Introduction
Importing exotic animal species to Europe for breeding purposes has a long tradition. In recent decades, more attention has been paid to possible threats related to “imported” parasites. This new approach results from two points of view: (1) the threat to the economic result of breeding and (2) possible epidemic or zoonotic problems. In Europe, including Poland, the importance of domesticated South American camelids has increased in recent decades because of their high-quality fibre, meat and hides. For instance, alpaca meat is becoming popular worldwide due to its lower cholesterol than red meat (Saeed et al., Reference Saeed, Rashid, Vaughan and Jabbar2018).
The growing popularity of these animals resulting from using their products and their role in alpacotherapy changed people’s attitudes toward diagnosing alpaca parasites. Ectoparasitic invasions were mainly described in the context of their influence on fibre quality (Bornstein, Reference Bornstein2010). In turn, intestinal parasites play an important role in veterinary medicine and as the etiological agents of zoonoses (Fugassa & Cafrune, Reference Fugassa and Cafrune2023). It should be emphasized that alpaca-related exotic parasites imported to new areas with their hosts result in new transfers that could threaten native fauna (Carmichael, Reference Carmichael2014). On the other hand, introducing alpacas to Europe and exposing these animals to native parasitic fauna may result in new host-parasite associations (Love, Reference Love2017). This issue is critical due to the uncontrolled movement of animals within the EU.
The first alpacas were brought to Poland at the beginning of the 21st century, and the first commercial farms were established in 2004 (Krajewska-Wędzina et al., Reference Krajewska-Wędzina, Radulski and Lipiec2020). It was estimated that there were 50 herds of alpacas in Poland, with nearly 2000 individuals (Markowska-Daniel et al., Reference Markowska-Daniel, Kita and Kalicki2018). Due to the commercial importance of alpacas and the close contact of animals with breeding keepers and people (especially using alpacotherapy), there was an urgent need to diagnose gastrointestinal parasites in these animals. Many years ago, Leguía (Reference Leguía1991) drew attention to the negative impact of intestinal parasites on the quality of fur and other products used. In turn, Windsor et al. (Reference Windsor, Teran and Windsor1992) pointed to the positive effect of deworming on the quality of fur of farmed animals. Unfortunately, only a few studies on diagnosing ectoparasites and potential health problems due to procaryotic pathogens in alpacas in Poland have been published (Markowska-Daniel et al., Reference Markowska-Daniel, Kita and Kalicki2018). On the other hand, the complete lack of data on the spread of gastrointestinal parasites in farms in Poland should be remedied as soon as possible, given the health of herds and people in contact with them.
This study aimed to estimate the prevalence of gastrointestinal parasites in alpacas from selected commercial farms in Poland and assess the health risks to farm animals and the zoonotic potential.
Material and methods
Sample collection
The diagnostic material comprised 223 stool samples from 97 individual animals from six breeding herds in Poland. The distance between the herd locations was from 100 to 500 km. The samples were tested fresh in summer 2019 (97 in July and 96 in August) and 2021 (30 in August). Among the animals tested in the summer of 2019 were individuals from Germany, Spain, Chile, and the United States, as well as animals born in Poland. The average age of individuals imported from abroad was five years ± 3 months, and they average stay in Poland at the time of sampling had been 0.5 year ± 1 month. Additionally, in the summer of 2021, we tested 30 animals born in Poland. Among the individuals tested, 95 were clinically healthy, while two were diagnosed with diarrhoea, and one died shortly after the test. The tested animals were 58 males and 39 females (Table 1). Some females were inseminated at the time of sample collection, but pregnancies were still not confirmed, so their status was not recorded. Faecal samples were collected from the animals immediately after defecation.
