Abstract
Red snow is a well-known phenomenon caused by microalgae thriving in alpine and polar regions during the melting season. The ecology and biodiversity of these organisms, which are adapted to low temperatures, high irradiance and freeze–thaw events, are still poorly understood. We compared two different snow habitats containing two different green algal genera in the European Alps, namely algae blooming in seasonal rock-based snowfields (Chlamydomonas nivalis) and algae dominating waterlogged snow bedded over ice (Chlainomonas sp.). Despite the morphological similarity of the red spores found at the snow surface, we found differences in intracellular organization investigated by light and transmission electron microscopy and in secondary pigments investigated by chromatographic analysis in combination with mass spectrometry. Spores of Chlainomonas sp. show clear differences from Chlamydomonas nivalis in cell wall arrangement and plastid organization. Active photosynthesis at ambient temperatures indicates a high physiological activity, despite no cell division being present. Lipid bodies containing the carotenoid astaxanthin, which produces the red color, dominate cells of both species, but are modified differently. While in Chlainomonas sp. astaxanthin is mainly esterified with two fatty acids and is more apolar, in Chamydomonas nivalis, in contrast, less apolar monoesters prevail.
Keywords: astaxanthin, cryoflora, snow algae, spores, ultrastructure
Red snow composed of Chlainomonas sp. was investigated with regard to its ecophysiology, secondary pigments and ultastructure, and several differences in astaxanthin composition and chloroplast arrangement were found when compared with Chlamydomonas nivalis.
INTRODUCTION
Long-lasting, slowly melting summer snow fields in alpine and polar regions are the predominant habitats for extremophilic microalgae causing red snow or other colorations (Hoham and Duval 2001). Photoautotrophs adapted to these harsh conditions mostly belong to the Chlamydomonadales (Chlorophyta; Komárek and Nedbalová 2008). Snow algae are of general interest in terms of understanding fundamental cellular strategies to cope with low temperatures, extreme irradiation and desiccation stress due to freezing events. In addition, highly abundant compounds reducing or preventing abiotic stress might be of commercial interest (Varshney et al.2015). Commonly, populations causing red snow are connected with Chlamydomonas cf. nivalis, which is recognized as a collective taxon (Kol 1968). The typical cell morphology consists of spherical red spores that have a single-layered cell wall never detached from the protoplast, occasionally encapsulated by cryoconite particles (Remias, Lütz-Meindl and Lütz 2005). This taxon has been reported from almost all mountainous and polar regions worldwide, and recently even from snow at an African glacier in Tanzania (Uetake et al.2014), the last continent so far without reports of Chlamydomonas (Cd.) cf. nivalis—the first report of snow algae from Africa (Atlas Mountains), by Duval, Duval and Hoham (1999), did not mention this species. Other algae causing red snow belong to the genus Chlainomonas. These cells are usually larger than the first species and have an ellipsoidal shape; cell walls were earlier described as being removed from the protoplast or multilayered; swarmers have four flagella; and the cytoplasm is almost entirely occupied by red pigments (Ettl 1983). Two species of this genus that live in snow have been described, Chlainomonas (Cn.) rubra (Hoham 1974a) and Cn. kolii (Hoham 1974b). They have been found in the European Alps (Kol 1970), North America (Hoham 1974a,b), New Zealand (Novis 2002a), Spitsbergen (Kvíderová 2012) and Bulgaria (Cepák and Lukavský 2013). Using phylogenetic trees based on rbcL gene sequences, both Novis et al. (2008) and Muramoto et al. (2010) found Chlainomonas embedded in a clade of Chloromonas species that also live in snow habitats, despite the spores of Chlainomonas having morphological similarities to a different, Chlamydomonas-related clade of snow algae.
The abundant secondary pigment of all snow algae that have been investigated is the keto-carotenoid astaxanthin (and esterified derivatives), which is responsible for the red to orange appearance of these green algae, in particular of the lipid bodies in the cytoplasm (Remias, Lütz-Meindl and Lütz 2005; 2013; Řezanka et al.2013). The physiological role of astaxanthin is multifunctional: it protects the chloroplast against excessive irradiation and thus prevents photoinhibition or UV damage, it may serve as a powerful antioxidant, and it may represent a ‘metabolic sink’ of the non-dividing spores (Li et al.2008; Lemoine and Schoefs 2010). As astaxanthin is a nitrogen-free compound, its synthesis is not limited by low nutrients in the habitat, which is the case for snow remote from sea shores or any animal colonies (Hoham and Duval 2001). Further essential snow algal compounds are, for example, polyols like glycerol or ice-nucleating proteins, which lower the intra- or extracellular freezing point or prevent formation of damaging ice crystals within or close to the cells (Leya 2013; Raymond 2014). In contrast, the red pigments of Chlainomonas have never been studied before.
Global distribution and local abundances of Chlainomonas causing red snow seems to be restricted compared with the commonly reported Cd. cf. nivalis. We investigate here the hypothesis that these genera have different ecological demands. Chlamydomonas cf. nivalis is typically known from exposed seasonal snowfields above timberline, whereas Chlainomonas was found either in shaded areas below a canopy (Hoham 1974b) or in locations where snow becomes slushy during summer because meltwater drainage is limited (Remias 2012). This is common either in snow on glacier surfaces or in snow on the melting ice cover of high mountain lakes (Novis 2002b; this study). Another reason for a low number of reports could be misidentifications. For example, cell stages of the snow alga Chloromonas (Cr.) bolyaiana (Kol 1970) and Cd. sanguinea (Ettl 1983) have similar morphologies. Additionally, old spores of Chlainomonas turn from ellipsoidal to spherical during maturation and thus become almost identical to those of Cd. cf. nivalis (Hoham 1974a). In addition, the red cytoplasmic pigmentation is very similar in appearance to that of Cd. cf. nivalis.
Consequently, an intention of this study was to demonstrate specific characteristics of Chlainomonas spores at the light microscopy (LM) level, especially in contrast to Cd. cf. nivalis. Moreover, transmission electron microscopy (TEM) investigations were performed to visualize differences. Finally, chromatographic methods (liquid chromatography using chemotaxonomic characteristics) were used to test for different secondary pigment patterns. The ecophysiology of Chlainomonas has been mainly uninvestigated so far, and probably the only work was by Novis (2002b) for Cn. kolii. Therefore, a further aim of this study was to achieve insight into cellular adaption strategies. Field samples were harvested in situ mainly from snow slush on the melting ice cover of a high alpine lake in the Austrian Alps, where blooms of this species occur annually. We performed structural and ultrastructural studies, photosynthesis measurements and analysis of the secondary red pigmentation. The results were partly compared with red snow caused by Cd. cf. nivalis originating from the same region. For the latter, several physiological studies were previously reported (Stibal et al.2007; Lukeš et al.2014). Additionally, a ‘chemotaxonomic’ approach was undertaken for the first time with snow algae, comparing the patterns of native astaxanthin derivatives. We hypothesized that different taxa causing red snow, despite having a rather similar morphology, can be distinguished either by their ecological demands or by the polarity and molecular size of their individual astaxanthin esters. Moreover, we investigated apparent cytological differences.
