The aim of the study was to compare glade and forest-glade edge plant community attributes for man-made, upper and lower natural glades. Two plots were set up in twelve glades at 2.5, 12.5 m and three plots in thirtee...The aim of the study was to compare glade and forest-glade edge plant community attributes for man-made, upper and lower natural glades. Two plots were set up in twelve glades at 2.5, 12.5 m and three plots in thirteen glades at 2.5, 12.5 and 22.5 m depending on the size of the glade. The results showed that plants total abundance, percentage basal cover, species richness and species diversity for upper and lower natural glades differed significantly p < 0.05 and p < 0.01 respectively and species diversity for man-made glades p < 0.001. Plant species abundance, richness and diversity were highest at the forest-glade edge and decreased towards the glade interior. Plant species composition of the three glades types differed significantly (MRPP: T = -4.51, p < 0.001 and A = 0.17). Grasses’ total abundance and species richness and forbs species diversity differed significantly for man-made glades p < 0.01. For upper natural glades, grasses species richness was highly significant p < 0.001 while for forbs species richness and diversity were significant P < 0.01. Lower natural glades grasses and forbs’ total abundance, species richness and species diversity differed significantly p < 0.01 and p < 0.001 respectively. Growth forms in the lower natural glades were associated with the forest-glade edge or glade interior χ<sup>2</sup> = 15.95, df = 4, p Eleusine jaegeri, Heterogon contortus, Senna mimisoides, Digitaria scalarum, Clutia abyssinica) were habitat indicators for disturbed areas, wet humid grey/black clay soils for upper natural glades and three (Solanum incanum, Senna didymobotrya, and Pennistem mezianum, were indicators of overgrazed areas and black clay soils for man-made glades. In conclusion, plant species abundance, richness and diversity were highest at the forest-glade edge and decreased towards the glade interior, while plant species composition differed significantly between the three-glade types. The plant growth form for lower natural glades was associated with forest-glade edge and glade interior.展开更多
Human presence is detrimentally affecting natural environments. Glades are an example of such envi-ronments. As glades diminish in number, proper restoration efforts are essential for the preservation of the habitats...Human presence is detrimentally affecting natural environments. Glades are an example of such envi-ronments. As glades diminish in number, proper restoration efforts are essential for the preservation of the habitats’ unique ecosystems, biodiversity and natural processes. To ensure glade survivorship, evaluation of glade restoration efforts is critical. As indicators of the trophic level of producers in a food chain, wildflowers can serve as overall indicators of the restoration process. A comparison of wildflower species presence and abundance between recently restored and control glades offer insights into the restoration progress. In this paper, I propose the us-age of a novel method for assessing restoration effi-cacy. I outline step-by-step how to apply such a method. I then explain how the implementation of such a method can be used to address questions re-garding the restoration effort’s efficacy.展开更多
文摘The aim of the study was to compare glade and forest-glade edge plant community attributes for man-made, upper and lower natural glades. Two plots were set up in twelve glades at 2.5, 12.5 m and three plots in thirteen glades at 2.5, 12.5 and 22.5 m depending on the size of the glade. The results showed that plants total abundance, percentage basal cover, species richness and species diversity for upper and lower natural glades differed significantly p < 0.05 and p < 0.01 respectively and species diversity for man-made glades p < 0.001. Plant species abundance, richness and diversity were highest at the forest-glade edge and decreased towards the glade interior. Plant species composition of the three glades types differed significantly (MRPP: T = -4.51, p < 0.001 and A = 0.17). Grasses’ total abundance and species richness and forbs species diversity differed significantly for man-made glades p < 0.01. For upper natural glades, grasses species richness was highly significant p < 0.001 while for forbs species richness and diversity were significant P < 0.01. Lower natural glades grasses and forbs’ total abundance, species richness and species diversity differed significantly p < 0.01 and p < 0.001 respectively. Growth forms in the lower natural glades were associated with the forest-glade edge or glade interior χ<sup>2</sup> = 15.95, df = 4, p Eleusine jaegeri, Heterogon contortus, Senna mimisoides, Digitaria scalarum, Clutia abyssinica) were habitat indicators for disturbed areas, wet humid grey/black clay soils for upper natural glades and three (Solanum incanum, Senna didymobotrya, and Pennistem mezianum, were indicators of overgrazed areas and black clay soils for man-made glades. In conclusion, plant species abundance, richness and diversity were highest at the forest-glade edge and decreased towards the glade interior, while plant species composition differed significantly between the three-glade types. The plant growth form for lower natural glades was associated with forest-glade edge and glade interior.
文摘Human presence is detrimentally affecting natural environments. Glades are an example of such envi-ronments. As glades diminish in number, proper restoration efforts are essential for the preservation of the habitats’ unique ecosystems, biodiversity and natural processes. To ensure glade survivorship, evaluation of glade restoration efforts is critical. As indicators of the trophic level of producers in a food chain, wildflowers can serve as overall indicators of the restoration process. A comparison of wildflower species presence and abundance between recently restored and control glades offer insights into the restoration progress. In this paper, I propose the us-age of a novel method for assessing restoration effi-cacy. I outline step-by-step how to apply such a method. I then explain how the implementation of such a method can be used to address questions re-garding the restoration effort’s efficacy.
