Microcystin Production by Microcystis aeruginosa in a Phosphorus-Limited Chemostat

The production of microcystins (MC) from Microcystis aeruginosa UTEX 2388 was investigated in a P-limited continuous culture. MC (MC-LR, MC-RR, and MC-YR) from lyophilized M. aeruginosa were extracted with 5% acetic acid, purified by a Sep-Pak C₁₈ cartridge, and then analyzed by high-performance liquid chromatography with a UV detector and Nucleosil C₁₈ reverse-phase column. The specific growth rate (μ) of M. aeruginosa was within the range of 0.1 to 0.8/day and was a function of the cellular P content under a P limitation. The N/P atomic ratio of steady-state cells in a P-limited medium varied from 24 to 15 with an increasing μ. The MC-LR and MC-RR contents on a dry weight basis were highest at μ of 0.1/day at 339 and 774 μg g⁻¹, respectively, while MC-YR was not detected. The MC content of M. aeruginosa was higher at a lower μ, whereas the MC-producing rate was linearly proportional to μ. The C fixation rate at an ambient irradiance (160 microeinsteins m⁻² s⁻¹) increased with μ. The ratios of the MC-producing rate to the C fixation rate were higher at a lower μ. Accordingly, the growth of M. aeruginosa was reduced under a P limitation due to a low C fixation rate, whereas the MC content was higher. Consequently, increases in the MC content per dry weight along with the production of the more toxic form, MC-LR, were observed under more P-limited conditions.     

Impact of Inorganic Carbon Availability on Microcystin Production by Microcystis aeruginosa PCC 7806

Batch culture experiments with the cyanobacterium Microcystis aeruginosa PCC 7806 were performed in order to test the hypothesis that microcystins (MCYSTs) are produced in response to a relative deficiency of intracellular inorganic carbon (C_i,i). In the first experiment, MCYST production was studied under increased C_i,i deficiency conditions, achieved by restricting sodium-dependent bicarbonate uptake through replacement of sodium bicarbonate in the medium with its potassium analog. The same experimental approach was used in a second experiment to compare the response of the wild-type strain M. aeruginosa PCC 7806 with its mcyB mutant, which lacks the ability to produce MCYSTs. In a third experiment, the impact of varying the C_i,i status on MCYST production was examined without suppressing the sodium-dependent bicarbonate transporter; instead, a detailed investigation of a dark-light cycle was performed. In all experiments, a relative C_i,i deficiency was indicated by an elevated variable fluorescence signal and led to enhanced phycocyanin cell quotas. Higher MCYST cell quotas (in the first and third experiments) and increased total (intracellular plus extracellular) MCYST production (in the first experiment) were detected with increased C_i,i deficiency. Furthermore, the MCYST-producing wild-type strain and its mcyB mutant showed basically the same response to restrained inorganic carbon uptake, with elevated variable fluorescence and phycocyanin cell quotas with increased C_i,i deficiency. The response of the wild type, however, was distinctly stronger and also included elevated chlorophyll a cell quotas. These differences indicate the limited ability of the mutant to adapt to low-C_i,i conditions. We concluded that MCYSTs may be involved in enhancing the efficiency of the adaptation of the photosynthetic apparatus to fluctuating inorganic carbon conditions in cyanobacterial cells.     

Cellular Microcystin Content in N-Limited Microcystis aeruginosa Can Be Predicted from Growth Rate

Cell quotas of microcystin (Q_MCYST; femtomoles of MCYST per cell), protein, and chlorophyll a (Chl a), cell dry weight, and cell volume were measured over a range of growth rates in N-limited chemostat cultures of the toxic cyanobacterium Microcystis aeruginosa MASH 01-A19. There was a positive linear relationship between Q_MCYST and specific growth rate (μ), from which we propose a generalized model that enables Q_MCYST at any nutrient-limited growth rate to be predicted based on a single batch culture experiment. The model predicts Q_MCYST from μ, μ_max (maximum specific growth rate), Q_MCYSTmax (maximum cell quota), and Q_MCYSTmin (minimum cell quota). Under the conditions examined in this study, we predict a Q_MCYSTmax of 0.129 fmol cell⁻¹ at μ_max and a Q_MCYSTmin of 0.050 fmol cell⁻¹ at μ = 0. Net MCYST production rate (R_MCYST) asymptotes to zero at μ = 0 and reaches a maximum of 0.155 fmol cell⁻¹ day⁻¹ at μ_max. MCYST/dry weight ratio (milligrams per gram [dry weight]) increased linearly with μ, whereas the MCYST/protein ratio reached a maximum at intermediate μ. In contrast, the MCYST/Chl a ratio remained constant. Cell volume correlated negatively with μ, leading to an increase in intracellular MCYST concentration at high μ. Taken together, our results show that fast-growing cells of N-limited M. aeruginosa are smaller, are of lower mass, and have a higher intracellular MCYST quota and concentration than slow-growing cells. The data also highlight the importance of determining cell MCYST quotas, as potentially confusing interpretations can arise from determining MCYST content as a ratio to other cell components.     

