Emergent trees in Colophospermum mopane woodland: influence of elephant density on persistence versus attrition

Author:

O’Connor Timothy1,Ferguson Angela2,Clegg Bruce W.3,Pallett Nita4,Midgley Jeremy J.2,Shimbani Julius5

Affiliation:

1. School of Animal, Plant and Environmental Sciences, University of the Witwatersrand, Johannesburg, Gauteng, South Africa

2. Department of Biological Sciences, University of Cape Town, Cape Town, Western Cape, South Africa

3. Department of Ecology, The Malilangwe Trust, Chiredzi, Chiredzi, Zimbabwe

4. Department of Botany, Rhodes University, Grahamstown, Eastern Cape, South Africa

5. Department of Ecology, Gonarezhou Conservation Trust, Chiredzi, Chiredzi, Zimbabwe

Abstract

Colophospermum mopane (mopane) forms mono-dominant woodlands covering extensive areas of southern Africa. Mopane provides a staple foodstuff for elephants, who hedge woodland by reducing trees to small trees or shrubs, leaving emergent trees which are too large to be pollarded. Emergent trees are important for supporting faunal biodiversity, but they can be killed by ringbarking. This study first examined the influence of elephant density on woodland transformation and the height distribution of canopy volume, and, second, whether canopy volume is maintained, and tall emergent trees too large to be broken can persist, under chronic elephant utilisation. Three regimes of 0.23, 0.59 and 2.75 elephants km−2 differed in vegetation structure and the height structure of trees. Areas under the highest elephant density supported the lowest total canopy volume owing to less canopy for plants >3 m in height, shorter trees, loss of most trees 6–10 m in height, but trees >10 m in height (>45 cm stem diameter) persisted. Under eight years of chronic utilisation by elephants, transformed mopane woodland maintained its plant density and canopy volume. Plant density was greatest for the 0–1 m height class, whereas the 3.1–6 m height class provided the bulk of canopy volume, and the 1.1–3 m height layer contained the most canopy volume. Emergent trees (>10 m in height) suffered a loss of 1.4% per annum as a result of debarking. Canopy dieback of emergent trees increased conspicuously when more than 50% of a stem was debarked, and such trees could be toppled by windthrow before being ringbarked. Thus relict emergent trees will slowly be eliminated but will not be replaced whilst smaller trees are being maintained in a pollarded state. Woodland transformation has not markedly reduced canopy volume available to elephants, but the slow attrition of emergent trees may affect supported biota, especially cavity-dependent vertebrate species, making use of these trees.

Funder

The Malilangwe Trust and the Gonarezhou Conservation Trust as part of their operational responsibilities

Angela Ferguson was funded by The Malilangwe Trust

Timothy O’Connor and Julius Shimbani were funded by the Gonarezhou Conservation Trust

Publisher

PeerJ

Reference78 articles.

1. Vegetation composition and elephant damage in the Sengwa Wildlife Research Area, Zimbabwe;Anderson;Journal of the South African Wildlife Management Association,1974

2. A model-framed evaluation of elephant effects on tree and fire dynamics in African savannas;Baxter;Ecological Applications,2005

3. Do elephants over-utilize mopane woodlands in northern Botswana?;Ben-Shahar;Journal of Tropical Ecology,1996

4. Controlling the false discovery rate: a practical and powerful approach to multiple testing;Benjamini;Journal of the Royal Statistical Society,1995

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