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Article

Enhanced Resting Cyst Production in Harmful Dinoflagellate Akashiwo sanguinea Amended with Taebaek Coal Powder

1
Industry-Academia Cooperation Foundation, Gangneung Yeongdong University, Gangneung 25521, Republic of Korea
2
Biological Resource Center/Korean Collection for Type Cultures (KCTC), Korea Research Institute of Bioscience and Biotechnology, Jeongeup 56212, Republic of Korea
3
Office of the President, Gangneung Yeongdong University, Gangneung 25521, Republic of Korea
4
Department of Bioresource & Environmental Engineering, KRIBB School of Biotechnology, University of Science and Technology (UST), Daejeon 34113, Republic of Korea
*
Authors to whom correspondence should be addressed.
J. Mar. Sci. Eng. 2026, 14(4), 332; https://doi.org/10.3390/jmse14040332
Submission received: 30 December 2025 / Revised: 31 January 2026 / Accepted: 6 February 2026 / Published: 9 February 2026
(This article belongs to the Section Marine Biology)

Abstract

The dinoflagellate Akashiwo sanguinea is a prominent harmful algal bloom (HAB) species responsible for significant mortalities of marine fauna. Its life cycle, which includes a benthic resting cyst stage, is fundamental to its bloom dynamics and geographic dispersal. This study investigates the effects of Taebaek coal powder, a silicate-rich mineral supplement, on the growth and life-stage transitions of A. sanguinea. Cultures were grown in standard f/2 medium (control) and f/2 medium amended with an extract of the coal powder. We monitored culture performance using fluorometry for quantitative biomass assessment and imaging flow cytometry (FlowCam) for qualitative life-stage analysis. The coal powder amendment conferred a distinct advantage, promoting both vegetative proliferation and the formation of resting cysts. Fluorescence-based measurements showed that the coal powder-amended cultures reached a density equivalent of 3851 ± 214 cells mL−1 by day 4, significantly outpacing the control (2963 ± 351 cells mL−1). Peak vegetative abundance in the treated cultures reached 6967 ± 423 cells mL−1 on day 14, compared to 5979 ± 288 cells mL−1 in the control. Critically, resting cyst production was substantially enhanced in the coal powder treatment, with densities reaching 32–37 cysts mL−1 by the end of the experiment, compared to 22–26 cysts mL−1 in the control. These findings demonstrate that mineral supplementation with Taebaek coal powder can significantly augment both vegetative growth and encystment in A. sanguinea, suggesting a potential link to micronutrient availability, though the underlying mechanisms remain to be elucidated. This enhanced cyst production method may prove valuable for harvesting cysts for ecophysiological research and highlights the need to explore how mineral-induced life-cycle shifts could influence bloom dynamics in a context-dependent manner.

