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Article

Occurrence of Leishmaniasis in Iberian Wolves in Northwestern Spain

by
Javier Merino Goyenechea
1,2,
Verónica Castilla Gómez de Agüero
3,4,
Jesús Palacios Alberti
2,
Rafael Balaña Fouce
1,* and
María Martínez Valladares
3,4
1
Departamento de Ciencias Biomédicas, Facultad de Veterinaria, Universidad de León, Campus de Vegazana s/n, 24071 León, Spain
2
Centro del Lobo Ibérico “Félix Rodríguez de la Fuente” Robledo De Sanabria, 49393 Puebla De Sanabria, Spain
3
Departamento de Sanidad Animal, Facultad de Veterinaria, Universidad de León, Campus de Vegazana s/n, 24071 León, Spain
4
Instituto de Ganadería de Montaña, CSIC—Universidad de León, Finca Marzanas. Ctra. León-Grulleros s/n, 24346 León, Spain
*
Author to whom correspondence should be addressed.
Microorganisms 2023, 11(5), 1179; https://doi.org/10.3390/microorganisms11051179
Submission received: 28 March 2023 / Revised: 24 April 2023 / Accepted: 26 April 2023 / Published: 30 April 2023
(This article belongs to the Special Issue Vector-Borne Infections in Wildlife)
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Abstract

:
Canine leishmaniasis is an important vector-borne protozoan disease in dogs that is responsible for serious deterioration in their health. In the Iberian Peninsula, as in most countries surrounding the Mediterranean Sea, canine leishmaniasis is caused by Leishmania infantum (zymodeme MON-1), a digenetic trypanosomatid that harbors in the parasitophorous vacuoles of host macrophages, causing severe lesions that can lead to death if the animals do not receive adequate treatment. Canine leishmaniasis is highly prevalent in Spain, especially in the Mediterranean coastal regions (Levante, Andalusia and the Balearic Islands), where the population of domestic dogs is very high. However, the presence of this disease has been spreading to other rural and sparsely populated latitudes, and cases of leishmaniasis have been reported for years in wildlife in northwestern Spain. This work describes for the first time the presence of wolves that tested positive for leishmaniasis in the vicinity of the Sierra de la Culebra (Zamora province, northwestern Spain), a protected sanctuary of this canid species, using PCR amplification of L. infantum DNA from different non-invasive samples such as buccal mucosa and those from both ears and hair. In addition to live animals (21), samples from carcasses of mainly roadkill animals (18) were also included and analyzed using the same technique, obtaining a positivity rate of 18 of the 39 wolves sampled (46.1%) regardless of their origin.

1. Introduction

Canine leishmaniasis (CanL) is a re-emerging vector-borne disease produced by the protist parasite Leishmania infantum [1,2]. CanL is endemic in the coastal regions surrounding the Mediterranean basin, and it is increasingly spreading to the northern areas of southern European countries, including Spain, with a cold continental climate in winter and mild temperatures in spring and summer [3]. Currently, the vectors of the disease (dipteran species of the genus Phlebotomus or sand flies) have colonized almost the entire Iberian Peninsula, and therefore, CanL is being diagnosed more frequently in areas previously described as non-endemic [4]. CanL is usually lethal in untreated dogs, and lesions are associated with inflammatory reactions including peripheral lymphadenopathy and hepatosplenomegaly. Dermatological signs include alopecia, dermatitis, onychogryphosis and epistaxis. Renal disease is severe and may progress from nephrotic syndrome to chronic renal failure [2,5,6].
CanL is endemic in all European countries bordering the Mediterranean Sea, but the distribution of the disease is heterogeneous between and within countries [7]. In Greece, the mean seropositivity to CanL in dogs was 22.1%. In the Balkan countries, seropositivity ranged from 1.8–10.6% [8]. In Italy, a canine population prevalence of 10–40% was detected in the Campania region [9], whereas in France, the highest prevalence (between 8.1 and 28%) was found in areas closer to the Mediterranean Sea [10]. In Spain, unlike Portugal, the lowest figures have been found in inland and northern regions, whereas in Levante, Andalusia and the Balearic Islands, the average seropositivity is higher than 17% [11,12]. The spread of the disease to pets in non-endemic northern European countries [13] has been attributed to several factors including global warming, pet tourism and pet trade [14,15].
The first description of this infection in wildlife was made by Rioux and coworkers, who found several cases of leishmaniasis in red foxes (Vulpes vulpes) in southern France [16]. The incorporation of PCR as a diagnostic technique has facilitated the detection of wildlife animals that have been in contact with the parasite in some way, confirmed in many cases by the use of complementary immunological and parasitological techniques. In addition to foxes, many other mammals have tested positive for leishmaniasis using this technique, including wild canids [17,18], felids such as lynxes, wild cats, mustelids [19,20,21], hares, rabbits, bats and rodents [22,23,24], among others.
Wolves are expected to be potential reservoirs of the pathogen due to their phylogenetic similarity to dogs, their social habits and their proximity to rural areas, where dogs continue to play important domestic, guarding, shepherding and hunting roles [25]. Since the first description of leishmaniasis in wolves in Croatia in 2003—reported by Beck and coworkers in 2008 [26]—studies on the existence of this disease have been spurious, unsystematic and, in most cases, carried out on the remains of accidentally killed or poisoned animals [27,28,29].
Finally, the importance of CanL should not only be addressed from the point of view of the suffering of infected animals, but also as a real public health problem that may worsen with global warming. Therefore, it is of great importance to prevent infection as much as possible and eventually eradicate the disease, which implies close collaboration between authorities and health professionals. In the present work, we describe the presence, by means of semiquantitative PCR, of L. infantum DNA in buccal mucosa, ears and hair taken from both animal carcasses (found by environmental protection services) and live Iberian wolves (Canis lupus signatus) housed in a semicaptive wolf reserve located in the province of Zamora (Castilla y León, northwestern Spain).

