versión On-line ISSN 2071-0771
versión impresa ISSN 0075-6458
Koedoe vol.56 no.1 Cape Town ene. 2014
Kerry SlaterI Konrad MullerII
IDepartment of Environmental Sciences, University of South Africa, South Africa
IIShamwari Game Reserve, Eastern Cape, South Africa
Brown hyaenas (Hyaena brunnea) were introduced to Shamwari Game Reserve in the Eastern Cape Province during 2002, but their feeding ecology is poorly understood. Feeding observations of brown hyaena by field guides and the collection of 31 scats from the study area took place over an 11 month period. Standard techniques were used to analyse the scats and identify prey items present. Ten dietary categories were identified from the scats, with a mean of 3.2 dietary categories per scat. Large mammal remains were found in 30 of the 31 scats, with kudu being the most abundant (61.0% of scats). Overall the two methods indicated at least 14 mammal species being fed on by the brown hyaena. The presence of mainly large mammal remains and invertebrates (in 38.7% of all scats), together with the feeding observations of mainly large mammals by field guides, suggests that brown hyaena in Shamwari are mainly scavengers and that sufficient carrion is available, thereby reducing the need for them to hunt. A 52.0% occurrence of plant matter was found in the scats, suggesting that plant material is an important component of their diet. Further studies are underway to investigate the feeding ecology of brown hyaena in Shamwari and surrounding areas.
CONSERVATION IMPLICATIONS: Comprehensive scat analysis over a number of years, monitoring of individual movement patterns and population numbers of brown hyaena in and around conservation areas will be beneficial in quantifying resource use of this species.
Investigating the diet of free-ranging animals provides information of resources available to and utilised by these animals, but this information is not always available to wildlife area managers because of constraints on time-consuming field work. The diet of a carnivore is a reflection of its feeding type (specialist or opportunistic), the availability of its potential prey and its morphological, behavioural and physiological adaptations (Kok & Nel 2004).
Previous studies on brown hyaenas (Hyaena brunnea) have shown it to have a diverse diet and, although primarily a scavenger of mammals, it also forages for insects, reptiles, birds and their eggs, and plants (Burgener & Gusset 2003; Kuhn, Wiesel & Skinner 2008; Maude 2005; Mills & Mills 1978; Owens & Owens 1978; Skinner 1976; Skinner & Chimimba 2005; Skinner & Van Aarde 1981; Van der Merwe et al. 2009). Despite being generalist feeders, they appear to lean towards specific prey items depending on their habitat. For example, in the southern Kalahari, 58 different food types were identified in faecal samples (Mills & Mills 1978), but along the Namib Desert coast, the bulk of the brown hyaena's diet is Cape fur seals (Arctocephalus pusillus) (Goss 1986; Kuhn et al. 2008; Siegfried 1984; Skinner & Van Aarde 1981). Brown hyaenas are inefficient predators and food obtained by hunting is rare (Mills & Mills 1978). In the southern Kalahari, only 4.7% of hunting attempts were successful and those vertebrates hunted successfully made up only 4.2% of the total vertebrate diet (Mills 1978). Vertebrates hunted were also of small sizes and included birds such as korhaan (Eupodotis sp.), small mammals such as springbok lamb (Antidorcus marsupilis), springhare (Pedetes capensis), striped polecat (Ictonyx striatus) and bat-eared fox (Otocyon megalotis) (Mills 1990). Along the Namib coast, between 2.9% (Goss 1986) and 9.6% (Wiesel 2010) of the Cape fur seal pups eaten were killed by the brown hyaenas themselves. In areas where brown hyaena ranges overlap with agricultural lands (Skinner 1976; Skinner & Van Aarde 1981) or human settlements (Kuhn et al. 2008), remains of domestic dogs, cats, cattle, goats, sheep, horses and donkeys (Maude 2005) have been found in their faecal scats.
