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editorial
. 2026 Feb 10;17:1794724. doi: 10.3389/fmicb.2026.1794724

Editorial: Occurrence of harmful algal blooms and marine biotoxins

Pierina Visciano 1,*
PMCID: PMC12929949  PMID: 41743131

This Research Topic aimed to explore the global circulation of harmful algal blooms (HABs), i.e., phytoplanktonic toxin-producing microalgae as a consequence of climate change and anthropogenic pollution sources (Griffith and Gobler, 2020). The objective was to understand changes in seasonal patterns, the frequency and location of HAB hotspots, and the diversity of causative species. HABs can produce marine biotoxins, which are classified as either water-soluble biotoxins, such as saxitoxin and domoic acid (responsible for paralytic shellfish poisoning and amnesic shellfish poisoning, respectively), or lipophilic biotoxins (i.e., okadaic acid and dinophysistoxins), which are associated with diarrhetic shellfish poisoning (Annunziata et al., 2023). Among the latter group, Dinophysis species are dominant along the coasts of many European countries and may cause the closure of shellfish collection areas due to the presence of okadaic acid analogs. Vieira et al. investigated the cell density of Dinophysis acuminata in water samples taken weekly along the Portuguese mainland coast over a 13-year period from 2006 to 2018 and found that it was primarily favored by low sea surface temperature and high photosynthetically active radiation. These environmental factors were selected as conditions for producing empirical models capable of predicting the algal population sizes.

Phytoplankton communities are also influenced by nutrient composition, which varies under various dynamic processes, such as submarine groundwater discharge (SGD), sediment suspension events, and upwelling. Becerra-Reynoso et al. reported rapid increases in diatom populations due to new nutrients supplied to the system by upwelling. Conversely, when alternative nutrients, such as dissolved or particulate organic nitrogen, were dispersed into the environment through SGD, mixoplankton (e.g., dinoflagellates and other unknown flagellates) tended to predominate.

The toxicity of a new strain of Karenia papilionacea, isolated from the Yellow Sea in China, was assessed by exposing marine organisms to cell cultures of this algal species. Significant adverse effects were reported, with more than 50% mortality occurring within 48 h for rotifers and finfish, and after 72 h for brine shrimp. A low impact on the hatching success of healthy brine shrimp eggs was observed (Chen, Gao et al.).

Mi and Liu described the structure and properties, origin, and toxicity of tetrodotoxin (TTX), a lethal neurotoxin most commonly found in fish belonging to the Tetrodontidae family, but also in other marine organisms, such as mollusks, echinoderms, and snails (Hu et al., 2022). The authors also summarized the most recent analytical methods for TTX detection, such as bioassays, immunoassays, chromatographic analysis, and biosensors, including their advantages and limitations.

Harmful cyanobacterial blooms (cyanoHABs) are particularly abundant in warm, nutrient-rich freshwater lakes, reservoirs, and estuaries. They produce secondary metabolites called cyanotoxins, which can have potential adverse effects on animals, plants, and humans. The impact of seasonal hydrological disturbances on cyanoHABs in coastal Louisiana was studied by Hammond et al., who found higher biomass and maximum microcystin concentrations in summer and fall compared to winter. The influence of weather on phytoplankton, along with that of water temperature and salinity, was also reported.

Microcystin toxicity is associated with protein phosphatase inhibition and potential liver cancer (Schreidah et al., 2020). Several control strategies have been actively explored, such as the coculture of Microcystis aeruginosa with bacterial species belonging to the genera Bacillus, Brevibacillus, and Chryseobacterium (Zhang et al., 2021, 2019). It should be noted, however, that the use of algicidal bacteria can induce the release of harmful secondary metabolites, and therefore, it is necessary to select specific strains capable of degrading both algae and cyanotoxins (Massey and Yang, 2020). Chen, Xiong et al. isolated a Bacillus subtilis strain with strong algaecidal activity against M. aeruginosa and microcystin-degrading ability. This degradation process may occur primarily within bacterial cells and has been associated with the mlr gene cluster, which encodes a set of enzymes capable of breaking down microcystin molecules (Morón-López et al., 2023).

