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Chapter 16
Contested Frameworks
in Environmental Ethics
Clare Palmer
Abstract This chapter provides an overview of some key, and contrasting, ideas in
environmental ethics for those unfamiliar with the field. It outlines the ways
in which environmental ethicists have defended different positions concerning
what matters ethically, from those that focus on human beings (including issues of
environmental justice and justice between generations) to those who argue that nonhuman animals, living organisms, ecosystems and species have some kind of moral
status. The chapter also considers different theoretical approaches to environmental
ethics in terms of consequentialist, broadly deontological and virtue theories.
Finally, three different interpretations of moral pluralism in environmental ethics
are introduced: pluralism about values, pluralism about theories, and a pragmatic,
methodological pluralism.
Keywords Environmental ethics • Moral considerability • Moral pluralism •
Anthropocentrism • Ethical holism
16.1
Introduction
Environmental ethics emerged as an academic field during the 1970s, and grew
rapidly. Today, courses in environmental ethics are taught in universities across
the world; textbooks, journals and monographs in the field have proliferated.1
As the field has grown, it has diversified, now supporting a wide range of contrasting
views concerning what should be understood as the fundamental problems of
environmental ethics, how to approach and prioritize such problems and, more
1
For a longer, though still brief history, see http://www.cep.unt.edu/novice.html
C. Palmer (*)
Department of Philosophy, Texas A&M University,
4237 TAMU, College Station, TX 77843-4237, USA
e-mail: cpalmer@philosophy.tamu.edu
R. Rozzi et al. (eds.), Linking Ecology and Ethics for a Changing World: Values,
191
Philosophy,
and: Action,
Ecology (EBSCOhost)
and Ethics 1,
DOI 10.1007/978-94-007-7470-4_16,
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C. Palmer
specifically, what has value, why it has value, and in what kind of ethical theory
such values should be embedded.
Attempting to give an overview of such a contested field in a short paper is
difficult; so this paper is necessarily limited. I will outline three kinds of divisions
in broadly “Anglo-American” approaches to environmental ethics. This means there
will inevitably be important omissions. I won’t discuss environmental philosophy
more generally construed (including approaches drawn from Continental or Latin
American philosophical traditions, Deep Ecology, Ecofeminism and Social
Ecology2) and I won’t focus on particular issues (such as ecological restoration3,
climate change or wilderness4) that have been highly significant in the development
of the field. Instead, I’ll concentrate on underlying theoretical frameworks, which
may help to locate different approaches to such issues (while noting that some
environmental ethicists argue that this theoretical approach is the wrong starting
place). Some of the conflicting approaches to environmental ethics I’ll discuss are
derived from differences found more generally within ethics. Others relate to the
specifically environmental concerns of the field.
The conflicts I’ll explore here offer different answers to the following three
questions:
1. Are human individuals the only things that matter morally? If not, what else is of
moral relevance, and why?
2. What approach to ethical theory should environmental ethicists adopt?
3. Should environmental ethicists be ethical monists or pluralists?
Commitment to a particular answer to question 1 doesn’t require any particular
answer to question 2. So, there can be disagreements along two dimensions;
approaches to environmental ethics can diverge both about what matters morally
and about ethical theory. However, answers to the first two questions may lead to a
particular answer to question 3.
16.2
16.2.1
Conflicting Approaches: Moral Status
Key Terminology
The first key term here is “moral status” or, alternatively, “moral considerability”. Most simply, “moral status” is usually used to refer to something or being
2
For more information about approaches drawn from Continental philosophy, see Brown and
Toadvine (2003); Foltz and Frodeman (2004), and from Latin American philosophy see Rozzi
(2012). For Deep Ecology see Brennan and Witoszek (1999); for Social Ecology, see Bookchin
(1995), Light (1998); for ecofeminism, see Plumwood (1994), Warren (1997).
3
But see Elliot (1997), Throop (2000) on ecological restoration.
4
See Callicott and Nelson (1998) on wilderness.
