Skip to main content
Download PDF

Twenty-year evolution of Leishmania infantum infection in dogs in Valdeorras (Galicia, Northwestern Spain): implication of climatic factors and preventive measures

Parasites & Vectors volume 17, Article number: 281 (2024) Cite this article

Abstract

Background

Abiotic factors play a significant role in the evolution of Leishmania infantum infection due to its vectorial nature. This study aims to assess the evolution in the detection of new L. infantum infection cases in Valdeorras (Ourense, Northwestern Spain) over a 20-year period and how different climatic variables and preventive measures may have affected it.

Methods

Indirect immunofluorescence antibody tests (IFAT) were performed on serum samples collected from dogs attending the ‘Servicios Veterinarios de Sil’ veterinary clinic (Valdeorras, Northwestern Spain) between May 2003 and April 2023 to detect L. infantum exposure. The percentage of new cases of L. infantum infection was calculated from May of one year to April of the following year. Climatic conditions in the region, global sales of ectoparasiticides and the number of vaccines against L. infantum delivered in the veterinary clinic from 2003 to 2022 were recorded. Statistical analyses were conducted to determine the associations between these factors and the percentage of new cases of L. infantum infection.

Results

A total of 2909 dogs were assessed, and 3785 IFAT tests were performed between May 2003 and April 2023. The mean percentage of new seropositive cases over the 20-year period studied was 21.65 ± 10.8%, with a decline from the beginning to the end of the period studied. The percentage was significantly higher between May 2003 and April 2008 compared with the other periods (May 2008 to April 2013, May 2013 to April 2018 and May 2018 to April 2023). There was a positive correlation between the percentage of new cases of L. infantum infection and the maximum relative humidity in winter. Conversely, there was a negative correlation between the percentage of new cases and sales of ectoparasiticides and vaccination against L. infantum.

Conclusions

This study is one of the longest evaluations of the evolution of L. infantum infection in a fixed location and its association with external factors including climatic conditions and preventive measures. The results confirm that Valdeorras is a high-risk area for L. infantum infection. The use of ectoparasiticides and vaccines against L. infantum has been shown to play a significant role in preventing L. infantum infection, highlighting the crucial role of veterinarians in the fight against this disease.

Graphical Abstract

Background

Canine leishmaniosis (CanL) is a disease caused in Spain by the protozoan Leishmania infantum [1, 2]. Dogs constitute the main reservoir for this parasite [1,2,3,4]. Although occasional vertical and horizontal transmission has been described [2,3,4,5], the main mode of transmission in Europe is the bite of an infected female phlebotomine sand fly (Phlebotomus perniciosus and P. ariasi) [3, 4, 6]. Traditionally, the geographical distribution of phlebotomine sand flies had been estimated to be between 50° north and 40° south latitudes [3, 7]. However, as predicted by some authors, the distribution has expanded beyond these latitudes [8,9,10,11,12].

In this context, Northwestern Spain was traditionally considered a leishmaniosis-free region, presumably because its cold and rainy climate limits the presence of sand flies [13, 14]. Nevertheless, two cases of apparently autochthonous canine leishmaniosis were reported in Galicia in the early 1990s [15]. In addition, a seroprevalence study carried out in the early 2000s in Valdeorras (Ourense, Galicia, Spain) changed the perception of the disease in this area, being henceforth considered hyperendemic for L. infantum infection [13]. The prevalence of L. infantum infection reported in Galicia ranges from 2.5% to 7.5% [13, 14, 16], while in Ourense it has been found to be higher, from 7.5% to 35.6% depending of the studies and their methodology [5, 13, 17]. Ourense presents a particular supra-Mediterranean climate, which distinguishes it from other nearby regions in northern Spain belonging to the temperate bioclimatic zone, where the prevalence of L. infantum infection is lower [5].

The main phlebotomine species vectors of L. infantum described in these areas are Phlebotomus perniciosus and P. ariasi [5, 18,19,20]. Phlebotomus ariasi is less abundant and is found in more localised regions due to its preference for colder, more humid and mountainous climates, as well as for higher altitudes [5, 7, 9, 18, 21,22,23,24]. Phlebotomus perniciosus is more widespread because it is less affected by climatic conditions. It prefers drier and warmer environments and is found at lower altitudes than P. ariasi [5, 9, 18, 25]. Both P. perniciosus and P. ariasi have been previously reported in Ourense Province [5, 19]. It is considered that the phlebotomine sand fly season in Spain begins in early May, although in some regions it has been reported as early as April, and ends between late October and November, with its peak activity between July and September [3, 4, 26,27,28]. It is determined by the climatic conditions of the region, such as temperature, relative humidity and wind speed [20, 29]. Any change in the environment alters the ecological balance and the context in which parasites and vectors reproduce and transmit disease [30, 31].

The main measures for the prevention of L. infantum infection include the use of ectoparasiticides as the most effective strategy, accompanied by the vaccination of healthy seronegative dogs against L. infantum to prevent the development of the disease and reduce the risk of transmission [4, 32, 33].