Iron-stimulated toxin production in Microcystis aeruginosa.

Nitrate- and phosphate-limited conditions had no effect on toxin production by Microcystis aeruginosa. In contrast, iron-limited conditions influenced toxin production by M. aeruginosa, and iron uptake was light dependent. A model for production of toxin by M. aeruginosa is proposed.     

Spatiotemporal Variations in Microcystin Concentrations and in the Proportions of Microcystin-Producing Cells in Several Microcystis aeruginosa Populations

With the aim of explaining the variations in microcystin (MC) concentrations during cyanobacterial blooms, we studied several Microcystis aeruginosa populations blooming in different freshwater ecosystems located in the same geographical area. As assessed by real-time PCR, it appeared that the potentially MC-producing cells (mcyB⁺) were predominant (70 to 100%) in all of these M. aeruginosa populations, with the exception of one population in which non-MC-producing cells always dominated. Apart from the population in the Grangent Reservoir, we found that the proportions of potentially MC-producing and non-MC-producing cells varied little over time, which was consistent with the fact that according to a previous study of the same populations, the intergenic transcribed spacer (ITS) genotype composition did not change (38). In the Grangent Reservoir, the MC-RR variant was the dominant microcystin variant throughout the bloom season, despite changes in the ITS composition and in the proportions of mcyB⁺ cells. Finally, the variations in total MC concentrations (0.3 to 15 μg liter⁻¹) and in the MC cellular quotas (0.01 to 3.4 pg cell⁻¹) were high both between and within sites, and no correlation was found between the MC concentrations and the proportion of mcyB⁺ cells. All of these findings demonstrate that very different results can be found for the proportions of potentially MC-producing and non-MC-producing cells and MC concentrations, even in M. aeruginosa populations living in more or less connected ecosystems, demonstrating the importance of the effect of very local environmental conditions on these parameters and also the difficulty of predicting the potential toxicity of Microcystis blooms.Microcystins (MCs) are the most common cyanotoxins and have been involved in several animal and human poisoning episodes (8). These hepatotoxic cyclic heptapeptides are synthesized by a multifunctional enzyme complex (10, 40), and the discovery of the gene cluster encoding this complex has made it possible in recent years to develop molecular tools for studying the relative proportions of MC-producing and non-MC-producing cells in natural cyanobacterial populations. Potentially MC-producing and non-MC-producing cells can coexist in these populations, but the factors and processes governing the dynamics of these subpopulations remain unclear.Some recent papers on the Microcystis genus have shown that the proportions of potentially MC-producing cells can differ considerably from lake to lake. For example, in Lake Wannsee, Germany, this proportion was between 0 and 40% (28), as it was in Lake Oneida, United States (18), and in Lake Mikata, Japan (48). In contrast, large variations over time (6 to 93%) of potentially MC-producing cells were found in the Grangent Reservoir, France (4). Major variations (30 to 80%) were also found in a natural French population of Planktothrix agardhii (3), and the variations in the proportions of potentially MC-producing cells reflected those of the MC concentrations. However, only 54% of the variation in MC concentrations could be explained by changes in the proportion of MC-producing cells, suggesting that a considerable part of the MC concentrations was also due to variations in MC cell quotas. These findings suggest that the toxic risks during cyanobacterial proliferations are due to variations in both the proportion of MC-producing cells and the production of MC by the toxic cells.Numerous papers have already investigated the impact of various biotic and abiotic environmental factors on microcystin production by toxic cells. These studies demonstrate that MC production can be influenced by temperature (35), light (46), nutrients such as nitrogen and phosphorus (12, 32), pH (39), iron (42), xenobiotics (17, 34, 45), and predators (22, 23, 47). Despite inconsistent results, the production of microcystins by the cells does seems to be linked to their growth rate (11, 31, 33), which is itself affected by environmental conditions. On the other hand, several studies of variations in the proportions of MC-producing cells have demonstrated the potential influence of nutrient concentrations (9, 48) and light and temperature (5), and two papers (3, 5) have suggested that there is a negative correlation between the proportions of MC-producing cells and the abundance of cyanobacterial cells. These findings are consistent with the data of Kardinaal and Visser (26), showing that in Dutch lakes there is a negative relationship between the densities of cyanobacterial cells and the mean MC concentration in the cells.In an overall attempt to explain the variations of toxicity during cyanobacterial blooms, we studied the spatiotemporal variations in MC concentrations and in the proportions of MC-producing and non-MC-producing cells in several Microcystis aeruginosa populations blooming in different freshwater ecosystems located in the same geographical area. The point of this study was to analyze these variations in terms of the characteristics of these ecosystems and the population dynamics of the M. aeruginosa populations. In addition, these data were compared to the variations in the intergenic transcribed spacer (ITS) composition of the same populations recently reported by Sabart et al. (38). The proportion of potentially MC-producing cells was estimated by a real-time quantitative PCR approach, the change in threshold cycle (ΔC_T) method recently developed by Briand et al. for Planktothrix (3) and Microcystis (4) and targeting the mcyB (mcyA for Planktothrix) and phycocyanin (PC) genes.     

