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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50 David A. Wardle <strong>and</strong> Duane A. Peltzer<br />
Role of herbivory<br />
Compensatory plant<br />
growth responses<br />
high % NPP consumed<br />
most OM returned to soil<br />
as fecal material<br />
Plant traits<br />
high growth rate<br />
short-lived tissue<br />
Decomposer subsystem<br />
high litter quality<br />
high rates decomposition<br />
<strong>and</strong> mineralization<br />
low rates of carbon<br />
sequestration in soil<br />
high shoot leaf area<br />
poorly defended leaves<br />
high leaf nutrient content<br />
EARLY SUCCESSIONAL<br />
ECOSYSTEMS<br />
High supply<br />
rates of<br />
plant<br />
available<br />
nutrients<br />
Retardation of<br />
succession<br />
(Foliar<br />
herbivores)<br />
HERBIVORY<br />
Acceleration of<br />
(Foliar <strong>and</strong> root<br />
herbivores)<br />
NUTRIENT REPLETE NUTRIENT-LIMITED<br />
<strong>Succession</strong><br />
succession<br />
Low supply<br />
rates of<br />
plant<br />
available<br />
nutrients<br />
Plant traits<br />
slow growth rate<br />
long-lived tissues<br />
low shoot leaf area<br />
well-defended leaves<br />
low leaf nutrient content<br />
Role of herbivory<br />
noncompensatory plant<br />
growth responses<br />
low % of NPP consumed<br />
most OM returned to soil<br />
as litter<br />
Decomposer subsystem<br />
low litter quality<br />
low rates of decomposition<br />
<strong>and</strong> mineralization<br />
high rates of carbon<br />
sequestration in soil<br />
LATE SUCCESSIONAL<br />
ECOSYSTEMS<br />
Figure 3.2 Mechanistic basis of how herbivores affect the decomposer subsystem at a plant community level,<br />
through altering successional trajectories. Reproduced from Bardgett <strong>and</strong> Wardle (2003) with permission from the<br />
<strong>Ecological</strong> Society of America.<br />
3.3 Browsing Mammals <strong>and</strong> New Zeal<strong>and</strong> Rainforests<br />
Foliar herbivory is an important driver of many ecosystems, <strong>and</strong> depending<br />
on the ecosystem considered, between 1 <strong>and</strong> 50% of NPP is consumed by<br />
herbivores (McNaughton et al. 1989). The intensity of herbivory is influenced by<br />
succession, with earlier successional systems often being subjected to a greater<br />
intensity of herbivory than later successional systems. Further, herbivores are<br />
important in influencing the direction <strong>and</strong> rate of vegetation succession; in fertile<br />
systems, herbivores retard succession while in infertile systems they promote<br />
succession (Bardgett <strong>and</strong> Wardle 2003) (Fig. 3.2).<br />
Aboveground herbivores influence not just plant growth <strong>and</strong> plant communities,<br />
but also indirectly affect decomposers <strong>and</strong> decomposer processes across a<br />
range of temporal <strong>and</strong> spatial scales (Bardgett et al. 1998, Wardle <strong>and</strong> Bardgett<br />
2004). In the short-term, herbivory can induce significant flow of C from the<br />
plant to the rhizosphere microflora, creating an aboveground feedback through<br />
enhancing N availability for the plants (Hamilton <strong>and</strong> Frank 2001). In the longer