2. Materials and Methods

2.1. Origin of the Animals

The study was carried out in the province of Zamora (Castilla y León, Spain) in northwestern Spain (see map in Figure 1) with two well-characterized climate types: a humid climate in the mountainous area (the northwestern area of the province), with abundant rainfall, cold winters, snowfall and mild summers; an extreme continental climate, which affects the rest of the province, with cold winters and hot summers. At present, the wolf occupies practically the entire territory of Zamora (Figure 1); however, there is a mountain range called “Sierra de La Culebra” that has the highest density of Iberian wolves in the Iberian Peninsula. This is where they cohabit with other species of carnivores [30]. In the last Regional Census elaborated by Sáenz de Buruaga and coworkers between 2012 and 2013, 179 wolf packs were identified in the Community of Castilla y León, of which 152 were located to the north of the Duero River and 27 to the south. The province of Zamora was assigned 45 of these packs [31,32].
A key enclave for protection of the Iberian wolf, named “Centro del Lobo Ibérico Félix Rodríguez de la Fuente” (Iberian Wolf Center) [33], is located in northwest Zamora. It maintains a stable population of 14 wolves kept in semi-freedom and distributed among three established packs. The wolves are kept in an ecosystem similar to that of the Sierra de La Culebra. The wolves at the Iberian Wolf Center are housed in three different enclosures, interacting with each other and also with members of the management team.

2.2. Sampling

Samples were collected from 39 Iberian wolves (Canis lupus signatus) in the province of Zamora. Some of the samples came from live animals captured and tagged as part of the Iberian wolf management plan in Castilla y León (7), and others (14) were obtained at the Iberian Wolf Center’s “Félix Rodríguez de la Fuente”. Other samples were collected from wolves killed by natural causes (1), motor vehicles (14) or from legal hunting activity (wolf hunting in Spain was authorized north of the Duero River until 2021) carried out between the years 2017 and 2021 (3).
Animals either captured in the wildness or those living in semicaptivity in the Iberian Wolf Center were subjected to an exhaustive protocol established by the Management and Veterinary Care Unit before sampling. After capture, the first action of the veterinary team consisted of sedation with a mixture of ketamine (15 mg/kg body weight) and medetomidine hydrochloride (30 μg/kg body weight) via intramuscular injection using a blowgun. During the 20 min of sedation, a GPS geolocation collar was placed, and biometric measurements were taken.
Samples of buccal mucosa, ears and hair were taken from wolves. The first two samples were taken with the help of a sterile swab; for the buccal mucosa, a scraping of the inside of the cheek was performed to collect as many buccal cells as possible. Ear samples were collected by scraping the epithelial mucosa of the inner ear. Regarding hair collection, individual hairs were taken, including the hair follicle, from the heads of the animals. After sample collection, all samples were sent refrigerated to the laboratory for analysis. Once in the laboratory, they were stored at −20 °C until DNA extraction.
Sampling of the wolf carcasses was done after the necropsy and also included buccal mucosa, ear swabs and hairs, collected as previously described. Additionally, samples of spleen, liver, kidney, muscle, skin and blood from cavities and urine were also routinely obtained.

2.3. PCR Analyses of the Samples

DNA extraction from all samples was performed following the protocols described in the GeneJet genomic DNA purification kit (Thermo Scientific™, Waltham, MA, USA) for samples collected with a swab or directly from tissue following the manufacturer’s instructions. The final DNA elution volume was 25 μL per sample. As a positive control, DNA extraction from a culture of L. infantum promastigotes was also performed.
To analyze the parasite load in the animal’s hair, initially, groups of 5, 10 and 20 individual hairs were taken from a positive wolf, and DNA extraction was performed on these three groups independently. For the rest of the hair samples, the extraction was done using 10 hairs from the head of the same wolf.
All samples were analyzed via qualitative PCR after amplification of a 131 base pair (bp) fragment of the kinetoplast minicircle of L. infantum using the newly synthesized primers (Forward: 5′-CCCAAACTTTTCTGGTCCTC-3′; Reverse: 5’-TTACACCAACCCCCAGTTTC-3′) corresponding to a conserved region of DNA minicircle of L. infantum kinetoplast. As an internal control, to confirm that cells had been collected with the swab, a fragment of 303 bp of the gene coding the Na+/Ca2+ exchanger (NCX1) was also amplified in the buccal mucosa and inner ear samples using the pair of primers previously described [34] (Forward 5′-CCTAGGTCTCCTGCAGTGAAGT-3′; Reverse: 5′-CCAAGACCCTTCCTTTGGA-3′). The PCR amplification was carried out using DNA AmpliTools HotSplit Master Mix (BioTools, Jupiter, FL, USA) in a final volume of 20 µL, and the primer concentration was 0.5 µM each. Regarding the DNA volume added for each reaction, 5 µL and 1 µL of DNA were added for the amplification of L. infantum and the NCX1 gene, respectively. The thermocycler used (Biorad, Hercules, CA, USA) was set to run for 5 min at 95 °C, followed by 40 cycles each of 30 s at 95 °C, 30 s at 60 °C, 30 s at 72 °C and finally, an extension step at 72 °C for 5 min. Amplification products were analyzed via electrophoresis in 2% agarose TBE (Tris base, boric acid and EDTA). The specific amplified fragments were purified using a SpeedTools Clean-up kit (BioTools), and Sanger sequencing was done at the University of León Sequencing Facility to confirm the specificity of the PCR.