MATERIALS AND METHODS
Field work and sample preparation
Chlainomonas sp. was collected from slushy red snow at the ice cover of Gossenkölle Lake (Kühtai valley, Tyrol, Austria) on 19 June 2008 (sample HW02), 12 June 2009 (AS02), 3 June 2010 (GK04), 15 June 2010 (GK12) and 11 June 2015 (DR67). A further sample was harvested from snow slush at Hallstätter glacier close to Mount Dachstein (Upper Austria) on 17 July 2009 (DR53). The complete list of Chlainomonas sp. collections with elevation, geographic position and snow chemistry is given in Table 1. Chlamydomonas cf. nivalis causing red snow was also collected in the Austrian Alps; a complete list with collection details is given in Supplementary Table 1. Before harvesting cells with a stainless steel shovel, a surface snow layer of approximately 1 cm, containing also allochthonous debris was removed. Then, snow was gently melted at 4°C and further cleaned of impurities by filtering through stainless steel sieves with 800, 400, 200 and 100 μm mesh size. The electrical conductivity of the meltwater was measured with a Cond 340i, and the pH with an Inolab system (both WTW Instruments, Germany). For TEM, field samples were further cleaned of microdebris by density centrifugation, using a gradient with layers of 0, 50 and 100% Percoll (Sigma-Aldrich) at 400 g for 10 min. For analytical purposes, the meltwater containing the cells was vacuum filtered through 47 mm glass fiber disks (Whatman GF/C). Filters with attached cells were rapidly frozen in liquid nitrogen and subsequently freeze-dried in a lyophilisator for 48 h. The lyophilized samples were stored at –50°C until analysis.
Table 1.
Sample | Date | Location | GPS position | Altitude (m) | pH | EC (μS cm−1) | Length (μm) | Width (μm) |
---|---|---|---|---|---|---|---|---|
HW02 | 19 Jun 2008 | Gossenkölle lake, T | N47°13.753 E11°00.863 | 2411 | 5.9 | 2.1 | 28–36 | |
AS02 | 12 Jun 2009 | Gossenkölle lake, T | N47°13.753 E11°00.863 | 2411 | 5.8 | 10.0 | 32.7 ± 5.9 | |
GK04 | 3 Jun 2010 | Gossenkölle lake, T | N47°13.753 E11°00.863 | 2411 | 6.0 | 6.9 | n/a | n/a |
DR53 | 17 Aug 2009 | Hallstätter Glacier, U | N47°28.640 E13°36.927 | 2640 | 5.9 | 7.1 | 26.5 ± 3.8 | 22.2 ± 4.8 |
GK12 | 15 Jun 2010 | Gossenkölle lake, T | N47°13.753 E11°00.863 | 2411 | 5.4 | 2.6 | 27.4 ± 4.9 | 23.3 ± 2.8 |
DR67 | 11 Jun 2015 | Gossenkölle lake, T | N47°13.762 E11°00.885 | 2411 | 5.3 | 7.4 | 36.3 ± 3.5 | 33.1 ± 2.1 |
Abbreviations: EC, electrical conductivity; n/a, not available; T, Tyrol; U, Upper Austria.
Light and transmission electron microscopy
For LM studies of ripening spores, field samples were kept alive in the laboratory for several weeks after collection at 4°C and approximately 100 μmol PAR m−2 s−1 (16 h d−1). Cells were observed by a Zeiss (Carl Zeiss AG, Jena, Germany) Axiovert 200M light microscope equipped with a Zeiss MRc5 camera with a ×63, 1.4 NA objective. Specimen temperature was kept at 1°C during observation to prevent heat stress in a thermoregulated chamber (LM-TCC; Buchner, Lütz and Holzinger 2007). Chlorophyll autofluorescence images were captured with a Zeiss 09 filter set (ex: 450–490 nm, em: 515 nm long pass (LP). Cell numbers per unit meltwater volume were obtained with a 0.5 mL plankton-counting chamber according to Kolkwitz (Hydro-Bios, Kiel, Germany). The TEM fixation of the sample HW02 and embedding protocol was applied according to Holzinger, Roleda and Lütz (2009). Briefly, samples were fixed in 2.5% glutaraldehyde in 10 mM caccodylate buffer (pH 7.0) for 2 h at 4°C, postfixed in 1% OsO4 overnight at 4°C, gradually dehydrated and embedded in modified Spurr's resin. Ultrathin sections were prepared by a Leica Ultramicrotome and counterstained, and samples were examined with a Zeiss Libra 120 TEM at 80 kV.
DNA isolation, polymerase chain reaction and phylogenetic analyses
The field sample of Chlainomonas sp. DR67 was centrifuged and 200 μL of the Instagene Matrix (Bio-Rad Laboratories, USA) was added to the pellet. Then, the cells were mechanically damaged by shaking with glass beads in a Mixer Mill MM 400 (Retsch, Germany). The mixture was kept at 56°C for 30 min while being stirred, vortexed shortly and subsequently kept at 99°C for 8 min without stirring. After being shortly vortexed again, the samples were centrifuged at 17 000 g for 2 min and the supernatant was used as a polymerase chain reaction (PCR) template. The primers 7F and 1391R (Verbruggen et al.2009) were used for the amplification of the rbcL gene. Each PCR reaction contained 13.15 mL sterile Milli-Q water, 2 mL MgCl2 (25 mM), 2 mL AmpliTaq Gold 360 Buffer (Applied Biosystems, Carlsbad, CA, USA), 0.4 mL dNTP mix (10 mM), 1 mL of the 7F primer, 0.25 mL of the 1391R primer (primer concentration 25 pmol mL–1), 0.2 mL AmpliTaq Gold 360 DNA Polymerase and 1 mL DNA (10 ng μL−1). The PCR consisted of an initial denaturation for 3 min at 94°C, followed by 35 amplification cycles, each with a 1 min denaturation step at 94°C, 1 min annealing at 40°C and 2 min extension at 72°C, and a final extension stage at 72°C. for 5 min. The purification of the PCR product and DNA sequencing were performed by Macrogen Inc. (Seoul, South Korea). The newly obtained sequence was submitted to the European Nucleotide Archive (ENA) under the accession number LN897303. An 899 nucleotide alignment was created using additional rbcL sequences of 17 related strains and two outgroup strains, published in the GenBank database. Two different phylogenetic analyses were performed: Bayesian inference (BI) and maximum likelihood (ML). The sequence evolution model was determined as GTR + gamma by MrModelTest 2.3 (Nylander 2004) using the Akaike Information Criterion. The BI phylogenetic tree was constructed using MrBayes 3.2.1 (Ronquist and Huelsenbeck 2003). Two parallel Markov chain Monte Carlo runs were carried out for 3 000 000 generations, each with one cold and three heated chains. Convergence of the two cold chains was checked by the average standard deviation of split frequencies: the value was 0.000971. Trees and parameters were sampled every 100 generations, and trees from the initial 1000 generations were discarded using the sumt burnin function. Bootstrap analysis was performed by maximum likelihood (ML) in Garli 2.0 (Zwickl 2006) and PAUP* Portable version 4.0b10 (Swofford 2002). ML analyses consisted of rapid heuristic searches (100 pseudo-replicates) using automatic termination (genthreshfortopoterm command set to 100 000).
