Resumen
In altered environments, such as agricultural lands, studies of amphibian parasites can provide helpful information about the food web structure, parasite species abundance and composition, and environmental stress. Here, we investigate the parasitic digeneans in three amphibian families (Leptodactylidae, Bufonidae and Hylidae) in a rice field (30 ha) from Corrientes Province, Argentina. A total of 171 amphibian specimens were collected between March 2017 and February 2018. Amphibian trematode parasites in this area included 18 species, with dominance of common species. The trematode fauna was characterized by only one species (Choledocystus vitellinophillum) with high prevalence (>50%). The dominant adult species corresponded to Catadiscus propinquus for most of the hosts (80%), and when only larval trematodes were analysed, the dominant metacercariae in most hosts (60%) were strigeids larvae. Of the total trematode individuals (n = 278), 57% corresponded to metacercariae that complete their life cycles mainly in birds. The amphibians Leptodactylus chaquensis and Lysapsus limellus presented high species richness. This is related to the microhabitats occupied by these hosts as well as with the biology of their parasites. Infection of all the trematode taxa for which larvae and adults were examined occurs through a sequence of trophic relationships. Finally, the results expand the knowledge of the biodiversity and ecology of parasite helminths in amphibians from agricultural landscapes; furthermore, this information is a fundamental baseline to quantify the loss of biodiversity and assess the health of the ecosystem.
Métodos
The agricultural area was located ~85 km southwest of the city of Corrientes (27°49?S, 58°46?W), Corrientes Province, Argentina. The area sampled had 30 ha. During the sampling period, the depth of the irrigated channels ranged between 5.0 and 50.0 cm. All adult specimens were anesthetized using topical 2% lidocaine cream, and then dissected following standard protocols (Goater and Goater, 2001). The present study complies with all the regulations and ethical and legal considerations for the capture and use of animals established by the National Council of Scientific and Technical Research of Argentina. Snout-vent length (SVL) and body weight of each specimen were recorded. During necropsy, hosts were sexed and their oesophagus, stomach, intestines, lungs, liver, kidneys, body cavity, musculature, integument, and brain were examined for parasites. Trematodes were counted and studied either in vivo or mounted in 0.6% saline solution or killed in hot distilled water, fixed in 70% ethyl alcohol, stained with hydrochloric carmine, and mounted in Canada balsam. They were identified following Yamaguti (1975), Gibson et al. (2002), Niewiadomska et al. (2002), and Jones et al. (2005). Parasite specimens were deposited in the Helminthological Collection of Centro de Ecología Aplicada del Litoral (CECOAL), Corrientes, Corrientes province, Argentina [accession numbers CECOAL: 17030102, Tylodelphys sp.; 17112208, Strigeidae gen. sp. 12; 17101726, Heterodiplostomum sp; 17040616, Rauschiella palmipedis; 17032916, Choledocystus vitellinophillum; 17040615, 17101707, 17101726, 17112239. Catadiscus propinquus; 17040615, Haematoloechus longiplexus; 17040619, Gorgoderina parvicava 17101728, Gorgoderina cryptorchis].
Prevalence and intensity of infection for trematode parasites were calculated following Bush et al. (1997). Trematode species data were classified into common and rare categories. Those parasites that were recorded as infecting more than one family of amphibians were considered as common; while those that were only recorded from species within a single amphibian family were classified as rare. The total number of trematode species, Shannon index (H´) and evenness (J?) were used to calculate species richness and diversity at component community. The diversity index was used with decimal logarithms (loge). The Berger-Parker index of dominance (d) was used for determining the most abundant species. To determine the qualitative similarity between component communities was used Jaccard?s coefficient similarity index and a Cluster Analysis was then performed using the UPGMA (Unweighted Pair Group Method Average) method. Calculations were made using the software package Past 3.75 (Hammer et al., 2001).