Abstract:SummaryThe baobab tree population of the Msembe study area was surveyed for the third time in 1989. Although tree density had dropped between the 1976 and 1982 surveys, there was no significant change between 1982 and 1989, probably because most bull éléphants had been killed by poachers. The change in the baobab size distribution between 1976 and 1989 is similar to that predicted by a model simulating the effects of elephant browsing on baobabs. It suggests that elephant browsing has a different effect on bao… Show more
“…Several factors including those not investigated, could explain this spatial distribution. Wilson (1988) and Barnes et al (1994) suggested that baobab densities are very variable across landscapes as they are affected by a number of establishment factors, such as insect outbreaks, past human activities, droughts or edaphic variables (Edkins et al 2007), all interacting in a complex and unpredictable ways (Scholes and Walker 1993). In Gonarezhou, Tafangenyasha (1992) suggested that herbivores (e.g., elephant and tree squirrels), drought, and increased density of associated species could bring about deaths of baobabs.…”
“…Several factors including those not investigated, could explain this spatial distribution. Wilson (1988) and Barnes et al (1994) suggested that baobab densities are very variable across landscapes as they are affected by a number of establishment factors, such as insect outbreaks, past human activities, droughts or edaphic variables (Edkins et al 2007), all interacting in a complex and unpredictable ways (Scholes and Walker 1993). In Gonarezhou, Tafangenyasha (1992) suggested that herbivores (e.g., elephant and tree squirrels), drought, and increased density of associated species could bring about deaths of baobabs.…”
“…PFR may be an extreme case of increased animalrelated damage resulting from increases in animal densities within reserves, but shifts in community composition following animal-induced damage to vegetation have been proposed in several studies, e.g. elephant browsing in African savannahs (Barnes et al 1994) and white-tailed deer browsing in eastern North America (Long & Carson 1998). We concur with Guariguata (1998) that 'interspecific patterns of post-damage response' may generally be a critical lifehistory parameter that affects the structure, species composition and diversity of tropical forests.…”
Summary 1The lowland rain forest at Pasoh Forest Reserve in Peninsular Malaysia is subject to disturbance by native wild pigs ( Sus scrofa ). Female pigs snap off woody plants up to 3.5 m tall to construct nests for reproduction, damaging >170 000 saplings km − 2 year − 2. We investigated the ability of 1808 woody saplings to survive and resprout over a 3-year period following pig and experimental stem snap. 2 Most plants resprouted to some degree, but, in understorey conditions, growth of new shoots was slow. More than 90% of stems were alive 3 months after damage, but > 40% had not yet produced a single fully expanded leaf. Mortality at 36 months was higher for resprouting saplings (33%) than for undamaged control saplings (9%). Survival of damaged stems was highly and positively correlated with stump basal diameter. Canopy species consistently showed lower survivorship than midstorey, understorey and treelet species but no differences in survivorship were found for habit (tree vs. liana) or leaf morphology (simple vs. compound). 3 The number and total length of resprout shoots (TSL) were strongly, positively correlated with stump diameter. Canopy species produced greater TSL but fewer new shoots than did smaller-stature species. Trees and lianas produced similar TSL at 3 and 6 months, but trees produced more TSL at 12 and 36 months. Simple-leaved plants consistently had longer TSL than compound-leaved plants. 4 Both species and families differed greatly in terms of survival, TSL and number of shoots. Dipterocarpaceae, which comprises 24% of basal area in the forest, and Euphorbiaceae, the most species-rich family, had especially poor survivorship of damaged individuals. 5 Our results suggest that elevated pig densities found in small forest reserves such as Pasoh are likely to alter tree community composition as a result of the differential ability of species to regenerate following physical disturbance. Regeneration of canopy tree species, particularly in the silviculturally important and heavily dominant family Dipterocarpaceae, may be particularly susceptible to pig-related disturbance.
“…Rather, we assess the impact of elephants visiting this square kilometer, i.e., elephants can be dealt with as a timevarying input into the model, and different scenarios may be analyzed. We consider this approach more realistic than limiting our analysis, as in some earlier studies [4,5,82,99], to various constant elephant "stocking densities." In addition, this approach naturally extends to a geographic information systems setting in which our model is used to evaluate the effects of elephants in each of many grid cells on top of which elephant movements are imposed (cf.…”
Section: Elephant Populationmentioning
confidence: 97%
“…for transitions within metaclasses), we set l i =1 (i=2, 3,4,6,8). Any given level of growth, g i , may also entail shading out other plants in the same or lower height class and so we introduce h i as a "crowding coefficient", representing the proportion of plants overshadowed by the individuals growing from class i to i+1 (see Fig.…”
We describe the development and parameterization of a grid-based model of African savanna vegetation processes. The model was developed with the objective of exploring elephant effects on the diversity of savanna species and structure, and in this formulation concentrates on the relative cover of grass and woody plants, the vertical structure of the woody plant community, and the distribution of these over space. Grid cells are linked by seed dispersal and fire, and environmental variability is included in the form of stochastic rainfall and fire events. The model was parameterized from an extensive review of the African savanna literature; when available, parameter values varied widely. The most plausible set of parameters produced long-term coexistence between woody plants and grass, with the tree-grass balance being more sensitive to changes in parameters influencing demographic processes and drought incidence and response, while less sensitive to fire regime. There was considerable diversity in the woody structure of savanna systems within the range of uncertainty in tree growth rate parameters. Thus, given the paucity of height growth data regarding woody plant species in southern African savannas, managers of natural areas should be cognizant of different tree species growth and damage response attributes when considering whether to act on perceived elephant threats to vegetation.
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