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Review

Environmental Factors Modulate Saxitoxins (STXs) Production in Toxic Dinoflagellate Alexandrium: An Updated Review of STXs and Synthesis Gene Aspects

by
Quynh Thi Nhu Bui
1,†,
Biswajita Pradhan
2,3,†,
Han-Sol Kim
1 and
Jang-Seu Ki
1,2,*
1
Department of Life Science, Sangmyung University, Seoul 03016, Republic of Korea
2
Department of Biotechnology, Sangmyung University, Seoul 03016, Republic of Korea
3
Department of Botany, Model Degree College, Rayagada 765017, Odisha, India
*
Author to whom correspondence should be addressed.
†
These authors contributed equally to this work and share the first authorship.
Toxins 2024, 16(5), 210; https://doi.org/10.3390/toxins16050210
Submission received: 2 February 2024 / Revised: 23 April 2024 / Accepted: 28 April 2024 / Published: 30 April 2024
(This article belongs to the Section Marine and Freshwater Toxins)
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Abstract

:
The marine dinoflagellate Alexandrium is known to form harmful algal blooms (HABs) and produces saxitoxin (STX) and its derivatives (STXs) that cause paralytic shellfish poisoning (PSP) in humans. Cell growth and cellular metabolism are affected by environmental conditions, including nutrients, temperature, light, and the salinity of aquatic systems. Abiotic factors not only engage in photosynthesis, but also modulate the production of toxic secondary metabolites, such as STXs, in dinoflagellates. STXs production is influenced by a variety of abiotic factors; however, the relationship between the regulation of these abiotic variables and STXs accumulation seems not to be consistent, and sometimes it is controversial. Few studies have suggested that abiotic factors may influence toxicity and STXs-biosynthesis gene (sxt) regulation in toxic Alexandrium, particularly in A. catenella, A. minutum, and A. pacificum. Hence, in this review, we focused on STXs production in toxic Alexandrium with respect to the major abiotic factors, such as temperature, salinity, nutrients, and light intensity. This review informs future research on more sxt genes involved in STXs production in relation to the abiotic factors in toxic dinoflagellates.
Keywords:
Alexandrium; saxitoxin; temperature; salinity; nutrients; light intensity; STX synthesis gene (sxt)
Key Contribution: Environmental factors modulate the production of saxitoxin (STX) and its derivatives (STXs) in the marine dinoflagellates Alexandrium. Macro- and micro-nutrients also play a critical role in the production of STXs in Alexandrium. Environmental factors affect STXs production via the regulation of STX-biosynthesis genes sxtA4 and sxtG. STX synthesis play a crucial role in the adaptation mechanism of Alexandrium.

1. Introduction

Photosynthetic organisms occur in vast quantities in aquatic environments, and they are mostly known as phytoplankton. Not just in freshwater environments, but also in marine ecosystems, phytoplankton play an important role as primary producers [1,2,3,4,5,6]. The organisms are very diverse, varying from photosynthesizing bacteria to plant-like eukaryotic algae. They are classified by pigments and important groups that include diatoms, dinoflagellates, and green algae, although many other groups are represented [7].
Dinoflagellates are a wide category of unicellular microeukaryotes, and half of them are photosynthetic [8]. Thus, they play a crucial role in primary production and coral reef formation in aquatic environments [1,8,9]. They could be a new source of bioactive secondary metabolites, including toxins such as amphidinolides, amphidinol, azaspiracid, ceramide, spirolides, and symbioramide [10,11]. Some dinoflagellates, however, are the main cause of harmful algal blooms (HABs) and produce poisonous substances [12]. The most damaging dinoflagellate toxins are saxitoxin (STX) and its derivatives (STXs), brevetoxins (BTXs), maitotoxins (MTXs), ciguatoxins (CTXs), pinnatoxins (PnTXs), palytoxins (PLTXs), yessotoxins, zooxanthellatoxins, dinophysistoxins, karlotoxins, azaspiracids (AZAs), okadaic acid, and domoic acid [12]. The molecular structures of their representative toxins are displayed in Figure 1.
Among those toxic compounds, STXs, also known as paralytic shellfish toxins (PSTs), are neurotoxic alkaloids naturally produced by certain marine dinoflagellates [13]. PSTs block voltage-gated sodium channels of neurons in a reversible manner, inducing paralysis, and such STXs are 2000-times more lethal than sodium cyanide by weight [14]. They are classified into several subgroups based on their chemical structure, such as carbamoyl derivatives (STXs, neosaxitoxin (neoSTX), gonyautoxins1–4 (GTX1–4), N-sulphocarbamoyl derivatives (GTX5–6 and C1–4), dicarbamoyl derivatives [dicarbamoyl-STX (dcSTX), dicarbamoyl neosaxitoxin (dcneoSTX), and dicarbamoyl gonyautoxins 1–4 (dcGTX1–4)], and other less-frequent deoxy-decarbonylated, mono-hydroxy-benzoate, di-hydroxy benzoate, and sulphated benzoate analogs [15]. Each compound has a different toxicity and is quantified using the toxicity effect factor (TEF) [16].
In a marine environment, STXs are naturally produced by Alexandrium spp., Gymnodinium catenatum, and Pyrodinium bahamense [17,18,19]. Among them, Alexandrium distribute in coastal waters and/or estuary environments, and more than 34 species of the genus have been morphologically identified to date [20,21,22]. Specifically, Alexandrium catenella, Alexandrium pacificum, and Alexandrium minutum are major species causing environmental and industrial damage due to PSTs [23]. Under ideal growth circumstances, some Alexandrium grow quickly, generating HABs [13].
HABs of toxic Alexandrium can cause paralytic shellfish poisoning (PSP), which can result in illness or mortality in humans via the ingestion of contaminated seafoods [24]. Firstly, shellfish filter-feed toxic dinoflagellates, then the toxins accumulate in the glands of shellfish. In addition, the toxins can be transferred to a variety of marine life, including crabs, starfish, mollusks, turtles, fish, octopus, marine mammals, and seabirds, via bioaccumulation [25]. Therefore, the outbreak of toxic dinoflagellates, especially Alexandrium, is a key factor influencing the safety of marine organisms and seafood.
Previous studies, including environmental and laboratory, have showed that the proliferation of toxic Alexandrium and their STXs production are affected by environmental factors, such as light intensity, temperature, carbon dioxide (CO2), salinity, and nutrition [23,26]. Figure 2 represents a schematic view of how major environmental factors affect cell physiology and STXs synthesis in toxic Alexandrium. Specifically, water temperature may be more important than nutrients or salinity in determining the abundance of A. catenella and the generation of STXs [20]. Environmental investigations and laboratory research imply that temperature may alter the production of STXs in toxic Alexandrium, despite the fact that this is contentious [27]. The dynamics of the abiotic variables that drive cell growth and photosynthesis, such as high inorganic nutrient concentrations, optimum temperatures, and light conditions, are not always linked to Alexandrium proliferation [28]. Moreover, it is also unclear that STX production is caused by changes in cellular biomass [29].
Toxic Alexandrium species are one of the best model organisms for studying STX production, due to their toxicity, wide distribution, and negative impacts on marine habitats. Understanding how environmental conditions influence genetic traits and STXs production in Alexandrium is critical [30]. Therefore, this review focused on environmental factors that modulate STXs production by influencing the growth as well as metabolism of STX metabolites and related STX synthesis genes (sxt) in toxic Alexandrium. In addition, this work will review the insights into STXs production, focusing on the role of several gene complexes in Alexandrium.

2. Environmental Factors Trigger STXs Production via Altering Growth, Physiology, and Genetic Modulation

Environmental variables, such as nutrients, salinity, temperature, and light intensity, influence the growth of Alexandrium cells, of which factors somehow affect STXs production [30,31]. For example, A. minutum has a substantially greater cellular toxin capacity when grown in phosphate (PO4)-depleted conditions [32]. In addition, temperature and light had effects on the cell growth of Alexandrium, and modulated its cellular toxicity [31,33]. The overall production of STXs in relation to environmental factors via altering the growth, physiology, and involvement of genes is detailed below.

2.1. Nutrients Modulate the Production of STXs

In terms of nutrition, Alexandrium is an opportunistic genus, but one should not expect it to have simple links with conventional nutrients. For instance, A. catenella may thrive in both relatively pure and nutrient-rich environments, as well as in waterways that have experienced nutrient abatement [34]. On the contrary, certain concentrations of nutrients, such as carbon (C), nitrogen (N), phosphorus (P), trace metals, and vitamins, also disturb STXs synthesis by Alexandrium. Consequently, it is difficult to generalize the nutritional role in Alexandrium and its nutrient-dependent mechanisms in relation to HAB formation and PST production. Although the detailed metabolisms are still unknown, nutrient conditions leading to the optimal growth of Alexandrium are suspected to influence SXT production. Table 1 summarizes the nutrient conditions for maximum PST production in the genus Alexandrium and its toxicity levels.

2.1.1. Carbon (C)

Alexandrium species consume dissolved organic carbon (DOC) and dissolved inorganic carbon (DIC) and create oxygen similar to other autotrophs; however, maintenance respiration rates are higher in Alexandrium species compared to other phytoplankton genera, such as diatom Skeletonema costatum and Ochrophyta Olisthodiscus luteus [35]. Interestingly, Alexandrium appears to excrete very little DOC, although DIC loss due to respiration is likely to be significant [36]. Depending on the nutritional and physiological state of cells, C fixation seems to be predominantly affected by N availability in Alexandrium tamarense [37]. The uncoupling of C and N metabolism is also observed in cultures, with significant increases in C/N ratios following N exhaustion in a time scale of 10 to 17 days [38]. As C is required for Alexandrium’s growth and development, it may modulate STXs production. The C-C bond is important for the STXs synthetic process [39]. On the other hand, anthropogenic activities have contributed to the increase in the atmospheric partial pressure of CO2 (pCO2) altering the dynamics of DIC and changing oceans’ carbonate chemistry [40,41,42]. These factors may affect phytoplankton, which convert inorganic C into organic and secondary metabolites. Previously, Van de Waal et al. (2014) reported that pCO2 did not significantly affect the growth and elemental composition of A. tamarense; however, increased pCO2 reduced PST content [43]. As a result, increased pCO2 shifted the PST composition toward more sulfated analogs, thus possibly reducing the cellular toxicity of A. tamarense [43]. To date, the toxicity of Alexandrium under C-rich or -low environments is still not clear. Hence, further research should be carried out in order to understand STXs production and the genes involved in STXs production in C-rich or -low environments.
Table 1. Toxin production in the genus Alexandrium under varying nutrient conditions. Saxitoxins equivalent (STXs eq) values were are rounded up to a single digit.
Table 1. Toxin production in the genus Alexandrium under varying nutrient conditions. Saxitoxins equivalent (STXs eq) values were are rounded up to a single digit.
SpeciesStrainNutrient
Source		Condition Range (µM/L)Highest STXs Condition
(µM/L)		ToxinsSTXs eq (fmol/cell)Reference
A. tamarensePr18bNO30–880880STX, neoSTX, GTX1–4, C1–325–49[44]
CI01NO30–880880C210–60[45]
CI01PO45–405C220–76
A. minutum-PO413–9113STX, GTX1–410–27[32]
-NH440–15015029–31
-NO35–496496STX, GTX2, GTX1,46–80[46]
-NH43–23023010–19
A. pacificumHYM9704NO350–500-neoSTX, GTX1/3, C1–215–74[47]
PO41–50-68–121
A. catenellaAC11Fe0–101GTX1–410–89[48]

2.1.2. Nitrogen (N)

N resources are essential ingredients used to generate nucleic acids, proteins, and other cell components for Alexandrium growth and survival [44]. The N/P ratio is also one of the important factors that affects cell size and biovolume. For example, an increase in the N/P ratio (P-limitation) resulted in an increase in the cell sizes of A. minutum [44] and Alexandrium fundyense [49]. Perhaps, the increase in cell biovolume is induced by arresting cells in the G1 phase without undergoing cell division [50,51], while other non-P compounds are synthesized. Laboratory culture studies have evaluated Alexandrium’s growth charges influenced by nitrate (NO3), ammonium (NH4), and urea availability [52,53,54,55,56].
Particularly, NH4 contributed a higher N source than NO3 for the growth requirements of A. catenella, while the differences were not always significant [52]. Alexandrium consumes urea and utilizes it to support both cellular physiological and molecular processes in both laboratory and environmental conditions [57]. Growth rate with the supplementation of urea may be lower than that with an NO3 or NH4 supply. On the other hand, a previous study reported that strains of A. catenella and A. fundyense did not grow under the condition where urea was supplied as the sole N-source [58]. According to John and Flynn [49], amino-N cannot be used to support the significant growth of A. fundyense. Variations in N-dependent growth between strains must be reduced since N availability and their compositions were not always effectively regulated.

