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Untitled Document
FINAL DRAFT
A Journey of Discovery
Buzz Holling
December 2006
It is now mid September 2006. I am writing in a sun-drenched room at our cottage
in Ontario, thinking of the unrolling events of the last few months. It is a
surprising time with some light events and some very dark ones.
For me, the light, bright events, come from the birth of twin grandsons, living
on Vancouver Island. They turn my mind from the present dark colors of international
and US politics and governance, and add balance in the promise youth opens for
the future. And, on the same positive note, I have also met a large group of
new and old friends, on two recent trips- one trip to South Africa and one to
Montreal, where we met bubbling communities of people, young and old, experimenting
in new options for interracial design and novel social and scientific experimentation.
The collapse of apartheid in South Africa has slowly opened huge potential and
hope. This is just the opposite of the public mood I see in the United States.
It stunned me to discover that major new centers, truly international in character,
have emerged for resilience studies and policies- for the world's coral reefs
in Australia, for climate change in the UK and for regional and global social
and ecological systems in Sweden. And all this is apparently influenced deeply
by the discoveries and experiments presented by my own work over the last decades.
All that says the world is exuberantly healthy and productive. But there are
other, very dark events.
In the United States, the mood and currents of thought and politics perceived
among good friends at our main home in the small fishing village of Cedar Key,
on the Gulf of Mexico is depressing. They are good friends, but now deeply pessimistic
ones. The political situation in the United States is quite simply ugly. It
is a time when the power of the state has achieved a rigidity unseen since the
triumphs of the falling of the Berlin Wall. Politicians have reacted to extreme
disturbances, like the appalling terrorist attacks of 9/11, with a powerful
military response, a blind view of history and cultures, and a greedy desire
for narrow benefit. Global economic expansion and dependence on peaking oil
supplies, particularly in the Middle East, lock geopolitics into a self-destructive
state, from which transformation is extraordinarily difficult.
It is the classically destructive phase of the mature part of an adaptive cycle.
It is also potentially creative, because opportunities for innovative experiments
and novel enterprises start to open at such times. It is a time of potentially
creative destruction. And a recent mid term election in the United States in
November 2006 at least hints at a shift into a renewal that requires deep changes
nationally and internationally. Democracy is indeed a huge invention that stimulates
assessment of a society and institutions whose leaders have become rigid and
myopic. Democracy, at times, can trigger its renewal.
That is what I want to end up discussing here. But I want to get to that point
by musing about the personal contributions I've made, my colleagues have made
and our colleagues in science have at times questioned, at times supported.
That is the true skepticism of science unfolding. At times it is turned over
by truly novel discoveries- a kind of Kuhnian revolution of thought and approach.
I think that transformation has happened, and I will describe my personal journey
in science that, with other such journeys, contributed to the transformation.
Introduction
In May 2003, three graduate students from a mid-west university in the US,
discovered that three of my papers were among the 13 most cited papers/books
by authors in the journal Ecosystems 1998-2000. They asked me to comment on
the papers- their origin, relevance and directions the field of ecosystem ecology
might be headed.
Holling, C.S. 1973. Resilience and stability of ecological systems. Ann. Rev.
of Ecol. and Syst. 4: 1-23.
Holling, C.S. 1986. The resilience of terrestrial ecosystems; local surprise
and global change. In: W.C. Clark and R.E. Munn (eds.). Sustainable Development
of the Biosphere. Cambridge University Press, Cambridge, U.K. Chap. 10: 292-317.
Holling, C.S. 1992. Cross-scale morphology, geometry and dynamics of ecosystems.
Ecological Monographs. 62(4):447-502.
Each of those papers was a synthesis paper about ecosystems and their components
that was the culmination of several years of earlier work. And, in fact, there
were two additional synthesis papers, one of which preceded these three, but
with a focus on behavioral ecology, not ecosystems. And one of which followed
them, and was the first step in integrating ecological and social systems, again
not just ecosystems. Overall, the five papers represent a progression from experimental
work seeking for high certainty about simple systems, to systems work of high
uncertainty about complex systems. In the latter situation, the unknown is inevitable,
methods need to accept that reality and the rules for simplifying are not traditional
ones. In a way, the work progressed from a focus on understanding more and more
about less and less, to learning less and less about more and more!
The earliest paper was:
Holling, C.S. 1965. The functional response of predators to prey density and
its role in mimicry and population regulation. Mem. Ent. Soc. Can. 45: 1-60
It has been heavily referenced over the 41 years since it was published.