The aim of this study was to assess the evolution of the percentage of annual new cases of L. infantum infection over a 20-year period (2003–2023) in a specific area with a known high prevalence of the parasite (Valdeorras, Ourense, Northwestern Spain). Furthermore, considering the multitude of factors influencing the presence of L. infantum infection in a given area, we aimed to determine the possible influence of certain climatic variables and preventive measures implemented over the time on this L. infantum infection incidence. We hypothesised that the percentage of newly detected cases in this area has decreased over the 20-year period. We further suggested that climatic variables that potentially could impact the vector and its habitat, along with implemented preventive measures, are interrelated factors that could potentially influence the incidence of L. infantum infection.

Methods

Study design

This retrospective longitudinal study was conducted in O Barco de Valdeorras, Ourense, Galicia (Northwest Spain: 42° 25′ 0″ N, 6° 58′ 59″ W), which occupies a portion of the alluvial plain of the Sil River, nestled amidst the surrounding mountain ranges. It represents a narrow and deep tectonic trench, along which the river follows the course dictated by a network of fractures. The municipality’s altitude ranges from 310 to 1537 m, being the village at an elevation of 326 m above sea level. It hosts a population of 13,277 inhabitants, with no significant variations since 2003 up to the present day. All the samples were collected at the ‘Servicios veterinarios de Sil’ veterinary clinic over a 20-year period (from May 2003 to April 2023). Four practices are currently working in O Barco de Valdeorras, but this clinic was the first to be open in the municipality.

The study included dogs tested for L. infantum infection by indirect immunofluorescence antibody test (IFAT) based on practitioners’ clinical criteria, including prophylactic health check-up plans, regardless the presence or absence of clinical signs compatible with CanL. Practitioners responsible for the recruitment of samples were the same during the entire period of study. Dogs that had been vaccinated against leishmaniosis or that had previously tested positive were excluded.

IFAT serodiagnosis

Serum of canine blood samples (25 µL) was used for diagnosis at the Canine Leishmaniosis and Ehrlichiosis Diagnostic Service of the Complutense Veterinary Teaching Hospital of the Complutense University of Madrid. Serodiagnosis was performed by detecting specific antibodies against L. infantum using the indirect immunofluorescence antibody test (IFAT) for anti-Leishmania-specific immunoglobulin G (IgG) antibodies as previously described [34,35,36]. Antigen was obtained from a culture of promastigotes of L. infantum L-75 established in Novi, McNeal and Nicolle medium. Plates were examined using an Olympus BH-2® epifluorescence microscope (Olympus Imaging America Inc., Center Valley, Pennsylvania, United States) with a blue filter and ×400 objective.

Serodiagnosis data collection

Each sample was identified with a laboratory registration number and was blindly analysed. The IFAT result of each sample was classified as positive (≥ 1/100) or negative (< 1/100), considering the established cut-off (1/100).

The percentage of new cases of L. infantum infection was calculated for 12-month periods (total of 20 periods) from May of one year to April of the following year, corresponding to the sand fly season. For the analysis comparison, the data were grouped in four clusters: May 2003 to April 2008, May 2008 to April 2013, May 2013 to April 2018 and May 2018 to April 2023.

Climatic variables

The dataset utilised in this study compromises daily measurements of precipitation (mm), temperature (°C) and relative humidity (%) spanning the period from 2003 to 2022 in Valdeorras. These data were sourced from the Spanish Meteorological Agency (AEMET), considering the official data provided by the meteorological observatory located in O Barco de Valdeorras. This observatory was located 650 m away from the veterinary clinic where this study was performed. Parameters including mean, maximum and minimum values for temperature, total precipitation, and maximum and minimum relative humidity were recorded for each season: spring (March–May), summer (June–August), autumn (September–November) and winter (December–February).

Furthermore, aggregate metrics were computed, encompassing total annual precipitation, precipitation of the wettest month and season, precipitation of the driest season, precipitation of the warmest and coolest seasons, mean temperatures of the warmest and coolest seasons, and the lowest and mean minimum temperatures for the month of July for each year within the study period. These variables have been previously reported to potentially influence the development of Phlebotomus or the prevalence of canine leishmaniosis [8, 20, 23, 28, 37, 38].

Ectoparasiticides and vaccinations against canine leishmaniosis

Data were collected from the overall annual sales of ectoparasiticides and the annual number of vaccinations against canine leishmaniosis administered at the ‘Servicios veterinarios del Sil’’ veterinary clinic during the study period (2003–2022).

Statistical analysis

The results were statistically analysed using the IBM SPSS Statistics software v.29.0.2.0 (IBM, Armonk, NY, USA). Significant differences among the percentages of new positive dogs for L. infantum infection in the different periods of time were analysed using the chi-square test. As the Shapiro–Wilk test indicated a lack of normal distribution, a Spearman’s correlation analysis was employed to evaluate the relationship between the percentage of new positive cases and climatic variables. Considering the sand fly season and the time needed for L. infantum antibody production after infection, for seasonal variables, data were collected from winter and spring from the same year and from summer and autumn from the previous year [20, 23, 26]. Additionally, sales of ectoparasiticides in dogs and vaccinations against canine leishmaniosis were also assessed using Spearman’s correlation test. The linear trend of the variables over time was analysed and graphically represented using GraphPad Prism 9.4 software (GraphPad Software, Boston, Massachusetts, USA). A statistically significant difference was set at P < 0.05.

Results

A total of 2909 dogs met the inclusion criteria during this period. Globally, a total of 3785 IFAT tests were conducted. There are more IFATs than dogs because some of them had the test performed several times over their life during the 20-year period of study.

