ABSTRACT

Barium and strontium are often used as proxies of marine productivity in palaeoceanographic reconstructions of global climate. However, long-searched biological drivers for such correlations remain unknown. Here, we report that taxa within one of the most abundant groups of marine planktonic protists, diplonemids (Euglenozoa), are potent accumulators of intracellular barite (BaSO4), celestite (SrSO4), and strontiobarite (Ba,Sr)SO4. In culture, Namystinia karyoxenos accumulates Ba2+ and Sr2+ 42,000 and 10,000 times higher than the surrounding medium, forming barite and celestite representing 90% of the dry weight, the greatest concentration in biomass known to date. As heterotrophs, diplonemids are not restricted to the photic zone, and they are widespread in the oceans in astonishing abundance and diversity, as their distribution correlates with environmental particulate barite and celestite, prevailing in the mesopelagic zone. We found diplonemid predators, the filter-feeding zooplankton that produces fecal pellets containing the undigested celestite from diplonemids, facilitating its deposition on the seafloor. To the best of our knowledge, evidence for diplonemid biomineralization presents the strongest explanation for the occurrence of particulate barite and celestite in the marine environment. Both structures of the crystals and their variable chemical compositions found in diplonemids fit the properties of environmentally sampled particulate barite and celestite. Finally, we propose that diplonemids, which emerged during the Neoproterozoic era, qualify as impactful players in Ba2+/Sr2+ cycling in the ocean that has possibly contributed to sedimentary rock formation over long geological periods.
IMPORTANCE We have identified that diplonemids, an abundant group of marine planktonic protists, accumulate conspicuous amounts of Sr2+ and Ba2+ in the form of intracellular barite and celestite crystals, in concentrations that greatly exceed those of the most efficient Ba/Sr-accumulating organisms known to date. We propose that diplonemids are potential players in Ba2+/Sr2+ cycling in the ocean and have possibly contributed to sedimentary rock formation over long geological periods. These organisms emerged during the Neoproterozoic era (590 to 900 million years ago), prior to known coccolithophore carbonate biomineralization (~200 million years ago). Based on reported data, the distribution of diplonemids in the oceans is correlated with the occurrence of particulate barite and celestite. Finally, diplonemids may provide new insights into the long-questioned biogenic origin of particulate barite and celestite and bring more understanding of the observed spatial-temporal correlation of the minerals with marine productivity used in reconstructions of past global climate.

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 Ca2+ (3, 4). The soluble form of Ba2+ is typically toxic for animals (e.g., use of rodenticides) due to its capacity to block K+ channels, while insoluble BaSO4 acts as a common contrast agent in medical radio-imaging (5). In contrast, soluble Sr2+ is not harmful, with the exception of the radioactive isotope 90Sr2+ occurring as a nuclear contaminant that accumulates in marine biota and sediments (6). Indeed, in some algae, Sr2+ can almost fully replace Ca2+ without any discernible deleterious effects (7). In humans, Sr2+ treatment of osteoporosis is used to prevent fractures (8). Moreover, predictions concerning climate change stress the increased relevance of higher environmental mobilization of Sr2+ and Ba2+ due to enhanced solubility upon marine acidification (9). Apart from chemical precipitation treatments of radioactive 90Sr2+ and toxic Ba2+, there have been new attempts for bioremediation using cyanobacteria, algae, and fungi (1, 2, 6, 10).
In marine environments, microorganisms accumulate more Sr2+ than Ba2+, possibly due to higher solubility and availability, i.e., the concentration of Sr2+ is around 88 μM compared to 40 to 150 nM Ba2+ (11, 12). In protists, Sr2+ is mostly present in the form of celestite (also referred to as celestine; SrSO4) and strontianite (SrCO3), while Ba2+ forms barite (BaSO4) or witherite (BaCO3) (13, 14). Moreover, Ba2+ and Sr2+ commonly substitute for each other in various ratios to form strontiobarite and baritocelestite (Ba,Sr)SO4 (15). Celestite with traces of Ba2+ 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 Sr2+ (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 Ba2+ and Sr2+ 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). Ba2+ and Sr2+ 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 Ba2+ and Sr2+ to the sea floor (24). However, until now, abundant planktonic organisms capable of selective intracellular accumulation of both Ba2+ and Sr2+ 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 Sr2+ 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 (2931), are capable of massive intracellular accumulation of Sr2+ and Ba2+. Specifically, three cultivable diplonemids accumulate celestite and sometimes barite crystals in intracellular concentrations of Sr2+ 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 (3234). 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.

RESULTS

Light microscopy and analysis of crystals by Raman microscopy.

To determine the chemical composition of biogenic crystals directly within intact cells, Raman microscopy, a vibrational spectroscopic method sensitive to molecular composition, was used. Out of 21 strains belonging to 15 diplonemid species, three members of the distantly related genera Lacrimia and Namystinia, represented by Lacrimia sp. YPF1808, Lacrima lanifica, and Namystinia karyoxenos, were shown to possess celestite crystals (Fig. 1A). Their Raman spectra were congruent with the spectra of mineral celestite and chemically prepared precipitates of SrSO4 (Fig. 1F), matching also Raman spectra of celestite reported elsewhere (36). Due to the countercation sensitivity of the position of the most intense Raman band at around 1,000 cm−1 belonging to the symmetric ν1 vibrational mode of the SO42– tetrahedron, biogenic celestite could be unambiguously identified as SrSO4 and was easily distinguishable from barite, baritocelestite, gypsum (CaSO4), or calcite (CaCO3) (see Fig. S1 in the supplemental material). Small relative-intensity nuances of other Raman bands of biogenic celestite from various cells (Fig. S2) can be explained by differences in crystal structures (lattice defects), trace admixtures of Ba2+, and/or orientations of the crystals, as these are present also in the spectra of mineral reference and chemical precipitates.
FIG 1
FIG 1 Distribution of celestite in diplonemids, based on Raman microscopy analysis. (A) Phylogenetic tree of diplonemids based on 29 with genera containing celestite (blue), other screened genera (black), and unexamined clades (gray). (B to E) DIC micrographs of N. karyoxenos (B and C), Lacrimia sp. YPF1808 (D), and L. lanifica (E) with celestite crystals marked by arrowheads; arrow points to a large polygonal crystal. Scale bar, 10 μm. (F) Raman spectra of biogenic celestite crystals found in diplonemid cells (blue) and celestite mineral (black). (G to I) Raman chemical maps of N. karyoxenos (G), Lacrimia sp. YPF1808 (H), and L. lanifica JW1601 (I) with celestite in blue and other cytoplasmic contents in white. Scale bar, 2 μm.
When N. karyoxenos was examined by light microscopy with differential interference contrast (DIC), the crystalline structures appeared as small birefringent particles moving fast by Brownian motion (Fig. 1B and C; Movie S1). They were most prominent within the enlarged lacunae, which are peripheral membrane-bounded compartments positioned directly beneath the subpellicular microtubular corset (Movie S1), following the addition of 0.1% (wt/vol) formaldehyde. Within a single culture, the size and quantity of crystals inside the cells ranged from a few small particles (Fig. 1B) up to multiple large, tightly packed, polygonal crystals reflecting the shape of orthorhombic prisms (Fig. 1C). The crystalline particles of Lacrimia sp. YPF1808 and L. lanifica were far less prominent under the light microscope than those of N. karyoxenos. However, large crystals were visible around the posterior vacuole with DIC (Fig. 1D and E; Movie S1) and under polarized light (Movie S1).