The other is much more recent:
Holling, C.S. , Lance H. Gunderson and Garry D. Peterson. 2002. Sustainability
and Panarchies. In: Gunderson, Lance H. and C.S. Holling (eds), 2002. Panarchy:
Understanding Transformations in Human and Ecological Systems. Island Press.
Chapter 3, 63-102.
This last paper presents all I think I have learned over the years about the
structure, function and history of ecosystems, social systems and the way they
survive, evolve and succeed or fail. I have no idea how well that paper will
affect the community of science or practice, but I am very happy with its content,
although not with its style of writing.
I am writing now to give a personal view of what I believe I have discovered
- my personal, explorers' guide of intellectual journeys that truly excited
me when, as it seemed to me, wondrous new lands periodically suddenly emerged
that no one had seen or remarked on before. For scientists, those are the times
when a tsunami wave of excitement triggers a passion for discovery.
How it began
Let me start with the origins of the first paper the students discovered, that
on Resilience. Since that paper really opened my eyes to the ecosystem scale,
I'll then spend a bit more time referring to it, and how it originated.
That paper came from a series of earlier experimental studies and papers analyzing
a particular process, predation. The goal was to see how far one could go by
being precise, realistic, general and integrative. These are goals that normally
are dealt with independently in at least partial isolation from each other in
order to achieve useful and useable simplification. (The key, classic references
are Holling, C.S. 1965. The functional response of predators to prey density
and its role in mimicry and population regulation. Mem. Ent. Soc. Can. 45: 1-60
and Holling, C.S. 1966. The functional response of invertebrate predators to
prey density. Mem. Ent. Soc. Can. 48: 1-86).
Those studies did well, and eventually led to a way to classify categories
of predation into four types of functional response (how much they eat) and
three types of numerical responses (how many there are). The categories and
resulting simplified models seemed to apply to everything from bacteria foraging
for food to submarines hunting ships! But none of that was ecosystem research.
It was all traditionally experimental and analytical; but at least it was synthetic,
non-linear and had great generality.
The key conclusion relevant for ecosystem science, was that it was possible
to develop small suites of well tested realistic models and define a small number
of general classes of responses for key population processes. The marvelous
dean of ecology at that time, Bob Macarthur, wrote me at the time of the publication
of the first Functional Response paper, arguing the work was too detailed and
complex to be very useful for theory in ecology. That is true in a narrow sense,
but he did not know that the paper was a planned step in a process that finally
did yield less complex equations, but ones more complex than was traditional
for the theory of the time. The "somewhat more complex", however,
led to a world of differences in the behavior of systems, because of the non-linearities
in the processes. And, most important, the equations representing the various
classes of processes, were sufficiently realistic, something I thought then,
and now know, was a central need for further development of theory for ecosystems.
That was the first hint of the "Rule of Hand" - not too simple, not
too complex- that was highlighted in the conclusions to the book Panarchy (Gunderson
and Holling, 2002). That is, all that is needed is a handful of key variables.
The classic "disc equation experiments" and paper launched the whole
sequence that led, finally, to simpler mathematical representations that captured
the essential reality that I thought was needed (Holling, 1959).
The same simple equation and experiments also became the foundation for the
development of optimal foraging theory, when Eric Charnov joined my laboratory
as a visiting student at the University of British Columbia. He accepted the
basic construct of the disc equation, that the time available for a predator
was divided into time spent in various categories of search, prey handling and
digestive pauses. And I gave him the wonderful data I had collected from experiments
with praying mantids, that he then used to show that optimality emerged in prey
choices by predators. I never went in that direction myself, but many others
have, and so a well tested theory of optimal foraging developed, launched from
the infamous disc experiments and equation.
My interests were more focused on describing and integrating the components
of behavior to add generality. That is what ended up in the Functional Response
papers, where the effects of hunger, learning and avoidance were shown experimentally
in a way that permitted expansion of the disc equation. Truly the work began
to be applicable to predation by insects, birds, mammals and fish. As an example,
one of my students even enjoyed himself in eastern Africa observing the distances
of stalk and attack of lions attacking gazelles and wildebeests, He was in one
vehicle filming the action as his wife did the same in a protective cage, some
distance away. Binocular perception allows calculation of distances between
predator and prey! It was a fine piece of work with as much a consequence for
understanding the co-evolution of attack and escape strategies as for behavior.
And there were a number of other such generalizing examples and tests.
It ended up being truly general, leading, ultimately, to the four basic types
of functional responses and equations for them. It also became the point in
the early 1960's, where I discovered the tremendous value of simulation models.