The percentage of new L. infantum infection cases was calculated for each sand fly season, as outlined in Table 1. The mean percentage of new seropositive cases over the 20-year period studied was 21.65 ± 10.8%. These percentages, classified into grouped clusters were as follows: 35.3% (May 2003 to April 2008), 17.9% (May 2008 to April 2013), 18.8% (May 2013 to April 2018) and 12.9% (May 2018 to April 2023). The results obtained in the first cluster (May 2003 to April 2008) were significantly higher than those of subsequent groups, while the fourth cluster (May 2018 to April 2023) showed significant lower values (χ2 = 112.553, df = 3, P < 0.001), indicating a decreasing linear trend as illustrated in Fig. 1.

Table 1 Percentage of new L. infantum infection cases in the sandfly seasons from May 2003 to April 2023
Full size table
Fig. 1
figure 1

Annual percentage of new L. infantum infection cases. Trend over phlebotomine sand fly activity seasons. The line represents the linear trend (P < 0.0001, R2 = 0.581), indicating a decreasing trend. Each data point corresponds to the percentage (%) of new L. infantum infection cases diagnosed annually, using the period season of the phlebotomine sand fly activity

Full size image

Seasonal precipitation, temperature and relative humidity in Valdeorras from 2003 to 2022 are presented in Tables 2 and 3. The wettest season varied from year to year among spring, autumn and winter. Based on the series of data available, the wettest year was 2016 (1019.5 mm), with an especially rainy winter (550.7 mm), while the driest year was 2004 (344.4 mm) (Table 2). The driest season was mainly summer, except for the autumn of 2007, spring of 2009 and winter of 2012 (Table 3). The lowest total precipitation recorded during the driest season of all the years with available data was 35.2 mm in summer of 2008. The warmest season recorded was always summer, with the highest mean temperature of 24.3 °C in 2022. Conversely, the summer’s lowest mean temperature was 20.8 °C in 2007. Winter was consistently the coldest season, with the highest mean temperature of 8.7 °C in both 2016 and 2020. The lowest minimum temperature in July over the 20-year period of study, was recorded in 2012 at 7.5 °C. Additionally, the lowest mean minimum temperature in July was recorded in 2009 at 13.9 °C.

Table 2 Seasonal precipitation, temperature and relative humidity in Valdeorras from 2003 to 2022
Full size table
Table 3 Selected climate characteristics in Valdeorras from 2003 to 2022
Full size table

Table 4 presents the overall sales of ectoparasiticides and vaccinations against L. infantum infection in the clinic. From 2003 to 2022, a total of 3702 ectoparasiticides were sold in the ‘Servicios veterinarios de Sil’ veterinary clinic. The highest sales were recorded in 2018, and the lowest were in 2013. CanL vaccination began at the veterinary clinic in 2012, with the highest number of vaccinations recorded in that year, followed by 2022. The lowest recorded vaccination rate was in 2014. By 2022, a total of 816 CanL vaccines have been administered at the veterinary clinic.

Table 4 Global sales of ectoparasiticides and vaccinations against CanL at the ‘Servicios veterinarios de Sil’ veterinary clinic from 2003 to 2022
Full size table

The higher the maximum relative humidity in winter (Spearman's rank correlation coefficient (rs) = 0.60, P = 0.029), the greater the percentage of new L. infantum infection cases. This maximum relative humidity in winter showed a significant linear decline over time when data were available (Fig. 2).

Fig. 2
figure 2

Maximum relative humidity (RH) in winter. Trend from 2009 to 2022. The line represents the linear trend (P = 0,003, R2 = 0.571), indicating a decreasing trend. Each data point corresponds to the mean maximum relative humidity in winter (December of the previous year to February of the following year)

Full size image

Although not statistically significant, other climatic variables were correlated close to statistical significance with the percentage of positive dogs. This was the case for the maximum (rs = 0.39, P = 0.095) and the mean (rs = 0.42, P = 0.071) temperature in summer, which were positively correlated with the percentage of new positive cases.

With regard to prophylactic measures, higher sales of ectoparasiticides in the practice were correlated with a decrease in new L. infantum infection cases (rs = −0.56, P = 0.010). Similarly, there was a moderate negative correlation (rs = −0.52, P = 0.018) between the percentage of new L. infantum infection cases and vaccination against the disease in dogs.

Discussion

To the best of our knowledge, this study, along with a recently published study in Spain [39], represents one of the most extensive longitudinal retrospective analyses of L. infantum serological status in owned dogs within our geographical area. Following the fundamental work of Amusategui et al. [13], which profoundly changed the understanding of L. infantum infection dynamics in Valdeorras and Ourense, subsequent investigations have explored the disease landscape in this region [5, 14, 16, 17].

The mean percentage of new seropositive cases to L. infantum infection identified over the 20-year duration of this study (21.65 ± 10.8%) aligns with the classification established by Gálvez et al. [5] of Ourense as a hyperendemic area (seroprevalence > 17%). In northern Spain, the seroprevalence of L.infantum infection is higher than in the rest of the Iberian Peninsula. Nonetheless, Ourense has been found to have high seroprevalences due to its highly suitable climatic conditions for L. infantum expansion [5]. The potential bias resulting from differences in methodology must be carefully considered when analysing the differences between this result and the seroprevalences obtained in previous studies [5, 13, 14, 17]. Some authors have used different Leishmania diagnostic tests (rapid test or ELISA) [14, 16], while others performed IFAT as done in this study [5, 13, 17]. It is important to consider that our study only used the first seropositive detection for each dog, whereas other studies determined the overall seroprevalence without making this distinction [5, 14, 16, 17].