Photosynthesis
Light-dependent oxygen production and respiration was measured 1 day after collection (sample GK04) in a temperature-controlled 3 mL acryl-chamber thermostated to 1°C, connected with a Fibox 3 optode and an oxygen dipping probe (PreSens, Germany) according to Remias et al. (2013). The average turnover per unit time of four replicates (n = 4) was normalized to the amount of chlorophyll a per sample. The chlorophyll a content was calculated after cell extraction with a PE Lambda 20 spectrophotometer (Remias et al.2013).
Pigment characterization by HPLC
Freeze-dried algae were ground with a grinding mill with Teflon jars and quartzballs (Mikro-Dismembrator S, Sartorius, Germany) and dissolved in 3 mL N,N-dimethylformamide (Sigma-Aldrich) for apolar pigment extraction. Extracts were stored at –50°C prior to use. Chlorophylls, primary and secondary carotenoids and α-tocopherol were identified and quantified with a RP C18 HPLC column protocol in combination with diode array and fluorescence detector in a row, according to Remias and Lütz (2007).
Astaxanthin-ester comparison by liquid chromatography–mass spectrometry
The individual signatures of astaxanthin derivatives (peak size, retention time, molecular weight) of Chlainomonas sp. and Cd. cf. nivalis were compared with an Agilent 1100 HPLC system using a diode array detector, coupled with a Bruker Esquire 3000 mass spectrometer. Chromatographic conditions were as follows. HPLC column: Jupiter 5μ C18 300A, 250 × 2 mm (Phenomenex), thermostated at 25°C; solvent A: methanol; solvent B: acetonitrile–dichloromethane–methanol, 2:1:1; pumping rate: 0.4 mL min−1. Acetonitrile and methanol were of HPLC gradient quality. Linear mobile phase gradient: 1% B, 0–15 min; 1–77.7% B, 15–50 min; 100% B, 51–55 min (wash step); and 1% B, 55–65 min (reconditioning). Filters with freeze-dried algae were extracted in dichloromethane, and the supernatant was then vaporized and the residue resolved in methanol and centrifuged prior to injection of the supernatant. Mass spectrometry was performed using atmospheric pressure chemical ionization at positive mode (APCI+), drying temperature 250°C, ionization at 400°C, dry gas 10 L min−1 and vaporization at 50 p.s.i. Ion trap scanning was set from 200 to 1500 m/z. The MSMS mode was used for fragmentation of astaxanthin ester peaks to determine the presence of either a mono- or diester at a given retention time. Consequently, the liquid chromatography–mass spectrometry (LC-MS) set-up was used for the calculation of the native astaxanthin mono- to diester ratio by semi-quantitative summing of the integrated peak areas of both groups. Triglyceride peaks, which also occurred abundantly in the apolar extract and thus in the MS detector, were distinguished from astaxanthin esters with similar retention times by the missing spectral absorbance in the VIS region (chromatogram: 480 nm) and subsequently not used for the chemotaxonomic comparison. For the latter, the two largest MS ions of each astaxanthin ester peak were used in combination with their chromatographic retention time. Peaks with a height less than 50 mAU were not used due to MS signal noise.
RESULTS
Field observations
Chlainomonas sp. was sampled in the Austrian Alps during four growth seasons in a 7-year period. It was harvested from snow slush bedded on the surface ice cover of the high alpine Gossenkölle Lake, and one sample from waterlogged snow slush on glacial ice close to the Mount Dachstein (for location photographs, see Supplementary Figs 1 and 2). The exact geographic positions, elevations, pH (ranging from 5.4 to 5.9) and electrical conductivities (ranging from 2.6 to 7.4 μS cm−1) of snow meltwater are summarized in Table 1. The Chlainomonas population at Gossenkölle Lake was a regular local phenomenon, as it was observed every growing season sampled from 2008 to 2015, and harvested material consisted practically only of this species, despite the other snow algae Cr. cf. nivalis, Cr. brevispina, Cr. rosae var. psychrophila and Cd. cf. nivalis being present in the vicinity of the lake. For comparison, blooms of Cd. cf. nivalis were taken from seasonal snowfields above timberline. The population densities of Chlainomonas sp. were approximately 3 × 103 (HW02) and 1 × 104 cells mL−1 snow meltwater (GK12), compared with 5 × 104 for Cd. cf. nivalis (HW16), resulting in a more intense appearance of the latter red snow.
Cell structure and ultrastructure
Chlainomonas sp. had swarmers with four flagella and their length was about the same as that of the cells (Fig. 1a). They were seen moving slowly when observed by LM and without notable cell rotation. Flagella were oriented at the backside during the movement (see Supplementary Video 1). They retained functionality only when observed below 2°C, and otherwise they were discharged within seconds when cells were exposed to higher temperatures. Occasionally cells had less than four flagella. The motile cells were of ellipsoidal shape with average sizes of 26–36 μm in length and 23–33 μm in width (see Table 1). A typical papilla was usually not present, but four flagella grooves were observed in the cell envelope (Fig. 1b). A very characteristic detail of this stage was, to a varying extent, widened and partially thickened smooth cell walls in the anterior and posterior section (Fig. 1c and d). The protoplast was more or less circular; further details were almost entirely obscured by the red secondary pigments, but with three exceptions. First, four contractile vacuoles were present at the anterior apex; second, a central more or less spherical region with a diameter of about 2–3 μm appeared brightened in LM, representing the location of the nucleus (Fig. 1c), as proved by TEM (see below); and third, the lipid bodies containing astaxanthin frequently did not reach the margins of the protoplast, but instead many small plastids (position and morphology made visible using chlorophyll auto fluorescence; Fig. 1e) were located parietally and sometimes visible as a more or less greenish ‘corona’ (Fig. 1f). These three characteristics were never observed for the morphologically similar Cd. cf. nivalis.
