Cytogenetics and the Health and Conservation of Wildlife

Steven C. Kingswood and Arlene T Kumamoto, Center for Reproduction of Endangered Species, Zoological Society of San Diego, POB 551, San Diego, CA 92112-0551, USA

Cytogenetics is the science of chromosome structure, function, behavior, and pathology. Chromosome investigations scan, at a gross level, the entire genome of an organism. In the field of human medicine, the involvement of chromosomes in diseases and developmental disorders is widely recognized by biologists and clinicians. For example, Down syndrome, Klinefelter's syndrome, and Turner's syndrome are but a few disorders in humans that are caused by chromosomal abnormalities (Verma & Babu, 1995; Batch et al., 1997). These abnormalities generally are the result of either gain, loss, or rearrangement of entire chromosomes or portions thereof. Techniques to diagnose chromosomal disorders in fetuses during early pregnancy have led to rapid growth of clinical human cytogenetics, and today, there are more than 400 laboratories worldwide that specialize in identification of chromosomal abnormalities (Knutsen & Rebolloso, 1998). In contrast, we estimate that only a handful of labs actively apply cytogenetics to the health and conservation of wildlife. Here, we will take an opportunity to review the role of cytogenetics in wildlife onservation and management, using as examples the results of some of our recent

Cytogenetic analyses are most effectively applied to problems of hybridization and species identification, but they can also be appropriate for some questions involving gene evolution, population structure and variation, and phylogeny (Hillis et al., 1996). The importance of cytogenetics to veterinary medicine and wildlife conservation lies with detecting numerical and structural chromosomal variation between and within populations, identifying chromosomally abnormal individuals and assessing potential reproductive fitness of heterozygotes. Reproductive consequences of chromosomal heterozygosity and hybridization can be determined with analysis of chromosomal configurations during meiosis.

Matings between chromosomally-different individuals can compromise reproduction in heterozygous progeny by increasing their mortality or reducing their fertility. Thus, if different geographical populations are distinguished by chromosomal rearrangements, then management practices, such as wildlife translocation, captive breeding, and reintroduction, might be jeopardized if specimens from these different populations are brought together (Benirschke & Kumamoto, 1991; Robinson & Elder, 1993). Furthermore, chromosomal rearrangements may be involved with protection of coadapted gene complexes (Sites & Moritz, 1987); consequently, well-intentioned conservation efforts involving chromosomally-distinct animals might inadvertently disrupt natural processes of evolution and speciation. Our cytogenetic research is largely focused on the mammalian family Bovidae, particularly the antelopes of Africa and Asia. Chromosome diploid (2n) numbers in antelopes and other bovids vary from 2n = 30 to 2n 60. Most of this variation is due to the rearrangement of chromosome arms through centric fusions, which involves fusion of two single-armed (acrocentric) chromosomes to produce a bi-armed (metacentric) chromosome. The evolutionary result of centric fusion is a decrease in the diploid number from that of the ancestor. Theoretically, centric fissions could produce two acrocentric chromosomes from one metacentric chromosome, resulting in an increase of the diploid number, but centric fusions are believed the dominant form of chromosomal evolution in the Bovidae (Gallagher & Womack, 1992).

Several species of antelopes are polymorphic for centric fusions, but the effect of these chromosomal rearrangements on reproduction seems to vary. In male goitered gazelles (Gazella subgutturosa), there is no indication that heterozygosity for a single centric fusion has a negative effect on meiosis (Kingswood et al., 1994). However, perinatal mortality rates of ca. 50-60% in Soemmerring's gazelles (G. soemmerringii) and 47-71% in suni (Neotragus moschatus) may be due to the captive breeding of chromosomally incompatible individuals. The polymorphisms in captive populations of suni and Soemmerring's gazelles, respectively, are the result of two and three centric fusions (Benirschke et al., 1984; Kingswood etal., 1998a).

Chromosomal variation in these two species of antelopes may reflect differences between geographical populations. For example, the captive-born sum in our study that are descendants of animals wild-caught at Mount Kenya (N. m. akeleyi) have 2n = 52 chromosomes, and those that are descendants of suni wildcaught in Natal, South Africa (N. m. zuluensis) have 2n = 56 chromosomes. The notion that populations of suni are chromosomally distinct, in spite of their phenotypic uniformity, exemplifies the importance of cytogenetics in identifying "management units," that is, populations experiencing such low levels of gene flow so as to function independently (Moritz, 1994).