Total Dissolved Organic Nitrogen (DON)

The effects of dissolved organic nitrogen (DON; >1 kDa) originated from riverine on A. tamarense growth in f/2 medium were not significant, despite the fact that chlorophyll contents dropped as the riverine DON level rose [59]. On the other hand, riverine high-molecular-weight (10–100 kDa) DON could benefit A. minutum [60]. Similarly, the synergism effects of DON and NO3 boosted the growth rate of A. catenella by 34% when compared to growth on NO3 alone [61]. However, the increased growth rate was not due to NH4, suggesting that DON was used directly [61]. Furthermore, in semi-continuous cultures, the effects of marine autotrophic-dissolved organic matter (DOM) on A. catenella growth were found to be favorable [61].

Nitrate (NO3)

Diverse studies have suggested that Alexandrium has a linear kinetics of N uptake during NO3 assimilation and varies its toxin production [45,62]. The highest toxin content (53.6 fmol/cell) of A. pacificum was observed in the NO3 replete (1.76 mM) condition [63]. Particularly, an increase in NO3 supply continued to increase the toxin yield in A. tamarense [45]. The effect of low NO3 (88.2 µM NaNO3) supplementation on cell biomass and toxin content increased cell density and toxin content by 20–76%, and the toxin value was 43,600 cells/mL [45]. The results show that adding NO3 to the cultures at various stages of growth increases the toxin yield by 46% on average [45]. However, continuous low-level NO3 supplementation may contribute to an effective increase in A. tamarense toxin yield [64]. The NO3 absorption systems of A. catenella and A. minutum have been found to be extremely sensitive to NH4 inhibition [65].

Ammonium (NH4)

NH4 was discovered to block the urea absorption mechanism in A. catenella, but this effect appeared to be strain-dependent [56]. Alexandrium species are observed to have unusually high internal levels of arginine and glutamine, which could be precursors to STXs, in different growth periods [66]. In addition, NH4 values of 40–150 and 3.0–230 µM/L trigger the production of STXs by 29.2–31.8 and 10–19 fmol/cell in A. minutum, respectively [32,46]. At a concentration of 100 µM NH4, substrate absorption was inhibited in some A. tamarense species [37]. Intra-specific variations in uptake and assimilation kinetics are also significant [62,67]. In addition, NO3 triggers the formation of C2 (10–60 fmol/cell) in A. tamarense [45]. Despite the extensive research into Alexandrium toxicity and toxin-producing activity in N-rich and -deficient settings, the relationship of N and SXTs production cannot be clarified yet, and the results are not consistent and are sometimes controversial. Therefore, further research should be conducted to better understand STXs production and the genes implicated in STXs production in N-rich or -deficient environments.

Soil and Bacteria Extracts

The precise mineral or nutrient presence in culture media is required, and soil extracts may help to limit N losses from culture media. In this regard, early research on Alexandrium sp. showed that soil extract could boost the growth process compared to completely inorganic media [68]. In addition, soil extracts initiate rapid cell division and promote the rapid growth of the dinoflagellate P. bahamense [69]. Humic substances, which result from the biochemical transformation of plant or animal tissues in sediments, have been found to stimulate the growth of Alexandrium in a variety of media [68]. Similarly, humic additives considerably increased A. tamarense growth rates compared to the controls [70]. Moreover, the addition of humic compounds of riverine origin to an NO3-limited medium increased the growth rate of A. catenella [71]. However, humic compounds in equimolar concentrations might replace NO3 as an N source, while allowing the same species to thrive at equal rates [72].

2.1.3. Phosphorus (P)

Organic P, such as adenosine triphosphate, glycerophosphate, and guanosine diphosphate, can boost the growth rate of some Alexandrium species; inorganic P is usually regarded the principal nutrient for Alexandrium [58]. Low-molecular-weight organic P appears to be hydrolyzed into inorganic PO4 before being used for A. tamarense growth [73]. Few studies have looked into inorganic P absorption in Alexandrium [74]. In A. catenella, the half-saturation of the STXs production of Alexandrium constants ranged from 0.01 to 2.6 mM and were shown to be proportional to the growth rate [75]. There have been no reports on multiphasic kinetics, but the concentration range that has been investigated thus far is relatively limited. However, Alexandrium appears to be a “storage specialist,” as it can store PO4 for future use during periods of P deficiency [76]. A wide range of PO4 concentrations resulted in 20.0–76.0 STXs equivalent (STXs eq) fmol/cell of PST in A. tamarense, while A. minutum produced 10.0–27.5 STXs eq fmol/cell [32]. Furthermore, 1–50 µM/L of PO4 increased the STXs production of A. pacificum within 24 h and then decreased [47]. N-stress alone resulted in a decrease in toxin per cell, but N-stress followed by P-stress did not, implying that P is involved in the regulation of toxin metabolism [77]. Despite the fact that few investigations on the toxicity and toxin-producing activities of Alexandrium in P-rich or -deficient environments have been performed effectively, further research is still necessary to understand STX production and the genes involved in P-rich or -deficient environments.

2.1.4. Miscellaneous

Trace metals, such as selenium, nickel, copper (Cu), cobalt, molybdenum, iron (Fe), manganese, and zinc, are required for algal growth, and they may modulate STXs production in toxic Alexandrium [78]. Among those, Fe is the most critical element in dinoflagellate metabolism, including chlorophyll production, electron transport, photosynthesis, and N assimilation [79,80,81]. Specifically, Alexandrium has a high Fe requirement for its growth and development. The effect of Fe deficiency on A. tamarense, for example, reduced the growth rate and chlorophyll a concentration by approximately half [80]. On the other hand, a high concentration of Fe reduced the total toxicity levels to 10.4 fmol/cell (10 µM) compared to 33.6 fmol/cell (1 µM) [80]. This suggests that Fe influences the particular growth rate, cellular biochemical composition, and the synthesis of the toxins in the dinoflagellate Alexandrium [48]. In addition, Cu induced toxin production via modulating the growth rate and photosynthetic activity concentration dependently in dinoflagellate A. minutum [82]. In addition, metals alter soluble proteomes and toxin profiles in Alexandrium pacificum by inhibiting the photosynthetic proteins [78]. Under metal as well as heavy metal stress circumstances, metals modified the STXs profile and soluble proteomes in A. pacificum, and such adaptive proteomic responses are related to the development of metal-contaminated ecosystems [78]. However, further studies are required to establish whether trace metals trigger STXs production in toxic Alexandrium via modulating the growth.

2.2. Temperature: The Most Decisive Factor for STXs Production in Alexandrium

Similar to nutrient conditions, water temperature is a critical environmental factor that affects cell growth and STXs production in both PST-producing cyanobacteria and dinoflagellates [26,29,31,83]. Numerous studies have shown that Alexandrium species have different optimal growth temperatures, and even the strains of the same species have varied growth rates and STXs toxicity under identical temperature conditions (Table 2). Overall, a high STXs content was observed during the exponential period under optimal growth conditions [6]. Interestingly, STX synthesis is considerably linked to the growth rate of the species, especially the exponential phase, and therefore, the highest PST levels were mainly analyzed at optimal growth temperatures [26,31,84]. Alexandrium tamarense, for example, displayed values in the range of 1.4–2.7 STXs eq fmol/cell and 42.3 STXs eq fmol/cell when cultured at 17 °C and 15 °C, respectively [85,86]. Temperature influences the STXs profile of A. catenella, modulating C1 to GTX4 when increasing the temperature from 12 °C to 18–30 °C [87]. Additionally, at 12 °C, C2 dominated at almost all salinities except at 35 and 40 psu, which convert to C3 and C4 [87]. For examples, Ogata et al. (1987) reported that PST production in A. tamarense increased with a decrease in growth rates (8 °C), while the increased toxicity at (16 °C) was less noticeable [84]. Similarly, a maximum STXs content was observed at the lowest temperature of 12 °C with moderate growth rates [85]. Also, STXs production in A. catenella Alex03 and A. pacificum Alex05 significantly increased under cold stress, while it decreased under heat stress [26].
In addition, it was confirmed that not only the total toxicity, but also the composition of the STX analogs, was changed, and the cellular PST levels increased due to an increase in the proportion of toxic compounds with a high TEF [16]. For example, A. catenella ACT03 showed a dominance of the C2 toxin when grown at 12–18 °C, while GTX5 became dominant at temperatures in the range of 21–30 °C [87]. Similarly, A. catenella Alex03 also mainly produced GTX1 in a range of temperatures (12, 16, and 20 °C), and especially, the absolute concentration of GTX1 (75.4 STXs eq fmol/cell) increased at an optimal growth temperature (16 °C; 86.4 fmol/cell), resulting in about a 4-fold increase in total STXs eq compared to 20 °C [26]. Like A. pacificum Alex05, GTX3 and GTX4 were predominantly synthesized at 12, 16, and 20 °C, and the STXs eq considerably increased at 16 °C (64.0 fmol/cell) [31]. Even field surveys showed that total STX levels in scallops contaminated by A. tamarense occurred at low temperatures were higher than those at a high temperature [85]. All the results indicate that STXs synthesis is directly affected by temperature and its related processes in Alexandrium.

