ECOLOGICAL MANAGEMENT
The enormous scale of the extinction
crisis we are now facing poses daunting challenges. The number of species
threatened with extinction is so vast that it is virtually impossible to
imagine that more than a few of the most important individual species will
receive detailed study. It would seem that our most realistic hope for
preventing extinction on a massive scale is to manage entire systems to
conserve their biodiversity. The idea is that we should manage an ecosystem and
its processes in a way that will protect its structure. Our hope is that by
doing so we will also protect the populations of most or all species that are
part of that ecosystem.
In the last ten or fifteen years
“ecological management” or “large-scale conservation” has become the mantra of
many conservation organizations, both public and private. In broad outline the
objectives of ecological management seem clear and unobjectionable:
To maintain hierarchical patterns of
biological diversity as well as the processes and functions supporting the
phenomena that spawned them. Grumbine (1994) suggests that ecological
management is based on three observations:
1. To
protect biological diversity the processes that produced it must be protected
as well.
2. Species
richness alone is not a good measure of management success.
3. Management
must be planned for the long-term, possibly even for the indefinite future,
i.e., ecological management is intended to result in both a sustainable system
and a set of sustainable management activities.
Groom et al. (2005) suggest a slightly
different definition, one that explicitly recognizes the role of social,
economic, and institutional factors in ecological management projects:
An approach to maintaining or restoring
the composition, structure, and function of natural and modified ecologicals
for the goal of long-term ecological and human sustainability. It is based on a
collaboratively developed vision of desired future conditions that integrates
ecological, socioeconomic, and institutional perspectives, applied within a
geographic framework defined primarily by natural ecological boundaries (Figure
5.2).
Before discussing concerns that have
been raised about ecological management, let’s outline the steps in the process
that might be followed in developing an ecological management plan. According
to Harwell (1997), the development of the ecological management plan falls
naturally into four distinct phases:
1.
Determining the current status and
threats,
2.
Identifying the biologically achievable
management goals,
3.
Characterizing societal factors that
influence the choice of management goals, and
4.
Establishing management goals.
CURRENT STATUS AND THREATS
Before you can manage a system you have
to know what its characteristics are. In the case of an ecosystem that means
knowing its current status and the threats it may be facing. That means doing
at least two things:
1. Determining
the boundaries of the ecosystem to be managed and the types of habitat within
it that are to be managed and
2. Developing
a conceptual model of human influences on the ecosystem.
The threats are manifold, and nearly
all are related to human pressures.
BIOLOGICALLY ACHIEVABLE MANAGEMENT GOALS
Once you’ve figured out what the system
is that you’re trying to protect and you’ve identified the threats to the
system, you have to figure out what endpoints are biologically achievable. To
identify what things are possible it is necessary to select appropriate
measures for the “health” of various ecological components.
An implicit part of defining biological
achievable management goals is that the goals are sustainable for the
indefinite future.
SOCIETAL FACTORS
Human and societal influences except to
the extent, pose a direct threat to the species. Conservation initiatives may
sometimes be needed at a very broad scale, and at that very broad scale humans
are almost always part of the system.
That
means if the system is to be managed sustainably, attention must be given not
only to the needs of non-human organisms in the system but to those of humans
as well.
There are three different ways in which
it is necessary to assess societal factors.
1.
The human activities that lead to
substantial influences on or domination of ecosystems must be identified and
understood.
2.
The legal, economic, institutional,
political, and other societal factors that affect the frequency and scale of
those activities must identified and understood.
3.
The values and preferences of relevant
interest groups with an influence on the ecosystem must be characterized.
The last of these items may be the most
difficult for many environmentalists to accept. The list of biologically
achievable management goals is likely to include a range of options from those
where large portions of the ecosystem are substantially free of human influence
to those where large portions of the ecosystem are human-dominated or
human-influenced.
ESTABLISHING MANAGEMENT GOALS
With all of that in place, all that is
necessary is to “establish ecological sustainability goals in terms of
ecological endpoints and human values.”
If you are a biologist participating in
such a process, your expertise will be particularly important in defining what
endpoints are achievable. While biological expertise is needed to define the
range of the possible, choosing among possible endpoints is a question of
values.
Biologists have no special competence
on this choosing among competing values. We can describe the consequences of
different choices, but we don’t necessarily have any special standing to choose
one set of consequences over another. In a discussion about choosing among
endpoints, what biologists can do is to make sure that everyone discusses only
scenarios that can be achieved and that everyone understands the tradeoffs
among them.
As Harwell et al. (1999) point out,
decisions about design and implementation of an ecological management program
lie along a continuum:
1. Societal
values will have a dominant role in determining the outcome of those that are
predominantly concerned with defining the management goals.
2. Scientific
expertise will have a dominant role in determining the outcome of those that
are predominantly concerned with measuring how the system responds.
3.
Societal values and scientific
expertise will have equal roles in determining the system endpoints that will
be measured to determine whether management goals are being achieved.
ADAPTIVE MANAGEMENT
Adaptive management
is simply the idea that management actions are like experiments. They are tests
of hypotheses about how the system works. So if we monitor the results of those
tests, we can confirm or reject our hypotheses and improve our understanding of
the system while we manage it. We do not have to wait until all of the answers
are in. We can gather some of them while we proceed.
A CRITIQUE OF ECOLOGICAL MANAGEMENT
Goldstein (1999) argues that the
ecological management not only often fails to honor those principles, but also
that it is largely an attempt to bypass the requirement for life history
information on all species of concern.
He
goes on to argue that this attempt is doomed to failure for three reasons:
1.
Measures of local species richness can
diminish the contribution of threatened species to priority setting.
2.
Good “indicator taxa” don’t exist,
i.e., it’s not possible accurately to predict community properties from the
presence or absence of certain taxa.
3.
Concepts like ecological integrity,
ecosystem function, ecosystem resilience, ecosystem health, and naturalness don’t
provide concrete guidelines for management.
His
objection boils down to this:
For management strategies and
techniques to be successful at preserving anything other than perceived
structures, functions, and processes of landscapes, they must be evaluated
against the performance of populations and metapopulations in those managed
landscapes, including but not limited to the most sensitive and threatened
species . . . ecological management will be successful only if ecosystem is
used in a sense that can be guaged with precision and if the criteria used
actually reflect the needs of natural entitites we wish to protect rather than
abstracted emergent properties, functions, and processes of groups of
organisms.
Comments
Post a Comment