Morphology, localization, and elemental analysis of intracellular crystals.

Examination with light, Raman, transmission electron microscopy (TEM), and serial block-face scanning electron microscopy (SBF-SEM) showed that the crystalline inclusions in two clades of diplonemids differed in their localization and shapes. In semithin resin-embedded sections of N. karyoxenos, numerous orthorhombic prismatic and bipyramidal crystals were localized mostly inside the lacunae (Fig. 2A, C, and D), with a preference towards the cell posterior. Occasionally, crystals were found inside the large posterior vacuole (Fig. 2A) and in smaller vacuoles scattered throughout the cytoplasm (Fig. 2A and B). Only small crystals could be seen in semithin sections, while bigger crystals dropped out, leaving empty crystal-shaped holes. Due to frequent rupturing, it was not possible to visualize celestite crystals in semithin epoxy resin sections of Lacrimia species. Thus, we used the SBF-SEM approach, which showed that the celestite crystals of Lacrimia sp. YPF1808 appeared mostly in small membrane-bounded compartments with electron-transparent matrix (Fig. 2H to L) adjacent to the large posterior vacuole (Fig. 2H, I, and K). Three-dimensional (3D) reconstruction revealed that each of these compartments contained one crystal of variable size (Movie S2). Less frequently, crystals were found inside the posterior vacuole (Fig. 2I) or in compartments localized near the anterior flagellar pocket (Movie S2), while they were absent from the cytoplasm and other organelles. The crystals had a shape of rhombic prisms (Fig. 2J and M) or asymmetric tabular prismatic structures with pyramidal and pedial terminations (Fig. 2K and N). Although in L. lanifica the celestite crystals were mostly lost from the TEM sections, the positions of holes and ruptures within them and the analysis by Raman microscopy showed similar localizations and sizes of the crystals as those of Lacrimia sp. YPF1808 (Fig. 2D, E, H, and I). Likewise, the membrane-bounded compartments were positioned around the posterior vacuole (Fig. 2F), with small asymmetric flattened crystals preserved only occasionally in TEM sections (Fig. 2G).
FIG 2
FIG 2 Crystal structures of naturally occurring celestite with possible barite admixtures in diplonemids. (A to E) TEM images of semithin sections of N. karyoxenos with longitudinally sectioned cell showing bipyramidal (red arrows) and prismatic (blue arrow) crystals inside peripheral lacunae and posterior vacuole (A); crystals contained within small vacuoles (B); prismatic (C) and bipyramidal (D) crystals inside lacunae; and a schematic representation of prismatic (blue) and bipyramidal (red) crystals (E). (F and G) TEM images of semithin sections of L. lanifica JW1601, with cells cross-sectioned through a posterior vacuole. An arrow points to a small membrane-bounded compartment with the hole left after a dropped-out crystal (F), and another arrow indicates a crystal inside a membrane-bounded compartment and the rupture introduced by a crystal during sectioning (G). (H to L) SBF-SEM images of Lacrimia sp. YPF1808 showing celestite crystals inside membrane-bounded compartments and the large posterior vacuole (I). (M and N) 3D reconstructions of celestite correspond to the images in panels J and K, respectively, in shape of rhombic prism (M) or asymmetric tabular prismatic crystal with pyramidal and pedial terminations (N). PV, posterior vacuole; M, mitochondrion; S, endosymbiotic bacteria; La, lacuna lumen; R, rupture; Sr, celestite crystal; N, nucleus. Scale bar, 2 μm (A and F), 1 μm (B and H to K), and 500 nm (C, D, and G).
The presence of celestite crystals (Fig. 1 and 2) was further confirmed by elemental analysis using energy-dispersive X-ray (EDX) spectroscopy in the cryo-SEM-EDX mode of freeze-fractured Lacrimia sp. YPF1808 (Fig. 3A and C; Fig. S3) and N. karyoxenos cells (Fig. 3B and C; Fig. S4) and by TEM-EDX of whole air-dried cells of L. lanifica (Fig. 3E). Atomic percentages estimated by cryo-SEM-EDX analysis were 7.2% Sr and 7.2% sulfur (S), compared to 1.1% Sr and 1.8% S in Lacrimia sp. YPF1808 and N. karyoxenos, respectively. The dominance of C, N, and O atoms can be explained by the presence of ice and signals from other cellular contents obtained from deeper and/or surrounding areas.
FIG 3
FIG 3 Elemental analysis of diplonemids. (A to C) Cryo-SEM-EDX images of Lacrimia sp. YPF1808 (A) and N. karyoxenos (B), complemented with EDX elemental spectral analysis (C) obtained from the area marked by circles 1 and 2, respectively. (D) SEM-EDX images of Lacrimia sp. YPF1808 showing the presence of S, Sr, and Ba. (E to G) TEM analysis of celestite microcrystals in a micrograph of a dried cell of L. lanifica (E), of a semithin section of N. karyoxenos (F), or EDX spectra (G) from the corresponding areas marked 3 to 5, with red lines highlighting the positions of O, Sr, Ba, and S. Cu and C originated from the support grid, and Os and U originated from staining compounds. (H) Electron diffraction for h0l-oriented sections through the 3D ED data sets from the corresponding areas shown in panels E and F. The celestite unit cell is displayed as a yellow rectangle. Scale bar, 2 μm.
The identities of celestite crystals in Lacrimia sp. YPF1808 (1 μm-thick sections from resin blocks used for SBF-SEM) and N. karyoxenos (250 nm-thick resin sections examined by TEM) were confirmed by SEM-EDX and TEM-EDX, respectively (Fig. 3D, F, and G; Fig. S5). Additionally, a significant amount of Ba2+ was detected in the crystals from N. karyoxenos. Crystallographic analysis by electron diffraction showed that the diffraction of measured crystals corresponded to celestite structure (isostructural with BaSO4) with space group Pnma and lattice parameters a = 8.3 Å, b = 5.3 Å, and c = 6.8 Å in L. lanifica. Larger lattice parameters (a = 8.7 Å, b = 5.5 Å, c = 7.1 Å) were observed in N. karyoxenos, which may be explained by the replacement of Sr2+ with larger Ba2+ in the structure of celestite.

Quantitative analysis by ICP-MS and SBF-SEM.