2.3. Salinity Modulates STXs Production in Alexandrium

In the aquatic ecosystem, salinity plays a vital role in controlling organisms’ physiological activities and metabolic processes [95]. Salinity impacts ion concentration or osmotic regulation, which leads to a change in cell size in dinoflagellates [96]. In addition, it also enables the control of intracellular and extracellular enzymes to achieve a stable environment for optimal metabolic activities [97]. Several studies have suggested that Alexandrium has species-specific salinity tolerance depending on the geographical origins. For example, Malaysian A. minutum displayed high salinity tolerance (5–30 psu) [98], but A. tamiyavanichii and A. tamarense flourished in a 20–30 psu salinity range [99]. According to Bui et al. (2021), the optimal salinity for A. pacificum isolated in Korea was recorded in the range of 30 and 35 psu [30], whereas A. insuetum showed maximal growth at 25 psu [100]. These show that different salinity tolerance ranges enable the strain to survive under salinity gradient conditions with different growth patterns [101]. Thus, the effects of salinity on STXs synthesis also varied by research cases, depending on the toxin-producing species and strains [99,102]. Thus, it is still controversial whether low-salinity stress or optimal-salinity conditions have a significant correlation with STXs production in Alexandrium [87].
The average salinity of marine environments is 33 psu, and diverse laboratory studies have reported that the optimal growth salinity of Alexandrium spp. is 25–35 psu. Previous studies also reported that Alexandrium tended to produce the highest toxic content under optimal salinity conditions. For example, four different strains of A. catenella produced the highest toxin levels ranging from 14.8 to 238.9 STXs eq fmol/cell at 35 psu [102]. Similarly, A. tamiyavanichii also peaked in PST contents with optimal growth rates under salinity of 20 and 25 psu [99]. In the case of A. pacificum, the highest STXs eq (35.8 fmol/cell) was measured under the optimal condition of 30 psu [98]. Parkhill and Cembella [44] also report that there is a positive correlation between the salinity-dependent growth rate and cellular toxicity of Alexandrium, indicating that the PST quota is affected by salinity, like other environmental factors.
Contrary to the above results, A. minutum AmKB06 produced the highest toxin levels (12.0 fmol/cell) at 5 psu, even the optimal growth salinity rates were 15 and 30 psu [99]. In an environmental survey, the PST content of A. minutum AM89BM, which occurs in the coast of Brittany (France), was low (10.0 fmol/cell), under 30 to 37 psu, while up to 50.0 fmol/cell was monitored at 15 psu [103]. In contrast, no significant changes in the toxin content were observed when A. fundyense experienced short-term exposure to higher and lower salinities [66]. Considering these results, this is still controversial due to the complex relationship between the growth rate, cellular toxin profile, and salinity [84,87].
Apart from total toxicity, salinity also alters the STXs profiles of Alexandrium. For example, A. pacificum mainly produces GTX4 and C2 at 25–40 psu, while GTX3 is only detected at 20 psu [30]. Hwang and Lu (2000) report that low salinity stimulates A. minutum to produce higher amounts of GTX1, while high salinity leads cells to synthesize higher amounts of GTX2–3 [104]. In the case of A. catenella, total cellular STXs levels in response to salinity changes were related to changes in C2, GTX4, and GTX5 toxins [87]. In addition, the toxin composition of GTX2+3 was decreased in A. minutum with the increase in salinity conditions, and at early and late exponential phases [99]. From these experimental results, we found that the STXs composition of Alexandrium changed depending on the salinity conditions and growth stage. Table 3 summarizes the optimal growth conditions and toxin production in the genus Alexandrium under different salinity conditions from the published literature.
Variations in membrane transport routes are one of the initial cell reactions to salinity changes, causing metabolic functions to be modified [95]. Extreme salinity conditions may limit the production of STXs by altering arginine synthesis, the primary precursor of STX biosynthesis [98]. It consequently decreases the activity of ornithine, glutamine, arginine, and carbamoyl phosphate synthesis metabolism [105]. To date, the toxin-producing activity of Alexandrium in various salt environments is still unclear; hence, more research should be carried out to understand STXs production in toxic dinoflagellates.
Table 3. Optimal growth conditions and saxitoxins (STXs) production in the genus Alexandrium under different salinity conditions from the published literature. STXs equivalent (STXs eq) values are rounded up to a single digit.
Table 3. Optimal growth conditions and saxitoxins (STXs) production in the genus Alexandrium under different salinity conditions from the published literature. STXs equivalent (STXs eq) values are rounded up to a single digit.
SpeciesStrainOriginSalinity RangeOptimal Growth SalinityHighest STXs ConditionToxinsSTXs eq (fmol/cell)Reference
A. catenellaPFB38Chile15–353535neoSTX, GTX1–595[102]
ACT03Mediterranean Sea10–403035C1–4, GTX3–550[87]
A. fundyenseMIUSA15–352530STX, neoSTX, GTX1–462[91]
BoFUSA15–352530–35STX, neoSTX, GTX1–473–75
A. minutumAM89BMFrance12–3720–3715-50[103]
AmKB06Malaysia2–30155GTX1–6, C2, neoSTX, dcSTX12[99]
Alexsp17Vietnam5–3510–1530–35STX, neoSTX, dcSTX, C2, GTX2–430[98]
A. ostenfeldiiAOSH1Canada15–333315C3 −[33]
OKNL21Netherlands3–34225STX, GTX2/3/5, C1–252[106]
A. peruvianumApKS01Malaysia2–302525GTX1–6, C2, neoSTX, dcSTX0.8[99]
A. pacificumAlex05Republic of Korea20–403030neoSTX, dcSTX, dcGTX2, STX, GTX1–6, C1–236[30]
A. tamarensePr18bCanada10–302525STX, neoSTX, GTX1–4, C1–3179[44]
AtPA01Malaysia2–3020–3015GTX1–6, C2, neoSTX, dcSTX0.8[99]
A. tamiyavanichiiAcMS01Malaysia2–302520GTX1–6, C2, neoSTX, dcSTX80[99]

2.4. Light Intensity: The Crucial Factor for the Growth of Alexandrium and STXs Production

Until now, STXs have been identified as being produced by photosynthetic cyanobacterium, such as Dolichospermum spp., Raphidiopsis raciborskii, and dinoflagellates, like Alexandrium spp. and G. catenatum [107]. Thus, the direct and indirect effects of light on STXs production are considerable and complex. Previous studies have already shown that photosynthetic activity affects STXs synthesis [44,84]. In detail, STXs biosynthesis requires the use of additional C skeletons produced during photosynthesis, such as amino acids and acetate, as well as high-energy light intermediates, such as ATP and NADH/NADPH [108]. Such amino acids are produced during short periods of photo-assimilation [109], and this also requires incorporated NO3 [110,111]. Therefore, the decrease in light intensity can suppress the fresh synthesis of amino acids and N assimilation [84], affecting growth and varied metabolisms, including the production of secondary metabolites.
Photo-assimilation plays an important role in the production of toxins by the dinoflagellate A. tamarense [84]. The photo-assimilation of NO3 or ammonia (NH3) into amino acid precursors may be related to the production of STXs requiring abundant N sources [63,84]. In this regard, the intensity of light controls Alexandrium growth rate and STXs synthesis, where lowering the intensity of light increases the toxicity, while decreasing growth increases and vice versa [84]. Contrary to this, Parkhill and Cembella [44] reported that changes in PST levels were largely independent of light, but depended on the growth stages, suggesting that light did not provide a direct response to STXs synthesis. Various other studies have found that Alexandrium species respond differently to the increase or decrease in PST levels depending on light strength [85,91,92,104]. Table 4 summarizes the optimal growth conditions and toxin production in the genus Alexandrium under different light intensities from the published literature.
The amount of light passing through water and its spectral quality are both important factors for determining the photosynthetic rate of dinoflagellates [112]. Since water selectively absorbs and scatters white light, the intensity and spectrum quality of light vary significantly depending on its turbidity and depth. Several dinoflagellates have a meroplanktonic life cycle and migrate vertically from nutrient-depleted and light-rich surface water to dark but nutrient-rich water, facing varied light intensities and spectral-light characteristics [113]. Their plastids are unique among photosynthetic alveolates, since they contain the light-harvesting system based on peridinin–chlorophyll–protein (PCP) [114]. When irradiance is inhibited, dinoflagellate Glenodinium sp. increases photon capture and maintains photosynthetic efficiency by increasing the pigment molecules linked to the reaction centers in chloroplasts [115]. As such, the quality of light affects the algal photosynthesis rate, which is very important since it affects cellular metabolism, such as pigment composition, nutrient and C uptake, and even toxin synthesis [116].
Many studies have reported that light intensity and spectrum quality have a significant effect on the synthesis of various toxins and secondary metabolites of microalgae [117,118]. In the case of toxic dinoflagellates, especially Alexandrium spp., STXs production is also influenced by light quality. For example, A. tamarense displayed the highest toxin production at 150 μmol photons/m2/s and the amount was 0.93–5.9 fmol/cell [44]. The toxins (neoSTX, GTX1–6, and C1–2) produced in A. catenella at 100 μmol photons/m2/s are recorded at 150–350 STXs eq fmol/cell [119]. Additionally, A. catenella ACT03 produced toxins like GTX3–5, C2/4 in a range of 13.7–24.7 STXs eq fmol/cell at 260 μmol photons/m2/s [87]. Moreover, in A. fundyense, the highest toxin production rates were 20–100 and 60–150 STXs eq fmol/cell at 175 and 425 μmol photons/m2/s, respectively [91]. In addition, A. tamiyavanichii produced 60.0–180.0 fmol STXs eq/cell (STX, GTX1–5, C2, dcSTX) at light range of 10–100 μmol photons/m2/s [92]. In addition, A. minutum displayed GTX1, GTX4 production values of 10–42 fmol/cell at a light range of 10–100 μmol photons/m2/s [92]. At 100 μmol photons/m2/s, A. pacificum produced 800–1400 STXs eq fmol/cell, and this is the maximum production of STX [119]. Overall, these findings show that light plays a crucial role in algal growth and cellular metabolism, thereby affecting PST production in Alexandrium.
Table 4. Optimal growth conditions and saxitoxins (STXs) production in the genus Alexandrium under different irradiance conditions from the published literature. STXs equivalent (STXs eq) values are rounded up to a single digit.
Table 4. Optimal growth conditions and saxitoxins (STXs) production in the genus Alexandrium under different irradiance conditions from the published literature. STXs equivalent (STXs eq) values are rounded up to a single digit.
SpeciesStrainLight Range
(μmol Photons/m2/s)		Optimal Growth ConditionHighest STXs ConditionToxinsSTXs eq (fmol/cell)Reference
A. tamarensePr18b40–470230 150STX, neoSTX, GTX1–4, C1–30.9–6[44]
A. catenellaACT0310–260−260GTX3–5, C2/414–25[87]
KNU-YS-0110–300300100neoSTX, GTX1–6, C1–2150–350[119]
A. fundyenseMI6–425425175STX, neoSTX, GTX1–420–100[91]
BoF6–425425425STX, neoSTX, GTX1–460–150
A. tamiyavanichiiAcMS0110–100100>50STX, GTX1–5, C2, dcSTX60–180[92]
A. minutumAmKB0210–100100>24GTX1/410–42[92]
A. pacificumLIMS-PS-279210–300200100GTX1–6, C1–2, dcGTX2–3800–1400[119]

3. Adaptation Mechanism of Alexandrium in Response to Environmental Conditions

Organisms respond differently to different environmental drivers, mostly as a result of metabolic disruptions [120]. Moreover, it can be expected that different stressors affect the metabolic pathways responsible for the production of various toxin groups [120]. Despite intensive efforts to understand the effects of environmental conditions on STX synthesis in diverse Alexandrium species, it still remains difficult to predict how these harmful dinoflagellates will respond to abiotic factors and result in toxicity changes. Moreover, reports on the factor interactions of multiple environmental conditions often contradict each other, and thus form a complex picture that is difficult to explain [13]. Other reports on the STXs production of Alexandrium in relation to such abiotic factors also highlight this problem [23,94]. As described previously, several abiotic factors obviously affect Alexandrium growth and its toxicity. As well as abiotic factors, genetic factors, like phenotypic variability, have long been recognized in phytoplankton, and have recently become the focus of significant research in the genus Alexandrium [23]. Molecular research has revealed that Alexandrium populations have a lot of genetic variations [23,121]. Such variations are expected to represent the adaptation of the population to environmental and climate changes [122]. Climate factors control the diversity within a particular species, and each population has different preferred temperature, salinity, pCO2, and nutrient conditions [123]. For all parameters, significant effects of genotype on the response to temperature and salinity changes were identified [124]. For example, experiments testing the responses of varied strains under predicted changes in environmental conditions by the end of the century have been performed to better characterize the consequences of potential genotype shifts in relation to climate change in the future [123]. These findings suggest that the adaptation to abiotic factors is aided by altering the genetic variation.

