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Laikipia Hartebeest: Exactly what are we attempting to conserve?
Nicholas Georgiadis and Collins OumaMpala Research Centre
RESULTS
We found only subtle genetic differences between hartebeest with Lelwel morphology (in Laikipia and Ruma NP) and those with Cokes morphology (in Naivasha, Meru NP, Nairobi NP, the Mara-Serengeti, and Ngorongoro), and the genetic transition between them appeared seamless. This was surprising because morphological differences between the two are striking, even over distances as short as 100 km (Fig. 1).
Previous analyses have suggested that different hartebeest forms in Africa diverged over the last two hundred thousand years when climate changes triggered continent-wide habitat shifts, ‘temporarily’ confining separate hartebeest populations to isolated savanna patches. Our results agree with this scenario, but further suggest that Cokes and Lelwel subsequently re-contacted each other and interbred, presumably after the climate cycle reversed, and hartebeest spread as the savannas expanded once more. As a result, the populations in Laikipia, Ruma NP, and Meru NP are all hybrid, but each has a subtly unique genetic makeup (Table 1) and morphology. The former two have greater affinities with Lelwel, the latter, at least morphologically, with Cokes. Despite their morphological similarities, the Meru NP hartebeest were not closely aligned with Cokes in Nairobi NP and Naivasha in the genetic sense (Fig. 3).
RATIONALE
Species’ geographical ranges are today so fragmented, it is often difficult to know whether remnant populations were once connected by dispersal and migration, or isolated by natural barriers. We need to know this information when action must be taken to conserve a species, for example, when individuals from one location are added to those in another. Fortunately, the required information can be reconstructed by analyzing patterns of genetic variation that is encoded in the DNA of individuals from different locations. We used this approach to examine the genetic makeup of hartebeest in Laikipia, asking, Exactly what, in the evolutionary sense, are we attempting to conserve?
HORN SHAPES AND SAMPLING LOCATIONS
For a century hartebeest in this ecosystem have been known to be morphologically ‘different’ from hartebeest elsewhere (Fig. 1). They have been variously referred to as ‘Laikipia’, ‘Jackson’s’, ‘Kenya’, or ‘Lelwel’ hartebeest, but rarely with formal reference or definition. Many resemble true Lelwel hartebeest, with robust horns that stand upright then sweep backwards, but there is broad variation in horn shape and size. Lelwel hartebeest were once distributed between central Kenya and the Central African Republic, but persist today in highly fragmented remnants (Fig. 2). Hartebeest in Laikipia have long been considered to be hybrid between Lelwel and Cokes hartebeest, the common form in southern Kenya and northern Tanzania.
Collecting samples with biopsy darts, from dung, and from incidental mortality, we compared the genetic makeup of hartebeest in Laikipia with those in Ruma NP, Meru NP, Naivasha, Nairobi NP, Mara-Serengeti NP, Ngorongoro, and elsewhere in Africa, using both mitochondrial DNA sequences and nuclear (microsatellite) markers.
CONSERVATION IMPLICATIONSA conventional approach to conserving hartebeest might aim to preserve or restore populations wherever they occurred naturally, particularly in protected areas. A more contemporary approach would attempt to conserve or even recreate the fragmented and diverse remnants of intricate evolutionary processes that have been operating over vast space and time, such as the one described here involving hybridization between different hartebeest forms. For example, dwindling numbers in Meru NP prompted conservation managers to propose supplementing the Meru hartebeest with individuals imported from elsewhere. Similarities in gross morphology might suggest a suitable source population to be Naivasha or Nairobi NP. A preferable strategy would aim to conserve the evolutionary products of hybridization by breeding up the remaining individuals at Meru in a large, predator-free area. If supplementation from elsewhere becomes mandatory, the goal would be to maintain a population with hybrid characteristics.