1. Introduction

The unarmored dinoflagellate Akashiwo sanguinea (Hirasaka) G. Hansen & Moestrup is a cosmopolitan species commonly observed in estuarine and coastal waters worldwide [1,2]. This species is notorious for forming extensive, persistent, and often monospecific harmful algal blooms (HABs) [3]. These blooms pose a significant threat to marine ecosystems and coastal economies. For instance, large-scale blooms have been directly linked to mass mortalities of fish and invertebrates, primarily due to the generation of anoxic conditions upon bloom decay [4,5]. Furthermore, A. sanguinea blooms can produce massive proteinaceous surfactants that coat the feathers of seabirds, neutralizing their natural water repellency and insulation and leading to death from hypothermia [6]. Given these severe ecological and economic impacts, understanding the mechanisms that regulate the life cycle and bloom dynamics of A. sanguinea is of paramount importance.
The life history of A. sanguinea, like many dinoflagellates, involves a biphasic cycle that alternates between a motile, planktonic vegetative stage and a dormant, benthic resting cyst stage [7,8]. The formation of these resting cysts, typically through sexual reproduction, is a critical ecological strategy that confers numerous advantages. Cysts can remain viable in sediments for extended periods, with A. sanguinea cysts reported to survive for up to 9 months [7]. This dormancy allows the species to endure unfavorable environmental conditions, such as extreme temperatures, nutrient depletion, or darkness [9,10]. Subsequently, these benthic cyst beds act as a seed bank for re-populating the water column when conditions become favorable again, thereby initiating recurrent blooms and contributing to their geographical dispersal and long-term persistence [8,11].
The transition from vegetative growth to sexual reproduction and encystment is governed by a complex interplay of environmental cues. Factors such as temperature, light, and grazing pressure are known to play a role [9,10]. However, nutrient availability is widely recognized as one of the most critical triggers [12]. For many dinoflagellate species, including A. sanguinea, limitation of macronutrients, particularly nitrogen, is a potent inducer of encystment [13,14]. Under nitrogen-limited conditions, A. sanguinea undergoes significant physiological and biochemical changes, diverting resources away from cell division and towards the production of energy-rich storage compounds. Studies have shown that newly formed cysts contain significantly lower levels of chlorophyll and protein but exhibit a massive accumulation of carbohydrates and lipids, which serve as energy reserves to sustain the cell during dormancy and fuel subsequent germination [14,15].
While the role of macronutrients (N, P) in regulating dinoflagellate life cycles has been extensively studied, the influence of mineral particles and their associated trace elements remains a significant knowledge gap. Natural waters, especially in coastal and estuarine systems, contain a complex matrix of suspended minerals that can influence phytoplankton physiology. These mineral dusts can act as a source of essential trace metals (e.g., Fe, Mn, Zn), which are required as cofactors for numerous metabolic enzymes involved in photosynthesis and nutrient assimilation [16]. Conversely, they can also act as stressors or alter the bioavailability of other nutrients in the water column. The precise impact of such mineral-rich microenvironments on the life-cycle progression of HAB species like A. sanguinea is not well characterized.
Taebaek coal ore is a refused coal ore (Shell type) from the coal mining region of Taebaek, Republic of Korea. This material is primarily composed of silica (SiO2, 61.1%) and alumina (Al2O3, 17.7%), with significant amounts of carbon (9.31%), iron oxide (Fe2O3, 5.17%), and various trace elements including potassium, calcium, magnesium, and manganese [17]. Due to its complex mineralogical composition, Taebaek coal powder has been investigated for various recycling applications, including as a raw material for glass and ceramics. Given this composition, we hypothesized that an aqueous extract from Taebaek coal powder could provide a controlled source of dissolved mineral-derived trace elements in sterile culture and serve as a simplified model system to test how mineral/trace-element enrichment influences the physiological state and life-cycle progression of A. sanguinea.
To test this hypothesis in a controlled setting, we prepared a sterile coal-derived leachate (coal powder-conditioned seawater) and compared cultures grown in coal powder–amended versus standard f/2 media. The primary research question of this study was: Does supplementation with a coal powder extract enhance vegetative growth and, more importantly, the production of resting cysts in A. sanguinea? To address this, we provided a comparative analysis of vegetative growth, life-stage transitions, and, most importantly, the efficiency of resting cyst production. By employing high-throughput flow imaging microscopy (FlowCam) alongside traditional fluorometric methods, we characterized the impact of the mineral amendment on both population growth and life-stage transitions. The results provide novel insights into the role of natural mineral supplements in regulating dinoflagellate life cycles and offer a practical method for enhancing cyst yields for research, while also laying a foundation for future studies examining how mineral-induced encystment may influence HAB dynamics in a context-dependent manner.

