Monitoring of Tawny owl (Strix aluco) in Kharkiv Region, Ukraine

Yehor Yatsiuk, Nataliia Brusentsova, Yuliya Filatova

Field surveys were made between April 2004 and November 2014 in NNP Homilsha Forest, between May 2011 and March 2015 in Kharkiv Forest Park and between April 2013 and May 2017 in NNP Slobozhanskyi.

In NNP Homilsha Forest and in Kharkiv Forest Park, pellets were collected during regular checks of nest boxes and all known tree cavities. In the first area, all sites were visited three times a year: in mid-April, beginning of July and late November or early December. In the second area, all sites were visited two times a year: in April-May and in November-December. During each check, we collected all pellets from each site which allowed us to separate samples by seasons. In NNP Slobozhanskyi, pellets were sampled only occasionally under cavity trees or on the ground.

Collected pellets were macerated in water, then the wool/fur of prey was removed and the bones were collected and dried (Novikov 1949). Samples of pellets from each locality collected at one time were processed together, with number of prey specimens determined for each sample (Yatsiuk and Filatova 2017).

Prey species were identified following taxonomic keys (Nebogatkin 1987, März 2007, Voronetsky and Kuzmenko 2013). The maximal number of individuals for each vertebrate prey species was determined as the maximal number of upper and lower jaws.

When it was impossible to identify prey remains to species level, they were assigned to higher-level genus or family level. Remains of voles from Microtus “arvalis” group were treated as the East European vole (Microtus levis Miller, 1908) in accordance with earlier karyological studies in the studied region (Zagorodniuk 1993, Zagorodniuk 2008). Unidentified remains of mice (assigned to category Muridae) belonged to each of two genera, Mus or small Apodemus. Category Apodemus includes either A. sylvaticus or A. uralensis as both species can occur in the region (Naglov 1996, Zagorodniuk 2020), but it was not possible to distinguish between them, based on bone remains present. Two remains of Mustela sp. probably belong to M. nivalis. Remains of Soricidae represent small shrews, either Sorex or Crocidura.

Pellet samples were identified by the authors with consultations from the specialists from the Crimea Plague Control Station, Kharkiv Sanitary-Epidemiological Station and Kharkiv National University.

The study area is located in Kharkiv Region, Ukraine, at the southern border of the East European forest-steppe ecoregion (Fig. 1) (Olson et al. 2001). The climate of the region is moderately-continental with mean air temperatures between +21°C in July and -7°C in January and average annual precipitation 540 mm (Golikov et al. 2011). During the study period, the average duration of snow cover was 90-100 days, with more stable cover on elevated sites and frequent thawing in river valleys. The terrain of the region is undulating plains with elevations between 90 and 220 m. The total forest cover is 13.16% in the northern forest-steppe part of the region and includes two main forest types. Broadleaved forests grow on rich clay soils on elevated sites and cover 9.7% of the total area. The main tree species is oak (Quercus robur) with a high proportion of lime (Tilia cordata), maples (Acer platanoides and A. campestre) and ash (Fraxinus excelsior). Coniferous forests grow on sandy river terraces and cover 3.4% of the total area. The dominating tree species is pine (Pinus sylvestris) with a small share of deciduous stands (mainly aspen Populus tremula and black alder Alnus glutionsa in carrs); broadleaved species occur in a relatively small proportion.

Figure 1.  

Location of study sites.

The first study area in NNP Homilsha Forest is located in the broadleaved forest along Siversky Donets River. Clearcut-based silviculture with 90-120 years rotations was used here up to 2007 when it ceased after the creation of the National Park. Currently, most of forest stands here are of natural origin and old-growth forest with the age of 100-150 years covering about half of its territory. The study area is surrounded by rural areas and riverine habitats.

The second study area in Kharkiv Forest Park is located at the northern part of the city. It is a part of a larger forest continuing for about 20 km to the north from Kharkiv. No clearcuts are done in this forest; however, thinnings and sanitary cuttings are practised. The mean stand age is 60–100 years. There is a gradient of transformation from recreational grounds in the southern part to semi-natural stands in the northern part. The study area is mostly surrounded by built-up areas.

The third study area is located in pine and broadleaved forests along the Merla River valley in NNP Slobozhanskyi. Pine forests here include frequent wet depressions and fens. Before the creation of the National Park in 2009, clearcut-based silviculture with 90-110 years rotations was used here. Currently, most of pine stands here are of planted origin with mean age 50-90 years. The mean age of broadleaved forest is 80-120 years and clearcut-based silviculture has been similarly ceased here since 2009.

49.554 and 50.127 Latitude; 35.160 and 36.361 Longitude.

The presented dataset covers 23 mammal species from six orders and nine families with 1213 occurrences in total.

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