4. Genetic Understanding of Environmental Factors and STXs Biosynthesis sxt Genes

STX is biochemically synthesized by the stepwise involvement of eight core enzymes following catalytic reactions, as seen in Figure 3 [125,126]. The biochemical studies of PSTs started with STX, which was first isolated from the Alaskan butter clam Saxidomus giganteus in 1957 [127]. Additionally, the structure of STX was also discovered in the 1980s in a PST-producing cyanobacterium, R. raciborskii T3, and the candidate gene (sxt) cluster for the PST biosynthesis pathway was identified. Twenty-six proteins grouped in a single 35 kb cluster have 30 catalytic functions [125,126]. Among these, eight enzymes (sxtA, sxtB, sxtD, sxtG, sxtS, sxtH/T, sxtU, and sxtI) are directly involved in STX synthesis in cyanobacteria [125,126,128,129]. Moreover, genes participating in the tailoring, regulation, and transportation of STXs are involved in synthesizing various PST analogs [130,131,132,133]. Similarly, toxic dinoflagellates have sxt gene homologs to cyanobacteria [12,134,135,136].
Among the genes, sxtA is known to be involved in the initial stage of STX synthesis and is the most widely studied [140]. Cyanobacterial sxtA includes the N-terminal and C-terminal, while dinoflagellate sxtA contains four catalytic domains (sxtA1, sxtA2, sxtA3, and sxtA4) [128]. The single mRNA candidate of sxtA was found in cyanobacteria, while more than two sxtA isoforms were found in toxic dinoflagellates A. fundyense, A. minutum, A. catenella, and A. pacificum through RNA-sequencing analysis [141,142]. These consist of “sxtA short form” that encodes three catalytic domains (sxtA1–3) and a “sxtA long form” that encodes four catalytic domains (sxtA1–4) [141]. A recent study revealed that sxtA1–3 domains were stably present in bacteria, cyanobacteria, and dinoflagellates, but the sxtA long form was only found in STX-producing cyanobacteria and dinoflagellates [107,135]. Through various molecular studies, sxtA4 was identified in various toxic dinoflagellates, including Alexandrium spp., G. catenatum, and P. bahamense. Furthermore, it was suggested that the presence of sxtA4 and its copy number have a significant relationship with STX synthesis [9,134].
Further genetic studies were also conducted focusing on the secondary core sxtG gene, which catalyzes the incorporation of the amidino group from the product of sxtA in the STX synthesis process [141,143]. Similar to sxtA, the loss and/or modification of the gene results in the breakdown of the initial reaction in STX production, and it may lead to a loss of the ability of toxin production in both cyanobacteria and dinoflagellates [144]. In addition to this, the existence and mutation of other sxt genes were also linked to PST production [31,144]. As a result, sxt gene structure and expressional regulations are two critical aspects to investigate in order to properly comprehend PST synthesis processes in dinoflagellates, especially Alexandrium.
In general, the cell size changes according to the cell division rate, which may alter cytotoxicity in toxic dinoflagellates [145]. Therefore, it was necessary to determine whether environmental factors induce STXs production or simply change cellular toxicity depending on the cell size. To understand the alternation in STXs synthesis from a molecular perspective, core sxt genes, especially sxtA and sxtG, were identified in toxic Alexandrium, and their transcription patterns were evaluated under different environmental conditions (Figure 4). In summary, the expression patterns of sxtA and sxtG and their correlation with PST production were different under salinity and water temperature conditions.
Temperature, especially cold stress and optimal conditions, induced both cellular STXs levels and the two core gene expression levels in the toxic dinoflagellates A. catenella Alex03 and A. pacificum Alex05 [26,31]. On the other hand, the gene expression levels decreased under high-salinity conditions (40 psu), and there was no significant relationship between cellular STXs toxicity in A. pacificum [30]. Instead, the author suggested that STX tailoring genes (sxtX and sxtN) may be involved in the structural conversion from STX to other derivatives, including GTXs and dcGTXs. Besides sxtA and sxtG, recent studies reported the full-length sequences of sxtB [136], sxtU [146], and sxtI [63] from Alexandrium spp., and showed the correlation between their expression, toxin production, and environmental changes. Since each STXs metabolite has a different TEF, affecting the total STXs eq [16], it is contradictory to interpret the reduction in STXs eq as a decrease that is an absolute reduction. Therefore, further research is needed to understand the entire transcriptional response of sxt that relates to STXs production (sxtB, sxtD, sxtI, sxtS, and sxtU), modification (sxtL, sxtN, and sxtX), and transport (sxtF and sxtM), which alter the toxins’ composition [139]. Additionally, other environmental factors, such as nutrients and light, may influence STXs biosynthesis genes and PST production in dinoflagellates. Hence, more research should focus on the genes responsible for STXs synthesis in Alexandrium under different abiotic stress conditions.

5. Conclusions and Future Prospects

The cell growth and STXs production of toxic Alexandrium are obviously affected by environmental conditions, including nutrients, salinity, temperature, and light intensity. Recent studies on the expression and regulation of sxt shed light on the influence of abiotic factors on toxin production in diverse strains of Alexandrium. However, molecular research on sxt and PST synthesis in Alexandrium is rare, and no definite conclusion has yet been reached. Therefore, further research should be carried out to understand the molecular mechanism of STXs production based on entire transcriptome analysis under diverse environmental conditions. Multi-omcis-based studies, especially transcriptomic and metabolomic approaches, are considered as an alternative to assess the large-scale molecular mechanisms of dinoflagellates due to their extraordinary genomic features. Analyses of intracellular metabolic changes under varied environmental conditions, such as eutrophication, acidification, and increase in water temperature, allowed us to understand the mechanisms of HABs and PST outbreaks. In this regard, finding molecular detection research on the selected biomarkers highly relevant to STXs synthesis will provide us with information to predict and manage PSP occurrences. Finally, computational models that compute the interaction between abiotic factors and physiological and molecular influences can help us better forecast the global changes in Alexandrium proliferation patterns and PST production conditions in marine ecosystems.

Author Contributions

Conceptualization, B.P.; methodology, B.P.; software, B.P.; validation, B.P. and J.-S.K.; investigation, B.P. and J.-S.K.; data curation, B.P.; writing—original draft preparation, B.P.; writing—review and editing and figure editing, B.P., H.-S.K. and Q.T.N.B.; visualization, B.P. and J.-S.K.; supervision, J.-S.K.; funding acquisition, J.-S.K. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

We thank to Sangmyung University for providing the necessary facilities to carry out this work.

Conflicts of Interest

The authors declare no conflicts of interest. The funders had no role in the design of the study; in the collection, analyses, or interpretation; in the writing of the manuscript; or in the decision to publish the results.

