Toxic cyanobacterial cells containing microcystins induce oxidative stress in exposed tilapia fish (Oreochromis sp.) under laboratory conditions

The use of the fish cell lines RTG-2 and PLHC-1 to compare the toxic effects produced by microcystins LR and RR

Cyanobacterial toxins, especially microcystins (MC), are found in eutrophied waters through the world. Acute poisonings of animals and humans has been reported following MC exposure. In the present study, two fish cell lines, PLHC-1 and RTG-2, were evaluated after exposure to the cyanobacterial toxins MC-LR and MC-RR. The effects of different concentrations of the toxins were investigated in both cell lines at morphological and biochemical levels (total protein content, lactate dehydrogenase leakage, lysosomal activity and succinate dehydrogenase activity). The results obtained showed a decrease in protein content and no relevant increase in cell disruption, except for MC-LR in PLHC-1 cells. Morphological changes produced by microcystins were cellular swelling, blebbling, rounding, reduction in the cell number and increase in the number and size of lysosomal bodies. In addition, steatosis was produced in hepatoma PLHC-1 cells, particularly with MC-RR. Furthermore, the fish PLHC-1 cell line was more sensitive than RTG-2 cells to the cyanobacterial toxins compared, being the stimulation of the lysosomal function and the induction of steatosis the most specific changes detected.

Acid and alkaline phosphatase activities and pathological changes induced in Tilapia fish (Oreochromis sp.) exposed subchronically to microcystins from toxic cyanobacterial blooms under laboratory conditions

The effects of microcystins (MCs) from cyanobacterial cells on the enzymatic activities of acid and alkaline phosphatases (ACP and ALP) from liver, kidney and gill tissues, and the histopathological changes in freshwater Tilapia fish (Oreochromis sp.) were investigated under laboratory conditions. Fish were exposed to cyanobacterial cells (60.0 microg MC-LR/fish per day) through their diet at different exposure times (14 and 21 days). The cells were fed to the fish in two types of oral administration: mixed with a commercial fish food or crushed into a commercial fish food so that the toxins were released. ACP and ALP activities changed in response to MCs in a time-dependent manner, and these changes were more prominent in liver and kidney. The way the MCs were administered had no influence on the biochemical parameters. Similarly, the most severe histopathological changes were observed in the same two organs, although the gills and intestines were also affected. The parenchymal architecture of the liver was dissolved, and round hepatocytes with the appearance of pyknotic nuclei were detected. Kidney lesions consisted of the dilation of Bowman's space and necrotic epithelial cells with pyknotic nuclei in the tubules. These findings suggest that low and repeated doses of MC-LR from cyanobacterial cells induce toxicity in tilapia fish although no adverse effects were detected.