Short communicationDrepanocladus lycopodioides rediscovered in the Czech Republic: Abandoned quarries as refugia for endangered fen species
Introduction
Drepanocladus lycopodioides (Brid.) Warnst., syn. Pseudocalliergon lycopodioides (Brid.) Hedenäs, Scorpidium lycopodioides (Brid.) H.K.G. Paul, is a moss species of semi-aquatic calcareous habitats, including mostly calcareous and extremely rich fens, wet depressions in limestone areas and dune slacks (Hedenäs, 2003; van Tooren and Bruin, 2004). The distributional range of D. lycopodioides comprises Iceland, southern Scandinavia, Finnish Lapland, Denmark, the Baltic states, Ukraine, western Siberia, and western and central Europe (Hedenäs, 2003). Its core distribution area is the south Swedish Baltic area, i.e. Öland, Gotland, and the Stockholm Archipelago (Hedenäs and Bisang, 2015).
During the second half of the 20th century, the moss declined in many parts of Europe due to the intensification of agricultural management and degradation of suitable habitats (Hedenäs and Bisang, 2015). In view of its overall decline and current rarity, D. lycopodioides has been included among vulnerable taxa (VU) in the Red list of European bryophytes (Hodgetts et al., 2019). The species is often classified in higher categories of threat in national red lists, such as “critically endangered” in Norway and Slovakia (http://www.artsdatabanken.no, Mišíková et al., 2019) or “endangered” in Hungary and Romania (e.g. Papp et al., 2010; Ştefănuţ and Goia, 2012).
Historical data on the occurrence of the species in the Czech Republic is scarce (see Supplementary material for a list and further characteristics of known historical sites). According to Váňa (1981), a lowland calcareous mire nearby Hrabanov in central Bohemia represents the last place in the Czech Republic where the species was found in 1923. On the checklist and Red Lists of bryophytes of the Czech Republic (Kučera et al., 2012), D. lycopodioides is currently evaluated as extinct (RE). The species is also extremely rare in the surrounding countries. In Slovakia, for example, the species has been documented only in the Borská nížina lowland, where it was observed in the Abrod Nature Reserve until recently (Janovicová and Kubinská, 2002). In 2019, a population of D. lycopodioides was unexpectedly discovered by E. Šmerdová in the abandoned sandstone quarry known as “Lom Rasová” in the Bílé Karpaty (White Carpathian Mts) in the south-eastern part of the Czech Republic. The quarry currently represents the only known locality in the Czech Republic and one of two sites of D. lycopodioides in the Western Carpathians. The second confirmed record comes from the “Puścizna Rękowiańska” fen near Czarny Dunajec in the Orawsko-Nowotarska Kotlina basin in southern Poland (Ellis et al., 2016).
The aims of this study are (i) to describe the newly discovered locality, and first and foremost (ii) to draw the attention of bryologists and conservationists to quarries as potential refugia for endangered fen bryophytes in current landscapes.
Section snippets
Locality description
The newly discovered locality of D. lycopodioides is a former sandstone quarry situated near the village of Komňa (Fig. 1). The bedrock in the area is composed of Carpathian flysch, i.e. sedimentary rocks of Tertiary age characterised by alternating layers of sandstones and claystones. The mining at the site was performed by the open-pit mining method and took place from the end of the 18th century until the end of the 1960s (Mackovčin and Jatiová, 2002). Since then, the site has been left for
Site conditions and local vegetation
The population of D. lycopodioides occurs in the northern part of the quarry, at the margin of a shallow terrain depression filled with water (Fig. 2). Forming several small cushions, the moss inhabits a total area of approximately 1.2 m2. The water pH is 7.0–7.6, and the water conductivity of 320–570 μS/cm suggests calcium-rich water. The plot is periodically over-flooded in the autumn and winter, while it can dry out completely in the summer.
The following vegetation plot was sampled in the
Author contribution
Tomáš Peterka: conceptualization, writing - original draft
Eva Šmerdová: investigation, writing - review & editing
Michal Hájek: investigation, writing - review & editing
Eva Mikulášková: validation, writing - review & editing
Petra Hájková: investigation, writing - review & editing
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgements
We are grateful to three anonymous referees and Elisabeth Gross for their comments that helped us improve the previous version of the manuscript. Jan Kučera performed molecular barcoding of the herbarium specimen. Martin Večeřa created the map. The research was supported by the Czech Science Foundation (project GJ19-20530Y). PH was partially supported by a long-term research development project of the Czech Academy of Sciences (RVO 67985939).
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For references that are not in English see Supplementary material.