Additionally, the number of positive dogs in our study may be different than in the overall community. On the one hand, considering the specific characteristics of a population attended in a veterinary clinic, this number can be higher due to a biased population of sick animals [40]. However, on the other hand, dogs attended in a veterinary practice usually have lower prevalences of the disease than other populations such as stray dogs, as previously shown in the same area of study [14].

The higher percentage of new seropositive cases observed during the initial lustrum (May 2003 to April 2008, 35.3%) may be attributed to the limited awareness and understanding of CanL among both pet owners and veterinarians within the region at that time. This lack of awareness might have resulted in a lower testing for the disease during routine health check-ups. Consequently, as previously shown in the area [14], fewer animals were being tested, and of those analysed, a greater proportion would have been found to be seropositive for L. infantum infection. As CanL gained greater attention within the veterinary community in this area, practitioners likely increased their focus on early diagnosis and prevention, as well as raising awareness among dog owners. This shift in approach could theoretically be one of the reasons that explains the decline in the number of new positive cases over time, despite the presence of potential favourable weather conditions for sand fly development. Similar explanations have been recently proposed for the declining prevalence of other vector-borne pathogens, such as Dirofilaria immitis [41].

Historically, dogs in rural areas of Spain, like Valdeorras, often lived outdoors, increasing their exposure to sand flies and, consequently, to L. infantum infection [14, 42,43,44]. However, contemporary trends indicate a shift towards dogs living indoors and experiencing improved lifestyles. This change, coupled with the implementation of enhanced preventive measures and disease management strategies, could also contribute to the observed decrease in the prevalence of infected dogs [43].

Regarding environmental factors, this study found a positive correlation between the maximum relative humidity during winter and new cases of L. infantum infection, corroborating the results of Risueño et al. [20]. They observed a positive association between maximum relative humidity from November to April and the presence of sand flies, which indirectly correlates with subsequent leishmaniosis cases [20]. This positive correlation could be attributed to the necessity of a humid environment for sand fly development [20, 45, 46]. However, it should be interpreted with caution since different variables acting simultaneously, such as the exact household of every dog and other climatic, ecological or sociological factors, may act as confounding factors.

The amount of rainwater could, on the one hand, promote the presence of organic matter (i.e. vegetation) essential for the vector’s biological cycle [20, 29, 47]. Conversely, the same rainfall might impede the sand fly’s flight. However, no correlation was found between recorded precipitation and the percentage of new cases of L. infantum infection in our study, which can be interpreted as a reflection of the lack of association between precipitation and sand fly presence observed in another study [7].

Temperature stands out as one of the most influential climatic factors affecting leishmaniosis transmission and sand fly ecology [7, 20, 37, 48]. However, different authors have reported conflicting results on its influence on sand fly presence, abundance or density and, consequently, in L. infantum transmission. Some studies have indicated that higher temperatures correlate with increased sand fly occurrence [7, 24, 26, 49, 50] and human leishmaniosis incidence [29, 37], while others have found no association or even a negative influence [47]. Variations in results could be attributed to factors such as the species of phlebotomine analysed, the specific bioclimatic area under study, or differences in the methods used to assess climatic data [8, 22, 47, 48, 51]. In our study, a certain trend towards significance was detected between an increase in maximum or mean temperature of the warmest season (summer) and an increased incidence of L. infantum infection. Although it has been established that sand flies remain active at a minimum temperature of 17 °C [28], our findings do not reveal a significant relationship between the lowest minimum temperature or the mean minimum temperature of the month of July (the month associated with the maximum risk of L. infantum transmission [28]) and the number of positive cases. The lowest minimum temperature recorded in July in Valdeorras consistently fell below 17 °C, with only two instances (2006 and 2022) showing a slight elevation in the mean minimum temperature. Nevertheless, it is worth noting that sand flies frequently seek refuge in burrows or shelters where temperatures may not dip as low [27, 28, 50].

Although this study has spanned a considerable length of time, its sample size (n = 20) precludes the possibility of conducting multivariate analysis with statistically significant outcomes. Thus, while the climatic findings are intriguing, a more extensive dataset may be necessary to accurately evaluate the impact of climate change. On the other hand, due to the retrospective nature of the study, we were unable to assess some other interesting climatic variables such as wind in this article.