2. Materials and Methods

2.1. Algal Culture and Maintenance

A clonal, axenic culture of Akashiwo sanguinea AS01 was obtained from the Korean Collection for Type Cultures (KCTC). Stock cultures were maintained in silicate-free f/2 medium, prepared using natural seawater that was filtered through a 0.22 µm membrane and subsequently autoclaved at 121 °C for 30 min. The salinity of the medium was adjusted to 35 psu using sterile distilled water or concentrated seawater brine. The cultures were incubated at 20 ± 1 °C under a 12:12 h light–dark cycle, with illumination provided by cool white fluorescent lamps at a photon flux of approximately 100 µmol photons m−2 s−1 [18]. To maintain the cultures in the exponential growth phase, they were transferred to fresh f/2 medium every two weeks.

2.2. Taebaek Coal Powder and Preparation of Amended Medium

The refused coal ore used in this study was sourced from a mine in Taebaek, Republic of Korea. The material was finely ground to a powder with a particle size of less than 100 µm. A conditioned seawater medium was prepared by adding 10 g of the Taebaek coal powder to 1 L of 0.22 µm-filtered natural seawater. The mixture was autoclaved at 121 °C for 15 min, allowed to cool, and then filtered again through a 0.22 µm membrane to remove remaining particulates. This process yielded a clear, mineral-enriched seawater. This conditioned seawater was then used as the base for preparing the f/2 medium, following the standard f/2 nutrient enrichment protocol. This final medium is referred to as the “coal powder-amended medium.” The control medium consisted of standard f/2 prepared with the same batch of filtered and autoclaved seawater but without the coal powder treatment. It should be noted that this process creates a leachate, and the precise chemical composition of the dissolved components was not characterized in this study. Because the extract was produced by autoclaving and re-filtration, the resulting chemical speciation and bioavailability of dissolved constituents may differ from natural coastal mineral inputs (e.g., dust deposition or sediment resuspension), which often include particle-associated phases and occur without sterilization. Accordingly, this treatment should be considered a simplified, sterile leachate model rather than a direct environmental analog; importantly, the control medium underwent the same filtration and autoclaving steps to ensure internal comparability.

2.3. Growth and Encystment of A. sanguinea

Time-course experiments using batch cultures were conducted to determine the effects of the Taebaek coal powder amendment on the growth and cyst formation of A. sanguinea. All treatments were conducted in triplicate in 2 L Erlenmeyer culture flasks containing 1 L of medium. Algal cells from an exponential growth phase culture were inoculated into the flasks to achieve an initial cell density of approximately 300 cells mL−1. The flasks were incubated under the same temperature and light conditions as the stock cultures (20 ± 1 °C, 12:12 h L:D cycle, 100 µmol photons m−2·−1).
Morphological observations were performed on an inverted microscope at 200× to 400× magnification. Aliquots (2 mL) were settled in Utermöhl chambers for 30 min prior to observation. Vegetative cell dimensions were measured using an ocular micrometer. Resting cysts were identified by their spherical shape and thick wall. Images were recorded with a digital camera.
The specific growth rate (µ) was calculated for the exponential growth phase using the formula: µ = (ln(N2) − ln(N1))/(t2 − t1), where N1 and N2 are the cell densities at times t1 and t2.
Then, the Chl a concentrations were measured with a fluorometer (Trilogy, Turner Design, San Jose, CA, USA) by a fluorometric technique [19]. To convert fluorescence readings into cell densities, a calibration curve was established prior to the experiment by correlating fluorescence values with direct microscopic counts from a serial dilution of an A. sanguinea culture (R2 > 0.99).
Resting cyst counts were also recorded while monitoring algal growth according to the morphological characteristics described in Chen et al. (2015) [13]. Resting cysts were identified by their characteristic spherical shape and thick, smooth cell wall. The encystment ratio (S, %) during the experiment was calculated using the following equation:
S = (2 × C)/(M + 2 × C) × 100%
where C is the cyst density (cysts mL−1) and M is the vegetative cell density (cells mL−1).