Buoyancy regulation of Microcystis flos-aquae during phosphorus-limited and nitrogen-limited growth

The dominance of gas-vacuolate cyanobacteria is often attributedto their buoyancy and to their ability to regulate buoyancyin response to environmental conditions. Changes in absolutegas vesicles volume, carbohydrate content, protein content andcolony buoyancy of Microcystis flos-aquae were investigatedduring nitrogen-limited, phosphorus-limited and nutrient-repletegrowth. When nutrient-replete, M. flos-aquae cells consistentlyhad excess gas vesicles, which provided sufficient buoyancythat the influence of daily carbohydrate changes on cells uponfloatation was negligible. However, during nitrogen-limitedgrowth, gas vesicle volume per cell decreased significantlywith nitrogen exhaustion. The maximum decrease of gas vesiclevolume was up to 84–88%. At the same time, cellular carbohydratecontent had an accumulation trend. The decrease of gas vesiclebuoyancy together with the daily increase in carbohydrate aresuggested to explain the daily changes in the cell floatation.During phosphorus-limited growth, gas vesicle volume per celldecreased slightly (maximum to 22–32%), and they stillprovided sufficient buoyancy that most cells kept floating eventhough there were significant daily carbohydrate changes. Sincenitrogen limitation caused more significant buoyancy loss thanphosphorus limitation did, surface water blooms may disappearor appear frequently in nitrogen limited water bodies whilethey may persist a longer time in phosphorus limited water bodies.The quantitative analysis in buoyancy change by gas vesicles,carbohydrate and protein suggested that long-term buoyancy regulationwas mainly determined by changes of gas vesicle volume whereasshort-term buoyancy regulation was mainly determined by carbohydrateaccumulation and consumption. Both long-term and short-termbuoyancy regulation were influenced by cell nutrient status.Furthermore, gas vesicle volume per cell and protein contentchanged in the same way in both nitrogen-limited and phosphorus-limitedgrowth, which implied that the decrease of gas vesicles wereassociated with controls of total protein synthesis.     

Photosynthesis and primary production of Microcystis aeruginosa Kutz. in Lake Kasumigaura

Seasonal changes in the photosynthesis and primary productionof Microcystis aeruginosa Kütz. were investigated in LakeKasumigaura during 1981–1982. Microcystis always showeda light-saturated photosynthesis-light curve. Both P_max andthe initial slope of the photosynthesis-light curve of Microcystisin early summer were very high, so it was concluded that Microcystisutilized both low and high light intensities efficiently. TheP_max of Microcystis was found to be a function of the watertemperature except in August and September. The linear regressionon the temperature-P_max relationship discontinued at 11°C,where the P_max value dropped; Microcystis did not photosynthesizebelow 4°C. The initial slope of the curve was also descendingbelow 11°C. It is suggested that Microcystis changes itsphysiological properties below 11°C. The highest value ofgross production calculated for M. aeruginosa was 5.4 gC m^–2d^–1 in July; the annual gross production was estimatedto be 300 gC m^–2year^–1 (i.e., 40% of the total primaryproduction in this lake).     