In addition to the suni, our research has identified the Kirk's dik-dik (Madoqua kirkii) as another species of antelope in which geographic chromosomal differences exceed phenotypic differences, referred to as "cryptic chromosomal variation" by Robinson & Elder (1993). Populations of Kirk's dik-dik from eastern and south western Africa have chromosomal complements of 2n = 46-48. Unlike the chromosomal variation in other species of bovids, which appears predominated by cen tric fusions, cytogenetic differences between Kirk's dik-diks are the result of six other chromosomal rearrangements, including inversions, additions or deletions, a translocation, and a tandem fusion. The captive population of M. kirkii in North America, derived From Kenya and Tanzania, is characterized as having two cytognetic types, arbitrarily designated as cytotypes A and B. Hybridization between cytotypes A and B resulted in sterile male offspring; female off spring of such matings were fertile. Male sterility in cytotype A x B hybrids was presumably the result of impaired meiosis from one or a combination of the six rearrangements (Ryder et al., 1989; Kumamoto et al., 1994). East African populations of Kirk's dik-dik that are reproductively isolated, but not readily distinguish able morphologically, would by definition be cryptic species (Mayr, 1970). Unfortunately, lack of preciise information on the geographic origin of the captive population precludes reclassification of animals repre senting cytotypes A and B into separate species.

The difficulty of correlating cytogenetic data with geographic information is a common problem when studying captive populations. Cytogenetic studies of captive animals are further limited because they probably do not demonstrate the full range of chromosomal variation present in wild populations. This highlights the importance of documenting the cytogenetics of natural Populations of wildlife. Nevertheless, field chromosomes

are visible only during cell division (mitosis or meiosis), which occurs only in living, dividing cells of blood or tissue samples; thus, in attempting to collect samples from wild populations, the problem of quickly transporting live cells to a cytoenetic laboratory is one of the major challenges to chromosomal investigations. Samples utilized in molecular genetic studies, on the other hand, do not require live cells, and as a result, are easier to collect and process in the field.

We have had the opportunity to collect a few samples from two wild populations of antelopes for cytogenetic studies: Kirk's dik-dik in Namibia and waterbuck (Kobus ellipsiprymnus) in Kenya (Kumamoto et al., 1994; Kingswood et al., 1998b). Kirk's dik-diks in Namibia (2n = 48) are chromosomally different from the captive population derived from East Africa (2n = 46-47). Our waterbuck study, including the samples from Kenya and the captive population in North America, documented cytogenetic differences between the K e. ellipsipryTnus (Zn = 50-S2) and K e. defassa (2n = 53-54) subspecies groups. These data suggest to us that chromosomally- different populations of each species should be managed separately.

Because of the potentially deleterious effects of chromosomal heterozygosity on fertility, Benirschke & Kumamoto (1991) and Robinson & Elder (1993) sug gested that animals selected for captive breeding, rein troduction, or translocation projects be cytogenetically screened and grouped according to chromosomal compatibility. Potential application of cytogenetics to wildlife management and conservation is further implied by the IUCN/SSC Re-introduction Specialist Group !in proposing that individuals selected for rein troduction should be of the same taxonomic unit and, ideally, closely related genetically to those which were extirpated (Anonymous, 1992).

Taxonomic status of the Indian gazelle (G. bennettii) and Saudi gazelle (G. saudiya) was clarified with cytogenetic studies. These two species have been considered by some authors as beint. conspecific with either G. dorcas (2n = 30-31) or gazella (2n = 34-35). However, G. bennettii has 2n = 49-52 chromosomes and G. saudiya has 2n = 46-53 chromosomes, and the extent of their cytogenetic differences with G. dorcas and G. gazella indicates that they are reproductively isolated from both of these species (Furley et al., 1988; Rebholz etal., 1991; Kumamoto etal., 1995).

Quantitative analyses of cytogenetic differences can also be used to lend insight into taxonomic relationships above the species level. Among antelopes of the genus Damaliscus, for example, the number of centric fusions that distinguish the chromosomes of D. hunteri (2n = 44) from D. lynatus (2n = 36) and D. pygargus (2n = 38) supports separate placement of D. hunteri in the subgenus Beatragus, or possibly in the genus Beatragus, as has been suggested by some mammalogists (Kumamoto etal., 1996). D. hunten, commoril called the hirola, or Hunter's hartebeest, is one of the most endangered antelopes; a recent survey of this monotypic species estimated a total population of 300 animals. Given that measures of taxonomic distinctiveness are necessary to establish conservation priorities, the fact that D. hunteri is chromosomally quite different from other species of Damaliscus exemplifies the importance of using cytogenetic data to identify unique taxa.

As in clinical human cytogenetics, identification of chromosomally abnormal individuals is a useful tool for managing the reproductive health of an animal population. However, detection of chromosomal abnormali-

ties is predicated upon having documented "normal values" for each species. Insofar as we have just begun to scratch the surface of what is known about the chro mosomes of wild popluations, the real importance of cytogenetics to wildlife conservation and management