We studied the seasonal variation in concentrations of nutrients and phytoplankton in Lake Yogo for 2 years, from May 2000 to May 2002, in order to clarify the seasonal succession of phytoplankton and the effect of various manipulations on it. It was revealed that in spite of the installation of aeration systems and the pumping of mesotrophic water from Lake Biwa during the summer season, the trophic state of Lake Yogo overall has not improved during the past few decades. However, the pumping of water from Lake Biwa did affect the concentrations of nutrients and the periods of cyanobacterial bloom during the summer. The pumping period was different in each year, and the cyanobacterial bloom occurred during the period without pumping in both years. The aeration destratification was not strong enough to prevent cyanobacterial blooms. Cyanobacteria and Bacillariophyceae contributed most to the phytoplankton biomass in both years. Aphanizomenon, Anabaena, and Microcystis were the main genera among cyanobacteria. The bloom of Aphanizomenon or Anabaena occurred early in the summer, and was then replaced by Microcystis. Aphanizomenon was almost always present, and often formed bloom even in winter. The seasonal succession of Bacillariophyceae was almost the same in both years and was well categorized: winter-growing species such as Aulacoseira pusilla (F. Meister) Tuji et Houki and species of Thalassiosiraceae, spring-growing species such as Asterionella formosa Hassall, Fragilaria crotonensis Kitton, and Synedra cf. acus, and fall-growing species such as Aulacoseira ambigua (Grunow) Simonsen, and Aulacoseira granulata (Ehrenb.) Simonsen.

Diel changes in the frequency of dividing cells (FDC) of three Microcystis species were investigated in a small eutrophic pond from July to October 2005. The representative species was M. aeruginosa (Kütz.) Kütz., constituting 57%-86% of the Microcystis population throughout the study period, and the remainder were M. viridis (A. Braun) Lemmerm. and M. wesenbergii (Komárek) Komárek. The FDC of M. aeruginosa and M. wesenbergii increased in the daytime and fell in the nighttime in July and August, but this regular variation was not observed in September or October. The in situ specific growth rates of Microcystis species were estimated based on the assumption that the specific growth rate can be given as an absolute value of the derivative of FDC with respect to time. The calculated values were similar among species-0.15-0.38 · d(-1) for M. aeruginosa, 0.14-0.63 · d(-1) for M. viridis, and 0.18-0.61 · d(-1) for M. wesenbergii. The specific growth rates in July and August slightly exceeded those in September and October. The analysis of the in situ specific growth rate of Microcystis indicated that recruitment of the benthic population or morphological change, rather than massive growth, was at least partly responsible for the dominance of M. aeruginosa in the study pond.

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To clarify whether nutrients limit the growth of Microcystis aeruginosa (Kütz.) Kütz during the growing season in Lake Yogo, we examined the cellular ratios of carbon (C), nitrogen (N), and phosphorus (P) in the populations of M. aeruginosa from August to December 2001. We also measured cellular C, N, and P ratios of M. aeruginosa under batch culture conditions. The cellular levels of N and P of M. aeruginosa in natural population changed more than twofold. The atomic N : C ratio of natural populations of Microcystis fluctuated from 0.11 to 0.26. The atomic P : C ratio fluctuated from 0.0080 to 0.024. The N : C, P : C, and N : P ratios of exponentially growing M. aeruginosa in N-and P-rich medium were 0.19, 0.013, and 15 on average. The growth of M. aeruginosa was suppressed below the N : C ratio of 0.13 under the N-free condition and below the P : C ratio of 0.0026 in the P-free condition. In the natural population, the N : C ratio was low on August 1-2 (0.11) and the P : C ratio was low (less than 0.011) until September. The Microcystis population on August 1-2 was N limited, judging from the results of the culture experiment. In other periods, the population seemed to be supplied with a sufficient amount of N. Although the P : C ratio was low (approximately 0.01) during August and September, it was several times larger than the value of the reduction of growth rate that occurred in culture. P limitation did not occur during the study period. N became more of a limiting factor than P for the formation of blooms of Microcystis. No blooms were observed in August and September, in spite of the increase of cellular levels of N. The formation of Microcystis blooms in Lake Yogo seems to be affected by artificial manipulations such as pumping from Lake Biwa and outflow.

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