-maker is
not in it self an argument against it. Considering what our experience tells us about human
beings, however, we must be aware of the risk of bias. This is a reason for some degree of
healthy suspicion. When dealing with future generations we also have to take into account
the fact that we for obvious reasons cannot mitigate the risk by letting them take part in the
decision.
The fourth objection is in fact two: That it goes against the principle that harm is more
important than benefit, and that it goes against the principle that it is wrong to let one person
pay for someone else’s benefit even if the benefit is larger than the harm.
I have already discussed both these intuitions. The second one is discussed above and
the first one is discussed in section 3.3.1, where we concluded that it was in need of better
justification before we dare to accept it and that we therefore do not want to rely on it in this
investigation.
The conclusion from this sub-section must be that the accumulation of knowledge is
very large and it is reasonable to assume that it will increase the capacities of future
generations to deal with problems that seem overwhelming to us, but that we cannot straight
off take this as a valid excuse for downplaying our responsibilities. There are still moral
problems with imposing the costs of our progress on future generations even if they can
handle it. We have also seen that there are uncertainties that have to be dealt with, and that
the accumulation of knowledge may even in some cases be an argument in favour of
preservation.
432
Shrader-Frechette 2000 p.773
132
4.2. Conclusions
For anthropocentric instrumentalism, it is important to show that we have moral duties
to consider the interests of future generations. In this chapter, we have seen that there are
many difficulties but that it is quite reasonable to assume that we have such duties as long as
we do not adhere to a contractarian or communitarian approach to ethics, and as long as we
accept interpersonal comparisons. We have found some reasons to restrict our duties to
future generations in certain situations e.g. by discounting, which weakens the power of
anthropocentric instrumentalism somewhat.
We have to add however, that if duties to future generations of human beings is a good
reason to consider extinction a moral problem, a non-anthropocentric view that accepts
duties also to future generations of non-human life, would give us an even stronger reason
for preservation.
133
5. Something is Lacking
Alan Randall tells us that: “The earth’s biota may be viewed as a resource or a
complex group of resources.”433 The question is, may it exclusively be viewed as a resource
or a complex group of resources, or are there other types of value that have to be considered
in order to answer the question of what is wrong with extinction? Maybe it is problematic in
itself to regard other species just as resources? We have up to now assumed an
anthropocentric instrumental vantage point in order to test what obligations anthropocentric
instrumentalism place upon us regarding other species. As philosophers, we cannot stop
there. We must also ask whether something in our moral intuitions cannot be captured by the
view of the earth’s biota as a resource or as a complex group of resources even if this view
supplies us with strong reasons for preservation of the biota. Let us illustrate this with an
analogy:
Imagine a meeting in the southern part of USA some time during the first half of the
nineteenth century. A group of slave owners has gathered to discuss some disturbing
rumours about the slave trade. These rumours say that the slave ships are coming in less and
less frequently. Presumably because the slave traders have to travel further and further inland
on the African continent to find new slaves. There are even worries that if they continue to
harvest slaves at the same pace, Africa will soon run out of humans suitable for slavery. At
the same time, the cotton harvests have been larger than ever, so the economy is going great.
As a result, the slaves who have done the harvesting are completely worn out. Many have
become sick or permanently crippled. Some have even died, and “to be honest” – one of the
slave owners admit – “we have mistreated our slaves”. “In fact” – he continues – “some of
us do have a tendency to use the whip a little too much. Not that the slaves didn’t deserve it,
but we have noticed that the slaves that have been too severely punished have had trouble
working after a while. So maybe we should try to treat our slaves a little wiser? After all, the
slave system has worked well for us and we want it to work well even for our children and
grandchildren, and we should definitely develop this system so that more white people can
have their own plantations and prosper economically. In short, we need a more sustainable
development of the slave trade!”
433
Randall 1986 p.79
134
For a present day observer, it is immediately obvious what is wrong with this picture.
The slave owners regard the slaves as merely resources for them to use, and instead of
abolishing a genuinely immoral system, they are looking for methods to prolong it.
There are obviously many differences between the picture above and the problems we
are dealing with in this investigation, but I trust the reader does not let the main point of the
analogy get lost among the differences: The slave owners in the story did not really care for
the slaves. They just cared for the work they could do, and the reason for lessening the
pressure on the slaves was exclusively about productivity. In the same way, according to
anthropocentric instrumentalism, other species should be preserved not out of concern for
the species or their individual members, but only out of concern for ourselves and future
human generations. The species should be preserved in order to be better utilised, not in
order to assure a morally acceptable solution.
