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Linking Restoration and Ecological Succession (Springer ... - Inecol

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Biomass/Height etc.<br />

Max<br />

Recovery<br />

Impact<br />

Chapter 4 Retrogressive <strong>Succession</strong> <strong>and</strong> <strong>Restoration</strong> on Old L<strong>and</strong>scapes 71<br />

Impact<br />

Progressive Regressive<br />

approx. 140K years<br />

Partial recovery<br />

or collapse<br />

Figure 4.1 In young l<strong>and</strong>scapes after an impact the vegetation tends to return to the<br />

original state, whereas on old l<strong>and</strong>scapes vegetation will only partially recover or collapse<br />

(modified from Walker et al. 2001).<br />

escaped the direct effects of the Pleistocene glaciations that destroyed the Tertiary<br />

l<strong>and</strong>scapes <strong>and</strong> weathering mantles over much of the northern hemisphere.<br />

In old l<strong>and</strong>scapes, the residual products of weathering have formed thick soil<br />

mantles generally lacking weatherable minerals <strong>and</strong> have low concentrations<br />

of available plant nutrients. The extensive areas of lateritic soils in Australia,<br />

<strong>and</strong> in the tropics generally are examples of this (Sanchez 1976). As secondary<br />

minerals form in the weathering zone, there is an initial increase in available<br />

plant nutrients, but this decreases rapidly as the supply of weatherable minerals<br />

is depleted (Stark 1978, Walker <strong>and</strong> Syers 1976). With progressive weathering,<br />

plant nutrient availability decreases, <strong>and</strong> plant species trend toward those<br />

with more efficient mechanisms of nutrient capture <strong>and</strong> storage. Aboveground<br />

biomass is reduced, the proportion of belowground biomass increases <strong>and</strong> physiological<br />

<strong>and</strong> morphological adaptations are common (Lamont 1981, Walker et<br />

al. 1987, Pate 1994). The system may be stable in its undisturbed state, but is<br />

particularly vulnerable to disturbance as shown by a lesser ability to recycle nutrients<br />

or retain water. An example is the failure of tropical rainforests on yellow<br />

podzolic or lateritic soils to regenerate after clearing, burning, <strong>and</strong> agricultural<br />

use (Sanchez 1976). The implication is that halting an inevitable decline after<br />

disturbance may be impossible in old l<strong>and</strong>scapes, <strong>and</strong> at best one has to settle<br />

for a stable system state different from the original as a restoration end-point.<br />

In summary, natural retrogressive succession has the following attributes:<br />

1. A decline in ecosystem productivity <strong>and</strong> complexity occurs over millennia<br />

due to processes associated with soil weathering, especially a decline in<br />

nutrient availability <strong>and</strong> declines in a range of soil properties that affect the<br />

water cycle.<br />

2. The intact ecosystems of old l<strong>and</strong>scapes are usually stable as the result of<br />

the gradual development of adaptive plant physiological <strong>and</strong> morphological<br />

traits.<br />

3. Man-induced disturbances (clearing, burning, grazing, <strong>and</strong> farming) push<br />

old systems quickly into further decline (new system states) <strong>and</strong> key system<br />

functions may be lost permanently.<br />

4. <strong>Restoration</strong> expectations (end-points) in old l<strong>and</strong>scapes are different from<br />

young l<strong>and</strong>scapes <strong>and</strong> a stable system state different from the original state<br />

may be the best outcome.

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