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

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Chapter 3 Aboveground–Belowground Linkages, Ecosystem Development, <strong>and</strong> Ecosystem <strong>Restoration</strong> 61<br />

restoration, <strong>and</strong> highlights the importance of considering the belowground subsystem<br />

in both short- <strong>and</strong> long-term processes. The examples we provide above<br />

for the interactions of herbivores, fire, <strong>and</strong> invasions in these processes each emphasizes<br />

the importance of a combined aboveground–belowground approach<br />

to underst<strong>and</strong>ing vegetation succession, the ecological role of disturbance, <strong>and</strong><br />

the restoration of ecological interactions <strong>and</strong> processes.<br />

Some aspects of these aboveground <strong>and</strong> belowground interactions are clearly<br />

predictable: aboveground communities shift through succession <strong>and</strong> ecosystem<br />

development, from relatively rapidly growing, nutrient dem<strong>and</strong>ing plant<br />

species to slower-growing, nutrient-conserving species. Parallel changes occur<br />

in the soil subsystem, with shifts from domination by the bacterial-based<br />

to the fungal-based energy channel, from arbuscular-mycorrhizal to ectomycorrhizal<br />

communities, <strong>and</strong> from r-selected to K -selected soil fauna. These<br />

corresponding shifts in aboveground <strong>and</strong> belowground communities influence<br />

the nature of feedbacks between them, <strong>and</strong> this in turn has important consequences<br />

for ecosystem processes such as nutrient <strong>and</strong> C fluxes, NPP, <strong>and</strong><br />

ecosystem C sequestration. However, at local scales, the outcome of many of<br />

these interactions is context-dependent <strong>and</strong> hence not easily predictable; therefore<br />

underst<strong>and</strong>ing these linkages may or may not be helpful for restoration<br />

efforts depending on whether the linkages of interest are predictable over temporal<br />

<strong>and</strong> spatial scales relevant for restoration. The challenge for future work<br />

is to underst<strong>and</strong> which aboveground–belowground linkages are important for<br />

restoration within a given system, <strong>and</strong> in particular, underst<strong>and</strong> how belowground<br />

processes both determine <strong>and</strong> respond to restoration treatments. Below<br />

we outline some of the key challenges <strong>and</strong> future research areas for developing<br />

closer links between aboveground–belowground interactions, succession, <strong>and</strong><br />

restoration.<br />

Belowground communities clearly play a pivotal role in successional processes,<br />

plant community composition, <strong>and</strong> ecosystem processes (as outlined<br />

in the sections above), but their role in restoration remains poorly underst<strong>and</strong>.<br />

A major issue that can be resolved in the short-term is determining whether<br />

restoration efforts that focus solely on the aboveground community have the<br />

desired effects on the belowground community. <strong>Restoration</strong> practitioners typically<br />

focus on the aboveground components because these are visible <strong>and</strong><br />

amenable to manipulation. For the immediate future, soil communities will not<br />

be widely manipulated or used to assess restoration success for the practical reason<br />

that underst<strong>and</strong>ing shifts in belowground communities is relatively difficult<br />

<strong>and</strong> requires quite specialized skills to identify or quantify soil biota. Clearly,<br />

research is needed to determine how closely restoration efforts aboveground<br />

are mirrored belowground; this can be accomplished in the first instance by<br />

the inclusion of soil biologists in monitoring restoration projects. Most restoration<br />

treatments involve either the addition of native species or the removal of<br />

nonnative species; these adaptive management experiments can be extremely<br />

informative if they include carefully designed controls (i.e., intact native systems<br />

<strong>and</strong> un-manipulated, invaded reference systems), <strong>and</strong> then compare both<br />

aboveground <strong>and</strong> belowground properties among these treatments. This approach<br />

can be used to resolve key questions such as whether removing a weed<br />

species from a system reverses the effects of that weed belowground, whether<br />

there are persistent effects on the soil biota or nutrient availability in the system,<br />

<strong>and</strong> whether these effects are minor compared to differences between intact

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