INTRODUCTION
Although in most environments strontium (Sr) and barium (Ba) are present in trace amounts, they can be accumulated in substantial quantities by some organisms (
1,
2). Depending on their environmental availability, these elements are mostly taken up nonselectively together with Ca
2+ (
3,
4). The soluble form of Ba
2+ is typically toxic for animals (e.g., use of rodenticides) due to its capacity to block K
+ channels, while insoluble BaSO
4 acts as a common contrast agent in medical radio-imaging (
5). In contrast, soluble Sr
2+ is not harmful, with the exception of the radioactive isotope
90Sr
2+ occurring as a nuclear contaminant that accumulates in marine biota and sediments (
6). Indeed, in some algae, Sr
2+ can almost fully replace Ca
2+ without any discernible deleterious effects (
7). In humans, Sr
2+ treatment of osteoporosis is used to prevent fractures (
8). Moreover, predictions concerning climate change stress the increased relevance of higher environmental mobilization of Sr
2+ and Ba
2+ due to enhanced solubility upon marine acidification (
9). Apart from chemical precipitation treatments of radioactive
90Sr
2+ and toxic Ba
2+, there have been new attempts for bioremediation using cyanobacteria, algae, and fungi (
1,
2,
6,
10).
In marine environments, microorganisms accumulate more Sr
2+ than Ba
2+, possibly due to higher solubility and availability, i.e., the concentration of Sr
2+ is around 88 μM compared to 40 to 150 nM Ba
2+ (
11,
12). In protists, Sr
2+ is mostly present in the form of celestite (also referred to as celestine; SrSO
4) and strontianite (SrCO
3), while Ba
2+ forms barite (BaSO
4) or witherite (BaCO
3) (
13,
14). Moreover, Ba
2+ and Sr
2+ commonly substitute for each other in various ratios to form strontiobarite and baritocelestite (Ba,Sr)SO
4 (
15). Celestite with traces of Ba
2+ is well known for forming the complex skeletons of acanthareans (
16). Intracellular barite crystals form statoliths of some freshwater charophyte algae and statocysts of marine ciliates, in which they likely play a role in graviperception (
13,
17,
18). Haptophytes and foraminiferans form intracellular barite crystals with trace amounts of Sr
2+ (
19,
20), while strontianite and witherite occur in microalga
Tetraselmis (
21) and coccolithophorids (
14,
22). The exact role of these crystalline inclusions remains unknown.
Marine Ba
2+ and Sr
2+ are frequently correlated with particulate organic carbon in the water column and sediments on the sea floor, indicating that microorganisms are capable of accumulating these elements (
11,
23,
24), yet the celestite-rich skeletons of acanthareans dissolve during sedimentation (
25). Ba
2+ and Sr
2+ carbonates and phosphates known from coccolithophorids and bacteria, respectively, contribute to the cycling of these elements with possible conversion to sulfates in the process of diagenesis (
10,
14,
22,
26). In addition, barite, strontiobarite and celestite crystals are frequently found associated with fecal pellets, which contribute to the sedimentation of particulate Ba
2+ and Sr
2+ to the sea floor (
24). However, until now, abundant planktonic organisms capable of selective intracellular accumulation of both Ba
2+ and Sr
2+ sulfates have not been identified (
12,
13). The substantial work of Dehairs et al. (
24) presents a series of evidence pointing to the biogenic origin of barite/celestite microcrystals, including micrographs of environmental microcrystals covered by desiccated cellular organic matter. Variable composition of marine suspended microcrystalline sulfates are commonly ascribed to barite with minor admixtures of Sr
2+ alongside 10 to 30% of crystals dominated by celestite (
24). Such variability is most plausibly explained by active biological catalysis (
24). Despite the well-documented evidence-based predictions of the biogenic origins of barite and celestite minerals in the oceans (
24,
27), the lack of organisms responsible for their production led to the gradual focus on microenvironment-mediated precipitation, stepping away from consideration of their biological origin (
28).
Here, we show that diplonemids (Diplonemea, Euglenozoa), a group of biflagellated heterotrophic protists (
29–31), are capable of massive intracellular accumulation of Sr
2+ and Ba
2+. Specifically, three cultivable diplonemids accumulate celestite and sometimes barite crystals in intracellular concentrations of Sr
2+ much greater than in other organisms (
10,
19). In the world’s oceans, diplonemids have only recently been recognized as omnipresent and one of the most diverse and abundant groups of microeukaryotes (comparable to microalgae), with a prevalence within the mesopelagic protist community (
32–34). Although relatively rare, they are present in freshwater bodies as well (
35). We analyzed their crystalline inclusions by a range of complementary approaches and discuss here their possible biological functions and role in biogeochemical cycles.