2.4. Life-Stage Characterization by Imaging Flow Cytometry

Morphological characteristics, size distribution, and life-stage composition of the cultures were monitored every two days throughout the 20-day experimental period using a Benchtop FlowCam Cyano imaging flow cytometer (Yokogawa Fluid Imaging Technologies, Scarborough, ME, USA). This instrument combines flow cytometry with high-resolution digital imaging, enabling qualitative observation and morphological analysis of individual cells [20]. The FlowCam system was equipped with a 532 nm excitation laser and a color digital camera capable of capturing both brightfield and fluorescence images. For this study, a 10× objective lens was used in combination with a 100 μm flow cell to optimize image quality for A. sanguinea cells within the typical size range of this species. The system was operated in laser-trigger mode to ensure consistent detection of fluorescent particles while minimizing background interference. At each sampling time point, 1 mL aliquots were withdrawn from each culture bottle using sterile pipettes to prevent contamination. Each sample was processed immediately after collection to minimize potential artifacts from cell settling or behavioral changes. The FlowCam analysis parameters were standardized as follows: flow rate of 0.5 mL min−1, trigger threshold set to detect particles with equivalent spherical diameter (ESD) ≥ 10 μm, and image capture rate optimized to ensure high-quality images of all detected particles [21].

2.5. Image Analysis and Morphometric Measurements

Captured images were processed using Visual Spreadsheet software (Version 6, Fluid Imaging Technologies) to extract morphological parameters for each detected cell. The analysis protocol included automated particle detection followed by manual verification to ensure accurate identification of A. sanguinea cells and exclusion of debris or other particles. For each cell, the following morphometric parameters were measured: diameter, length, width and area. Cell size distributions were analyzed using 5 μm size bins to track temporal changes in population structure. Morphological classification was based on established criteria, including cell shape, size, and fluorescence characteristics.

2.6. Statistical Analysis

All data are presented as mean ± standard deviation (SD) from at least three independent experiments and analyzed by the GraphPad Prism 9.0 software (GraphPad Software Inc., La Jolla, CA, USA). Statistical comparisons between the control and coal powder-amended treatments were performed using a two-tailed Student’s t-test. If the p-value was less than 0.05 (* p < 0.05), the differences were considered statistically significant.

3. Results

3.1. Morphological Characterization of Life-Cycle Stages

Both light microscopy and FlowCam imaging successfully captured the key life-cycle stages of A. sanguinea throughout the 20-day culture period (Figure 1). Four distinct stages were identified: (1) motile vegetative cells, characterized by their typical pentagonal, dorsoventrally flattened morphology; (2) dividing vegetative cells, identified by the presence of a clear cleavage furrow; (3) sexually reproducing pairs, observed as closely appressed cells of similar size; and (4) non-motile resting cysts, distinguished by their spherical shape and thick, refractile cell wall. The FlowCam provided a high-throughput visualization of these stages, capturing the morphological continuum from vegetative cells to the formation of planozygotes and ultimately resting cysts (Figure 1I).

3.2. Effect of Coal Powder Amendment on Vegetative Growth

The addition of the Taebaek coal powder extract had a significant positive effect on the vegetative growth of A. sanguinea. The overall increase in phytoplankton biomass was quantified using chlorophyll a fluorescence as a proxy for cell density. These measurements indicated that while both treatments started at similar densities, the coal powder-amended cultures reached a density equivalent of 3851 ± 214 cells mL−1 by day 4, significantly outpacing the control (2963 ± 351 cells mL−1). This growth advantage was sustained, with the treated cultures peaking at a maximum density of 6967 ± 423 cells mL−1 on day 14, compared to 5979 ± 288 cells mL−1 in the control (Figure 2, Table 1). Consequently, the specific growth rate (µ) during the exponential phase, derived from these fluorescence data, was significantly higher in the coal powder treatment (0.299–0.314 d−1) than in the control (0.224–0.269 d−1).
To complement these bulk biomass measurements, imaging flow cytometry (FlowCam) was employed to qualitatively observe the population and confirm the presence of various life-history stages. The high-resolution images captured by the FlowCam provided visual confirmation of the fluorometry data, showing a visibly higher density of healthy vegetative cells in the amended cultures during the exponential growth phase. More importantly, this imaging approach was crucial for distinguishing vegetative cells from other life stages, such as dividing cells and developing cysts, which cannot be differentiated by bulk fluorescence alone. This qualitative visual evidence supported the quantitative finding that the coal powder amendment stimulated robust vegetative proliferation before the onset of mass encystment.

