Disturbance and Habitat Factors in a Small Reserve: Space use by Establishing Black Rhinoceros (Diceros bicornis)

2014 ◽  
Vol 44 (2) ◽  
pp. 148-160 ◽  
Author(s):  
Karen Odendaal-Holmes ◽  
Jason P. Marshal ◽  
Francesca Parrini
1967 ◽  
Vol 101 (920) ◽  
pp. 357-358 ◽  
Author(s):  
David A. Hungerford ◽  
H. Sharat Chandra ◽  
Robert L. Snyder

1964 ◽  
Vol 38 (1-2) ◽  
pp. 171-174 ◽  
Author(s):  
J. G. Tremlett

In South Africa, a filarioid infestation has been associated with lesions in the skin of the black rhinoceros (Schulz and Kluge, 1960). Similar lesions had been reported earlier from Kenya, as consistently occurring in these animals but their aetiology was unknown (Spinage, 1960). Recently the opportunity occurred to examine lesion material from four black rhinoceros located in the Royal Tsavo National Park Kenya. From this material adult helminths were recovered and identified (Round, 1964), and further pathological studies made. In addition, one rhinoceros showed evidence of an otitis.


2018 ◽  
Vol 57 (2) ◽  
pp. 268-269
Author(s):  
Peter R. Law ◽  
Zoe C. Jewell ◽  
Sky K. Alibhai

SLEEP ◽  
2012 ◽  
Vol 35 (11) ◽  
pp. 1569-1574 ◽  
Author(s):  
Rachel Santymire ◽  
Jordana Meyer ◽  
Elizabeth W. Freeman

1988 ◽  
Vol 24 (3) ◽  
pp. 547-550 ◽  
Author(s):  
Ellen S. Dierenfeld ◽  
Raoul du Toit ◽  
R. Eric Miller

2012 ◽  
Vol 43 (3s) ◽  
pp. S48-S54 ◽  
Author(s):  
Stephane F. Helary ◽  
Joanne A. Shaw ◽  
Derek Brown ◽  
Marcus Clauss ◽  
Norman Owen-Smith

Koedoe ◽  
2017 ◽  
Vol 59 (1) ◽  
Author(s):  
Zoliswa N. Nhleko ◽  
Dan M. Parker ◽  
Dave J. Druce

Black rhinoceroses (Diceros bicornis) are endangered and the southern-central sub-species (Diceros bicornis minor) is considered critically endangered. We assessed the reproductive lifehistories of black rhinoceroses in Hluhluwe–iMfolozi Park (HiP), KwaZulu-Natal, South Africa, to determine whether this historically important donor sub-population was meeting regional reproductive targets. Detailed life-history information for known individuals (n = 79–120) was used to investigate reproductive parameters between 1998 and 2013. Mean age at sexual maturity was 12 years, which exceeded a target period of 7 years and 5 months. The mean inter-calving interval was 3 years and 8 months – 8 months longer than the recommended 3 years. The poor population performance of the HiP black rhinoceroses could be a result of poor habitat quality, poor animal condition, females losing their first calves, predation of calves or a negative social effect of annual live-harvesting of the population. However, we believe that the estimated ecological carrying capacity of black rhinoceroses at HiP (a figure used to ascertain whether the population can be harvested at all) may be incorrect, leading to the poor reproductive performance. We recommend that the accuracy of the ecological carrying capacity estimate be assessed as a matter of urgency and that a moratorium be placed on the live-harvesting of individuals until the estimate has been refined.Conservation implications: Our results provide key data which can be used to refine black rhinoceros breeding targets in South Africa and the region more broadly


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