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Lion Management Fact Sheet HISTORY OF LION MANAGEMENT: In South Africa, lions had disappeared from most of their historical range, and have subsequently been reintroduced into smaller, fenced areas across the country This has resulted in several free-ranging populations that are isolated from one another in these smaller areas. Karoo NP is one such area. LION CONSERVATION MANAGEMENT The management of lions in Karoo NP forms part of a broader predator management approach for the Frontier Region and other smaller parks within SANParks. Management of carnivores in parks in the Frontier Cluster is guided by park-specific objectives primarily aiming at the conservation and promotion of the unique landscapes represented in four parks: Addo Elephant National Park, Karoo National Park, Mountain Zebra National Park and Camdeboo National Park Carnivore management in the Frontier Cluster encapsulates four key management aspects. 1. SANParks wishes to restore the ecological processes driven and influenced by large carnivores. 2. Restricted size and fragmentation of these Parks may accentuate localized carnivore impacts on prey as well as reduced genetic integrity of individuals living there. 3. Restricted park size may also accentuate predator conflicts with neighbours. 4. Given that the Frontier Cluster is a key wildlife viewing attraction apparently enhanced by large carnivores, a fourth aspect relates to how the absence or inconspicuousness of certain species may influence the Frontier Cluster’s capability of generating revenue through tourist experiences and expectations. The restoration and maintenance of predation is a key objective for SANParks in achieving ecosystem objectives. The main aim of the predator management plan is to restore the ecological role of large carnivores as apex predators in the terrestrial ecosystem, and has associated benefits for tourism The plan explicitly recognises that smaller, fenced parks pose particular constraints on predator management. For example: o smaller parks have lower/reduced habitat diversity and suitability, and hence lower species diversity of prey as well as predators; o fences limit dispersal and movement opportunities and can therefore often lead to artificially increased predator abundances through altered social dynamics; o these spatial constraints reduce the likelihood of normal predator-prey relationships, increase the likelihood that related individuals can breed with one another, and reduce the possibility of other normal social interactions between individuals In addition, the plan recognises that these issues are confounded by the expectations and attitudes of stakeholders, both positive (e.g. the assumption that the presence of large carnivores enhances a tourism experience) and negative (e.g. through livestock losses after breakouts), and tries to balance these by means of four primary objectives (see table at the end of this document) Overall, the management approach focuses on managing ecosystem processes, rather than on managing species based on defining a “carrying capacity” Specifically, the approach hinges on mimicking the natural behaviour around social dynamics of predators, including sex-specific dispersal events, dominance hierarchies, socially-induced reductions in birth rates, and socially-induced mortality events, all of which have been based on published scientific literature For example: o Female lions live in groups either to defend cubs from nomadic males, or to defend their territories from other groups o Defence is associated with conflicts with other lions and may induce stress and carry risk for individual survival o In small, confined areas, nomadic males are often absent and these areas often contain only one pride o The drivers of group living are therefore reduced in such small, confined areas, and it is predicted that mortality risks and social stress are weaker. Adult females lose body condition, and younger females that may never have bred may not be in adequate condition to do so, thereby increasing the age at first reproduction in larger areas. Coalition take-overs are a key driver of cub mortality, but cannot occur in areas with only one coalition. Therefore, To mimic the social dynamics of female lions, five management options are available: (i) increase the age at first reproduction using contraception of subadult females; (ii) establish longer intervals between births using contraception of adult females; (iii) reduce agespecific birth rates through reduced litter sizes using uni-lateral tubetying of fallopian tubes; (iv) mimic female dispersal by removing as well as introducing subadult females; (v) mimic higher death rates of old females by removing the oldest females in the pride. SANParks managers and scientists together use modelling approaches to define a particular combination of the five options to achieve an average pride size of four in smaller, fenced parks. o Similarly, three management options are available for males: (i) mimic male dispersal through removal and introductions of subadults; (ii) mimic pride take-overs by switching males with those from other populations of lions (tenure is on average three years); (iii) mimic higher death rates of old males by removing the oldest males. SANParks managers and scientists again use modelling approaches to identify individuals to achieve a coalition tenure of at least three years, allowing each coalition to have only one breeding opportunity. No active switching of coalitions may be required if subadult male introduction and removal of old males are staggered. A