3.3. Enhancement of Resting Cyst Formation

The most striking effect of the Taebaek coal powder amendment was the significant enhancement of resting cyst production. While resting cysts were formed in both treatments as the cultures entered the stationary phase, their abundance was consistently and significantly higher in the coal powder-amended medium (Figure 3A). Cysts began to appear in both treatments around day 10, but their accumulation was more rapid in the treated cultures. By the end of the experiment (day 20), the resting cyst density in the coal powder treatment reached 32–37 cysts mL−1, which was approximately 1.5 times higher than the 22–26 cysts mL−1 observed in the control cultures (Figure 3A). In addition, the calculated encystment rate further supported this pattern (Figure 3B). The encystment rate of Akashiwo sanguinea in the control cultures remained relatively low, ranging from 4.02% to 5.45%, whereas it was markedly higher in the coal powder-amended cultures, reaching 8.33–9.45%. These data indicate that the mineral amendment increased net resting cyst accumulation and the apparent encystment ratio under our culture conditions

3.4. Cell Size Dynamics

FlowCam-based morphometric analyses of cell area (µm2), equivalent spherical diameter, cell length, and cell width were performed to determine whether the growth-promoting effect of coal powder amendment was associated with changes in cell size. Across the 20-day experimental period, all measured size parameters remained temporally stable within each treatment, with no evident shifts as cultures progressed from the exponential to the stationary phase (Figure 4A–H). Although the size distributions between treatments largely overlapped, cells in the coal powder-amended cultures consistently exhibited a slight reduction in area, diameter, length, and width compared with the control, without clear temporal variation (Figure 5A–D). These results indicate that the increased cell abundance observed under coal powder treatment was not accompanied by cell enlargement and was instead primarily attributable to enhanced cell division.

