Research paperIntegrative approach reveals new species of water bears (Pilatobius, Grevenius, and Acutuncus) from Arctic cryoconite holes, with the discovery of hidden lineages of Hypsibius
Introduction
Recent climate changes and increasing warming of polar and high mountain ecosystems are the main threats to psychrophiles. Consequently, due to a rapid change in environmental conditions, these organisms might completely disappear or hide in cold refugia (Fountain et al. 2012; Milner et al. 2017; Zawierucha & Shain 2019). Considering that the world is being subjected to the so-called sixth mass extinction, description and documentation of the current status of biodiversity is highly needed (Eisenhauer et al. 2019). Therefore, studies on the biodiversity in cryospheric habitats have gained special attention in recent years (Cauvy-Fraunie & Dangles 2019; Zawierucha & Shain 2019; Stibal et al. 2020). Glaciers and ice sheets form one of the coldest ecosystems, with the surface of a glacier (called the supraglacial zone), being the most biologically active and productive (Hodson et al. 2008; Cook et al. 2016b). The supraglacial zone consists of various habitats and forms myriads of niches for unicellular and multicellular organisms (Takeuchi et al. 2000; Stibal et al. 2006; Hodson et al. 2008; Franzetti et al. 2017; Zawierucha et al. 2019a). The most species-rich glacial ecosystems are cryoconite holes - extreme water-filled reservoirs embodied directly in the ice (Takeuchi et al. 2000; Hodson et al. 2008; Sommers et al. 2019a, b). The dark colour of cryoconite sediment reduces albedo of the glacier surface and absorbs solar radiation, which influences the formation of these water pools (Takeuchi et al. 2001; Cook et al. 2016b). Cryoconite holes are inhabited by primary producers like cyanobacteria and algae, heterotrophic bacteria, protozoans and invertebrates (Porazinska et al. 2004; Zawierucha et al. 2016a, 2018a; Pittino et al. 2018) represented by tardigrades and rotifers in Arctic cryoconite holes (Zawierucha et al. 2016a, 2020). Due to strong environmental selection pressure in cryoconite holes, organism assemblages inhabiting these ecosystems are mostly unique and different from those found in tundra or in other freshwater Arctic ponds. Instead of being embedded in soils or rocks, water and sediments in cryoconite holes are surrounded by ice that keeps the temperatures at near freezing even during summer days. For instance, the average temperature at the bottom of cryoconite holes on Arctic glacier is 0.08 °C with the maximum of 0.22 °C (Zawierucha et al. 2019b). In addition to low temperatures, Arctic cryoconite holes on small valley glaciers are dynamic and characterised by periodic freezing, removal of sediments from the bottom, and/or collapsing during stochastic weather events (e.g. rain and foehn winds) (Mueller et al. 2001; Zawierucha et al. 2019b). Such abiotic conditions most probably favour specialised, cold-adapted stenothermic ice inhabitants (Zawierucha et al. 2019a; Stibal et al. 2015). Recent biological studies on cryoconite holes are mostly focused on bacterial and photoautotroph physiology and diversity (e.g., Williamson et al. 2018; Pittino et al. 2018; Sommers et al. 2019a, b). Invertebrates, regrettably, although they are apex consumers in such extreme ecosystems, were not in the main scope of most of these studies (for review of the literature on the topic see Hodson et al. 2008; Cook et al. 2016b; Kaczmarek et al. 2016).
The fragmentary data on the diversity of metazoans in glacial ecosystems is a warning sign that the biodiversity of glacial habitats is still largely overlooked and underestimated. This is especially worrisome given the magnitude of glacial habitat loss anticipated this century (e.g. WGMS 2020; Zawierucha & Shain 2019). Indeed, the diversity of invertebrates inhabiting ice, although poor, is considered unique and often endemic (Zawierucha et al. 2016a, 2018c, 2019a), therefore a description of such endangered extremophiles is highly needed.
Tardigrada, also known as water bears, are one of the most common and abundant invertebrates inhabiting cryoconite holes worldwide, with densities in the holes being similar to other freshwater pools or limno-terrestrial ecosystems (Porazinska et al. 2004; Zawierucha et al. 2019a,b). So far, over 1300 tardigrade species have been described, mostly from bryophytes and lichens (Nelson et al. 2015; McInnes & Pugh 2018; Degma et al. 2020). As a result of their evolutionary history, tolerance to unfavourable conditions, small size and probable long-range distance dispersal by wind, tardigrades inhabit a variety of environments, from limno-terrestrial (soil, bryophytes, lichens) to aquatic (sediments, plants), including cryoconite holes (e.g., Nelson et al. 2015; McInnes et al. 2017; Zawierucha et al. 2019a). Tardigrades play an important role in trophic webs at a multitrophic level as carnivorous, omnivorous, herbivorous and microbivorous species (Hallas & Yeates 1972; Guidetti et al. 2012; Guil & Sanchez-Moreno 2013). As apex consumers in cryoconite holes due to grazing, they may potentially influence the diversity and density of other organisms inhabiting cryoconite holes ( T. Jaromerska pers. observ.), thus, they might be an important part of cryoconite ecosystems. Tardigrades seem to be well adapted to cryoconite hole environments due to intrinsic physiological features favouring life on ice, e.g. ability of tardigrades to enter cryobiosis (Møbjerg et al. 2011; Zawierucha et al. 2018c). Even though taxonomic studies on tardigrade biodiversity have been conducted in high mountain and polar regions (Cesari et al. 2016; Kaczmarek et al. 2018; Guidetti et al. 2019; Zawierucha et al. 2018b, 2019c; Dueñas-Cedillo et al. 2020; Stec et al. 2020), they focused mostly on bryophytes or lichens, and other glacial or glacier-adjacent environments have rarely been investigated (Grøngaard 1994; Zawierucha et al. 2019a, b). Studies on tardigrades in cryoconite holes have a long tradition, but published records are fragmentary and rare. To the best of our knowledge, tardigrades along with rotifers were the first animals described from cryoconite holes (Von Drygalski 1897; Jensen 1928), and studies on tardigrade fauna have continued since then (e.g. Dastych 1985, 2019; Grøngaard 1994; Grøngaard et al. 1992, 1999; Dabert et al. 2015; Zawierucha et al. 2018a, 2019a, b).