The successional cell stage was a mature ‘resting spore’. These either occurred in samples collected later in the season just before complete melt of the lake ice, or developed from swarmers kept in meltwater at 4°C in the laboratory for several weeks (Fig. 1g). These cells lost flagella, had no partial thickened outermost cell wall anymore and were always spherical. Alternatively, the chloroplasts were located around the central nucleus as indicated by their auto-fluorescence (Fig. 1h). A new, characteristic secondary cell wall was formed inside, and it became thicker and less translucent during aging, maybe accompanied by incrustation. The outer cell wall remained thin, was not incrusted and had a dark outer margin. A third or multiple thin outermost and transparent envelopes (Fig. 1g) frequently accompanied it. Further cellular details like stigma, spines on the wall exterior, cell divisions or any other stages in the life cycle were not observed in field material. Occasionally, some small red flagellates with prominent papilla but uncertain taxonomic affiliation were found (Supplementary Fig. 3).
More detailed information on Chlainomonas’ cytoarchitecture was gained using TEM. The nucleus was centrally located and surrounded by numerous lipid bodies (Fig. 2a). Typical was a peripheral arrangement of many small plastids containing starch grains but no pyrenoid. Of note were several vacuoles of unknown function with electron-dense content, which was partly crystallized (Fig. 2b). Figure 2c shows a cell with bilayered cell wall; the outer cell wall layer was widened at the anterior and posterior typical of swarmers of this species. Mature spores with three cell wall layers (Fig. 2d) had plastids not directly located below the cell membrane, and one can assume a high physiological activity through the presence of many Golgi bodies with attached vesicles (Fig. 2e). The nucleoplasm contained occasional remarkable strand-like clusters (Fig. 2f). In contrast, TEM of Cd. cf. nivalis (Supplementary Fig. 4) showed only single-walled spores of spherical shape and attached cryoconite particles. There was always one central chloroplast with naked pyrenoid, surrounded by lipid bodies.
Phylogenetic analyses
Phylogenetic analyses of the rbcL sequence placed the field sample Chlainomonas sp. DR67 among other species of the genus Chlainomonas. All species of the genus form a well-supported monophylletic clade (Fig. 3). Interestingly, Cn. rubra and Cn. kolii from North America and New Zealand were more closely related to each other than to Chlainomonas sp. from the Austrian Alps. Consequently, no species affiliation was performed for the samples of this work. Other close relatives of Chlainomonas were several species of Chloromonas that also live in snow.
Photosynthesis
Dark respiration and light-dependent oxygen production were measured at 1°C, close to ambient conditions. The photosynthetic performance was tested under five different light levels (Fig. 4). At low light conditions (48 μmol PAR m−2 s−1) a net oxygen production of 10.6 ± 3.9 μmol O2 (mg Chl h)−1 was already achieved, considering a more than two-fold oxygen consumption during the dark phase. No photoinhibition was observed up to 1378 μmol PAR m−2 s−1.
Pigments
HPLC of apolar extracts revealed astaxanthin as the only secondary carotenoid of Chlainomonas sp. It causes the red coloration of cells due to its abundance compared with chlorophylls and primary carotenoids. Cells have about five times more astaxanthin than chlorophyll a (sample AS02). Further pigment contents (relative ratios of pigments and of α-tocopherol to chlorophyll a in comparison with Cd. cf. nivalis) are given in Supplementary Table 2. A representative chromatogram of Chlainomonas sp. (Supplementary Fig. 5) shows a large number of peaks with varying size and identical online absorption maxima either at 470 nm, or alternatively at 466 nm in combination with an additional side maximum at 370 nm. Their spectral absorptions are in accordance with all-trans and 13 cis-astaxanthin standards (Supplementary Fig. 6), which, however, had much earlier chromatographic retention times of 2.2 and 2.5 min than the algal peaks (from 3.7 to 45.1 min). Consequently, astaxanthin was accumulated natively for the most part as a number of different derivatives (e.g. more than 99% of total astaxanthin peak area in sample AS02), the secondary carotenoid therefore becoming more apolar.
Despite the same red cell color, HPLC of Cd. cf. nivalis interestingly exhibited many differences in relative peak sizes and retention times of astaxanthin derivatives (Supplementary Fig. 7). For instance, very apolar peaks with high retention times were relatively small, while Chlainomonas sp. typically had relatively larger peaks in this region (Supplementary Fig. 5). These characteristic patterns of the two species were constant, regardless of collecting season or growing site in the Austrian Alps. Additionally, a sample of Cn. rubra from New Zealand (courtesy of Phil Novis, Landcare Research, Lincoln, NZ) exhibited a chromatogram like the populations of this study from Europe with a characteristic dominance of peaks with late retention times and α-tocopherol levels much higher than in Cd. cf. nivalis.
Comparison of astaxanthin derivatives
Taking the species-specific constancy of astaxanthin derivatives in chromatograms of both snow algae into account, independent of the collection year and location, a tentative comparison was undertaken, using the two main parameters of molecular size (m/z) and compound polarity (retention time). Additionally, the abundance of pigment derivative classes was calculated. Therefore, LC-MS was applied with apolar extracts to gain information about the nature of astaxanthin derivatives in detail. Using APCI+, the detector received carotenoid ions as [M+H]+. This, and the mode of astaxanthin fragmentation during MS, was clarified by injecting two astaxanthin standards (all-trans and 13-cis isomer). A characteristic phenomenon was an m/z = –18 split-off and a minor m/z = –36 split-off from the native compound with the all-trans and 13-cis isomer, respectively (Supplementary Fig. 8). Most likely one water [M+H-18]+ and two water molecules [M+H-2×18]+, respectively, were cleaved from the carotenoid. The same mechanism was found frequently for astaxanthin derivatives, either spontaneously without active MS fragmentation or during the active MSMS fragmentation process, too. By fragmentation, astaxanthin mono- and diesters were identified by cleavage of either one or two fragments, respectively, with a size typical for algal fatty acids, and an astaxanthin residue was finally left. A representative example of diester fragmentation is given in Supplementary Fig. 9.
