1. Introduction
Phosphorus (P) is a major nutrient central to the processes of energy and information storage and exchange in cell [
1,
2,
3]. Most of the habitats accessible to microalgae are characterized by variable availability of P [
4,
5], but inorganic P species (referred to below as P
i) are usually present at limiting concentrations [
6,
7,
8]. To withstand prolonged P shortage, microalgae developed a set of adaptations collectively called “luxury uptake” [
6,
7]. The latter includes the capability of absorbing P
i in amounts much greater than their metabolic demand [
9]. Another set of mechanisms converting the newly acquired P
i into relatively metabolically inert polyphosphate (PolyP) and store it into the cell vacuole serve to avoid fatal displacement of the equilibria of vital metabolic reactions in which P
i participates [
1,
3].
Possibly as a side effect of these adaptations, microalgae became remarkably resilient to high levels of external P
i by far exceeding its environmental concentrations (1 g L
–1 and more [
10]). Some microalgal species found in P-polluted sites display very high P
i tolerance (see e.g. [
10]). It makes microalgae a powerful vehicle for biocapture of P from waste streams [
11] increasing thereby sustainability of using P resources which is currently notoriously low (< 20%) [
12]. Indeed, there are numerous reports on successful use of microalgae exerting luxury uptake of P [
13,
14] for biotreatment of waste streams to avoid eutrophication [
12,
15] and produce environmentally friendly biofertilizers [
16,
17].
From the practical view, microalgae-based approaches for P biocapture from waste streams offer advantages conventional techniques such as EPBR [
2,
18]. Using waste- and side-streams as P source for industrial cultivation of microalgae makes the bulk bioproducts such as P biofertilizers [
16,
19] or biofuels economically viable [
20]. Biomass of microalgae is a potential source of PolyP that can be used in medicine, for the development of biomaterials, and in food industry [
21,
22].
Despite the promise of microalgae-based P capture, its use is hindered by insufficient knowledge of luxury P uptake mechanisms [
1,
3] and the lack of strains resilient to high concentration of P
i since many algal species commonly used in biotechnology can be inhibited already at P
i concentration above 0.1–0.3 g L
–1 [
23,
24].
Nevertheless, there are reports on the toxicity of exogenic P
i to microalgae [
23,
24,
25] although the mechanisms of this phenomenon a far from being understood. Still, understanding of P toxicity is important e.g. for development of viable biotechnologies for the nutrient biocapture from P-rich waste streams and/or the highly nutrient-polluted sites. To further bridge this gap, we investigated failure of high P resilience in P-starved cultures. The
Micractinium simplicissimum strain IPPAS C-2056 recently isolated from a P-polluted site served as a model organism for this study. The cultures of the
M. simplicissimum grown in P-replete media exhibit a very high P
i-resilience [
10]. In our recent experiments on P starvation, we observed a sudden culture death upon replenishment of Pi to the P-depleted culture of the
M. simplicissimum. Here, we report on the effect of abrupt increase of the external P
i on the cell viability, P
i uptake, internal content of P and PolyP. We elaborate on possible mechanisms of P
i-induced death of microalgal cells acclimated to P deficiency. Special attention was paid to the potential role short-chain PolyP in these mechanisms.
3. Discussion
To the best of our knowledge, this is the first report on a failure of tolerance to a high external concentration of P
i in a microalga
Micractinium simplicissimum IPPAS C-2056 which was previously shown to be highly tolerant to this stressor [
10]. We attempted to link the actual level of tolerance to the state of acclimation of the microalga to different P availability in the medium. We also tried to infer a plausible hypothesis explaining these apparently controversial phenomena from the physiological and ultrastructural evidence collected during this study and backed up by the current knowledge of luxury P uptake and physiological role of PolyP in microalgal cells.
Importantly, the phenomenon of failed P
i tolerance was observed only in the situation when P-starved
M. simplicissimum culture was re-fed with P
i despite the fact that the concentration of the P
i added was far below the level potentially toxic to P-sufficient cultures of this microalga [
10]. The dramatic response of
M. simplicissimum to abrupt re-feeding with P
i was accompanied by a peculiar pattern of changes in distribution of P in the cells. There were other physiological manifestations (e.g., the variation in the photosynthetic apparatus condition) indicative of the acclimation state of the microalga. Overall, the acclimation of
M. simplicissimum to P shortage at the first phase of the experiment manifested the onset of mild stress similarly to that during diverse stresses documented in other microalgae such as
Chlorella vulgaris [
26] or
Lobosphaera incisa [
27,
28].
Specifically, a moderate reduction of the photosynthetic apparatus has been observed as reflected by a decline in chlorophyll (
Figure 2) and accumulation of carbon-rich reserve compounds (
Figure 5,
Figure A1 and
Figure A2) along with a depletion of P reserves in the cell. These rearrangements were accompanied with up-regulation of photoprotective mechanisms based on thermal dissipation of the observed light energy which is also typical of acclimation of microalgae to nutrient shortage [
26,
28,
29]. Nevertheless, the cells retained their structural integrity, and their photosynthetic apparatus remained functional despite clearly observed expansion of the thylakoid lumens. Interestingly, the cells of the P-starved culture which already ceased to divide possessed a sizeable amount of PolyP granules and a N-containing matter accumulated it their vacuoles similarly to that documented in other microalgae [
27,
30,
31]. These P reserves are obviously represented by a slowly mobilizable fraction of PolyP which frequently remains even in the P-starved cells [
7,
32].