References

  1. Pradhan, B.; Maharana, S.; Bhakta, S.; Jena, M. Marine phytoplankton diversity of Odisha coast, India with special reference to new record of diatoms and dinoflagellates. Vegetos 2021, 35, 330–344. [Google Scholar] [CrossRef]
  2. Behera, C.; Pradhan, B.; Panda, R.; Nayak, R.; Nayak, S.; Jena, M. Algal Diversity of Saltpans, Huma (Ganjam), India. J. Indian Bot. Soc. 2021, 101, 107–120. [Google Scholar] [CrossRef]
  3. Dash, S.; Pradhan, B.; Behera, C.; Nayak, R.; Jena, M. Algal flora of Tampara lake, Chhatrapur, Odisha, India. J. Indian Bot. Soc. 2021, 101, 1–15. [Google Scholar] [CrossRef]
  4. Dash, S.; Pradhan, B.; Behera, C.; Jena, M. Algal diversity of Kanjiahata lake, Nandankanan, Odisha, India. J. Indian Bot. Soc. 2020, 99, 11–24. [Google Scholar] [CrossRef]
  5. Behera, C.; Dash, S.R.; Pradhan, B.; Jena, M.; Adhikary, S.P. Algal diversity of Ansupa lake, Odisha, India. Nelumbo 2020, 62, 207–220. [Google Scholar] [CrossRef]
  6. Reich, A.; Lazensky, R.; Faris, J.; Fleming, L.E.; Kirkpatrick, B.; Watkins, S.; Ullmann, S.; Kohler, K.; Hoagland, P. Assessing the impact of shellfish harvesting area closures on neurotoxic shellfish poisoning (NSP) incidence during red tide (Karenia brevis) blooms. Harmful Algae 2015, 43, 13–19. [Google Scholar] [CrossRef]
  7. Pierella Karlusich, J.J.; Ibarbalz, F.M.; Bowler, C. Phytoplankton in the Tara ocean. Ann. Rev. Mar. Sci. 2020, 12, 233–265. [Google Scholar] [CrossRef] [PubMed]
  8. Taylor, F.; Hoppenrath, M.; Saldarriaga, J.F. Dinoflagellate diversity and distribution. Biodivers. Conserv. 2008, 17, 407–418. [Google Scholar] [CrossRef]
  9. Wang, H.; Guo, R.; Lim, W.-A.; Allen, A.E.; Ki, J.-S. Comparative transcriptomics of toxin synthesis genes between the non-toxin producing dinoflagellate Cochlodinium polykrikoides and toxigenic Alexandrium pacificum. Harmful Algae 2020, 93, 101777. [Google Scholar] [CrossRef]
  10. Pradhan, B.; Kim, H.; Abassi, S.; Ki, J.-S. Toxic effects and tumor promotion activity of marine phytoplankton toxins: A Review. Toxins 2022, 14, 397. [Google Scholar] [CrossRef] [PubMed]
  11. Pradhan, B.; Ki, J.-S. Phytoplankton toxins and their potential therapeutic applications: A journey toward the quest for potent pharmaceuticals. Mar. Drugs 2022, 20, 271. [Google Scholar] [CrossRef] [PubMed]
  12. Stüken, A.; Orr, R.J.; Kellmann, R.; Murray, S.A.; Neilan, B.A.; Jakobsen, K.S. Discovery of nuclear-encoded genes for the neurotoxin saxitoxin in dinoflagellates. PLoS ONE 2011, 6, e20096. [Google Scholar] [CrossRef] [PubMed]
  13. Anderson, D.M.; Alpermann, T.J.; Cembella, A.D.; Collos, Y.; Masseret, E.; Montresor, M. The globally distributed genus Alexandrium: Multifaceted roles in marine ecosystems and impacts on human health. Harmful Algae 2012, 14, 10–35. [Google Scholar] [CrossRef]
  14. Cestèle, S.; Catterall, W.A. Molecular mechanisms of neurotoxin action on voltage-gated sodium channels. Biochimie 2000, 82, 883–892. [Google Scholar] [CrossRef] [PubMed]
  15. Wiese, M.; D’agostino, P.M.; Mihali, T.K.; Moffitt, M.C.; Neilan, B.A. Neurotoxic alkaloids: Saxitoxin and its analogs. Mar. Drugs 2010, 8, 2185–2211. [Google Scholar] [CrossRef] [PubMed]
  16. EFSA. Marine biotoxins in shellfish–Saxitoxin group, scientific opinion of the panel on contaminants in the food chain. EFSA J. 2009, 1019, 1–76. [Google Scholar]
  17. Deeds, J.R.; Landsberg, J.H.; Etheridge, S.M.; Pitcher, G.C.; Longan, S.W. Non-traditional vectors for paralytic shellfish poisoning. Mar. Drugs 2008, 6, 308–348. [Google Scholar] [CrossRef] [PubMed]
  18. Oshima, Y.; Sugino, K.; Itakura, H.; Hirota, M.; Yasumoto, Y. Comparative studies on paralytic shellfish toxin profile of dinoflagellates and bivalves. In Toxic Marine Phytoplankton; Granelli, E., Sundstrom, B., Edler, L., Anderson, D.M., Eds.; Elsevier Science Publishing: New York, NY, USA, 1990; pp. 391–396. [Google Scholar]
  19. Anderson, D.M.; Sullivan, J.J.; Reguera, B. Paralytic shellfish poisoning in northwest Spain: The toxicity of the dinoflagellate Gymnodinium catenatum. Toxicon 1989, 27, 665–674. [Google Scholar] [CrossRef] [PubMed]
  20. Vandersea, M.W.; Kibler, S.R.; Tester, P.A.; Holderied, K.; Hondolero, D.E.; Powell, K.; Baird, S.; Doroff, A.; Dugan, D.; Litaker, R.W. Environmental factors influencing the distribution and abundance of Alexandrium catenella in Kachemak bay and lower cook inlet, Alaska. Harmful Algae 2018, 77, 81–92. [Google Scholar] [CrossRef]
  21. Condie, S.A.; Oliver, E.C.; Hallegraeff, G.M. Environmental drivers of unprecedented Alexandrium catenella dinoflagellate blooms off eastern Tasmania, 2012–2018. Harmful Algae 2019, 87, 101628. [Google Scholar] [CrossRef] [PubMed]
  22. Guiry, M.; Guiry, G. AlgaeBase. World-Wide Electronic Publication, National University of Ireland, Galway. Available online: http://www.algaebase.org (accessed on 20 December 2023).
  23. Murray, S.; John, U.; Savela, H.; Kremp, A. Alexandrium spp.: Genetic and ecological factors influencing saxitoxin production and proliferation. In Climate Change and Marine and Freshwater Toxins, 2nd ed.; Botana, L.M., Louzao, M.C., Eds.; Walter de Gruyter GmbH: Berlin, Germany; Boston, MA, USA, 2015; pp. 125–155. [Google Scholar]
  24. Etheridge, S.M. Paralytic shellfish poisoning: Seafood safety and human health perspectives. Toxicon 2010, 56, 108–122. [Google Scholar] [CrossRef] [PubMed]
  25. Llewellyn, L.; Negri, A.; Robertson, A. Paralytic shellfish toxins in tropical oceans. Toxin Rev. 2006, 25, 159–196. [Google Scholar] [CrossRef]
  26. Kim, H.; Park, H.; Wang, H.; Yoo, H.Y.; Park, J.; Ki, J.-S. Low temperature and cold stress significantly increase saxitoxins (STXs) and expression of STX biosynthesis genes sxtA4 and sxtG in the dinoflagellate Alexandrium catenella. Mar. Drugs 2021, 19, 291. [Google Scholar] [CrossRef] [PubMed]
  27. Eckford-Soper, L.K.; Bresnan, E.; Lacaze, J.-P.; Green, D.H.; Davidson, K. The competitive dynamics of toxic Alexandrium fundyense and non-toxic Alexandrium tamarense: The role of temperature. Harmful Algae 2016, 53, 135–144. [Google Scholar] [CrossRef] [PubMed]
  28. Gettings, R.M.; Townsend, D.W.; Thomas, M.A.; Karp-Boss, L. Dynamics of late spring and summer phytoplankton communities on Georges Bank, with emphasis on diatoms, Alexandrium spp., and other dinoflagellates. Deep Sea Res. Part II Top. Stud. Oceanogr. 2014, 103, 120–138. [Google Scholar] [CrossRef]
  29. Cirés, S.; Delgado, A.; González-Pleiter, M.; Quesada, A. Temperature influences the production and transport of saxitoxin and the expression of sxt genes in the cyanobacterium Aphanizomenon gracile. Toxins 2017, 9, 322. [Google Scholar] [CrossRef] [PubMed]
  30. Bui, Q.T.N.; Kim, H.; Park, H.; Ki, J.-S. Salinity affects saxitoxins (STXs) toxicity in the dinoflagellate Alexandrium pacificum, with low transcription of SXT-biosynthesis genes sxtA4 and sxtG. Toxins 2021, 13, 733. [Google Scholar] [CrossRef]
  31. Wang, H.; Kim, H.; Park, H.; Ki, J.-S. Temperature influences the content and biosynthesis gene expression of saxitoxins (STXs) in the toxigenic dinoflagellate Alexandrium pacificum. Sci. Total Environ. 2022, 802, 149801. [Google Scholar] [CrossRef] [PubMed]
  32. Hii, K.S.; Lim, P.T.; Kon, N.F.; Takata, Y.; Usup, G.; Leaw, C.P. Physiological and transcriptional responses to inorganic nutrition in a tropical Pacific strain of Alexandrium minutum: Implications for the saxitoxin genes and toxin production. Harmful Algae 2016, 56, 9–21. [Google Scholar] [CrossRef]
  33. Maclean, C.; Cembella, A.D.; Quilliam, M.A. Effects of light, salinity and inorganic nitrogen on cell growth and spirolide production in the marine dinoflagellate Alexandrium ostenfeldii (Paulsen) Balech et Tangen. Bot. Mar. 2003, 46, 466–476. [Google Scholar] [CrossRef]
  34. Collos, Y.; Bec, B.; Jauzein, C.; Abadie, E.; Laugier, T.; Lautier, J.; Pastoureaud, A.; Souchu, P.; Vaquer, A. Oligotrophication and emergence of picocyanobacteria and a toxic dinoflagellate in Thau lagoon, southern France. J. Sea Res. 2009, 61, 68–75. [Google Scholar] [CrossRef]
  35. Langdon, C. On the causes of interspecific differences in the growth-irradiance relationship for phytoplankton. Part I. A comparative study of the growth-irradiance relationship of three marine phytoplankton species: Skeletonema costatum, Olisthodiscus luteus and Gonyaulax tamarensis. J. Plankton Res. 1987, 9, 459–482. [Google Scholar]
  36. Flynn, K.J.; Clark, D.R.; Xue, Y. Modeling the release of dissolved organic matter by phytoplankton. J. Phycol. 2008, 44, 1171–1187. [Google Scholar] [CrossRef] [PubMed]
  37. Leong, S.C.Y.; Maekawa, M.; Taguchi, S. Carbon and nitrogen acquisition by the toxic dinoflagellate Alexandrium tamarense in response to different nitrogen sources and supply modes. Harmful Algae 2010, 9, 48–58. [Google Scholar] [CrossRef]
  38. Flynn, K.; Jones, K.; Flynn, K. Comparisons among species of Alexandrium (Dinophyceae) grown in nitrogen-or phosphorus-limiting batch culture. Mar. Biol. 1996, 126, 9–18. [Google Scholar] [CrossRef]
  39. Paladugu, S.R.; James, C.K.; Looper, R.E. A direct C11 alkylation strategy on the saxitoxin core: A synthesis of (+)-11-saxitoxinethanoic acid. Org. Lett. 2019, 21, 7999–8002. [Google Scholar] [CrossRef] [PubMed]
  40. Tortell, P.D.; Payne, C.D.; Li, Y.; Trimborn, S.; Rost, B.; Smith, W.O.; Riesselman, C.; Dunbar, R.B.; Sedwick, P.; DiTullio, G.R. CO2 sensitivity of Southern Ocean phytoplankton. Geophys. Res. Lett. 2008, 35, 1–5. [Google Scholar] [CrossRef]
  41. Kaushal, S.S.; Duan, S.; Doody, T.R.; Haq, S.; Smith, R.M.; Johnson, T.A.N.; Newcomb, K.D.; Gorman, J.; Bowman, N.; Mayer, P.M. Human-accelerated weathering increases salinization, major ions, and alkalinization in fresh water across land use. Appl. Geochem. 2017, 83, 121–135. [Google Scholar] [CrossRef] [PubMed]
  42. Raven, J.A.; Gobler, C.J.; Hansen, P.J. Dynamic CO2 and pH levels in coastal, estuarine, and inland waters: Theoretical and observed effects on harmful algal blooms. Harmful Algae 2020, 91, 101594. [Google Scholar] [CrossRef] [PubMed]
  43. Van de Waal, D.B.; Eberlein, T.; John, U.; Wohlrab, S.; Rost, B. Impact of elevated pCO2 on paralytic shellfish poisoning toxin content and composition in Alexandrium tamarense. Toxicon 2014, 78, 58–67. [Google Scholar] [CrossRef] [PubMed]
  44. Parkhill, J.-P.; Cembella, A.D. Effects of salinity, light and inorganic nitrogen on growth and toxigenicity of the marine dinoflagellate Alexandrium tamarense from northeastern Canada. J. Plankton Res. 1999, 21, 939–955. [Google Scholar] [CrossRef]
  45. Wang, D.-Z.; Hsieh, D.P. Effects of nitrate and phosphate on growth and C2 toxin productivity of Alexandrium tamarense CI01 in culture. Mar. Pollut. Bull. 2002, 45, 286–289. [Google Scholar] [CrossRef] [PubMed]
  46. Lim, P.-T.; Leaw, C.-P.; Kobiyama, A.; Ogata, T. Growth and toxin production of tropical Alexandrium minutum Halim (Dinophyceae) under various nitrogen to phosphorus ratios. J. Appl. Phycol. 2010, 22, 203–210. [Google Scholar] [CrossRef]
  47. Han, M.; Lee, H.; Anderson, D.M.; Kim, B. Paralytic shellfish toxin production by the dinoflagellate Alexandrium pacificum (Chinhae Bay, Korea) in axenic, nutrient-limited chemostat cultures and nutrient-enriched batch cultures. Mar. Pollut. Bull. 2016, 104, 34–43. [Google Scholar] [CrossRef] [PubMed]
  48. Yarimizu, K.; Mardones, J.I.; Paredes-Mella, J.; Norambuena-Subiabre, L.; Carrano, C.J.; Maruyama, F. The effect of iron on Chilean Alexandrium catenella growth and paralytic shellfish toxin production as related to algal blooms. BioMetals 2022, 35, 39–51. [Google Scholar] [CrossRef] [PubMed]
  49. John, E.; Flynn, K. Growth dynamics and toxicity of Alexandrium fundyense (Dinophyceae): The effect of changing N/P supply ratios on internal toxin and nutrient levels. Eur. J. Phycol. 2000, 35, 11–23. [Google Scholar] [CrossRef]
  50. Juhl, A.R.; Latz, M.I. Mechanisms of fluid shear—Induced inhibition of population growth in a red-tide dinoflagellate. J. Phycol. 2002, 38, 683–694. [Google Scholar] [CrossRef]
  51. Yeung, P.K.K.; Wong, J.T.Y. Inhibition of cell proliferation by mechanical agitation involves transient cell cycle arrest at G1 phase in dinoflagellates. Protoplasma 2003, 220, 173–178. [Google Scholar] [CrossRef] [PubMed]
  52. Dyhrman, S.T.; Anderson, D.M. Urease activity in cultures and field populations of the toxic dinoflagellate Alexandrium. Limnol. Oceanogr. 2003, 48, 647–655. [Google Scholar] [CrossRef]
  53. Huang, K.; Feng, Q.; Zhang, Y.; Ou, L.; Cen, J.; Lu, S.; Qi, Y. Comparative uptake and assimilation of nitrate, ammonium, and urea by dinoflagellate Karenia mikimotoi and diatom Skeletonema costatum s.l. in the coastal waters of the East China Sea. Mar. Pollut. Bull. 2020, 155, 111200. [Google Scholar] [CrossRef] [PubMed]
  54. Chang, F.H.; McClean, M. Growth responses of Alexandrium minutum (Dinophyceae) as a function of three different nitrogen sources and irradiance. N. Z. J. Mar. Freshw. Res. 1997, 31, 1–7. [Google Scholar] [CrossRef]
  55. Shankar, S.; Townsend, D.W.; Thomas, M.A. Ammonium and maintenance of bloom populations of Alexandrium fundyense in the Gulf of Maine and on Georges Bank: Results of laboratory culture experiments. Mar. Ecol. Prog. Ser. 2014, 507, 57–67. [Google Scholar] [CrossRef]
  56. Jauzein, C.; Loureiro, S.; Garcés, E.; Collos, Y. Interactions between ammonium and urea uptake by five strains of Alexandrium catenella (Dinophyceae) in culture. Aquat. Microb. Ecol. 2008, 53, 271–280. [Google Scholar] [CrossRef]
  57. Collos, Y.; Vaquer, A.; Laabir, M.; Abadie, E.; Laugier, T.; Pastoureaud, A.; Souchu, P. Contribution of several nitrogen sources to growth of Alexandrium catenella during blooms in Thau lagoon, southern France. Harmful Algae 2007, 6, 781–789. [Google Scholar] [CrossRef]