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Contested Frameworks in Environmental Ethics
193
that we should take directly into account in our decision-making; “we may not
treat it just in any way we please” (Warren 2000, p. 3). Even if some thing, or
being, with moral status is useful to us, it is not just useful; it is also something
for which we should be directly concerned. On most accounts something that
possesses moral status has interests, a good of its own. Some further distinctions
are useful here:
(a) To say that something has moral status/considerability is not necessarily to say
that it has rights. Rights possession is usually construed much more narrowly
(see Goodpaster 1978). Most environmental ethicists, if they accept rights arguments at all, confine rights to a small group of beings, either just human beings,
or more broadly, humans and mammals.
(b) To say that some thing or being has moral status says nothing about comparative value. Moral status/moral considerability should be understood as threshold terms. If we say a being has moral status, all we’re saying is that it counts
for something. The term “moral significance” is usually reserved for comparative judgments of value; we could say that two beings (say a bear and a
beetle) are morally considerable, but that the bear has more moral significance than the beetle.
(c) Moral status/considerability is often closely related to the term intrinsic
value. But the term “intrinsic value” is used in many different ways, too
complex to discuss here.5 However, two points to note: In environmental
ethics, “intrinsic value” is commonly used to mean non-instrumental value;
the “value of things as ends in themselves regardless of whether they are
also useful as means to other ends” (Brennan and Lo 2008). Second, on
some accounts, to say that some being, thing, or state has intrinsic value just
is to say that it is morally considerable. But, alternatively, it is also possible
to argue that some thing (such as a painting) can be valued intrinsically,
without having to maintain that it has moral status (see Cahen (1988) for
further discussion of this distinction).
16.2.2
Understandings of Moral Status
There are two independent fault lines within environmental ethics with respect to
moral status. These are (a) an anthropocentric/non-anthropocentric fault line, and
(b) an individualist/holistic fault line. There is also substantial disagreement over
(c) what capacities or qualities give some thing or being moral status, and add to its
moral significance.
5
So, for instance, on some accounts intrinsic value is taken to mean the value some thing or state
has in itself, independently of its relations; while alternatively, on other accounts, intrinsic value is
the value an object, state or fact has an end, rather than as a means. See O’Neill (1992); McShane
(2007) and Zimmerman (2010) for further discussion.
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16.2.3
C. Palmer
Anthropocentrism/Non-anthropocentrism
Anthropocentrism just means “human-centered,” and as such can refer very broadly
to worldviews and attitudes, as well as to values. Here, however, I’m concerned with
a narrower sense of anthropocentrism, anthropocentrism about moral status. This
can take different forms. On one view, only humans have moral status; the natural
world matters only inasmuch as it is important or useful for human beings. An alternative form of anthropocentrism maintains that humans have higher, or much higher,
moral significance than anything else in the natural world, but that at least some
nonhuman beings or things have some degree of moral significance. These are
sometimes called “strong” and “weak” anthropocentric views, although these terms
can be used in different ways.6 A non-anthropocentric view maintains that at least
some nonhuman beings or things have high moral significance; perhaps as high, or
even higher, than human beings. Non-anthropocentric views can also take many
forms, however, as I’ll explain below.
Very significant environmental ethics problems exist, even if one is strongly or
weakly anthropocentric about moral status. For even if only humans are thought to
have moral status, there are still substantial inter-human environmental justice
issues with relation to the environment. In the case of human contemporaries, some
individuals and groups (both within nations, and internationally) may bear a disproportionate burden of environmental harms, be unfairly deprived of access to key
environmental resources, and be excluded from decision-making procedures about
the environments in which they live. And justice issues between generations can be
even more starkly drawn. Future generations are vulnerable to the actions of present
generations; they can play no direct part in decision-making about actions that will
affect them; and environmental costs, burdens and deprivations can be pushed forward to future people, while present people gain the benefits.
The term “anthropocentric” in environmental ethics has sometimes carried negative valence (in a similar way to the negative valence popularly carried by the term
“egocentrism”). However, some environmental ethicists have strongly defended
anthropocentric approaches to ethics, especially for strategic reasons. In public policy
debates, it is maintained, anthropocentric arguments for environmental protection are
much more likely to be persuasive than non-anthropocentric ones (de-Shalit 2000;
Light 2002). Norton (1993, 1997) argues that if anthropocentrism is sufficiently
reflective – that is, if it takes future people, ecosystem services, and other cultural
and aesthetic interests seriously enough – there will, in practice, be convergence
between anthropocentric and non-anthropocentric environmental policy. So, there is
no need to argue for more contentious, non-anthropocentric ethical views. However,
these views are highly contested in environmental ethics, as I’ll point out later.
