The presence of microcystins and other cyanobacterial bioactive peptides in aquatic fauna collected from Greek freshwaters.
Toxic bloom-forming cyanobacteria can cause animal death and adversely affect human health. Blooms may contain microcystins (MCs), cyanobacterial heptapeptide hepatotoxins and other peptides such as anabaenopeptins and anabaenopeptilides. MCs have been shown to occur in various aquatic organisms including mussels, water snails, crustaceans and fish. Muscle and viscera samples from eight species of fish (Acipenser gueldenstaedtii, Carassius auratus, Carassius gibelio, Cyprinus carpio, Perca fluviatilis, Rutilus rubilio, Silurus aristotelis and Silurus glanis), a frog (Rana eperotica), a mussel (Anodonta sp.) and a water snail (Viviparus contectus) were analyzed by high-performance liquid chromatography (HPLC), protein phosphatase 1 (PP1) inhibition assay (PP1IA) and ELISA. MC(s) was detected in all fish, frog, mussel and water snail samples tested by PP1IA and ELISA, including the frog R. eperotica and the freshwater snail V. contectus, in which the occurrence of MCs was not previously known. MC concentration ranged from 20 to 1500 ng g(-1)dw and from 25 to 5400 ng g(-1)dw in muscle and visceral tissue of fishes and frogs, respectively. In mussel and water snail tissue MC concentration ranged from 1650 to 3495 ng g(-1)dw. HPLC analysis revealed peaks having the same UV spectrum as anabaenopeptin- or anabaenopeptilide-like compounds, not previously known to occur in aquatic fauna tissue. The concentrations of the compounds detected ranged from 1.5 to 230 microg g(-1)dw. Comparison of the PP1IA and ELISA showed that values obtained with PP1IA where higher than those obtained with ELISA. Anabaenopeptins and/or anabaenopeptilides occurring in faunal tissue may account for the higher PP1IA values as we found that PP1 activity was inhibited by the purified anabaenopeptins A (45-60% inhibition) and B (5-75% inhibition). Purified anabaenopeptilides 90A and 90B exhibited weaker PP1 inhibition activity (5-35 and 5-23% inhibition, respectively). This is the first report of MC occurrence in aquatic animals collected from freshwaters of southern Europe.
Gkelis
S
S
Department of Botany, P.O. Box 109, GR-541 24, Aristotle University of Thessaloniki, Greece.
Lanaras
T
T
Sivonen
K
K
D000818:Animals; D049877:Anodonta / Q000737:chemistry / Q000187:drug effects* / Q000502:physiology; D001427:Bacterial Toxins / Q000032:analysis; D002851:Chromatography, High Pressure Liquid / Q000662:veterinary; D000458:Cyanobacteria / Q000502:physiology*; D000087522:Cyanobacteria Toxins; D004797:Enzyme-Linked Immunosorbent Assay / Q000662:veterinary; D005399:Fishes / Q000502:physiology*; D005618:Fresh Water; D049851:Gastropoda / Q000737:chemistry / Q000187:drug effects* / Q000502:physiology; D006115:Greece; D008387:Marine Toxins / Q000032:analysis; D052998:Microcystins / Q000032:analysis*; D009132:Muscles / Q000737:chemistry; D010455:Peptides / Q000032:analysis; D010749:Phosphoprotein Phosphatases / Q000037:antagonists & inhibitors; D054645:Protein Phosphatase 1; D011898:Ranidae / Q000502:physiology*
D001427:Bacterial Toxins; D000087522:Cyanobacteria Toxins; D008387:Marine Toxins; D052998:Microcystins; D010455:Peptides; C078588:microcystin; D010749:Phosphoprotein Phosphatases; D054645:Protein Phosphatase 1