Predictors of plant diversity in a hyperarid desert wadi ecosystem

The aim of this study was to identify trends in plant diversity, and examine their predictive relationships with environmental variables (water stress, soil texture and grazing intensity) and vegetation characteristics (total vegetation and individual species cover), along a 340 km transect through an area of hyper-arid desert in southern Egypt. The major part of the transect is located within the boundaries of the Wadi Allaqi Man and Biosphere (MAB) Reserve. In total 55 plant species were recorded from the transect. A TWINSPAN classification of the data identified four of the seven main vegetation types, previously identified as present in the area by Springuel et al. (1997). Sites dominated by Vegetation type I occurred exclusively in the lowest stretch of the Wadi Allaqi system, most heavily influenced by flood and seepage from Lake Nasser, and characterized by dense stands of Tamarix nilotica (Ehrenb.) Bunge and Glinus lotoides L. Vegetation type IIIb was represented at sites higher up the wadi system, characterized by sparser vegetation dominated by Acacia ehrenbergiana Hayne, Acacia tortilis subsp. raddiana (Savi) Brenan and Aerva javanica (Burm. f.) Juss.ex Schult. Vegetation type IIIa occurred in the middle region of Wadi Allaqi and was characterized by Salsola imbricata Forssk. andCullen plicatum (Delile) C. H. Stirt. Vegetation type IV, the most species rich, was limited to upstream sites of Wadis Allaqi and Eiqat. Plant β -diversity (as species turnover between individual sites along the transect, assessed using Whittakerʹs βwindex) showed a rising trend of plant species turnover from sites low in the wadi system to sites located in the upper part of the wadi. Plant α -diversity within these vegetation types (as species richness R: number of species present per 500 m2unit area) was linearly correlated with plant diversity measured using Simpsonʹs index (D). R was reasonably well predicted from three variables: plant cover, soil moisture and grazing intensity (following a third order polynomial model). This model predicted R in the original data set with 52•9% success (r=0•73, p<0•001). The study suggested that vegetation cover estimates, in association with simple estimates of intensity of habitat stress (water availability) and disturbance (grazing intensity), can provide a rapid indication of the biodiversity support capacity of desert habitats