6
“Strong” and “weak” anthropocentrism can be used in different ways. For instance, these terms
may describe the origin of values, or the objects of values; here I’m referring to the objects of
values. Bryan Norton takes “strong anthropocentrism” to mean instrumentally valuing nature for
consumptive uses and “weak anthropocentrism” to mean “widely” instrumentally valuing nature
for nonconsumptive “higher uses” (e.g. as an aesthetic and spiritual resource).
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Contested Frameworks in Environmental Ethics
16.2.4
195
Individualistic/Holistic
A second distinct fault line concerns whether only individuals can be thought to
have moral status. Actually, putting it this way begs a key question, since one problem here concerns what constitutes an “individual.” Traditionally, “individual” has
referred to individual human beings, animals and other living organisms. Many
views in environmental ethics maintain that only individuals of these kinds – some
or all organisms – can have moral status. Why? Most simply, because (on this view)
only living individuals can have a well-being, interests, can be harmed or benefited,
and/or have a good of their own. And it is only beings about which we can make
these kinds of claims that could have moral status. If something can’t be harmed or
benefited (it is argued) why should we take it directly into account morally?
However, this opens up two possible responses, both of which can be found
within environmental ethics. The first is to argue that some things in the natural
world generally thought of as groups, sets or collectives, have more cohesion than
these terms imply. This cohesion is such that they can be thought of as “quasiindividuals” that can be in some way harmed or benefited, and thus that they can,
like more traditional individuals, have moral status. The second response is to
maintain that groups such as communities should be valued, or can have moral status,
as a group, even though they lack individual-like qualities. Both these responses –
I’ll call them “holistic” – may conflict strongly with individualist, organism-focused
views. The conflict between these approaches has underpinned some of the most
enduring disputes in environmental ethics, particularly in the context of ecosystem
management, hunting and culling, where the claims of particular individuals may
compete with the claims of “wholes” such as systems or species.
16.2.5
Differing Grounds for Moral Status
It is generally thought that individual adult humans are “paradigm cases” of moral
status. However, even in the human case, reasons for maintaining this differ. In
starkly simple terms, there are two important traditions here. One – a broadly
Kantian tradition – focuses on human rationality; the second on human sentience
(very roughly, the human capacity to feel and to experience). Most strong ethical
anthropocentrism works with the first tradition. Humans are autonomous, capable
of reasoning, in particular of reasoning about ethics; they can enter into agreements
with one another; they can reciprocate. Nothing else has such capacities; and these
are the capacities that underpin moral status. So, only humans have moral status.
Some worries about this view immediately arise. If this is the basis of moral
status, only some humans will have it. Infants, the senile, those in comas, those with
severe mental disabilities and fetuses are not capable of this kind of sophisticated
reasoning. So, they do not appear to have moral status. For some philosophers, this
implication alone (sometimes unhappily called the Argument from Marginal Cases)
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C. Palmer
is sufficient reason to reject the view. Others have attempted to extend arguments
about reason to include those who are partial reasoners, potential reasoners or past
reasoners; and yet others argue that it is enough for an individual to be “of the same
kind” as those that do reason, where “kind” is interpreted as “species” (Cohen
1986). However, these arguments are problematic, as has frequently been pointed
out (most comprehensively in Nobis 2004).
The second perspective grounds moral status not on individuals’ reason, but on
individuals’ sentience. As the utilitarian philosopher Jeremy Bentham (1989)
famously commented, “The question is not, Can they reason? nor, Can they talk?
but, Can they suffer?” But if suffering is what matters, many non-human animals
should also have moral status along with human beings. Although, of course, animal
suffering has been a long-standing issue of popular, philosophical, and theological
concern, it was the publication of Peter Singer’s Animal Liberation in 1975 that led
to the prominence of sentience-centered ethics. Singer argued that suffering matters
morally wherever it is found, and that every being that can suffer should be taken
equally into account in our moral decision-making. Although many disagreed with
Singer’s account of animals’ moral significance, the idea that if a being is sentient
then it should be understood to have moral status has been very widely accepted,
both inside and outside environmental ethics. This view forms a key individualist
position in environmental ethics.
