К вопросу о миграциях орла-могильника и степного орла в Туркменистане

Степной орёл в Алтае-Саянском регионе – результаты исследований 2019–2023 годов

In 2017, a total of 36 ornithologists and birdwatchers participated in the work of the Raptor Ringing Center of the Russian Raptor Research and Conservation Network and ringed 498 individuals of 23 species of Birds of Prey and Owls. The leading species that have maximum ringed individuals is Steppe Eagle ( Aquila nipalensis ) – 146 individuals; it followed by White-Tailed Eagle ( Haliaeetus albicilla ) and Osprey ( Pandion haliaetus ) – 53 individuals per species, Imperial Eagle ( Aquila heliaca ) – 45 individuals, and Saker Falcon ( Falco cherrug ) – 42 individuals. During the last 7 months of 2017 and the first 4 months of 2018 we got an information about 37 ringed raptors, 32 of them were possible to read and identify. The highest number of recoveries we got from Eastern Imperial Eagle and White-Tailed Eagle (6 recoveries per species).

In work of the Raptor Ringing Center of the Russian Raptor Research and Conservation Network in 2014 participated 39 ornithologists-researchers and birdwatchers who have ringed in total 889 individuals of 23 species of birds of prey (Falconiformers) and owls. From colour marked birds the leaders are Upland Buzzard ( Buteo hemilasius ) – 154 ind., Eastern Imperial Eagle ( Aquila heliaca ) – 110 ind., Steppe Eagle ( Aquila nipalensis ) – 95 ind., Long-Legged Buzzard ( Buteo rufinus ) – 87 ind., White-Tailed Eagle ( Haliaeetus albicilla ) – 78ind. For 2014 and the first 5 months of 2015 the information was received about the registration of 50 birds with rings from which 39 birds were identified . Among returns the leaders are Eastern Imperial Eagle (14 ind.) and White-Tailed Eagle (9ind.).

Степной орел на территории резервата «Бокейорда» и Ащиозекского заказника (Западно-Казахстанская область) в 2022–2023 годы

Abstract: Despite recovery plans, the Spanish Imperial Eagle ( Aquila adalberti ) and the Iberian lynx ( Lynx pardinus ) are in danger of extinction. These two flagship species tend to occur in pristine Mediterranean forests, and both prey preferentially on the rabbit ( Oryctologus cuniculus ). Spanish lynxes and eagles have sister species in continental Europe, the Eurasian lynx ( Lynx europaeus ) and the Eastern Imperial Eagle ( A. heliaca ), respectively. Recent genetic evidence indicates that these two pairs of species started to diverge from their ancestor species slightly less than 1 million years ago, when the longest‐lasting Pleistocene glaciations covered Europe. We hypothesize that the Iberian lynx and the Spanish Imperial Eagle emerged as separate species in the Pleistocene refugia of southern Spain, where they hunted yet another locally evolved species, the rabbit, on which they have become dependent for survival. Two large predators that emerged at the same time may go extinct simultaneously because of their inability to shift to alternative prey. Many other relict species, including numerous species from oceanic islands, have naturally small populations because of evolutionary constraints and are permanently threatened with extinction. Recovery plans aimed at putting these species out of danger are unrealistic, as their populations are and have been chronically scarce. We suggest that what these species need are maintenance plans designed to buffer population declines due to either stochastic or human‐induced events. A metaphor for this would be “emergency care units” for conservation.

Visual migration surveys, especially at bottlenecks, can be a vital tool to evaluate population fluctuations in environmentally sensitive species. Raptors are considered to be important bioindicators that can help identify environmental catastrophes. Substantial proportions of the global population of Steppe Eagles (Aquila nipalensis) and Levant Sparrowhawk (Accipiter brevipes) concentrate at Eilat, Israel, during the spring and autumn migrations, but counts from seven autumn and seven spring migration surveys indicate a constant decline in Steppe Eagle numbers. Further, the number of juveniles observed in these counts dropped steadily from 30% in the early 1980s, to 1.4% in 2000. The numbers observed at Eilat are well below the range of the numerical fluctuations observed in previous surveys. In Levant Sparrowhawks, no decline in total numbers is evident, but a significant change in the adult to juvenile age ratio was noted between the population trapped in the 1980s and that sampled in the late 1990s. The cumulative evidence of the decrease in the total numbers of Steppe Eagles, the decreasing proportion of subadults within the population, and the decrease in adult:young ratio in the Levant Sparrowhawk population trapped leads us to suggest that the Chernobyl accident on 26 April 1986 may have negatively affected wildlife populations, not only to the west with the spread of the radio-active plume, but farther east than previously assumed.

