Population genetic structure of European wildcats inhabiting the area between the Dinaric Alps and the Scardo-Pindic mountains

Habitat fragmentation and loss have contributed significantly to the demographic decline of European wildcat populations and hybridization with domestic cats poses a threat to the loss of genetic purity of the species. In this study we used microsatellite markers to analyse genetic variation and structure of the wildcat populations from the area between the Dinaric Alps and the Scardo-Pindic mountains in Slovenia, Croatia, Serbia and North Macedonia. We also investigated hybridisation between populations of wildcats and domestic cats in the area. One hundred and thirteen samples from free-leaving European wildcats and thirty-two samples from domestic cats were analysed. Allelic richness across populations ranged from 3.61 to 3.98. The observed Ho values ranged between 0.57 and 0.71. The global FST value for the four populations was 0.080 (95% CI 0.056–0.109) and differed significantly from zero (P < 0.001). The highest FST value was observed between the populations North Macedonia and Slovenia and the lowest between Slovenia and Croatia. We also found a signal for the existence of isolation by distance between populations. Our results showed that wildcats are divided in two genetic clusters largely consistent with a geographic division into a genetically diverse northern group (Slovenia, Croatia) and genetically eroded south-eastern group (Serbia, N. Macedonia). Hybridisation rate between wildcats and domestic cats varied between 13% and 52% across the regions.

First Description of Sarcoptic Mange in a Free-Ranging European Wildcat (Felis silvestris silvestris) from Spain

Sarcoptic mange caused by the mite Sarcoptes scabiei is a worldwide-distributed skin infestation with a wide range of hosts, among them several species within the Felidae family. Sarcoptes scabiei was diagnosed in a dead adult female European wildcat (Felis silvestris silvestris) from Spain, based on histological evaluation of skin biopsies and identification of the arthropod from skin scrapings and molecular methods. This is the first description of Sarcoptes scabiei in a European wildcat. Due to its critical demography in the southernmost population of the Iberian Peninsula, the impacts of infectious diseases, including sarcoptic mange, as a new potential threat should be considered during disease surveillance programs of the species’ populations.

Endoparasites of European Wildcats (Felis silvestris) in Greece

The European wildcat (Felis silvestris) is the only wild felid living in Greece. Wildcat populations are declining due to anthropogenic and phenological unfavourable conditions, and parasites may have an additional negative impact. In the present study, the occurrence of endoparasites in wildcats in Greece and the potential threats posed to wildcats, domestic animals, and humans in the study areas has been investigated. In a six-year period, 23 road-killed wildcats and 62 wildcat faecal samples were collected from different areas of the country. Necropsy for the detection of endoparasites and standard parasitological examinations of faecal samples were performed. Parasites were morphologically identified and, in selected cases, molecularly analysed. All necropsied wildcats (100%) were infected by three to 10 different parasite taxa, with the most prevalent being Taenia taeniaeformis (73.9%), Toxocara cati (60.9%), Angiostrongylus chabaudi (56.5%), Ancylostoma tubaeforme (39.1%), Cylicospirura spp. (34.8%), Troglostrongylus brevior (34.8%), and Capillaria aerophila (33.8%). Of the 62 faecal samples examined, 53 (85.5%) were positive for one or more parasite elements (larvae, eggs, or oocysts). The most frequent were T. cati (45.2%), A. chabaudi (29%), C. aerophila (24.2%), and Ancylostomatidae (17.7%). This is the first survey on endoparasites affecting wildcats in Greece. Some of the parasites here found are frequent in domestic and wild felids, while others, i.e., Oslerus rostratus and Cylicospirura petrowi, were described for the first time in the European wildcat. Most of them have a significant pathogenic potential, causing severe to hazardous diseases to infected felids and some, under specific circumstances, can also threaten human health.

Population genetic structure of European wildcats inhabiting the area between the Dinaric Alps and the Scardo-Pindic mountains

Habitat fragmentation and loss have contributed significantly to the demographic decline of European wildcat populations and hybridization with domestic cats poses a threat to the loss of genetic purity of the species. In this study we used microsatellite markers to analyse genetic variation and structure of the wildcat populations from the area between the Dinaric Alps and the Scardo-Pindic mountains in Slovenia, Croatia, Serbia and North Macedonia. We also investigated hybridisation between populations of wildcats and domestic cats in the area. One hundred and thirteen samples from free-leaving European wildcats and thirty-two samples from domestic cats were analysed. Allelic richness across populations ranged from 3.61 to 3.98. The observed Ho values ranged between 0.57 and 0.71. The global FST value for the four populations was 0.080 (95% CI 0.056–0.109) and differed significantly from zero (P < 0.001). The highest FST value was observed between the populations North Macedonia and Slovenia and the lowest between Slovenia and Croatia. We also found a signal for the existence of isolation by distance between populations. Our results showed that wildcats are divided in two genetic clusters largely consistent with a geographic division into a genetically diverse northern group (Slovenia, Croatia) and genetically eroded south-eastern group (Serbia, N. Macedonia). Hybridisation rate between wildcats and domestic cats varied between 13% and 52% across the regions.