Some environmental ethicists, however, argue that sentience-centered approaches
do not go far enough. Moral status is still limited to those beings that have an “experiential well-being”. But, such philosophers argue, we can make sense of the idea of
“well-being” without requiring that it be experienced. Failing to water a houseplant
is bad for the plant; it is contrary to the plant’s interests. On this basis, it is argued,
we should extend moral concern to plants; indeed, to all living things. On views of
this kind – biocentric ethical views – all living organisms have moral status (though
this should not be taken to mean that they all have high moral significance). Although
biocentric ethicists have made slightly different arguments for the moral status of all
living things, this approach to environmental ethics has been very significant (see
Taylor 1986; Agar 2001; Varner 1988; Attfield 1987).
These moves in environmental ethics are sometimes called ethical extensionism.
Ideas of moral status have been extended from humans, to individual sentient
animals, to all living organisms. However, this isn’t the only way in which extensionism in environmental ethics has moved. It has also extended holistically, outward
from human communities to include, for instance, ecosystems and species.
The most prominent kind of holism – ecocentric holism, or ecocentrism –
originates in the work of Aldo Leopold (1949). Leopold argues for a rather different
form of ethical extensionism: “The land ethic simply enlarges the boundaries of the
community to include soils, waters, plants and animals, or collectively, the land”
(Leopold 1968, p. 204). The starting point of Leopold’s ethical extension is not the
individual, but the community; and inanimate things (such as “waters”) have moral
relevance, since they form part of “the land.” The focus here is on whole ecological
communities or ecosystems, and on emergent properties they may possess. So
Leopold’s land ethic famously maintains that “A thing is right as long as it tends to
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Contested Frameworks in Environmental Ethics
197
preserve the integrity, stability, and beauty of the land community. It is wrong as it
tends otherwise” (Leopold 1968, p. 224). Integrity and stability are not properties
possessed by individual community members, but by the community as a whole.
In the past several decades, a number of environmental ethicists have attempted
to develop a systematic underpinning for ecocentric ethics (see, for example,
Callicott 1989; Rolston 1988; Johnson 1991). These accounts as to why ecological
communities or ecosystems should be valued as wholes or accorded moral status
differ considerably. Callicott (1989) argues – drawing on Hume and Darwin – that
just as we have emotional loyalties and moral responsibilities towards human
communities in which we are located, so too we should have such loyalties and
responsibilities to the ecological communities of which we are also members. The
argument proposed by Rolston (1988) focuses on ecosystems as wild processes that
create and nurture life; it would be peculiar, Rolston insists, to value the organisms,
the products of the system, without recognizing the value of the processes that
produced them. Johnson (1991) argues that ecosystems should be understood as
quasi-individuals with “interests,” interests that don’t necessarily coincide with the
interests of their members.
However, ecocentric views have run into many difficulties, including what kind
of thing an ecological community, or an ecosystem, might be thought to be. Are
ecosystems really distinct from what’s around them – do they have boundaries? Do
ecological communities form any kind of coherent whole, or are they aggregates of
individuals (and do different communities have different degrees of cohesion)?
Does it make sense to talk about “ecosystem” or “ecological community” health?
Do ecological communities reach a stable equilibrium, or are they in a constant state
of flux and disequilibrium? (see McShane 2004; Odenbaugh 2007; Pickett and
Ostfeld 1995). The more indistinct, incoherent, and rapidly changing ecosystems or
communities seem to be, the more difficult it becomes to maintain certain kinds of
ecocentric ethics, especially those that depend on the idea of ecological communities
or ecosystems as having a “good” or “interests” that can be “set back.”