SBF-SEM-based 3D reconstructions of Lacrimia sp. YPF1808 (Movie S2) showed the presence of celestite crystals in all 20 analyzed cells, ranging from 2 to 16 celestite particles per cell (Fig. 4D; Table S2). In total, more than 100 crystals were analyzed, with a volume ranging from 0.017 to 7 μm3 (Fig. 4C; Table S2). The impacts of the measured celestite contents on the overall cell density ranged from 0.05% to 9%, with an average of 1.3 ± 0.5% (Fig. 4E; Table S2). The calculations were based on the measured volumes, known density of celestite (3.9 g·cm−3), and common cellular densities of 0.985 to 1.156 g·cm−3 reported elsewhere (37).
FIG 4
FIG 4 SBF-SEM images of celestite crystals in Lacrimia sp. YPF1808. (A) 3D reconstruction of a cell. Cytoplasm is shown in yellow, large posterior vacuole is in orange, and celestine crystals are in cyan. Scale bar, 1 μm. Descriptive analysis of measured data is for cells (n = 20) and crystals (n = 106). (B) Distribution of cell volumes. (C) Distribution of celestite crystal volumes on a log scale. (D) Number of celestite crystals per cell. (E) Impacts of celestite crystals on cell density; boxplots show medians and quartiles, and whiskers show the range from minimum to maximum values excluding outliers, represented by single data points.
The lack of celestite crystals in other analyzed species (Diplonema japonicum, Paradiplonema papillatum, and Rhynchopus sp. YZ270) was consistent with the minute 88Sr content measured by ICP-MS. The high values of 88Sr in N. karyoxenos, Lacrimia sp. YPF1808, and L. lanifica corresponded to the abundance of intracellular crystals detected by Raman microscopy, TEM, and SBF-SEM. Since direct measurement of the dry mass was impossible due to the inevitable presence of salts from the medium, the elemental composition analysis by ICP-MS was calculated in atoms per cell or femtomoles per cell. To calculate Sr and Ba content per dry mass, the latter was subsequently estimated by quantitative phase imaging using holographic microscopy (Table 1). The 88Sr amounts ranged from 0.01 fmol·cell−1 in P. papillatum to 5,500 ± 570 fmol·cell−1 (mean ± standard deviation) in N. karyoxenos, corresponding to 340 ± 38 mg·g−1. Lacrimia sp. YPF1808 and L. lanifica were also potent 88Sr accumulators, with 370 ± 58 fmol·cell−1 (130 ± 25 mg·g−1) and 54 ± 8 fmol·cell−1 (64 ± 13 mg·g−1), respectively. Depending on the species, the intracellular concentration of 88Sr was 1,200 to almost 10,000 times higher than in the surrounding medium (Tables 1 and S2).
Table 1
Table 1 ICP-MS quantification of 88Sr and Ba in diplonemidsa
SpeciesD. japonicumP. papillatumRhynchopus sp. YZ270L. lanifica JW1601Lacrimia sp. YPF1808N. karyoxenos
Number of cells per ml in culture2.1·105 ± 9.2·1032.2·106 ± 2.1·1058.1·105 ± 2.6 ·1047.6·105 ± 2.5·1043.7·106 ± 1.7·1051.33·106 ± 5.9·104
Dry weight of cell (pg)109 ± 2.968.0 ± 2.074.2 ± 2.774.1 ± 3.5248.1 ± 8.21,421 ± 11
Sr (fmol·cell–1)0.22 ± 0.010.013 ± 0.0010.08 ± 0.0254.4 ± 8.4366 ± 585,530 ± 570
Sr (mg·g–1)0.17 ± 0.100.02 ± 0.010.10 ± 0.0764 ± 13129 ± 25340 ± 38
pabacde
SrSO4 (mg·g–1)n/an/an/a135271715
Concentration of Sr (folds)*bn/an/an/a1,520 ± 6801,240 ± 55010,000 ± 3,300
Ba (fmol·cell–1)n/an/an/a2.0 ± 0.565 ± 101,200 ± 130
Ba (mg·g–1)n/an/an/a3.7 ± 1.135.8 ± 6.8116 ± 14
pn/an/an/aabc
BaSO4 (mg·g–1)n/an/an/a6.361198
Concentration of Ba (folds)*bn/an/an/a1,130 ± 6604,300 ± 1,90042,000 ± 14,000
Total Ba,Sr(SO4) (mg·g–1)n/an/an/a141332913
a
The dry weight was measured by quantitative phase imaging (n = 150 cells). Results of ICP-MS are displayed as mean values of biological triplicates with standard error of the mean. All figures are rounded to two significant numbers. The amounts of 88Sr and Ba per dry mass (mg·g−1) was logarithmically transformed and statistically analyzed by one-way ANOVA p < 0.001 (F = 1747.8 and F = 88.6; total degree of freedom: df = 17 and df = 8, respectively), with Tukey’s post-hoc test significant differences on the level p < 0.05 in column p.
b
*, calculated as atoms·cell−1 based on analyzed cell pellets relative to the theoretical value in atoms·cell−1 originating from the culture medium alone (8 mg·l−1 Sr2+ and 0.64 mg·l−1 Ba2+ – as listed in SI Appendix Table S1); in N. karyoxenos, the amount of accumulated Ba exceeds total Ba available per volume of culture medium due to repeated passages of pelleted cells into fresh medium. n/a, not analyzed.
Compared to the massive accumulation of 88Sr in diplonemids, the naturally co-occurring Ba was present in much lower amounts (Table 1 and S2), slightly above the detection limit of TEM-EDX analysis (Fig. 3G), possibly reflecting a 12.5 times lower Ba2+ concentration in the seawater growth medium (Table S1). Nevertheless, the cells concentrated Ba2+ on average 1,000 to over 42,000 times above the level in the growth medium (Table S1), reaching 1,200 ± 130 fmol·cell−1 (120 ± 14 mg·g−1) in N. karyoxenos, with lower values in Lacrimia sp. YPF1808 (65 ± 10 fmol·cell−1, or 36 ± 7 mg·g−1) and L. lanifica (2 ± 1 fmol·cell−1, or 4 ± 1 mg·g−1). Altogether, (Ba,Sr)SO4 accumulation reached 91%, 33%, and 14% of dry weight in N. karyoxenos, Lacrimia sp. YPF1808, and L. lanifica, respectively. All strains showed significantly different levels of accumulated Sr or Ba contents (Table 1). Although the concentration of Ba2+ in our experiment was 30 to 45 times higher than in nature, the stoichiometry per cell was 5 orders of magnitude lower than in the oceans (Table 1).

Ba2+ loading experiments and elimination of Sr2+ and Ba2+ from the medium.

Under our cultivation conditions, Ba2+ was 20 times less abundant than Sr2+ (Table S1), which resulted in formation of celestite with Ba2+ admixtures in the examined species. In oceans, the proportion is even 30 times lower (11, 12). Here, we tested whether increases in Ba2+ content would impact the biomineralization process by cultivation in artificial seawater loaded with equimolar amounts of Ba2+ and Sr2+ to 88 μM. To prevent spontaneous precipitation of barite, we supplemented sulfates with NaCl to maintain the osmolarity of the medium. This resulted in the formation of all mineral combinations: pure barite (Raman marker at 988 cm−1), celestite (1,000 cm−1), and mixed forms of (Ba,Sr)SO4 (991 cm−1; strontiobarite or baritocelestite) (Fig. 5), revealing that diplonemids do not show a strong preference toward the accumulation of either element.
FIG 5
FIG 5 Raman maps and spectra of barite and celestite crystals in diplonemids cultivated with equimolar amounts of Sr2+ and Ba2+ in the medium. (A to F) A single cell of N. karyoxenos containing cocrystallized fractions dominated by celestite in the central part (E; cyan) with gradually overlapping barite (B to D; shades of green) toward the periphery of its pure fraction (A; yellow), and the merged Raman map of of panels A to E (F). The limited spatial resolution of Raman microscopy did not allow distinguishing conglomerates of pure-species microcrystals from a single crystal with a variable elemental composition. (G to M) Two cells of Lacrimia sp. YPF1808 (G and H) and two cells L. lanifica (I and J) contained pure barite (K; yellow) and celestite (M; blue) and homogenously mixed crystals of (Ba,Sr)SO4 (L; orange).
Both L. lafinica and Lacrimia sp. YPF1808 contained mostly mixed crystals of (Ba,Sr)SO4. In N. karyoxenos, pure celestite prevailed in the central part of crystals (999 cm−1) while barite dominated at the periphery (988 cm−1), and they gradually overlapped each other (Fig. 5C to F). Additionally, after several passages in the artificial medium without Ba2+ and Sr2+ (Table S1), barite and celestite were no longer detectable by Raman microscopy. The lack of Ba2+ and Sr2+ did not result in altered morphology or growth impairment. We did not observe any Ca2+- or Mg2+-containing crystals despite high concentrations of both elements in the medium.

