Linking Restoration and Ecological Succession (Springer ... - Inecol
Linking Restoration and Ecological Succession (Springer ... - Inecol
Linking Restoration and Ecological Succession (Springer ... - Inecol
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176 Richard J. Hobbs et al.<br />
“State”<br />
Time<br />
Figure 8.2 Classical restoration trajectory (solid line) <strong>and</strong> increasingly wider targets<br />
(dashed <strong>and</strong> dotted lines) reflecting unpredictability or variability of endpoints <strong>and</strong> multiple<br />
potential outcomes for restoration. Options can exp<strong>and</strong> or contract through the<br />
restoration process.<br />
Precise restoration of original species assemblages <strong>and</strong>/or ecosystem functions<br />
is almost always unrealistic because of the dynamic nature of disturbance<br />
<strong>and</strong> changing reference systems. If we think in terms of restoration trajectories<br />
(Fig. 8.2), the general aim in restoration is to move the system from its current<br />
(degraded) state to a stable target state. Diagrams usually depict this with<br />
a single arrow joining the current <strong>and</strong> target states. However, it has to be acknowledged<br />
that there are numerous factors that affect the predicted direction<br />
<strong>and</strong> cohesiveness of the trajectory. These include factors that are beyond the<br />
control of project managers, such as prolonged drought, <strong>and</strong> practical issues<br />
that are part <strong>and</strong> parcel of fieldwork, including delays in supply or poor quality<br />
materials. Options may contract due to unexpected loss of species (e.g.,<br />
from surrounding habitat destruction, species extinction) or due to an inability<br />
of the soil <strong>and</strong> belowground biotic systems to respond (e.g., crossing thresholds<br />
for recovery for soil structure). Options may also increase if new species<br />
(e.g., weeds) colonize, l<strong>and</strong> use changes, or societal views change to be more<br />
accepting <strong>and</strong> even dem<strong>and</strong>ing of novel rather than original systems (Hobbs<br />
et al. 2006). <strong>Restoration</strong> trajectories will also undoubtedly be impacted by climate<br />
change but in an unknown way (Harris et al. 2006). Hence trajectories<br />
are likely to be more dynamic than usually depicted, <strong>and</strong> options may exp<strong>and</strong><br />
or contract along the way. Adaptive management strategies are the best way<br />
to deal with divergence from anticipated end-points. Although in many cases<br />
restoration trajectories are less predictable than we would like, we suggest that<br />
knowledge from succession theory can reduce the unpredictability. <strong>Restoration</strong><br />
needs to move toward an evidence-based paradigm <strong>and</strong> as pointed out earlier,<br />
evidence can come from many sources.<br />
The final stage of a restoration that aims for complete species replacement<br />
is rarely achieved (see Chapters 2, 5, <strong>and</strong> 6). First, broad scale disturbances