Some environmental ethicists maintain that species have moral status, a view
that’s usually grafted onto the position taken by some philosophers of biology
that a species is not a class or set but rather a kind of concrete particular, an individual. For, it is argued, a species is connected not by relations of similarity common to the constituents of sets, but rather by causal and spatiotemporal
connections (see, for instance, Hull 1978; Crane 2004). These descriptive arguments about how best to conceive of species are used to base claims about species’ moral status. Johnson (2003, p. 478), for instance, argues that a species is a
living entity, an ongoing process that maintains near equilibrium with its environment. This kind of life process, he argues, has interests in “whatever contributes to its coherent and effective functioning as the particular ongoing life process
which it is.” Such species interests, Johnson (2003, p. 479) maintains, can be
distinguished from the sum of the interests of individuals of the species; something could be in the interests of a species that’s not in the interests of any individuals that are part of it. For this reason, Johnson argues, species’ interests are
of moral significance; other things being equal, we should protect and promote
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198
species’ interests. Of course, arguments of this kind are contentious; even if this
description of a species is accepted, the claims that species have interests, and
that those interests are of moral relevance, are troublesome to defend (see, for
instance, Sandler and Crane 2006).
I’ve identified two key fault lines here: between anthropocentric views and a
variety of non-anthropocentric views; and between individualistic/holistic views.
Commitments with respect to one don’t necessarily determine commitments with
respect to the other; individualistic views can be both anthropocentric and nonanthropocentric, as can holistic views.
16.3
Conflicting Approaches: Ethical Theory
I’ve focused so far on competing approaches to moral status. However, to be
action-guiding, ideas about moral status must be embedded within what’s called
an ethical theory. I’ll outline three differing ethical theories that have been important
in environmental ethics: consequentialism, deontology, and virtue ethics. I will
show how these link back to ideas about moral status, and indicate key conflicts
between them.7
16.3.1
Consequentialism
A consequentialist aims at bringing about best outcomes, most commonly by his or
her actions or practices. Standard forms of consequentialism are maximizing (we
should bring about the best expected outcomes possible), and require us to take the
whole outcome into account (including the outcomes of omitting to do things we
could have done).8 Given this framework, what we take “best outcomes” to be in
terms of what we think is good (or bad) is critical. This takes us back to moral status,
because the capacities that give moral status/significance are usually closely
connected to what we think is “good.” Here’s an example: Suppose we take a
sentience-centered position on moral status, so beings that can feel pleasure and
pain matter morally. Then we combine it with a consequentialist ethical theory. This
gives us the basic structure of what’s known as hedonistic utilitarianism; utilitarianism
is the best-known form of consequentialism. For a sentience-centered consequentialist, “pleasure” is the good (to be maximized) and “pain” is the bad (to be
7
I won’t discuss some theories important in ethics more generally (such as ethical egoism and
moral contractarianism) that have been less significant in environmental ethics.
8
This is, of course, oversimplified; there are forms of consequentialism that don’t focus on actions;
and there are satisficing, not maximizing consequentialisms; but these variations have not been
highly significant in environmental ethics.
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Contested Frameworks in Environmental Ethics
199
minimized). The aim of actions, then, will be to bring about the greatest amount of
expected pleasure, net of pain; this constitutes the “best outcome.”9 But consequentialism does not only apply where states of pleasure (pain) are the good (bad). Other
forms of utilitarianism emphasize preference satisfaction, where the good is satisfied preferences, and the bad frustrated preferences; for biocentric consequentialists
the good (to be maximized) is organismic flourishing, and the bad (to be minimized)
is setting back organismic flourishing (see Attfield 1987). Holistic views may also
be consequentialist; one might aim at maximizing ecosystemic health, or species
flourishing. Consequentialists have very diverse ideas of what constitutes the good.
What makes them consequentialist is the forward-looking aim at best outcomes.
16.3.2
Deontology
Consequentialist ethical theories contrast with what are (roughly) known as deontological theories. Consequentialists aim to bring about the best states of affairs in the
world – states such as pleasure and flourishing. But one worry about consequentialism is that to get to the best states of affairs, particular individuals may need to be
sacrificed. So, for instance, if inflicting suffering on one would relieve the suffering
of many, a consequentialist may require that the one suffers. Second, the maximizing nature of consequentialism seems relentless; all our actions seem to be swept up
into the moral sphere.10
Deontologists, therefore, argue that consequentialism is unjust (in requiring
the sacrifice of some individuals to create best states of affairs overall) and overdemanding (in requiring a constant aim at best consequences). In particular,
deontological theorists argue that there are some things that should never be
permitted, even if doing them does bring about the best consequences; there
should be restrictions on maximizing the good. Most deontological theorists also
argue that one is not always required to maximize the good; for instance, it is at
least sometimes permissible to pursue one’s own private interests (such as reading
a good book in the armchair) even though better consequences might be brought
about if one did something else.
