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The measurements of scapula, pelvis, humerus, ulna, radius, tibia, femur, and the first three vertebrae of the adult wild cat Felis silvestris Schreber, 1777 from Bulgaria were used in this study. Considerable differences between the sexes were revealed at three levels of significance in most of the sizes of scapula, pelvis, and vertebrae. The males were bigger than the females. No significant differences were found in the limb bones, except in the length of the humerus. Widening of the female pelvis was not observed. The variability of the skeletal parts examined was found to be comparatively low for most of them.
The European wildcat Felis silvestris silvestris is one of the most endangered mammals in Poland. In 1954, when the Tatra National Park (TNP) was established in the highest part of the Polish Carpathians, the wildcat was considered a rare species but nevertheless present in this region. However, its occurrence was never properly recorded there. The aim of this study was to verify whether wildcats occur in the TNP using genetic methods to distinguish wildcats from domestic cats F. s. catus. Between March and May 2015, hair samples were collected from 40 lure sticks treated with valerian, a cat attractant, in a region of the park with presumed high habitat suitability for wildcats. Neither wildcats nor hybrids with domestic cats were identified using control region haplotype sequencing and analysis of different nuclear markers. However, thirteen samples indicating the presence of the domestic cat in the protected area were collected. The Bayesian clustering analyses of microsatellite and SNP genotypes revealed no evidence for any admixture with wildcats. While our study cannot prove the absence of wildcats in the study area, it strongly suggests that wildcats are at least very rare in the region and a continued rigorous monitoring is recommended.
Fourteen wildcats Felis siluestris silvestris Schreber, 1777 were trapped in winter 1993 in the southern part of the Swiss Jura Mountains as a bycatch. During the last thirty years of protection the presence of wildcats in Switzerland could be confirmed by a few dead-found individuals, but the status of the species was unknown. This is the first indication of an existing population. Even though the upper distribution limit of wildcats in central and western Europe is described at 800 m a.s.l., most individuals were caught in altitudes from 970 to 1200 m. We registered a higher catching success in south exposed beech forest and in the sycamore forest, than in the northern exposed Norway spruce forest. During snowcover above 30 cm no wildcats were caught. The capture sites were located within distances of 200-1900 m from human settlements.
Wildcats Felis silvestris Schreber, 1775 were captured for radio collaring as a part of a study of their spatial distribution and social organisation in southern Slovenia between 1999 and 2001. Double-door box traps, with a roof that bears easily break (bear permeable traps), have been used to capture individuals. The distances between traps were between 550 to 2200 m. They were set out on logging roads and narrow trails in the forest. Nine wildcats, one lynx Lynx lynx (Linnaeus, 1758) and one feral cat were caught as target species and 19 badgers Meles meles and one bear cub Ursus arctos as non-targets. The catching success was 1 wildcat/58 trap-days and seems to be in correlation with the lunar cycle. Overall, 7 males and 2 female wildcats were captured which might indicate sex biased trapping selection. Methodological improvements shortened the time of handling procedures. Improved field protocols as well as restraining and immobilisation procedures increased reliability and safety of drug administrations, decreased potential chances for injuries and reduced overall stress of captured animals.
The definition of the wildcat Felis silvestris Schreber, 1775 in Scotland is conten­tious, in light of long-term interbreeding with domestic cats F. catus Linnaeus, 1758. Two morphological groupings (Group 1 and Group 2) have previously been proposed to explain the variation found in wild-living cats in Scotland, with Group 1 cats closest to wildcats and Group 2 cats to domestic cats. Data from the reproductive tracts of 185 wild-living cat carcasses and evidence of reproductive activity in 31 live cats were analysed in order to compare reproductive activity between the morphological groups, and in relation to seasonality and existing data on wildcats and domestic cats. For males, Group 2 cats had a greater mean relative testes size than Group 1 cats. Estimated from corpora lutea, there was a suggestion that Group 1 females showed more seasonality in oestrous than Group 2 cats. In all wild-living cats, the mean litter size was 4.3 and estimated birth dates were throughout the year, but least in winter. A high number of pseudopregnancies were recorded. The results were consistent with the hypothesis that Group 2 cats are closer to domestic cats. However, the variation observed in the sample of wild-living cats reported here, suggested that reproduction was neither strictly seasonal nor outside the range observed in some feral cat popu­lations.
Analyses were made of 118 skull measurements of adult wild cats Felis silvestris Schreber, 1777 from Bulgaria, taken on 24 males, 20 females, and 10 animals whose sex was not known in advance. Group (cluster) analysis of cases, factor analysis, and stepvise discriminant analysis were adapted. The cluster analysis of cases indicated a high level of sex mixture (up to 40%), which suggested the importance of the outliers in the data. Six keys to sexual dimorphism, of very high statistical significance were produced, through the stepvise discriminant analysis. They included from 9 down to 1 variables each, which provided from 100% down to 93.8% of correct sex classification of wild cat skulls.
The contemporary occurrence of wildcat Felis silvestris (Schreber, 1775) in the Polish part of the Carpathian Mountains was evaluated in 1998-2000 with personal inquiries in all forest inspectorates of Krosno and Kraków Regional Directorates of State Forests and five national parks (NP). Additional information on the presence of wildcat was collected by snow tracking in three winter seasons: 1998/1999 through 2000/2001. Wildcat presence was confirmed only for Bieszczady Mountains, Pogórze Przemyskie, and Beskid Niski Mountains (13 forest inspectorates and 2 national parks: Bieszczady NP and Magurski NP).
The feeding ecology of the European wildcat Felis silvestris Schreber, 1777 was studied by analysing 220 scats collected between January and December 1994 at Serra da Malcata Nature Reserve (Portugal). Feeding trials, carried out with a captive male and female, allowed the author to relate the dry excreted weight of prey items in the scats with the fresh biomass ingested. Rodents, particularly Apodemus silvaticus and Microtus lusitanicus, were the dominant component of the diet. Lagomorphs, mostly rabbit Oryctolagus cuniculus, were the second most heavily consumed item in terms of consumed biomass, being more preyed upon, in spring and summer. Although insectivores were regularly consumed throughout the year, this group only represented a small fraction of the total consumed biomass. Reptiles, especially species of Lacer- tidae, were the third most favoured quarry, with higher predator pressure in spring and summer. Bird remains were found at low levels throughout the year. Insects and plants were unimportant items in the diet. The wildcats feeding spectrum showed little variation throughout the year.
We have applied counting of annual cementum lines in canine root to estimate the age of 165 Iberian wildcats Felis silvestris Schreber, 1775. Results indicate that (1) closure of apical foramen of canine root occurs from 6 to 18 months of age, (2) cementum lines are formed in autumn-winter, (3) the first autumn-winter, either a non-continuous line, a continuous "kitten line" or no line can be formed, depending on individual variation in timing of closure of apical foramen, (4) since 7% of wildcats form a kitten line, it needs to be identified in order to avoid an incorrect counting, (5) the first continuous line useful for counting is formed during the second autumn-winter, when animals are 21 months old. For Iberian wildcats, age in years can be estimated by adding 1 to the number of continuous lines. For a more accurate estimation, we propose a formula including months from birth to first line formation, number of annual tines, and months from last line formation to death (A = 9m + Ly + Mm).
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