After re-feeding of the P-starved culture of
M. simplicissimum with 800 mg L
–1 P
i, up to 20% of the added P
i was gradually removed from the medium by the cells by the 3
rd day of incubation (
Figure 3). Approximately 5% of the added P
i was reversibly adsorbed on the surface of the cells. DAPI staining revealed characteristic yellow fluorescence localized in the cell wall (
Figure 6). This observation is in line with the previously documented ability of this strain to adsorb P
i and form P-containing nanoparticles on its surface structures [
10]. This fining also corroborates previous reports on dynamic phosphorus depots in cell wall of diverse organisms including fungi, bacteria [
21,
33] and microalgae [
34]. As revealed by EDX spectroscopy, PolyP are characterized by co-localization with calcium, magnesium or (less frequently) potassium and sodium [
35,
36,
37]. In certain cases, we also observed the P peak in combination with that of uranium. Since the uranyl cation used for the sample preparation binds to phosphate, carboxyl, and sulfhydryl groups [
38], this can be a manifestation of phosphorylated proteins and nucleic acids in these cell compartments.
The amount of P internalized by the cells as well as the amount of intracellular PolyP also increased during the first four hours after re-feeding. Later, the amount of total intracellular P remained at the level of 4% of cell dry weight but the PolyP content started to decline. (Notably, the method of PolyP assay used here is optimized for long-chain PolyP, the internal PolyP content can be slightly underestimated since a part of short-chain PolyP can escape detection.) At the same time, the EDX spectral signature of PolyP was still detected in different part of the cells (
Figure 7 and
Table A1). Starting from 1 d of incubation, the progressive signs of cell rupture were recorded. Thus, a recovery of photosynthetic apparatus would be expected normally after P
i replenishment. Instead of this we observed a complete failure of photoprotective mechanisms indicative of acute damage to the cell similar to the effect of severe stress or a toxicant in a sublethal concentration [
39]. Confronting the observed effects with the reports on P
i toxicity found in the literature [
23,
40], we hypothesized that short-chain PolyP might be involved in the massive cell death observed in
M. simplicissimum after its re-feeding with P
i following P-starvation.
A possible scenario of the short-chain PolyP-mediated P
i toxicity might involve the following steps. First, the P-deprived microalgal cells deploy, as a common pattern of the nutrient shortage acclimation, the mechanisms making them capable of fast P
i uptake [
1,
6,
7,
26]. At the same time, their capability of photosynthesis becomes impaired because of the reduction of photosynthetic apparatus (see also
Figure 8). Upon re-feeding of the culture acclimated to P shortage, a large amount of P
i rapidly enters the cell. As a result, the biosynthesis of PolyP is triggered since PolyP serve as buffer for storage of P
i when it becomes available [
41,
42]. However, the cell acclimated to a nutrient shortage is, to a considerable extent, metabolically quiescent (in particular, its photosynthetic apparatus is down, and a large part of light energy it captures is dissipated into heat). At the same time, the biosynthesis of PolyP is very energy intensive, and this energy comes mostly from photosynthesis [
43]. As the net result, these processes trigger the mass accumulation of short-chain PolyP, but the newly formed PolyP cannot be further elongated due to metabolic restrictions mentioned above. Overall, the toxic effect of the short-chain PolyP rapidly accumulated in all compartments of the cell leads to its damage and, eventually, death which was the case under our experimental conditions.
It should be noted in addition that the barrier function of the cell wall regarding P
i uptake is an important determinant of the P
i resilience in
M. simplicissimum [
10]. P
i refeeding of the culture pre-starved of P triggers cell division and hence the increase in the proportion of young cells in the cell population whose cell wall can be less efficient a barrier to P
i uptake then cell wall of mature cells. This can render the young cells more vulnerable to the surge of P
i into the cell.
The hypothesis outlined above can explain the observed phenomenon of the failed P
i tolerance since the toxic effect of short-chain PolyP initially described in yeast cells [
40] was also implied in
Chlorella regularis [
23]. In these works, disorganization of cell structure has been proposed a major hallmark of elevated P
i toxicity mediated by PolyP. This hypothesis is also supported by the presence of genes encoding the PolyP polymerases from VTC family [
1,
2,
3] potentially involved in the synthesis of the short-chain PolyP [
39], in the genome of a closely related representative of the genus
Micractinium,
M. conductrix [
44]. A homologue of one of these genes was putatively discovered in our pilot studies of the species used in this work,
M. simplicissimum (in preparation).
It was also demonstrated recently that it is the PolyP that accumulates outside the cell vacuole is the main factor of PolyP-mediated toxicity of elevated external P
i [
25]. One can speculate that, mechanistically, the toxicity of extra-vacuolar short-chain PolyP can interfere with protein folding and/or matrix synthesis of biomolecules. This capability of interacting with important polymeric biomolecules is attributed to PolyP as a trait of this “molecular fossil” retained from ancient times when they were potentially involved in the genesis of life [
45].
Finally, we would like to underline the importance of understanding the limits of high tolerance of microalgae to elevated levels of external Pi not only for basic science, but from the practical standpoint as well. One should consider that abrupt changes of P availability can cause the normally high Pi tolerance of microalgae to fail and lead to a sudden culture crash. This is possible, particularly in the wastewater treatment facility during injection of a new portion of P-rich wastewater to P-depleted culture. Nevertheless, the toxic effects of Pi in microalgae remain quite underexplored, therefore further studies are in asset.
Author Contributions
Conceptualization, A.S. and O.G.; methodology, I.S., S.V. and L.S.; validation, O.G., and E.L.; formal analysis, P.S. and S.V.; investigation, I.S., L.S., O.C., K.S., O.B., O.G., P.S. and P.Z; writing—original draft preparation, A.S. and O.G.; writing—review and editing, A.S., E.L. and O.G.; visualization, O.G. and P.Z.; supervision, E.L.; project administration, A.S. and E.L.; funding acquisition, A.S, S.V. All authors have read and agreed to the published version of the manuscript.