The expression of the experimental results into a generalized model of predation,
showed me how significant the new programming languages and computers were in
explosively expanding our power of understanding. They made it more natural
to represent non-linearities of various kinds. And projections of the results
were dramatically easier.
But it became completely clear that some rigor had to be applied - don't try
everything; just expand slowly on the basis of what we know. Then slowly add
the partially known and unknown guesses, testing against the reality of whole
systems behavior along the way. The work therefore avoided the tendencies that
exploded in the International Biology Program of the time, where often more
and more was expressed about more and more, in a way that smothered the work
in over-complexity. A simple thread of modeling and investigation became much
more powerful. Again, that was the discovery of the "Rule of Hand"-complex
enough, but not too complex.
At this point two paths opened. One was marvelous work with various beasts
to expand the behavioral discoveries. That was done with Larry Dill, a well
known behavioral ecologist, who, in my view, is simply the best whole animal
experimentalist in the world! He has developed elegant and insightful explorations
of salmon and killer whales on the west coast, of archer fish and their aerial
prey, of dolphins, dugongs and sharks in Shark Bay, Australia. We developed
experiments with small fish reacting to barracuda and model predators, and to
mock situations with an endless patterned belt that showed that their movement,
once they were located on the edge of their "zone of fear", was dictated
by the appearance of a corner- no corner on a belt, therefore no movement. Of
mahimahi attacking prey, and of schooling and solitary fish in a Hawaiian oceanarium
disturbing and reacting to potential predators. And on to ducks off the coast
of British Columbia reacting to boats; and of school children in a field reacting
to a runner as an aircraft filmed the interactions. And to flocking ibis in
Florida sketching V's, W'S and Y's in the air as they flowed, almost with magic,
from foraging grounds to nesting islands. Beautiful situations - not work at
all, but full of the joys of understanding the patterns of life.
All showed the foundations we earlier had discovered. That is, there were general
laws, expressible in general equations of fairly simple form that explained
all the variants we observed and filmed, each as a limiting condition of a general
equation. Moreover, we discovered that the rules were not precise and accurate,
but rather were simple and just sufficient. In short, they were "quick
and dirty" and were adaptive. Adaptive options are retained to correct
a response if a mistake is made.
So we concluded that nature does not optimize for the "best" based
on assumptions of complete knowledge, in the traditions of simple decision theory.
Nor are its responses efficient. The actions were based on just sufficient information
to assure adequately the object's fundamental nature and provide options for
reversal- likely small enough to attack safely vs. likely big enough to avoid.
That is all strictly the consequence of evolved responses. It has the same features
that later characterized the tactics and goals of Adaptive Ecosystem Management
that Carl Walters and I later developed for designing policies and responses
for managing resources in ecosystems. The mistakes become possibilities for
learning, not routes to failure. Larry and I began to write a book, but that
book, partially done, still waits completion.
That was because another path began to swallow my attention. This path moved
me into very new territory, that was truly ecological. By that I mean I began
to recognize that the way organisms are affected by their environment is only
half the story. The way that effect feeds back to affect the environment itself
is the other half. That interaction creates new structures, some at one scale,
some at others, and those create new options for evolutionary change. At what
scales was that significant? Were all species interacting in important ways?
Or were there a few that developed relations among themselves and their environment
that created new entities upon which evolution and human management acted? All
that was launched by my discovery, or invention of resilience.
Resilience
My bridge to studying ecosystems started once I shifted to combine the functional
and numerical response equations with others concerning other processes in order
to make a population model, of interacting predator and prey. That is when,
suddenly and unexpectedly, multi-stable states appeared. Lovely indeed. Great
fun and a big surprise to me! A new landscape for exploration opened.
Non-linear forms of the functional responses (e.g. the Type 3 S-shaped response)
and of reproduction responses (e.g. the Allee effect) interacted to create two
stable equilibria for interacting populations, with an enclosed stability domain
around one of them. It was the responses at low densities that were critical-
that is where vertebrate predators have yet to learn to locate the prey easily,
and where mates are too scarce to find each other easily. Once discovered, it
seemed obvious that conditions for multi-stable states were inevitable. And
that, being inevitable, there were huge consequences for theory and for practice.
Up to that time, a concentration on a single equilibrium and assumptions of
global stability had made ecology, as well as economics, focus on near equilibrium
behavior, and on fixed carrying capacity with a goal of minimizing variability.
Command and control was the policy for managing fish, fowl, trees, herds, and
freedom was unlimited to provide opportunity for people.