The abundances of astaxanthin derivatives were compared between Chlainomonas sp. and Cd. cf. nivalis (Fig. 5). In each species, astaxanthin was esterified with one or two fatty acids of different size and polarity. Both snow algae had similar pigment monoesters in terms of size and polarity (at lower retention times), but a more individual pattern was present for higher retention times and for diesters in general. In a final step, the ratios of mono- to diesters of astaxanthin of both species were compared by summing the respective HPLC peak areas (Supplementary Table 3). As a prominent difference, Chlainomonas sp. stored the majority of astaxanthin derivatives in the diester form, and to the contrary, Cd. cf. nivalis stored them in the less apolar monoester form. There were no indications of any further kind of astaxanthin derivatives in any of the samples from both species.
DISCUSSION
This study was performed with field material with the intention of describing Chlainomonas sp. in its authentic physiological and cytological state in alpine habitat conditions. Generally, chloromonads in culture exhibit a very different phenotype, without secondary pigments, hardly forming any resting stages, or with striking cytoarchitecture such as secondary wall structures or chloroplast shape rearrangements. Moreover, many snow algae are not available in culture collections, though one field sample collected for this study (HW02) was deposited in the CCCryo collection (Fraunhofer, Potsdam-Golm, Germany) and transformed into a green strain by cultivation (strain CCCryo 345-09 ‘Chloromonas sp.’).
The slightly acidic pH values and low electrical conductivities of algal snow meltwater were similar to those for Cd. cf. nivalis and many other snow algae of habitats with low nutrients (Hoham and Duval 2001; Hoham et al.2007). Spijkerman et al. (2012) suggested that the distribution of snow algae also depends on topographical and geological parameters like slope, occurrence of meltwater rivulets and rock formation.
Only a few reports of Chlainomonas red snow (in contrast to Cd. nivalis) exist, for which there are a number of reasons. One factor is the special ecological requirements. The preferred habitat of Chlainomonas sp. used in this study is waterlogged snow, which is mainly the case at ice covers of high mountain lakes and in snow bedded on plain glacier surfaces. Novis (2002b) found that growth of Cn. kolii was boosted after heavy rainfall during alpine summer, causing wetter snow conditions. Probably these spores are, despite possessing multiple cell wall layers compared with Cd. nivalis, more sensitive to both desiccation stress and higher temperatures, which would be the fate in non-permanent and rock-based snowfields after complete melt every season. In fact, at the Gossenkölle Lake Chlainomonas sp. ends up in water after complete melt, and thus protected from higher temperatures and desiccation; however, the complete life cycle including spring time with cell divisions and putative migration to the ice surface remains to be investigated. In summer, as the cells lose flagella after complete snow melt, they will most likely sink to the lake bed, or in the case of the samples from the Hallstätter glacier, remain on an icy surface. To the contrary, Cd. cf. nivalis seems to be adapted to temporary warmer conditions (Lukeš et al. (2014) consider it to be a ‘cryotolerant mesophile’), because cells were found intact on soil or rock surface after snow melt, whereas no populations from slushy sites were ever reported. Also Cn. rubra and Cn. kolii differ in their habitat from Chlainomonas sp., as they were found mostly associated with coniferous tree canopies, where snow was not slushy but shaded much of the day (Hoham 1974a,b).
A significant diagnostic detail valid for the LM description of Chlainomonas is a cell wall throughout ‘distant’ from the protoplast (Ettl 1983). However, Chlainomonas sp. from the Austrian Alps only possesses partially thickened walls practically at the anterior and posterior cell poles (representing a kind of papilla and pseudopapilla). The populations were morphologically identical neither to the descriptions of Cn. kolii (swarmers with collar-like papilla, spores with outer, ephemeral envelope consisting of mosaic plates) nor to Cn. rubra (cell wall of swarmers thickened all around, spores with striking spikes at the surface). However, similarities were found to other poorly described taxa known from red snow, namely Cr. bolyaiana (which, however, is much larger than Chlainomonas sp.) and Cd. sanguinea (about the same cell sizes and thickened cell walls at the poles; however, flagella 1.5–2 times cell length and spores with only two wall layers). The fact that cell shape and plastid morphology (respectively their arrangement) of Chloromonadalean algae can change drastically depending on the stage of the life cycle has already been shown for Cr. nivalis (Remias et al.2010), and it is most likely the same for Chlainomonas sp. For example, the numerous small plastids of spores can be rearranged from a peripheral to a central position close to the nucleus. Moreover, they probably originate from a larger single chloroplast in an earlier stage of the life cycle. In general, environmental factors and culture conditions may influence details like the presence or peculiarity of a pyrenoid or stigma, which were classically regarded as important diagnostic details. Summarizing, species determination using LM remains difficult, as cell shape and chloroplast morphology may change during development, and earlier descriptions like those summarized in Kol (1968) were performed on fixed material and without any life cycle studies. Consequently, older reports of Cr. bolyaiana and Cd. sanguinea, which look very similar to Chlainomonas ssp., have to be scrutinized. Still, a separation of Chlainomonas ssp. against Cd. nivalis field samples at the LM level should be possible, taking into account that the first species is usually larger (average cell lengths clearly more than 25 μm) and possess either ovoid stages with (partly) thickened cell walls with four flagella (groves) or spherical spores with multi-layered cell walls. Moreover, mature spores are not covered with cryoconite. Considering these details, a study of Kawecka (1981) probably did not describe spore formation of Cd. nivalis, but instead of a Chlainomonas living in the Polish High Tatra Mountains.
TEM was performed because large amounts of astaxanthin mask taxonomically relevant details at the LM level. It was shown that the cell walls of Chlainomonas sp. were not ‘detached’ from the cytoplasm as initially described for this genus and that is typical for the green alga Haematococcus pluvialis (Ettl 1983). Instead, the outermost wall layer is usually thickened and consists of less electron dense cell wall material. This may also be the situation for certain stages of Cn. kolii or Cn. rubra. The innermost cell wall layer of mature, multi-layered spores with its higher electron density may play a role in long-term survival. Novis (2002b) showed by TEM that Cn. kolii possesses small peripheral plastids (like the species from the Austrian Alps), and this phenomenon seems to be typical within the Chloromonas ‘snow clade’, as shown for other species, e.g. Cr. polyptera (Remias et al. 2013) or Cr. chenangoenis (Hoham et al.2006; Matsuzaki, Hara and Nozaki 2014). The small pyrenoid-free plastids may also be arranged inside the cell surrounding the nucleus. It remains open whether these small plastids are independent or in practice only portions of a single chloroplast. A physiological benefit of this strategy could be a better metabolite exchange with the cytoplasm at low temperatures due to a better membrane surface to volume ratio. The existence of many small cytoplasmic vacuoles with electron dense content that is partly crystallized was described earlier for Cd. cf. nivalis (Lütz-Meindl and Lütz 2006), but their physiological role remains unknown. They seem to be common in green algae, but their abundance in some snow algae is striking; e.g. in the recently described Cr. krienitzii from Japan (Matsuzaki et al.2015), they were visible by means of LM and TEM. A further characteristic detail of Chlainomonas ssp. and Chloromonas ssp. snow algae is the strictly centrally located nucleus, which is sheltered from excessive high alpine UV radiation by the surrounding astaxanthin. In contrast, Cd. cf. nivalis has no prominent central nucleus, but a single axial chloroplast with naked pyrenoid instead (Supplementary Fig. 8). Moreover, the cell walls are single-layered, typically possess attached cryoconite particles and are never partially thickened. Finally, spores of this species are generally smaller (around 20 μm in diameter). In summary, despite similarities of mature, spherical spores of Chlainomonas sp. and Cd. nivalis, significant differences in structural details exist.