What this story shows is that a full account of why it is morally problematic to
contribute to the extinction of other species possibly involves more than instrumental values
for human beings. Even if that value is enough to establish that something is wrong, it may
not give the whole moral picture.
Even so, could we not just play along and appeal to the instrumental value of the
species for tactical reasons? When we started our investigation of anthropocentric
instrumentalism as an answer to our main question, we noted that this answer has a
dominating position in national and international policy documents. Could we not use that in
order to get the protection we want even if it is not (totally) for the right reasons? It is not
uncommon to hear phrases with that purport from active environmentalists, but there are
risks connected with this strategy. One risk is that by using this tactic we will get what we
ask for, but not what we want. It happens now and then that environmentalists and
environmental groups seemingly successfully use anthropocentric instrumentalist arguments
to back up their claims but when they finally get what they asked for they are still not happy.
The government, city council or company they have been negotiating with cannot
understand why the environmentalists are still complaining since they got what they asked
for. Sometimes even the environmentalists themselves have difficulties explaining what is
wrong. They may disagree among themselves about why, but they at least agree that
something is wrong. The problem might be that the environmentalists want to preserve an
area or a species because they see some kind of value in it that exceeds the human resource
135
value, while what they got (and what they probably argued for) is a law (/policy/agreement
etc.) that preserves the species in order to use it more efficiently by the human society.
Very often, it seems that a species is preserved only as a way of producing new
individuals that can be utilised. For many, this is counter to their moral intuitions, and it
seems that even if this way of handling nature is rather prudent, there is something wrong
with it. Many would say – like in the example with the slave owner convention above – that
it is something morally wrong.
J. Baird Callicott makes an analogy with space travellers who find life on another
planet, and after having established that it is life, they eradicate it. Intuitively, there seems to
be something wrong about this – something morally wrong. Callicott claims that this would
be more wrong compared to if they had eradicated some interesting geological patterns.434
Apparently, this extraterrestrial life form does not have any greater resource value for us so
why is it still wrong?
This question will be subject for a continued investigation and another book. This part
of the investigation has reached the stage where it is time to wrap it up and see what we have
found out.
434
Callicott 1986 p.142
136
6. Summary and Conclusions
This book contains the first part of an investigation aimed at finding out why it is
morally wrong (at least prima facie) to cause species to go extinct. That it is morally wrong
seems to be a very basic and widely held intuition. It seems reasonable that a moral theory
worth taking seriously ought to be able to account for that intuition.
The most common attempt to answer our question is to refer to the instrumental value
of the species for human beings – the anthropocentric instrumental approach as I have
chosen to call it. This is the answer that is discussed in this book.
We have found many ways in which different species have instrumental value for
human beings – both individually and as a part of ecosystems and of biodiversity in general.
We could not guarantee however that this includes all species. In some cases, it also turned
out that the instrumental value of the species in fact favours exploitation maybe even as far
to the extinction of the species. We also noticed that there is no guarantee that the
instrumental value of the species can always outweigh the competing values that we would
gain by different encroachments that contribute to the extinction of the species.
We found however that there are some special circumstances that help push the scale
in the direction of preservation. I am thinking of some particular types of value such as
choice value and transformation value – values that in general seem to favour preservation of
species. This principle shows us that it would be rational from an anthropocentric
instrumental vantage point to rule in favour of preservation in many of the cases where we
are uncertain about the value of the species, about the best way of utilising the value, or
about the connection between the species and other species or biodiversity in general. I am
finally thinking of the moral principle that we have duties to consider the future interests of
generations to come. We found that with a few exceptions it is justified to adopt such a
principle. This in combination with the principles of precaution ought in general to urge us
not to cause the extinction of species unless we have very trustworthy evidence that they will
not turn out to be more valuable alive to future generations in comparison to what we can get
from driving them to extinction.
In relation to the discussion about the value of other species for human beings, it is
worth noticing that all the arguments we have found in favour of preservation would be even
stronger – and therefore account even better for the intuition that it is at least prima facie
137
wrong to cause extinction – if we also accepted that other entities than human beings can
have moral standing.
Finally, we noticed that our moral intuitions strongly indicate that even in the cases
where the instrumental value of other species for human beings talks in favour of
preservation, there is still something lacking. Something we have to account for in order to
totally account for our moral intuition against extinction.
The conclusion will have to be that anthropocentric instrumentalism is in favour of
preservation in many cases – probably in more cases than is generally acknowledged – but
that it is not enough to give a complete account of the intuition that it is prima facie morally
wrong to contribute to the extinction of species. We therefore have to continue our search for
such an account.
138
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