Brown hyaenas are sparsely distributed over the arid and semi-arid regions of southern Africa (Mills & Hofer 1998). Owing to the shy behaviour of this animal, only a handful of papers report on their diet and are mainly restricted to arid areas. There is therefore generally a lack of this information in most of their distribution range.
During the early 1990s, the Eastern Cape Province transformed large areas of agriculture to more economically viable game farming, ecotourism and conservation areas (Hayward et al. 2007). This change in land use led to numerous wildlife species being reintroduced to former domestic livestock farms. These reintroductions included large predator species that had historically occurred in the eastern Cape region, with the main aim of these reintroductions being to restore ecological integrity, conserve threatened species and maximise ecotourism (Hayward et al. 2007). Although translocation of large carnivores is common, there is often very little or no post-release monitoring (Hofmeyer & Van Dyk 1998).
Research method and design
This article describes a preliminary study on the diet of brown hyaenas at Shamwari Game Reserve in South Africa's Eastern Cape Province (33°25'40''S, 26°05'32''E). Shamwari is approximately 25 000 ha, traversing four geological formations (i.e. Bokkeveld series shale, Witteberg quartzite, Karoo sandstone and Sundays River formations) (O'Brien 2004). Vegetation types in Shamwari include: Kowie Thicket, Bhisho Thornveld, Suurberg Quartzite Fynbos and Suurberg Shale Fynbos (Mucina & Rutherford 2006). Shamwari is situated in the spring-dominant rainfall region of the province and receives about 550 mm of rainfall per annum (Low & Rebelo 1996; Stone, Weaver & West 1998). Permanent water is available in the semi-perrenial Bushman's River that flows through the reserve for 27.6 km and there are a number of small earth dams.
Carnivores that have been reintroduced to Shamwari include cheetah, leopard, lion, serval, African wild dog and brown hyaena. Historical records indicate that brown hyaenas had not been seen in the eastern Cape region since the 1960s (Hayward et al. 2007). During 2002, two adult male and four adult female brown hyaenas wild caught from Northern Cape Province farms were reintroduced to the reserve and, by 2004, an estimated population of 15 hyaenas could be found in Shamwari. During 2007, seven adults and sub-adults were relocated from Shamwari to other Eastern Cape reserves. Despite this apparent success of reintroducing brown hyaenas into Shamwari, no detailed study on their diet has been conducted.
Data on feeding observations of brown hyaenas documented by field guides whilst out on game drives with guests were collected between April 2008 and June 2009 (Figure 1). These recordings included the date, species being fed on, size and any other related information. Thirty-one fresh faecal scats were also collected from 11 latrines throughout the study area between April 2008 and May 2009 (Figure 2). Dried scats were placed into a nylon netting envelope and rinsed with warm water to loosen the hair and other objects trapped inside. The scats were dissected manually and all hair samples were removed. A representative sample was selected for analysis by inspecting all the hairs visually from each faecal scat and selecting at least one hair for each size, thickness, shape, colour and length (Maude 2005). This increased the chances of identifying all mammal species represented by hair in each faecal sample. A scale imprint was made of each hair sample by placing the hair onto a glass slide that was covered with liquid gelatine. Once the gelatine had dried, the hair was removed from the slide leaving the imprint of the hair's scale on the slide. Each hair sample was placed into the front section of a Pasteur pipette. Wax was melted and sucked up into the pipette and then dipped into cold water to solidify the wax. A cross-section of the hair was made by cutting the front end of the pipette into small slices with a surgical blade. The size and shape of the medulla and cortex of each cross-section, together with the scale imprints, were used to identify mammal species represented in each sample from reference material (Keogh 1983; Maude 2005; Perrin & Campbell 1980). Samples from mammal species occurring in the reserve were also used to make up a reference key (see Appendix 1). Remains of insects, reptiles, fruit, bone, hair, feathers and any other objects were identified by manually sorting through the faecal scats.