3. Results

3.1. Set-Up of a PCR-Based Method for L. infantum DNA in Wolf Hair

Wolf hair is a non-traumatic, easy and safe place to collect samples from wild animals. L. infantum amplification in wolf hair samples was determined by extracting DNA for PCR amplification using increasing numbers of hairs (5, 10 and 20).
As shown in Figure 2, a quantity-dependent 131 bp band was amplified from L. infantum DNA when the pair of primers corresponding to the kinetoplast DNA were used. This figure shows that the amplified band was observed from 10 hairs onwards; therefore, with the rest of the samples, it was decided to analyze a total of 10 hairs per animal. In the same Figure, a 303 bp band encoding Canis lupus NCX1 gene was also amplified, showing its validity to be used for the collection of wild animal samples.

3.2. Occurrence of Leishmaniasis in Living Wolves

The present study was conceived to address the presence of L. infantum in live captured or semicaptive wolves. Table 1 shows details on the 21 wolves that were sampled for the presence of L. infantum kinetoplast DNA in tissues, including buccal mucosa, right and left ears and hair. Of the 21 samples, 14 (9 females and 5 males) belonged to specimens residing in semicaptive conditions at the Iberian Wolf Center during the period from 2018 to 2022. Until the beginning of 2022, samples were taken from the mouth, both ears and eventually from hair. From this date onwards, and once the method described in Figure 2 was implemented, samples were taken only from hair. Samples of oral mucosa and both ears were taken from the seven wild animals captured and subsequently released during routine wildlife control plans during the period 2017–2019. Five of these wolves (three males and two females) were positive for CanL, representing more than 70% positivity. With the exception of the specimen captured in Lobeznos (a 7.5-year-old male that tested positive for CanL in the ear), all animals were positive in the oral sample, which proved to be the most reliable place for sampling until its replacement in early 2022 by hair samples. Of the 14 samples taken during this period from semi-captive wolves in the Iberian Wolf Center, seven (50%) were positive in some of the samples. Of these, five of the nine females (55%) and two of the five males (40%) were PCR-positive. Overall, 12 wolf specimens (seven females and five males) of the twenty-one animals sampled alive and living in semi-captive conditions (57%) were positive for leishmaniasis.
One of the specimens sampled in the Iberian Wolf Center (identified as Brasa, a 6-year-old female) showed positivity in all samples obtained (buccal mucosa, ear and hair) and presented external symptoms of leishmaniasis (weight loss, onychogryphosis, slight lymphadenopathy and alopecia around the eyes). However, a second animal (identified as Dakota, a 9-year-old female) was positive in all samples except hair and showed no evident signs of leishmaniasis. The rest of the animals sampled were hair-positive and were equally asymptomatic.

3.3. Occurrence of Leishmaniasis in Dead Wolves

Table 2 shows the data collected from the sampling performed on the carcasses of 18 wolves (16 males and 2 females) sampled for the presence of L. infantum, including oral mucosa, right and left ears and hair. Of the 18 carcasses, 14 (77.7%) were struck by motor vehicles and found as roadkill in different areas of the province of Zamora, 3 specimens (16.7%) were killed during legal hunting and 1 wolf (5.5%) was found dead as a result of wounds received in a fight (a 5-year-old male). All animals’ oral mucosa were sampled (with the exception of one specimen sampled in Palacios de Sanabria, from which only both ears were sampled); of those, six (five males and one female) were positive (33.3%) and twelve (eleven males and one female) were negative (66.6%). Two specimens were positive in hair but not in oral samples. In no cases did the condition of the animals’ remains allow us to evaluate their symptoms of leishmaniasis.
In summary, taking into account the wolves that were positive for Leishmania in carcasses (6 of 18) and those that were positive in animals captured alive (12 of 21), the incidence of positivity was 18 of the 39 animals sampled (46.1%).