pride takeover should then follow naturally, with subsequent consequences for cub mortality. This systems-based approach provides opportunities for ecological processes to play out, restoring these ecological processes and/or mimicking the outcomes of ecological processes, including the maintenance of genetic variability. It also provides opportunities for improving the regional conservation of lions, through the switching of male coalitions and reintroduction of individuals The possibility of behavioural changes or other surprise or unexpected outcomes associated with this approach have been recognized, and have been structured as hypotheses for evaluating the consequences of a socially-based approach to carnivore management, embedded within SANParks’s Strategic Adaptive Management framework. Learning achieved by observing these outcomes is used to fine-tune future management interventions. This sophisticated approach to lion management is in line with contemporary scientific and conservation thinking, and is supported by the Lion Management Forum in South Africa. This approach has placed SANParks at the forefront of predator management internationally, with many conservation organisations following suit. Several peer-reviewed scientific papers are testimony to this KAROO NATIONAL PARK LIONS For Karoo NP, 4 adult (2 male and 2 female) and 4 juvenile (3 female, 1 male) lions were initially introduced from Addo Elephant NP in 2010. This group was subsequently supplemented by additional animals from different parentages (to maximize genetic integrity), as part of the mimicking of lion social dynamics and dispersal outlined above. Periodically introducing new males mimics the dispersal of new males into the population, thereby potentially leading to coalition swaps which happen in large systems like the Kgalagadi and Kruger National Park. In the process new genes are also brought into the population. It should also be noted that the size of the park is such that several numbers more of lions could be easily accommodated in the park. For example, two young males (about 2 years old at the time) were introduced in November 2012 as part of the Frontier cluster carnivore management plan. The lion (called Sylvester by the public) was born in the park to one of the original adult males, and one of the females who had been brought to Karoo NP from Addo Elephant National Park as a cub. He is a young dispersing male that has not been able to bond with another male because his only sibling was a sister and there were no other single males in the lion population in Karoo NP with which he could possibly form a coalition. This is not an unusual situation in the larger systems whose dynamics are being mimicked in Karoo NP. After the lion’s first escape, the park introduced another two lions in November of 2015. The decision to bring in these two lions was made solely on the basis of trying to provide the lion (Sylvester) with a coalition partner (they were only brought in after he was already in the boma after the first escape). Being a single, young male, there is every chance that, on leaving his mother and sister, Sylvester may have come into conflict with the other adult males present in the park by that time, and that this precipitated his desire to get as far away from them as possible. His ousting from the park was therefore most likely prompted by conflict with two older coalition males. However, this behaviour is not unexpected by the approach of mimicking lion social behaviour. Rather, it was facilitated by a small wash-away area underneath the boundary fence after heavy rains After his capture, he was fitted with a combination satellite/VHF collar to find his location should he manage to get out again He was kept in a boma for approximately 5 months in an attempt to keep him separated from any conflict from rival males while awaiting a potential coalition partner. Unfortunately this partner died under anaesthetic while having a collar fitted prior to releasing them from the boma. “Sylvester” was released from the boma nearly 4 months ago and no signs of conflict with other males was observed since then. He was observed during the aerial census in February 2016, feeding on an eland that he had brought down by himself and was in good condition. His latest escape was detected by means of the regular monitoring of his satellite collar, and a helicopter and SANParks veterinarian were immediately dispatched to immobilise him while various options for his future could be considered (these options were outlined in the SANParks press release of 30 March 2016). Carnivore management objectives for the Frontier Region. Objective 1 To restore the large carnivore species assemblages typical of the Frontier Region by mimicking the re-colonization of Addo, Karoo and Mountain Zebra through species introductions Objective 2 To maintain sustainable predator-prey relations by inducing social limitations through: Mimicking changes in carnivore survival associated with social stress and prey biomass limitations Mimicking changes in carnivore fecundity by increasing the age of first reproduction and/or interval between births Mimicking high mortality in young cubs and old individuals Objective 3 To maintain carnivore genetic integrity by inducing social limitations through dispersal and changes in dominance hierarchies. Objective 4 To align and manage the carnivore management programme with stakeholder and affected parties’ expectations and concerns where appropriate Objective 5 To evaluate, inform and revise carnivore management through collaborative research and monitoring agreements