Feeding experiments.

Fecal pellets are an important agent mediating sedimentation of biogenically accumulated minerals to the sea floor: large aggregates of crystals held together by undigested fecal organic matter enable their fast sinking, thus preventing dissolution of micrometer-sized crystals in the water column, which is undersaturated for barite and celestite (15, 24). To experimentally address whether zooplankton feeds on diplonemids and whether their celestite crystals are carried into fecal pellets, we incubated N. karyoxenos and Lacrimia sp. YPF1808 with freshly captured filter-feeding marine copepods Centropages typicus, Temora longicornis, and Acartia sp., starved for 12 h prior to the experiment. After 5-day cocultivation, we determined by Raman microscopy that the fecal pellets contained copious amounts of celestite derived from diplonemids (Fig. 6B). In the control system of the same population of copepods fed with freshly collected marine plankton, the fecal pellets contained undigested chlorophyll, carotenoids with remnants of lipids, calcite particles, and contaminating polystyrene microplastic particles, but lacked celestite crystals (Fig. 6B).
FIG 6
FIG 6 Schematic representation of the biological impact on Ba2+ and Sr2+ cycling in the oceans. (A) Hypothetical scenario of trace elements inlet, plankton uptake, recycling, and sedimentary deposition. The major source of trace elements is driven by river influx and less prominently by aerial deposition (9) and is mostly balanced by the same amount of total deposition in sediments, correlated with the total marine productivity and particulate organic matter deposition (24). A great proportion of these trace elements is being recycled by living organisms after release from dead cells. Acantharea (image adapted from referene 69) take up a substantial portion of Sr2+ and Ba2+, which are further recycled in upper 400 m (25). Coccolithophorids build their scales from calcium carbonate with minor amounts of Ba2+ and Sr2+ that are proportional to the seawater contents (22), being partially recycled upon dissolution or transported to the marine sediments in fecal pellets (24). The Ba2+ accumulated by bacteria sediments in the aggregates of marine snow (26) or is recycled. We highlighted diplonemids as potential players in the marine cycle of both elements and drivers of biogenic formation of celestite and barite crystals found in suspended matter everywhere in the world oceans (24), and they can also feed on bacteria or particulate organic matter or scavenge the dead bodies of zooplankton as major heterotrophic protists in the mesopelagic zone. (B) Raman microscopy analysis of fecal pellets produced by copepods experimentally fed with diplonemids, which contained celestite crystals (cyan) and undigested lipids, including sterols (gray). In the control samples of copepods fed with microalgae, fecal pellets contained undigested carotenoids, chlorophyll (yellow-orange-red), and calcite particles (pink), with unexpected particles of polystyrene microplastics (measured as a single spectrum [not shown on the Raman map]). Scale bars, 20 μm.

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 Ba2+ and Sr2+ 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 Sr2+ and Ba2+ accumulation in some diplonemids outperforms that of any other reported organisms (10, 13, 21, 4244). Indeed, while the intracellular concentration of Sr2+ 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 Sr2+ together with 120 mg·g−1 Ba2+, which in the form of sulfate represents 90% of the cellular dry mass, pointing to the unique Sr2+ and Ba2+ 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)SO4, apparently not discriminating one element over the other. Hence, we explain the higher content of Sr2+ over Ba2+ inside the crystals by the higher availability of the former element in seawater. Although the mechanisms behind intracellular accumulation of Sr2+ and Ba2+ 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 Sr2+ uptake and transportation within eukaryotic cells have been shown to occur via commonly present transporters of divalent cations, i.e., the Ca2+ uniporter and H+/Ca2+ 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 Ca2+ and Sr2+ is usually comparable (45, 46), some organisms including diplonemids clearly favor Ba2+ and Sr2+ over Ca2+ (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 CaSO4 or any of its forms (gypsum, bassanite, anhydride, etc.), even though the concentration of Ca2+ in the cultivation medium or in the environment is several orders of magnitude higher than that of Sr2+ and Ba2+.
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 Ba2+/Sr2+, 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 Ba2+ 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 Ba2+/Sr2+ 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 Ba2+/Sr2+ cycling, diplonemids have been shown to ingest bacteria as one of their sources of nutrition (30); if bacteria were loaded with Ba2+/Sr2+ 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 Ba2+, in which case they may accumulate more Ba2+ than Sr2+. In principle, we experimentally supported such a scenario upon doping the cells with equimolar Ba2+ and Sr2+ concentrations (Fig. 5). Finally, we do not exclude that some species of diplonemids to be described in future would prefer Ba2+ over Sr2+ 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.

MATERIALS AND METHODS

Cell cultures, cultivation, and light microscopy.

For all experiments, axenic cultures were grown in seawater-based Hemi medium (see Table S1 in the supplemental material) supplemented with 1% horse serum and 0.025 g/liter LB broth powder (53). An artificial seawater medium lacking Sr2+, Ba2+, and sulfates was prepared from 288 mM NaCl, 8 mM KCl, 718 mM KBr, 100 mM MgCl2, 12 mM CaCl2, 40 mM HBO3, and 60 mM NaF, supplemented with 1% (vol/vol) heat-inactivated horse serum (Sigma-Aldrich) and 25 mg LB broth powder (Amresco). The medium was used as rinsing solution for preparation of ICP-MS samples and cell microcrystal depletion to be measured via quantitative phase imaging (QPI) (see below). For Ba2+ loading experiments, BaCl2 was added in equimolar amounts with respect to naturally occurring (88 μM) Sr2+ (12).
Axenic clonal cultures of 17 species of diplonemids were grown either at 27°C (Paradiplonema papillatum ATCC 50162), 22°C (Namystinia karyoxenos YPF1621), or 13°C (of D. aggregatum YPF1605, D. japonicum YPF1604, Flectonema sp. DT1601, Hemistasia phaeocysticola, Lacrimia lanifica JW1601, Lacrimia sp. YPF1808, Rhynchopus sp. YZ270 cl. 10.3, Rhynchopus sp. YZ270 cl. 9, Rhynchopus sp. DT0301, Rhynchopus humris YPF1505, R. euleeides ATCC 50226, R. serpens YPF1515, and Sulcionema specki YPF1618). P. papillatum and R. euleeides were isolated from coastal surface waters (United States) in 1985 and 1986, respectively. The remaining species originated either from coastal seawater around Japan or from Enoshima Aquarium (Kanagawa, Japan) and were continuously maintained in culture for 1 to 7 years prior to the analyses. The identity of not-yet-formally described species was established based on the 18S rRNA sequences as described previously (54). Dense cultures of trophic cells (55) were harvested by centrifugation at 3,000 × g for all subsequent analyses.
Light microscopy images and videos were taken with an Olympus BX53 microscope equipped with a DP72 microscope digital camera using CellSens software v. 1.11 (Olympus) and processed with GIMP v. 2.10.14, Irfan View v. 4.54, and Image J v. 1.51 software. Polarized microscopy was performed using crossed polarizers installed to a Raman microscope (as specified below).

Environmental sampling.