4. Discussion

Numerous publications mention the presence of Leishmania spp. in wildlife with different degrees of prevalence, depending on the geographical environment and climatic conditions suitable for the transmission vector during some season of the year (for a recent review, see [35]). Global warming is leading to the emergence of phlebotomine vectors in regions of the planet with cold continental climates. In the Iberian Peninsula, rising temperatures are causing the spread of sand flies to higher latitudes and altitudes than they had typically been found [4]. Phlebotominae are detected over longer annual periods due to earlier emergence from late February or early March and increasingly mild autumns, thereby delaying their disappearance until early December [36].
An example that confirms the importance of wildlife in the biological cycle of Leishmania was the outbreak of leishmaniasis caused by L. infantum that appeared in Madrid (Spain) in 2009–2012 due to the construction of a park near a residential area infested with hares and rabbits that caused more than 800 cases of leishmaniasis in humans [37].
The first reported case of CanL in wolves was described by Mohebali and coworkers in a seroprevalence study carried out in Iran to assess the impact of the disease in dogs [38]. In Europe, the first description of a dead grey wolf (Canis lupus) with visceral leishmaniasis caused by L. infantum was reported in central and southern parts of Dalmatia (Croatia), where the disease is endemic. The carcass of the animal, found dead in 2003, showed typical manifestations of the disease such as chronic dermatitis, generalized hair loss, scaling, skin erosions and ulcerations, cachexia, orchitis, lymphadenitis and hepatomegaly and splenomegaly, signs widely described in CanL. Parasitological diagnosis revealed the presence of found amastigotes in circulating macrophages. The PCR amplification of DNA samples was compatible with L. infantum [25,26].
The area sampled by us in the present study is one of the richest in wolves in the Iberian Peninsula due to the mountainous region of “Sierra de la Culebra”, which is an environmental heritage site and contains the largest wolf population. The Iberian Wolf Center “Félix Rodríguez de la Fuente” occupies a privileged position near this place, where it has maintained for years a stable population of 14 wolves in an area of 20 hectares where the animals are fed and watched over by specialized veterinarians and caretakers. Thanks to these facilities, we have been able to monitor their population for CanL prevalence using noninvasive sampling methods and detection based on the amplification of a specific region of L. infantum kinetoplast DNA via PCR. Wolf hair is a nontraumatic, easily accessible and safe site for wildlife sampling. L. infantum amplification in wolf hair samples was determined via PCR on an increasing number of hairs (5, 10 and 20) from a positive animal; amplification was observed from 10 hairs, and thus, the hair samples examined contained 10 individual hairs. Other non-invasive samples, such as those from buccal mucosa and ears, were in both cases collected by scraping with a swab, and they were also analyzed in this study for subsequent molecular analysis.
According to our findings, the prevalence of CanL obtained in the Iberian Wolf Center in the period 2018–2022 was high, estimated at 50%. This percentage can be as high as 57% when we add the positives found in other animals captured alive, sampled and subsequently released (Table 1). These values are much higher than those obtained with captive wolves under the European Endangered Species Breeding Programme (EEP), which covers different localities in the Iberian Peninsula and southern France. In this study, it was confirmed that 3 wolves out of a total of 33 individuals tested (9%) were PCR-positive with low levels of L. infantum DNA in peripheral blood [39]. Other studies have been carried out in captive animals from zoological parks far from their natural environment [40]. In a survey carried out with wild animals, including three wolves from a zoo of southeastern Spain, one of the three wolves (33.3%) tested positive for L. infantum via PCR analysis performed on a skin sample [29]. One (50%) of two wolves from a zoo in Murcia (southeastern Spain) sampled in the period 2008–2017 tested positive in the spleen, liver or skin via PCR targeting the ITS2 of L. infantum. An analysis of kDNA sequences revealed genotype 2 derived from a single nucleotide polymorphism (SNP) in a wolf, which is the same as that found in domestic dogs [25].
In our study, Leishmania-positive results obtained from samples of dead wolves show an incidence of 33.3% of the carcasses analyzed in the period 2017–2022 (Table 2). Several works have sampled dead wolves to find Leishmania DNA.
The results of the present work show a positivity rate to Leishmania of 6/18 samples from dead wolves, which represents an incidence of 33.3% of the carcasses analyzed in the period 2017–2022 (Table 2). In a prior study, in which spleen and blood samples were collected from 39 wolves in the period 1990–2007 from different regions of Spain [26], the mean positivity values were higher than 20.5% but with a higher incidence in Castilla y León (33.3%) than in Asturias (18.1%). In another study conducted in Asturias, blood samples and carcasses of 39 wolves collected during the period 2008–2010 from legal hunting, motor vehicle collisions or poisoning were analyzed via PCR using DNA extracted from mandibular lymph nodes. PCR analysis of the samples allowed us to determine a positivity rate of 46.2%, similar to the infection rate estimated in our study (46.1%), considering both live and dead animals. The presence of cutaneous lesions in 15 wolves was the only macroscopic alteration detected, but this could be due to coinfections with other pathogens [41].
Another retrospective study was also conducted in the Asturias region between 2008 and 2014 as part of an established wildlife health surveillance program. Using the remains of 102 necropsied wolves, a leishmaniasis seroprevalence of 33.3% was estimated; these values are lower than those provided in our results (46.1% considering the total rate of infection), with no differences between sex and age. A generalized positivity to Leishmania and an apparent increase in prevalence during this period were observed. According to these results, CanL does not seem to constitute a threat to the maintenance of Asturian wolf populations; thus, the authors propose that wolves may be useful sentinel species for the surveillance of L. infantum in field conditions [28].
It is very striking that Asturias, located in the north of Spain and considered non-endemic to leishmaniasis and phlebotome-free, has only a slightly lower prevalence than the province of Zamora, located 250 km further south, where the presence of phlebotomes and the occurrence of CanL in dogs is high [36]. These results are in line with the first leishmaniasis prevalence study conducted in the Piedmont region (northwestern Italy), where a 25.71% prevalence (CI95% 14.16–42.07) of wolves sampled after death by motor vehicle between 2009 and 2017 were positive for L. infantum as assessed using conventional PCR on spleen samples [42]. However, these values are much higher than those found in Iran in 2018, where the estimated infection rate was 10.2% [43].
From these studies, it is clear that the presence of Leishmania in wildlife, and more specifically in the wolf, is a proven fact that needs to be monitored not only at the level of systematic academic studies, but also during early disease control campaigns. Because the role of the wolf as a pathogen reservoir may be increasing with climate change, and linked with the fact that that vector is increasing its presence in higher and higher latitudes, leishmaniasis may turn into an emerging infection in larger nuclei of populations that had never been challenged before by this pathogen. In addition, in this work, we demonstrate the usefulness of hair samples for the diagnosis of this infection, which can help diagnose the infection without hunting the animal, as sometimes hair remains can be found in the habitats of these animals.

