Unusual multiparasitism causes overweight in a wood mouse, Apodemus sylvaticus (Rodentia: Muridae), from a post-fire regeneration area.
Key words: multiple parasitism, massive infection, Taenia parva, perturbed Mediterranean ecosystem, Serra Calderona, Spain
Multiparasitism, defined as the simultaneous presence of two or more parasite species in one host, is the rule rather than the exception in Nature (Bordes & Morand 2011). From an ecological point of view, multiparasitism can be understood as an evolutionary strategy aiming at the increase of fitness of the parasite species involved in the infection. Nevertheless, some authors consider this situation unusual given the weakening of the host and the resulting increase in susceptibility in acquiring multiple infections (Cansi et al. 2012).
The presence of two or more individuals belonging to the same parasite species in one host is frequently found. Moreover, intraspecific interactions between parasites may have a negative impact on the body size and fecundity of the parasites and may even produce a stronger immunological response (Bush et al. 2001). This interaction known as crowding effect and experimentally evidenced in some helminth species leads to an adjustment of the biomass of the parasite infrapopulation to the host capacity (Roberts & Janovy 2009).
Parasites are considered an important source of information concerning the stability of ecosystems (Marcogliese 2005), and numerous publications propose the role of parasites, particularly helminths, as biological tags of environmental impacts (Sures 2001, Jankovska et al. 2005, Fuentes et al. 2010). The binomial host-parasite tends to have a balance between the two species, requiring a long process of co-evolution which involves the establishment of a parasite population without implying the death of the host (Bush et al. 2001). Although these interactions are usually more stable in unaltered environments, they exercise a rather negative impact on areas affected by anthropic actions or natural disasters given their lower stability and resistance to environmental alterations due to the long-lasting regeneration process.
Environmental impacts influence the density of intermediate and definitive hosts, making them more susceptible to infections (Lafferty & Holt 2003) and giving way to an increase in prevalence and even to the pathogenicity of parasites (Holmes 1996). The behaviour of parasites after a perturbation of the ecosystem is the result of multiple factors guaranteeing the restructuring of the biological cycle in such a way that the regulation of a parasite infracommunity will be conditioned by the direct effects of the perturbation, the changes in host population dynamics and by the pressure exercised by the other infrapopulations as well as climatic conditions (Fuentes et al. 2009). Herein, an unusual case of multiparasitism in a wood mouse, Apodemus sylvaticus, originating from a post-fire regeneration area is described, highlighting the potential relationship between multiparasitism and a perturbed ecosystem.
Material and Methods
This study forms part of the research line of the scientific group Parasites and Fire (PAF) of Universitat de Valencia, Spain, concerning the study of the role of helminths of small mammals as biological tags in the post-fire regeneration process of a Mediterranean ecosystem, namely Serra Calderona Natural Park, situated between the provinces of Castello and Valencia (Comunitat Valenciana, Spain), having suffered a devastating wildfire in the summer of 1992 (Fuentes et al. 2007, 2010, Sainz-Elipe et al. 2012). Periodic surveys to analyze the epidemiological evolution of the helminthfauna of small mammals related to post-fire regeneration as well as the influence of various intrinsic and extrinsic factors have been carried out. The study of small mammals and the helminthological analysis were done following the methodology proposed by Galan-Puchades et al. (1999) and Fuentes et al. (2000, 2007, 2010), having analyzed more than 1000 wood mouse specimens hitherto.
Herein, the case of a sexually active A. sylvaticus male having reached the unusual weight of 44.0 g, is presented. The specimen was found dead in Rebalsadors, one of the regeneration sites, in the winter of 2012, the 20th post-fire year. The rodent had been captured and marked at the same site in the previous season of the survey, the spring of 2011, when the mouse was registered as an inactive male of 22.5 g. During the previous examination at the laboratory, the presence of some swellings in the abdominal region was noteworthy (Fig. 1).
The wood mouse was found to be parasitized by a total of 31 parasites belonging to seven helminth species: four Brachylaima sp. (Trematoda: Digenea) in the small intestine; four adult Gallegoides arfaai in the small intestine and six metacestodes of Taenia parva (Cestoda) in the abdominal cavity; one Mastophorus muris in the stomach, six Syphacia stroma in the small intestine, seven Trichurs muris and three Syphacia frederici (Nematoda), the two latter species in the caecum.
The T. parva metacestodes encountered differed in size, being in various developmental stages (Fig. 2). One of these polycephalic metacestodes was completely formed, with a total of 21 long strobila, pseudosegmented and presenting scolices with 21 pairs of hooks, all of them wrapped in a cyst of 4.6 cm. Three other metacestodes presented a smaller diameter of 2-3 cm, having 21 scolices each, without strobila. The remaining two metacestodes, 1-2 cm in diameter, presented an incipient stage of development. The total weight of the cysts was 12 g.
