Fatal Sarcoptes scabiei and Demodex sp. co-infestation in wolves (Canis lupus ) at the Białowieża National Park, Poland – is it a consequence of climate change?
Pubblicato online: 20 dic 2024
Pagine: 551 - 562
Ricevuto: 21 mag 2024
Accettato: 12 dic 2024
DOI: https://doi.org/10.2478/jvetres-2024-0068
Parole chiave
© 2024 Michał K. Krzysiak et al., published by Sciendo
This work is licensed under the Creative Commons Attribution-NonCommercial-NoDerivatives 3.0 License.
The grey wolf (
The current lifestyle of wolves is the result of adaptation, resilience and innate behaviour in an almost completely urbanised environment. This increasing interpenetration of the synanthropic and sylvatic environments raises the potential for pathogen transmission, many of which are zoonotic. An additional driver for the emergence of diseases that threaten protected species in particular is climate change, which may directly affect the ecology of microorganisms, their vectors such as arthropods and their reservoirs such as rodents and bats (16). An indirect effect of climate change is heat stress in animals, which affects their immune and endocrine functions, reproduction and metabolism and increases their susceptibility to infection/invasion by pathogens which are often opportunistic. Furthermore, climate change may reduce access to food and water, force migration and increase local animal density, and therefore increase interspecies and intraspecies encounters. Sudden climate events are particularly dangerous and do not allow for the adaptation which takes place when the changes gradually progress (3). Sarcoptic mange is considered a neglected disease, whereas
This is the first clinical description of
The Białowieża National Park (BNP) (52°42'11"–52°48'58" N, 23°55'30"–23°56'22" E) covers an area of 10,517.27 ha, which constitutes one sixth of the Polish part of the primeval Białowieża Forest (BF). Strict protection covers 6,059.27 ha (57.6% of the Park’s area), active protection 4,104.63 ha (39%) and landscape protection 353.37 ha (3.4%). Around the Park, a protection zone (buffer zone) has been created, which includes managed forests of 3,224.26 ha. The buffer zone is a game protection zone, where hunting is not practiced (26). The BNP protects the best-preserved fragment of the BF – Europe’s last lowland natural forest of primeval character. The relief of this area shaped by a glacier is not very varied, ranging in the BNP from 145.5 m above sea level (at the confluence of the Braszcza and Narewka rivers) to 175.3 m above sea level (at Babia Góra near Masiewo), which corresponds to only an approximate 30 m difference in absolute height. The whole BNP lies in the basin of the Narewka river, a left tributary of the Narew. The BF is characterised by a high proportion of wetland forested areas, meadows and river valleys, which are periodically flooded. The climate is classified as moderate continental and cool with influences of the Atlantic. The average annual air temperature between 1991 and 2020 was 7.4℃, and the average annual precipitation is 638.3 mm. Most of the precipitation falls in the vegetation season (53). The BNP is characterised by high biodiversity. More than 800 species of vascular plant, more than 3,000 species of spore plant and fungus, almost 200 species of moss and approximately 300 species of lichen can be found here. More than 8,000 species of invertebrate, about 120 species of breeding bird and 52 species of mammal are found in the Park area. Besides the protected grey wolf and lynx, the BF is inhabited by the world’s largest population of free roaming European bison (
In the early spring of 2022, several apparently sick wolves with alopecia were reported by forest rangers and border patrols inside the territory of the BNP. Monitoring was then implemented across the whole Park’s 10,517.27 ha. More than half of the BNP remains under strict protection, meaning anthropopressure is kept to a minimum and only educational and research work is allowed there. It is a valuable natural area which has been included in the UNESCO World Heritage List since 1977. The monitoring sites selected for the study were an adequate representation of the species’ range in terms of numbers and distribution of animals. The locations for cameras for wolf observation were selected on the basis of direct observations of park rangers and data from the BNP inventory, including data on individuals recorded on photo and video traps giving the exact location and number of individuals. The cameras were placed in different places over the whole territory of the BNP, in strict, active and landscape (buffer zone) protection areas. Apart from photo and video monitoring, foresters observed wolves directly all the time and reported what they saw. Two models of camera were used, the first being a TETRAO SPROMISE S328 trap (IBO PL, Kraków, Poland) for recording from a distance of up to 25 m using a 0.6 s shutter speed and motion sensor. Its 940 nm invisible beam infrared illuminates night shots and is undetectable. The camera operates in temperatures between -20°C and +60°C and takes photographs with resolution 12/30 Mpx or captures video at 30 frames/sec for up to 30 s with audio recording. The second camera was a SnapShot Cloud 4G (DÖRR, Neu-Ulm, Germany). It is equipped with 57 invisible Black Vision LEDs, allowing monitoring up to 20 m. The shutter speed is 0.4 s, and video capture is in HD with sound for up to 59 s.
For the on-site surveillance of possible mange cases, analysis was made of the sampling data recorded between January and March 2022 by ten camera traps located as described in Table 1. In the morning of 17th March 2022, the carcass of a young female wolf was found in forest division No. 339C of the BNP (C1, Table 1). The carcass was frozen at -20°C until it was necropsied by the BNP’s supervising veterinarian, at which time samples for further laboratory analysis were collected and a necropsy protocol was prepared.
No. | Division No. | GPS coordinates | Presence of alopecic/sick wolves (number) |
---|---|---|---|
C1 | 339C | 52.7418N; 23.7959E | Yes (2)* |
C2 | 159B | 52.7991N; 23.8267E | Yes (1) |
C3 | 130C | 52.8031N; 23.8280E | No |
C4 | 226A | 52.7803N; 23.8770E | Yes (1) |
C5 | 159D | 52.7926N; 23.8271E | Yes (1) |
C6 | 374A | 52.7282N; 23.9074E | No |
C7 | 135D | 52.8041N; 23.9189E | No |
C8 | 287C | 52.7537N; 23.8758E | No |
C9 | 284B | 52.7570N; 23.8430E | No |
C10 | 259B | 52.7683N; 23.9189E | No |
* – the same location as where the dead wolf (Figs 2a and 3) was found which was later necropsied; here another alopecic one was recorded (Fig. 2d)
The nature of the skin lesions suggested a parasitological infection. Scabies invasion was initially diagnosed based on the presence of clearly visible, characteristic lesions on the skin. In order to confirm the primary diagnosis, scrapings were taken from the lesions for parasitological examinations. First, the scraping was examined directly under an optical microscope at 100× and 400× magnifications. Then the sample was placed in a Petri dish and treated with 10% KOH, heated to 40°C and incubated for 2 h. After the epidermis had been dissolved by the KOH, the surface of the preparation was examined under an optical microscope under the magnifications given earlier.
The test was performed at the Veterinary Hygiene Laboratory in Gdańsk. A sample of brain tissue was collected following the opening of the skull in the necropsy room. Tissue was collected from Ammon’s horn and the thalamus, cerebral cortex and medulla oblongata and subjected to the direct fluorescent antibody test (FAT) according to the WOAH Terrestrial Manual (68) as used in all diagnostic and reference laboratories (59, 61). After smears were prepared on slides and flame fixed, they were stained with a drop of specific conjugate for 30 min at 37°C and washed with phosphate buffered saline. For the purpose of the FAT, a lyophilised, adsorbed anti-rabies immunofluorescent conjugate (Bio-Rad Anti-Rabies Nucleocapsid Conjugate; Bio-Rad, Marnes-la-Coquette, France) was used, which is a suspension of fluorescein isothiocyanate-labelled monoclonal antibodies. Fluorescent antibody test slides were examined for specific fluorescence and the presence of nucleocapsid protein aggregates of rabies virus using a microscope.
Commercial kits were used for the detection of DNA sequences specific for bacteria among the
Climate data for the BF were obtained from the Institute of Meteorology and Water Management and the Polish Geological Institute through the
The camera surveillance (Table 1, Fig. 1) tracked five wolves with severe alopecia of the entire body (Fig. 2). In addition, border guards (Fig. 2a) and forest rangers (Fig. 2b) also observed alopecic wolves, some of which may have been the same individuals. All the mangy wolves were young, 1–2 years old, and were mostly wandering alone (Supplementary Video S1). Two of them had used haystacks in mid-forest meadows left for European bison and cervids as their shelters instead of the burrows used by other pack members. Skin lesions indicative of S

