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Journal of Zoology - CERU - University of Pretoria

Journal of Zoology - CERU - University of Pretoria

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K. D. Young, S. M. Ferreira and R. J. van AardeElephant spatial use in wet and dry savannasTable 3 Proportion <strong>of</strong> the total number <strong>of</strong> grid cells (1 km 2 ) <strong>of</strong> each study site falling into structural vegetation classes as defined by Mayaux et al. (2003)Areas wherecroplandswere mixedwith openvegetationSwampbushlandand grasslandHerbaceouscoverbetween1 and 5%Herbaceouscover between5 and 15%without shrubcanopyShrub canopycover o20%.Herbaceouscover between15 and 40%Tree and shrubcanopy covero20%. Herbaceouscover 440%Shrub canopycover 415%.Canopy heighto5 m. No treelayerShrub canopycover 415%.Canopy heighto5 m. Sparsetree layer o15%Tree canopycover between15 and 40%.Canopy height45mTree canopycover440%.Canopyheight45mStudy siteEtosha 0.03 0.47 0.30 0.01Khaudum 0.35 0.55 0.11NG11 0.17 0.02 0.70 0.11 0.09Kafue 0.01 0.60 0.24 0.01 0.12Lower 0.03 0.16 0.37 0.07 0.06 0.01 0.31ZambeziSouthLuangwa0.50 0.02 0.48Elephant spatial use and vegetationproductivityWe regressed elephant home-range sizes (pooled for wet anddry savannas), our measure <strong>of</strong> utilization uniformity andour measure <strong>of</strong> inter-seasonal repeated visits against seasonspecificvegetation productivity measures per site and pervegetation structural class for each site.Selection within home rangesWe compared maximum NDVI for visited 5 km 2 grid cellswithin each 10 day period with the same number <strong>of</strong> randomlyselected 5 km 2 grid cells (pseudo-absences; Engler,Guisan, & Rechsteiner, 2004). We permutated this procedure10 000 times (see Gentle, 1943) and proposed a nullmodel that the mean value <strong>of</strong> visited grid cells was drawnfrom the same distribution as values from randomly selectedgrid cells within the same 10 day period. We rejected the nullmodel if Po0.05. For each elephant- and season-specific set<strong>of</strong> 10 day time periods, we calculated the proportion <strong>of</strong>periods where the mean maximum NDVI <strong>of</strong> visited gridcells was higher, and significantly (Po0.05) higher, thanthat for randomly selected grid cells.We further assessed whether elephant cows selected forareas <strong>of</strong> higher NDVI within structural vegetation classes(Mayaux et al., 2003). We removed the effect <strong>of</strong> time onNDVI values by calculating a residual maximum NDVI(rC j(t) ) value for each grid cell <strong>of</strong> each elephant’s seasonalhome range for each 10 day NDVI data period as followsrC jðtÞ ¼ C jðtÞX nj¼1C j =m ðtÞwhere C j(t) is the maximum NDVI value <strong>of</strong> cell j at time t,and m is the mean maximum NDVI value <strong>of</strong> all grid cells attime t. We then used a one-tailed t-test (Zar, 1984) tocompare mean residual maximum NDVI for visited gridcells with the same number <strong>of</strong> randomly selected grid cellswithin each structural vegetation class that was representedin each elephant- and season-specific home range for the firstwet and the first dry season <strong>of</strong> our study. We then calculatedthe proportion <strong>of</strong> residual mean maximum NDVI valuesthat were higher for visited than randomly selected grid cellsfor wet and dry savannas.ResultsElephant spatial useHome rangesHome-range sizes <strong>of</strong> elephant cows from dry savannas werethree- and four-fold those <strong>of</strong> elephants from wet savannasduring the wet and dry seasons, respectively (two-tailedt-test: wet season, t=3.35, d.f.=34, P=0.002; dry season,t=3.50, d.f.=34, P=0.001) (Fig. 2a). Although seasonaldifferences between wet- and dry-season home-range sizes<strong>Journal</strong> <strong>of</strong> <strong>Zoology</strong> 278 (2009) 189–205 c 2009 The Authors. <strong>Journal</strong> compilation c 2009 The Zoological Society <strong>of</strong> London 193

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