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Spatial heterogeneity of the soil seed bank in the tropical semi ...

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PERERA 83due to abundance <strong>of</strong> Ageratum conyzoides <strong>seed</strong>s, acharacteristic feature <strong>of</strong> <strong>the</strong> <strong>soil</strong> <strong>seed</strong> <strong>bank</strong> <strong>of</strong> <strong>the</strong>ecotone.Seeds <strong>of</strong> forest species were, ma<strong>in</strong>ly, present<strong>in</strong> <strong>the</strong> forest <strong>soil</strong> <strong>seed</strong> <strong>bank</strong> although a few <strong>of</strong><strong>the</strong>m were also found <strong>in</strong> <strong>the</strong> <strong>soil</strong> <strong>seed</strong> <strong>bank</strong> <strong>of</strong> <strong>the</strong>forest-grassland ecotone (Table 1). They were,however, hardly found <strong>in</strong> <strong>the</strong> grassland <strong>soil</strong> <strong>seed</strong><strong>bank</strong>. Most <strong>of</strong> <strong>the</strong> typical grassland species werefound <strong>in</strong> <strong>the</strong> forest <strong>soil</strong> although <strong>the</strong>y were found<strong>in</strong> <strong>the</strong> <strong>soil</strong> <strong>seed</strong> <strong>bank</strong>s <strong>of</strong> <strong>the</strong> grassland and <strong>the</strong>ecotone <strong>in</strong> large quantities. When <strong>the</strong> woodyspecies were considered, it became evident that<strong>seed</strong>s <strong>of</strong> <strong>the</strong> most common woody forest specieswere not represented <strong>in</strong> <strong>the</strong> <strong>soil</strong> <strong>seed</strong> <strong>bank</strong>except for Diplodiscus verrucosus (Thw.)Kosterm. and Memecylon umbellatum Burm. f.(Table 2).Density <strong>of</strong> <strong>seed</strong>s <strong>in</strong> <strong>the</strong> surface <strong>soil</strong>Seed densities <strong>in</strong> <strong>the</strong> <strong>soil</strong> varied significantlywith <strong>the</strong> distance form <strong>the</strong> forest grasslandboundary (one way ANOVA: P < 0.001). The mean<strong>seed</strong> density was higher <strong>in</strong> <strong>the</strong> grassland (8339 ±918) and at <strong>the</strong> forest-grassland ecotone grassland(6990 ± 2751)(Fig. 3). However, <strong>the</strong>re was anabrupt decl<strong>in</strong>e <strong>in</strong> <strong>the</strong> densities <strong>of</strong> <strong>seed</strong>s <strong>in</strong> <strong>the</strong> <strong>soil</strong>beyond 5 m distance <strong>in</strong>to <strong>the</strong> forest and <strong>the</strong> density<strong>of</strong> <strong>the</strong> forest <strong>soil</strong> <strong>seed</strong> <strong>bank</strong> was 583 ± 236. Therewas a very high <strong>in</strong>teraction between <strong>the</strong> distanceand <strong>the</strong> transects (blocks), especially <strong>in</strong> <strong>the</strong>Table 1. Distribution <strong>of</strong> typical forest and grassland species (as a percentage <strong>of</strong> <strong>the</strong> total number <strong>of</strong> plots <strong>in</strong> eachcategory) <strong>in</strong> <strong>the</strong> two <strong>soil</strong> <strong>seed</strong> <strong>bank</strong> types and at <strong>the</strong> forest-grassland ecotone.Species category Species Grassland<strong>in</strong>teriorFrequency (%)Forest-grasslandecotoneForest <strong>in</strong>teriorForest species Diplodiscus verrucosus 0 5 19Peperomia pellucida 0 10 38Flueggea leucopyrus 0 35 75Walsura trifoliolata 0 0 25Grassland species Ageratum conyzoides 33 85 38Phyllanthus amarus 8 10 7L<strong>in</strong>dernia crustacea 58 75 19Desmodium triflorum 25 55 0Oldenlandia herbacea 42 60 0Ocimum canum 25 25 6Scoparia dulcis 50 25 7Mimosa pudica 67 55 31Table 2. Dom<strong>in</strong>ant woody species <strong>in</strong> <strong>the</strong> stand<strong>in</strong>g vegetation and <strong>the</strong> on <strong>the</strong> <strong>soil</strong> (Species <strong>in</strong> each category arearranged <strong>in</strong> descend<strong>in</strong>g order <strong>of</strong> abundance).Forest vegetation (studied by Jayas<strong>in</strong>gham 1991)Dimorphocalyx glabellus, Mallotus rhamnifolius,Glycosmis sp., Polyalthia kor<strong>in</strong>ti, Diospyrosovalifolia, Diplodiscus verrucosus, Memecylonumbellatum, Drypetes sepiaria, Catunaregamsp<strong>in</strong>osa, Phyllanthus polyphyllusSoil <strong>seed</strong> <strong>bank</strong> estimated by <strong>the</strong> current studyForest <strong>in</strong>teriorFlueggea leucopyrus, Chromolaena odorata, Diplodiscusverrucosus, Memecylon umbellatum, Salacia oblonga, Walsuratrifoliolata, Phyllanthus reticulatusForest - grassland ecotoneFlueggea leucopyrus, Chromolaena odorata, Phyllanthusreticulatus, Diplodiscus verrucosusGrassland <strong>in</strong>teriorAristolochia <strong>in</strong>dica, Calotropis gigantea

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