Table 1. Alpacas examined during study
Sample examination
All samples were examined using the modified method of McMaster (Raynaud et al., Reference Raynaud, William and Brunault1970; Sweeny et al., Reference Sweeny, Ryan, Robertson and Jacobson2011). One gram of faecal sample was used for each test. The intensity of infection was calculated as the number of eggs per 1 gram of faeces. The morphological diagnosis of parasite eggs was performed based on Zajac & Conboy (Reference Zajac and Conboy2012).
Statistical analysis
The exploratory data analysis used the CANOCO for Windows 4.5 software (Ter Braak & Šmilauer, Reference Ter Braak and Smilauer2002). The preliminary analysis results (Detrended Correspondence Analysis) showed that the variability of biological data was best described by a linear model (gradient length was 2.260). Therefore, redundancy analysis (RDA) was used for further analysis. A forward selection procedure was used during the RDA analysis to assess the relationships between explanatory and biological variables. Their statistical significance and the significance of the canonical axes were also evaluated using the Monte Carlo permutation test for 499 repetitions. For analyses, the data were logarithmically transformed [ln(x+1)] and centred, and the results were presented on an ordination diagram.
Results
In five of six herds studied, alpacas had gastrointestinal parasites. Of the 97 animals examined, 56 (57.7%) had at least one parasite species. Among these positive cases, 28 were co-infected with two or more parasite species. The presence of at least 11 species of parasites has been found. The prevalence of each gastrointestinal parasite is summarized in Table 2. The typical appearance of the egg or oocyst of the parasites is shown in Figure 1.
Table 2. Prevalence of parasites in tested alpacas
* Or oocysts of Protista.
Figure 1. Detected forms of parasites: (A) egg of Nematodirus sp. (barr = 30 μm), (B) oocyst of Eimeria macusaniensis (barr = 30 μm).
Nematodirus sp. was the most prevalent of the helminths, followed by Trichostrongylus sp., Strongyloides sp., and Camelostrongylus sp. We also detected two types of Capillaria eggs that differed in size and eggs of tapeworm Moniezia sp. (Table 3).
Table 3. Size of protist oocysts and nematode eggs
Of the protozoan parasites, oocysts of two Eimeria species (E. macusaniensis and smaller Eimeria sp.) and Cryptosporidium sp. were found (Table 3).
In the RDA analysis, which included only the significant explanatory variables, the first two axes explained 22.9% of the total variability. The relationship between biological data and explanatory variables accounted for 89.8% of the variation. Monte Carlo permutation tests showed that the RDA ordination axes were significant (axis 1: F = 38.820, p = 0.0020; all axis: F = 6.175, p = 0.0020).
RDA analysis showed that the presence of parasites and their number in faeces was related to, among others, the individual’s country of origin, sex and age (Fig. 2). Parasite species located in the lower right part of the ordination diagram (e.g., Camelostrongylus, Eimeria, Capillaria) more often infected female alpacas. On the other hand, the parasites located at the upper part of the ordination space were noted inside young hosts. They were also more common and numerous in the German alpaca population.
Figure 2. Redundancy analysis (RDA) ordination diagram showing the results of the study on parasite infection in alpaca Vicugna pacos. Parasites: Strongyl = Strongyloides sp., Nem = Nematodirus sp., Cryptosp = Cryptosporidium sp., E. mac = Eimeria macusaniensis, Capillar = Capillaria sp., Trichost = Trichostrongulus sp., Camelost = Camelostrongylus sp., Eimeria = Eimeria sp., Oesophag = Oesophagus sp., Moniezia = Moniezia sp., Trichu = Trichuis sp. PLAGUE = presence of parasites.
Discussion
The results of this study revealed for the first time that alpacas raised in Poland have gastrointestinal parasites similar to those described in other countries outside of South America (Franz et al., Reference Franz, Wittek, Joachim, Hinney and Dadak2015; Hyuga & Matsumoto, Reference Hyuga and Matsumoto2016).