Deontological theories in environmental ethics emphasize rules, principles,
duties, rights or some combination of these. The basic idea is that we should adopt
certain principles or respect certain rights, rather than that we are required always
to maximize the good. Although the distinction between deontological and consequentialist approaches occurs in all kinds of environmental ethics, the most prominent battle has been between utilitarian and rights theorists concerning animals.
A hedonistic utilitarian, of the kind mentioned above, could support animal
9
There are other forms of consequentialism that work with intended or actual, not expected
outcomes.
10
Some sophisticated forms of consequentialism – in particular various kinds of indirect consequentialism avoid these difficulties; I’m just sketching relatively simple forms here.
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C. Palmer
experimentation in certain (rare) circumstances, where the expected outcome of
some particular painful experiments would be to reduce overall suffering.
However, deontological rights theorists – such as Tom Regan (1984) – reject this
view. For Regan, if a being has moral status (he has a rather sophisticated account
of moral status) then it has rights. And one should not infringe on a being’s rights,
even if doing so would bring about best outcomes overall. On this view, practices
such as eating meat and animal experimentation should be abolished, because
they infringe on animals’ rights. A consequentialist approach, in contrast, while
finding many instances of both meat eating and animal experimentation morally
objectionable (because they don’t maximize pleasure/minimize pain overall)
would not support absolute abolition of such practices.
Deontological approaches are not confined to sentience-centered views. Paul
Taylor, a prominent biocentric ethicist, argues that we have certain deontological
duties to respect all wild individual living organisms. Deontological views could
also be holistic; for instance, we might have duties towards species, such that we
should never render a species extinct, even if doing so would promote the flourishing of five other species.
16.3.3
Virtue Ethics
Rather than being concerned primarily with actions and practices (as consequentialists are) or with rights, principles or rules (as deontological theorists are),
virtue theorists are primarily interested in character. Virtue ethics asks how we
should live, what sort of people we should be, what it is to be a “good person” and
how to make ourselves into such a person. Virtues (vices) are understood as dispositions or traits of character that it is desirable (undesirable) to have. In an
environmental context then, what’s at stake is not so much norms of action as
norms of character (Sandler and Cafaro 2005, p. 1); that is, virtue ethics concerns
our attitudes and dispositions with respect to the environment. Obviously, this
yields a very different moral theoretical approach to one that’s either outcomeoriented (as is consequentialism) or rule-following (as deontology). For this reason,
environmental virtue ethics is less obviously concerned with environmental policy
and legislation. But still, virtue ethicists can argue, character is the right place for
our primary ethical focus. Our environmental actions flow from our characters. If
we are greedy, selfish, short-sighted, complacent, ungrateful, and callous in our
attitudes and dispositions towards people, animals and the non-human world, then
it is not surprising that environmental crises result. As Sandler and Cafaro (2005,
p. 3) argue: “How one interacts with the environment is largely determined by
one’s disposition towards it, and it seems to many that the enabling cause of reckless environmental exploitation is the attitude that nature is a boundless resource
for satisfying human wants and needs.” Virtue ethics, then, is an ethical approach
that claims to get at the heart of environmental problems by examining the kinds
of people we are.
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201
A related theoretical approach, sometimes called the “ethics of care,” has also
played an important role in debates in environmental ethics, in particular in feminist
approaches to animal ethics (see Donovan and Adams 2007). Care ethics, as its
name suggests, maintains that caring relationships, usually with particular others,
lie at the heart of ethics; we should attend to individual people (or other organisms)
rather than primarily to consequences or principles. Virtue and care ethics share
certain features in common; indeed, it has been argued that care ethics should be
understood as a form of virtue ethics (where “being caring” is taken to be a critical
virtue). Both approaches maintain that human emotions should play a significant
part in ethical decisions; we are not only rational beings. Developing and expressing
the moral emotions such as compassion, sympathy and empathy should form part of
a rich and flourishing moral life. This emphasis on the place of human emotion in
ethical decisions, as well as the focus on character, makes for a contrast between
deontological and consequentialist approaches on the one hand, and care and virtue
ethics on the other.
