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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84 Joe Walker <strong>and</strong> Paul Reddell<br />
4.7 Retrogressive Rainforest <strong>Succession</strong>s: What Lessons<br />
for <strong>Restoration</strong>?<br />
Recognizing <strong>and</strong> underst<strong>and</strong>ing the widespread occurrence <strong>and</strong> nature of retrogressive<br />
succession on old soils in the humid tropical is fundamental to successfully<br />
<strong>and</strong> predictably restoring sustainable <strong>and</strong> functional forest cover to<br />
these areas.<br />
Activities to restore forest cover in the humid tropics are varied in their<br />
primary purpose. These can range from habitat replacement for rare species<br />
conservation, through to tree establishment for catchment protection or for<br />
plantation forestry. Each purpose is likely to have different objectives in relation<br />
to productivity, species composition, <strong>and</strong> ecosystem function, as well are<br />
require different implementation methods suited to the purpose, budget, <strong>and</strong><br />
local conditions. Where these activities are planned in old l<strong>and</strong>scapes, there<br />
are two broad approaches that can be applied to deal with the implications of<br />
retrogressive succession. These are:<br />
1. Alter the site conditions to ameliorate as far as possible the degraded state<br />
of the disturbed system <strong>and</strong> restore its pre-disturbance state.<br />
2. Recognize the new system state <strong>and</strong> set realistic endpoint, composition, <strong>and</strong><br />
productivity objectives consistent with this post-disturbance, retrogressed<br />
state.<br />
In some instances, especially where the main impacts of disturbance have<br />
been on site nutrient capital, it may be possible to use a well-planned fertilizer<br />
strategy to recapitalize limiting nutrients into the disturbed area <strong>and</strong> return it<br />
to a potential state <strong>and</strong> vegetation type closer to the original. However, this<br />
is often likely to be expensive <strong>and</strong> resource intensive. Interestingly, the most<br />
limiting nutrient after disturbance in many old l<strong>and</strong>scapes is calcium (Nykvist<br />
1998), which is accumulated in wood <strong>and</strong> bark <strong>and</strong> has an essential role in lignin<br />
formation. Treatments to ameliorate the effects of anthropogenically accelerated<br />
retrogression on hydrological characteristics may also be technically possible,<br />
especially to increase surface infiltration, however these are unlikely to be<br />
economically feasible on the broad scale.<br />
A less resource intensive approach that is likely to be more widely applicable<br />
is to recognize the biophysical constraints in the new post-disturbance, system<br />
state <strong>and</strong> develop endpoint objectives for composition, structure, productivity,<br />
<strong>and</strong>/or function based on this state. In many areas there may be l<strong>and</strong>scape “analogues”<br />
of the new state, where natural erosion <strong>and</strong> weathering have progressed<br />
more rapidly in particular l<strong>and</strong>scape locations <strong>and</strong> where existing plant communities<br />
can be used as models for species composition, structure, productivity,<br />
<strong>and</strong> function in the restoration process.<br />
4.8 What Do We Need to Know to Restore Old Disturbed L<strong>and</strong>scapes?<br />
Fundamental to the restoration of old disturbed l<strong>and</strong>scapes is recognition that:<br />
1. Retrogressive succession (in which total nutrient capital declines <strong>and</strong> hydrologic<br />
functioning changes as systems age) is a normal, long-term, natural<br />
process in old l<strong>and</strong>scapes.