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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.

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