16.4
Conflicting Approaches: Monism and Pluralism
I have so far outlined different views on moral status and ethical theory. But
suppose one finds several different accounts of moral significance plausible,
though they appear to be in conflict? Or suppose one finds attractive (or repellent!)
elements of different ethical theories? This raises questions about whether one
should be a monist or a pluralist in environmental ethics. In fact, the terms “monist”
and “pluralist” can be understood in various different ways; what I say here will
inevitably simplify these debates, which can be framed rather differently (see
Brennan 1992; Wenz 1993). With this caveat in mind, I will discuss three kinds of
pluralism: pluralism about values, pluralism about ethical theory, and what has
been called methodological pluralism.
16.4.1
Value Pluralism
Environmental ethicists have argued for the moral importance of many different
capacities, (such as sentience), states (such as pleasure), and qualities (such as naturalness). And I have had no room to discuss other ethical considerations that are
generally thought to be important – such as justice, equality, and liberty. But there may
be occasions where these values might conflict; or at least, respecting one might
mean denying another.
One way of thinking about this is to maintain that only one value is fundamentally
morally important. The others are either not values at all, or are not independently
valuable; they should be “cashed out” in terms of one “master” value. This is the
route taken by value monists. Value pluralists, on the other hand, accept that there is
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more than one (and perhaps many) moral values and considerations. These values
cannot all be translated into one “master value currency,” but neither should they be
silenced or ignored. Values really are plural, and potentially in conflict with each
other. The central problem for value monists, then, is to identify this “master”
fundamental value, explain why it is so significant, and how to translate other values
into its terms. The central problem for value pluralists is to provide a way of prioritizing or balancing competing values when they come into conflict.
Hedonistic utilitarianism is a key example of value monism. The master, fundamental value/disvalue is pleasure/pain; all other values and considerations can be
translated into the master value (so, justice is important inasmuch as it maximizes
pleasure and minimizes pain; rationality is important inasmuch as it intensifies or
lessens pains and pleasures). Sometimes this is called “strong value commensurability:” since there is a master value, all values are commensurable. However, many
environmental ethicists reject strong value commensurability. They argue that
values are fundamentally plural. For instance, both “being sentient” and “being
rational” are morally important; rationality is not only important because it can
enhance or reduce pleasure and pain. Hence there can be a genuine conflict between
these values. How does one deal with such conflicts?
On the view that’s sometimes called “weak value commensurability,” one can
consistently rank values. For instance, one can say that both sentience and rationality
are important, but that when they conflict, one (say, rationality) always has priority
over the other (sentience). That is, some kind of lexical priority rule can be adopted,
where one value (or an amount of the value) is always given priority over another
value (or amount of the value). Other value pluralists reject such regular ranking
patterns, arguing for different forms of value incommensurability. On these views,
value-rankings either vary by context (so in some cases one might prioritize one
value, in other cases a different value) or on some occasions at least, values just cannot be ranked at all; rational choices can’t be made between them. The philosopher
Isaiah Berlin famously called these “tragic choices.”
Value pluralism of one kind or another has the significant advantage, as Carter
(2005, p. 76) puts it, of “recognizing that each value continually exercises its pull.”
This position has been widely adopted in environmental ethics. There are individualist value pluralists who maintain that, for instance, being alive, being sentient, being
rationally autonomous are all different but important values, and have come up with
various frameworks for decision-making in situations of conflict. Equally, there are
holistic value pluralists, who maintain, for instance, both that “species protection”
and “naturalness” are values, and have systems for adjudicating between them when
species protection requires human intervention. And finally there are ethicists – such
as Johnson (1991) – who accept both individualist and holistic values, and find ways
of balancing, prioritizing or trading off these values when they conflict.11
11
This kind of value pluralism is of particular significance to consequentialists, who aim at bringing about the best outcomes. There is a similar kind of pluralism of principles, more common
among deontologists, that I do not have space to discuss here.
