The abundance of potentially Microcystis aeruginosa-infectious cyanophages in freshwater was studied using g91 real-time PCR. A clear increase in cyanophage abundance was observed when M. aeruginosa numbers declined, showing that these factors were significantly negatively correlated. Furthermore, our data suggested that cyanophage dynamics may also affect shifts in microcystin-producing and non-microcystin-producing populations.The major bloom-forming cyanobacterial species Microcystis aeruginosa forms noxious blooms in many eutrophic freshwater lakes, ponds, and reservoirs. A limited population (limited number of strains) of M. aeruginosa in the environment produces potent hepatotoxins called microcystins (7). These potent toxins in the M. aeruginosa blooms have caused many cases of animal and human poisoning (3,8,16).Previously, most studies have focused on relationships among the cyanobacterial bloom dynamics and the changes in physicochemical factors (e.g., nutrient supply, light, and temperature) that influence cyanobacterial growth in the aquatic environment (28). Since the discovery that viruses are widespread in marine ecosystems (4), cyanophages that can infect cyanobacteria have been thought to be an alternative factor that may control the succession of cyanobacterial blooms (12,14,15,18,19). In addition, cyanophages can also influence the clonal composition of the host Synechococcus communities (14, 27) and could account for some of the cyanobacterial diversity observed in natural communities (22,25,30). Nevertheless, little is known about how freshwater cyanophages can affect the abundance and clonal composition of cyanobacterial blooms in lakes over time.Our aim is to determine if the cyanophages have potential quantitative and qualitative effects on the M. aeruginosa communities in Lake Mikata in Japan. We performed two independent real-time PCR assays to monitor the dynamics of M. aeruginosa and its cyanophage communities. To quantify M. aeruginosa, we used the phycocyanin intergenic spacer (PC-IGS) that was previously used to examine total M. aeruginosa numbers (9, 32). A second real-time PCR assay was used to quantitatively detect potentially M. aeruginosa-infectious cyanophages using the primers targeting the viral sheath proteinencoding gene (g91) previously identified by Takashima et al.(21). To determine the effect of the cyanophages on the internal dynamics of the total M. aeruginosa communities, we examined the fluctuation in the abundance of potentially microcystin-producing M. aeruginosa populations using the real-time PCR and microcystin synthetase gene (mcyA)-specific primers (32) and monitored the relative size of the microcystin-producing subpopulation compared to the total population in relation to the cyanophage numbers using a field survey of M. aeruginosa blooms in a Japanese lake.Water samples were collected from the surface layer (0.5 m) once per month from April to October in 2006 at a fixed point (35°33ЈN, 135°53ЈE) in Lake Mikata (Fig. 1). The cyanobacterial cells used for ...