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Woody Seedlings (woody + seedling)
Selected AbstractsWhy do species of woody seedlings change rank in relative growth rate between low and high irradiance?FUNCTIONAL ECOLOGY, Issue 2 2001L. Sack First page of article [source] The influence of tree canopies and elephants on sub-canopy vegetation in a savannahAFRICAN JOURNAL OF ECOLOGY, Issue 1 2010Robert Guldemond Abstract The apparent influence of elephants on the structure of savannahs in Africa may be enhanced by management activities, fire and other herbivores. We separated the effect elephants have on grasses, woody seedlings (<0.5 m) and saplings (0.5,2 m) from the effect of tree canopies (canopy effect), and herbivory (park effect). We defined the canopy effect as the differences between plant abundances and diversity indices under tree canopies and 20 m away from these. Our testing of the park effect relied on the differences in the sub-canopy plant indices inside and outside a protected area that supported a range of herbivores. We based our assessment of the elephant effect on sub-canopy vegetation indices associated with elephant induced reductions in tree canopies. The park and canopy effects were more pronounced than the elephant effect. The park effect suppressed the development of woody seedlings into saplings. Conditions associated with tree canopies benefited woody plants, but not the grasses, as their indices were lower under trees. Elephants reducing canopies facilitated grass species tolerant of direct solar radiation. We concluded that management should consider other agents operating in the system when deciding on reducing the impact that elephants may have on vegetation. Résumé L'influence apparente des éléphants sur la structure des savanes africaines pourrait bien être accentuée par les activités de gestion, les feux et les autres herbivores. Nous avons séparé l'effet que les éléphants ont sur les herbes, les jeunes plants ligneux (<0,5 m) et les arbustes (0,5,2 m) de ceux de la canopée des arbres (effet canopée) et de la présence d'herbivores (effet parc). Nous avons défini l'effet canopée comme la différence entre les indices d'abondance et de diversité des plantes sous la canopée des arbres et à 20 m de ceux-ci. Notre expérimentation de l'effet parc se basait sur la différence des indices de végétation sous canopée à l'intérieur et à l'extérieur d'une aire protégée qui accueille toute une gamme d'herbivores. Nous avons fondé notre évaluation de l'effet éléphants sur les indices de végétation sous canopée, associés aux réductions induites par les éléphants dans la canopée des arbres. Les effets parc et canopée étaient plus prononcés que l'effet éléphants. L'effet parc supprimait le développement des jeunes plants ligneux en arbustes. Les conditions liées à la canopée des arbres bénéficiaient aux plantes ligneuses mais pas aux herbes, car leurs indices étaient inférieurs sous les arbres. Les canopées réduites par les éléphants favorisaient les espèces d'herbes tolérantes à la lumière directe du soleil. Nous en avons conclu que toute gestion devrait considérer l'impact d'autres agents dans le système lorsqu'il s'agit de réduire l'impact que les éléphants peuvent avoir sur la végétation. [source] Seedling regeneration, environment and management in a semi-deciduous African tropical rain forestJOURNAL OF VEGETATION SCIENCE, Issue 5 2009Edward N. Mwavu Abstract Questions: How is seedling regeneration of woody species of semi-deciduous rain forests affected by (a) historical management for combinations of logging, arboricide treatment or no treatment, (b) forest community type and (c) environmental gradients of topography, light and soil nutrients? Location: Budongo Forest Reserve, Uganda. Methods: Seedling regeneration patterns of trees and shrubs in relation to environmental factors and historical management types were studied using 32 0.5-ha plots laid out in transects along a topographic gradient. We compared seedling species diversity, composition and distribution patterns along topographic gradients and within types of historical management regimes and forest communities to test whether environmental factors contributed to differences in species composition of seedlings. Results: A total of 85 624 woody seedlings representing 237 species and 46 families were recorded in this rain forest. Cynometra alexandri C.H. Wright and Lasiodiscus mildbraedii Engl. had high seedling densities and were widely distributed throughout the plots. The most species-rich families were Euphorbiaceae, Fabaceae, Rubiaceae, Meliaceae, Moraceae and Rutaceae. Only total seedling density was significantly different between sites with different historical management, with densities highest in logged, intermediate in logged/arboricided and lowest in the nature reserve. Forest communities differed significantly in terms of seedling diversity and density. Seedling composition differed significantly between transects and forest communities, but not between topographic positions or historical management types. Both Chao-Jaccard and Chao-Sørensen abundance-based similarity estimators were relatively high in the plot, forest community and in terms of historical management levels, corroborating the lack of significant differences in species richness within these groups. The measured environmental variables explained 59.4% of variance in seedling species distributions, with the three most important being soil organic matter, total soil titanium and leaf area index (LAI). Total seedling density was positively correlated with LAI. Differences in diversity of >2.0 cm dbh plants (juveniles and adults) also explained variations in seedling species diversity. Conclusions: The seedling bank is the major route for regeneration in this semi-deciduous tropical rain forest, with the wide distribution of many species suggesting that these species regenerate continuously. Seedling diversity, density and distribution are largely a function of adult diversity, historical management type and environmental gradients in factors such as soil nutrient content and LAI. The species richness of seedlings was higher in soils both rich in titanium and with low exchangeable cations, as well as in logged areas that were more open and had a low LAI. [source] The Role of Soil Seed Banks in the Rehabilitation of Degraded Hillslopes in Southern Wello, Ethiopia,BIOTROPICA, Issue 1 2000Kebrom Tekle ABSTRACT The species composition in the soil seed bank of degraded hillslopes in southern Wello, Ethiopia, was assessed using the seedling emergence method and compared with that of the standing vegetation. Surface soils were sampled at 0-to 5-cm depth from 49 plots of four physiognomic vegetation classes (hereafter vegetation classes): forests, shrublands, grasslands, and degraded sites. Soils were spread on sterile sand in a glasshouse and watered. Emerging seedlings were recorded for five months until no new seedlings emerged. A total of 3969 seedlings belonging to 71 species and 30 families germinated. The species composition of the seed bank was dominated by 53 herb species (75%) compared to 2 tree species which accounted for only 3 percent of the total number of species. Seedling density differed significantly among vegetation classes and ranged from 391 to 7807 seeds/m2. Mean species richness also differed significantly among the vegetation classes. Forty-two species were found to be common to the seed banks and the standing vegetation; however, correspondence between species numbers and composition of the seed banks and the standing vegetation was poor. Although most of the species that germinated in the seed banks were herbs and grasses, they can develop a vegetative cover and contribute to reduction of soil erosion. Regeneration of the tree species (some of which have seed viability up to four years) however, requires both time and the presence of mature individuals. Together with hillside closure and soil conservation measures (e.g., terracing), planting of native woody seedlings might help to expedite rehabilitation of degraded hillslopes devoid of trees and shrubs. [source] | ||||||||||