Author Contributions

Conceptualization, M.M.V. and R.B.F.; methodology, M.M.V., J.M.G. and V.C.G.d.A.; validation, M.M.V.; formal analysis, M.M.V.; investigation, V.C.G.d.A. and J.M.G.; resources, J.P.A. and M.M.V.; data curation, M.M.V. and R.B.F.; writing—original draft preparation, R.B.F.; writing—review and editing, R.B.F. and M.M.V.; supervision, M.M.V. and R.B.F. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Data Availability Statement

Data is unavailable due to privacy.

Acknowledgments

The authors acknowledge the Centro del Lobo Ibérico “Félix Rodríguez de la Fuente” and the Junta of Castilla y León.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Reguera, R.M.; Morán, M.; Pérez-Pertejo, Y.; García-Estrada, C.; Balaña-Fouce, R. Current status on prevention and treatment of canine leishmaniasis. Vet. Parasitol. 2016, 227, 98–114. [Google Scholar] [CrossRef] [PubMed]
  2. Ribeiro, R.R.; Michalick, M.S.M.; da Silva, M.E.; Dos Santos, C.C.P.; Frézard, F.J.G.; da Silva, S.M. Canine leishmaniasis: An overview of the current status and strategies for control. Biomed. Res. Int. 2018, 2018, 3296893. [Google Scholar] [CrossRef] [PubMed]
  3. Pennisi, M.G. Leishmaniosis of companion animals in Europe: An update. Vet. Parasitol. 2015, 208, 35–47. [Google Scholar] [CrossRef] [PubMed]
  4. Bravo-Barriga, D.; Ruiz-Arrondo, I.; Peña, R.E.; Lucientes, J.; Delacour-Estrella, S. Phlebotomine sand flies (Diptera, Psychodidae) from Spain: An updated checklist and extended distributions. Zookeys 2022, 1106, 81–99. [Google Scholar] [CrossRef]
  5. Travi, B.L.; Cordeiro-da-Silva, A.; Dantas-Torres, F.; Miró, G. Canine visceral leishmaniasis: Diagnosis and management of the reservoir living among us. PLoS Negl. Trop. Dis. 2018, 12, e0006082. [Google Scholar] [CrossRef]
  6. Meléndez-Lazo, A.; Ordeix, L.; Planellas, M.; Pastor, J.; Solano-Gallego, L. Clinicopathological findings in sick dogs naturally infected with Leishmania infantum: Comparison of five different clinical classification systems. Res. Vet. Sci. 2018, 117, 18–27. [Google Scholar] [CrossRef]
  7. Morales-Yuste, M.; Martín-Sánchez, J.; Corpas-Lopez, V. Canine leishmaniasis: Update on epidemiology, diagnosis, treatment, and prevention. Vet. Sci. 2022, 9, 387. [Google Scholar] [CrossRef]
  8. Vaselek, S. Canine Leishmaniasis in Balkan—A review of occurrence and epidemiology. Acta Trop. 2021, 224, 106110. [Google Scholar] [CrossRef]
  9. Baldi, L.; Mizzoni, V.; Guarino, A. Canine leishmaniasis in Campania: New and old foci. Parassitologia 2004, 46, 217–220. [Google Scholar]
  10. Le Rutte, E.A.; van der Wilt, L.S.; Bulstra, C.A.; Nieboer, D.; Kontoroupis, P.; de Vlas, S.J.; Richardus, J.H. Incidence and geographical distribution of canine leishmaniosis in 2016–2017 in Spain and France. Vet. Parasitol. Reg. Stud. Rep. 2021, 25, 100613. [Google Scholar] [CrossRef]
  11. Vélez, R.; Ballart, C.; Domenech, E.; Abras, A.; Fernández-Arévalo, A.; Gómez, S.A.; Tebar, S.; Muñoz, C.; Cairó, J.; Gállego, M. Seroprevalence of canine Leishmania infantum infection in the Mediterranean region and identification of risk factors: The example of North-Eastern and Pyrenean areas of Spain. Prev. Vet. Med. 2019, 162, 67–75. [Google Scholar] [CrossRef]
  12. Gálvez, R.; Montoya, A.; Cruz, I.; Fernández, C.; Martín, O.; Checa, R.; Chicharro, C.; Migueláñez, S.; Marino, V.; Miró, G. Latest trends in Leishmania infantum infection in dogs in Spain, Part I: Mapped seroprevalence and sand fly distributions. Parasit. Vectors 2020, 13, 204. [Google Scholar] [CrossRef]
  13. Baneth, G.; Koutinas, A.F.; Solano-Gallego, L.; Bourdeau, P.; Ferrer, L. Canine leishmaniosis—New concepts and insights on an expanding zoonosis: Part one. Trends Parasitol. 2008, 24, 324–330. [Google Scholar] [CrossRef]
  14. Shaw, S.E.; Langton, D.A.; Hillman, T.J. Canine leishmaniosis in the United Kingdom: A zoonotic disease waiting for a vector? Vet. Parasitol. 2009, 163, 281–285. [Google Scholar] [CrossRef]
  15. Maia, C.; Cardoso, L. Spread of Leishmania infantum in Europe with dog travelling. Vet Parasitol. 2015, 213, 2–11. [Google Scholar] [CrossRef]
  16. Rioux, J.A.; Albaret, J.L.; Houin, R.; Dedet, J.P.; Lanotte, G. Ecologie des leishmanioses dans le sud de la France. 2. Les réservoirs selvatiques. Infestation spontanée du Renard (Vulpes vulpes L.). Ann. Parasitol. Hum. Comp. 1968, 43, 421–428. [Google Scholar] [CrossRef]
