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Evolutionary patterns of Pseudamnicola  D. Delicado et al.

              barriers that maintain isolated the split populations (Gavri-  genus, Corrosella, designating Corrosella falkneri as its type
              lets & Losos 2009; Glaubrecht 2011). However, a barrier  species. However, given the lack of other diagnostic char-
              does not need to be a geographic entity and may be also  acters for identifying each genus, Boeters (1984) concluded
              considered as a sudden shift of environmental conditions  that Corrosella should be a subgenus within Pseudamnicola.
              where the suitable habitat for a species ends (Fitzpatrick  This exemplification demonstrates the necessity of further
              et al. 2009; Pyron & Burbrink 2010). For instance, changes  studies to produce more exhaustive morphological and ana-
              in the chemical parameters of the aquatic environment can  tomical descriptions as well as well-supported, consistent
              favour allopatric separation between populations, especially  phylogenies. Hydrobiids s. str., and especially Pseudamnicola,
              for those groups that exhibit scarce dispersal abilities and  have weakly sculptured shells that exhibit scarce number of
              opportunities, resulting in restrictive distributions (Ponder  diagnostic characters (Arconada & Ramos 2003; Bichain
              & Colgan 2002; Perez et al. 2005). Freshwater gastropods,  et al. 2007; Strong et al. 2008) and therefore making it dif-
              which are typically habitat specialist, gather those proper-  ficult to establish clear species boundaries. By incorporating
              ties of limited dispersal capabilities and narrow-ranged dis-  molecular techniques and morphological and anatomical
              tributions and tend therefore to be strongly affected by  descriptions, Delicado et al. (2012, 2013) and Delicado &
              variation in their habitat. For this reason, they represent an  Ramos (2012) identified seven new species of P. (Corrosel-
              ideal model to investigate speciation processes associated  la), thus increasing the known species richness of this sub-
              with isolating mechanisms (e.g. Mav arez et al. 2002; Albr-  genus from five to 12. These studies not only revealed
              echt et al. 2007; von Rintelen et al. 2012; Schreiber et al.  cryptic species diversity within the genus, but also differ-
              2012; Delicado et al. 2013). In particular, one potential  ences in habitat requirements and distribution range
              candidate taxon that may provide valuable information  between the two subgenera. In fact, Delicado et al. (2013)
              about evolutionary processes in different environments is  found that these 12 species of P. (Corrosella) are mainly
              the microgastropod family Hydrobiidae Stimpson, 1965.  restricted to headwaters of mountainous regions of the Ibe-
                Hydrobiids are known to be presumably the most spe-  rian Peninsula and south of France, whereas around 45
              cies-rich family of freshwater gastropods, characterized  nominal species of P. (Pseudamnicola) have been recorded in
              besides by a long evolutionary history, wide distribution  streams, lakes and low river courses of several Mediterra-
              and ecological and morphological diversity. Recently, Wil-  nean islands and mainland territories (Pallary 1926; Sch€utt
              ke et al. (2013) published the most complete phylogenetic  & Bilgin 1970; Boeters 1976; Sch€utt & Sesen 1993; Ghamizi
              hypothesis on the superfamily Rissooidea (newly considered  et al. 1997; Gl€ oer et al. 2010; Bank 2011). These current
              as Truncatelloidea: Criscione & Ponder 2013) delineating  biodiversity patterns suggest different dispersal strategies
              the family Hydrobiidae s. str., as well as its distribution  between the subgenera: P. (Corrosella) may scarcely disperse
              range mainly to the Western Palearctic and eastern Nearc-  via habitat connection and suitability of habitats, which
              tic. Accordingly, this family comprises around 70 genus-  results in a pattern of isolation by distance (Wright 1943),
              level and 550 species-level taxa. Moreover, the diversity of  whereas the wider distribution range of P. (Pseudamnicola)
              habitat types which they inhabit is also remarkable.  may be a result of long-distance dispersions possibly via
              Approximately 35 hydrobiid species are brackish, and the  passive mechanisms (Delicado et al. 2013, 2014).
              rest occurs in freshwater ecosystems such as springs (the  Previous works revealed that diversification patterns of
              majority of the species according to Strong et al. 2008),  Pseudamnicola species belonging to the same subgenus are
              ponds, lakes and rivers. One inference of the hydrobiid  related to geographic isolation rather than ecological diver-
              phylogeny published by Wilke et al. (2013) is that species  gence (Delicado et al. 2013, 2014). Beyond what has been
              from the same subfamily seem to share similar ecological  shown by these studies, we hypothesize that the temporal
              requirements. A notable exception seems to be the genus  history and mode of diversification of the exclusively
              Pseudamnicola Paulucci 1878, whose evolutionary history  springsnail P. (Corrosella) species should differ of P. (Pseu-
              appears to have been influenced by a transition between  damnicola) species, which are more euryhaline in habit.
              two different environments. Consequently, this group may  Springs and headwaters of streams, the habitat type of
              be considered one of the key elements to understand the  P. (Corrosella) species, typically present more stable condi-
              origin and causes of the great hydrobiid diversity.  tions, being, however, more vulnerable to severe environ-
                Pseudamnicola was first proposed by Paulucci (1878) to  mental changes (as flooding or desiccation, pollution, etc.),
              differentiate between European and American Amnicola  which makes them isolated habitats and limiting factor for
              Gould & Haldeman, 1840 species, characterizing both  dispersion (Wilke et al. 2010). Moreover, due to their spa-
              groups mainly by their conchological features. Nearly a  tial location in small areas at high altitudes, most of these
              century later, Boeters (1970) studied the genus anatomically  springsnail species occur in a very confined number of
              and based on differences in female genitalia, defined a new  localities or even are single-site endemisms, increasing their



              404                                                        ª 2015 Royal Swedish Academy of Sciences, 44, 4, July 2015, pp 403–417
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