Initially, snow algae of the genus Chlainomonas were part of Sphaerellopsis (Kol 1968), a diagnosis based on cells with only two flagella. However, already Hoham (1974a) described practically all cells as possessing four flagella grooves in the cell wall, regardless of individual swarmers (which may lose some or all of the flagella, e.g. when the cells are stressed during LM), and consequently transferred them to Chlainomonas. The quadriflagellate nature of Cn. rubra was later confirmed by Novis et al. (2008) by TEM. The same authors showed the first molecular tree of snow algae including Cn. rubra and Cn. kolii by using rbcL sequences. Surprisingly, they found that the phylogenetic position of Chlainomonas was within the genus Chloromonas s.l., with Cr. chenangoensis from snow in northwestern America (Hoham et al. 2006) as the closest known relative. So far, all known species of Chloromonas, which are closely related to Chlainomonas, inhabit snow fields, which points to a common ancestor of this cryoflora lineage. However, these Chloromonas spp. from snow have a quite different morphology. Spores in the Chloromonas spp. clade typically possess small discoid plastids. Chloromonas forms overall smaller spores of fusiform shape when compared with Chlainomonas, and the cell walls are covered with prominent protuberances like flanges and spikes. Spiked cell walls were reported for a stage of Cn. rubra (Hoham 1974a), but we never found such a cell in alpine samples. Finally, the secondary pigmentation of Chloromonas spores from snow is less developed; they never accumulate astaxanthin to such an extent as Chlainomonas so as to be confused with Cd. cf. nivalis. Neither molecular data nor strains are available for Cr. bolyaiana and Cd. sanguinea, which could, due to similar physiology and morphology, possibly be located close to the genus Chlainomonas. 18S rDNA sequences of Chlainomonas sp. from Gossenkölle Lake were already previously registered at GenBank (entries GU117574 and GU117575, sample code HW01, designated as Chloromonas sp.). Chlamydomonas cf. nivalis from the Austrian Alps (Tyrol) was included as GU117577 (sample code P27/DR1). Remias et al. (2010) demonstrated using 18S rDNA that the alpine Chlainomonas sp. was embedded within the ‘Chloromonas snow’ clade, and thus the results are in accordance to those from rbcL analysis (see above). In contrast Cd. cf. nivalis from the Tyrolean Alps was shown to group with different members of the Chlamydomonadaceae forming the ‘red snow’ clade. Most recently, in an 18S phylogeny of Matsuzaki et al. (2015, fig. S13), two strains related to Chloromonas species and isolated from arctic Svalbard were recognized as the closest relatives of alpine Chlainomonas sp. Future investigations on biodiversity of polar and alpine snow and ice ecosystems should include a new approach presented by Lutz et al. (2015): using high-throughput sequencing of the small subunit ribosomal RNA gene with environmental samples taken from glaciers in Iceland, they found an overwhelming diversity of bacteria, archaea, fungi and algae, and could also roughly measure the abundances of these organisms on snow and ice.
Photosynthesis of snow algae has to cope with different kinds of abiotic stresses. Quite different light conditions can occur. On the one hand, almost darkness prevails when cells are situated deep below the surface of snow at the onset of summer. On the other hand, exposed cells at unshaded snow surfaces can be subject to very high VIS und UV irradiation. Membrane flexibility and protein functionality have to adjust to these changing conditions. Lukeš et al. (2014) were the first to elucidate cellular adaptations of Cd. cf. nivalis: they described thylakoid membranes that were mainly composed of negatively charged phosphatidylglycerol. Also different from conventional green algae, the photosynthetic D1 protein had increased structural flexibility owing to amino acid changes. This in part explains why this species is successful in non-permanent snow fields, where cells are exposed to significantly higher temperatures when on bare soil or rock after complete melt. Whether such adaptations exist for Chlainomonas sp. is unknown. At low temperatures, this species has about the same maximum photosynthetic performance values of approximately 175 μmol O2 μg Chl−1 h−1 as other snow algae such as Cr. nivalis (Remias et al.2010) and Cd. cf. nivalis (Remias, Lütz-Meindl and Lütz 2005).
So far, astaxanthin has proven to be the secondary pigment turning Chlamydomonadalean snow algae red, and this has been shown here for the first time for Chlainomonas. The two hydroxyl groups of this carotenoid allow a simple chemical modification via esterification with any fatty acid. Chain length of fatty acids and the presence or number of double bonds allows the alga to optimize the polarity of astaxanthin in accordance with storage conditions in their lipid bodies, which is influenced by the nature of the triglycerides present. Řezanka et al. (2014) performed lipidomic profiling with the snow alga Cr. pichinchae using high resolution LC-MS, and were able to characterize the triglycerides. They found triglyceride species from 0 to 12 double bonds and they contained only C16 and C18 fatty acids with 0 to 4 double bonds, indicating a high presence of poly-unsaturated fatty acids, which are beneficial in cold environments as they enhance the membrane fluidity. In an earlier study, Řezanka et al. (2013) characterized a new variation on astaxanthin derivatives, namely esters with glucose and fatty acids. Although they analysed a field sample of Cd. cf. nivalis collected close to our Tyrolean study site, we could not detect such glycolized astaxanthin in our samples by LC-MS. Glycolized astaxanthin is recognized by a characteristic MSMS O-glycosidic fragmentation of the monosaccharide from the carotenoid.
Chlainomonas sp. from the Alps and a sample of Cn. kolii from New Zealand (and consequently maybe the whole genus) had exceptional variants of astaxanthin: the majority was stored as di- instead of monoesters and were generally more apolar than those of Cn. cf. nivalis. This goes along with high levels of α-tocopherol, a major antioxidant of the chloroplast, which can probably compensate damage from high light stress (excessive VIS) to exposed plastids anchored directly below the cell wall.