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16.4.2
203
Pluralism About Ethical Theory
A second debate concerns pluralism in ethical theory. In environmental ethics,
this debate largely arose in response to a claim by Stone (1988) that a moral pluralist
might be a utilitarian in public life but adopt a non-consequentialist ethical theory
in his or her private life. This form of moral pluralism seems to endorse the view
that we could theory-switch in different contexts. The majority of environmental
ethicists have been skeptical about this kind of moral pluralism. Attfield (2003, p. 90)
argues that theory-switching is incoherent, since the same action could thereby
appear to be both right and wrong simultaneously. Other worries concern the
integrity of moral agents. Callicott (1990) goes so far as to maintain that theoryswitching is open to (perhaps unconscious) manipulation – if a theory comes up
with an answer you don’t like, you appear to be permitted to switch to the theory
that gives the answer you actually want. There seems to be a deeper worry about
the consistency involved in attempting to be pluralist about ethical theory than
value. While there could be pluralism in ethical theory that reduces worries about
theory-switching, this would require rules about which theory should be consistently applied in which circumstances, or a lexical ordering rule about which
theory has priority when there are conflicts. Of course, frequently ethical theories
coincide in the actions they recommend; in these cases we could describe the
action as multi-determined.
This isn’t to say, though, that aspects of different moral theories can’t be combined into one coherent theory. There are advocates of what’s called “virtue consequentialism,” where a commitment to virtues is adopted as an indirect way of
bringing about best consequences (Jamieson 2007). Other hybrid theories also
exist, for instance Scheffler’s (1984) hybrid consequentialism. However, hybrid
theories are not strictly pluralist, since they create a unified theory composed from
elements of several independent theories. True pluralism in ethical theory, especially
where this involves theory-switching, is not very common.
16.4.3
Methodological Pluralism
“Methodological pluralism” is particularly relevant to environmental policy and
practice, and is connected to a school in environmental ethics called “environmental pragmatism” (see Light 1996, 2002). Methodological pluralism maintains that,
in terms of making environmental policies and interacting with environmental professionals, we should be tolerant of a wide range of different values and theories.
People can and do value nature in many different ways; rather than seeking to
persuade people to value the “right things,” we should work with the values people
actually have. So, for instance, Andrew Light (2002) a prominent methodological
pluralist, argues that if we look at the actual environmental values people hold, we
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204
see that people are generally very concerned about the environment their children
and future people will live in, but have few non-anthropocentric concerns. Rather
than trying to persuade people to become non-anthropocentric (i.e., to have the
“right” values) it is better – methodologically – to work with their existing values
to achieve environmental protection. This may also involve adopting strategic
anthropocentrism.
Of course, this methodologically pluralistic argument is easier to maintain where
diverse theories and values coincide in practice. As we’ve seen, Norton argues that
if anthropocentrism is sufficiently “reflective,” then divergent positions about
anthropocentric/non-anthropocentric value will so converge. Yet, as critics have
pointed out, there will surely be some cases where anthropocentric and nonanthropocentric values come apart. Norton (1993) denies this, maintaining that most
such human/nature conflicts are set-ups. And, of course, if individuals’ values are
not sufficiently “reflective”, it still looks as though there is a need to persuade
people to embrace more wide-ranging human-centered values, which at least
constrains the breadth of methodological pluralism that is under discussion. More
fundamental objections to methodological pluralism have also been made. If
anthropocentrism is a morally objectionable attitude (like sexism, for instance) it
can be argued that there is good reason to try to change the attitude, even if agreement can be reached on particular actions and practices without doing so. So,
although in practice most environmental policy does spring from a coalition of different value positions, there is disagreement among environmental ethicists as to
whether methodological pluralism should be adopted as a governing approach in
practical and policy contexts.
16.5
Conclusion
I began with three questions:
1. Are human individuals the only things that matter morally? If not, what else is of
moral relevance, and why?
2. What approach to ethical theory should environmental ethicists adopt?
3. Should environmental ethicists be ethical monists or pluralists?
As we have seen, there are conflicting approaches – and answers – to all three
questions. The territory of environmental ethics still is highly contested. This raises
a series of further questions. Should such diversity about moral status, values,
and theory be welcomed? Is more agreement about these questions possible, or
desirable? What are the implications of such deep fissures in environmental ethics
for environmental professionals, in particular for those engaged in environmental
conservation and restoration? Is the best we can hope for, on the ground, some form
of methodological pluralism?
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