  58. Matsuda, A.; Nishijima, T.; Fukami, K. Effects of nitrogenous and phosphorus nutrients on the growth of toxic dinoflagellate Alexandrium catenella. Bull. Jpn. Soc. Sci. Fish. 1999, 65, 847–855. [Google Scholar] [CrossRef]
  59. Stolte, W.; Panosso, R.; Gisselson, L.-Å.; Granéli, E. Utilization efficiency of nitrogen associated with riverine dissolved organic carbon (> 1 kDa) by two toxin-producing phytoplankton species. Aquat. Microb. Ecol. 2002, 29, 97–105. [Google Scholar] [CrossRef]
  60. Fagerberg, T.; Carlsson, P.; Lundgren, M. A large molecular size fraction of riverine high molecular weight dissolved organic matter (HMW DOM) stimulates growth of the harmful dinoflagellate Alexandrium minutum. Harmful Algae 2009, 8, 823–831. [Google Scholar] [CrossRef]
  61. Loureiro, S.; Garcés, E.; Collos, Y.; Vaqué, D.; Camp, J. Effect of marine autotrophic dissolved organic matter (DOM) on Alexandrium catenella in semi-continuous cultures. J. Plankton Res. 2009, 31, 1363–1372. [Google Scholar] [CrossRef]
  62. Jauzein, C.; Collos, Y.; Garcés, E.; Vila, M.; Maso, M. Short-term temporal variability of ammonium and urea uptake by Alexandrium catenella (Dinophyta) in cultures. J. Phycol. 2008, 44, 1136–1145. [Google Scholar] [CrossRef] [PubMed]
  63. Abassi, S.; Kim, H.S.; Bui, Q.T.N.; Ki, J.S. Effects of nitrate on the saxitoxins biosynthesis revealed by sxt genes in the toxic dinoflagellate Alexandrium pacificum (group IV). Harmful Algae 2023, 127, 102473. [Google Scholar] [CrossRef] [PubMed]
  64. Hu, H.; Chen, W.; Shi, Y.; Cong, W. Nitrate and phosphate supplementation to increase toxin production by the marine dinoflagellate Alexandrium tamarense. Mar. Pollut. Bull. 2006, 52, 756–760. [Google Scholar] [CrossRef] [PubMed]
  65. Maguer, J.F.; l’Helguen, S.; Madec, C.; Labry, C.; Le Corre, P. Nitrogen uptake and assimilation kinetics in Alexandrium minutum (Dinophyceae): Effecr of N–limited growth rate on nitrate and ammonium interaction. J. Phycol. 2007, 43, 295–303. [Google Scholar] [CrossRef]
  66. Anderson, D.; Kulis, D.; Sullivan, J.; Hall, S.; Lee, C. Dynamics and physiology of saxitoxin production by the dinoflagellates Alexandrium spp. Mar. Biol. 1990, 104, 511–524. [Google Scholar] [CrossRef]
  67. Abassi, S.; Ki, J.-S. Increased nitrate concentration differentially affects cell growth and expression of nitrate transporter and other nitrogen-related genes in the harmful dinoflagellate Prorocentrum minimum. Chemosphere 2022, 288, 132526. [Google Scholar] [CrossRef] [PubMed]
  68. Prakash, A.A.; Rashid, M. Influence of humic substances on the growth of marine phytoplankton: Dinoflagellates. Limnol. Oceanogr. 1968, 13, 598–606. [Google Scholar] [CrossRef]
  69. Mustakim, G.R.; Shaleh, S.R.M.; Ayub, M.N.A. Effect of different concentration of soil extracts on the growth of Pyrodinium bahamense var. Compressum. Int. J. Fish. Aquat. Sci. 2019, 7, 353–355. [Google Scholar]
  70. Gagnon, R.; Levasseur, M.; Weise, A.M.; Fauchot, J.; Campbell, P.G.; Weissenboeck, B.J.; Merzouk, A.; Gosselin, M.; Vigneault, B. Growth stimulation of Alexandrium tamarense (Dinophyceae) by humic substances from the Manicouagan river (Eastern Canada). J. Phycol. 2005, 41, 489–497. [Google Scholar] [CrossRef]
  71. Carlsson, P.; Edling, H.; Béchemin, C. Interactions between a marine dinoflagellate (Alexandrium catenella) and a bacterial community utilizing riverine humic substances. Aquat. Microb. Ecol. 1998, 16, 65–80. [Google Scholar] [CrossRef]
  72. Doblin, M.; Legrand, C.; Carlsson, P.; Hummert, C.; Graneli, E.; Hallegraeff, G. Uptake of humic substances by the toxic dinoflagellate Alexandrium catenella. In Harmful Algal Blooms 2000; Hallegraeff, G.M., Blackburn, S.I., Bolch, C.J., Lewis, R.J., Eds.; UNESCO: Paris, France, 2001; pp. 336–339. [Google Scholar]
  73. Murata, A.; Leong, S.C.; Nagashima, Y.; Taguchi, S. Nitrogen:Phosphorus supply ratio may control the protein and total toxin of dinoflagellate Alexandrium tamarense. Toxicon 2006, 48, 683–689. [Google Scholar] [CrossRef] [PubMed]
  74. Ou, L.; Wang, D.; Huang, B.; Hong, H.; Qi, Y.; Lu, S. Comparative study of phosphorus strategies of three typical harmful algae in Chinese coastal waters. J. Plankton Res. 2008, 30, 1007–1017. [Google Scholar] [CrossRef]
  75. Jauzein, C.; Labry, C.; Youenou, A.; Quéré, J.; Delmas, D.; Collos, Y. Growth and phosphorus uptake by the toxic dinoflagellate Alexandrium catenella (Dinophyceae) in response to phosphate limitation. J. Phycol. 2010, 46, 926–936. [Google Scholar] [CrossRef]
  76. Labry, C.; Erard–Le Denn, E.; Chapelle, A.; Fauchot, J.; Youenou, A.; Crassous, M.-P.; Le Grand, J.; Lorgeoux, B. Competition for phosphorus between two dinoflagellates: A toxic Alexandrium minutum and a non-toxic Heterocapsa triquetra. J. Exp. Mar. Bio. Ecol. 2008, 358, 124–135. [Google Scholar] [CrossRef]
  77. Flynn, K.; Franco, J.M.; Fernández, P.; Reguera, B.; Zapata, M.; Wood, G.; Flynn, K.J. Changes in toxin content, biomass and pigments of the dinoflagellate Alexandrium minutum during nitrogen refeeding and growth into nitrogen or phosphorus stress. Mar. Ecol. Prog. Ser. 1994, 111, 99–109. [Google Scholar] [CrossRef]
  78. Jean, N.; Perié, L.; Dumont, E.; Bertheau, L.; Balliau, T.; Caruana, A.M.; Amzil, Z.; Laabir, M.; Masseret, E. Metal stresses modify soluble proteomes and toxin profiles in two Mediterranean strains of the distributed dinoflagellate Alexandrium pacificum. Sci. Total Environ. 2022, 818, 151680. [Google Scholar] [CrossRef] [PubMed]
  79. Rueler, J.G.; Ades, D.R. The role of iron nutrition in photosynthesis and nitrogen assimilation in Scenedesmus quadricauda (Chlorophyceae). J. Phycol. 1987, 23, 452–457. [Google Scholar] [CrossRef]
  80. He, H.; Chen, F.; Li, H.; Xiang, W.; Li, Y.; Jiang, Y. Effect of iron on growth, biochemical composition and paralytic shellfish poisoning toxins production of Alexandrium tamarense. Harmful Algae 2010, 9, 98–104. [Google Scholar] [CrossRef]
  81. Yang, I.; Beszteri, S.; Tillmann, U.; Cembella, A.; John, U. Growth-and nutrient-dependent gene expression in the toxigenic marine dinoflagellate Alexandrium minutum. Harmful Algae 2011, 12, 55–69. [Google Scholar] [CrossRef]
  82. Long, M.; Holland, A.; Planquette, H.; Santana, D.G.; Whitby, H.; Soudant, P.; Sarthou, G.; Hegaret, H.; Jolley, D.F. Effects of copper on the dinoflagellate Alexandrium minutum and its allelochemical potency. Aquat. Toxicol. 2019, 210, 251–261. [Google Scholar] [CrossRef] [PubMed]
  83. Taroncher-Oldenburg, G.; Kulis, D.M.; Anderson, D.M. Coupling of saxitoxin biosynthesis to the G1 phase of the cell cycle in the dinoflagellate Alexandrin fundyense: Temperature and nutrient effects. Nat. Toxins 1999, 7, 207–219. [Google Scholar] [CrossRef] [PubMed]
  84. Ogata, T.; Ishimaru, T.; Kodama, M. Effect of water temperature and light intensity on growth rate and toxicity change in Protogonyaulax tamarensis. Mar. Biol. 1987, 95, 217–220. [Google Scholar] [CrossRef]
  85. Hamasaki, K.; Horie, M.; Tokimitsu, S.; Toda, T.; Taguchi, S. Variability in toxicity of the dinoflagellate Alexandrium tamarense isolated from Hiroshima Bay, western Japan, as a reflection of changing environmental conditions. J. Plankton Res. 2001, 23, 271–278. [Google Scholar] [CrossRef]
  86. Tillmann, U.; John, U. Toxic effects of Alexandrium spp. on heterotrophic dinoflagellates: An allelochemical defence mechanism independent of PSP-toxin content. Mar. Ecol. Prog. Ser. 2002, 230, 47–58. [Google Scholar] [CrossRef]
  87. Laabir, M.; Collos, Y.; Masseret, E.; Grzebyk, D.; Abadie, E.; Savar, V.; Sibat, M.; Amzil, Z. Influence of environmental factors on the paralytic shellfish toxin content and profile of Alexandrium catenella (Dinophyceae) isolated from the Mediterranean Sea. Mar. Drugs 2013, 11, 1583–1601. [Google Scholar] [CrossRef]
  88. Navarro, J.; Munoz, M.; Contreras, A. Temperature as a factor regulating growth and toxin content in the dinoflagellate Alexandrium catenella. Harmful Algae 2006, 5, 762–769. [Google Scholar] [CrossRef]
  89. Lilly, E.; Kulis, D.; Gentien, P.; Anderson, D. Paralytic shellfish poisoning toxins in France linked to a human-introduced strain of Alexandrium catenella from the western Pacific: Evidence from DNA and toxin analysis. J. Plankton Res. 2002, 24, 443–452. [Google Scholar] [CrossRef]
  90. Abdulhussain, A.H.; Cook, K.B.; Turner, A.D.; Lewis, A.M.; Elsafi, M.A.; Mayor, D.J. The influence of the toxin producing dinoflagellate, Alexandrium catenella (1119/27), on the feeding and survival of the marine Copepod, Acartia tonsa. Harmful Algae 2020, 98, 101890. [Google Scholar] [CrossRef] [PubMed]
  91. Etheridge, S.M.; Roesler, C.S. Effects of temperature, irradiance, and salinity on photosynthesis, growth rates, total toxicity, and toxin composition for Alexandrium fundyense isolates from the Gulf of Maine and Bay of Fundy. Deep Sea Res. Part II Top. Stud. Oceanogr. 2005, 52, 2491–2500. [Google Scholar] [CrossRef]
  92. Lim, P.T.; Leaw, C.P.; Usup, G.; Kobiyama, A.; Koike, K.; Ogata, T. Effects of light and temperature on growth, nitrate uptake, and toxin production of two tropical dinoflagellates: Alexandrium tamiyavanichii and Alexandrium minuyum (Dinophyceae). J. Phycol. 2006, 42, 786–799. [Google Scholar] [CrossRef]
  93. Hadjadji, I.; Laabir, M.; Frihi, H.; Collos, Y.; Shao, Z.J.; Berrebi, P.; Abadie, E.; Amzil, Z.; Chomérat, N.; Rolland, J.L. Unsuspected intraspecific variability in the toxin production, growth and morphology of the dinoflagellate Alexandrium pacificum RW Litaker (Group IV) blooming in a South Western Mediterranean marine ecosystem, Annaba Bay (Algeria). Toxicon 2020, 180, 79–88. [Google Scholar] [CrossRef] [PubMed]
  94. Caruana, A.M.; Le Gac, M.; Hervé, F.; Rovillon, G.-A.; Geffroy, S.; Malo, F.; Abadie, E.; Amzil, Z. Alexandrium pacificum and Alexandrium minutum: Harmful or environmentally friendly? Mar. Environ. Res. 2020, 160, 105014. [Google Scholar] [CrossRef] [PubMed]
  95. Alkawri, A.; Ramaiah, N. Spatio-temporal variability of dinoflagellate assemblages in different salinity regimes in the west coast of India. Harmful Algae 2010, 9, 153–162. [Google Scholar] [CrossRef]
  96. Errera, R.M.; Campbell, L. Osmotic stress triggers toxin production by the dinoflagellate Karenia brevis. Proc. Natl. Acad. Sci. USA 2011, 108, 10597–10601. [Google Scholar] [CrossRef] [PubMed]
  97. Kirst, G. Salinity tolerance of eukaryotic marine algae. Annu. Rev. Plant Biol. 1990, 41, 21–53. [Google Scholar] [CrossRef]
  98. Lim, P.T.; Leaw, C.P.; Sato, S.; Thuoc, C.V.; Kobiyama, A.; Ogata, T. Effect of salinity on growth and toxin production of Alexandrium minutum isolated from a shrimp culture pond in northern Vietnam. J. Appl. Phycol. 2011, 23, 857–864. [Google Scholar] [CrossRef]
  99. Lim, P.-T.; Ogata, T. Salinity effect on growth and toxin production of four tropical Alexandrium species (Dinophyceae). Toxicon 2005, 45, 699–710. [Google Scholar] [CrossRef]
  100. Shin, H.H.; Baek, S.H.; Zhun, L.; Han, M.-S.; Oh, S.J.; Youn, S.-H.; Kim, Y.S.; Kim, D.; Lim, W.-A. Resting cysts, and effects of temperature and salinity on the growth of vegetative cells of the potentially harmful species Alexandrium insuetum Balech (Dinophyceae). Harmful Algae 2014, 39, 175–184. [Google Scholar] [CrossRef]
  101. Glaser, K.; Karsten, U. Salinity tolerance in biogeographically different strains of the marine benthic diatom Cylindrotheca closterium (Bacillariophyceae). J. Appl. Phycol. 2020, 32, 3809–3816. [Google Scholar] [CrossRef]
  102. Aguilera-Belmonte, A.; Inostroza, I.; Carrillo, K.S.; Franco, J.M.; Riobó, P.; Gómez, P.I. The combined effect of salinity and temperature on the growth and toxin content of four Chilean strains of Alexandrium catenella (Whedon and Kofoid) Balech 1985 (Dinophyceae) isolated from an outbreak occurring in southern Chile in 2009. Harmful Algae 2013, 23, 55–59. [Google Scholar] [CrossRef]
  103. Grzebyk, D.; Béchemin, C.; Ward, C.J.; Vérité, C.; Codd, G.A.; Maestrini, S.Y. Effects of salinity and two coastal waters on the growth and toxin content of the dinoflagellate Alexandrium minutum. J. Plankton Res. 2003, 25, 1185–1199. [Google Scholar] [CrossRef]
  104. Hwang, D.F.; Lu, Y.H. Influence of environmental and nutritional factors on growth, toxicity, and toxin profile of dinoflagellate Alexandrium minutum. Toxicon 2000, 38, 1491–1503. [Google Scholar] [CrossRef]
  105. Lazcano-Ferrat, I.; Lovatt, C.J. Effect of salinity on Arginine biosynthesis in leaves of Phaseolus vulgaris LP acutifolius A. Gray. Crop Sci. 1997, 37, 469–475. [Google Scholar] [CrossRef]
  106. Martens, H.; Van de Waal, D.B.; Brandenburg, K.M.; Krock, B.; Tillmann, U. Salinity effects on growth and toxin production in an Alexandrium ostenfeldii (Dinophyceae) isolate from The Netherlands. J. Plankton Res. 2016, 38, 1302–1316. [Google Scholar] [CrossRef]
  107. Murray, S.A.; Diwan, R.; Orr, R.J.; Kohli, G.S.; John, U. Gene duplication, loss and selection in the evolution of saxitoxin biosynthesis in alveolates. Mol. Phylogenet. Evol. 2015, 92, 165–180. [Google Scholar] [CrossRef] [PubMed]
  108. Wiese, M. Investigations into Abiotic and Biotic Factors Regulating Saxitoxin Synthesis in the Dinoflagellate Genus Alexandrium. Ph.D. Thesis, University of New South Wales, Sydney, Australia, 2012. [Google Scholar]
  109. Glover, H.; Beardall, J.; Morris, I. Effects of environmental factors on photosynthesis patterns in Phaeodactylum tricornutum (bacillariophyceae). I. Effect of nitrogen deficiency and light intensity. J. Phycol. 1975, 11, 424–429. [Google Scholar]
  110. Vingiani, G.M.; Štālberga, D.; De Luca, P.; Ianora, A.; De Luca, D.; Lauritano, C. De novo transcriptome of the non-saxitoxin producing Alexandrium tamutum reveals new insights on harmful dinoflagellates. Mar. Drugs 2020, 18, 386. [Google Scholar] [CrossRef] [PubMed]