DISCUSSION
The most studied biominerals in protists are extracellular calcite scales of haptophytes and silicate frustules of diatoms, while studies on intracellular mineral crystals are far less common (
38). After more than a century since the skeletons of marine acanthareans and freshwater streptophytes were found to contain celestite (
16) and barite (
39), respectively, we have identified potent accumulators of Ba
2+ and Sr
2+ in an unexpected group of eukaryotes, the diplonemids.
The heterotrophic diplonemids are widespread in the oceans and, as recently described, in astonishing abundance and diversity (
31,
33). Despite their abundance and extreme diversity, diplonemid flagellates remain a poorly known group of protists (
34) that are abundant from the surface to the deep sea, with a wide peak in the mesopelagic zone (
32,
33,
40,
41). The high capacity of intracellular Sr
2+ and Ba
2+ accumulation in some diplonemids outperforms that of any other reported organisms (
10,
13,
21,
42–44). Indeed, while the intracellular concentration of Sr
2+ in the most efficient accumulators known thus far (yeasts, desmids, and cyanobacteria) reaches a maximum of 220 mg·g
−1 per dry weight (
1,
10,
43),
N. karyoxenos contains as much as 340 mg·g
−1 Sr
2+ together with 120 mg·g
−1 Ba
2+, which in the form of sulfate represents 90% of the cellular dry mass, pointing to the unique Sr
2+ and Ba
2+ accumulation capacity of this diplonemid, while both
Lacrimia species are slightly less potent in this respect (
Table 1).
Interestingly, when both trace elements are provided in equimolar concentrations, diplonemids form pure celestite and barite and/or mixed forms of (Ba,Sr)SO
4, apparently not discriminating one element over the other. Hence, we explain the higher content of Sr
2+ over Ba
2+ inside the crystals by the higher availability of the former element in seawater. Although the mechanisms behind intracellular accumulation of Sr
2+ and Ba
2+ are largely unknown, it has been suggested that mineral crystals typically occur in membrane-bounded compartments or vacuoles, in which they are formed from supersaturated solutions via precisely regulated nucleation (
13). The Sr
2+ uptake and transportation within eukaryotic cells have been shown to occur via commonly present transporters of divalent cations, i.e., the Ca
2+ uniporter and H
+/Ca
2+ antiporter (
45,
46). The diplonemid nuclear genome is not yet available, but these transporters have been documented in the related kinetoplastid
Trypanosoma brucei (
47). Although the reported affinity to Ca
2+ and Sr
2+ is usually comparable (
45,
46), some organisms including diplonemids clearly favor Ba
2+ and Sr
2+ over Ca
2+ (
10). When such vacuoles contain sulfate solutions, they may function as a “sulfate trap” for those cations that precipitate easily in the presence of sulfates (
2). At the same time, we did not observe CaSO
4 or any of its forms (gypsum, bassanite, anhydride, etc.), even though the concentration of Ca
2+ in the cultivation medium or in the environment is several orders of magnitude higher than that of Sr
2+ and Ba
2+.
Densities of celestite and barite of 3.9 g·cm
−3 and 4.5 g·cm
−3, respectively, have been repeatedly reported as statoliths in ciliates or charophytic algae (
13,
17,
18). In comparison to the seawater density of 1.03 g·cm
−3 and typical cell density range between 0.985 and 1.156 g·cm
−3, the heavy crystals may help maintain appropriate buoyancy by counterbalancing light lipid droplets (0.86 g·cm
−3) (
37,
48). Indeed, the impact of celestite crystals is substantial, since they may increase the overall density of
Lacrimia sp. YPF1808 and
N. karyoxenos by up to 9% and 27%, respectively (
Table S2). According to Stokes’ law for small particles of low Reynolds numbers, the barite/celestite ballasting can significantly increase the sedimentary velocity for up to 50 to 200 m per month or 0.5 to 2 km per year (
Table S2). Hence, while the function of biomineralization in diplonemids remains unknown, we speculate that they may benefit from gravitropic sensing, which would allow directed movement and/or enable passive sedimentation. Another intriguing impact of barite and celestite is associated with their propensity to strong absorption of UV and blue light (
49). Hence, in surface waters, these minerals may contribute to UV protection. It is reasonable to assume that by forming celestite, protists adjust their inner osmolarity, the principle analogical to the formation of other cell inclusions, such as oxalate, calcite, or polyphosphate, that are either dissolved and osmotically active or crystallized or polymerized and osmotically inactive inside a vacuole (
13,
50).
