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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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