This study has shown that spores of snow algae can evolve quite different cellular strategies to adapt to the special snow environment. The photosynthesis of Chlainomonas sp. shows good performance under ambient light and temperature conditions, so that the cells can accumulate reserve metabolites like starch and astaxanthin esters for overwintering. Although the complete life cycle of this species is unknown, it seems to prefer summer snow with high water content in areas where cells are not subject to desiccation or high temperatures after snow melt. Consequently, we found this organism at locations where the flat snow fields had low water drain during melting. The psychrophilic nature of Chlainomonas sp. was not tested, but the fact that swarmers lose their flagella when exposed to temperatures above 1°C points to this direction. Similar observations on dropping flagella were made by Hoham (1974a). The high abundance of very apolar astaxanthin diesters differentiates Chlainomonas in its chemotaxonomic profile from the other two main groups of Chlamydomonadalean snow algae, the ‘Chloromonas-snow’ clade and the ‘Chlamydomonas-red snow’ clade.
Supplementary Material
Acknowledgments
We thank Siegfried Aigner, MSc. and Mag.biol. Hans Wastian, University of Innsbruck, for their assistance during sampling at Gossenkölle Lake and in the laboratory. Sabrina Obwegeser, MSc., University of Innsbruck is acknowledged for help in TEM sectioning and image generation. Furthermore, DR thanks Prof. Alexander Jäger at the Applied University Upper Austria in Wels for providing office facilities for preparation of this manuscript.
SUPPLEMENTARY DATA
FUNDING
This work was supported by the Czech Science Foundation grant to MP and the Austrian Science Fund (FWF) grant P to CL and grants P and to AH.
Conflict of interest. None declared.
REFERENCES
- Buchner O, Lütz C, Holzinger A. Design and construction of a new temperature controlled chamber for light- and confocal microscopy under monitored conditions: biological application for plant samples. J Microsc. 2007;225:183–91. doi: 10.1111/j.1365-2818.2007.01730.x. [DOI] [PubMed] [Google Scholar]
- Cepák V, Lukavský J. Cryoseston of the Pirin Mountains, Bulgaria. Acta Bot Croat. 2013;72:257–68. [Google Scholar]
- Duval B, Duval E, Hoham RW. Snow algae of the Sierra Nevada, Spain, and High Atlas mountains of Morocco. Internatl Microbiol. 1999;2:39–42. [PubMed] [Google Scholar]
- Ettl H. Süßwasserflora von Mitteleuropa. Band 9: Chloropyta I. Phytomonadina. Stuttgart, New York: Fischer; 1983. [Google Scholar]
- Hoham RW. New findings in the life history of the snow alga, Chlainomonas rubra (Stein et Brooke) comb. nov. (Chlorophyta, Volvocales) Syesis. 1974a;7:239–47. [Google Scholar]
- Hoham RW. Chlainomonas kolii (Hardy et Curl) comb. nov. (Chlorophyta, Volvocales), A revision of the snow alga, Trachelomonas kolii Hardy et Curl (Euglenophyta, Euglenales) J Phycol. 1974b;10:392–96. [Google Scholar]
- Hoham RW, Berman JD, Rogers HS, et al. Two new species of green snow algae from Upstate New York, Chloromonas chenangoensis sp. nov. and Chloromonas tughillensis sp. nov. (Volvocales, Chlorophyceae) and the effects of light on their life cycle development. Phycologia. 2006;45:319–30. [Google Scholar]
- Hoham RW, Duval B. Microbial ecology of snow and freshwater ice with emphasis on snow algae. In: Jones HG, Pomeroy JW, Walker DA, et al., editors. Snow Ecology. New York: Cambridge University Press; 2001. pp. 168–228. [Google Scholar]
- Hoham RW, Filbin RW, Frey FM, et al. The optimum pH of the green snow algae, Chloromonas tughillensis and Chloromonas chanangoensis, from Upstate New York. Arct Antarct Alp Res. 2007;39:65–73. [Google Scholar]
- Holzinger A, Roleda MY, Lütz C. The vegetative arctic green alga Zygnema is insensitive to experimental UV exposure. Micron. 2009;40:831–8. doi: 10.1016/j.micron.2009.06.008. [DOI] [PubMed] [Google Scholar]
- Kawecka B. Biology and ecology of snow algae. 2. Formation of aplanospores in Chlamyomonasnivalis (Bauer) Wille (Chlorophyta, Volvocales) Acta Hydrobiol. 1981;23:211–15. [Google Scholar]
- Kol E. Kryobiologie. Biologie und Limnologie des Schnees und Eises. I. Kryovegetation. In: Elster HJ, Ohle W, editors. Die Binnengewässer, Band XXIV. Stuttgart: Schweizerbart'sche Verlagsbuchhandlung; 1968. [Google Scholar]
- Kol E. Vom roten Schnee der Tiroler Alpen. Ann Hist Natur Mus Nat Hung. 1970;62:129–36. [Google Scholar]
- Komárek J, Nedbalová L. Green cryosestic algae. In: Seckbach J, editor. Cellular origin, life in extreme habitats and astrobiology, volume 11, Algae and cyanobacteria in extreme environments, part 4, Phototrophs in cold environments. Dordrecht: Springer; 2008. pp. 323–44. [Google Scholar]
- Kvíderová J. Research on cryosestic communities in Svalbard: the snow algae of temporary snowfields in Petuniabukta, Central Svalbard. Czech Polar Rep. 2012;2:8–19. [Google Scholar]
- Lemoine Y, Schoefs B. Secondary ketocarotenoid astaxanthin biosynthesis in algae: a multifunctional response to stress. Photosynth Res. 2010;106:155–77. doi: 10.1007/s11120-010-9583-3. [DOI] [PubMed] [Google Scholar]
- Leya T. Snow Algae: Adaptation Strategies to Survive on Snow and Ice. In: Seckbach J, Oren A, Stan-Lotter H, editors. Cellular origin, life in extreme habitats and astrobiology, volume 27, Polyextremophiles: Life under multiple forms of stress. Dordrecht: Springer; 2013. pp. 401–23. [Google Scholar]
- Li Y, Sommerfeld M, Chen F, et al. Consumption of oxygen by astaxanthin biosynthesis: A protective mechanism against oxidative stress in Haematococcus pluvialis (Chlorophyceae) J Plant Physiol. 2008;165:1783–97. doi: 10.1016/j.jplph.2007.12.007. [DOI] [PubMed] [Google Scholar]