The diet composition of breeding Eastern Imperial Eagles (Aquila heliaca) was analysed in Hungary between 2005 and 2017, and compared with two previously published datasets from the periods of 1982–1991 and 1992–2004. Altogether the distribution of 8543 prey items of 126 different species and 29 other taxa were analysed within a 36-years period. We found that the previously abundant Common Hamster (Cricetus cricetus) became marginal (7.42%), while European Sousliks (Spermophilus citellus) practically disappeared (0.03%) from the diet of Imperial Eagles. Small game species, like the Common Pheasant (Phasianus colchicus) and the Brown Hare (Lepus europaeus) composed a remarkable part of the diet (11.22% and 28.11% respectively), which raised some conflicts with hunters regionally and probably also contributed to the high prevalence of persecution incidents against the eagles. In parallel with the loss of traditional prey species, corvids (13.10%), pigeons (8.90%), waterbirds (6.83%), other rodents (6.71%), Roe Deers (Capreolus capreolus) (5.59%), raptors and owls (4.88%) became regularly detected prey species. The temporal changes of the main prey categories were analysed between 1998 and 2017, when the ratio of Hamster and Pheasant showed significant decrease (-27.29% and -6.38%, respectively). The ratio of Brown Hare also showed slight decrease (-3.98%), but the change was not significant. On the other hand, the ratio of corvids, waterbirds and Roe Deers within the diet showed significant increase (+18.20%, +6.25% and +5.39%, respectively). The observed flexibility in the foraging behaviour of Imperial Eagles greatly facilitate conservation efforts, as they seems to be able to utilize the most abundant prey sources, i.e. they were not depending solely from the status of any single specific prey source. However, eagles could only shift and survive in those regions, where their traditional preys decreased, if alternative species were available for them.

At present, four eagle species are regular breeders in the Czech Republic: White-Tailed Sea-Eagle (Haliaeetus albicilla), Eastern Imperial Eagle (Aquila heliaca), Lesser Spotted Eagle (Aquila [Clanga] pomarina), and Golden Eagle (Aquila chrysaetos). There is also a historical record of confirmed breeding of Greater Spotted Eagle (Aquila [Clanga] clanga) in 1847 in the region of Eastern Bohemia. At present, this species is only a rare visitor on autumn and spring passage. White-Tailed Sea Eagle (Haliaeetus albicilla) has re-colonized the country since the mid-1980s, after approx. one hundred years absence as a breeder. The recolonization started at two separate areas: South Bohemia, with birds coming mainly from German and Poland source population, and South Moravia, with birds coming from Pannonia, i.e. mainly from Hungary. Later the species occupied nearly the whole area of suitable habitats. The population is still increasing and currently reaches ca. 160–180 breeding pairs. Eastern Imperial Eagle (Aquila heliaca) has bred in the Check Republic for the first time in 1998 (there is one unconfirmed note about its breeding also in 1930s). Since then, the population is slowly growing, similarly as the whole Pannonian population (with source populations mainly in Hungary and Eastern Slovakia). So far, the breeding is limited to Pannonian region of the country (i.e. south-eastern part) but the first pairs have spread north and west during the last years. 23 territorial pairs were monitored in 2023. The Lesser Spotted Eagle (LSE, Aquila [Clanga] pomarina) was never an abundant species in the Czech Republic. Scarce population existed especially in submountainous regions and in the mountains throughout the CR. The last breeding pairs were documented at the end of 1980’s and the beginning of 1990’s in Šumava Mts. After more than 20 years, breeding of LSE was surprisingly confirmed in western Bohemia. Since 2012, one pair breeds there regularly. In 2018, a small new population was discovered in the north of Morava region and currently three pairs breed there. Since 2020, another pair breeds in eastern Bohemia. Presently, two pairs breed in this region but we presume that another 1–2 breeding pairs could be hiding in this region. Therefore, in 2023 we estimate the breeding population of the LSE in the Czech Republic as 6–8 pairs. Golden Eagle (Aquila chrysaetos) started to breed in Northern Moravia (NE part of the country) in 2013 (similarly as White-Tailed Sea Eagle after more than one hundred years of absence), partly as a result of re-introduction project carried out during 2006–2017 (27 birds originating from Slovakia were released). Along with the growing population size and range expansion in the neighbouring Slovakia, there are now min 5–6 occupied territories in Czech Republic. Osprey (Pandion haliaetus) is a regular passage migrant (both spring and autumn), with some birds oversummering and very rarely also wintering. Historical data about its regular breeding in 19th or even early 20th century are not fully confirmed. Several breeding attempts were recorded also during the last 20 years. These included nest building but the clutch was never laid. Short-Toed Snake Eagle (Circaetus gallicus) is a very rare visitor in the Czech Republic, but the number of observations seems to increase rapidly during the last 10 years. With the increasing population in Hungary and possibly also Slovakia, its breeding cannot be excluded in the near future.