The remaining helminths found had reached the adult stage and were encountered in their normal microhabitat. In the case of the four G. arfaai individuals, it was impossible to determine the exact weight of each one, as they had been damaged in the dissection process when some of the rings were broken. However, the total weight of these four adult tapeworms was 1.8 g. The remainder of the helminths was intact, having reached a total weight of approximately 0.1 g.
A weight of 40.0 g had until then been the maximum of adult specimens in Serra Calderona in the 20-year study period. However, the specimen described herein reached 44.0 g, a figure, according to the literature, larger than that considered the maximum for this species of small mammals (Blanco 1998).
After resection of the helminths, it was concluded that the actual weight of the mouse was approximately 30.1 g, in agreement with data gathered in the studies by Fuentes et al. (2000, 2007, 2010). Thus, considering that the helminth infracommunity itself presented a total weight of 13.9 g, it can be concluded that multiparasitism was the real cause of the overweight condition of this mouse.
Previous studies (Fuentes et al. 2007, 2010) demonstrated a greater diversity, abundance and species richness in perturbed areas undergoing a recuperation process, in which infracommunities of up to eight helminth species had been found.
Multiparasitism implies that members of the parasite infracommunity compete for food and space, but their success depends on the amount of resources and on the host's immunological response. In this sense, hosts able to tolerate a greater parasite burden could increase the transmission potential of a parasite species (Bordes & Morand 2011). The latter, in turn, would at the same time regulate the host's population growth, acting as a stabilizer of the ecosystem (Bush et al. 2001), and would simultaneously participate in natural selection, aiming at the preservation of the strongest genotypes. However, the host might be individually adversely affected, but its population might benefit (Combes 1996).
The helminth burden of each parasite species found corresponds to the values previously reported in this enclave, merely the number of T. parva metacestodes stands out. Fuentes et al. (2010) established that T. parva is a component species of the wood mouse host only in the non-burned area in Serra Calderona, which is verified by the greater prevalence as well as the average parasitism intensities registered in the control area. In the post-fire regeneration area a range of 1-3 metacestodes per host has been documented so far, while this range has increased to 1-6 metacestodes in the control area (unpublished data). Helminths of an indirect cycle, such as T. parva, are more susceptible to environmental perturbations, which makes it possible to use them as reliable biological tags of the reestablishment of the ecosystem's trophic chain, as they require the intervention of an intermediate host, in this case a rodent, serving as prey for its definitive host. In the Iberian Peninsula, the biological cycle of T. parva can usually only be completed through rodents of the genus Apodemus and the common genet (Genetta genetta), which act as intermediate and definitive host, respectively (Ribas et al. 2009). Therefore, the perseverance of this parasite in the ecosystem is only possible given the presence and interaction of the wood mouse and this carnivore. Moreover, in general, helminth infrapopulations remain stable along time, which is indicative of both a suitable trophic chain and of the ecosystem's stability. Thus, cases of most severe multiparasitism, massive infections and ectopic parasitism occur most frequently in perturbed ecosystems (Holmes 1996). In the present case, such a drastic increase in the helminth burden can be explained as a case of aberrant parasitism, a compensatory mechanism aiming at the increased likelihood of successful transmission. A large number of metacestodes in the intermediate host does not only increase the likelihood of successful infection of the definitive host but also causes the rodent to move in a clumsier manner and, thus, being more vulnerable and more easily detectable by its predators (Combes 2001, Poulin 2007).
The fact that the metacestodes found were in different developmental stages, and morphologically easily identifiable (Swiderski et al. 2007), stands out, as it is probable that the infestation took place as a consequence of the repeated ingestion of the infective form of the parasite, i.e. a taeniid egg. Previous studies indicate that T. parva adults reach enormous parasite burdens in the intestines of their definitive hosts (Ribas et al. 2009), resulting in millions of eggs expelled into the environment. Its omnivorous and opportunistic character prompts the wood mouse to ingest seeds, berries and invertebrates, thus facilitating the accidental and the repetitive ingestion of eggs which are fecal contaminants of these foods. On the other hand, experimental evidence has shown that some species of Taeniidae are able to exercise an immunological effect impeding the reinfection of the intermediate host by the same parasite species (Lightowlers 2010). Thus, it is likely that the wood mouse was parasitized as the consequence of only one infection, and the different development of the larvae might be due to a crowding-effect limiting their growth.
This is the first time, a case of overweight condition in A. sylvaticus as a consequence of multiparasitism has been registered, which means that parasitism, besides being a metabolic phenomenon, has to be considered as a possible cause of the abnormal increase in the host weight. Moreover, the presence of this wood mouse in a post-fire regeneration area could support the association between unusual parasitism and perturbed environments, which present a lower stability and resistance to external perturbations affecting all layers of the ecosystem, including the ecological niche of parasites.
This study has been supported by Project CGL2007-61173/BOS, Ministerio de Ciencia y Tecnologia, Madrid, Spain. We would also like to thank the Conselleria de Medi Ambient de la Generalitat Valenciana, Valencia, Spain, for the permissions to carry out field studies.