These findings highlight the critical importance of preventive measures against canine leishmaniosis, particularly given the current trends in climatic variables potentially favouring the development of vector-borne disease. The results of the current study support this, considering the reduction in the proportion of newly reported positive cases in the area as annual sales of all types of ectoparasiticides and vaccination against L. infantum rates increase. In a recent article that examined preventive measures against L. infantum infection in dogs in Europe, repellents were the only measures that showed a small increase each year [44]. These results are consistent with the statement that one of the best preventive strategies against L. infantum in dogs is the use of external parasiticides that prevent phlebotomine sand flies from biting [2, 28, 32]. However, it is important to acknowledge certain limitations regarding the collection data in our study. It would have been interesting to have specific data about the use of repellents specifically registered for the prophylaxis of L. infantum infection. However, considering the long period of study and its retrospective nature, data were only accessible for overall sales in the clinic. Additionally, it is common for pet owners in our country to procure these products from external suppliers, potentially leading to even higher usage than what is recorded internally. The sale of ectoparasiticides for dogs at a specific veterinary clinic could reflect the proactive commitment of pet owners and practitioners to take care of their pets’ health, particularly in preventing parasitic diseases. The optimal prophylactic protocol for preventing L. infantum infection also involves the vaccination of healthy seronegative dogs in addition to the use of ectoparasiticides [2, 28, 32]. Vaccines currently available do not prevent the infection but diminish the risk of developing the disease [4, 28]. ‘Servicios veterinarios de Sil’ started vaccinating dogs against L. infantum in 2012, the year when the first vaccine was commercialised in Spain. In this context, one of the reasons for not including vaccinated dogs in our study was the description of cross-reactions between antibodies from vaccination and from natural infection, leading to potential misinterpretation of the IFAT [4]. Furthermore, by not including vaccinated dogs, some infected animals may have been overlooked.

Data from this study reflect the challenging situation of L. infantum infection during a very long period, in practice, in a specific area from Northwestern Spain, where the situation of the disease has been changing during the last decades. These results cannot be directly extrapolated to the general population. However, the extended follow-up period further emphasises the significance and importance of this study’s findings. By analysing data trends, veterinarians can gain valuable insights into the prevalence, distribution and progression of this disease in dogs. Furthermore, this study serves as a potential tool in informing veterinary practices and public health initiatives aimed at controlling canine leishmaniosis.

Conclusions

To our knowledge, this is one of the longest studies evaluating the evolution of L. infantum infection in owned dogs in a fixed location and its association with external factors such as climatic conditions and preventive measures. The results obtained confirm that Valdeorras is a high-risk area for L. infantum infection. Although climatic conditions are fundamental in the ecology of the vector, they were not as relevant in the transmission of L. infantum as the use of ectoparasiticides and vaccines against L. infantum infection. Clinicians need to be aware of L. infantum infection, its aetiopathogenesis and strategies to control the disease. The importance of veterinarians raising awareness among dog owners of the seriousness of the disease and the need for preventive measures to protect both pets and public health is a cornerstone in the management of this vector-borne parasitic disease.

Availability of data and materials

All data regarding this study are included in the manuscript.

Abbreviations

CanL:

Canine leishmaniosis

IFAT:

Indirect immunofluorescence antibody tests

IgG:

Immunoglobulin G

References

  1. Piscopo TV. Leishmaniasis. Postgrad Med J. 2007;83:649–57.

    Article  PubMed  PubMed Central  Google Scholar 

  2. Solano-Gallego L, Miró G, Koutinas A, Cardoso L, Pennisi MG, Ferrer L, et al. LeishVet guidelines for the practical management of canine leishmaniosis. Parasites Vectors. 2011;4:86.

    Article  PubMed  PubMed Central  Google Scholar 

  3. Roura López X, Miró Corrales G, Sainz A, Estrada Peña A, Solano Gallego L. Leishmaniosis canina y felina en España y Portugal: 159 preguntas sobre las que siempre habías querido una respuesta. Servet. 2015.

  4. Morales-Yuste M, Martín-Sánchez J, Corpas-Lopez V. Canine leishmaniasis: update on epidemiology, diagnosis, treatment, and prevention. Vet Sci. 2022;9:387.

    Article  PubMed  PubMed Central  Google Scholar 

  5. Gálvez R, Montoya A, Cruz I, Fernández C, Martín O, Checa R, et al. Latest trends in Leishmania infantum infection in dogs in Spain, part I: mapped seroprevalence and sand fly distributions. Parasites Vectors. 2020;13:204.

    Article  PubMed  PubMed Central  Google Scholar 

  6. Lewis DJ. Phlebotomid sandflies. Bull World Health Organ. 1971;44:535–51.

    CAS  PubMed  PubMed Central  Google Scholar 

  7. Koch LK, Kochmann J, Klimpel S, Cunze S. Modeling the climatic suitability of leishmaniasis vector species in Europe. Sci Rep. 2017;7:13325.

    Article  PubMed  PubMed Central  Google Scholar 

  8. Fischer D, Moeller P, Thomas SM, Naucke TJ, Beierkuhnlein C. Combining climatic projections and dispersal ability: a method for estimating the responses of sandfly vector species to climate change. PLoS Negl Trop Dis. 2011;5:e1407.

    Article  PubMed  PubMed Central  Google Scholar 

  9. Trájer AJ. The effect of climate change on the potential distribution of the european phlebotomus species. Appl Ecol Env Res. 2013;11:189–208.

    Article  Google Scholar 

  10. Antoniou M, Gramiccia M, Molina R, Dvorak V, Volf P. The role of indigenous phlebotomine sandflies and mammals in the spreading of leishmaniasis agents in the Mediterranean region. Eur Commun Dis Bull. 2013;18:20540.

    CAS  Google Scholar 

  11. Melaun C, Krüger A, Werblow A, Klimpel S. New record of the suspected leishmaniasis vector Phlebotomus (Transphlebotomus) mascittii Grassi, 1908 (Diptera: Psychodidae: Phlebotominae)—the northernmost phlebotomine sandfly occurrence in the Palearctic region. Parasitol Res. 2014;113:2295–301.

