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Trematode species diversity in the faucet snail, Bithynia tentaculata at the western edge of its native distribution, in Ireland

Published online by Cambridge University Press:  18 September 2024

A. Faltýnková*
Affiliation:
Department of Forest Ecology, Faculty of Forestry and Wood Technology, Mendel University in Brno, Zemědělská 3, Brno, 613 00, Czech Republic
K. O’Dwyer
Affiliation:
Marine and Freshwater Research Centre, Atlantic Technological University, Old Dublin Road, Galway, H91 T8NW, Ireland
C. Pantoja
Affiliation:
Institute of Parasitology, Biology Centre of the Czech Academy of Sciences, Branišovská 31, 370 05 České Budějovice, Czech Republic
D. Jouet
Affiliation:
ESCAPE UR7510, USC ANSES PETARD, University of Reims Champagne-Ardenne, Faculty of Pharmacy, 51 rue Cognacq-Jay, 51096, Reims Cedex, France
K. Skírnisson
Affiliation:
Laboratory of Parasitology, Institute for Experimental Pathology, Keldur, University of Iceland, IS-112 Reykjavík, Iceland
O. Kudlai
Affiliation:
Institute of Ecology, Nature Research Centre, Akademijos 2, 08412, Vilnius, Lithuania
*
Corresponding author: A. Faltýnková; Email: faltyn.anna@gmail.com
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Abstract

Trematodes and their snail hosts have developed intimate parasite-host associations, with snails supporting a diverse and often species-specific trematode fauna. In the faucet snail, Bithynia tentaculata (Caenogastropoda, Littorinimorpha), a unique trematode fauna has been recorded recently. However, knowledge of the exact species identity, phylogenetic relationships, and geographical distribution remains limited as many of the species belong to groups with unclear or controversial taxonomical assignment. To contribute to our knowledge of the trematodes, we investigated the trematode fauna of B. tentaculata by examining a total of 556 snails from lakes in County Galway, Ireland. Using an integrative taxonomic approach including DNA sequence data analyses (28S rRNA gene, ITS1-5.8S-ITS2, ITS2, cox1, nad1) and morphological tools (taxonomical drawings and measurements), we identified nine trematode species of seven families, with seven species occurring as cercariae (Cyathocotyle prussica, Lecithodendrium linstowi, Lecithodendrium sp., Asymphylodora progenetica, Sphaerostoma bramae, Metorchis xanthosomus, and Notocotylus sp.) and three species occurring as metacercariae (A. progenetica, Parasymphylodora parasquamosa, and Sphaeridiotrema sp.). Except for S. bramae, all are new species records for Ireland and provide the most western distribution of these trematodes in Europe. The trematode species recorded are known to use a wide range of definitive hosts and have a wide geographical distribution; among them are species members of genera that are zoonotic (Metorchis) and pathogenic to wildlife (Cyathocotyle, Sphaeridiotrema, and Notocotylus). There remains an ongoing need for precise identification of the trematode species to ensure that wider ecological contexts are correctly understood and biodiversity and disease threats can be accurately evaluated.

Information

Type
Research Paper
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0), which permits unrestricted re-use, distribution and reproduction, provided the original article is properly cited.
Copyright
© The Author(s), 2024. Published by Cambridge University Press
Figure 0

Table 1. Summary data for the sequences of trematodes used for phylogenetic analyses; novel sequences generated in the present study are in bold

Figure 1

Table 2. List of larval trematode species and their prevalence in % (No. of infected snails) in the faucet snail, Bithynia tentaculata, in Irish lakes in County Galway

Figure 2

Figure 1. Phylogram resulting from Bayesian inference (BI) analysis based on the 28S rDNA sequences for species of Cyathocotyle and of the Cyathocotylidae with nodal support values shown at the node as BI/ML (maximum likelihood). Only values > 0.90 (BI) and > 70 (ML) are displayed. Scale bar indicates the expected number of substitutions per site. The sequence generated in this study is in bold.

Figure 3

Figure 2. Phylogram resulting from Bayesian inference (BI) analysis based on the 28S rDNA sequences (A) and ITS2 sequences (B) for species of Lecithodendrium and of the Lecithodendriidae with nodal support values shown at the node as BI/ML (maximum likelihood). Only values > 0.90 (BI) and > 70 (ML) are displayed. Scale bar indicates the expected number of substitutions per site. Sequences generated in this study are in bold.

Figure 4

Figure 3. Phylogram resulting from Bayesian inference (BI) analysis based on the 28S rDNA sequences for species of Sphaerostoma and of the Opecoelidae with nodal support values shown at the node as BI/ML (maximum likelihood). Only values > 0.90 (BI) and > 70 (ML) are displayed. Scale bar indicates the expected number of substitutions per site. Sequences generated in this study are in bold.

Figure 5

Figure 4. Phylogram resulting from Bayesian inference (BI) analysis based on the 28S rDNA sequences (A) and partial cox1 sequences (B) for species of Metorchis and the Opisthorchiidae with nodal support values shown at the node as BI/ML (maximum likelihood). Only values > 0.90 (BI) and > 70 (ML) are displayed. Scale bar indicates the expected number of substitutions per site. Sequences generated in this study are in bold.

Figure 6

Figure 5. Phylogram resulting from Bayesian inference (BI) analysis based on the 28S rDNA sequences (A) and ITS2 sequences (B) for species of Asymphylodora, Parasymphylodora, and the Lissorchiidae with nodal support values shown at the node as BI/ML (maximum likelihood). Only values > 0.90 (BI) and > 70 (ML) are displayed. Scale bar indicates the expected number of substitutions per site. Sequences generated in this study are in bold.

Figure 7

Figure 6. Phylogram resulting from Bayesian inference (BI) analysis based on the 28S rDNA sequences for species of Sphaeridiotrema and of the Psilostomidae (A) and for species of Notocotylus and of the Notocotylidae (B) with nodal support values shown at the node as BI/ML (maximum likelihood). Only values > 0.90 (BI) and > 70 (ML) are displayed. Scale bar indicates the expected number of substitutions per site. Sequences generated in this study are in bold.

Figure 8

Figure 7. Morphology of trematodes ex Bithynia tentaculata. (A, B) Cyathocotyle prussica (A, ventral view of body; B, total view); (C–E) Lecithodendrium linstowi (C, total view; D, stylet; E, sporocyst); (F, G) Lecithodendrium sp. (F, total view; G, stylet). Scale bars: A, C, E, 100 μm; B, 200 μm; D, G, 20 μm; F, 50 μm.

Figure 9

Figure 8. Morphology of trematodes ex Bithynia tentaculata. (A, B) Sphaerostoma bramae (A, total view; B, stylet); (C, D) Metorchis xanthosomus (C, ventral view of body; D, total view); (E–H) Notocotylus sp. (E, ventral view of body; F, total view; G, detail of eyespots and Yenchingensis-type of excretory system; H, redia). Scale bars: A, C, E, 100 μm; D, F, 200 μm; G, 50 μm; B, 10 μm; H, 400 μm.