Habitat differences do not explain population declines of sable antelope in an African savanna

Sable antelope, Hippotragus niger, populations have declined substantially in Kruger National Park, South Africa despite large-area protection from land use and poaching. Since Africa's large mammal populations are restricted to protected areas, understanding how to manage parks for biological diversity is critically important to the sustainability of faunal populations into the future. To better understand the drivers of sable decline, we analyzed landscapes where herds persist in the Pretoriuskop region of Kruger – identified by GPS collar telemetry data from eight individuals in five herds remaining in this area, and compared them to landscapes where sable herds have recently disappeared. We mapped these landscapes with satellite-based spectral data on vegetation greenness and fire frequency and Carnegie Airborne Observatory LiDAR (Light Detection and Ranging) data on 3-D vegetation structure. Within their home ranges, sable herds consistently selected areas with high fire frequency, high tree cover and low shrub cover. However, there were no consistent differences in habitat features between the home ranges of current sable herds and areas formerly supporting herds. Locally deteriorating habitat conditions were therefore not responsible for the decline in sables in this region of the park. Our study also illustrates how multi-sensor, 3-D mapping of ecosystems provides a means to assess causes and consequences of changing animal habitats over time.

[1]  Gregory P Asner,et al.  Advances in animal ecology from 3D-LiDAR ecosystem mapping. , 2014, Trends in ecology & evolution.

[2]  N. Owen‐Smith,et al.  Are relatively rare antelope narrowly selective feeders? A sable antelope and zebra comparison , 2013 .

[3]  A. Michel,et al.  Mycobacterium tuberculosis at the human/wildlife interface in a high TB burden country. , 2013, Transboundary and emerging diseases.

[4]  Gregory P. Asner,et al.  Lion hunting behaviour and vegetation structure in an African savanna , 2013, Animal Behaviour.

[5]  N. Owen‐Smith,et al.  Distributional niche of relatively rare sable antelope in a South African savanna: habitat versus biotic relationships , 2013 .

[6]  G. Asner,et al.  Spatial patterns in the effects of fire on savanna vegetation three-dimensional structure. , 2012, Ecological applications : a publication of the Ecological Society of America.

[7]  Changing distributions of larger ungulates in the Kruger National Park from ecological aerial survey data , 2012 .

[8]  N. Owen‐Smith,et al.  Habitat and resource partitioning between abundant and relatively rare grazing ungulates , 2012 .

[9]  N. Owen‐Smith,et al.  Shrinking sable antelope numbers in Kruger National Park: what is suppressing population recovery? , 2012 .

[10]  Izak P J Smit,et al.  Effects of fire on woody vegetation structure in African savanna. , 2010, Ecological applications : a publication of the Ecological Society of America.

[11]  N. Owen‐Smith,et al.  The importance of post-fire regrowth for sable antelope in a Southern African savanna , 2009 .

[12]  David E. Knapp,et al.  The relative influence of fire and herbivory on savanna three-dimensional vegetation structure. , 2009 .

[13]  Roberta E. Martin,et al.  Large-scale impacts of herbivores on the structural diversity of African savannas , 2009, Proceedings of the National Academy of Sciences.

[14]  B. W. Wilgen,et al.  An assessment of the implementation and outcomes of recent changes to fire management in the Kruger National Park , 2008 .

[15]  F. Ludwig,et al.  Improved quality of beneath-canopy grass in South African savannas: Local and seasonal variation , 2008 .

[16]  N. Owen‐Smith,et al.  Shifting prey selection generates contrasting herbivore dynamics within a large-mammal predator-prey web. , 2008, Ecology.

[17]  R. Sikes,et al.  Guidelines of the American Society of Mammalogists for the Use of Wild Mammals in Research , 2007 .

[18]  Roberta E. Martin,et al.  Carnegie Airborne Observatory: in-flight fusion of hyperspectral imaging and waveform light detection and ranging for three-dimensional studies of ecosystems , 2007 .

[19]  N. Owen‐Smith,et al.  Manifold interactive influences on the population dynamics of a multispecies ungulate assemblage , 2006 .

[20]  Jorge Soberón,et al.  Global Mammal Conservation: What Must We Manage? , 2005, Science.

[21]  Craig Packer,et al.  Planning for success: Serengeti lions seek prey accessibility rather than abundance , 2005 .

[22]  W. Bond,et al.  SHAPING THE LANDSCAPE: FIRE–GRAZER INTERACTIONS IN AN AFRICAN SAVANNA , 2005 .

[23]  B. W. Wilgen,et al.  Response of Savanna Fire Regimes to Changing Fire‐Management Policies in a Large African National Park , 2004 .

[24]  A. Sinclair,et al.  Can parks protect migratory ungulates? The case of the Serengeti wildebeest , 2004 .

[25]  J. Ogutu,et al.  ENSO, rainfall and temperature influences on extreme population declines among African savanna ungulates , 2003 .

[26]  M. Rietkerk,et al.  EFFECTS OF FIRE AND HERBIVORY ON THE STABILITY OF SAVANNA ECOSYSTEMS , 2003 .

[27]  Harry Biggs,et al.  Factors affecting the hunting success of male and female lions in the Kruger National Park , 2001 .

[28]  W. Cohen,et al.  Surface lidar remote sensing of basal area and biomass in deciduous forests of eastern Maryland, USA , 1999 .

[29]  H. Biggs,et al.  Long-term changes in the woody vegetation of the Kruger National Park, with special reference to the effects of elephants and fire , 1998 .

[30]  W. Gertenbach,et al.  Landscapes of the Kruger National Park , 1983 .

[31]  J. Grobler Feeding behaviour of sable Hippotragus niger niger (Harris, 1838) in the Rhodes Matopos National Park, Zimbabwe , 1981 .