Zooplankton was collected in the Bay of Villefranche sur Mer, France (43°40′N, 7°19′E) with a 10-min haul from 10 m to the surface, using a 20-μm-mesh-size plankton net. Captured copepods were transferred into 0.5 liters of freshly filtered natural seawater and starved for 12 h. Centropages typicus, Temora longicornis, and Acartia sp. were then picked under a dissection microscope. All experiments were carried out at cultivation temperature of the prey species of diplonemids (13°C for Lacrimia sp. YPF1808, room temperature for N. karyoxenos). Ten copepods were kept in 20 mL of diplonemid culture (105 cells mL−1) for 5 days, after which their fecal pellets were collected under a dissection microscope and immediately analyzed by Raman microscopy (as specified below).

Raman microscopy.

For the in situ determination of the chemical composition of intracellular structures, a confocal Raman microscope (alpha300 RSA; WITec, Germany) was used as previously described (5660). To immobilize the fast-moving flagellates on the quartz slide, 5 μL of the cell pellet was mixed with 5 μL of 1% (wt/vol) solution of low-melting-point agarose (catalog number 6351.5; Carl Roth, Germany), immediately spread as a single-cell layer between a quartz slide and coverslip, and sealed with CoverGrip sealant (Biotium, USA). Two-dimensional Raman maps were obtained with laser excitation at 532 nm (20 mW power at the focal plane) and oil-immersion objective UPlanFLN 100×, numerical aperture (NA) 1.30, or water-immersion objective UPlanSApo 60×, NA 1.20 (Olympus, Japan). A scanning step size of 200 nm in both directions and an integration time of 100 ms per voxel were used. A minimum of 30 cells were measured for each strain. Raman chemical maps were constructed by multivariate decomposition of the baseline-corrected spectra into the spectra of pure chemical components by using Project Plus 5.1 software (WITec, Germany).

TEM, TEM-ED, and TEM-EDX.

The protocol for the basic sample preparation of all kinds of electron microscopy approaches listed here is described in detail elsewhere (61). We used it with minor modifications, as stated below. Cell pellets were transferred to specimen carriers and immediately frozen in the presence of 20% (wt/vol) bovine serum albumin solution using a high-pressure freezer (Leica EM ICE, Leica Microsystems, Austria). Freeze substitution was performed in the presence of 2% osmium tetroxide diluted in 100% acetone at −90°C. After 96 h, specimens were warmed to −20°C at a step of 5°C/h. After another 24 h, the temperature was increased to 3°C (3°C/h). At room temperature, samples were washed in acetone and infiltrated with 25%, 50%, and 75% acetone/resin mixture for 1 h at each step. Finally, samples were infiltrated in 100% resin and polymerized at 60°C for 48 h. Semithin (250 nm) and ultrathin (70 nm) sections were cut using a diamond knife, placed on copper grids, and stained with uranyl acetate and lead citrate. TEM micrographs were taken with a Mega View III camera (SIS) using a JEOL 1010 TEM operating at an accelerating voltage of 80 kV.
For TEM-EDX, 10 μL of pelleted L. lanifica cells was spread over a holey carbon-coated copper grid, washed twice with 10 μL of distilled water in order to reduce the sea salts from the culture medium, and allowed to dry by evaporation at ambient temperature. Semithin sections of resin-infiltrated blocks of N. karyoxenos were prepared as stated above. For the identification of the crystalline phase, sections were studied by TEM on an FEI Tecnai 20 system (LaB6, 120 kV) equipped with an Olympus SIS charge-coupled-device camera Veleta (2,048 by 2,048 pixels) and an EDAX windowless EDX detector Apollo XLTW for elemental analysis. The diffraction data were collected by means of 3D electron diffraction (ED) (62). The data processing was carried out using PETS software (63). Structure solution and refinement were performed in the computing system Jana2006 (64).

Cryo-scanning electron microscopy with EDX.

Cells pellets were high-pressure frozen as described above and transferred into a Leica ACE 600 preparation chamber (Leica Microsystems, Austria) precooled at −135°C, fractured with a scalpel, freeze-etched at −100°C for 1 min, and sputter-coated with 2.5 nm of gold-palladium at −125°C. Specimens were transferred under vacuum using transfer system VCT100 (Leica Microsystems, Austria) and observed with a Magellan 400L SEM (FEI, Czech Republic and USA) precooled at −125°C (cryo-SEM). Topographical images and EDX measurements were obtained using an EDT detector and EDAX detector (Octane Elect Super; EDAX, USA), respectively, either at 5 keV/0.1 NA or 10 keV/0.8 NA. The taken spectra were analyzed with EDAX TEAM software and quantified by the eZAF method.

Serial block-face SEM.

The sample preparation of Lacrimia sp. YPF1808 by the high-pressure freezing technique followed the protocol for TEM sample preparation. After freeze-substitution, the samples were subsequently stained with 1% thiocarbohydrazide in 100% acetone for 1.5 h, 2% OsO4 in 100% acetone for 2 h at room temperature, and 1% uranyl acetate in 100% acetone overnight at 4°C. After every staining step, the samples were washed 3 times with 100% acetone for 15 min. Samples were then infiltrated with 25%, 50%, or 75% acetone-resin mixture for 2 h at each step, and finally infiltrated in 100% Hard Resin Plus 812 (EMS) overnight and polymerized at 62°C for 48 h. Resin-embedded blocks were trimmed and imaged using an Apreo SEM equipped with a VolumeScope (Thermo Fisher Scientific, Germany). Serial images were acquired at 3.5 keV, 50 pA, 40 Pa with a resolution of 6 nm, 100-nm slice thickness, and dwell time per pixel of 4 μs. Image data were processed in Microscopy Image Browser v2.702 (65) and Amira v2020.2. The resin-embedded blocks were also collected in the form of 1-μm-thick sections on a silicon wafer and analyzed by SEM-EDX (Magellan 400L system, as described above).
Based on volumetric data, we calculated the percentage of increase in cell density based on measured volumes of crystals compared to the theoretical crystal-free cells of the same volume and reported average theoretical density of 1.07 g·cm−3 (37).

ICP-MS.

For analysis of Ba and 88Sr concentrations, cultures were grown in triplicates, counted, and washed three times with 1 M sorbitol solution (for P. papillatum, D. japonicum, and Rhynchopus YZ270 cl. 10) or Sr- and Ba-free artificial seawater rinsing solution (see above) (for L. lanifica JW1601, Lacrimia sp. 1808, and N. karyoxenos) to remove Ba2+ and Sr2+ present in the cultivation medium. Cultivated cells were harvested by centrifugation and rinsed twice with 50 mL and once with 2 mL of the rinsing solution, and the resulting pellets were freeze-dried. A 0.5-mL digestion acid mix (425 μL of 70% HClO4 and 75 μL of 69% HNO3) prepared as described elsewhere (66) was added directly to the dried biomass. The digestion was done using a Fuji PXG4 Thermoblock (AHF Analysentechnik AG, Germany). After evaporation of the acid mix, 0.5 mL of 5% HCl was added to each test tube to redissolve the salts. The glass tubes were heated to 90°C for 1 h to obtain clear solutions. The final volume of 1.5 mL was adjusted with double-distilled H2O. Appropriate dilutions were made with 0.2% HNO3. Indium was added as an internal standard at 1 ng/mL to each test solution. The ICP multielement standard solution VI (Merck, Germany) was used to prepare standard curves. Analyses were done using an inductively coupled plasma sector-field mass spectrometer (ICP sfMS) Element XR-2 with jet interface (Thermo Fisher Scientific, Germany) following a described protocol (67). Medium resolution of 4,000 was used in Ba and 88Sr measurements in triplicate of each technical replicate, with the highest precision and lowest relative standard deviation. Additionally, the elemental composition of samples of standard growth medium and artificial seawater medium without sulfates, Ba2+, or Sr2+ were analyzed.

