The effects of microcystins on Daphnia galeata, a typical filter-feeding grazer in eutrophic lakes, were investigated. To do this, the microcystin-producing wild-type strain Microcystis aeruginosa PCC7806 was compared with a mcy− PCC7806 mutant, which could not synthesize any variant of microcystin due to mutation of a microcystin synthetase gene. The wild-type strain was found to be poisonous toD. galeata, whereas the mcy− mutant did not have any lethal effect on the animals. Both variants of PCC7806 were able to reduce the Daphnia ingestion rate. Our results suggest that microcystins are the most likely cause of the daphnid poisoning observed when wild-type strain PCC7806 is fed to the animals, but these toxins are not responsible for inhibition of the ingestion process.

Cyanobacteria are recognized as producers of a broad variety of bioactive metabolites. Among these, the peptides synthesized by the non-ribosomal peptide synthetase pathway occur in high structural variability. One class of cyanobacterial peptides, the cyanopeptolins or micropeptins, have been shown to be strong inhibitors of vertebrate serine proteases, like trypsin. In the present study we screened extracts of ten strains of the unicellular cyanobacterium Microcystis sp. for their potential to inhibit trypsin-like activity in the planktonic crustacea Daphnia, the main herbivores in freshwater ecosystem. Respective standardized IC(50)'s varied for nearly two orders of magnitude. In HPLC fractions we could identify mainly cyanopeptolins as active compounds by MALDI-TOF mass spectrometry. Cyanopeptolins were found in 22 structural variants with 13 variants produced by one strain alone. Peptides of the microviridin class were moderately active while no activity was evident for microginins and microcystins. Among the cyanopeptolins only those were active that had an arginine or lysine residue N-terminal to the modified amino acid 3-amino-6-hydroxy-piperidone. Structural variants that had a tyrosine residue at this particular position did not inhibit trypsin-like activity. The highly variable composition of the side chain of cyanopeptolins had no marked effect on the activity. Among the six cyanobacterial strains we tested intensively two did not produce any cyanopeptolins and were accordingly less active as crude extracts. The present study underlines the potential importance of the biochemistry of cyanobacteria for the feeding ecology of a planktonic herbivore.

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This paper describes the purification and characterization of microviridin J. a newly discovered metabolite of Microcystis that causes a lethal molting disruption in Daphnia spp., upon ingestion of living cyanobacterial cells. Microviridin J consists of an acetylated chain of 13 amino acids arranged in three rings and two side chains. Unlike other known isoforms of microviridin, microviridin J contains arginine that imparts a unique solution conformation characterized by proximal hydrophobic interactions between Arg and other regions of the molecule. This eventually results in the formation and stabilization of an additional ring system. Microviridin J potently inhibits porcine trypsin, bovine chymotrypsin, and daphnid trypsin-like proteases. The activity against trypsin is most likely due to Arg and its distinctive conformational interactions. Overall, the data presented for microviridin J emphasize once again the ability of cyanobacteria to produce numerous and potent environmental toxins.

As a part of a whole-lake, long-term experiment in biomanipulation in the hypertrophic Bautzen reservoir (G.D.R.), during three years (1984-1986) the dynamics of mouse-related LD 50 of Jficrocystis aeruginosa was compared with the biomass development of this blue-green and the grazing pressure exerted by Dupphnia grclenta. Since the three summer averages of the biomass of D. galeata revealed strong differences due to dccreasing predation activity of fish from 1964 to 1966, the effects of different grazing pressure on Microcystis toxicity could bo investigated under field conditions. Microcystis was nontoxic a t the beginning of the growing season and developed high toxicity during its first strong biomass increase in summer in all three years. But this decrease of the LD 50 together with the first biomass increase of the season is found in quite different periods in different years (1984: August, 1985: July, 1986: June). It is obvious that the higher the mean effective filtration rate of D. galeata during summer is found the faster the toxicity of Microcystis is formed. If these observations are combined with findings of other authors, the conclusion can be drawn that the development of toxic Microcystis blooms seems to be promoted by a combination of five conditions:(1) Presence of a mixture of toxic and nontoxic Microcystis strains a t the beginning of the growing season even if the portion of toxic strains is very low, (2) physical and chemical growth conditions which favour Microcystis over other phytoplankton, (3) high grazing pressure by zooplankton on edible food particles over a rather long period, (4) patchy distribution of the different Illicrocystis strains if nonselective filtrators such as Daphnia dominate the zooplankton, and (5) absence of defense mechanisms of Nicrocystis against grazing which are not coupled with toxicity (e.g. large colony size). These conclusions contribute to a better understanding of the possibilities and limits of in-lake eutrophication control b y biomanipulation and emphasize the need to combine top-down and bottom-up control mechanisms in eutrophic and hypertrophic waters.