In the present study, we provide a comprehensive structural and ultrastructural description, EELS element analysis, and a qualitative and quantitative determination of the soluble LMWCs of T. transpacifica. These are the first results on properties of the recently described genus Tsunamia (West et al. 2016). These data will help to understand the rather unique ecology of this alga. Tsunamia transpacifica has the astonishing ability to thrive for a long time on the ocean’s surface and is able to survive when drifted ashore. Under these differing conditions, particularly solar radiation and irregular dehydration are two of the main stressors which the alga can cope with.
Our TEM data confirmed the light microscopical observations on the parietal chloroplasts without pyrenoids (West et al. 2016). The chloroplast lobes showed parallel-arranged thylakoid membranes, typical for red algae and with a similar appearance as in other members of the Stylonematophyceae (e.g., West et al. 2005, 2007). In contrast, the large chloroplast of Rhodaphanes brevistipitata showed a central pyrenoid (West et al. 2007). The chloroplast of Rhodaphanes did not show an encircling thylakoid which is in contrast to T. transpacifica where up to three encircling thylakoids were observed. Distinct phycobilisomes were difficult to spot in T. transpacifica after the HPF/FS protocols applied in this study. The contents of the plastids and spaces between the thylakoid membranes appeared electron dense, suggesting a good structural preservation. The cytoplasm of several cells of T. transpacifica contained large amounts of starch grains, accounting for high physiological activity synthesizing this storage compound as was also observed in other red algae like Batrachospermum turfosum (Aigner et al. 2017). It was surprising to get absolutely non-satisfying results after chemical fixation for preserving the ultrastructure of T. transpacifica, a technique that is well established and has provided reasonable results in several other red algae such as Palmaria palmata and Odonthalia dentata (Holzinger et al. 2004) and the freshwater red alga B. turfosum (Aigner et al. 2017) as some examples from our laboratory.
Initially, we performed DNA staining to visualize the cell’s nuclei. However, we saw that common DNA dyes, like Hoechst 33,342 (Fig. 1e, g) and SYBR Green (not shown), only stained plastidal DNA in T. transpacifica, but were excluded from the nucleus. We conclude that the nuclear envelope of T. transpacifica is not permanent for these dyes, despite different fixations and staining procedures have been employed that were successful in nuclear staining in Viator vitreocola (Hansen et al. 2019). At the present stage, we cannot give an explanation which components of the nuclear envelope are responsible for this exclusion, so further examination is needed.
Ultrastructure and properties of Tsunamia cell walls
The cells were surrounded by a thick, multilayered cell wall, up to 2 µm in diameter. Currently, we do not have detailed information on the biochemical composition of the cell wall and the extracellular matrix of T. transpacifica, but the respective analysis is on the way, and there are some indications that xyloglucans and arabinogalactan proteins could play an important role in the adhesion mechanisms (Veenhof and West 2018; Zoe Popper, Galway, personal communication). In addition, Chroodactylon ornatum, also a member of the Stylonematophyceae, has been described to contain sulfated galactans in their mucilaginous sheath (Cabrera et al. 2014). Most importantly, we provide here ultrastructural evidence that in T. transpacifica, several cells covered by distinct cell walls are embedded together in an extracellular matrix composed of extracellular polymeric substances (EPS), which appears denser towards the outside. These EPS may contain organic electron-dense particles or bacteria, and their occurrence is likely the reason why these cells have the ability to stick tightly to the plastic surfaces. A possible factor for the difficulties in fixation of this alga is likely the chemical composition of the cell walls and the EPS, which possibly prevent proper resin infiltration.
Electron-dense bodies likely represent chloroplast-derived structures
Prominent electron-dense bodies similar in size and appearance as chloroplasts but lacking their internal structure with thylakoids were found in T. transpacifica samples. These bodies were found in different size classes, most of them in the dimensions of a chloroplast (i.e., ~ 1–2 µm), but also smaller “rounded bodies,” which may have a different content. The interpretation of these structures is difficult, but at least the smaller ones could resemble the brownish granules detected by LM in a previous study (West et al. (2016), Fig. 1c, cell indicated with arrow).
While electron-dense bodies are frequently observed in brown algae, where they are described as physodes, for example, in the Arctic kelp Saccharina latissima (Holzinger et al. 2011), they are uncommon for red algae. Physodes are described as phlorotannin-containing vesicles and due to their spectral properties have well characterized protective functions against enhanced UV radiation (Shibata et al. 2004; Schoenwaelder 2002). However, it seemed unlikely that the electron-dense bodies in T. transpacifica have a similar content, and the records of phlorotannins in red algae are sparse.
