Subdominant species distribution in microsites around two life forms at a desert grassland-shrubland transition zone

• Published in: Journal of vegetation science Vol. 15; no. 5; pp. 615 - 622
• Main Authors: Hochstrasser, T, Peters, D. P C
• Format: Journal Article
• Language: English
• Published: Opulus Press 01.10.2004
• Subjects: Annual; botanical composition; Bouteloua eriopoda; canopy; Deserts; Dominant plant; Ecology; Ecotone; ecotones; Functional group; Functional groups; Grasses; grasslands; Larrea tridentata; microhabitats; plant communities; Plants; s; Scale; Shrub invasion; shrublands; Shrubs; Soil texture; spatial distribution; Spatial heterogeneity; Species; temporal variation; Transition zones; understory; Vegetation canopies; New Mexico
• ISSN: 1100-9233; 1654-1103
• DOI: 10.1658/1100-9233(2004)015[0615:SSDIMA]2.0.CO;2

Question: In the same landscape context – at a desert grassland-shrubland transition zone, how does subdominant plant abundance vary in microsites around dominant grasses and shrubs? Location: Sevilleta LTER, New Mexico, USA (34°21′ N; 106°53′ W; 1650 m a.s.l.). Methods: We compared the distribution of subdominant plants in canopy, canopy edge and interspace microsites around individual shrubs (Larrea tridentata) and grasses (Bouteloua eriopoda) at a transition zone that has been encroached by shrubs within the past 50 - 100 a. Plots of variable size according to microsite type and dominant plant size were sampled. Results: Subdominant abundance was higher in microsites around L. tridentata shrubs than in microsites around B. eriopoda. Furthermore, differences in species abundance and composition were higher among microsites around grasses than among microsites around shrubs. The distribution of subdominants was mostly explained by their phenological characteristics, which indicates the importance of temporal variation in resources to their persistence. Conclusions: This study of coexistence patterns around dominants revealed ecological contrasts between two dominant life forms, but other factors (such as disturbances) have to be taken into consideration to evaluate landscape-scale diversity. Nomenclature: Anon. (1999).