The Laikipia population is also declining and is nowhere formally protected. A strategic plan should be designed to conserve the remaining hartebeest in Laikipia, particularly those in Solio Ranch in the extreme south, which holds by far the highest densities (if necessary, moving them elsewhere in Laikipia or beyond, but still retaining their identity). Similarly, suitable alternative refuges should be identified to keep the Ruma NP hartebeest intact, should this protected area not survive extreme pressures from surrounding humanity.
In Kenya there has been little unnatural mixing of wildlife populations by translocation, so opportunities to define and conserve ongoing evolutionary processes persist, and should be strenuously pursued. As this project has shown, the relevant research can be achieved by Kenyans through collaborations among national and international partners, in this case Mpala Research Centre, Kenyatta University, the Kenya Wildlife Service, the International Livestock Research Institute in Nairobi, and the Laboratory of Genomic Diversity in Maryland.
THANKS TO: Our collaborators were Drs. Al Roca, Olivier Hanotte, Nick Oguge, and Joel Ochieng. We thank Dr. Oystein Flagstad, Nasser Olwero, Tee Taylor, Robert Mills, Edward Parfet, Joseph Kioko, Dr. Richard Bagine, and KWS staff in Nakuru, Ruma and Nairobi NP’s. The project was supported by the Whitley Foundation, Lincoln Park Zoo, St. Louis Zoo, Mpala Wildlife Foundation, African Wildlife Foundation, Nancy and Lambeth Townsend, and Joan and Robert Weiss.
Nairobi NP
Meru NP
Laikipia District
Ruma NP
Fig. 1. Variation in hartebeest horn shape among the focal populations. Note the similarity between Nairobi (A. b. cokei) and Meru NP, and the hybrid appearance of Laikipia hartebeest.
Fig. 2. Distribution of hartebeest in Africa, with different symbols denoting different morphotypes. Symbols are filled grey if previously published mtDNA sequences from that location were used in this analysis, and black where new populations were added by this study.
Fig. 3. Cluster diagram of focal hartebeest populations based on genetic (microsatellite) similarities. Numbers represent % bootstrap values, an index of confidence in the robustness of each node. Fig. 4. Mitochondrial DNA genealogy of
hartebeest, colour-coded by morphotype: cokei (yellow), lelwel (blue), swaynei (light green), tora (dark green), and major (red). Southern African hartebeest (lichtensteini and caama) were used as outgroups.
Ngorongoro
Serengeti NP
Naivasha
Nairobi
LaikipiaRuma NP
Meru NP
cokei796H79-LAIK
H8-NAIVH34-NAIR
cokei747H20-LAIK
H13-RUMAH32-RUMA-s
H69-LAIKcokei748
swaynei10swaynei9
swaynei13swaynei7
swaynei8swaynei45
swaynei5swaynei6
cokei794H61-SERO
H54-SEROH43-NAIR
H7-NAIVcokei800
cokei786H5-SERO
H58-NAIVcokei797
H57-NAIVcokei35
cokei789cokei783H2-NGOR
cokei798
H27-NGORH12-NAIV
cokei802cokei792
cokei790cokei803
cokei804H9-NAIVcokei46cokei806
cokei809cokei807
cokei791
H3-SEROcokei795
cokei787lelwel3
lelwel44lelwel727
lelwel730neumanni
lelwel729tora78
major57lelwel72
tora33swaynei68
lelwel32
lelwel42lelwel73
lelwel4major79
lelwel41
lelwel43H18-LAIK
H17-LAIKH76-LAIK-s
lelwel74H1-SERO
cokei784lelwel2
lelwel726lelwel728
tora76tora532
tora75swaynei815
swaynei1swaynei2
swaynei3swaynei23swaynei4
swaynei12
somaliswaynei11
swaynei14major731
major746major735
major734major736
major7major732
buselaphusmajor6
major58liecht757liecht754
caama723
0.01 substitutions/site
Table 1. Values of Fst, an index of the degree to which pairs of populations are genetically subdivided (on a scale of 0-1), based on mitochondrial (below diagonal) and microsatellite data (above diagonal). Asterisks indicate values significantly greater than 0.