The multi-stable state reality, in contrast, opened an entirely different direction
that focused on behavior far from equilibrium and on stability boundaries. High
variability, not low variability, became an attribute necessary to maintain
existence and learning. Surprise and inherent unpredictability was the inevitable
consequence for ecological systems. Data and understanding at low densities,
rare because they are all the more difficult to obtain, were more important
than those at high-density. I used the word resilience to represent this latter
kind of stability
Hence the useful measure of resilience was the size of stability domains, or,
more meaningfully, the amount of disturbance a system can take before its controls
shift to another set of variables and relationships that dominate another stability
region. And the relevant focus is not on constancy but on variability. Not on
statistically easy collection and analysis of data but statistically difficult
and unfamiliar ones. That needs a different eye to see and a different theory
to perceive consequences.
About that time, I was invited to write a 1973 review article for the Annual
Review of Ecology and Systematics. I therefore decided to turn it into a review
of the two different ways of perceiving stability and in so doing highlight
the significance for theory and for practice. That required finding additional
rare field data in the literature that demonstrated flips of populations from
one level or state to another, as well as describing the recently discovered
known non-linearities in the processes that caused or inhibited the phenomenon.
That was a big job and I recall days when I thought it was all bunk, and days
when I believed it was all real. I finished the paper on a "good"
day, when all seemed pretty clear. By then I guess I was convinced. The causal,
process evidence was excellent, though the field evidence concerning population
flips, was only suggestive. Nevertheless the consequences for theory and management
were enormous. It implied that uncertainty was inevitable. And that ecosystems,
in an evolutionary time span, were momentary entities pausing in a flip to different
states. As I'll describe, it took about 30 years to confirm those conclusions
for others.
This paper began to influence fields outside population/community ecology a
bit - anthropology, political science, systems science first, then, later, ecosystem
science. It became the theoretical foundation for active adaptive ecosystem
management. But it was largely ignored or opposed by practitioners in the central
body of ecology. What followed was the typical and necessary skepticism released
by new ideas, that I'll describe briefly here because it is such a common foundation
for developing science.
One early ecological response to the paper was by Sousa and Connell (1985).
They asked the good question "was there empirical evidence for multi-stable
states?". They attempted to answer by analyzing published data on time
series of population changes of organisms to see if the variance suggested multi-stable
behavior. They found no such evidence. This so reinforced the dominant population
ecology single equilibrium paradigm, that the resilience concept was stopped
dead, in that area of science.
It seemed to be an example of evidence that refuted this new theory. But their
evidence was inappropriate and the theory was not! In fact, their evidence,
as is often the case, was really a model, incomplete because the collators unconsciously
used an inappropriate model for choosing data that were incomplete.
There are two problems with their analysis:
1) They did not ask any process question (are there common non-linear mechanisms
that can produce the behavior?). That is where the good new hard evidence that
I had discovered lay.
2) They rightly saw the need for long time series data on populations that
had high resolution. As population/community ecologists of tradition, however,
their view of time was a human view- decades were seen as being long. That view
is reinforced by a "quadrat" mentality. Not only small in time, but
small in spatial scale; and a theory limited to linear interactions between
individuals in single species populations or between two species populations,
all functioning at the same speed (e.g. predator/prey, competitors). It represents
the dangers caused by inferring that "microcosm" thought and experiments
have anything to contribute to the multiscale functioning of ecosystems. Steve
Carpenter has a perceptive critique of that tendency (Carpenter, 1996).
The multi-stable behavior can only be interpreted within the context of at
least three but, as suggested in the Panarchy paper/chapter, probably not more
than five variables. These variables need to differ qualitatively in speed from
each other. It is therefore inherently ecosystemic. It is the slow variables
that determine how many years of data are needed for their kind of test. None
of their examples had anywhere near the duration of temporal data needed.
As an example: The available 45 years of budworm population changes they analyzed
seemed long to Sousa and Connell and to all those conditioned by single variable
behavior and linear thinking of the times. But the relevant time scale for the
multi-equilibrium behavior of budworm is set by their hosts, the trees or the
slow variable. What is needed for their tests was yearly budworm data (the fast
variable) over several generations of trees (the slow variable), i.e. perhaps
one and a half centuries - not 45 years. The normal boom and bust cycle is 40-60
years
It has since taken 25 years of study of different ecosystems to develop data
for appropriate tests. Examples include those using paleo-ecological data covering
centuries at high resolution, the deep and shallow lake studies and experiments
of Carpenter (Carpenter 2000) in the United States and of Scheffer, in Europe
(Scheffer et al. 1993), the experimental manipulations of mammalian predator
and prey systems in Australia and Africa by Tony Sinclair (Sinclair et al. 1990),
and a variety of studies of specific ecosystems- sea urchin, coral reef etc.
