A mixed bloom of Prorocentrum lima species complex
and Aphanocapsa sp. under hypersaline conditions in
a mangrove lagoon of the Seaflower Biosphere Reserve,
Colombian Caribbean
Fig. 1. Old Point Regional Park, San Andrés Island, Seaflower Biosphere Reserve, showing the small
mangrove lagoon where the reddish discoloration was observed.
In March 2026, a small mangrove lagoon (~3,200 m2) located within a
Rhizophora mangle forest in Old Point
Regional Park, Seaflower Biosphere Reserve, San Andrés Island, developed a
reddish discoloration that intensified in
April (Fig. 1). The coloration gradually
decreased during May, when the lagoon
returned to its characteristic brownish
appearance.
On 14 April 2026, during the period
of maximum water discoloration, water samples were collected using a 5 L
Van Dorn bottle for phytoplankton enumeration and phytopigment analysis.
Temperature, salinity, pH, and dissolved
oxygen (DO) were measured in situ using a WTW multiparameter probe. Phytoplankton organisms were examined
using scanning electron microscopy
(SEM) and light microscopy with a Leica DME microscope equipped with 40
and 100 objectives. For quantitative
analysis, thoroughly homogenized 1 mL
subsamples were transferred to SedgwickRafter counting chambers, and
HARMFUL ALGAE NEWS NO. 84 / 2026
cell abundance was expressed as cells
L1. For phytopigment analysis, water
samples were filtered through Whatman GF/F glass-fiber filters, pigments
were extracted in 90% acetone, and
concentrations were determined spectrophotometrically.
Microscopic examination revealed a
mixed bloom dominated by the Prorocentrum lima species complex (PLSC)
and a coccoid cyanobacterium provisionally identified as Aphanocapsa sp.
(Chroococcales). Estimated abundances
were 4.53106 and 6.20106 cells L1,
respectively. Most Prorocentrum cells
were oval to rounded, although some
exhibited a more angular or pentagonal
outline. Cells measured 2226 μm in
length and 1019 μm in width (n = 30).
The valves exhibited trichocyst pores, a
rounded to occasionally angular posterior margin, and a relatively straight anterior margin. A small central V-shaped
depression was observed at the anterior end, with no conspicuous apical
spine. A large central pyrenoid was also
visible under light microscopy (Fig. 2).
Following the taxonomic assessment
and comparison with diagnostic morphological characters, these specimens
are better assigned to the Prorocentrum
lima species complex (N. Chomérat,
pers. comm.). Because species boundaries within the complex can be difficult
to resolve using morphology alone, we
retain the complex designation rather
than making a molecularly unverified
species-level assignment.
The high chlorophyll-a concentration (350 108 μg L1), carotenoid
concentration (83.28 40 μg L1),
and phytoplankton cell densities were
consistent with a high-biomass mixed
bloom. The very low DO concentration
recorded during sampling (0.1 mg L1)
may have resulted from intense oxygen
consumption associated with elevated
microbial and phytoplankton biomass,
together with restricted water exchange
within the lagoon. Notably, the filtrate
retained a reddish coloration after filtration, suggesting that dissolved, colloidal, or submicron components may
also have contributed to the overall discoloration. Pigmented microorganisms,
including halophilic archaea and bacte-
Fig. 2. Light micrographs of Prorocentrum
lima species complex cells. Pr = pyrenoid.
11
Harmful Algae News An IOC Newsletter on Toxic Algae and Algal Blooms No. 84 September 2026 https://hab.ioc-unesco.org/ Unveiling biotic controls of Alexandrium minutum in the Ría de Vigo (NW Spain) Understanding biotic interactions that regulate the dynamics of harmful algal bloom (HAB) species r
Fig. 2. The study area in the Ría de Vigo (NW Spain). The red dots indicate the locations where the A. minutum strains were isolated. [1]. We propose that such stable abiotic conditions may facilitate the establishment and persistence of key biotic interactions between the microalgae and their micr
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Fig. 5. Box and whisker plot showing the response ratios (RR) of Alexandrium minutum growth to the addition of different Zostera marina exudates at low (200300 μM DOC) and high (500600 μM DOC) concentrations. A total of 14 and 10 response ratios were included for the low and high concentration treat
dinoflagellates. It has been suggested that phenolic compounds produced by marine angiosperms, e.g. [25], may play a significant role in the negative interaction between these plants and dinoflagellate growth [56, 21]. However, this hypothesis has not yet been experimentally tested. Acknowledgement
Intense algal bloom during the austral summer in Inglesa and Calderilla Bays (Atacama, Chile): phytoplankton monitoring, environmental observations and implications for coastal aquaculture Fig. 1. Seawater discoloration in Inglesa Bay sector, Caldera during the first week of February 2026. (A) and
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Fig. 5. Abundance of other microplankton groups in February 2026 at the five sampling stations in the Caldera Bay System. 2. Rodríguez L 1978. Noticiario Mensual del Museo de Historia Natural de Chile 22(266):69 3. Rodríguez L 1985. Rev Biol Mar 21:173197. https://hdl.handle. net/20.500.14330/PER01
An overview of the 20182025 monitoring, detection, and control programme for Alexandrium catenella in Southern Chile The frequency, persistence, and geographical extent of harmful algal blooms (HABs) caused by the dinoflagellate Alexandrium catenella have increased in southern Chile over recent deca
3. 4. 5. 6. 7. 8. Fig. 2. Annual number of analysed samples and positive detections between 2018 and 2025. Bars represent the total number of samples collected each year. The red area indicates positive results (number shown at the base of each bar), whereas the blue area corresponds to negative res
A mixed bloom of Prorocentrum lima species complex and Aphanocapsa sp. under hypersaline conditions in a mangrove lagoon of the Seaflower Biosphere Reserve, Colombian Caribbean Fig. 1. Old Point Regional Park, San Andrés Island, Seaflower Biosphere Reserve, showing the small mangrove lagoon where t
Table 1. Measurements of physicochemical characteristics recorded during the mixed bloom of the Prorocentrum lima species complex and Aphanocapsa sp. Old Point, Colombia Lago delle Nazioni, Italy Paracas Bay, Peru 14 April 2026 December 2019 January 2020 2729 August 2017 4.5 106 4.7 107 2
morphological and molecular identification of benthic Prorocentrum and cyanobacteria with measurements of dissolved inorganic nutrients, dissolved and particulate organic carbon, phycotoxins, microbial community composition, sediment resuspension, and water-exchange and salinity dynamics. Acknowled
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