Genetic consequences of reintroduction in two elusive European felids

Genetic and genomic tools have provided researchers with the opportunity to address fundamental questions regarding the reintroduction of species into their historical range with greater precision than ever before. Reintroduction has been employed as a conservation method to return locally extinct species to their native range for decades. However, it remains unknown how genetic factors may impact population establishment and persistence at the population and metapopulation level in the short- and long-term. Genetic methods are capable of producing datasets from many individuals, even when only low quality DNA can be collected. These methods offer an avenue to investigate unanswered questions in reintroduction biology, which is vital to provide evidence based management strategies for future projects. The Eurasian lynx (Lynx lynx) and European wildcat (Felis silvestris) are elusive carnivores native to Eurasia and have been the subject of multiple reintroduction attempts into their native range. During the 19th and 20th century, the Eurasian lynx was extirpated from West and Central Europe due to increasing habitat fragmentation and persecution. Similarly, the European wildcat was the subject of human persecution, residing in a few refugia in West and Central Europe. After legal protection in the 1950s, subsequent reintroduction projects of both species began in the 1970s and 1980s and continue to the present. Despite this large focus on species conservation, little attention has been given to the consequences these reintroductions have on the genetic composition of the reintroduced populations and if the populations have a chance of persisting in the long term. These species have not yet benefited from the large range of genetic and genomic techniques currently available to non-model organisms, leaving many fundamental aspects of their reintroduction poorly understood. In my dissertation, I investigate demography, population structure, genetic diversity and inbreeding at the population and metapopulation level in both species. In the introduction, which lays the foundation for the subsequent chapters of this PHD, I provide background on reintroduction, its role in conservation and the genetic consequences on populations, especially populations of apex and mesocarnivores. In Publication I, I investigated the reemergence of the European wildcat in a low mountain region in Germany using fine-scale spatial analysis. I found that the reintroduced population has persisted and merged with an expanding natural population. The reintroduced population showed no genetic differentiation from the natural population suggesting there is a good chance this population has retained sufficient genetic diversity despite reintroduction. In Publication II, I tracked population development and genetic diversity over 15 years in a reintroduced lynx population to determine the genetic ramifications on a temporal scale. I found slow genetic erosion after a period of outbreeding, which fits in line with other reintroduced taxa sharing similar demographic histories. I also found the number of genetic founders to be a fraction of the total released individuals, indicating that reintroduced populations of elusive carnivores may have fewer founder individuals than previously thought. In Publication III, I sampled all surviving lynx reintroductions in West and Central Europe as well as 11 natural populations to compare levels of genetic diversity and inbreeding across the species distribution. I found that all reintroduced populations have lower genetic variability and higher inbreeding than natural populations, which urgently requires further translocations to mitigate possible negative consequences. These translocations could stem from other reintroduced populations or from surrounding natural populations. The results contribute to a growing body of evidence indicating that inbreeding is likely to be more prevalent in wild populations than previously understood. Finally, in the discussion I explore how genetic methods can be applied to post-reintroduction monitoring of felid species to illuminate questions relating to genetic composition after release. The methods employed in these studies and in future work will be highly dependent on the research questions posed. Additionally, I investigate the drivers of the observed genetic patterns including founder size, source population, environmental factors, and population growth. I found that genetic diversity loss patterns across these two felid species are not clearly defined, however, management actions can be taken to mitigate the negative effects of reintroductions. These management actions include further translocation, introducing a sufficient number of released individuals and situating reintroductions adjacent to natural populations. All of these actions can minimize genetic drift and inbreeding, two factors which negatively impact small populations. This thesis further supports mounting evidence that genetic considerations should be assessed before releasing individuals, which allows for incorporation of scientific evidence into the planning process thereby increasing the overall success of reintroduction projects. Ultimately, the resources developed during this dissertation provide a solid baseline and foundation for future work regarding the consequences of reintroductions. This is especially important as an increasing number of species are at risk of extinction and reintroductions of both the European wildcat and Eurasian lynx, as well as many others, are planned in the coming years.