Terry Hughes and his colleagues' works on coral reefs stand out as examples.
Carpenter's important summary paper makes the point (Carpenter, 2000).
Multi-stable states are real and of great importance, although they are difficult
to demonstrate. Surprise, uncertainty and unpredictability are the inevitable
result. Command and control management temporarily hides the costs, but the
ultimate cost of surprises produced by managing systems that ignore multi-stable
properties is too great. Active adaptive management as the only alternative
management response possible. Steve Carpenter and Buz (W.A.) Brock- a great
ecosystems scientist together with a wonderful "non-linear" economist-
show why in a classic paper where a minimal model of a watershed, farming styles,
of regional monitoring and regional decision regarding phosphate control, encounter
the surprises created as a consequence of a multi-stable state (Carpenter, Brock,
and Hanson, 1999).
Ecosystem Reality
The second paper the students identified was: Holling, C.S. 1986. The resilience
of terrestrial ecosystems; local surprise and global change. In: W.C. Clark
and R.E. Munn (eds.). Sustainable Development of the Biosphere. Cambridge University
Press, Cambridge, U.K. Chap. 10: 292-317.
For me, the 1973 "Resilience' paper launched the Adaptive Management work,
with Carl Walters at the University of British Columbia- a great friend and
a truly brilliant, maverick scientist who walks a non-traditional path that
creates new traditions. His work on adaptive management methods has been a classic
contribution to the field (Walters 1986). More recently he has advanced ecosystem
dynamics understanding using his creation of foraging arena theory which had
its beginnings in my own predation work (Walters and Martell 2004).
The resilience research led us to mobilize a series of studies of large scale
ecosystems subject to management- terrestrial, fresh water and marine. All this
was done with the key scientists and, in some cases, policy people who "owned
" the systems and the data. So the process encouraged two major advances.
One advance developed a sequence of workshop techniques so that we could work
with experts to develop alternative explanatory models and suggestive policies.
We learned an immense amount from the first experiment. That focused on the
beautiful Gulf Islands, an archipelago off the coast of Vancouver. We chose
to develop a recreational land simulation of recreational property. I knew little
about speculation, but we made up a marvelous scheme that used the predation
equations as the foundation- the land of various classes were the "prey",
speculators were the "predators" and a highest bidder auction cleared
the market each year. The equations were modifications of the general predation
equations. The predictions were astonishingly effective and persisted so for
at least a decade. As much as anything, it reinforced the earlier conclusion
that these equations were powerful and general. But the important conclusion
concerned the workshop process and the people.
The essence of those workshop methods were fun to present in a critical paper
where the workshop processes were described and where key personalities were
represented in delightful cartoons drawn by Roy Peterson, a cartoonist in Vancouver,
and methods were expressed as a game. (Holling, C.S. and A.D. Chambers. 1973
). It was fun to reveal the truth about characters like Snively Whiplash, The
Blunt Scot, The Utopians and The Peerless Leaders and such in this way, but
a reviewer in Ecology turned it down by saying "no one wants to know about
the games people in British Columbia play!" Bioscience reviewers were more
enlightened so I happily published there.
Those approaches helped shape the essential design and maintain the flexibility
of the big international Resilience Project that I began about two decades later.
It produces a turbulent, broad and delightful process of mutual discovery for
those who chose to be part of it.
I learned that the key design was to identify large, unattainable goals that
can be approached, but not achieved; ones that relate to fundamental values
of free speech, freedom, equity, tolerance and education. And then to add a
tough design for the first step, in a way that highlights or creates options
to design, later, a second step-and then a third and so on. We found that the
results were steps that rapidly covered more ground than could ever be designed
at the start. At the heart, that is adaptive design, where the unknown is great,
learning is continual and actions evolve.
The other advance provided a set of deep studies with modeling efforts, that
could be used in a comparative analysis of ecosystems behavior and ecosystems
management. Those examples included some 20-30 examples of crisis-ridden histories
of forests, fisheries, agriculture, human diseases and water resource development.
That is the part that particularly interested me.
One theoretical study suddenly helped significantly, when my eyes were opened
to the essential way to understand and display the (relatively simple) causes
of complex behavior (Ludwig, Jones and Holling, 1978). It was Don Ludwig and
Dixon Jones who taught me the way, using the essence of qualitative differential
equation theory.