4. Discussion

This study demonstrates that a mineral-rich supplement derived from Taebaek coal powder acts as a potent stimulant for both vegetative growth and sexual encystment in the harmful algal bloom dinoflagellate, Akashiwo sanguinea. Cultures amended with the coal powder extract exhibited significantly higher growth rates, achieved greater peak population densities, and, most critically, produced a substantially higher yield of resting cysts compared to the standard f/2 medium control. These results underscore the pivotal role that mineral-derived micronutrients can play in modulating the life-cycle progression and population dynamics of this key HAB species.
The central finding of this research is the pronounced enhancement of encystment. Notably, the higher cyst abundance and encystment ratio observed here should be interpreted as enhanced net cyst accumulation, rather than definitive evidence of increased sexual induction efficiency. Although we morphologically observed sexual stages (e.g., paired cells/planozygote-like forms) by microscopy/FlowCam, we did not quantify key sexual reproduction dynamics such as gamete pairing efficiency or planozygote formation rates, nor did we assess cyst survival. Therefore, while the coal extract clearly increased the final number of morphologically defined resting cysts, the specific step(s) of the sexual cycle that are affected remain to be resolved. The transition from a motile, vegetative state to a dormant, benthic cyst is a cornerstone of the ecological strategy of many dinoflagellates, yet the precise environmental cues that govern this process are multifaceted. While macronutrient limitation, especially of nitrogen, is a well-documented trigger for encystment in A. sanguinea [13], our findings reveal that the mineralogical context is also a critical regulatory factor. However, because the culture-medium chemistry was not characterized (i.e., dissolved macronutrients and dissolved trace/heavy-metal concentrations were not quantified), the present study cannot provide preliminary validation for micronutrient modulation or metal-associated stress as causal drivers; therefore, these mechanistic explanations are advanced as working hypotheses rather than evidence-based conclusions.
One plausible mechanism is the alleviation of trace metal limitation. Standard f/2 medium, while robust, may not perfectly replicate the complex suite of micronutrients available in natural coastal waters. Trace metals such as iron (Fe), manganese (Mn), zinc (Zn), and selenium (Se) are indispensable for phytoplankton, serving as essential cofactors in a vast array of metabolic pathways, including photosynthesis, respiration, and nitrate assimilation [16]. The silicate-rich Taebaek coal powder likely leached a cocktail of these bioavailable trace elements into the medium. The observed increase in vegetative growth rates and overall biomass in the amended cultures strongly supports this hypothesis, as it points to a direct stimulation of cellular metabolism, likely by satisfying a latent micronutrient demand. For instance, Fe is a notorious limiting nutrient in many marine systems, and its role in the photosynthetic apparatus is paramount. Similarly, Mn is a core component of the oxygen-evolving complex in Photosystem II, and Se is known to be required by some dinoflagellates for optimal growth.
Alternatively, the increased cyst accumulation is consistent with a stress-associated shift in life-history allocation. While trace metals are required at low levels, elevated concentrations of certain metals can impose physiological constraints, including oxidative stress and cellular damage [16], and have been discussed as potential triggers of encystment in dinoflagellates under specific chemical regimes [16]. Under this framework, coal-derived dissolved constituents could, in principle, contribute to conditions under which enhanced growth and resting-stage formation co-occur. However, in the absence of measurements of dissolved trace-metal concentrations/speciation, macronutrients, and cellular stress indicators, support for a stress-mediated pathway remains indirect, and the mechanism underlying the observed response cannot be resolved in the present study.
A third possibility involves the indirect alteration of macronutrient dynamics. The fine mineral particles of the coal powder could have acted as surfaces for the adsorption of dissolved inorganic nitrogen from the medium. This process would accelerate the onset of nitrogen limitation within the culture, which is a known, potent trigger for encystment in A. sanguinea [13]. This pathway constitutes a plausible, non-exclusive hypothesis whereby initial growth stimulation may accelerate macronutrient drawdown and, potentially in conjunction with adsorption, bias cultures toward nitrogen limitation-associated sexual induction and resting cyst formation; importantly, any application-oriented extrapolation would need to explicitly account for heavy-metal contamination and nutrient-regime perturbation (including eutrophication), which were not evaluated in this study.
It is noteworthy that these significant physiological shifts occurred without a major alteration in cell size. The FlowCam imaging confirmed that the cell area distribution remained stable, indicating that the coal powder amendment influenced the rate of cell cycle progression and the direction of the life-history pathway, rather than general cell enlargement. This suggests a targeted regulatory effect on the cellular machinery controlling division and sexual induction, a phenomenon that merits further molecular investigation.
From a methodological standpoint, this work validates the power of combining traditional fluorometric quantification with high-throughput flow imaging. While fluorometry provided robust quantitative data on population growth, the FlowCam offered valuable qualitative insights into population structure and life-stage transitions with a speed and detail that would be unattainable with manual microscopy alone, offering a comprehensive view of the dynamic changes in the cultures.
In conclusion, this study demonstrates that supplementing standard f/2 culture medium with an extract from Taebaek coal powder significantly promotes both the vegetative growth and, more importantly, the sexual encystment of the dinoflagellate Akashiwo sanguinea. The mineral amendment resulted in higher cell densities and a substantially greater yield of resting cysts compared to the control. The underlying chemical drivers remain unresolved because dissolved macronutrients and dissolved trace/heavy-metal concentrations in the culture medium were not quantified; accordingly, micronutrient enrichment, metal-associated stress, and altered macronutrient availability should be interpreted as alternative hypotheses rather than validated mechanisms. Taken together, our axenic laboratory experiments show that supplementation with the Taebaek coal extract increased vegetative cell density and, in parallel, markedly elevated resting cyst yields in A. sanguinea. These results indicate that coal-derived mineral cues can modulate both growth and the life-cycle transition toward encystment under controlled conditions. However, several limitations of the present study should be acknowledged to guide future research. Primarily, the use of a single concentration of the coal powder extract prevents a clear distinction between the dual hypotheses of micronutrient stimulation and concentration-dependent physiological stress. Future investigations should prioritize a dose–response experimental design to decouple these potential mechanisms. Additionally, this study was conducted with a single axenic clonal strain, which limits the generalizability of our findings to genetically diverse natural populations. Finally, as cyst viability and germination were not assessed, our results reflect net cyst accumulation rather than the production of viable resting cysts. Incorporating dose–response relationships, strain diversity, and viability assays will be critical for advancing the understanding of how mineral inputs regulate dinoflagellate life cycles.