Holographic microscopy and QPI.

Samples for holographic microscopy were immobilized prior to measurement as described above for Raman microscopy. Imaging was performed at the Q-Phase microscope (Tescan Orsay Holding, Czech Republic). The holographic Q-Phase microscope is equipped with halogen lamp illumination through an interference filter (λ[¼] 650 nm, 10 nm full-width, half-maximal) and microscope objective (Nikon Plan Fluor oil immersion, 60×, numerical aperture 1.4, providing lateral resolution of 0.57 μm). The numerical reconstruction of acquired data was performed using Q-Phase software (Tescan Orsay Holding, Czech Republic). The technique enables automated cell segmentation and quantitative analysis of cellular mass based on the specific proportions of thickness and refractive indices of measured cells in comparison to the reference (68). Due to the high variability of cell contents and sizes, at least 150 cells were analyzed for each strain. Because crystalline inclusions caused artifacts during capturing due to the big difference in refractive indices, we analyzed crystal-free cells cultivated in the artificial seawater medium lacking Sr2+, Ba2+, and sulfates (as specified above). We calculated the total dry mass of the cells as the sum of crystal-free cells, measured by holographic microscopy, and SrSO4 and BaSO4 amounts measured via ICP-MS. The dry weight ratios of trace elements measured via ICP-MS were calculated based on the total dry weight of corresponding strains.

Statistical data analysis.

Statistical analysis was conducted using SigmaPlot v. 12.5 and SPSS v. 23.0. Logarithmically normalized data were subjected to statistical tests (one-way analysis of variance [ANOVA] and Tukey’s post hoc) on an alpha level of 0.05. Calculations of standard errors of the means based on independent methods (i.e., ICP-MS quantification and QPI dry mass quantification) with different levels of variability were done according to mathematical conversion using Taylor expansion.

Data availability.

All data generated or analyzed during this study are included in the published article and its supplemental material files.

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.

Footnote

This article is a direct contribution from Julius Lukeš, a Fellow of the American Academy of Microbiology, who arranged for and secured reviews by Gabriel Gorsky, Laboratoire d'Océanographie Villefranche-sur-Mer, and Virginia Edgcomb, Woods Hole Oceanographic Institution.

Supplemental Material

File (mbio.03279-22-s0001.pdf)
File (mbio.03279-22-s0002.pdf)
File (mbio.03279-22-s0003.pdf)
File (mbio.03279-22-s0004.pdf)
File (mbio.03279-22-s0005.pdf)
File (mbio.03279-22-s0006.pdf)
File (mbio.03279-22-s0007.pdf)
File (mbio.03279-22-s0008.mov)
File (mbio.03279-22-s0009.mov)
ASM does not own the copyrights to Supplemental Material that may be linked to, or accessed through, an article. The authors have granted ASM a non-exclusive, world-wide license to publish the Supplemental Material files. Please contact the corresponding author directly for reuse.

