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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

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