Author Contributions

Conceptualization, J.K.K. and Z.L.; methodology, J.K.K., X.L. and W.S.S.; software, X.L.; validation, J.K.K., X.L. and W.S.S.; formal analysis, J.K.K., X.L. and Z.L.; investigation, J.K.K.; resources, Z.L.; data curation, J.K.K. and Z.L.; writing—original draft preparation, J.K.K., X.L. and Z.L.; writing—review and editing, J.K.K., X.L., W.S.S., and Z.L.; funding acquisition, J.K.K. All authors have read and agreed to the published version of the manuscript.

Funding

This research was supported by the Regional Innovation System & Education (RISE) program through the Gangwon RISE Center, funded by the Ministry of Education (MOE) and the Gangwon State (G.S.), Republic of Korea (2025-RISE-10-010).

Data Availability Statement

The original contributions presented in this study are included in the article. Further inquiries can be directed to the corresponding authors.

Conflicts of Interest

The authors declare no conflicts of interest.

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Figure 1. Morphological characterization of Akashiwo sanguinea life-cycle stages. Representative images were captured using light microscopy (AD) and imaging flow cytometry (FlowCam; EI). Key stages identified include: (A,E) motile vegetative cell; (B,F) dividing vegetative cell; (C,G) gamete pair undergoing sexual fusion; and (D,H) dormant resting cyst. Panel I illustrates the morphological progression from a motile cell to a mature resting cyst as captured by FlowCam. Light microscopy (AD) scale bars = 20 μm. The classification of life-cycle stages follows established morphological descriptions of A. sanguinea reported by Tang et al. [1].
Figure 1. Morphological characterization of Akashiwo sanguinea life-cycle stages. Representative images were captured using light microscopy (AD) and imaging flow cytometry (FlowCam; EI). Key stages identified include: (A,E) motile vegetative cell; (B,F) dividing vegetative cell; (C,G) gamete pair undergoing sexual fusion; and (D,H) dormant resting cyst. Panel I illustrates the morphological progression from a motile cell to a mature resting cyst as captured by FlowCam. Light microscopy (AD) scale bars = 20 μm. The classification of life-cycle stages follows established morphological descriptions of A. sanguinea reported by Tang et al. [1].
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Figure 2. Effect of Taebaek coal powder amendment on the vegetative growth of Akashiwo sanguinea. (A) Temporal changes in cell density (cells mL−1) in control (standard f/2 medium) and coal powder-amended cultures, as determined by chlorophyll a fluorescence measurements. (B) Corresponding specific growth rates (d−1) calculated during the exponential growth phase. Data points represent the mean of triplicate cultures, and error bars indicate the standard deviation (SD). Asterisks denote statistically significant differences between treatments (* p < 0.05).
Figure 2. Effect of Taebaek coal powder amendment on the vegetative growth of Akashiwo sanguinea. (A) Temporal changes in cell density (cells mL−1) in control (standard f/2 medium) and coal powder-amended cultures, as determined by chlorophyll a fluorescence measurements. (B) Corresponding specific growth rates (d−1) calculated during the exponential growth phase. Data points represent the mean of triplicate cultures, and error bars indicate the standard deviation (SD). Asterisks denote statistically significant differences between treatments (* p < 0.05).