REFERENCES

1.
Avery SV, Smith SL, Ghazi AM, Hoptroff MJ. 1999. Stimulation of strontium accumulation in linoleate-enriched Saccharomyces cerevisiae is a result of reduced Sr2+ efflux. Appl Environ Microbiol 65:1191–1197.
2.
Krejci MR, Wasserman B, Finney L, McNulty I, Legnini D, Vogt S, Joester D. 2011. Selectivity in biomineralization of barium and strontium. J Struct Biol 176:192–202.
3.
Bowen HJM, Dymond JA. 1955. Strontium and barium in plants and soils. Proc R Soc Lindon B Biol Sci 144:355–368.
4.
Pors Nielsen S. 2004. The biological role of strontium. Bone 35:583–588.
5.
Bhoelan BS, Stevering CH, van der Boog ATJ, van der Heyden MAG. 2014. Barium toxicity and the role of the potassium inward rectifier current. Clin Toxicol 52:584–593.
6.
Fukuda SY, Iwamoto K, Atsumi M, Yokoyama A, Nakayama T, Ishida K-I, Inouye I, Shiraiwa Y. 2014. Global searches for microalgae and aquatic plants that can eliminate radioactive cesium, iodine and strontium from the radio-polluted aquatic environment: a bioremediation strategy. J Plant Res 127:79–89.
7.
Walker JB. 1953. Inorganic micronutrient requirements of Chlorella. I. Requirements for calcium (or strontium), copper, and molybdenum. Arch Biochem Biophys 46:1–11.
8.
Bolland MJ, Grey A. 2016. Ten years too long: strontium ranelate, cardiac events, and the European Medicines Agency. Br Med J 354:i5109.
9.
Moore JW. 1991. Inorganic contaminants of surface water: research and monitoring priorities, 1st ed. Springer US, New York, NY.
10.
Cam N, Benzerara K, Georgelin T, Jaber M, Lambert JF, Poinsot M, Skouri-Panet F, Cordier L. 2016. Selective uptake of alkaline earth metals by cyanobacteria forming intracellular carbonates. Environ Sci Technol 50:11654–11662.
11.
Paytan A, Griffith EM. 2007. Marine barite: recorder of variations in ocean export productivity. Deep Sea Res II 54:687–705.
12.
Griffith EM, Paytan A. 2012. Barite in the ocean: occurrence, geochemistry and palaeoceanographic applications. Sedimentology 59:1817–1835.
13.
Raven JA, Knoll AH. 2010. Non-skeletal biomineralization by eukaryotes: matters of moment and gravity. Geomicrobiol J 27:572–584.
14.
Langer G, Nehrke G, Thoms S, Stoll H. 2009. Barium partitioning in coccoliths of Emiliania huxleyi. Geochim Cosmochim Acta 73:2899–2906.
15.
Monnin C, Cividini D. 2006. The saturation state of the world’s ocean with respect to (Ba,Sr)SO4 solid solutions. Geochim Cosmochim Acta 70:3290–3298.
16.
Bütschli O. 1906. Über die chemische Natur der Skelettsubstanz der Acantharia. Zool Anz 30:784–789.
17.
Hemmersbach R, Krause M, Bräucker R, Ivanova K. 2005. Graviperception in ciliates: steps in the transduction chain. Adv Space Res 35:296–299.
18.
Brook AJ, Fotheringham A, Bradly J, Jenkins A. 1980. Barium accumulation by desmids of the genus Closterium (Zygnemaphyceae). Br Phycol J 15:261–264.
19.
Gooday AJ, Nott JA. 1982. Intracellular barite crystals in two Xenophyophores, Aschemonella ramuliformis and Galatheammina sp. (Protozoa: Rhizopoda) with comments on the taxonomy of A. ramuliformis. J Mar Biol Ass 62:595–605.
20.
Fresnel J, Galle P, Gayral P. 1979. Résultats de la microanalyse des cristaux vacuolaires chez deux Chromophytes unicellulaires marines: Exanthemachrysis gayraliae, Pavlova sp. (Prymnesiophyceées, Pavlovacées). C R Hebd Seances Ser D Sci Nat 288:823–825.
21.
Martignier A, Filella M, Pollok K, Melkonian M, Bensimon M, Barja F, Langenhorst F, Jaquet JM, Ariztegui D. 2018. Marine and freshwater micropearls: biomineralization producing strontium-rich amorphous calcium carbonate inclusions is widespread in the genus Tetraselmis (Chlorophyta). Biogeosciences 15:6591–6605.
22.
Stoll HM, Rosenthal Y, Falkowski P. 2002. Climate proxies from Sr/Ca of coccolith calcite: Calibrations from continuous culture of Emiliania huxleyi. Geochim Cosmochim Acta 66:927–936.
23.
Dymond J, Collier R. 1996. Particulate barium fluxes and their relationships to biological productivity. Deep Res Part II Top Stud Oceanogr 43:1283–1308.
24.
Dehairs F, Chesselet R, Jedwab J. 1980. Discrete suspended particles of barite and the barium cycle in the open ocean. Earth Planet Sci Lett 49:528–550.
25.
De Deckker P. 2004. On the celestite-secreting Acantharia and their effect on seawater strontium to calcium ratios. Hydrobiologia 517:1–13.
26.
Martinez-Ruiz F, Jroundi F, Paytan A, Guerra-Tschuschke I, Abad MDM, González-Muñoz MT. 2018. Barium bioaccumulation by bacterial biofilms and implications for Ba cycling and use of Ba proxies. Nat Commun 9:1619.
27.
Bishop JKB. 1988. The barite-opal-organic carbon association in oceanic particulate matter. Nature 332:341–343.
28.
Horner TJ, Pryer HV, Nielsen SG, Crockford PW, Gauglitz JM, Wing BA, Ricketts RD. 2017. Pelagic barite precipitation at micromolar ambient sulfate. Nat Commun 8:1342.
29.
Kostygov AY, Karnkowska A, Votýpka J, Tashyreva D, Maciszewski K, Yurchenko V, Lukeš J. 2021. Euglenozoa: taxonomy, diversity and ecology, symbioses and viruses. Open Biol 11:200407.
30.
Prokopchuk G, Korytář T, Juricová V, Majstorović J, Horák A, Šimek K, Lukeš J. 2022. Trophic flexibility of marine diplonemids: switching from osmotrophy to bacterivory. ISME J 16:1409–1419.
31.
Tashyreva D, Simpson AGB, Prokopchuk G, Škodová-Sveráková I, Butenko A, Hammond M, George EE, Flegontova O, Záhonová K, Faktorová D, Yabuki A, Horák A, Keeling PJ, Lukeš J. 2022. Diplonemids: a review on “new” flagellates on the oceanic block. Protist 173:125868.
32.
Flegontova O, Flegontov P, Malviya S, Audic S, Wincker P, de Vargas C, Bowler C, Lukeš J, Horák A. 2016. Extreme diversity of diplonemid eukaryotes in the Ocean. Curr Biol 26:3060–3065.
33.
Flegontova O, Flegontov P, Londoño Castañeda AP, Walczowski W, Šantić D, Edgcomb VP, Lukeš J, Horák A. 2020. Environmental determinants of the distribution of planktonic diplonemids and kinetoplastids in the oceans. Environ Microbiol 22:4014–4031.
34.
de Vargas C, Audic S, Henry N, Decelle J, Mahé F, Logares R, Lara E, Berney C, Le Bescot N, Probert I, Carmichael M, Poulain J, Romac S, Colin S, Aury J-M, Bittner L, Chaffron S, Dunthorn M, Engelen S, Flegontova O, Guidi L, Horák A, Jaillon O, Lima-Mendez G, Lukeš J, Malviya S, Morard R, Mulot M, Scalco E, Siano R, Vincent F, Zingone A, Dimier C, Picheral M, Searson S, Kandels-Lewis S, Tara Oceans Coordinators, Acinas SG, Bork P, Bowler C, Gorsky G, Grimsley N, Hingamp P, Iudicone D, Not F, Ogata H, Pesant S, Raes J, Sieracki ME, Speich S, et al. 2015. Eukaryotic plankton diversity in the sunlit ocean. Science 348:1261605.
35.
Mukherjee I, Salcher MM, Andrei AŞ, Kavagutti VS, Shabarova T, Grujčić V, Haber M, Layoun P, Hodoki Y, Nakano SI, Šimek K, Ghai R. 2020. A freshwater radiation of diplonemids. Environ Microbiol 22:4658–4668.
36.
Zhou L, Mernagh TP, Mo B, Wang L, Zhang S, Wang C. 2020. Raman study of barite and celestine at various temperatures. Minerals 10:260.
37.
Walsby AE, Reynolds CS. 1980. Sinking and floating, p 371–412. In Morris I (ed), The physiological ecology of the phytoplankton. Blackwell Science, Oxford, United Kingdom.
38.
Knoll AH. 2003. Biomineralization and evolutionary history. Rev Mineral Geochem 54:329–356.
39.
Kreger DR, Boeré H. 1969. Some observations on barium sulphate in Spirogyra. Acta Bot Neerl 18:143–151.
40.
Gawryluk RMR, Del Campo J, Okamoto N, Strassert JFH, Lukeš J, Richards TA, Worden AZ, Santoro AE, Keeling PJ. 2016. Morphological identification and single-cell genomics of marine diplonemids morphological identification. Curr Biol 26:3053–3059.
41.
Cavan EL, Laurenceau-Cornec EC, Bressac M, Boyd PW. 2019. Exploring the ecology of the mesopelagic biological pump. Prog Oceanogr 176:102125.
42.
Fisher NS, Guillard RRL, Bankston DC. 1991. The accumulation of barium by marine phytoplankton grown in culture. J Mar Res 49:339–354.
43.
Brook AJ, Grime GW, Watt F. 1988. A study of barium accumulation in desmids using the Oxford scanning proton microprobe (SPM). Nucl Instruments Methods Phys Res 30:372–377.
44.
Sun S, Liu M, Nie X, Dong F, Hu W, Tan D, Huo T. 2018. A synergetic biomineralization strategy for immobilizing strontium during calcification of the coccolithophore Emiliania huxleyi. Environ Sci Pollut Res Int 25:22446–22454.
45.
Kirichok Y, Krapivinsky G, Clapham DE. 2004. The mitochondrial calcium uniporter is a highly selective ion channel. Nature 427:360–364.
46.
Schumaker KS, Sze H. 1986. Calcium transport into the vacuole of oat roots. Characterization of H+/Ca2+ exchange activity. J Biol Chem 261:12172–12178.
47.
Docampo R, Lukeš J. 2012. Trypanosomes and the solution of a fifty years-mitochondrial calcium mystery. Trends Parasitol 28:31–37.
48.
Veronis G. 1972. On properties of seawater, defined by temperature, salinity and pressure. J Mar Res 30:227–255.
49.
Gaft ML, Bershov LV, Krasnaya AR, Yaskolko VY. 1985. Luminescence centers in anhydrite, barite, celestite and their synthesized analogs. Phys Chem Minerals 11:255–260.
50.
Raven JA. 1985. Regulation of pH and generation of osmolarity in vascular plants: a cost-benefit analysis in relation to efficiency of use of energy, nitrogen and water. New Phytol 101:25–77.
51.
Butenko A, Hammond M, Field MC, Ginger ML, Yurchenko V, Lukeš J. 2021. Reductionist pathways for parasitism in Euglenozoans? Expanded datasets provide new insights. Trends Parasitol 37:100–116.
52.
De Vargas C, Aubry M-P, Probert I, Young J. 2007. Origin and evolution of coccolithophores: from coastal hunters to oceanic farmers, p 251–285. Evolution of primary producers in the sea. Elsevier, Amsterdam, Netherlands.
53.
Tashyreva D, Prokopchuk G, Yabuki A, Kaur B, Faktorová D, Votýpka J, Kusaka C, Fujikura K, Shiratori T, Ishida K-I, Horák A, Lukeš J. 2018. Phylogeny and morphology of new diplonemids from Japan. Protist 169:158–179.
54.
Prokopchuk G, Tashyreva D, Yabuki A, Horák A, Masařová P, Lukeš J. 2019. Morphological, ultrastructural, motility and evolutionary characterization of two new Hemistasiidae species. Protist 170:259–282.
55.
Tashyreva D, Prokopchuk G, Votýpka J, Yabuki A, Horák A, Lukeš J. 2018. Life cycle, ultrastructure, and phylogeny of new diplonemids. mBio 9:e02447-17.
56.
Moudříková Š, Sadowsky A, Metzger S, Nedbal L, Mettler-Altmann T, Mojzeš P. 2017. Quantification of polyphosphate in microalgae by Raman microscopy and by a reference enzymatic assay. Anal Chem 89:12006–12013.
57.
Moudříková Š, Mojzeš P, Zachleder V, Pfaff C, Behrendt D, Nedbal L. 2016. Raman and fluorescence microscopy sensing energy-transducing and energy-storing structures in microalgae. Algal Res 16:224–232.
58.
Moudříková Š, Nedbal L, Solovchenko A, Mojzeš P. 2017. Raman microscopy shows that nitrogen-rich cellular inclusions in microalgae are microcrystalline guanine. Algal Res 23:216–222.
59.
Barcytė D, Pilátová J, Mojzeš P, Nedbalová L. 2020. The arctic Cylindrocystis (Zygnematophyceae, Streptophyta) green algae are genetically and morphologically diverse and exhibit effective accumulation of polyphosphate. J Phycol 56:217–232.
60.
Pilátová J, Pánek T, Oborník M, Čepička I, Mojzeš P. 2022. Revisiting biocrystallization: purine crystalline inclusions are widespread in eukaryotes. ISME J 16:2290–2294.
61.
Yurchenko V, Votýpka J, Tesarová M, Klepetková H, Kraeva N, Jirků M, Lukeš J. 2014. Ultrastructure and molecular phylogeny of four new species of monoxenous trypanosomatids from flies (Diptera: Brachycera) with redefinition of the genus Wallaceina. Folia Parasitol 61:97–112.
62.
Gemmi M, Mugnaioli E, Gorelik TE, Kolb U, Palatinus L, Boullay P, Hovmöller S, Abrahams JP. 2019. 3D electron diffraction: The nanocrystallography revolution. ACS Cent Sci 5:1315–1329.
63.
Palatinus L, Brázda P, Jelínek M, Hrdá J, Steciuk G, Klementová M. 2019. Specifics of the data processing of precession electron diffraction tomography data and their implementation in the program PETS2.0. Acta Crystallogr B Struct Sci Cryst Eng Mater 75:512–522.
64.
Petříček V, Dušek M, Palatinus L. 2014. Crystallographic computing system JANA2006: general features. Z Krist 229:345–352.
65.
Belevich I, Joensuu M, Kumar D, Vihinen H, Jokitalo E. 2016. Microscopy Image Browser: a platform for segmentation and analysis of multidimensional datasets. PLoS Biol 14:e1002340.
66.
Zhao F, McGrath SP, Crosland AR. 1994. Comparison of three wet digestion methods for the determination of plant sulphur by inductively coupled plasma atomic emission spectroscopy (ICP-AES). Commun Soil Sci Plant Anal 25:407–418.
67.
Andresen E, Lyubenova L, Hubáček T, Bokhari SNH, Matoušková Š, Mijovilovich A, Rohovec J, Küpper H. 2020. Chronic exposure of soybean plants to nanomolar cadmium reveals specific additional high-affinity targets of cadmium toxicity. J Exp Bot 71:1628–1644.
68.
Strbkova L, Carson BB, Vincent T, Vesely P, Chmelik R. 2020. Automated interpretation of time-lapse quantitative phase image by machine learning to study cellular dynamics during epithelial–mesenchymal transition. J Biomed Opt 25:e086502.
69.
Decelle J, Not F. 2015. Acantharia. John Wiley & Sons, Hoboken, NJ.