- Lukeš M, Procházková L, Shmidt V, et al. Temperature dependence of photosynthesis and thylakoid lipid composition in the red snow alga Chlamydomonas cf. nivalis (Chlorophyceae) FEMS Microbiol Ecol. 2014;89:303–15. doi: 10.1111/1574-6941.12299. [DOI] [PubMed] [Google Scholar]
- Lutz S, Anesio AM, Edwards A, et al. Microbial diversity on Icelandic glaciers and ice caps. Front Microbiol. 2015;6:307. doi: 10.3389/fmicb.2015.00307. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Lütz-Meindl U, Lütz C. Analysis of element accumulation in cell wall attached intracellular particles of snow algae by EELS and ESI. Micron. 2006;37:452–8. doi: 10.1016/j.micron.2005.11.004. [DOI] [PubMed] [Google Scholar]
- Matsuzaki R, Hara Y, Nozaki H. A taxonomic study of snow Chloromonas species (Volvocales, Chlorophyceae) based on light and electron microscopy and molecular analysis of cultured material. Phycologia. 2014;53:293–304. [Google Scholar]
- Matsuzaki R, Kawai-Toyooka H, Hara Y, et al. Revisiting the taxonomic significance of aplanozygote morphologies of two cosmopolitan snow species of the genus Chloromonas (Volvocales, Chlorophyceae) Phycologia. 2015;54:491–502. [Google Scholar]
- Muramoto K, Nakada T, Shitara T, et al. Re-examination of the snow algal species Chloromonas miwae (Fukushima) Muramoto et al, comb. nov. (Volvocales, Chlorophyceae) from Japan, based on molecular phylogeny and cultured material. Eur J Phycol. 2010;45:27–37. [Google Scholar]
- Novis PM. New records of snow algae for New Zealand, from Mt Philistine, Arthur's Pass National Park. New Zeal J Bot. 2002a;40:297–312. [Google Scholar]
- Novis PM. Ecology of the snow alga Chlainomonas kolii (Chlamydomonadales, Chlorophya) in New Zealand. Phycologia. 2002b;41:280–92. [Google Scholar]
- Novis PM, Hoham RW, Beer T, et al. Two snow species of the quadriflagellate green alga Chlainomonas (Chlorophyta, Volvocales): Ultrastructure and phylogenetic position within the Chloromonas clade. J Phycol. 2008;44:1001–12. doi: 10.1111/j.1529-8817.2008.00545.x. [DOI] [PubMed] [Google Scholar]
- Nylander JAA. MrModeltest 2.3. Distributed by the author. Evolutionary Biology Centre, Uppsala University; Uppsala, Sweden: 2004. [Google Scholar]
- Raymond JA. The ice-binding proteins of a snow alga, Chloromonas brevispina: probable acquisition by horizontal gene transfer. Extremophiles. 2014;18:987–94. doi: 10.1007/s00792-014-0668-3. [DOI] [PubMed] [Google Scholar]
- Remias D. Cell structure and physiology of alpine snow and ice algae. In: Lütz C, editor. Plants in alpine regions. Cell physiology of adaption and survival strategies. Wien: Springer; 2012. pp. 175–86. [Google Scholar]
- Remias D, Karsten U, Lütz C, et al. Physiological and morphological processes in the Alpine snow alga Chloromonas nivalis (Chlorophyceae) during cyst formation. Protoplasma. 2010;243:73–86. doi: 10.1007/s00709-010-0123-y. [DOI] [PubMed] [Google Scholar]
- Remias D, Lütz-Meindl U, Lütz C. Photosynthesis, pigments and ultrastructure of the alpine snow alga Chlamydomonas nivalis. Eur J Phycol. 2005;40:259–68. [Google Scholar]
- Remias D, Lütz C. Characterisation of esterified secondary carotenoids and of their isomers in green algae: a HPLC approach. Algological Stud. 2007;124:85–94. [Google Scholar]
- Remias D, Wastian H, Lütz C, et al. Insights into the biology and phylogeny of Chloromonas polyptera (Chlorophyta), an alga causing orange snow in Maritime Antarctica. Antarct Sci. 2013;25:648–56. [Google Scholar]
- Řezanka T, Nedbalová L, Kolouchová I, et al. LC–MS/APCI identification of glucoside esters and diesters of astaxanthin from the snow alga Chlamydomonas nivalis including their optical stereoisomers. Phytochemistry. 2013;88:34–42. doi: 10.1016/j.phytochem.2013.01.003. [DOI] [PubMed] [Google Scholar]
- Řezanka T, Nedbalová L, Procházková L, et al. Lipidomic profiling of snow algae by ESI-MS and silver-LC/APCI-MS. Phytochemistry. 2014;100:34–42. doi: 10.1016/j.phytochem.2014.01.017. [DOI] [PubMed] [Google Scholar]
- Ronquist F, Huelsenbeck JP. MrBayes 3: Bayesian phylogenetic inference under mixed models. Bioinformatics. 2003;19:1572–74. doi: 10.1093/bioinformatics/btg180. [DOI] [PubMed] [Google Scholar]
- Spijkerman E, Wacker A, Weithoff G, et al. Elemental and fatty acid composition of snow algae. Front Microbiol. 2012;3:380. doi: 10.3389/fmicb.2012.00380. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Stibal M, Elster J, Šabacká M, et al. Seasonal and diel changes in photosynthetic activity of the snow alga Chlamydomonas nivalis (Chlorophyceae) from Svalbard determined by pulse amplitude modulation fluorometry. FEMS Microbiol Ecol. 2007;59:265–73. doi: 10.1111/j.1574-6941.2006.00264.x. [DOI] [PubMed] [Google Scholar]
- Swofford DL. PAUP*4.0b10. Phylogenetic Analysis Using Parsimony (*and Other Methods) Sunderland: Sinauer Associates; 2002. [Google Scholar]
- Uetake J, Tanaka S, Hara K, et al. Novel biogenic aggregation of moss gemmae on a disappearing African glacier. PLoS One. 2014;9:e112510. doi: 10.1371/journal.pone.0112510. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Varshney P, Mikulic P, Vonshak A, et al. Extremophilic micro-algae and their potential contribution in biotechnology. Bioresource Technol. 2015;184:363–72. doi: 10.1016/j.biortech.2014.11.040. [DOI] [PubMed] [Google Scholar]
- Verbruggen H, Ashworth M, LoDuca ST, et al. A multi-locus time-calibrated phylogeny of the siphonous green algae. Mol Phylogenet Evol. 2009;50:642–53. doi: 10.1016/j.ympev.2008.12.018. [DOI] [PubMed] [Google Scholar]
- Zwickl DJ. Ph.D. Thesis. University of Texas at Austin; 2006. Genetic algorithm approaches for the phylogenetic analysis of large biological sequence datasets under the maximum likelihood criterion. [Google Scholar]
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