Celestite-forming acanthareans are considered key players in the upper 400 m of the ocean, yet do not contribute to the sedimentary rock formation, as their skeletons dissolve upon decay of their cells (
25). Coccolithophorids and bacteria produce carbonates (
44) and/or phosphates (
26) of Ba
2+/Sr
2+, which can also be converted to sulfates either on the bacterial extracellular polymeric substances or in the microenvironment of decaying matter of marine snow aggregates in the process of diagenesis (
26). In the chemical continuum between pure barite and celestite, the latter represents 10 to 30% (
24), gradually decreasing, depending on the depth (
11,
12). The majority of biogenic particulate barite and celestite is recycled by simple dissolution (
25), microbial loop (
26), or resuspension of sediments (
24). However, the overall influx into the system is balanced by sedimentary deposition (
9,
24), which might have a biological driver. Seminal work of Dehairs et al. (
24) scrutinized all potential sources of particulate barite and celestite, and they did not find experimental support for either Ba
2+ incorporation in siliceous plankton or precipitations on decaying organic matter in sulfate-enriched microenvironments. Hence, they ultimately favored the biogenic origin of particulate barite/celestite being hypothetically formed by microorganisms inhabiting the high-productivity mesopelagic zone (
24) only to remain unknown since then. These predictions nicely correlate with our measurements in diplonemids, indicating that micron-sized celestite and sometimes barite crystals of variable Ba-Sr ratios (
Fig. 2 to 5) are scattered throughout the water column of the world’s oceans, with the highest prevalence in the mesopelagic zone (
32). Moreover, particulate barite/celestite is often found in fecal pellets and aggregates of marine snow, and finally, in the sediments (
24,
27,
32). By providing celestite-containing diplonemids to filter-feeding copepods, we found undigested celestite in their fecal pellets (
Fig. 6), the main transport system of micrometric biominerals into the sediments, although the majority is recycled (
24). Thus, diplonemids may be involved in Ba
2+/Sr
2+ cycling and/or in sedimentary deposition of celestite or barite. Since these protists likely emerged during the Neoproterozoic era (590 to 900 million years ago [MYA]), overlapping with the Ediacaran period (
51), their impact on biogenic marine sediments may cover several geological eras. The coccolithophores appeared around the same time as diplonemids, yet the onset of carbonate biomineralization has been timed to ~200 MYA (
52).
As another ecological addition to the big picture of Ba
2+/Sr
2+ cycling, diplonemids have been shown to ingest bacteria as one of their sources of nutrition (
30); if bacteria were loaded with Ba
2+/Sr
2+ in the form of (poly)phosphates, as reported elsewhere (
26), diplonemids may further transform it into barite upon digestion. Additionally, diplonemids are likely to feed on the organic matter of marine snow providing preconcentrated Ba
2+, in which case they may accumulate more Ba
2+ than Sr
2+. In principle, we experimentally supported such a scenario upon doping the cells with equimolar Ba
2+ and Sr
2+ concentrations (
Fig. 5). Finally, we do not exclude that some species of diplonemids to be described in future would prefer Ba
2+ over Sr
2+ or that there are other as-yet-unknown microbial bioaccumulators of these trace elements.
Based on the ability of some diplonemids to store massive amounts of celestite and to lesser extent barite, we speculate that more as-yet-unknown diplonemid species may qualify as impactful players of Ba2+/Sr2+ flow through the food web, eventually influencing the sedimentary records.
ACKNOWLEDGMENTS
This work was supported by ERD Funds projects OPVVV 16_019/0000759 (to J.L.), 15_003/0000336 KOROLID (to H.K. and B.S.N.H.), and 16_013/0001775 (to D.T., J.T., and M.V.); ERC CZ LL1601 (to J.L.); Czech Bioimaging grant LM2018129 (to J.P., D.T., J.T., and M.V.); Czech Science Foundation grant 21-26115S (to J.P. and P.M.); Czech Academy of Sciences travel grant VAJVA-19-68 (to D.T.); and the Gordon and Betty Moore Foundation GBMF9354 (to J.L.). We acknowledge CzechNanoLab Research Infrastructure and the grant support LM2018110 (to M.K.) and the Light Microscopy Core Facility and the grant support 18_046/0016045 (to J.P.) for help with holographic microscopy.
D.T., J.P., and J.L. designed the research; D.T., J.P., J.T., M.V., S.N.H.B., R.S., and M.K. performed the research; J.P., D.T., J.T., M.V., H.K., P.M., and J.L. analyzed the data; J.T., M.V., H.K., P.M., R.S., and M.K. contributed reagents and analytic tools; J.P., D.T., and J.L. wrote the paper.
We declare no conflict of interest.