Cyanobacterial bloom monitoring and assessment in Latin America

•There is limited data on cyanobacterial blooms and cyanotoxins in Latin America.•The perception of what constitutes a cyanobacterial bloom varies within and among countries.•Toxic cyanobacterial blooms are found in waterbodies used for different purposes.•Regulations regarding cyanobacteria and cya...

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Published in:Harmful algae Vol. 125; p. 102429
Main Authors: Aguilera, Anabella, Almanza, Viviana, Haakonsson, Signe, Palacio, Hilda, Benitez Rodas, Gilberto A., Barros, Mário U.G., Capelo-Neto, José, Urrutia, Roberto, Aubriot, Luis, Bonilla, Sylvia
Format: Journal Article
Language:English
Published: Netherlands Elsevier B.V 01-06-2023
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Summary:•There is limited data on cyanobacterial blooms and cyanotoxins in Latin America.•The perception of what constitutes a cyanobacterial bloom varies within and among countries.•Toxic cyanobacterial blooms are found in waterbodies used for different purposes.•Regulations regarding cyanobacteria and cyanotoxins in drinking and recreative waters are needed. Cyanobacterial blooms have serious adverse effects on human and environmental health. In Latin America, one of the main world's freshwater reserves, information on this phenomenon remains sparse. To assess the current situation, we gathered reports of cyanobacterial blooms and associated cyanotoxins in freshwater bodies from South America and the Caribbean (Latitude 22° N to 45° S) and compiled the regulation and monitoring procedures implemented in each country. As the operational definition of what is a cyanobacterial bloom remains controversial, we also analyzed the criteria used to determine the phenomena in the region. From 2000 to 2019, blooms were reported in 295 water bodies distributed in 14 countries, including shallow and deep lakes, reservoirs, and rivers. Cyanotoxins were found in nine countries and high concentrations of microcystins were reported in all types of water bodies. Blooms were defined according to different, and sometimes arbitrary criteria including qualitative (changes in water color, scum presence), quantitative (abundance), or both. We found 13 different cell abundance thresholds defining bloom events, from 2 × 103 to 1 × 107 cells mL−1. The use of different criteria hampers the estimation of bloom occurrence, and consequently the associated risks and economic impacts. The large differences between countries in terms of number of studies, monitoring efforts, public access to the data and regulations regarding cyanobacteria and cyanotoxins highlights the need to rethink cyanobacterial bloom monitoring, seeking common criteria. General policies leading to solid frameworks based on defined criteria are needed to improve the assessment of cyanobacterial blooms in Latin America. This review represents a starting point toward common approaches for cyanobacterial monitoring and risk assessment, needed to improve regional environmental policies.
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ISSN:1568-9883
1878-1470
1878-1470
DOI:10.1016/j.hal.2023.102429