New PDF release: Restoration Ecology: The New Frontier

By Jelte van Andel, James Aronson

Aimed toward Masters, and PhD scholars, academics, researchers and common source managers, this e-book explores the interface among recovery ecology and ecological recovery. Covers either the ecological options all in favour of recovery ecology and their sensible purposes. Written through a good workforce of ecologists from centres throughout Europe with a robust acceptance for recovery ecology. basically textbook round aimed particularly at complex undergraduate classes and postgraduate examine programmes.

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Additional info for Restoration Ecology: The New Frontier

Example text

If a reference system is being defined in terms of a ‘minimum structure’ (Pickett et al. 1989), it may mean either that the system can be confined to a few keystone species, the other species being more or less redundant, or that all the species in the community are to be included in the minimum structure in order to restore ecosystem functioning, with no species being redundant. These two contrasting points of view are still being discussed. Some authors favour the redundant-species hypothesis (only a few keystone species contribute to the functioning of the ecosystem), while others advocate the rivet hypothesis (all or almost all species essentially contributing to some ecosystem function); see for example Ehrlich and Ehrlich (1981, 1992), Lawton (1997), Prins and Olff (1998), van Andel (1998a), Waide et al.

Restoration objectives may or may not be met. After Hobbs and Norton (1996). Reproduced by permission of Blackwell Publishing. factor will not result in recovery of components of the original ecosystem that have been lost, because it has caused irreversible damage to the ecosystem involved, which may cause switches that are sometimes described in terms of ‘thresholds of irreversibility’ (Aronson et al. 1993b). ). Just rewetting the drained wetland will not lead to the return of the original species of that ecosystem.

The main information on keystone species has been derived from removal experiments (Paine 1980, Wardle et al. 1999), from exclosure experiments (Drent & Prins 1987, Drent & van der Wal 1999) and by estimating interaction strengths (Menge et al. 1994). Keystone species can be identified among plants, herbivores, predators, parasites and all other components of a biocoenosis. Tanner and Hughes (1994), working on coral reefs, showed that the importance of a species to the dynamics of an assemblage may be unrelated to its abundance at equilibrium.

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