It all started when Don took a half page I wrote explaining the essence of
the causes of forest changes mediated by spruce budworm in eastern Canada. He
then turned that into a coupled, three differential equation model that expressed
the interacting dynamics of budworm, foliage and trees. Meanwhile Dixon, with
help from Bill Clark and I, had been developing the big simulation model of
the system that emerged out of a series of workshops with the scientists and
policy people in New Brunswick. As part of our philosophy of economy in modeling,
I had been careful to leave out the effects of avian predation, relying on an
eventual check with measured behavior of the whole system in nature to tell
us what essentials we had missed. When we discovered that the behavior of the
simulation model simply did not match the field behavior, we used it and our
ecological knowledge to discover the "missing process", as a kind
of interactive, diagnostic procedure.
The missing piece turned out to be one with certain specific nonlinearities
at low densities of budworm and low volume of foliage. The only process we could
discover to fill the bill was predation by the 35 different species of insectivorous
birds. That linked us back to my earlier set of predation discoveries and we
added the effect using the predation equations and parameter data from the field.
The effect added progressively stronger predation as budworm densities rose
from low levels, and faded thereafter as budworm populations increased- that
is, a domed shaped response. Since the densities of birds were essentially constant,
that predation effect gradually weakened as the forest aged and the increasing
volume of foliage dispersed the searching by birds. The result was periodic
outbreak of the insect in older forests.
When these same bird predation effects were then added to Don's differential
equations, that too began to reflect what occurred in nature. So it was a beautiful
example of the power of linking three key methodological concepts; Don's qualitative
differential equation approaches, Dixon's scientifically infused simulation
modeling and my general process analysis modeling (Ludwig et al. 1978). The
advance led to a clear way to understand and compare the 20-30 examples of complex
ecosystem behavior in totally different kinds of situations (Holling, 1986).
The results appeared in the second paper discovered by the students i.e. in
Holling 1986. It is a chapter in the first (and maybe only) significant book
that deals with sustainability in a fundamental, interdisciplinary way. That
book was Bill Clark's inspiration and creation. My chapter for the first time
developed the theoretical discoveries emerging from the comparison of those
ecosystem studies. Some of the key features of ecosystems popped out: e.g. there
had to be at least three sets of variables, each operating at qualitatively
different speeds. There was an essential interaction across scales in space
and time covering at least three orders of magnitude. Non-linearities were essential.
Multi-stable states were inevitable. Surprise was the consequence.
And a puzzle emerged concerning what seemed to be an inevitable pathology of
resource management. In case after case, the same pattern appeared. An economic
or social problem was identified as being present or looming in the near future.
It was then narrowly defined and treated in a least cost manner for fast corrective
response. Then, unknown to all, the system evolved.
First, the problem seemed to disappear. Budworm outbreak populations became
controlled, forest fires were suppressed before spreading, water was stored
and irrigation became possible for agriculture, fisheries were augmented with
hatchery stocks, and so on. Second, industry expanded: pulp mills, tree harvesting,
agriculture, fisheries and with that, regional economic and social development.
Third, slow, unappreciated changes occurred that meant that resilience was
restricting, was declining. In most cases, the resilience declined because spatial
heterogeneity shifted to a more homogeneous state. A "spark", once
initiated, could therefore spread up scale. That is, conditions for outbreaks
in healthy forests spread, forest stands became more homogeneous in age and
became fuel rich, salt accumulated in soil as soil water levels rose, natural
fish stocks gradually went extinct leaving fisheries precariously dependent
on a few enhanced stocks. All became disastrous surprises waiting to happen.
Slowly decreasing resilience faced fast increasing economic and social dependencies
that made retreat and redesign extremely difficult. Working with nature was
rarely conceived. Instead, the response to correct the surprises, started or
continued a sequence that maintained the evolving system with more and more
costs. The classic example of that is the Everglades, which, after over 80 years
of four crises, now is launched into an eight billion dollar restoration, with
little active adaptive design. In contrast, the Columbia River system is deeply
involved in a policy that indeed does exploit natural forces in an interesting
adaptive scheme.
Other examples of "command and control", of passive and active adaptation
in regional social/ecological systems have been recently described in Olsson
et al 2006, leading to a set of considerations and actions we identified for
successful transformation toward adaptive governance,
This universal pattern represented one of the social traps later discovered
as a potential for panarchies. Subsequent avoidance of the trap can occur through
learning and actions to enhance resilience by reintroducing spatial heterogeneity
at appropriate scales. But often the remedial responses simply continued and
extended the process, protected by gradually increasing investments of money
to monitor, subsidize and control.
And I used the paper to present the first big theoretical synthesis. That was
the place where the "Adaptive Cycle" was first described and presented.