Thus, we speculate that the electron-dense bodies are possibly chloroplast-derived and could resemble degradation products of the chloroplasts. This is supported by the size of these structures and their inhomogeneous contents. An interesting observation supporting this interpretation of the electron-dense bodies was made by Coelho et al. (1998) who investigated a marine snail that produced its purple defensive ink exclusively from the accessory photosynthetic pigment phycoerythrin, deriving from the red seaweeds these snails are consuming. Interestingly, these authors showed TEM micrographs of “electron-dense granules” in the digestive vacuoles of red algae-fed snails which remarkably resemble our observations of the electron-dense bodies. By means of immunolabelling, Coelho et al. (1998) provided evidence for the chemical nature of the osmiophilic material and were able to detect P, S, Cl, Cr, and Fe by means of X-ray spectrum analysis (EDS) within a rhodoplast digestive vacuole. These data are partially similar to our observations; however, we did not detect Cr, but Co instead. Moreover, it should be tested if the electron-dense bodies in T. transpacifica also derived from phycoerythrin degradation.
Phosphorus, cobalt, and iron are accumulated in electron-dense bodies of Tsunamia
Phosphorus is ubiquitously present in the marine water column due to biological activity, weathering of P-rich sediments, and coastal upwelling, as well as from anthropogenic inputs into coastal waters such as fertilizers (White and Dyhrman 2013). The situation might be different in the open ocean where T. transpacifica was drifting and P can be temporarily limiting in certain situations in the North Pacific (Conkright et al. 2000). Some red algae show a bi-phasic kinetics of P uptake with saturable kinetics at low concentrations and a linear uptake at high external P concentrations (Friedlander and Dawes 1985). In the red alga Palmaria palmata, P uptake was bi-phasic without saturation (Martinez and Rico 2004). The biological function of P accumulation in red algae is likely the storage of this nutrient for periods of P deficiency.
A “luxury” consumption of P in freshwater benthic algae has been described by Stevenson and Stoermer (1982). These authors stated that the abilities of different algae to absorb nutrients are important ecological traits for the interspecific competition, and they found the second highest accumulation of polyphosphate bodies in Asterocytis smaragdina (Bangiophyceae) when compared to algal epiphytes from other phylogenetic positions like Cocconeis pediculus (diatom), which exhibited the highest density of polyphosphate bodies (Stevenson and Stoermer 1982). The number and size of polyphosphate granules is a suitable cellular indicator for eutrophication, i.e. the amount of phosphate in surface waters (Eixler et al. 2006). These authors also performed different localization experiments in the cyanobacterium Synechocystis sp. and the green alga Chlorella vulgaris (Eixler et al. 2005). By means of electron spectroscopic imaging, they found the most electron-dense (dark) areas that were corresponding to the highest P concentrations (Eixler et al. 2005). Also, Ota et al. (2016) draw a clear relationship between polyphosphate bodies and the accumulation of electron-dense bodies in the green alga Parachlorella kessleri. In this species, sulfur-depleted conditions led to the accumulation of P, but the respective signal was only detected in electron-dense bodies by energy dispersive X-ray analysis (Ota et al. 2016). In T. transpacifica, an even more sophisticated method, EELS, was employed that clearly detected accumulation of P in electron-dense bodies. When viewing electron-dense bodies from a structural perspective, also similarities to polyphosphate bodies described in cyanobacteria of the early TEM literature (Jensen 1968; Jensen and Sicko 1974; Jensen et al. 1977).
An accumulation of Co has been observed in electron-dense bodies as well as in intact chloroplasts in Tsunamia (Fig. 4d, f), further supporting the speculation that electron-dense bodies are derived from chloroplasts. Cobalt (II) is usually highly toxic to organisms and in particular to the photosynthetic apparatus of some algae and may be deposited there (e.g., El-Sheekh et al. 2003; Macfie et al. 1994). Thus, sequestering this heavy metal is likely beneficial for the alga and might in turn lead to changed and degraded chloroplasts. In contrast, an accumulation of Fe was only found in small rounded electron-dense bodies of Tsunamia grown in Melbourne.
However, at this stage, we can only speculate on the interpretation of these data. An effect of the cultivation medium is likely to be excluded as both media have basically the same chemical composition. However, light and temperature conditions for cultivation in the laboratories were different (5- to 10-µmol photons m−2 s−1 at 18–22 °C versus 6- to 30-µmol photons m−2 s−1 at 14–20 °C), and particularly the higher photosynthetic active radiation (PAR) in combination with lower temperatures could explain the contrasting results of Tsunamia grown at the University of Melbourne and at the University of Innsbruck.
