For the remainder of my talk I would like to
"deconstruct" spatial-dynamic processes by discussing features
that define these kinds of problems and ways that they might be modeled.
Then, I will illustrate using an example of bio-invasions. There are
several features of spatial-dynamic problems with which economists are
not particularly familiar. Figure 1 is an abstract representation that
captures the nature of these kinds of problems. The heart of the process
is the diffusion or dispersal process that governs the way something
spreads over space and creates patterns. Is movement random or
purposeful and behavioral? Are patterns self-generated, or are they also
influenced by directional forces such as winds and currents? Does the
front spread uniformly, or does it follow transportation corridors and
nodes of populations? What mechanism drives movement--animal transport,
human transport, spores, rhizomes, swimming, walking?
[FIGURE 1 OMITTED]
The other important aspect of spatial-dynamic problems concerns the
nature of space, and in particular boundaries, geometry, and
heterogeneity. What happens at boundaries, and how should we
characterize it? Mathematicians use terms such as absorbing or
reflecting boundaries or zero flux boundaries. When lemmings migrate to
breeding grounds near the sea at normal population levels, they reach
the barrier, mill around, and begin the process of breeding. But when
populations are high, they reach the sea and jump in, illustrating the
difference between reflecting and absorbing boundaries. Some boundaries
exist for biophysical reasons, such as the transition between land and
sea. Others exist because of habitat quality, and these boundaries may
be species specific. Yet other boundaries exist for geopolitical
reasons. For example, a forest pest spreading north from New England
into Canada might spread across the border but be treated as if it
stopped at the border when the U.S. Forest Service decides how much
control to initiate. Another important aspect is the geometry of space.
Is the relevant spatial unit like a featureless plain, or does it have
corridors or choke points that influence density and flux? Is space
homogeneous, or does it exhibit differentiated features that influence
either the diffusion pattern or damages? Soils often exhibit widely
varying character even within small scales, complicating the depiction
of the flows of water, oil, or contaminants. A landscape contains a
mosaic of human uses so that a bio-invasion might warrant more focused
control efforts at particular points that are located in advance of
certain areas with high potential damages.
Diffusion Processes
In light of the central role played by diffusion processes in
spatial-dynamic problems, it is useful to elaborate how they are
typically modeled (see Okubo and Levin 2002). What makes these kinds of
problems interesting is the fact that patterns are generated by
integrated dynamic and spatial forces. The simplest kind of
spatial-dynamics process can be represented by a diffusion equation
[partial derivative]C(X, t)/[partial derivative]t = [partial
derivative]/ [partial derivative]X [D [partial derivative]C(X,
t)/[partial derivative]X]
= D [[partial derivative].sup.2]C/[partial derivative][X.sup.2] (1)
This is a partial differential equation that expresses a process in
terms of derivatives in both time and space. This particular equation
represents the most basic type of diffusion, namely random diffusion.
Consider measuring the concentration C(X, t) of something like a group
of particles at a point on a line X at time t. Suppose that any particle
can move either right or left on the line with equal probability. Then,
it can be shown that the concentration of the particle will be governed
by Fick's Law, which states that the spatial diffusion at a point
will be proportional to the spatial gradient at that point (Murray
2002). Here, D is the diffusion coefficient, (assumed constant) which
indicates the rate of spatial flow. The essence of this idea is that
particles will flow on net from high to low density areas simply because
high-density areas have more particles that have a chance of ending up
in low-density areas than vice versa.
A partial differential equation like equation (1) is not something
with which economists are particularly familiar, and solving these kinds
of equations is difficult and somewhat of an art form in mathematics
(Holmes et al. 1994). As with ordinary differential equations that are
expressed only as a function of time, the explicit solution must
incorporate boundary conditions and initial conditions, in numbers equal
to the number of derivatives in the equation. Assume that this process
is started with a "point-source" injection of m particles at
the origin and at time zero, and that the one-dimensional line depicting
space is of infinite length in both directions away from zero. Then,
this particular equation can be explicitly solved to yield
C(X, t) = m/[square root of 4[pi]Dt] exp (-[X.sup.2]/4Dt). (2)
This describes how the concentration changes over space and time.
As figure 2 shows, the initial concentration spreads over space and
time. Recall that this process is completely driven by random movement.
At the origin initially, particles may move right or left with equal
probability. But because there is a point concentration, the gradient is
steep around the origin, and hence, more particles will move from the
origin to adjacent low-density points in space. This is Fick's Law
in action, causing the flow at a point to be proportional to the spatial
gradient at that point, and causing, at the global level, particles to
spread out over space.
[FIGURE 2 OMITTED]
Another useful representation of a diffusion process that fits many
examples found in resource problems is one described by
[partial derivative]C(X, t)/[partial derivative]t = D [[partial
derivative].sup.2]C/[partial derivative][X.sup.2] - V [partial
derivative]C/[partial derivative]X. (3)
This equation is simply the random diffusion representation
characterizing Fick's Law in equation (1), but modified to include
what is called an advection term. The advection term contains the
constant V that depicts drift of the process (Murray 2002). Advection
applies whenever a diffusion process is influenced by external forcing
factors such as wind or currents. If the advection process is strong
enough, the process depicted in figure 2 will not only dissipate the
initial infusion, but also shift the concentration over time as
suggested by the solution
C(X, t) = m/[square root of 4[pi]Dt] exp (-[(X - Vt).sup.2]/4Dt).
(4)
The solution to the diffusion with advection equation shows that
the maximum concentration shifts over time according to the term in the
exponent that acts as an axis shifter. (2)
A final representation of a diffusion process is the famous Fisher
reaction-diffusion equation
[partial derivative]P(X, t)/[partial derivative]t = D [[partial
derivative].sup.2]P/[partial derivative][X.sub.2] + [alpha][X.sup.2] +
[alpha]P(1 - P). (5)
This equation was examined by R.A. Fisher (1937) and it depicts a
process that is especially suitable to examining biological organisms.
It contains the random diffusion term but also a term that represents
logistic growth at a point in space. The logistic equation is a popular
and useful representation of density-dependent growth of populations. At
each point in space, then, a population P(X, t) will grow according to
two forces: (net) diffusion and local growth. The percentage rate of
local growth is highest when the population is smallest, and other
things equal the population approaches a carrying capacity level at each
point, where the carrying capacity is normalized at one in the above
equation.
As it turns out, it is impossible to derive a closed-form solution
similar to equations (2) and (4) for this equation. However, Fisher was
able to show that as time gets large, the solution exhibits what is
called a "traveling wave" property. A traveling wave can be
envisioned as similar to a tsunami, with the sea surface height behind
the wave at the same height as the crest. Kolmogorov, Petrovsky, and
Piscounov (1937) provided a conjecture about the velocity of the wave
front, namely that it is [square root of 4[alpha]D], or a value
associated with the product of the diffusion coefficient and the growth
rate of the logistic process at small population levels. This conjecture
has recently been proven correct (Uchiyama 1978). The reaction-diffusion
equation is a useful way of thinking about populations of plants, or
animals or even humans.
A Digression: The Genius of Harold Hotelling
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