Recently, two genera of tardigrades new for science have been described from cryoconite. Zawierucha et al. (2018c) erected a new genus Cryoconicus from glaciers in central Asia. Molecular data placed Cryoconicus in the family Ramazzottiidae as a sister clade to the cosmopolitan genus Ramazzottius. The classical erection of a genus based on morphology was supported by the dark pigmentation unusual for limno-terrestrial tardigrades, the morphology of ventral apophyses for the insertion of the stylet muscles (AISM), the absence of accessory points on the claw branches and the presence of cuticular bars under claws I-III (Guidetti et al. 2019; Zawierucha et al. 2018c). Dastych (2019) erected a new glacier-dwelling genus Cryobiotus that for years was classified as Hypsibius (currently comprising four cryoconite obligatory species, see also Dastych et al. 2003). The erection of Cryobiotus was based on morphological characters: pigmentation, big eyes, the morphology of claws and AISM (Dastych 2019). Recent descriptions of new tardigrade genera from glaciers is a robust indicator that tardigrades in glacial ecosystems still await discovery.
Tardigrade species richness in extreme glacial habitats is known to be lower than that of tundra or high mountain ecosystems, potentially as a consequence of the strong selection pressure of the cryosphere. However, our knowledge of diversity of glacier-dwelling tardigrades are underestimated due to lack of taxonomic focus on these habitats and there is an increasing evidence that some tardigrade species in cryoconite holes are unique obligatory glacier-dwelling animals (e.g. Dastych et al. 2003; Zawierucha et al. 2016a, 2019a).
In order to fully understand glacial ecosystems, elucidating their biodiversity is a crucial step. Zawierucha et al. (2016a) described the diversity of tardigrades from Arctic cryoconite holes and emphasised, to avoid taxonomic confusion, that species should be described as new taxa only if additional fresh material with individuals for exact comparison is available. Since that time, several contributions have been published and taxonomic obstacles removed (Cesari et al. 2016; Dastych 2018; Gąsiorek et al. 2017, 2018, 2019). Therefore, here we describe three new species of tardigrades and reveal new genetic lineages of likely cryptic taxa from the High Arctic cryoconite holes in Svalbard and Greenland.
Section snippets
Sampling
The cryoconite samples were collected from the bottom of cryoconite holes on glaciers in Spitsbergen, the edge and “dark zone” in south-west Greenland (GrIS) (Table 1, Fig. 1). In total, nine glaciers and the ice sheet were sampled. Cryoconite was collected across a variety of glaciers differing in their: (i) morphology (i.e., tidewater, ice sheet, valley), (ii) thermal regime (i.e., polythermal, cold-based), and (iii) elevation (i.e., terminating in the sea or in valleys), for details see
Taxonomic account
Phylum Tardigrada Doyère, 1840
Class Eutardigrada Richters, 1926
Order: Parachela Schuster et al., 1980
Superfamily: Hypsibioidea Pilato, 1969
Family: Hypsibiidae Pilato, 1969
Subfamily Pilatobiinae Bertolani, Guidetti, Marchioro, Altiero, Rebecchi & Cesari, 2014.
Genus Pilatobius Bertolani, Guidetti, Marchioro, Altiero, Rebecchi & Cesari, 2014.
Pilatobius glacialis sp. nov. Zawierucha, Buda, Gąsiorek (Fig. 2, Fig. 3, Table 2).
Diphascon recamieri: Dastych 1985, De Smet & Van Rompu 1994, Grøngaard
Discussion
In this study, we formally described three new tardigrade species and revealed the next three new species (potentially cryptic and not formally named) from cryoconite holes by using genetic, morphological and morphometric analyses. Unique glacial ecosystems and specific environmental conditions were thought to form assemblages consisting of both opportunistic and specialist taxa (Porazinska et al. 2004; Stibal et al. 2006). However, new studies supported and corroborated the hypothesis that a
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.
Acknowledgments
The field work and laboratory analyses were supported by the National Science Center grant no. NCN 2013/11/N/NZ8/00597 to K.Z. We thank the team of the Stanislaw Siedlecki Polish Polar Station in Hornsund for their hospitality and assistance during the field works. K.Z. is grateful to Joseph Cook for collection of samples in the dark zone of the Greenland Ice Sheet, Małgorzata Kolicka and Marie Šabacká for collection of samples in the Svalbard archipelago, Maciej Wilk for help in field works on
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