  111. Akbar, M.A.; Yusof, N.Y.M.; Sahrani, F.K.; Usup, G.; Ahmad, A.; Baharum, S.N.; Muhammad, N.A.N.; Bunawan, H. Insights into Alexandrium minutum nutrient acquisition, metabolism and saxitoxin biosynthesis through comprehensive transcriptome survey. Biology 2021, 10, 826. [Google Scholar] [CrossRef]
  112. Oh, S.J.; Kim, D.-I.; Sajima, T.; Shimasaki, Y.; Matsuyama, Y.; Oshima, Y.; Honjo, T.; Yang, H.-S. Effects of irradiance of various wavelengths from light-emitting diodes on the growth of the harmful dinoflagellate Heterocapsa circularisquama and the diatom Skeletonema costatum. Fish. Sci. 2008, 74, 137–145. [Google Scholar] [CrossRef]
  113. McGillicuddy, D.J., Jr.; Anderson, D.M.; Lynch, D.R.; Townsend, D.W. Mechanisms regulating large-scale seasonal fluctuations in Alexandrium fundyense populations in the Gulf of Maine: Results from a physical–biological model. Deep Sea Res. Part II Top. Stud. Oceanogr. 2005, 52, 2698–2714. [Google Scholar] [CrossRef]
  114. Prézelin, B.B.; Alberte, R.S. Photosynthetic characteristics and organization of chlorophyll in marine dinoflagellates. Proc. Natl. Acad. Sci. USA 1978, 75, 1801–1804. [Google Scholar] [CrossRef] [PubMed]
  115. Prézelin, B.B. The role of peridinin-chlorophyll a-proteins in the photosynthetic light adaption of the marine dinoflagellate, Glenodinium sp. Planta 1976, 130, 225–233. [Google Scholar] [CrossRef] [PubMed]
  116. Rivkin, R.B. Influence of irradiance and spectral quality on the carbon metabolism of phytoplankton. I. Photosynthesis, chemical composition and growth. Mar. Ecol. Prog. Ser. Oldendorf 1989, 55, 291–304. [Google Scholar] [CrossRef]
  117. Burja, A.M.; Banaigs, B.; Abou-Mansour, E.; Burgess, J.G.; Wright, P.C. Marine cyanobacteria—A prolific source of natural products. Tetrahedron 2001, 57, 9347–9377. [Google Scholar] [CrossRef]
  118. Salgado, P.; Vázquez, J.A.; Riobó, P.; Franco, J.M.; Figueroa, R.I.; Kremp, A.; Bravo, I. A kinetic and factorial approach to study the effects of temperature and salinity on growth and toxin production by the dinoflagellate Alexandrium ostenfeldii from the Baltic Sea. PLoS ONE 2015, 10, e0143021. [Google Scholar] [CrossRef]
  119. Nam, K.T.; Kim, S.-Y.; Moon, C.-H.; Kim, C.-H.; Oh, S.J. Effects of light wavelengths on the growth and paralytic shellfish toxin production of Alexandrium catenella and A. pacificum. J. Korean Soc. Mar. Environ. 2020, 26, 84–92. [Google Scholar] [CrossRef]
  120. Pistocchi, R. Factors affecting algal toxicity. In Toxins and Biologically Active Compound from Microalgae; Rossini, G.P., Ed.; CRC Press: Boca Raton, FL, USA; Taylor & Francis Group: London, UK, 2014; pp. 75–96. [Google Scholar]
  121. Alpermann, T.J.; Tillmann, U.; Beszteri, B.; Cembella, A.D.; John, U. Phenotypic variation and genotypic diversity in a planktonic population of the toxigenic marine dinoflagellate Alexandrium tamarense (Dinophyceae). J. Phycol. 2010, 46, 18–32. [Google Scholar] [CrossRef]
  122. Gao, Y.; Sassenhagen, I.; Richlen, M.L.; Anderson, D.M.; Martin, J.L.; Erdner, D.L. Spatiotemporal genetic structure of regional-scale Alexandrium catenella dinoflagellate blooms explained by extensive dispersal and environmental selection. Harmful Algae 2019, 86, 46–54. [Google Scholar] [CrossRef] [PubMed]
  123. Kremp, A.; Oja, J.; LeTortorec, A.H.; Hakanen, P.; Tahvanainen, P.; Tuimala, J.; Suikkanen, S. Diverse seed banks favour adaptation of microalgal populations to future climate conditions. Environ. Microbiol. 2016, 18, 679–691. [Google Scholar] [CrossRef] [PubMed]
  124. Iglesias-Prieto, R.; Trench, R. Acclimation and adaptation to irradiance in symbiotic dinoflagellates. II. Response of chlorophyll–protein complexes to different photon-flux densities. Mar. Biol. 1997, 130, 23–33. [Google Scholar] [CrossRef]
  125. Kellmann, R.; Mihali, T.K.; Jeon, Y.J.; Pickford, R.; Pomati, F.; Neilan, B.A. Biosynthetic intermediate analysis and functional homology reveal a saxitoxin gene cluster in cyanobacteria. Appl. Environ. Microbiol. 2008, 74, 4044–4053. [Google Scholar] [CrossRef] [PubMed]
  126. Kellmann, R.; Michali, T.K.; Neilan, B.A. Identification of a saxitoxin biosynthesis gene with a history of frequent horizontal gene transfers. J. Mol. Evol. 2008, 67, 526–538. [Google Scholar] [CrossRef] [PubMed]
  127. Schantz, E.J.; Mold, J.D.; Stanger, D.W.; Shavel, J.; Riel, F.J.; Bowden, J.P.; Lynch, J.M.; Wyler, R.S.; Riegel, B.; Sommer, H. Paralytic shellfish poison. VI. A procedure for the isolation and purification of the poison from toxic clam and mussel tissues. J. Am. Chem. Soc. 1957, 79, 5230–5235. [Google Scholar] [CrossRef]
  128. Moustafa, A.; Loram, J.E.; Hackett, J.D.; Anderson, D.M.; Plumley, F.G.; Bhattacharya, D. Origin of saxitoxin biosynthetic genes in cyanobacteria. PLoS ONE 2009, 4, e5758. [Google Scholar] [CrossRef] [PubMed]
  129. Hackett, J.D.; Wisecaver, J.H.; Brosnahan, M.L.; Kulis, D.M.; Anderson, D.M.; Bhattacharya, D.; Plumley, F.G.; Erdner, D.L. Evolution of saxitoxin synthesis in cyanobacteria and dinoflagellates. Mol. Biol. Evol. 2013, 30, 70–78. [Google Scholar] [CrossRef] [PubMed]
  130. Zhang, Y.; Zhang, S.-F.; Lin, L.; Wang, D.-Z. Comparative transcriptome analysis of a toxin-producing dinoflagellate Alexandrium catenella and its non-toxic mutant. Mar. Drugs 2014, 12, 5698–5718. [Google Scholar] [CrossRef] [PubMed]
  131. Zhang, Y.; Zhang, S.-F.; Lin, L.; Wang, D.-Z. Whole transcriptomic analysis provides insights into molecular mechanisms for toxin biosynthesis in a toxic dinoflagellate Alexandrium catenella (ACHK-T). Toxins 2017, 9, 213. [Google Scholar] [CrossRef] [PubMed]
  132. Wang, D.-Z.; Zhang, S.-F.; Zhang, Y.; Lin, L. Paralytic shellfish toxin biosynthesis in cyanobacteria and dinoflagellates: A molecular overview. J. Proteom. 2016, 135, 132–140. [Google Scholar] [CrossRef] [PubMed]
  133. Verma, A.; Barua, A.; Ruvindy, R.; Savela, H.; Ajani, P.A.; Murray, S.A. The genetic basis of toxin biosynthesis in dinoflagellates. Microorganisms 2019, 7, 222. [Google Scholar] [CrossRef] [PubMed]
  134. Kim, H.S.; Park, H.; Wang, H.; Kim, T.; Ki, J.S. Saxitoxins-producing potential of the marine dinoflagellate Alexandrium affine and its environmental implications revealed by toxins and transcriptome profiling. Mar. Environ. Res. 2023, 185, 105874. [Google Scholar] [CrossRef] [PubMed]
  135. Bui, Q.T.N.; Kim, H.; Wang, H.; Ki, J.S. Unveiling the genomic structures and evolutionary events of the saxitoxin biosynthetic gene sxtA in the marine toxic dinoflagellate Alexandrium. Mol. Phylogenet. Evol. 2022, 168, 107417. [Google Scholar]
  136. Kim, H.S.; Bui, Q.T.N.; Wang, H.; Ki, J.S. Molecular cloning, origin, and expression of saxitoxin biosynthesis gene sxtB from the toxic dinoflagellate Alexandrium catenella. J. Appl. Phycol. 2023, 35, 673–685. [Google Scholar] [CrossRef]
  137. Mihali, T.K.; Kellmann, R.; Neilan, B.A. Characterisation of the paralytic shellfish toxin biosynthesis gene clusters in Anabaena circinalis AWQC131C and Aphanizomenon sp. NH-5. BMC Biochem. 2009, 10, 1–13. [Google Scholar] [CrossRef] [PubMed]
  138. Mihali, T.K.; Carmichael, W.W.; Neilan, B.A. A putative gene cluster from a Lyngbya wollei bloom that encodes paralytic shellfish toxin biosynthesis. PLoS ONE 2011, 6, e14657. [Google Scholar] [CrossRef] [PubMed]
  139. Cullen, A.; D’Agostino, P.M.; Mazmouz, R.; Pickford, R.; Wood, S.; Neilan, B.A. Insertions within the saxitoxin biosynthetic gene cluster result in differential toxin profiles. ACS Chem. Biol. 2018, 13, 3107–3114. [Google Scholar] [CrossRef] [PubMed]
  140. Chekan, J.R.; Fallon, T.R.; Moore, B.S. Biosynthesis of marine toxins. Curr. Opin. Chem. Biol. 2020, 59, 119–129. [Google Scholar] [CrossRef] [PubMed]
  141. Orr, R.J.; Stüken, A.; Murray, S.A.; Jakobsen, K.S. Evolutionary acquisition and loss of saxitoxin biosynthesis in dinoflagellates: The second “core” gene, sxtG. Appl. Environ. Microbiol. 2013, 79, 2128–2136. [Google Scholar] [CrossRef]
  142. Akbar, M.A.; Mohd Yusof, N.Y.; Tahir, N.I.; Ahmad, A.; Usup, G.; Sahrani, F.K.; Bunawan, H. Biosynthesis of saxitoxin in marine dinoflagellates: An omics perspective. Mar. Drugs 2020, 18, 103. [Google Scholar] [CrossRef] [PubMed]
  143. Kim, H.S.; Bui, Q.T.N.; Shin, J.; Wang, H.; Ki, J.S. Promoter regions of sxtA and sxtG reveal relationship between saxitoxin biosynthesis and photosynthesis in toxic Alexandrium catenella. J. Appl. Phycol. 2024, 1–15. [Google Scholar] [CrossRef]
  144. Wang, H.; Kim, H.; Ki, J.-S. Preliminary result of de novo transcriptome sequencing of the marine toxic dinoflagellate Alexandrium catenella incubated under several different stresses. Mar. Biol. 2021, 168, 104. [Google Scholar] [CrossRef]
  145. Naves, J.L.; Prado, M.P.; Rangel, M.; De Sanctis, B.; Machado-Santelli, G.; Freitas, J.C. Cytotoxicity in the marine dinoflagellate Prorocentrum mexicanum from Brazil. Comp. Biochem. Physiol. C Toxicol. Pharmacol. 2006, 143, 73–77. [Google Scholar] [CrossRef] [PubMed]
  146. Bui, Q.T.N.; Ki, J.S. Molecular characterization and expression analysis of saxitoxin biosynthesis gene sxtU from toxigenic dinoflagellate Alexandrium pacificum. J. Appl. Phycol. 2023, 35, 687–700. [Google Scholar] [CrossRef]
Toxins 16 00210 g001
Figure 1. Molecular structures of different hazardous toxins derived from phytoplankton: (a) saxitoxins (STXs); (b) brevetoxin type A; (c) brevetoxin type B; (d) maitotoxins (MTXs); (e) ciguatoxins (CTXs); (f) pinnatoxins (PnTXs); (g) palytoxins (PLTXs); (h) yessotoxins; (i) zooxanthellatoxins; (j) dinophysistoxins; (k) karlotoxins; (l) azaspiracids (AZAs); (m) okadaic acid; and (n) domoic acid.
Figure 1. Molecular structures of different hazardous toxins derived from phytoplankton: (a) saxitoxins (STXs); (b) brevetoxin type A; (c) brevetoxin type B; (d) maitotoxins (MTXs); (e) ciguatoxins (CTXs); (f) pinnatoxins (PnTXs); (g) palytoxins (PLTXs); (h) yessotoxins; (i) zooxanthellatoxins; (j) dinophysistoxins; (k) karlotoxins; (l) azaspiracids (AZAs); (m) okadaic acid; and (n) domoic acid.
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Figure 2. A schematic view of environmental factors that affect cell physiology and saxitoxin: temperature, salinity, nutrients, and light on the physiological metabolism and toxin production of Alexandrium. Up and down arrows represent an increase and decrease in the parameters.
Figure 2. A schematic view of environmental factors that affect cell physiology and saxitoxin: temperature, salinity, nutrients, and light on the physiological metabolism and toxin production of Alexandrium. Up and down arrows represent an increase and decrease in the parameters.
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Figure 3. PST biosynthetic pathway in dinoflagellates. The sxt core and tailoring genes are in red and blue circles. The STX analogs are in colored rectangles. Gray indicates added groups catalyzed by each enzyme. ACP, acyl carrier protein; CoA, malonyl-CoA; Arg, arginine; NAD(P)+/NAD(P)H, oxidized/reduced forms of nicotinamide adenine dinucleotide; STX, saxitoxin; dcSTX, decarbamoyl-saxitoxin; GTXs, gonyautoxins; neoSTX, neosaxitoxin; C, N-sulfocarbamoyl-saxitoxin. Modified from Kellmann et al. [125], Mihali et al. [137,138], and Cullen et al. [139].
Figure 3. PST biosynthetic pathway in dinoflagellates. The sxt core and tailoring genes are in red and blue circles. The STX analogs are in colored rectangles. Gray indicates added groups catalyzed by each enzyme. ACP, acyl carrier protein; CoA, malonyl-CoA; Arg, arginine; NAD(P)+/NAD(P)H, oxidized/reduced forms of nicotinamide adenine dinucleotide; STX, saxitoxin; dcSTX, decarbamoyl-saxitoxin; GTXs, gonyautoxins; neoSTX, neosaxitoxin; C, N-sulfocarbamoyl-saxitoxin. Modified from Kellmann et al. [125], Mihali et al. [137,138], and Cullen et al. [139].
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Figure 4. A schematic representation of the STXs production pathway and gene regulations in toxic Alexandrium under temperature and salinity stresses. Thick up and down arrows represent an increase and decrease in parameters.
Figure 4. A schematic representation of the STXs production pathway and gene regulations in toxic Alexandrium under temperature and salinity stresses. Thick up and down arrows represent an increase and decrease in parameters.
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Table 2. Saxitoxins (STXs) production in the genus Alexandrium under different temperature conditions from the published literature. STXs equivalent (STXs eq) values are rounded up to a single digit.
Table 2. Saxitoxins (STXs) production in the genus Alexandrium under different temperature conditions from the published literature. STXs equivalent (STXs eq) values are rounded up to a single digit.
SpeciesStrainOriginTemperatureToxinsSTXs eq (fmol/cell)Reference
A. catenellaACC02Chile10–16 °C−3–75[88]
ATTL01France15 °C−0.2[89]
Alex03Republic of Korea12–20 °CneoSTX, dcSTX, dcGTX2, STX, GTX1–6, C1–215–97[26]
CCAP1119/27Scotland15 °C−9[90]
A. fundyenseBOFUSA5–20 °CSTX, neoSTX, GTX1–4211–544[91]
MIUSA5–20 °CSTX, neoSTX, GTX1–4100–532
A. lusitanicumBAH91Portugal15 °CGTX1–416[86]
AL3TGulf of Trieste15 °CGTX1–43
A. minutumAmSp01Vietnam25 ℃neoSTX, GTX1/3/411–13[92]
AmSp03Vietnam25 ℃neoSTX, GTX1/49–12
AmSp04Vietnam25 ℃neoSTX, GTX1/3/45–11
AmSp05Vietnam25 ℃dcSTX, neoSTX, GTX1–43–10
AmSp17Vietnam25 ℃dcSTX, neoSTX, GTX1/3/45
A. tamarenseATHS–95Japan17 °CC1–2, GTX1–41–3[85]
BAH181Orkney Island15 °CneoSTX, STX, B1–2, C1–2, GTX1–442[86]
GTPP01USA15 °CneoSTX, STX, B1–2, C1–2, GTX1–433
A. pacificumANG4–4Algerian20 °CneoSTX, STX, C2, GTX4/64[93]
Alex05Republic of Korea12–20 °CneoSTX, dcSTX, dcGTX2, STX, GTX1–6, C1–20.3–132[31]
IFR-ACA-15Mediterranean Sea17 °CC1–2, GTX4–5, dcGTX210–22[94]
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MDPI and ACS Style