Blanco J.C. 1998: Mamiferos de Espana. Volumen II. Geo Planeta, Barcelona.
Bordes F. & Morand S. 2011: The impact of multiple infections on wild animal hosts: a review. Infect. Ecol. Epidemiol. 1: 7346.
Bush A.O., Fernandez J.C., Esch G.W. & Seed J.R. 2001: Parasitism. The diversity and ecology of animal parasites. University Press, Cambridge.
Cansi E.R., Bonorino R., Mustafa V.S. & Guedes K.M.R. 2012: Multiple parasitism in wild maned wolf (Chrysocyon brachyurus, Mammalia: Canidae) in Central Brazil. Comp. Clin. Path. 21: 489-493.
Combes C. 1996: Parasites, biodiversity and ecosystem stability. Biodivers. Conserv. 5: 953-962.
Combes C. 2001: Parasitism. The ecology and evolution of intimate interactions. The University of Chicago Press, Chicago.
Fuentes M.V., Cerezuela A.M. & Galan-Puchades M.T. 2000: A helminthological survey of small mammals (insectivores and rodents) in the Serra Calderona mountains (Valencian Community, Spain). Res. Rev. Parasitol. 60: 25-35.
Fuentes M.V., Sainz-Elipe S. & Galan-Puchades M.T. 2007: Ecological study of the wood mouse helminth community in a burned Mediterranean ecosystem in regeneration five years after a wildfire. Acta Parasitol. 52: 403-413.
Fuentes M.V., Sainz-Elipe S., Saez-Duran S. & Galan-Puchades M.T. 2009: Helminth parasites of small mammals as biological indicators of the post-fire regeneration process in Mediterranean ecosystems and preliminary small mammal/helminth GIS models. Rev. Ibero-Latinoam. Parasitol. 1: 46-55.
Fuentes M.V., Sainz-Elipe S., Saez-Duran S. & Galan-Puchades M.T. 2010: The helminth community of the wood mouse Apodemus sylvaticus in a Mediterranean ecosystem in regeneration ten years after a wildfire. J. Helminthol. 84: 39-48.
Galan-Puchades M.T., Fuentes M.V., Cerezuela A. et al. 1999: A proposed methodology for the use of helminth parasites as biological tags in the study of postfire ecosystem regeneration processes. Vie Milieu 49: 45-50.
Holmes J.C. 1996: Parasites as threats to biodiversity in shrinking ecosystems. Biodivers. Conserv. 5: 975-983.
Jankovska I., Langrova I., Bejcek V. et al. 2005: Comparison of helminth fauna of shrew (Sorex araneus and Sorex minutus) in ecosystems affected and non-affected by industrial emissions. Helminthologia 42: 77-81.
Lafferty K.D. & Holt R.D. 2003: How should environmental stress affect the population dynamics of disease? Ecol. Lett. 6: 654-664.
Lightowlers M.W. 2010: Fact of hypothesis: concomitant immunity in taeniid cestode infections. Parasite Immunol. 32: 582-589.
Marcogliese D.J. 2005: Parasites of the superorganism: are they indicators of ecosystem health? Int. J. Parasitol. 35: 705-716.
Poulin R. 2007: Evolutionary ecology of parasites, 2nd ed. Princeton University Press, New Jersey.
Ribas A., Feliu C. & Casanova J.C. 2009: Distribution of the cestode Taenia parva (Taeniidae) along the digestive tract of the common genet (Genetta genetta). Helminthologia 46: 35-38.
Roberts L. & Janovy J. 2009: Foundations of parasitology, 8th ed. McGraw Hill, New York.
Sainz-Elipe S., Saez-Duran S., Galan-Puchades M.T. & Fuentes M.V. 2012: Small mammal (Soricomorpha and Rodentia) dynamics after a wildfire in a Mediterranean ecosystem. Mammalia 76: 251-259.
Sures B. 2001: The use of fish parasites as bioindicators of heavy metals in aquatic ecosystems: a review. Aquat. Ecol. 35: 245-255.
Swiderski Z., Miquel J., Mlocicki D. et al. 2007: Post-embryonic development and ultrastructural characteristics of the polycephalic larva of Taenia parva Baer, 1926 (Cyclophyllidea, Taeniidae). Acta Parasitol. 52: 31-50.
Angela L. DEBENEDETTI, Sandra SAEZ-DURAN, Sandra SAINZ-ELIPE, M. Teresa GALANPUCHADES and Marius V. FUENTES (*)
(*) Corresponding Author
Department of Parasitology, Faculty of Pharmacy, Universitat de Valencia, Av. Vicent Andres Estelles s/n, 46100 Burjassot-Valencia, Spain; e-mail firstname.lastname@example.org
Received 26 April 2016; Accepted 14 July 2016
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|Author:||Debenedetti, Angela L.; Saez-Duran, Sandra; Sainz-Elipe, Sandra; Galan-Puchades, M. Teresa; Fuentes,|
|Date:||Nov 1, 2016|
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