Nematodirus sp. eggs were the most common in the alpacas studied. Nematodirus spp. are parasites of the small intestine of ruminants and have a direct life cycle. Their larvae within ova are highly resistant to low temperatures, so their effective transmission depends on overwintering (Van Dijk & Morgan, Reference Van Dijk and Morgan2008). In Europe, Nematodirus lamae was reported from the United Kingdom as a very probable cause of the sudden death of alpacas (Mitchell & Hopkins, Reference Mitchell and Hopkins2016). Other species of this genus in ruminants, like N. battus, were reported from elsewhere in Europe, while N. helvetianus, N. filicollis and N. spathiger have been noted in mixed infections in this area (Lindqvist et al., Reference Lindqvist, Ljungström, Nilsson and Waller2001); however, they are considered more common across Australasia (McMahon et al., Reference McMahon, Edgar, Barley, Hanna, Brennan and Fairweather2017). Our study revealed the presence of Nematodirus sp. eggs similar in shape and size to N. abnormalis, described by Onar (Reference Onar1975). However, this nematode species is endemic in the Mediterranean climatic zone (Louw, Reference Louw1989), and its presence in alpacas in Poland—an area with a temperate climate—can result from the transfer from warmer regions. The fact that they are present in animals in five different herds indicates the success of this transfer.
The size of Trichostrongylus sp. eggs found in alpacas indicates their similarity to T. axei. This nematode was noted in ruminants inhabiting Zoos and wild habitats in Poland (Bartosik & Górski, Reference Bartosik and Górski2010). According to Souza et al. (Reference Souza, Souza, Mendez, Alcântara, Soares and Teixeira2013), T. axei belongs to zoonotic nematodes most frequently acquired through contact with herbivorous animals.
Eggs of Camelostrongylus sp. were noted in alpacas from four of six studied herds. The first finding of this parasite in alpaca was described in the United Kingdom (Welchman et al., Reference Welchman, Parr, Wood, Mead and Starnes2008). The active trade in alpacas in Europe probably contributed to this nematode’s spread. Some Camelostrongylus species were described in Europe only in captive exotic animals (Ortiz et al., Reference Ortiz, Ruiz de Ybanez, Abaigar, Goyena, Garijo, Espeso and Cano2006).
In four of the studied farms, we noted eggs of Strongyloides sp. In Poland, only S. papillosus was noted in ruminants. The parthenogenetic females were described as pathogenic for lambs (Romaniuk et al,. Reference Romaniuk, Gaca-Łagodzińska, Sokół, Michalski and Bah1995). However, the size of eggs in tested alpacas was longer than described by other authors (Peter et al., Reference Peter, Gitau, Mulei, Vanleeuwen, Richards, Witchtel, Uehlinger and Mainga2015). We can only suspect that the eggs found belong to this species.
Animals in two tested herds were infected with Trichuris sp. These parasites are highly prevalent in the world but rarely cause clinical signs. Species infecting ruminants in Poland include T. discolor, T. skrjabini and T. globulosa (Patyk, Reference Patyk1956; Karbowiak et al., Reference Karbowiak, Demiaszkiewicz, Pyziel, Wita, Moskwa, Werszko, Bien, Gozdzik, Lachowicz and Cabaj2014). Additionally, Dróżdż (Reference Dróżdż1966) described T. bovis in wild Cervidae. In South American Camelidae, T. tenuis was noted (Cafrune et al., Reference Cafrune, Aguirre and Rickard1999); however, this parasite was not described in animals outside their natural geographic range.
Only two animals from one herd were infected with Capillaria sp. In the faeces of alpacas, we found characteristic barrel-shaped eggs similar to those presented by Lambacher et al. (Reference Lambacher, Wittek, Joachim, Dadak, Stanitznig, Hinney, Tichy, Duscher and Franz2016). However, Capillaria species infecting birds or carnivores in Poland were generally noted (Tomczuk et al., Reference Tomczuk, Szczepaniak, Łojszczyk-Szczepaniak, Skrzypek, Łunkuszew, Dudko and Bojar2017), and Demiaszkiewicz et al. (Reference Demiaszkiewicz, Merta and Kobielski2016) found eggs of C. bovis in red deer. Given the direct life cycle of this nematode, transmission could have occurred while grazing alpacas in the wild.