Amylase production by a Schwanniomyces occidentalis mutant in chemostat culture

The crystalline cell surface layer (S-layer) from Bacillus stearothermophilis PV72 was used as a matrix for reversible immobilization of -d-galactosidase via disulphide bonds. In order to obtain an immobilization matrix stable towards acid, alkali and reducing agents such as dithiothreitol (DTT), the S-layer subunits were first cross-linked with glutaraldehyde. This was done in a way whereby 75% of the free amino groups remained unmodified, and then could be completely converted into sulphhydryl groups upon reaction with the monofunctional imidoester iminothiolane. After activation of the sulphhydryl groups with 2,2-dipyridyldisulphide, 550 g -d-galactosidase could be immobilized per milligram of S-layer protein, which corresponds to one -d-galactosidase molecule [relative molecular mass (M_r), 116000] per two S-layer subunits (M_r, 130 000). At least 90% of the sulphhydryl groups from the S-layer protein could be regenerated for further activation by cleaving the disulphide bonds with DTT. In comparative studies -d-galactosidase was linked to carbodiimide-activated carboxyl groups of the S-layer protein.Correspondence to: M. Sára     

铜绿微囊藻(Microcystis aeruginosa)对惠氏微囊藻(Microcystis wesenbergii)的化感作用

通过混合培养和添加过滤液两种方式观察铜绿微囊藻和惠氏微囊藻的生长曲线,探讨两种微囊藻之间的化感作用。结果表明:在混合培养条件下,两者能够形成相互抑制作用;当两者起始藻密度高于0.5×106cells.mL-1、混合比为1:1时,惠氏微囊藻的生长因化感作用而受到显著抑制(P<0.05),同时惠氏微囊藻也会对铜绿微囊藻产生一定的胁迫作用;处于对数生长期的铜绿微囊藻过滤液能抑制惠氏微囊藻的生长,且惠氏微囊藻起始藻密度低于0.5×106cells.mL-1,连续滴加该过滤液后,其生长受到极显著抑制(P<0.01)。     

Microcystin composition of an axenic clonal strain of Microcystis viridis and Microcystis viridis-containing waterblooms in Japanese freshwaters

Toxic cyclis heptapeptides (microcystin) in cells of an axenic clonal strain of Microcystis viridis were analyzed quantitatively. Cells from the logarithmic, stationary and death phases of batch culture contained 670, 618 and 372 μg toxic cyclic heptapeptides per g dry cells, respectively. The toxic peptides of the cells from the stationary phase consisted of microcystin RR (65%), microcystin LR (22%), microcystin YR (10%) and microcystin LA (3%). The composition of the toxic peptides changed only slightly through the phases of batch culture. Toxicities and the toxic peptide contents of Microcystis viridis-containing waterblooms in Japanese freshwaters were examined. All samples tested had toxic effects on mice after intraperitoneal injection. The toxic peptides in the samples were composed mainly of microcystin RR (50%) and microcystin LR (30%).     

Cryopreservation of a water-bloom forming cyanobacterium, Microcystis aeruginosa f. aeruginosa

A method for the Cryopreservation of Microcystis aeruginosa f. aeruginosa is described. For the five strains tested, dimethyl sulfoxide (DMSO) (3% v/v) was the only effective cryoprotectant for freezing to, and thawing from -196°C and allowed the successful recovery (>50%) of all the strains. The viability of frozen material was independent of the period of storage in liquid nitrogen. The strain NIES-44 (National Institute for Environmental Studies) had a recovery level of greater than 90% at 3–10% (v/v) DMSO in both two step and rapid cooling methods. The other three strains, NIES-87, 88 and 89 had greater than 60% of viability after freeze/thawing in presence of both 3% and 5% DMSO concentrations. On the other hand, the strain NIES-90 showed approximately 50% of viability in only 3% DMSO solution after two step cooling to and thawing from -196°C. This strain was damaged by greater than 4% DMSO and by rapid cooling to -196°C. It was found that cold shock injury and the cytotoxicity of DMSO were different at a strain level.     