Red algae such as Hypnea valentiae have the capacity to remove Co (II) ions from aqueous solutions in a pH- and temperature-dependent manner (Vafajoo et al. 2017). The biosorption of Co (II) has been tested in various seaweeds including the red algae Gracilaria edulis where the in situ uptake capacities were in the medium range and highest at pH 4–5 (Vijayaraghavana et al. 2005). Bioaccumulation of Co has been described in several red algae including Porphyra tenera, Palmaria palmata, Chondrus crispus (Kuyucak and Volesky 1988a), and Corallina elongata (Benabdallah et al. 2018). The earlier authors described the mechanism of biosorption of Co (II) in the brown alga Ascophyllum nodosum by physical binding to cell walls (Kuyucak and Volesky 1988b). The biosorption mechanisms involved are predominately ion exchange by the sulfated alginates of the cell wall which play a crucial role in the Co (II) binding whereas transport/passage of Co (II) across the cell wall/plasmalemma into the cell occurs to a lower rate and possibly in a temperature-dependent manner. However, these studies do not give any information on where the sequestered metal ions are localized. Indications for Fe (II) bioavailability in red algae are evident from the literature, and concentrations of 196 mg 100 g−1 dry weight were found in Gracilariopsis (Garcia-Casal et al. 2008) and Porphyra (Garcia-Casal et al. 2009). The accumulation of Fe (II) in small round electron-dense bodies in cells grown at the University of Melbourne might reflect the biosorption capacities of T. transpacifica for this trace element, whereas EELS of cells grown at the University of Innsbruck did not allow to detect Fe (II). Usually, Fe (II) is poorly soluble in sea water, and hence often limiting to phytoplankton growth as it is necessary for photosynthesis.
Putative function of soluble LMWCs as protective compounds
Marine algae that are frequently exposed to salinity changes or desiccation typically follow the metabolic strategy to keep the sodium and chloride concentrations in the cytoplasm as low as possible, because both ions negatively affect protein and organelle function, membrane integrity, and structural macromolecules (Kirst 1990). Instead and to generate sufficient osmotic pressure, organic osmolytes are synthesized and accumulated in the cytoplasm, which are compatible to all metabolic functions (Eggert and Karsten 2010). In red algae, numerous LMWCs have been identified (Eggert and Karsten 2010), and these often represent the main photosynthetic product. Most orders of red algae synthesize the heteroside floridoside, while most members of the Ceramiales generally form and accumulate instead of floridoside, the chemically related digeneaside (Kremer 1978). Most interesting is the observation that in some Ceramiales such as in the mangrove-associated genera Bostrychia and Stictosiphonia as well as in some early diverging red algal lineages (e.g., Stylonematophyceae), the polyol sorbitol can be found (Eggert and Karsten 2010), which is otherwise uncommon for red algae. With the exception of digeneaside that plays no more than a minor role in osmotic acclimation of red algae (Eggert and Karsten 2010), floridoside and sorbitol act as organic osmolytes. Our data clearly indicate that digeneaside, floridoside, and sorbitol occur together in Tsunamia, but in different concentrations of 14.4, 70.5, and 121.6 µmol g−1 DW, respectively. These amounts already reflect their osmotic relevance, i.e. the higher the content the more the compound plays a significant role in osmotic acclimation (Kirst 1990). Since these organic compounds can be accumulated and tolerated at high intracellular concentrations, and permit the generation of low water potentials without incurring metabolic damage (Yancey 2005), the term “compatible solute” was introduced by Brown and Simpson (1972). In general, the intracellular concentrations of floridoside and sorbitol are actively adjusted by photosynthesis-driven de novo biosynthesis or by remobilization of storage products and are directly proportional to external salinity or desiccation (Kirst 1990). In addition, the function of sorbitol and floridoside as compatible solutes was experimentally proven on enzyme extracts that originated from various mangrove red algae (Karsten et al. 1996). The in vitro activity of two key enzymes was strongly inhibited with increasing NaCl concentrations, while equimolar concentrations of sorbitol or floridoside did not inhibit enzyme function, with sorbitol exhibiting even a slightly stimulating effect (Karsten et al. 1996). In contrast, a comprehensive biochemical study on digeneaside in a euryhaline red alga experimentally proved that the content of this heteroside always remained low and unaffected by salinity (Karsten et al. 1994), and hence is not involved in osmotic acclimation.
So far, the joint occurrence of floridoside and digeneaside in red algae was reported in Stylonema alsidii and Stylonema cornu-cervi (Karsten et al. 1999) and later in Rhodochaete parvula (Karsten et al. 2003), which are all considered taxa of early diverging lineages (Stylonematophyceae, Compsopogonophyceae). In addition, in S. alsidii and S. cornu-cervi, sorbitol occurred as third LMWC (Karsten et al. 1999). However, also in some lineages of the Porphyridiophyceae (Erythrolobus coxiae, E. madagascariensis, and Timspurckia multipyrenoidosa), the co-occurrence of these two heterosides was reported, while members of Porphyridium and Flintiella possess only floridoside (Yang et al. 2010). The distribution patterns of these LMWCs in early diverging lineages of the Rhodophyta are of chemotaxonomic value (Karsten et al. 1999).