Only in one specimen were eggs of tapeworm Moniezia sp. found. They were pyramidal in shape, and their dimensions were similar to those of Moniezia expansa (Verocai et al., Reference Verocai, Chaudhry and Lejeune2020). This representative of Cestodes has a worldwide distribution (Zhang et al., Reference Zhang, Zhao, Kang, Wang and Bo2010). It has been reported in alpacas in Peru (Ortiz, Reference Ortiz2013) and European ruminants, including Poland (Piekarska et al., Reference Piekarska, Kuczaj, Wereszczyńska, Gorczykowski, Janeczko and Płoneczka-Janeczko2012).
The representatives of two genera of protists were observed in alpacas tested: Eimeria and Cryptosporidium. Eimeria macusaniensis belongs to common alpaca parasites in South America (Cafrune et al., Reference Cafrune, Marín, Rigalt, Romero and Aguirre2009) and probably was introduced to Japan (Hyuga & Matsumoto, Reference Hyuga and Matsumoto2016). Our report of its occurrence in Poland is the first described case, and considering the high specificity of the parasite to the host, it means that this coccidium was introduced with the imported Camelidae. The smaller oocysts of Eimeria sp. were similar to Eimeria lamae described by Gomez-Puerta et al. (Reference Gomez-Puerta, Carrasco, Robles, Vargas-Calla, Cribillero, Arroyo, Castillo, Lopez-Urbina and Gonzalez2021) in Vicuna pacos from the Peruvian Andes. However, without molecular data, this suggestion cannot be confirmed. In Poland, similar cysts were observed in rabbits (Sadzikowski et al., Reference Sadzikowski, Szkucik, Szczepaniak and Paszkiewicz2008) and goats (Mickiewicz et al., Reference Mickiewicz, Czopowicz, Moroz, Witkowski, Szaluś-Jordanow, Nalbert, Markowska-Daniel, Górski and Kaba2017). However, their proposed identity is contradicted by the host specificity of species in the genus Eimeria. Cryptosporidium genus is a species-rich protist group that can only be identified based on molecular diagnostics. Representatives of this genus are common animal parasites and zoonotic agents (e.g., Cryptosporidium parvum). This species was diagnosed in Vicugna pacos by Zhang et al. (Reference Zhang, Li, Li, Xu, Hou and Qi2020). In this context, it is necessary to control the presence of oocysts in animals, especially in alpacotherapy, to minimise the risk of transmitting infection from alpacas to humans.
The presence of parasitic protists, tapeworm, and nematodes in alpacas bred in European countries fully justifies the necessary monitoring of infections in these animals. As our results and the research of various authors indicate, the introduction of alpacas resulted in both the transmission of parasites from domestic native ruminants to newcomers and the import of South American parasites to new areas (Dubey, Reference Dubey2018). The lack of reports from many countries of the Old World concerning alpaca parasites may result from the lack of appropriate regulations and the limited knowledge about the etiological factors of these animals (Neubert et al., Reference Neubert, von Altrock, Wendt and Wagner2021). As Rickard (Reference Rickard1994) indicated, camelids respond differently to certain parasites than cattle or sheep. Depending on the parasitic burden, infections in alpacas can be subclinical, mild, or lead to death if untreated (Fowler, Reference Fowler and Wiley-Blackwell2010). Clinical signs due to endoparasites are usually unspecific. Poor growth, anorexia and anaemia can occur. Diarrhoea is more often observed in younger animals, but in many cases, it is absent at the early stages of infection. The malabsorption of minerals and micronutrients and loss of proteins can result from damage to the intestinal mucosa, leading to reduced growth and performance (Franz et al., Reference Franz, Wittek, Joachim, Hinney and Dadak2015).