BackgroundReports from the health center of Yazd province of increasing cutaneous leishmaniasis (CL) cases led us to carry out an epidemiological study using standard techniques in Ardakan County, central Iran, during 2001.Patients and MethodsData was collected on the prevalence of scars and ulcers over a period of 14 months among 621 households in three villages around Ardakan County. Smears were prepared by scraping the edges of the ulcers. We collected the same data on all school children aged 7 to 11 years old in the area. To determine the reservoir host of the disease, rodents and dogs were caught and examined. Sandflies were collected biweekly from indoor and outdoor locations in the study area, and then identified. Parasites isolated from human and rodents were characterized by RAPD-PCR technique.ResultsThe prevalence of scars and ulcers were 30.4% and 24.6%, respectively, in 3024 individuals in the three villages. Individuals 10 to 14 years of age were the most highly infected age group, with a rate of 28.4%. Males and females were equally infected. Examination of 892 students in primary schools showed a rate of 22.9% for scars and 23.7% for ulcers. Meriones libycus (42.2%) and Rhombomys opimus (57.8%) were present around the villages. Both were infected with Leishmania. Three of 19 M. libycus (15.7%) and 3 out of 26 R. opimus (11.5%) had positive results. The active season of sandflies was late April to late November. Phlebotomus papatasi and Sergentomyia sintoni were the dominant species indoors and outdoors. Natural leptomonad infection was found in P. caucasicus and S. sintoni from gerbil and Jird burrows.ConclusionBased on this survey, there is an epidemic of zoonotic CL in the area, with Leishmania major as the agent, M. libycus and R. opimus as the reservoir hosts, and most probably Phlebotomus papatasi as the vector because about 77% of indoor sandflies were of this species.

Following the epidemic of cutaneous leishmaniasis in Khatam County, Yazd Province, this study was carried out to determine vector, and animal reservoir host(s) and investigate the human infection during 2005-2006. Four rural districts where the disease had higher prevalence were selected. Sticky paper traps were used to collect sand flies during April to November, biweekly. Meanwhile rodents were captured using Sherman traps from August to November. Households and primary schools were visited and examined for human infection in February 2006. The parasite was detected by RAPD-PCR method. The rate of ulcers and scars among the inhabitants was 4.8% and 9.8%, respectively. Three rodent species were captured during the study: Meriones libycus, Rhombomys opimus, and Tatera indica. Six sand fly species were also collected and identified; among them Phlebotomus papatasi had the highest frequency. Leishmania major was detected as the agent of the disease in the area. It was detected from R. opimus and native people.

Cutaneous and visceral forms of leishmaniasis are the most important protozoan infection in the Middle East and North Africa (MENA). Review the current knowledge on leishmaniasis in the MENA. The data presented in this review are gathered primarily from WHO reports and from an extensive literature search on PubMed. There are four cycles of transmission of leishmaniasis: zoonotic cutaneous leishmaniasis (ZCL), induce by Leishmania (L.) major, transmitted by Phlebotomus (P.) papatasi, with rodent species of Psammomys obesus, Meriones libycus, Nesokia indica, and Rhombomys opimus are considered as host reservoirs. Zoonotic visceral leishmaniasis (ZVL) is inducing by L. infantum, transmitted by several Phlebotomus spp. of the sub-genus Larroussius and mainly P. perniciosus in more than one-half of the MENA countries and the dog species of Canis familiaris are considered as the main reservoirs. Anthroponotic cutaneous leishmaniasis (ACL), induce by L. tropica and transmitted by P. sergenti, without any non-human reservoir in most cases. Anthroponotic visceral leishmaniasis (AVL) induces by L. donovani spreads through P. alexandri, circulates exclusively in humans. There are many challenges facing the successful control of leishmaniasis. However, there is continuing research into the treatment of leishmaniasis and potentially vaccinations for the disease.