  17. Sgroi, G.; Iatta, R.; Veneziano, V.; Bezerra-Santos, M.A.; Lesiczka, P.; Hrazdilová, K.; Annoscia, G.; D’Alessio, N.; Golovchenko, M.; Rudenko, N.; et al. Molecular survey on tick-borne pathogens and Leishmania infantum in red foxes (Vulpes vulpes) from southern Italy. Ticks Tick Borne Dis. 2021, 12, 101669. [Google Scholar] [CrossRef]
  18. Mitková, B.; Hrazdilová, K.; D’Amico, G.; Duscher, G.G.; Suchentrunk, F.; Forejtek, P.; Gherman, C.M.; Matei, I.A.; Ionică, A.M.; Daskalaki, A.A.; et al. Eurasian golden jackal as host of canine vector-borne protists. Parasit. Vectors 2017, 10, 183. [Google Scholar] [CrossRef]
  19. Lima, C.M.; Santarém, N.; Neves, N.C.; Sarmento, P.; Carrapato, C.; de Sousa, R.; Cardoso, L.; Cordeiro-da-Silva, A. Serological and molecular survey of Leishmania infantum in a population of Iberian Lynxes (Lynx pardinus). Microorganisms 2022, 10, 2447. [Google Scholar] [CrossRef]
  20. Del Río, L.; Chitimia, L.; Cubas, A.; Victoriano, I.; De la Rúa, P.; Gerrikagoitia, X.; Barral, M.; Muñoz-García, C.I.; Goyena, E.; García-Martínez, D.; et al. Evidence for widespread Leishmania infantum infection among wild carnivores in L. infantum periendemic northern Spain. Prev. Vet. Med. 2014, 113, 430–435. [Google Scholar] [CrossRef]
  21. Alcover, M.M.; Ribas, A.; Guillén, M.C.; Berenguer, D.; Tomás-Pérez, M.; Riera, C.; Fisa, R. Wild mammals as potential silent reservoirs of Leishmania infantum in a Mediterranean area. Prev. Vet. Med. 2020, 175, 104874. [Google Scholar] [CrossRef] [PubMed]
  22. Ortega-García, M.V.; Salguero, F.J.; Rodríguez-Bertos, A.; Moreno, I.; García, N.; García-Seco, T.; Luz Torre, G.; Domínguez, L.; Domínguez, M. A pathological study of Leishmania infantum natural infection in European rabbits (Oryctolagus cuniculus) and Iberian hares (Lepus granatensis). Transbound. Emerg. Dis. 2019, 66, 2474–2481. [Google Scholar] [CrossRef] [PubMed]
  23. Azami-Conesa, I.; Martínez-Díaz, R.A.; González, F.; Gómez-Muñoz, M.T. First detection of Leishmania infantum in common urban bats Pipistrellus pipistrellus in Europe. Res. Vet. Sci. 2020, 132, 172–176. [Google Scholar] [CrossRef] [PubMed]
  24. Navea-Pérez, H.M.; Díaz-Sáez, V.; Corpas-López, V.; Merino-Espinosa, G.; Morillas-Márquez, F.; Martín-Sánchez, J. Leishmania infantum in wild rodents: Reservoirs or just irrelevant incidental hosts? Parasitol. Res. 2015, 114, 2363–2370. [Google Scholar] [CrossRef]
  25. Ortuño, M.; Latrofa, M.S.; Iborra, M.A.; Pérez-Cutillas, P.; Bernal, L.J.; Risueño, J.; Muñoz, C.; Bernal, A.; Sánchez-López, P.F.; Segovia, M.; et al. Genetic diversity and phylogenetic rela-tionships between Leishmania infantum from dogs, humans and wildlife in south-east Spain. Zoonoses Public Health 2019, 66, 961–973. [Google Scholar] [CrossRef]
  26. Beck, A.; Beck, R.; Kusak, J.; Gudan, A.; Martinković, F.; Artuković, B.; Hohšteter, M.; Huber, Đ.; Marinculić, A.; Grabarević, Ž. A case of visceral leishmaniosis in a gray wolf (Canis lupus) from Croatia. J. Wildl. Dis. 2008, 44, 451–456. [Google Scholar] [CrossRef]
  27. Sobrino, R.; Ferroglio, E.; Oleaga, A.; Romano, A.; Millán, J.; Revilla, M.; Arnal, M.C.; Trisciuoglio, A.; Gortázar, C. Characterization of widespread canine leishmaniasis among wild carnivores from Spain. Vet. Parasitol. 2008, 155, 198–203. [Google Scholar] [CrossRef]
  28. Oleaga, A.; Zanet, S.; Espí, A.; Pegoraro de Macedo, M.R.; Gortázar, C.; Ferroglio, E. Leishmania in wolves in northern Spain: A spreading zoonosis evidenced by wildlife sanitary surveillance. Vet. Parasitol. 2018, 255, 26–31. [Google Scholar] [CrossRef]
  29. Risueño, J.; Ortuño, M.; Pérez-Cutillas, P.; Goyena, E.; Maia, C.; Cortes, S.; Campino, L.; Bernal, L.J.; Muñoz, C.; Arcenillas, I.; et al. Epidemiological and genetic studies suggest a common Leishmania infantum transmission cycle in wildlife, dogs and humans associated to vector abundance in Southeast Spain. Vet. Parasitol. 2018, 259, 61–67. [Google Scholar] [CrossRef]
  30. Piscopo, N.; Gentile, L.; Scioli, E.; Eguren, V.G.; Carvajal Urueña, A.M.; García, T.Y.; Alberti, J.P.; Esposito, L. Management models applied to the human-wolf conflict in agro-forestry-pastoral territories of two Italian protected areas and one Spanish game area. Animals 2021, 11, 1141. [Google Scholar] [CrossRef]