Information & Contributors

Information

Published In

cover image mBio
mBio
Volume 14Number 128 February 2023
eLocator: e03279-22
Editor: L. David Sibley, Washington University School of Medicine
PubMed: 36645306

History

Received: 1 December 2022
Accepted: 5 December 2022
Published online: 16 January 2023

Keywords

  1. Euglenozoa
  2. barite
  3. biocrystallization
  4. biogeochemical cycles
  5. celestite

Contributors

Authors

Institute of Parasitology, Biology Centre, Czech Academy of Sciences, České Budějovice, Czech Republic
Faculty of Science, Charles University, Prague, Czech Republic
Institute of Physics, Faculty of Mathematics and Physics, Charles University, Prague, Czech Republic
Institute of Parasitology, Biology Centre, Czech Academy of Sciences, České Budějovice, Czech Republic
Institute of Parasitology, Biology Centre, Czech Academy of Sciences, České Budějovice, Czech Republic
Institute of Parasitology, Biology Centre, Czech Academy of Sciences, České Budějovice, Czech Republic
Faculty of Sciences, University of South Bohemia, České Budějovice, Czech Republic
Syed Nadeem Hussain Bokhari
Institute of Plant Molecular Biology, Biology Centre, Czech Academy of Sciences, České Budějovice, Czech Republic
Institute of Scientific Instruments, Czech Academy of Sciences, Brno, Czech Republic
Institute of Physics, Czech Academy of Sciences, Prague, Czech Republic
Faculty of Sciences, University of South Bohemia, České Budějovice, Czech Republic
Institute of Plant Molecular Biology, Biology Centre, Czech Academy of Sciences, České Budějovice, Czech Republic
Institute of Physics, Faculty of Mathematics and Physics, Charles University, Prague, Czech Republic
Institute of Parasitology, Biology Centre, Czech Academy of Sciences, České Budějovice, Czech Republic
Faculty of Sciences, University of South Bohemia, České Budějovice, Czech Republic

Editor

L. David Sibley
Editor
Washington University School of Medicine

Notes

Jana Pilátová and Daria Tashyreva contributed equally.
The authors declare no conflict of interest.

Metrics & Citations

Metrics

Note:

  • For recently published articles, the TOTAL download count will appear as zero until a new month starts.
  • There is a 3- to 4-day delay in article usage, so article usage will not appear immediately after publication.
  • Citation counts come from the Crossref Cited by service.

Citations

If you have the appropriate software installed, you can download article citation data to the citation manager of your choice. For an editable text file, please select Medlars format which will download as a .txt file. Simply select your manager software from the list below and click Download.

View Options

Figures and Media

Figures

Media

Tables

Share

Share

Share the article link

Share with email

Email a colleague

Share on social media

American Society for Microbiology ("ASM") is committed to maintaining your confidence and trust with respect to the information we collect from you on websites owned and operated by ASM ("ASM Web Sites") and other sources. This Privacy Policy sets forth the information we collect about you, how we use this information and the choices you have about how we use such information.
FIND OUT MORE about the privacy policy