    Article  PubMed  Google Scholar 

  12. Naucke TJ, Menn B, Massberg D, Lorentz S. Sandflies and leishmaniasis in Germany. Parasitol Res. 2008;103:65–8.

    Article  Google Scholar 

  13. Amusategui I, Sainz A, Aguirre E, Tesouro MA. Seroprevalence of Leishmania infantum in northwestern Spain, an area traditionally considered free of leishmaniasis. Ann N Y Acad Sci. 2004;1026:154–7.

    Article  PubMed  Google Scholar 

  14. Díaz-Regañón D, Roura X, Suárez ML, León M, Sainz Á. Serological evaluation of selected vector-borne pathogens in owned dogs from northern Spain based on a multicenter study using a commercial test. Parasit Vectors. 2020;13:301.

    Article  PubMed  PubMed Central  Google Scholar 

  15. Puerta JL. Leishmaniosis. In Plan de Profilaxis y Lucha contra las Enfermedades del Perro. Xunta de Galicia. 62nd–64th ed. 1993.

  16. Miró G, Montoya A, Roura X, Gálvez R, Sainz A. Seropositivity rates for agents of canine vector-borne diseases in Spain: a multicentre study. Parasites Vectors. 2013;6:117.

    Article  PubMed  PubMed Central  Google Scholar 

  17. Miró G, Checa R, Montoya A, Hernández L, Dado D, Gálvez R. Current situation of Leishmania infantum infection in shelter dogs in northern Spain. Parasites Vectors. 2012;5:60.

    Article  PubMed  PubMed Central  Google Scholar 

  18. Aransay AM, Testa JM, Morillas-Marquez F, Lucientes J, Ready PD. Distribution of sandfly species in relation to canine leishmaniasis from the Ebro Valley to Valencia, northeastern Spain. Parasitol Res. 2004;94:416–20.

    Article  PubMed  Google Scholar 

  19. Bravo-Barriga D, Ruiz-Arrondo I, Peña RE, Lucientes J, Delacour-Estrella S. Phlebotomine sand flies (Diptera, Psychodidae) from Spain: an updated checklist and extended distributions. ZooKeys. 2022;1106:81–99.

    Article  PubMed  PubMed Central  Google Scholar 

  20. Risueño J, Muñoz C, Pérez-Cutillas P, Goyena E, Gonzálvez M, Ortuño M, et al. Understanding Phlebotomus perniciosus abundance in south-east Spain: assessing the role of environmental and anthropic factors. Parasites Vectors. 2017;10:189.

    Article  PubMed  PubMed Central  Google Scholar 

  21. Branco S, Alves-Pires C, Maia C, Cortes S, Cristovão JMS, Gonçalves L, et al. Entomological and ecological studies in a new potential zoonotic leishmaniasis focus in Torres Novas municipality, Central Region. Portugal Acta Trop. 2013;125:339–48.

    Article  CAS  PubMed  Google Scholar 

  22. Ballart C, Guerrero I, Castells X, Baròn S, Castillejo S, Alcover MM, et al. Importance of individual analysis of environmental and climatic factors affecting the density of Leishmania vectors living in the same geographical area: the example of Phlebotomus ariasi and P. perniciosus in northeast Spain. Geospat Health. 2014;8:389–403.

    Article  PubMed  Google Scholar 

  23. Díaz-Sáez V, Corpas-López V, Merino-Espinosa G, Morillas-Mancilla MJ, Abattouy N, Martín-Sánchez J. Seasonal dynamics of phlebotomine sand flies and autochthonous transmission of Leishmania infantum in high-altitude ecosystems in southern Spain. Acta Trop. 2021;213:105749.

    Article  PubMed  Google Scholar 

  24. Prudhomme J, Rahola N, Toty C, Cassan C, Roiz D, Vergnes B, et al. Ecology and spatiotemporal dynamics of sandflies in the Mediterranean Languedoc region (Roquedur area, Gard, France). Parasites Vectors. 2015;8:642.

    Article  PubMed  PubMed Central  Google Scholar 

  25. Durán-Martínez M, Ferroglio E, Acevedo P, Trisciuoglio A, Zanet S, Gortázar C, et al. Leishmania infantum (Trypanosomatida: Trypanosomatidae) phlebotomine sand fly vectors in continental mediterranean Spain. Environ Entomol. 2013;42:1157–65.

    Article  PubMed  Google Scholar 

  26. Alten B, Maia C, Afonso MO, Campino L, Jiménez M, González E, et al. Seasonal dynamics of phlebotomine sand fly species proven vectors of mediterranean leishmaniasis caused by Leishmania infantum. PLoS Negl Trop Dis. 2016;10:e0004458.

    Article  PubMed  PubMed Central  Google Scholar 

  27. Deplazes P, Eckert J, Mathis A, von Samson-Himmelstjerna G, Zahner H. Parasitology in veterinary medicine. Wageningen: Wageningen Academic Publishers; 2016.

    Book  Google Scholar 

  28. Gálvez R, Montoya A, Fontal F, Martínez De Murguía L, Miró G. Controlling phlebotomine sand flies to prevent canine Leishmania infantum infection: a case of knowing your enemy. Res Vet Sci. 2018;121:94–103.

    Article  PubMed  Google Scholar 

  29. Ramezankhani R, Sajjadi N, Nezakati esmaeilzadeh R, Jozi SA, Shirzadi MR. Climate and environmental factors affecting the incidence of cutaneous leishmaniasis in Isfahan, Iran. Environ Sci Pollut Res. 2018;25:11516–26.