  31. Sáenz de Buruaga, M.; Canales, F.; Campos, M.A.; Noriega, A.; Muñoz, F.J.; Navamuel, N. Censo Regional de Lobo (Canis lupus) en Castilla y León; Consejería de Fomento y Medio Ambiente de la Junta de Castilla y León y Ministerio de Agricultura, Alimentación y Medio Ambiente, (TRAGSATEC); Consultora de Recursos Naturales, S.L.: Gasteiz, Spain, 2015. [Google Scholar]
  32. Fernández-Gil, A.; Barrientos, L.M.; Nuño Nuño, Á.; Naves Cienfuegos, J.; Ordiz, A.; Quevedo, M.; Revilla, M. Estimaciones de Tamaño de Grupo: Implicaciones para la Conservación y Gestión de las Poblaciones Ibéricas de Lobos III Congreso Ibérico del Lobo; Asociación Galega de Custodia do Territorio: Lugo, Spain, 2012. [Google Scholar]
  33. Centro del Lobo Ibérico de CyL—Félix Rodríguez de la Fuente. Available online: https://centrodellobo.es/ (accessed on 22 February 2021).
  34. Geisweid, K.; Weber, K.; Sauter-Louis, C.; Hartmann, K. Evaluation of a conjunctival swab polymerase chain reaction for the detection of Leishmania infantum in dogs in a non-endemic area. Vet. J. 2013, 198, 187–192. [Google Scholar] [CrossRef]
  35. Azami-Conesa, I.; Gómez-Muñoz, M.T.; Martínez-Díaz, R.A. A systematic review (1990–2021) of wild animals infected with zoonotic Leishmania. Microorganisms 2021, 9, 1101. [Google Scholar] [CrossRef]
  36. European Centre for Disease Prevention and Control and European Food Safety Authority. Mosquito Maps; ECDC: Stockholm, Sweden, 2021; Available online: https://ecdc.europa.eu/en/disease-vectors/surveillance-and-disease-data/phlebotomine-maps (accessed on 22 March 2023).
  37. Arce, A.; Estirado, A.; Ordobás, M.; Sevilla, S.; García, N.; Moratilla, L.; de la Fuente, S.; Martínez, A.M.; Pérez, A.M.; Aránguez, E.; et al. Re-emergence of leishmaniasis in Spain: Community outbreak in Madrid, Spain, 2009 to 2012. Euro Surveill. 2013, 18, 20546. [Google Scholar] [CrossRef]
  38. Mohebali, M.; Hajjaran, H.; Hamzavi, Y.; Mobedi, I.; Arshi, S.; Zarei, Z.; Akhoundi, B.; Naeini, K.M.; Avizeh, R.; Fakhar, M. Epidemiological aspects of canine visceral leishmaniosis in the Islamic Republic of Iran. Vet. Parasitol. 2005, 129, 243–251. [Google Scholar] [CrossRef]
  39. Sastre, N.; Francino, O.; Ramírez, O.; Enseñat, C.; Sánchez, A.; Altet, L. Detection of Leishmania infantum in captive wolves from Southwestern Europe. Vet. Parasitol. 2008, 158, 117–120. [Google Scholar] [CrossRef]
  40. Souza, T.D.; Turchetti, A.P.; Fujiwara, R.T.; Paixão, T.A.; Santos, R.L. Visceral leishmaniasis in zoo and wildlife. Vet. Parasitol. 2014, 200, 233–241. [Google Scholar] [CrossRef]
  41. Oleaga, A.; Vicente, J.; Ferroglio, E.; Pegoraro de Macedo, M.R.; Casais, R.; del Cerro, A.; Espí, A.; García, E.J.; Gortázar, C. Concomitance and interactions of pathogens in the Iberian wolf (Canis lupus). Res. Vet. Sci. 2015, 101, 22–27. [Google Scholar] [CrossRef]
  42. Battisti, E.; Zanet, S.; Khalili, S.; Trisciuoglio, A.; Hertel, B.; Ferroglio, E. Molecular survey on vector-borne pathogens in alpine wild carnivorans. Front. Vet. Sci. 2020, 7, 1. [Google Scholar] [CrossRef]
  43. Mohebali, M.; Moradi-Asl, E.; Rassi, Y. Geographic distribution and spatial analysis of Leishmania infantum infection in domestic and wild animal reservoir hosts of zoonotic visceral leishmaniasis in Iran: A systematic review. J. Vector Borne Dis. 2018, 55, 173–183. [Google Scholar]
Microorganisms 11 01179 g001 550
Figure 1. Distribution map of sampled and PCR-positive wolves (green areas) studied in Zamora (northwestern Spain) for the detection of Leishmania DNA from 2017 to 2022.
Figure 1. Distribution map of sampled and PCR-positive wolves (green areas) studied in Zamora (northwestern Spain) for the detection of Leishmania DNA from 2017 to 2022.
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Microorganisms 11 01179 g002 550
Figure 2. Detection of kinetoplast Leishmania DNA in hair of wolves infected with L. infantum. M: molecular weight ladder. PCR for the NCX1 or L. infantum (Li) amplification with 5, 10 or 20 hairs. In addition, positive (NCX_+ and Li_+) and negative (NCX_− and Li_−) controls were included in the reaction.
Figure 2. Detection of kinetoplast Leishmania DNA in hair of wolves infected with L. infantum. M: molecular weight ladder. PCR for the NCX1 or L. infantum (Li) amplification with 5, 10 or 20 hairs. In addition, positive (NCX_+ and Li_+) and negative (NCX_− and Li_−) controls were included in the reaction.
Microorganisms 11 01179 g002
Table
