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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Chapter 8 Integrating <strong>Restoration</strong> <strong>and</strong> <strong>Succession</strong> 169<br />
Table 8.1 Fields of study that strongly influence restoration, the primary impact each has on<br />
restoration, <strong>and</strong> potential problems conducting restoration without addressing the contributions from<br />
each field.<br />
Field Impact Problems if omitted<br />
<strong>Succession</strong> Predictions of temporal<br />
change <strong>and</strong> setting targets<br />
Wrong trajectory identified for biodiversity outcomes,<br />
wrong species mixtures, arrested trajectory, improper<br />
manipulation of soil nutrients, goals too narrow<br />
Assembly Filters Difficulty starting, mismatch of available propagules<br />
<strong>and</strong> the local environment<br />
L<strong>and</strong>scape Ecology Regional information Efforts limited to a single ecosystem or patch, poor<br />
exchange <strong>and</strong><br />
estimates of role of surrounding biota, applying a<br />
extrapolation<br />
“solution” to the wrong place<br />
Disturbance Ecology Initiation <strong>and</strong> boundaries Multiple restarts, loss of biomass <strong>and</strong> soil organic<br />
matter from improper species choices, inadequate<br />
site stabilization<br />
Climate Change Shifting reference systems Old communities no longer function as references or<br />
propagule sources, complications of novel<br />
communities<br />
Historical Ecology Legacies Wrong targets set, belowground influences ignored<br />
Environmental Ethics Aesthetics, goals relating to Societal values <strong>and</strong> expectations not achieved, visually<br />
<strong>and</strong> Philosophy naturalness <strong>and</strong> place unpleasant, ill-fitting or unachievable targets <strong>and</strong><br />
lack of project support or maintenance<br />
introduced in Chapter 1: why, where, what, how, <strong>and</strong> when? Explicitly, what are<br />
the perceived environmental or ecological issues leading to why restoration is<br />
being undertaken? What is the environmental domain <strong>and</strong> spatial extent where<br />
restoration will take place? How does the technical evaluation of what to expect<br />
help set end-points or targets following restoration? What evaluation of costs<br />
<strong>and</strong> benefits, operational control, resources, <strong>and</strong> knowledge is needed in order<br />
to decide how to implement the restoration program? Finally, when are physical<br />
manipulations of sites, vegetation establishment, ongoing reviews of progress,<br />
monitoring, <strong>and</strong> further interventions needed?<br />
8.2 Why Is <strong>Restoration</strong> Needed?<br />
It is often obvious why ecosystem, l<strong>and</strong>scape, <strong>and</strong> mine site restoration is<br />
needed, given the visual evidence from most parts of the world of increasing<br />
impacts by humans <strong>and</strong> natural events on l<strong>and</strong>scapes. These impacts have<br />
left large areas of l<strong>and</strong> <strong>and</strong> water bodies polluted, reduced biodiversity <strong>and</strong> have<br />
dramatically decreased the use that can be made of our natural resources. Nevertheless,<br />
it is important to decide if <strong>and</strong> why restoration is required in particular<br />
contexts, <strong>and</strong> there are a variety of different biological <strong>and</strong> practical reasons<br />
why restoration activities are carried out. As discussed by Hobbs <strong>and</strong> Norton<br />
(1996), restoration is fundamentally conducted to improve or sustain ecosystem<br />
goods <strong>and</strong> services, which may include aesthetic <strong>and</strong> societal preferences. To<br />
achieve this broad goal, restoration activities may be required to reverse severe,<br />
localized disturbances such as tailings from mine sites, to reinstate productive<br />
capacity in degraded agricultural systems, to maintain or return conservation<br />
values in protected areas, or to reinstate broader l<strong>and</strong>scape processes essential<br />
to the continuation of both rural <strong>and</strong> urban production <strong>and</strong> conservation enterprises.<br />
The scope for applying successional concepts to restoration activities<br />
was shown in the preceding chapters to vary greatly in each of these cases.