Resilience in aquatic ecosystems - hysteresis, homeostasis, and ...
Resilience in aquatic ecosystems - hysteresis, homeostasis, and ...
Resilience in aquatic ecosystems - hysteresis, homeostasis, and ...
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16<br />
Reynolds/ Aquatic Ecosystem Health <strong>and</strong> Management 5 (2002) 3–17<br />
stress (Costanza <strong>and</strong> Mageau, 1999). Is this not just<br />
another way of ask<strong>in</strong>g how much structural <strong>and</strong><br />
resourc<strong>in</strong>g resilience the system has<br />
In the same way that systems emerge only through<br />
the aggregate of the behaviors of <strong>in</strong>dividual organisms<br />
of discrete populations, so system health should be<br />
manifest <strong>in</strong> the representation of key <strong>in</strong>dicator species<br />
<strong>and</strong> functional types. Thus, the <strong>in</strong>dices of ecosystem<br />
susta<strong>in</strong>ability promoted by Costanza <strong>and</strong> Mageau<br />
(1999) provide a ready framework of dimensions for<br />
dist<strong>in</strong>guish<strong>in</strong>g “good” from less desirable resilience.<br />
The l<strong>in</strong>es <strong>in</strong> Figure 5a represent the axes of a threedimensional<br />
plot, which share a common orig<strong>in</strong> at<br />
“0”. The z-dimension corresponds to specific process<strong>in</strong>g<br />
rate (represent<strong>in</strong>g gross primary production,<br />
forag<strong>in</strong>g rate, oxidative capacity); the y-dimension<br />
corresponds to structure (represent<strong>in</strong>g greater species<br />
richness <strong>and</strong> <strong>in</strong>terconnectance, more <strong>in</strong>formation<br />
organized <strong>in</strong> more biological complexity). These two<br />
axes def<strong>in</strong>e a (y-z) plane analogous to that used by<br />
Reynolds (1999) to dist<strong>in</strong>guish lakes on the basis of<br />
their metabolic properties. The third (x-) dimension<br />
corresponds to resilience as a separate measure of<br />
ecosystem behavior. It was not qualified by Costanza<br />
<strong>and</strong> Mageau; their <strong>in</strong>tention is the “structural” context<br />
but it holds for “resourc<strong>in</strong>g” too. In Figure 5b, two trajectories<br />
of ecosystem development are <strong>in</strong>serted <strong>in</strong>to<br />
the three-dimensional space created by the axis<br />
boundaries. For simplicity, they refer strictly to the<br />
early development <strong>and</strong> they do not show symptoms of<br />
disturbance. Both trajectories commence close to the<br />
orig<strong>in</strong> <strong>and</strong>, quite properly, demonstrate high biomass<br />
production. Both trajectories acquire resilience, also<br />
as anticipated but one of them also rises with respect<br />
to the y axis, as it ga<strong>in</strong>s more species, develops more<br />
network connectances <strong>and</strong> becomes more complex.<br />
This is the trajectory of Ulanowicz’ (1986) ascendancy<br />
<strong>and</strong> the resilience it builds is of the structural k<strong>in</strong>d.<br />
The other trajectory advances <strong>in</strong> productivity <strong>and</strong> process<strong>in</strong>g<br />
but the biomass <strong>in</strong>vestment is <strong>in</strong> a few specialist<br />
species, not <strong>in</strong> structural diversity. Managers<br />
will attest to its high resilience to therapy. The second<br />
trajectory acquires resourc<strong>in</strong>g resilience but high<br />
diversity is delayed. It is productive but has low <strong>in</strong>formation.<br />
Presently judgement resides with the view that<br />
high-diversity, low-productivity systems are healthier<br />
than low-diversity ones, though high productivity is a<br />
characteristic of early successions <strong>and</strong> it is what<br />
makes them so attractive for exploitation. For<br />
exploitation to be susta<strong>in</strong>able, systems must always be<br />
allowed the resilience to recover their ascendancy.<br />
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