Table 1. PCR detection of Leishmania infantum in different samples of live captures and from the Iberian Wolf Center “Felix Rodríguez de la Fuente” (2017–2022), Zamora (Northwest Spain), including source, date sampling sex, age and site of sampling (R. ear: right ear; L. ear: left ear).
Table 1. PCR detection of Leishmania infantum in different samples of live captures and from the Iberian Wolf Center “Felix Rodríguez de la Fuente” (2017–2022), Zamora (Northwest Spain), including source, date sampling sex, age and site of sampling (R. ear: right ear; L. ear: left ear).
Name (Id.)Sample SourceDateGenderYearsMouthR. EarL. EarHair
La AlbañezaLive capture8 November 2017female5---n.d. *
LobeznosLive capture17 March 2018male7.5-+n.d.n.d.
BrevanasLive capture23 October 2018female0.5+--n.d.
CabañasLive capture23 October 2018female0.5---n.d.
PereruelaLive capture4 December 2018female1.5+--n.d.
MahideLive capture10 December 2018male0.5+--n.d.
BrasaIberian Wolf Center21 March 2018female6++n.d.+
El CasalLive capture18 October 2019male0.5+--n.d.
DakotaIberian Wolf Center23 March 2021female9+++-
ClaritaIberian Wolf Center7 May 2021female10---n.d.
SauronIberian Wolf Center7 May 2021male10--+n.d.
JaraIberian Wolf Center7 May 2021female8---n.d.
OscuraIberian Wolf Center7 May 2021female10n.d.--n.d.
AtilaIberian Wolf Center10 November 2021male9---n.d.
LlaguIberian Wolf Center10 November 2021male2---n.d.
RobledoIberian Wolf Center10 November 2021male6---n.d.
SanabriaIberian Wolf Center2 February 2022female3n.d.n.d.n.d.+
TeraIberian Wolf Center2 February 2022female3n.d.n.d.n.d.-
FelixIberian Wolf Center3 February 2022male1n.d.n.d.n.d.+
NieblaIberian Wolf Center3 February 2022female1n.d.n.d.n.d.+
LunaIberian Wolf Center3 February 2022female1n.d.n.d.n.d.+
* n.d.: not determined.
Table
Table 2. PCR detection of Leishmania infantum in different samples obtained from dead Iberian wolves (2017–2022) from the province of Zamora (Northwest Spain), including source, date sampling sex, age and site of sampling (R. ear: right ear; L. ear: left ear).
Table 2. PCR detection of Leishmania infantum in different samples obtained from dead Iberian wolves (2017–2022) from the province of Zamora (Northwest Spain), including source, date sampling sex, age and site of sampling (R. ear: right ear; L. ear: left ear).
Sampling PlaceDateCause of DeathGenderYearsMouthR. EarL. EarHair
Puebla de Sanabria 210 November 17Motor vehiclemale5---n.d. *
Palacios de Sanabria10 January 18Motor vehiclemale3n.d.++n.d.
Puebla de Sanabria 31 March 18Motor vehiclemale2.5-++n.d.
Puebla de Sanabria2 March 18Motor vehiclemale2.5-n.d.n.d.n.d.
Cañizo1 October 18Motor vehiclefemale7.5+--n.d.
Vega del Castillo1 February 19Fightingmale5+n.d.n.d.n.d.
San Cebrián16 April 20Motor vehiclefemale4-n.d.n.d.-
Ayoo18 December 20Legal huntingmale4-n.d.n.d.+
Perilla de Castro30 January 21Legal huntingmale5---n.d.
Cerezal23 February 21Motor vehiclemale4---+
Santovenia12 March 21Motor vehiclemale5-n.d.n.d.n.d.
Burganes12 March 21Legal huntingmale4-n.d.n.d.n.d.
Torres del Carrizal 26 July 21Motor vehiclemale4-n.d.n.d.n.d.
Torres del Carrizal5 September 21Motor vehiclemale1---n.d.
Cerezal de Aliste1 March 22Motor vehiclemale4-n.d.n.d.n.d.
Puebla de Sanabria1 March 22Motor vehiclemale3-n.d.n.d.n.d.
Villanueva8 March 22Motor vehiclemale2-n.d.n.d.n.d.
Gallegos del Río8 March 22Motor vehiclemale3-n.d.n.d.n.d.
* n.d.: not determined.
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Merino Goyenechea, J.; Castilla Gómez de Agüero, V.; Palacios Alberti, J.; Balaña Fouce, R.; Martínez Valladares, M. Occurrence of Leishmaniasis in Iberian Wolves in Northwestern Spain. Microorganisms 2023, 11, 1179. https://doi.org/10.3390/microorganisms11051179

AMA Style

Merino Goyenechea J, Castilla Gómez de Agüero V, Palacios Alberti J, Balaña Fouce R, Martínez Valladares M. Occurrence of Leishmaniasis in Iberian Wolves in Northwestern Spain. Microorganisms. 2023; 11(5):1179. https://doi.org/10.3390/microorganisms11051179

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Merino Goyenechea, Javier, Verónica Castilla Gómez de Agüero, Jesús Palacios Alberti, Rafael Balaña Fouce, and María Martínez Valladares. 2023. "Occurrence of Leishmaniasis in Iberian Wolves in Northwestern Spain" Microorganisms 11, no. 5: 1179. https://doi.org/10.3390/microorganisms11051179

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