Similarly, the coculture of M. aeruginosa with the non-toxin-producing cyanobacterium Synechococcus elongatus, supplemented with 3-(3,4-dichlorophenyl)-1,1-dimethylurea as a photosynthesis inhibitor, reduced both algal biomass and microcystin production. This activity was more effective at 30 °C than at 23 °C and under high-nitrogen, low-phosphorus conditions (Lee et al.).

In conclusion, global warming, acidification, and deoxygenation of marine and freshwater ecosystems, which cause eutrophication and HAB phenomena, should be addressed to protect the environment, animals, and human health. Including HAB species in experimental studies and monitoring programs could provide a more ecologically relevant perspective within a One Health approach.

Editorial on the Research Topic Occurrence of harmful algal blooms and marine biotoxins

Footnotes

Edited and reviewed by: Eva Sintes, Spanish Institute of Oceanography (IEO), Spain

Author contributions

PV: Writing – review & editing, Writing – original draft, Conceptualization, Investigation.

Conflict of interest

The author(s) declared that this work was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

The author PV declared that they were an editorial board member of Frontiers, at the time of submission. This had no impact on the peer review process and the final decision.

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References

  1. Annunziata L., Campana G., Aloia R., Scortichini G. (2023). Official controls for the determination of lipophilic marine biotoxins in mussels farmed along the Adriatic coast of Central Italy. J. Mass Spectrom. 9999, 1–11. doi: 10.1002/jms.4963 [DOI] [PubMed] [Google Scholar]
  2. Griffith A. W., Gobler C. J. (2020). Harmful algal blooms: a climate change co-stressor in marine and freshwater ecosystems. Harm. Algae 91:101590. doi: 10.1016/j.hal.2019.03.008 [DOI] [PubMed] [Google Scholar]
  3. Hu C., Zhang Y., Zhou Y., Xiang Y., Liu Z., Wang Z., et al. (2022). Tetrodotoxin and its analogues in food: recent updates on sample preparation and analytical methods since 2012. J. Agric. Food Chem. 70, 12249–12269. doi: 10.1021/acs.jafc.2c04106 [DOI] [PubMed] [Google Scholar]
  4. Massey I. Y., Yang F. (2020). A mini review on microcystins and bacterial degradation. Toxins 12:268. doi: 10.3390/toxins12040268 [DOI] [PMC free article] [PubMed] [Google Scholar]
  5. Morón-López J., Serwecińska L., Balcerzak Ł., Glińska S., Mankiewicz-Boczek J. (2023). Algicidal bacteria against cyanobacteria: practical knowledge from laboratory to application. Crit. Rev. Environ. Sci. Technol. 54, 239–266. doi: 10.1080/10643389.2023.2232257 [DOI] [Google Scholar]
  6. Schreidah C. M., Ratnayake K., Senarath K., Karunarathne A. (2020). Microcystins: biogenesis, toxicity, analysis, and control. Chem. Res. Toxicol. 33, 2225–2246. doi: 10.1021/acs.chemrestox.0c00164 [DOI] [PubMed] [Google Scholar]
  7. Zhang C., Massey I. Y., Liu Y., Huang F., Gao R., Ding M., et al. (2019). Identification and characterization of a novel indigenous algicidal bacterium Chryseobacterium species against Microcystis aeruginosa. J. Toxic. Environ. Health A 82, 845–853. doi: 10.1080/15287394.2019.1660466 [DOI] [PubMed] [Google Scholar]
  8. Zhang Y., Chen D., Zhang N., Li F., Luo X., Li Q., et al. (2021). Transcriptional analysis of Microcystis aeruginosa co-cultured with algicidal bacteria Brevibacillus laterosporus. Int. J. Environ. Res. Public Health 18:8615. doi: 10.3390/ijerph18168615 [DOI] [PMC free article] [PubMed] [Google Scholar]

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