The distribution of camera traps (C1–C10, Table 1) installed for the monitoring of mange cases in wolves in the Białowieża National Park in winter 2021/2022. Red tags – locations where severely alopecic wolves were observed. Red square in the bottom left corner map – the location of the BNP in Europe

Observations of severely alopecic wolves in Białowieża National Park: a – camera trap image of the wolf found dead a day later (Table 1, C1 and Fig. 3); b – camera trap image from the camera positioned on a European bison carcass (Table 1, C4); c – photo taken by a Polish border guard on the border with Belarus on the bridge over the Narewka river (Kosy Most; 52.7996N, 23.8284E) near location of trap C2 (Table 1); d – photo taken by a forest ranger in the same midforest meadow as trap C1 (Table 1)
The observed clinical signs in the female wolf found dead, which was estimated to be 2 years old (born in 2020), included alopecia of the entire body, hyperkeratosis, emaciation and dehydration, anaemia of the mucous membranes (Fig. 3a), presence of soil and fragments of vegetation in the mouth (Fig. 3b), a stomach with little digestive content, empty intestines, a considerably enlarged gallbladder, precipitation spots in the left lung, foci of emphysema and heart chambers filled with clotted blood. Because foreign bodies were in the mouth and it was unverifiable whether they were taken in during the agonal state, ante or post mortem and the digestive tract was empty, the wolf’s brain was first referred for virological examination for rabies.

