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Article ? AI-assigned paper type based on the abstract. Classification may not be perfect — flag errors using the feedback button. Tier 2 ? Original research — experimental, observational, or case-control study. Direct primary evidence. Human Health Effects Sign in to save

A review and assessment of cyanobacterial toxins as cardiovascular health hazards

Archives of Toxicology 2022 35 citations ? Citation count from OpenAlex, updated daily. May differ slightly from the publisher's own count. Score: 50 ? 0–100 AI score estimating relevance to the microplastics field. Papers below 30 are filtered from public browse.
Zorica Svirčev, Liang Chen Liang Chen Geoffrey A. Codd, Liang Chen Geoffrey A. Codd, Liang Chen Kinga Sántha, Kinga Sántha, Liang Chen Damjana Drobac, Stamenko Šušak, Aleksandra Vulin, Liang Chen Tamara Palanački Malešević, Liang Chen Geoffrey A. Codd, Geoffrey A. Codd, Jussi Meriluoto, Jussi Meriluoto, Liang Chen Liang Chen

Summary

Researchers reviewed over 100 studies on the cardiovascular effects of cyanotoxins—potent compounds produced by algal blooms in eutrophic waters—finding evidence of harm across seven toxin classes but concluding that typical environmental exposures pose a greater risk to the liver than the heart.

Eutrophicated waters frequently support bloom-forming cyanobacteria, many of which produce potent cyanobacterial toxins (cyanotoxins). Cyanotoxins can cause adverse health effects in a wide range of organisms where the toxins may target the liver, other internal organs, mucous surfaces and the skin and nervous system. This review surveyed more than 100 studies concerning the cardiovascular toxicity of cyanotoxins and related topics. Over 60 studies have described various negative effects on the cardiovascular system by seven major types of cyanotoxins, i.e. the microcystin (MC), nodularin (NOD), cylindrospermopsin (CYN), anatoxin (ATX), guanitoxin (GNTX), saxitoxin (STX) and lyngbyatoxin (LTX) groups. Much of the research was done on rodents and fish using high, acutely toxin concentrations and unnatural exposure routes (such as intraperitoneal injection), and it is thus concluded that the emphasis in future studies should be on oral, chronic exposure of mammalian species at environmentally relevant concentrations. It is also suggested that future in vivo studies are conducted in parallel with studies on cells and tissues. In the light of the presented evidence, it is likely that cyanotoxins do not constitute a major risk to cardiovascular health under ordinary conditions met in everyday life. The risk of illnesses in other organs, in particular the liver, is higher under the same exposure conditions. However, adverse cardiovascular effects can be expected due to indirect effects arising from damage in other organs. In addition to risks related to extraordinary concentrations of the cyanotoxins and atypical exposure routes, chronic exposure together with co-existing diseases could make some of the cyanotoxins more dangerous to cardiovascular health.

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