    Article  Google Scholar 

  30. Patz JA, Graczyk TK, Geller N, Vittor AY. Effects of environmental change on emerging parasitic diseases. Int J Parasitol. 2000;30:1395–405.

    Article  CAS  PubMed  Google Scholar 

  31. Sutherst RW. Global change and human vulnerability to vector-borne diseases. Clin Microbiol Rev. 2004;17:136–73.

    Article  PubMed  PubMed Central  Google Scholar 

  32. Miró G, López-Vélez R. Clinical management of canine leishmaniosis versus human leishmaniasis due to Leishmania infantum putting “One Health” principles into practice. Vet Parasitol. 2018;254:151–9.

    Article  PubMed  Google Scholar 

  33. Dantas-Torres F, Miró G, Baneth G, Bourdeau P, Breitschwerdt E, Capelli G, et al. Canine leishmaniasis control in the context of one health. Emerg Infect Dis. 2019;25:1–4.

    Article  PubMed  PubMed Central  Google Scholar 

  34. Tesouro MA. Aspectos clínicos y laboratoriales del diagnóstico de la leishmaniosis canina. Estudio epidemiológico en la provincia de Madrid. Departamento de Patología general y Médica. Facultad de Veterinaria. UCM; 1984.

  35. Amusategui I, Sainz A, Rodríguez F, Tesouro MA. Distribution and relationships between clinical and biopathological parameters in canine leishmaniasis. Eur J Epidemiol. 2003;18:147–56.

    Article  CAS  PubMed  Google Scholar 

  36. Portero M, Miró G, Checa R, Martínez de Merlo E, Fragío C, Benito M, et al. Role of Leishmania infantum in meningoencephalitis of unknown origin in dogs from a canine leishmaniosis endemic area. Microorganisms. 2021;9:571.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  37. Medenica S, Miladinović-Tasić N, Stojanović NM, Lakićević N, Rakočević B. Climate variables related to the incidence of human leishmaniosis in Montenegro in southeastern Europe during seven decades (1945–2014). Int J Environ Res Public Health. 2023;20:1656.

    Article  PubMed  PubMed Central  Google Scholar 

  38. Gálvez R, Descalzo MA, Guerrero I, Miró G, Molina R. Mapping the current distribution and predicted spread of the leishmaniosis sand fly vector in the Madrid region (Spain) based on environmental variables and expected climate change. Vector Borne Zoonotic Dis. 2011;11:799–806.

    Article  PubMed  Google Scholar 

  39. Sanz CR, Sarquis J, Ángeles Daza M, Miró G. Exploring the impact of epidemiological and clinical factors on the progression of canine leishmaniosis by statistical and whole genome analyses: from breed predisposition to comorbidities. Int J Parasitol. 2024;S0020–7519:00058–64.

    Google Scholar 

  40. Alcover MM, Ballart C, Serra T, Castells X, Scalone A, Castillejo S, et al. Temporal trends in canine leishmaniosis in the Balearic Islands (Spain): A veterinary questionnaire. Prospective canine leishmaniosis survey and entomological studies conducted on the Island of Minorca, 20 years after first data were obtained. Acta Trop. 2013;128:642–51.

    Article  CAS  PubMed  Google Scholar 

  41. Mendoza-Roldan J, Benelli G, Panarese R, Iatta R, Furlanello T, Beugnet F, et al. Leishmania infantum and Dirofilaria immitis infections in Italy, 2009–2019: changing distribution patterns. Parasites Vectors. 2020;13:193.

    Article  PubMed  PubMed Central  Google Scholar 

  42. Müller A, Montoya A, Escacena C, de la Cruz M, Junco A, Iriso A, et al. Leishmania infantum infection serosurveillance in stray dogs inhabiting the Madrid community: 2007–2018. Parasites Vectors. 2022;15:96.

    Article  PubMed  PubMed Central  Google Scholar 

  43. Gálvez R, Miró G, Descalzo MA, Nieto J, Dado D, Martín O, et al. Emerging trends in the seroprevalence of canine leishmaniosis in the Madrid region (central Spain). Vet Parasitol. 2010;169:327–34.

    Article  PubMed  Google Scholar 

  44. Baxarias M, Homedes J, Mateu C, Attipa C, Solano-Gallego L. Use of preventive measures and serological screening tools for Leishmania infantum infection in dogs from Europe. Parasites Vectors. 2022;15:134.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  45. Theodor O. On the relation of Phlebotomus papatasii to the temperature and humidity of the environment. Bull Entomol Res. 1936;27:653–71.

    Article  CAS  Google Scholar 

  46. Dolmatova AV, Delina NA, Abonnenc E, Rageau J, Kobylansky A. Les phlébotomes (Phlebotominae) et les maladies qu’ils transmettent. O.R.S.T.O.M.; 1971.

  47. Gálvez R, Descalzo M, Miró G, Jiménez M, Martin O, Santos-Brandao F, et al. Seasonal trends and spatial relations between environmental/meteorological factors and leishmaniosis sand fly vector abundances in Central Spain. Acta trop. 2010;115:95–102.

