scholarly journals Incorporating dominant species as proxies for biotic interactions strengthens plant community models

2014 ◽  
Vol 102 (3) ◽  
pp. 767-775 ◽  
Author(s):  
Peter C. le Roux ◽  
Loïc Pellissier ◽  
Mary S. Wisz ◽  
Miska Luoto
2009 ◽  
pp. 27-53
Author(s):  
A. Yu. Kudryavtsev

Diversity of plant communities in the nature reserve “Privolzhskaya Forest-Steppe”, Ostrovtsovsky area, is analyzed on the basis of the large-scale vegetation mapping data from 2000. The plant community classi­fication based on the Russian ecologic-phytocoenotic approach is carried out. 12 plant formations and 21 associations are distinguished according to dominant species and a combination of ecologic-phytocoenotic groups of species. A list of vegetation classification units as well as the characteristics of theshrub and woody communities are given in this paper.


2020 ◽  
Vol 34 (7) ◽  
pp. 1497-1506
Author(s):  
Maja K. Sundqvist ◽  
Nathan J. Sanders ◽  
Ellen Dorrepaal ◽  
Elin Lindén ◽  
Daniel B. Metcalfe ◽  
...  

Author(s):  
Mário L. Garbin ◽  
Karlo G. Guidoni-Martins ◽  
Renan K. Hollunder ◽  
Pierre Mariotte ◽  
Fabio R. Scarano ◽  
...  

2014 ◽  
Vol 20 (3) ◽  
pp. 237 ◽  
Author(s):  
Peter J Berney ◽  
G. Glenn Wilson ◽  
Darren S. Ryder ◽  
R.D.B Whalley ◽  
John Duggin ◽  
...  

We examined the effects of grazing exclusion over a period of 14 years on the species richness and community composition of three plant communities with different dominant species and water regimes in the Gwydir Wetlands in eastern Australia. Responses to grazing exclusion varied among the three plant communities, and were most likely to be evident during dry periods rather than during periods of inundation. In frequently flooded plant communities, there was an increase in phytomass following exclusion of domestic livestock, but changes in plant community composition and species richness due to livestock exclusion varied depending on the morphological attributes of the dominant plant species. In a plant community where tall sedge species were dominant, livestock exclusion further increased their dominance and overall species richness declined. In contrast, where a prostrate grass species such as Paspalum distichum was dominant, species richness increased following livestock exclusion, due to an increase in the abundance of taller dicotyledon species. However, livestock exclusion in a community where flooding was less frequent and native grass species have been largely replaced with the introduced species Phyla canescens, resulted in no significant changes to phytomass, species richness or community composition among the grazing exclusion treatments over time. Our results indicate responses to exclusion of domestic livestock are dependent upon the dominant species within the plant community and will likely vary over time with the extent of wetland inundation. Grazing exclusion alone, without increased flooding, is unlikely to restore floristically degraded floodplain plant communities.


1984 ◽  
Vol 62 (1) ◽  
pp. 142-153 ◽  
Author(s):  
E. F. Karlin ◽  
L. C. Bliss

A broad range of water chemistry (pH 3.5–8.2; Ca, 2–120 mg L−1) and substrate chemistry (pH 3.3–7.8; Ca, 4–138 mequiv. 100 g−1) exists among peatlands present in central Alberta. The six peatlands comprising the main study sites included strongly minerotrophic, moderately minerotrophic, and weakly minerotrophic systems. Variation in substrate chemistry along the hollow to hummock gradient in strongly and moderately minerotrophic peatlands was high (ranging from highly minerotrophic peats to ombrotrophic peats), while variation in substrate chemistry in weakly minerotrophic peatlands was slight (weakly minerotrophic peats to ombrotrophic peats) along the same gradient. Substrate chemistry and plant community composition of hollow and low-hummock communities varied considerably along the strongly minerotrophic to weakly minerotrophic peatland gradient. In contrast, the chemistry of the upper peat layers of the hummocks and hummock plant community composition were similar in all of the peatlands studied. Distributional patterns of plant species in weakly minerotrophic peatlands are not primarily in response to gradients in substrate chemistry but arise from gradients in substrate moisture and biotic interactions. This is not the case for strongly and moderately minerotrophic systems, where gradients in substrate chemistry may also strongly influence plant species distribution. The increase in complexity of the substrate environment in peatlands along the weakly minerotrophic to strongly minerotrophic gradient is reflected by a parallel increase in plant species diversity.


2004 ◽  
Vol 82 (11) ◽  
pp. 1576-1585 ◽  
Author(s):  
W L Strong

The composition and abundance of vascular plants within a boreal Populus tremuloides Michx. stand in west-central Alberta were assessed three, five, nine, and 20 years after clearcutting. Rapid re-establishment of Populus tremuloides and other species such as Amelanchier alnifolia (Nutt.) Nutt. ex M. Roemer and Rosa acicularis Lindl. occurred primarily in response to vegetative propagation. Some minor compositional variability occurred among the year 3 plots (n = 88), but they were considered members of the same plant community, with 88% of the plots undergoing similar developmental processes during the course of the study. Some dominant species substantially increased in canopy cover, although most species maintained a relatively consistent level of abundance over time. Floristic richness was similar in year 3 (64 species) and year 20 (62 species) with the survival of 52 initiating species in year 20. The variability in floristic richness included the invasion of 32 species and the extirpation of 34 species. Stand development over a 20-year period best fit a tolerance model of succession because of the rapid development of dominant species, the lack of a major understory composition change, and a similar degree of dominance concentration among species. Understory vegetation growth was constrained by overstory shading.Key words: plant community, tolerance model, secondary succession.


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