Dietary diversity (H) was calculated from the scats using the Brillouin index and the cumulative diversity (Hk) was plotted against the number of scats to determine if the brown hyaenas diet had been adequately sampled (Glen & Dickman 2006). The percentage occurrence of each prey item or species in the total number of scats was calculated as an indication of how frequently the hyaenas fed on each dietary component (Loveridge & Macdonald 2003). This was calculated by the number of scats containing a particular food item / total number of scats x 100. The relative percentage occurrence (number of times a specific food item was encountered / total number of occurrences of all food items x 100) indicated the importance of each food item to the overall diet (Loveridge & Macdonald 2003). A 95% confidence interval for both the percentage occurrence and the relative percentage occurrence were generated from 1000 bootstrap simulations (Andheria, Karanth & Kumar 2007).
Eighty-one feeding observations of brown hyaenas were made by field guides during the study period (Table 1). Fifty-seven (70.00%) of the feeding observations were of brown hyaenas feeding on large mammals, of which 62.00% were of Ruminantia or Perrisodactyla. During the observations these larger items were always carried away from the carcass to be eaten elsewhere. On one occasion, a female brown hyaena was observed carrying a large piece of a gemsbok for over 3 km during 30 min of observation. Twelve observations (14.80%) of brown hyena feeding on two white rhino carcasses that had been killed in a territorial dispute were made during the study period. A giraffe that had died of natural causes was observed being fed on by brown hyaenas eight times (9.88%). Of the total observations, 11.00% (five blesbok, one kudu and three springbok) were kills that brown hyaenas had stolen from cheetah. Brown hyaenas were also observed to kill and eat one leopard tortoise (Geochelone pardalis) and three angulate tortoises (Chersina angulata).
The use of a cumulative Brillouin index (Hk) indicated that the scat sample size of 31 scats was sufficient for brown hyaenas (Figure 3). We found a mean of 3.2 dietary categories per hyaena scat. Large mammal remains (> 10 kg) were found in 30 of the 31 scats and were clearly the most important dietary component for brown hyaenas (Table 2). Five species of large mammals were identified from the scats, with kudu being the most frequent, representing 61.0% occurrence in the diet. Blesbok and bushbuck contributed 58.1% and 41.9% to the brown hyaena's diet, respectively. Plains zebra contributed 29.0% and warthog 12.0% to diet. Overall, at least 14 mammal species were found to be included in the hyaena's diet, as well as a variety insects, reptiles, birds and plant material.
Brown hyaenas usually only hunt small mammals (Owens & Owens 1978) and therefore the high number of large mammals being observed to be eaten and the hair found in the faecal scats was more than likely indicative of these prey items having been scavenged. This study confirms the findings of other such studies where remains in brown hyaena scats were mainly from members of the order Ruminantia (Burgener & Gusset 2003; Van der Merwe et al. 2009). The low frequency of small species in this study may suggest that sufficient carrion is available due to the presence of other predators in the same area as the hyaenas, thereby reducing the need for them to hunt. Although the occurrence of plant material found in the scats (52%) is not as high as found in brown hyaenas living in arid areas (Mills & Mills 1978), plant material is still an important component of the diet for brown hyaenas in Shamwari. Invertebrates that were consumed were more likely ingested during feeding off carcasses.
This article represents the first documented study of the dietary habits of brown hyaenas in Shamwari Game Reserve in the Eastern Cape. Further studies are currently underway to explore the feeding ecology and the influence of apex predators on the scavenging behaviour of the brown hyaenas in Shamwari Game Reserve and surrounding areas.
We thank Shamwari Game Reserve for permission to conduct the project. Nadia Muller, Dr Murray Stokoe and the Shamwari Rangers Department assisted with logistics of the project.
The authors declare that they have no financial or personal relationships that may have inappropriately influenced them in writing this article.
K.M. (Shamwari Game Reserve) was responsible for data collection and the initial draft of the article. K.S. (University of South Africa) was the project supervisor, analysed the data and wrote the final article.
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Private Bag X6
Florida 1710, South Africa
Received: 05 Feb. 2013
Accepted: 18 Sept. 2013
Published: 28 Feb. 2014