Brian G. Kotak

VARIABILITY OF THE HEPATOTOXIN MICROCYSTIN‐LR IN HYPEREUTROPHIC DRINKING WATER LAKES1

The patterns of occurrence of the peptide hepatotoxin microcystin‐LR (MC‐LR) was studied in three hypereu‐trophic hardwater lakes (Coal, Driedmeat, and Little Beaver) in central Alberta, Canada, over three open‐water seasons. MC‐LR concentration was based on high‐performance liquid chromatography detection and expressed as μg.g−1 of total plankton biomass, ng.L−1 of lake water, and μg.g−1 of Microcystis aeruginosa Kuetz. emend. Elenkin. MC‐LR was highly variable temporally (differences up to 3 orders of magnitude) within each lake over an individual year, between years in an individual lake, and between lakes in any year. Seasonal (within‐year) changes in MC‐LR concentration (expressed in the preceding units) were positively correlated to the abundance and biomass Of the cyanobacterium M. aeruginosa (r =0.60–0.77), total and total dissolved phosphorus concentration (r =0.46–0.59), pH (r=0.38–0.58), and chlorophyll a (r=0.25–0.59). Surprisingly, there was no relationship between MC‐LR concentration and water temperature (range: 7°‐24°C, r =‐0.13 to 0.02) and a negative correlation with nitrate concentration (r =–0.27 to ‐0.34). In two synoptic surveys examining spatial variability, MC‐LR concentrations were quite variable (CV of 185 and 36% between sampling sites for Coal and Little Beaver lakes, respectively). Spatial distribution of MC‐LR on any one day was correlated with the abundance and biomass of M. aeruginosa. Over a 24‐h period, MC‐LR concentration in M. aeruginosa decreased more than 6‐fold at night relative to daytime concentrations. In general, analytical and within‐site variation of MC‐LR was relatively small (CV < 4 and 9%, respectively) but greatest both within and between years in a lake followed by diel and spatial variation.

Occurrence and toxicological evaluation of cyanobacterial toxins in Alberta lakes and farm dugouts

Abstract The occurrence of neuro- and hepatotoxins produced by cyanobacteria (blue-green algae) was assessed in eight lakes and six farm dugouts, located in Alberta. Anatoxin-a, an alkaloid neurotoxin produced by Anabaena flos-aquae , was not detected in the lake blooms with gas chromatography-mass spectrometry (GC-MS). Algal blooms which contained Microcystis aeruginosa almost always had detectable concentrations of microcystin-LR, a peptide hepatotoxin, based on high performance liquid chromatography (HPLC) analyses. Bloom samples from the six farm dugouts contained no detectable quantity of either anatoxin-a or microcystin-LR. However, anatoxin-a and microcystin-LR were detected in algae isolated and subsequently cultured from two separate dugouts. Microcystin-RR was not detected in any bloom sample collected. Among three lakes studied in greater detail, the concentration of microcystin-LR present in the blooms was highly variable between lakes and temporally within each lake over the limited sampling period. Fast atom bombardment-mass spectrometry (FAB-MS) performed on a composite of several bloom samples from one lake confirmed the identity of microcystin-LR. Bioassays were performed with a subset of the bloom samples to determine acute toxicity to mice. Intraperitoneal injection of bloom extracts containing microcystin-LR resulted in a massive dose-dependent pooling of blood in the liver, shock and very rapid (as quickly as 50 min post-injection) death of injected mice.

Hepatic and renal pathology of intraperitoneally administered microcystin-LR in rainbow trout (Oncorhynchus mykiss).

In 26 hr laboratory trials a dose of 1000 micrograms/kg microcystin-LR (MC-LR) caused 100% mortality in rainbow trout, while no mortality was observed at doses of 400 micrograms/kg or less. The liver to body mass ratio increased in fish exposed to the toxin which was likely due to water retention in the liver. In contrast to mammalian studies, hemorrhage of the liver was rare in fish. Exposure to MC-LR caused widespread hepatocellular swelling and lysis of hepatocyte plasma membranes, resulting in liquifactive necrosis (organelles floating in a milieux of cellular debris). Kidney lesions in the fish consisted of coagulative tubular necrosis with a dilation of Bowmans space. Lesions observed in the liver and kidney of fish exposed to MC-LR were considerably different than those previously reported for mammals.