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Figure 3. Enhancement of resting cyst formation in Akashiwo sanguinea by Taebaek coal powder amendment. (A) Temporal progression of resting cyst density (cysts mL−1) in control and treated cultures over the 20-day experimental period. (B) Comparison of the final encystment rate (%) on day 20. All data are presented as the mean ± standard deviation (SD) of three independent replicates. Asterisks denote statistically significant differences between treatments (* p < 0.05).
Figure 3. Enhancement of resting cyst formation in Akashiwo sanguinea by Taebaek coal powder amendment. (A) Temporal progression of resting cyst density (cysts mL−1) in control and treated cultures over the 20-day experimental period. (B) Comparison of the final encystment rate (%) on day 20. All data are presented as the mean ± standard deviation (SD) of three independent replicates. Asterisks denote statistically significant differences between treatments (* p < 0.05).
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Figure 4. Analysis of Akashiwo sanguinea cell size dynamics in response to coal powder amendment. (AH) Temporal tracking of key morphometric parameters (cell area, equivalent spherical diameter, length, and width) throughout the 20-day experiment.
Figure 4. Analysis of Akashiwo sanguinea cell size dynamics in response to coal powder amendment. (AH) Temporal tracking of key morphometric parameters (cell area, equivalent spherical diameter, length, and width) throughout the 20-day experiment.
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Figure 5. Comparative histograms of cell morphometric parameters on day 14. (AD) Comparative histograms of cell area distribution for control and treated cultures, showing a consistent but slight reduction in cell size in the amended group. All measurements were obtained via FlowCam analysis.
Figure 5. Comparative histograms of cell morphometric parameters on day 14. (AD) Comparative histograms of cell area distribution for control and treated cultures, showing a consistent but slight reduction in cell size in the amended group. All measurements were obtained via FlowCam analysis.
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Table 1. Comparison of maximum specific growth rate (µ_max) and maximum cell density of Akashiwo sanguinea in control and coal powder-amended cultures, based on chlorophyll a fluorescence measurements.
Table 1. Comparison of maximum specific growth rate (µ_max) and maximum cell density of Akashiwo sanguinea in control and coal powder-amended cultures, based on chlorophyll a fluorescence measurements.
Treatmentµ_Max (d−1)Maximum Cell Density (Cells mL−1)
Control (f/2)0.615979 ± 288
Coal Powder0.626967 ± 423
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MDPI and ACS Style

Kim, J.K.; Lian, X.; Seo, W.S.; Li, Z. Enhanced Resting Cyst Production in Harmful Dinoflagellate Akashiwo sanguinea Amended with Taebaek Coal Powder. J. Mar. Sci. Eng. 2026, 14, 332. https://doi.org/10.3390/jmse14040332

AMA Style

Kim JK, Lian X, Seo WS, Li Z. Enhanced Resting Cyst Production in Harmful Dinoflagellate Akashiwo sanguinea Amended with Taebaek Coal Powder. Journal of Marine Science and Engineering. 2026; 14(4):332. https://doi.org/10.3390/jmse14040332

Chicago/Turabian Style

Kim, Jeong Kwon, Xudong Lian, Won Seok Seo, and Zhun Li. 2026. "Enhanced Resting Cyst Production in Harmful Dinoflagellate Akashiwo sanguinea Amended with Taebaek Coal Powder" Journal of Marine Science and Engineering 14, no. 4: 332. https://doi.org/10.3390/jmse14040332

APA Style

Kim, J. K., Lian, X., Seo, W. S., & Li, Z. (2026). Enhanced Resting Cyst Production in Harmful Dinoflagellate Akashiwo sanguinea Amended with Taebaek Coal Powder. Journal of Marine Science and Engineering, 14(4), 332. https://doi.org/10.3390/jmse14040332

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