The aim of the current study was to survey the species diversity and Leishmania infection of rodents in the Gonbad -e- Kavoos City and County, northeastern Iran, during 2018–2019. Totally, 20 rural and four urban areas endemic for leishmaniasis were selected and visited monthly. Rodent species diversity indices were calculated in different spatial and temporal scales. Species richness was also calculated using rarefaction curves to estimate the number of species in unequal sample sizes. A total of 167 rodents belonging to 7 species, 6 genera, and 2 families were collected. Rattus rattus (34.7%) and Rattus norvegicus (18.6%) were identified as dominant species. The largest Margalef and Menhinick species richness (DMg = 1.55; DMn = 1.01) and the highest value of the Shannon index (H′ = 1.71) were observed in rural areas. Seasonal abundance of the rodents varied among species and showed that the highest richness (DMg = 1.27; DMn = 0.65) occurred in spring and the highest value of Shannon index (H′ = 1.72) was noted in summer. Rarefaction curves confirmed that the highest species richness occurred in summer and spring in the rural area. Seasonal fluctuations of R. rattus and R. norvegicus have a significant impact on the changes in rodent species diversity. Investigations of Leishmania infection showed that amastigote forms of Leishmania were observed in 15.4% of smears taken from Rhombomys opimus and Meriones libycus and examined under the light microscope. The highest rate of Leishmania infection was observed during the summer.

The occurrence of the Corsac Fox, Vulpes corsac, is replete with ambiguity and uncertainty in the literature. We present the first confirmed record of the species from Iran. In the course of a survey, we found two Corsac Fox furs in Tehran Market in 2013 and separately recorded one adult and a group of three young in semi-arid steppes in central Turkmen Sahra, Golestan Province, in June 2014. Great Gerbil (Rhomobomys opimus), Libyan Jird (Meriones libycus), and Long-eared Hedgehog (Hemiechinus auritus) are among prey items. The Corsac Fox has a limited range in Iran and is threatened by habitat fragmentation and road kill.

Between 1 977 and 201 3 nesting of 72 different pairs of imperial eagle was recorded in Slovakia. The nesting population in Slovakia is concentrated in two subpopulations with the nesting area distant about 200 km. In Eastern Slovakia nesting of 42 pairs was recorded whilst in Western Slovakia 30 pairs were nesting. Authors present results of 37 years period of survey focused on distribution and trend of nesting population, as well as habitat preferences of the species. The paper compares results from Western and Eastern Slovakia. From Western Slovakia further data are evaluated, such as threats negatively influencing the population, period of hatching and other aspects of nesting biology. During the survey period the number of known nesting pairs in Slovakia has increased from five in 1 977 to 53 in 201 3. In total, 908 nesting events have been recorded during this period with 642 successful nesting events and 1 ,080 fledglings. In Western Slovakia the pairs prefer foothills, whilst in Eastern Slovakia most of the pairs nest in lowlands. Strong anthropic pressure is significantly influencing the distribution and size of the population as well as the habitat preferences of the species.

Survival rate is usually the greatest contributor to population growth in long‐lived species, and its accurate estimation along with the evaluation of the factors influencing it is therefore essential for effective conservation. Here, we studied the survival of breeding eastern imperial eagles Aquila heliaca in Hungary between 2011 and 2022 and investigated the effect of poisoning, the leading known anthropogenic cause of mortality. We used the Cormack‐Jolly‐Seber mark‐recapture model to estimate annual apparent survival and encounter probabilities based on the capture histories of 208 males and 411 females. We obtained encounter data from the DNA profiles of shed feathers collected at the nest sites, which we also supplemented with presences inferred from parentage analysis. The most supported model estimated a constant 91.6% annual survival over the study period, but models including the effect of sex and poisoning rate on survival had similar support. Sex difference in survival was less than 1% on average, but the survival of males decreased more with poisoning rate than the survival of females. However, due to smaller encounter probabilities, the estimates for males were less precise compared to females. Males may be more at risk from poisoning than females not only due to their more active foraging behaviour during incubation and chick‐rearing but also due to their smaller body size. Apart from providing direct practical information for the conservation management of imperial eagles, our results also highlight the importance of long‐term studies for estimating population parameters of birds of prey.