That is, there are four components of change in ecosystems, the traditionally
known and slowly evolving exploitation and conservation phases and the newer,
fast, unpredictable creative destruction and renewal phases. The first two are
when capital and skills are slowly accumulated, but resilience is typically
gradually lost. The last two are when unpredictability explodes, capital is
freed for other roles and novelty can become implanted. Moreover, those same
four components seemed to provide a general metaphor for all systems, and examples
were discussed from economics, technology, institutions and psychology. In fact,
I discovered that the creative destruction phase had already been posited decades
earlier by an economist, Schumpeter, for international businesses. Maybe economists
were not all so narrow!
From Ecosystems and Economics to Social Systems
That was the foundation for another series of studies that finally led to an
effort to collaborate with economists, ecologists, social scientists and mathematicians
to develop an integrative theory and examples of systems change and evolution.
The rationale was that the theories developed in each of those disciplines were
not wrong, just incomplete in different ways. The results and the integration
was presented in the "Panarchy " book of the Resilience Project (Gunderson
and Holling 2002). I tried to summarize my present understanding of complex
adaptive systems in the first three chapters, and in the conclusions in Chapter
15. Perhaps those chapters, and the book, will eventually have the citations
and influence of the three papers that were highlighted by the student's discovery
of key Ecosystem references.
Writing the third, key chapter of theoretical synthesis, (Holling et al. 2002)
was like a "mind dump"! I was happy with the content I wrote, but
the style is very condensed, very dense. Some sentences could have been expanded
to a few pages, some short paragraphs to a full chapter. But space was limiting.
As modest help, I also wrote an essential condensation of the book in Holling,
2001. And a more lightly written summary that expanded the work to its possible
relevance to the big social and political changes that were set in motion after
the terrorist attacks on September 11, 2001 (Holling 2004). I suggested it was
the time for small scale abundant experiments in living, and working. It is
a time when individuals have the greatest chances for influence, as resisting
institutions weaken and fail. Do not develop an overall plan for those experiments,
but set a tactical goal, which, in this case is novelty, safety and low cost.
The invention of the internet offers explosive opportunity. Some fail, some
succeed and that can provide seeds for subsequent healthy re-creation. That
is a way for the trap, now global, to be transformed into something more positive
for the future of people. There are ways out!
But maybe that alone is too naïve and hopeful. Consider the present moment.
I wrote the above paper one and a half years after 9/11. Now it has been five
years. What has been unrolling is the same pathology as described earlier for
the resource management pathologies. So far, the responses to terrorism have
been largely quick and expensive military fixes and security checks, followed
by quick successes. But the result has led political leaders to ignore the slowly
enrolling causes, and long-term failure.
Therefore, in addition to a plethora of experiments, now it is clear we also
need to attend the slow variables as well. We need responses to the slow, deep
changes that have caused the explosion. It is not just evil loose in the world.
There is humiliation, inequality and ignorance, combined with an exaggerated
fixation on a particular extreme identity found in the fundamentalism of the
religions of Abraham- of Christians, Muslims and Jews. That is a slow process
to create; a slow process to redress. And all is made more rigid by the dependence
of developed countries and of powerful ones on the oil of the Middle East. People
seem locked into their personal, fear-ridden regimes that are self re-enforcing,
creating differences between them, not bridging them: a deep, deep trap. Panarchy
perhaps helps in providing a theory and contexts.
The essence of our conclusions to the Panarchy book occurred to me on a plane
as I flew to a meeting with officers of a foundation that was new to me. I had
to summarize, succinctly, the whole resilience project for them, and this became
the way to do exactly that. There were, initially 12 conclusions- my 12 Commandments
from the Resilience Mountain! But I do like those conclusions. They appear in
Chapter 15 of the Panarchy book.
A broad, flexible and openly managed MacArthur Foundation grant made integrative
work possible for that project. A marvelous group of people became the heart
of the panarchy component - Buz Brock, Steve Carpenter, Carl Folke, Lance Gunderson,
Don Ludwig, Lin Ostrom, Garry Peterson, Martin Scheffer, Brian Walker and Frances
Westley. This is a mix that is strongly ecosystemic but also has powerful economic,
social and mathematical science expertise.
One workshop was held in Zimbabwe at a moment in the nation's history where
experiments were being tried and successfully implemented that shifted from
disastrous drought-sensitive cattle ranching to larger spatial scale cooperative
wildlife management and tourism. Ranchers learned to remove the barriers in
their minds and the fences on their land. They learned to abandon the ideas
of the past because there was literally no alternative- loans and insurance
were impossible to get and savings had disappeared.