External inspection of a wolf carcass showing: a – advanced alopecia; hyperkeratosis; emaciation and severe dehydration and anaemia; b – presence of soil and fragments of vegetation in the mouth suggestive of some neurological symptoms, which were nevertheless ruled out by a negative rabies test result
Infections with rabies and tick-borne pathogens in the necropsied wolf were excluded. In the skin scrapings, a low number of mature forms of

Ventral views of a
The average monthly absolute and average maximum temperature, minimum temperature, average temperature and minimum temperature at ground level for BNP trended upwards between 1951 and 2021, and the increase in temperature has been particularly dynamic in the last 10 years, with an average rise of 2°C (Supplementary Fig. S1 a–c). Interestingly, cyclical changes in the temperature at ground level were observed, with values decreasing from the early 1960s to the 1990s, and then increasing by one degree over the last two decades (Supplementary Fig. S1d). While monthly precipitation has not changed much in years for which data was collected, with the exception of noticeable increases between the 1950s and 1970s (Supplementary Fig. S1e), the annual number of rainy days has been on a steady increase since the 1950s (Supplementary Fig. S1f). However, the maximum snow depth in winter and the annual number of days with snow cover have been decreasing quite substantially. When the data was narrowed down to the winter months only (January–March) in the last two decades, more pronounced changes were observed in the last ten years (Fig. 5). The climate has warmed to such an extent that the average minimum temperature in winter has increased from below -5°C to above -2°C, and the average minimum temperature at ground level has risen by as much as 10°C (Fig. 5a). The winters have become less snowy (Fig. 5b), an example being the 2021/2022 winter when snow cover was almost negligible, as can be seen in the footage from the camera traps (Supplementary Video S1 and S2), despite the trend for snow depth having been rising in recent years (Fig. 5b).

Local polynomial smoothed lines of the distribution of selected monthly meteorological data for Białowieża Forest, obtained from the Polish Institute of Meteorology and Water Management in the winter months of January–March between 2001 and 2021. a – solid blue line: average minimum temperature (Tmin); dotted maroon line: average minimum temperature at ground level (Tmin ground); b – solid navy-blue line: average maximum snow depth in cm; dashed maroon line: average number of days with snow cover
Scabies is considered a neglected tropical disease, and its re-emergence in animals and humans is becoming a challenge in many parts of the world. The exacerbation of parasite invasions can be seen as a symptom of environmental changes that affect general health and susceptibility to endemic and conditionally pathogenic commensals. For example, an association between human scabies caused by
Scabies and demodicosis are caused by parasitic mites classified as the Acari subclass within the Arthropoda phylum and Arachnida class. They belong to two distinct orders. Mites of the
Mange in wildlife reflects emerging worldwide challenges and pressure on nature (47).
Climate change has been discussed as a driver for scabies in humans (47) and wildlife (31, 66). Optimal humidity and temperature promote efficient reproduction and survival of mites in the environment (66). An indirect influence of climate change is on host health and susceptibility to adverse factors, where it induces heat stress and weakens the resilience of mammals (48). An increasing percentage coverage of water habitats by camera traps was associated with higher probabilities of apparent scabies in foxes (11). Białowieża Forest is characterised by a high percentage of wetlands, which together with milder winter temperatures favouring mite survival may have intensified the exposure of its wolves to mites and fostered mite transmission between them. Any animal infected with
The disease severity and clinical course of both infestations are strictly dependent on the non-specific and specific immune response. This is particularly evident in the course of demodicosis. This invasion is assumed to occur in a significant proportion of the host population in an asymptomatic form. In contrast, its clinical form is closely associated with periodic immune decline or immunomodulatory disorders. For this reason, a
It has been observed that scabies in wolves is most often limited to certain parts of the animal’s skin (the hind legs, tail and head) (Video S2) and only in extreme cases affects all parts of the body (41, 49, 55). Immune response mechanisms can also explain one species’ greater susceptibility to scabies than another’s (44). It was recently demonstrated that
An assessment of the epidemiological situation should also take into account the presence of other predators that may be both competitors and sources of infection. As shown recently for foxes in Spain (11), camera health monitoring should be considered an effective tool for the conservation of protected species such as the wolf and has the advantage of being non-invasive. The wolf’s conservation is a matter with a rising profile because the increasing population sizes of the species in many parts of Europe and environmental changes may promote the spread of pathogens and increase the risks of an epidemic, which is shown here at the micro-scale of the BFo. Furthermore, as predators, wolves are a good model species for exposure to infectious and non-infectious threats, as their food is mostly wildlife. An additional motivation for their surveillance is that wolves can potentially contribute to the spread of diseases, even those that are not a threat to them (5, 12, 13, 39, 40, 62, 65, 69).
An outbreak of severe cases of mange related to mixed infestation of