Bui, Q.T.N.; Pradhan, B.; Kim, H.-S.; Ki, J.-S. Environmental Factors Modulate Saxitoxins (STXs) Production in Toxic Dinoflagellate Alexandrium: An Updated Review of STXs and Synthesis Gene Aspects. Toxins 2024, 16, 210. https://doi.org/10.3390/toxins16050210

AMA Style

Bui QTN, Pradhan B, Kim H-S, Ki J-S. Environmental Factors Modulate Saxitoxins (STXs) Production in Toxic Dinoflagellate Alexandrium: An Updated Review of STXs and Synthesis Gene Aspects. Toxins. 2024; 16(5):210. https://doi.org/10.3390/toxins16050210

Chicago/Turabian Style

Bui, Quynh Thi Nhu, Biswajita Pradhan, Han-Sol Kim, and Jang-Seu Ki. 2024. "Environmental Factors Modulate Saxitoxins (STXs) Production in Toxic Dinoflagellate Alexandrium: An Updated Review of STXs and Synthesis Gene Aspects" Toxins 16, no. 5: 210. https://doi.org/10.3390/toxins16050210

APA Style

Bui, Q. T. N., Pradhan, B., Kim, H. -S., & Ki, J. -S. (2024). Environmental Factors Modulate Saxitoxins (STXs) Production in Toxic Dinoflagellate Alexandrium: An Updated Review of STXs and Synthesis Gene Aspects. Toxins, 16(5), 210. https://doi.org/10.3390/toxins16050210

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