The essential aspect of diagnosing alpaca parasites in commercial herds is the zoonotic nature of such species as Trichostrongylus axei or Cryptosporidium parvum. Particular attention should be paid to the possibility of transmission of alpaca parasites with a holoxenic lifecycle to children in petting zoos or during alpacotherapy (Halsby et al., Reference Halsby, Twomey, Featherstone, Foster, Walsh and Hewitt2017). According to Walker (Reference Walker2018), a faecal examination in alpaca herds should be done on each animal before any anthelmintic is administered, which is impractical, especially in large herds. The author suggests that, as a minimum, 10% of the animals or at least 10 animals, should be tested two to three times a year.
Our results suggest mandatory regular parasitological testing in commercial alpaca herds, particularly those used in alpacotherapy.
Statistical analysis showed that parasites and their number in faeces were related to the individual’s country of origin, sex and age. Additionally, the largest herd had the most significant count of parasitic taxons, which greater infection possibilities between animals and lower success rates of deworming strategies can cause. We cannot exclude existing parasites showing anthelmintic resistance in a much larger herd. Large herds should be dewormed more regularly and often, which can lead to the rise of populations partially resistant to anthelmintic drugs (Hodgkinson et al., Reference Hodgkinson, Kaplan, Kenyon, Morgan, Park, Paterson, Babayan, Beesley, Britton, Chaudhry, Doyle, Ezenwa, Fenton, Howell, Laing, Mable, Matthews, McIntyre and Devaney2019). Moreover, individuals of various origins in the largest herd could have influenced the composition of the parasitic fauna. The number of eggs (or oocysts) was higher in female than male alpacas. A host’s immunity can significantly impact egg production due to internal parasites (Rosenberg et al., Reference Rosenberg, Dyer and Foster2013). The results of a more significant count of eggs between sexes but not in the parasite taxon can show that the immunity of the females was weaker because of the possible pregnancy (Pazos et al., Reference Pazos, Kraus, Muñoz-Fontela and Moran2012). Younger animals were also characterized by greater intensity of infection, which may be the result of lower immunocompetence of the defence system of these animals compared to older animals (Colditz et al., Reference Colditz, Watson, Gray and Eady1996). What is surprising is the strong parasitism of individuals imported from Germany. Unfortunately, import documents only indicate the country directly transported to Poland. It is possible that these individuals were brought to Europe from other countries. When importing exotic animal species to Europe, parasite diagnostics should be carried out carefully. The present research is the first attempt in Poland to assess the infestation of alpaca herds with intestinal parasites. The relatively large number of parasite taxa found (at least 11) is surprising. Already, preliminary studies indicate an association between the infection and the sex of the hosts, possibly due to the reduced immunity of pregnant females. Due to the diversity of alpacas’ parasitic fauna and potentially zoonotic parasites, we postulate that the veterinary care of herds should be increased. Even in the case of asymptomatic infections, there is a risk of parasite transmission between farmed alpacas, wild and farmed ruminant fauna, and even humans and alpacas.
Conclusions
Analysis of the consequences associated with alien species usually concerns organisms accidentally introduced to new areas. Meanwhile, omitting alien species of economic importance is a grave mistake, which results from the belief that alien-farmed species are kept isolated from natural ecosystems.
However, the present research results indicate that the threat associated with such introductions may have a more complex dimension beyond the newcomers’ gene pool. One aspect worth emphasising is the problem of intestinal parasites, which do not necessarily affect the economic results of breeding foreign species. However, their transfer may have far-reaching effects by creating new host-parasite associations. These consequences may have both veterinary and medical dimensions.
Declarations
Conflict of interest: The author(s) declare none.
Ethical standard
The conducted research does not require the consent of the National Ethical Committee for Animal Experiments.
Open access
