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Jones, A.L.
The potential overlap in habitat space of caracal (Caracal caracal) and blue duiker (Philantomba monticola) in KwaZulu-Natal, South Africa: an environmental niche modelling approach
2016  Full Book

I compiled a comprehensive occurrence database for caracal and blue duiker using historical data, recent sightings and survey responses from conservancies and protected areas throughout KZN. I then used niche-based environmental models (Maxent) to map the potential suitable habitat space of caracal and blue duiker, based on the occurrence data and different combinations of environmental and human impact variables. I calculated two niche overlap indices to quantify habitat niche overlap and compared these to 1000 expected overlap indices in a null model to test for niche equivalence. After spatial filtering, my database comprised 94 caracal and 90 blue duiker occurrence points for 1994 to 2013. For both species, vegetation biome, specifically forests, was the most important variable, with rainfall second most important. Approximately two-thirds of KZN was moderate to highly suitable habitat for caracal and one third was moderate to highly suitable habitat for blue duiker. The potential suitable habitat maps matched mostly with published distribution ranges for both species. Nonetheless, occurrence data within comparably lower habitat suitability, suggest caracal may have expanded their range further towards the north east of the province. The niche overlap scores were considerably high (_D _= 0.683 and _I _= 0.924), yet the caracal and blue duiker niche models were not identical, which can be expected of a generalist carnivore with a broad niche compared to the narrow niche of a specialist herbivore. At the highest threshold of habitat suitability the overlap between caracal and blue duiker covered 7% of KZN with 20% of the overlap occurring in 70% of the forest biome. The overlap consisted primarily of a large region in the midlands, smaller regions in the south and forest patches throughout KZN. Human impact variables contributed much less to the models than environmental variables and although the negative impact was mostly < 10%, the effect was widespread over ~60% of KZN for both species. My results confirm that the caracal distribution range has expanded historically from the western highlands to the south coast of KZN and thus overlaps considerably with the blue duiker distribution range in the midlands and southern coastal forests. Although the proportion of blue duiker in caracal diet reported in studies elsewhere is low (5% or less), any new threat to a blue duiker population already under pressure from a variety of other threats, could lead to an irrecoverable decline. Thus further studies investigating the effects of the expanding caracal population on the diminishing blue duiker population and other vulnerable prey species are warranted.

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