During that period, the government watched and security agents stalked. Ultimately
the larger scale of federal government action destroyed the imaginative regional
experiments on recovery. And now the country erodes and slowly collapses. It
is truly destruction, without much sign, yet, of recovering creative destruction.
In that workshop, the economists proposed a specific route to theory expansion
that seemed to me to be too limiting, too much a useful stretch for economics,
but insufficient for our larger theme. So I encouraged two projects to emerge.
One, (the economists') was called the theory project. It faced the difficulties
presented by non-linearities in their models- an important step in itself. The
second (the ecosystem/social) was therefore named the ante-theory project (or
to some, caught by the humor of the situation, the "anti"- theory
project). We could have attempted a synthesis at that time. But spawning two
separate activities seemed to have a greater potential for discovery. That happened,
but it was with something of a sacrifice in quickly joining ecology and economics.
That still requires interesting further steps in order to achieve a deep and
useful synthesis that might join ecosystem science, non-linear economics and
social science.
That is all part of the penalty and opportunity in cross-disciplinary investigation
among brilliant, accommodating but stubborn participants. In such cases, the
best for the moment often is not to solve the problem, but just separate, encourage
two streams, and continue to see what develops. I think we are still in that
slow, but healthy process.
I got involved on the Science Boards of the Beijer Institute and Santa Fe Institute
and a bit in Beijer's biodiversity project run by the economist Charles Perrings.
Later I launched my own "Resilience Project", with Karl-Goran Maler
and Carl Folke at Beijer that led in five years to well over 100 papers written
by a wide disciplinary range of participants, that were published in specialist
and interdisciplinary journals. We guessed that over 300 scholars became part
of the sequence of workshops
In addition, a core part of the project was the design and preparation of four
books. One was the integrative Panarchy book (Gunderson and Holling, 2001) that
was meant to show what we developed to test and integrate the separate theories
and knowledge in ecosystem science, economics and aspects of the social sciences..
The other books were designed to address separately the ecosystemic, social
and economic dimensions of resilience. The ecosystem book focused on multi-stable
states in large scale ecosystems (Gunderson and Pritchard, 2002). The social
one was a lovely book on governance of and institutions for social-ecological
systems (Berkes, Colding and Folke, 2003). The economic one concerned non-linear
economics focused on renewable resource ecosystems (Dasgupta, P. and K.-G. Maler
2003).
Younger colleagues are now becoming the "engines" and spirit that
are now taking over and driving the intellectual advances. I think in particular
of Marty Andries, Graham Cumming, Line Gordon, Marco Janssen, Ann Kinzig, Jon
Norberg, Per Olsson, and Garry Peterson. I have learned from each of them directly,
and perhaps helped them, as well as from a bunch of others who are working closely
with other folks who helped lead the Panarchy project.
Resilience and multi-stable states now seem to be pervading notable parts of
ecosystem science and related social sciences, and even emerging in policy.
Both features are affecting international policy of some nations. And I note
in a bibliographic survey by Marco Janssen, that the original 1973 resilience
paper has been a central reference that links vulnerability and resilience research.
That is indeed pleasing since it took such a long time to happen. And it was
delightful to have a major review paper on resilience appear in the same Annual
Review series that my original paper did 31 years earlier (Folke et al 2004).
Carl Folke made that happen!
Finally, among the emerging influential pieces, Martin Scheffer has a major
book on the same subject in press with Princeton University. It was inspired
by his own remarkable experimental demonstrations of ecosystem flips in shallow
lake systems in Europe- the first experimental demonstrations of the reality
of multi-stable states in ecosystems.
And Thomas Homer-Dixon's recent book (2006) on political change in a turbulent
world, culminates with the significance of resilience and panarchy. He names
it "The Upside of Down: Catastrophe, Creativity and the Renewal of Civilization".
Now that is Panarchy! It is where crisis and opportunity merge in the affairs
of man. It is a book that expands the theoretical and applied relevance to the
profoundly important issues underlying international, religious and economic
extremism of our times.
And recently I read the new book by Frances Westley and colleagues (2006),
"Getting to Maybe"! The title is a take-off on the well known book
on negotiation techniques, "Getting To Yes". But the work avoids the
certainty of "Yes", replacing it with the realistic, evolving reality
of useful "Maybe's". She describes the paths achieved by ordinary
people designing mutual relationships and creating imaginative organizations
at local, and regional scales. She describes the way to move to engage real
politics. It is a deeply revealing book based in large measure on the complexity
theories of Panarchy, and the practical experience of Frances, a very wise person!
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