Self-Correcting
Mechanisms and Dynamic Equilibrium
Stream corridors
exhibit a dynamic form of stability, known as dynamic equilibrium. Dynamic
equilibrium refers to the ability of system to persist within a range
of conditions (Federal Interagency Stream Restoration Work Group, 1998).
Maintaining this balance requires the presence of a series of self-correcting
mechanisms in the ecosystem. A disturbance to the stream ecosystem triggers
a response from these self-correcting mechanisms allowing maintenance
of the dynamic equilibrium.
Disturbances
result from both naturally occurring and human-induced events. Climatic
factors often play a role in naturally occurring disturbances and generally
involve below- or above-normal precipitation and concomitant runoff. Human-induced
disturbances often relate to changing land use patterns associated with
development activities within the watershed.
Disturbances
and the river system’s response to them occur at both temporal and spatial
scales, and a crude correlation can be drawn between them (Figure 1.9).
At the stream reach scale, for example, cumulative effects of wave action
from recreational boating over decades can be a major cause of bank erosion
along popular reaches. At the river basin scale, the composite effect
of major land-use changes in a watershed over a century, such as clearing
of hardwood forests and substitution of agricultural crop production,
may cause substantial chronic disturbances with long-term consequences
for the river system.
Figure
1.9 Temporal and Spatial Factors Influence Ecosystem Response
While many
stream ecosystems can tolerate fairly significant disturbances and maintain
dynamic equilibrium, threshold levels exist. When thresholds are exceeded,
the system becomes unstable. As the ecosystem adjusts over time, it moves
towards a new dynamic equilibrium that may be different than the one that
existed prior to the disturbance. In some instances, disturbances alter
the system to such an extent that it cannot recover unless the cause of
the disturbance is removed or actions are taken to restore stream functions.
At present, the relationships between threshold levels and the associated
range of conditions required for ecosystem stability are not well understood.
Research efforts in this area currently focus on identifying and quantifying
threshold levels.
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