Fruit-frugivore interactions in a Malagasy littoral forest - Universiteit ...
Fruit-frugivore interactions in a Malagasy littoral forest - Universiteit ...
Fruit-frugivore interactions in a Malagasy littoral forest - Universiteit ...
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Intersite comparison<br />
characteristics were analysed with two-way analyses of variance. Data were arcs<strong>in</strong>e<br />
transformed for these analyses. Statistical analyses were run accord<strong>in</strong>g to Siegel (1956)<br />
with the help of SAS and SPSS software.<br />
RESULTS<br />
Climate and phenology<br />
Figure 2 shows phenology and annual precipitation for both study sites. Annual ra<strong>in</strong>fall<br />
was 2,480mm <strong>in</strong> STL and 721mm <strong>in</strong> KIR dur<strong>in</strong>g the study period. The phenological<br />
patterns considered <strong>in</strong> this study differ slightly from the overall pattern at both sites as<br />
published previously (Sorg and Rohner 1996; Donati 2002) because only a subset of the<br />
complete phenological dataset was used for comparison.<br />
In KIR ripe fruits are available year round with a m<strong>in</strong>imum <strong>in</strong> April. ‘Fleshy’ and ‘nonfleshy’<br />
fruit species are equally (50%) represented <strong>in</strong> KIR (Fig. 2). Dur<strong>in</strong>g the dry season<br />
(May through October) non-fleshy fruits predom<strong>in</strong>ate. As <strong>in</strong>dicated before, <strong>in</strong> STL there<br />
are no clearly def<strong>in</strong>ed wet or dry seasons. <strong>Fruit</strong> abundance here is highest from January<br />
through March, rather limited from April through October with a lean period from June to<br />
August. The majority (81%) of fruit species <strong>in</strong> STL are characterised as ‘fleshy’. In<br />
contrast to KIR, the representation of the ‘non-fleshy’ fruits rema<strong>in</strong>s low but fairly constant<br />
(4-7%) <strong>in</strong> STL throughout the year.<br />
Soil conditions<br />
In the upper layer (A horizon) soils are more acid and conta<strong>in</strong> higher concentrations of<br />
organic matter, nitrogen and phosphor <strong>in</strong> STL than <strong>in</strong> KIR (Table 3). Exchange capacity<br />
has not been measured for STL. The situation at STL is similar to the data available for<br />
Ranomafana, an evergreen ra<strong>in</strong><strong>forest</strong> site at higher altitude (Ganzhorn et al. 1999b).<br />
There, growth rate of trees is higher than at Kir<strong>in</strong>dy, probably due to the longer growth<br />
season. However, the probability of fruit<strong>in</strong>g is reduced, <strong>in</strong>dicat<strong>in</strong>g that fruit production is<br />
associated with higher stress for the trees of the evergreen <strong>forest</strong>. It is unclear how these<br />
different constra<strong>in</strong>ts affect the type of fruits produced.<br />
Floristics<br />
Both datasets have 30 families (40%) and 19 genera (10%) <strong>in</strong> common but no tree<br />
species (Table 2). In STL the four most important plant families were Rubiaceae (23<br />
species), Euphorbiaceae (8), Flacourtiaceae (6), and Myrtaceae (6). They accounted for<br />
25% of all species. In KIR Fabaceae (16), Euphorbiaceae (14), Tiliaceae (9), Rubiaceae<br />
(8), and Combretaceae (6) were the five most important plant families. They accounted<br />
for 31% of the species. The representation of these top eight families is not correlated<br />
between the two datasets (rs=0.18; P=0.7, N=8). The representation of large and small<br />
trees, shrubs and other growth forms <strong>in</strong> the samples did not differ between sites (Table<br />
4).<br />
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