    Article  PubMed  Google Scholar 

  48. Trájer AJ. The potential impact of climate change on the seasonality of Phlebotomus neglectus, the vector of visceral leishmaniasis in the East Mediterranean region. Int J Environ Health Res. 2019;31:932–50.

    Article  PubMed  Google Scholar 

  49. Tarallo VD, Dantas-Torres F, Lia RP, Otranto D. Phlebotomine sand fly population dynamics in a leishmaniasis endemic peri-urban area in southern Italy. Acta Trop. 2010;116:227–34.

    Article  PubMed  Google Scholar 

  50. Cotteaux-Lautard C, Leparc-Goffart I, Berenger JM, Plumet S, Pages F. Phenology and host preferences Phlebotomus perniciosus (Diptera: Phlebotominae) in a focus of Toscana virus (TOSV) in South of France. Acta Trop. 2016;153:64–9.

    Article  CAS  PubMed  Google Scholar 

  51. Chamaillé L, Tran A, Meunier A, Bourdoiseau G, Ready P, Dedet JP. Environmental risk mapping of canine leishmaniasis in France. Parasites Vectors. 2010;3:31.

    Article  PubMed  PubMed Central  Google Scholar 

Download references

Acknowledgements

The paper has been sponsored by Elanco Animal Health in the framework of the CVBD® World Forum Symposium. The authors sincerely thank Ricardo García from the ‘Departamento de Ayuda a la Investigación, Área de Informática y Comunicaciones’ of the Complutense University of Madrid for the statistical support. The authors also want to thank Constantino Rodríguez (‘Tino’) for all his work and friendship during many years and for his technical support at the Canine Leishmaniosis and Ehrlichiosis Diagnostic Service of the Complutense Veterinary Teaching Hospital of the Complutense University of Madrid. The authors also want to sincerely thank the AEMET (State Meteorological Agency) for their invaluable help in the collection of climatic variables. The graphical abstract was created with Biorender.com.

Funding

P.O. has been funded by the FPU grant from the Ministry of Universities, Government of Spain (FPU22/02388).

Author information

Authors and Affiliations

  1. Department of Animal Medicine and Surgery, College of Veterinary Medicine, Complutense University of Madrid, Avda. Puerta de Hierro S/N, 28040, Madrid, Spain

    Patricia Olmeda, David Díaz-Regañón, Alejandra Villaescusa, Inmaculada Amusategui, Fernando Rodríguez-Franco, Mercedes García-Sancho, Daniel Martín-Fraile & Ángel Sainz

  2. Veterinary Clinic “Servicios Veterinarios del Sil”, C/ Coruña 9, O Barco de Valdeorras, 32300, Ourense, Spain

    Adolfo García & Francisco Herrero

  3. Department of Veterinary Medicine, Surgery and Anatomy, College of Veterinary Medicine, University of León, Campus de Vegazana, 24071, León, Spain

    Miguel A. Tesouro

Authors
  1. Patricia Olmeda
    View author publications

    You can also search for this author in PubMed Google Scholar

  2. David Díaz-Regañón
    View author publications

    You can also search for this author in PubMed Google Scholar

  3. Alejandra Villaescusa
    View author publications

    You can also search for this author in PubMed Google Scholar

  4. Inmaculada Amusategui
    View author publications

    You can also search for this author in PubMed Google Scholar

  5. Adolfo García
    View author publications

    You can also search for this author in PubMed Google Scholar

  6. Francisco Herrero
    View author publications

    You can also search for this author in PubMed Google Scholar

  7. Miguel A. Tesouro
    View author publications

    You can also search for this author in PubMed Google Scholar

  8. Fernando Rodríguez-Franco
    View author publications

    You can also search for this author in PubMed Google Scholar

  9. Mercedes García-Sancho
    View author publications

    You can also search for this author in PubMed Google Scholar

  10. Daniel Martín-Fraile
    View author publications

    You can also search for this author in PubMed Google Scholar

  11. Ángel Sainz
    View author publications

    You can also search for this author in PubMed Google Scholar

Contributions

P.O., writing original draft, data analysis, writing, review and editing; A.S., A.V. and D.D-R., writing, review and editing; M.G-S. and F.R-F, review and editing; A.S., project coordination; A.G. and F.H., sample collection; M.A.T., I.A., A.S., D.D-R. and P.O., IFAT. I.A, A.S., D.D.-R. and P.O., reading and interpretation of the IFAT results; D.M-F., data analysis. All authors read and approved the final manuscript.

Corresponding author

Correspondence to Ángel Sainz.

Ethics declarations

Ethics approval and consent to participate

Not applicable.

Consent for publication

Not applicable.

Competing interests

The authors declare that they have no competing interests.

Additional information

Publisher’s Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Rights and permissions

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article’s Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article’s Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated in a credit line to the data.

Reprints and permissions

About this article

Check for updates. Verify currency and authenticity via CrossMark

Cite this article

Olmeda, P., Díaz-Regañón, D., Villaescusa, A. et al. Twenty-year evolution of Leishmania infantum infection in dogs in Valdeorras (Galicia, Northwestern Spain): implication of climatic factors and preventive measures. Parasites Vectors 17, 281 (2024). https://doi.org/10.1186/s13071-024-06357-8

Download citation

  • Received:

  • Accepted:

  • Published:

  • DOI: https://doi.org/10.1186/s13071-024-06357-8

Keywords

Parasites & Vectors

ISSN: 1756-3305

Contact us