Overwintering of Microcystis aeruginosa Kutz. in a shallow lake

The standing crop and photosynthetic activity of Microcystisaeruginosa Kütz. in both the plankton and sediment wereinvestigated from November 1979 to May 1982 in Lake Kasumigaura,Japan. The number of planktonic colonies of this species decreasedfrom early autumn to early spring, but increased in the sedimentduring late summer and autumn. The overwintering colonies inthe sediment were –100–1000 times greater per unitarea than those in lake water. No photoinhibition of photosynthesiscould be observed in overwintering Microcystis. The values ofthe initial slopes of photosynthesis-light (P-I) curves weresimilar to those of the summer population, although the maximumphotosynthetic rate (P_max) measured at 20°C was lower thanthat of the summer planktonic population. In winter the valuesof initial slope of the P-I curve, and the ratio of phycobilinto chlorophyll a sorted from sediment were higher than in coloniesfrom the plankton.     

Allelopathic effect of Microcystis aeruginosa on Microcystis wesenbergii: microcystin-LR as a potential allelochemical

Microcystis aeruginosa and Microcystis wesenbergii are two cyanobacteria commonly found in eutrophic shallow lakes. Previous studies reported that microcystin-producing M. aeruginosa could have an increased competitive potential on other algae and aquatic plants, and microcystin-LR (MC-LR) was regarded as an allelochemical. Based on this hypothesis, the allelopathic interaction between these two cyanobacteria was studied for the first time under laboratory conditions, and potential allelochemicals were screened. Cyanobacteria biomass and microcystin-LR (MC-LR) concentration were monitored under different culture conditions. The potential allelochemicals from M. aeruginosa were investigated by extract fractionation and GC(LC)/MS analysis. The growth of M. wesenbergii was inhibited by the addition of cell-free filtrates of M. aeruginosa whereas M. aeruginosa was promoted by the addition of cell-free filtrates of M. wesenbergii. The higher polarity the extract of M. aeruginosa is, the stronger the inhibition effect of the extract on M. wesenbergii will be. According to our results, M. aeruginosa has a significant allelopathic inhibition effect on M. wesenbergii. Allelopathic compounds from M. aeruginosa have synergistic effects on inhibition of M. wesenbergii. Besides microcystin, there may be other allelopathic compounds in M. aeruginosa.     

铜绿微囊藻的分子研究进展

中国淡水湖泊、水库众多,富营养化问题严重。铜绿微囊藻是中国湖泊、水库及其他水域生态系统发生、形成富营养化危害的主要藻类。目前对铜绿微囊藻的研究主要集中在水华成因、生长的特点、作用机理等,对其生命活动相关的分子机制研究不多。该文主要从生物节律、毒素合成、藻胆蛋白合成及其调控机制和ATP合成酶等四个方面综述了铜绿微囊藻的分子研究进展,为今后进一步研究铜绿微囊藻的分子作用机理及其防治具有重要意义。     

Antialgal activity of a hepatotoxin-producing cyanobacterium,Microcystis aeruginosa

Antimicrobial activity of toxin produced by a freshwater bloom-forming cyanobacterium Microcystis aeruginosa has been studied. When tested against certain green algae, cyanobacteria, heterotrophic bacteria and fungi, the toxin inhibited growth of only green algae and cyanobacteria. The toxin has been partially purified employing Thin layer chromatography (TLC) and High-performance liquid chromatography (HPLC) techniques and appears to be microcystin-LR (leucine–arginine). Both crude and purified toxins showed toxicity to mice, the clinical symptoms in test mice being similar to those produced by hepatotoxin. Purified toxin at a concentration of 50 g ml^–1 caused complete inhibition of growth followed by cell lysis in Nostoc muscorum and Anabaena BT1 after 6 days of toxin addition. Addition of toxin (25 g ml^–1) to the culture suspensions of the Nostoc and Anabaena strains caused instant and drastic loss of O₂ evolution. Furthermore a marked reduction (about 87%) in the ¹⁴CO₂ uptake was also observed at a concentration of 50 g ml^–1. Besides its inhibitory effects on photosynthetic processes, M. aeruginosa toxin (50 g ml^–1) also caused 90% loss of nitrogenase activity after 8 h of its addition. Experiments performed with ¹⁴C-labelled toxin indicate that the toxin uptake by cyanobacterial cells occurs both in light and dark. These results demonstrate that the toxin is strongly algicidal and point to the possibility that it may have an important role in establishment and maintenance of toxic blooms of M. aeruginosa in freshwater ecosystems. The relative significance of the hepatotoxic effect and the algicidal effect of the toxin is discussed with reference both to survival and dominance of M. aeruginosa in nature.