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Regeneration following clearing in a Jamaican montane forest: results of a ten-year study

Published online by Cambridge University Press:  10 July 2009

A. M. Sugden ,
E. V. J. Tanner  and
V. Kapos
A. M. Sugden
Affiliation:
Botany School, Downing Street, Cambridge, CB2 3EA, England
E. V. J. Tanner
Affiliation:
Botany School, Downing Street, Cambridge, CB2 3EA, England
V. Kapos
Affiliation:
Missouri Botanical Garden, 2345 Tower Grove Avenue, St Louis, Missouri 63110, USA
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Abstract

Succession was monitored over ten years in a 10×10m plot in forest with mor humus at 1550 m in the Blue Mountains of Jamaica, following the removal in January 1975 of all aerial plant parts and some of the root material. In April 1977, August–January 1980/1 and August 1984, all woody recruits in the plot were tagged and numbered, identified and measured (height), and mapped on a 1 m grid. The height of coppice was recorded. Ten of the eleven tree species present before felling produced coppice shoots. Two individuals almost attained canopy height by 1984. Twenty tree species and three shrub species were recruited from seed; six of the tree species were normally absent from the forest. Species composition changed very little with time.

The rate of seedling recruitment was greatest immediately after clearing. The overall den-sity of individuals changed little after 1977. Overall mortality of recruits was about 10% per annum. Mortality of the earliest recruits declined with time since establishment. Later recruits and individuals with poor growth had higher mortality than other plants. Mortality was not density-dependent. Growth rates of recruits were relatively slow. Only ten individuals exceeded 4 m by 1984.

Recruitment rates, density, growth and species diversity were greatest in the parts of the plot where the mor humus had been removed or piled up during the initial clearance. Recruit-ment, growth and density were least, and mortality was greatest, at the edge. There was no relationship between any of these parameters and the presence of coppicing stumps.

Tree species showed a clear spectrum from obligate gap-demanders to obligate shade-bearers. The persistence of gap-demanding species in this forest (in which gaps are normally rare) may be due to infrequent hurricanes, and also to a natural ability to produce basal sprouts. The succession conforms to an initial floristic composition model; it is slow, and we suggest that at least 50 years will elapse before the plot begins to resemble the undisturbed forest.

Keywords

coppicedisturbanceJamaicaregenerationseedlingssuccessiontropical montane forest
Type
Research Article
Information
Journal of Tropical Ecology , Volume 1 , Issue 4 , November 1985 , pp. 329 - 351
Copyright
Copyright © Cambridge University Press 1985

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