The possible role of ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด sp. on regeneration of die-back forests of Horton Plains National Park
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University of Peradeniya , Sri Lanka
Abstract
Some natural forest communities including the Upper Montane Rain Forest (UMRF) of Horton Plains, Pidurutalagala ridge, Kobonilgala near Corbett's gap in Knuckles range and the summits of Hakgala Strict Nature Reserve in Sri Lanka are seriously deteriorating due to stand level dieback. The extent of forest die-back in the Horton Plains National Park (HPNP) was estimated as 654 ha of forest, representing 24.5 % of the forests and 17.2 % of the total area of the national park. Die-back is severe in the Totapolakanda and Kirigalpotta areas, where more than 75 % of the canopy trees were dead and the remaining trees showing signs of die-back. Larger trees were more prone to die-back than smaller ones. Forest regeneration in these two areas was very slow. Although, some previous reports attribute the die-back to the severity of the weather conditions, there is little information available on the causes of dieback, the process of and factors controlling the regeneration of die-back areas. It has been reported that damage caused to tree barks browsing by Sambar deer in the Horton Plains is significant. In this research, study sites were selected using a remote-sensed map of HPNP and two die-back forest types were recognized based on the presence or absence of ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด spp. beside the composition of the vegetation. Eight, ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด free or ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด dominated 50 m X 20 m transects (further divided in to five 20 m X 10 m segments) were selected randomly. Saplings (< 5 cm dbh) in those segments were recorded. Specimens were taken from unidentified individuals and were identified using the specimens in the national herbarium. ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด cover in ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด dominated die-back sites were above 70% 80%. In the sites dominated with ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด spp, 6 - 13 forest tree saplings were recorded, and the light intensity of the ground was 15-30 ฮผmol.m-ยฒs-1. In contrast, ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด free regenerating - forest die back sites consists of 28 - 70 tree saplings and receive 50-70 ฮผmol.mยฒs-1 to the ground level. The number of tree saplings observed in the ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด free sites is significantly higher (p = 0.0006) than the number of saplings found in the ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด dominated sites. Further, the number of trees > 1 m height was higher in the ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด free sites (32-57 individuals) than in the ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด dominated sites (12-17 individuals). Our results revealed that there is an impact of ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด cover on availability of saplings of the other forest species. Further, it seems that the growth and development of the tree saplings were also affected by the ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด cover. ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด in the dieback forest in HPNP seems to act as a barrier and limits necessary conditions such as light, soil surface and nutrients for the growth of some of the tree species, and may result in the delay of regeneration of the die-back forest. However, further observations are required to determine whether ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด vegetation is reestablished and acts as a barrier periodically in the same area or remains as ๐๐ต๐ณ๐ฐ๐ฃ๐ช๐ญ๐ข๐ฏ๐ต๐ฉ๐ฆ๐ด free, regenerating forest stands.
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Proceedings of the Peradeniya University International Research Sessions (iPURSE) - 2014, University of peradeniya, P 560