AiM  Vol.6 No.5 , April 2016
Dynamics of Cylindrospermopsin Production and Toxin Gene Expression in Aphanizomenon ovalisporum
ABSTRACT
Aphanizomenon ovalisporum is a cylindrospermopsin (CYN)-producing cyanobacteria species that due to its increasing worldwide distribution has become an important health alarm in the last few years. Several clusters of genes involved in CYN production have been described in different CYN+ cyanobacteria genera, named aoa for Aphanizomenon and cyr for Cylindrospermopsis and others strains. The sequences of those genes are highly similar, but a rearrangement in gene order is also observed. The information on the control of CYN production by gene expression is still scarce, especially in Aphanizomenon. To obtain further information about the control of CYN production in A. ovalisporum, we have quantified the intra and extracellular CYN content, during nine days in BG11 batch cultures under optimal conditions. In parallel, the expression of four genes related to CYN synthesis, aoaA-C and cyrJ, has been analyzed by real time q-PCR. The results show a similar pattern of total CYN accumulation and gene expression. Most of the CYN is found intracellularly. Considering the high nitrogen content in the CYN molecule, we have explored if nitrogen assimilation could be related to CYN synthesis. We found inside the aoaA and aoaC sequences several putative binding domains for the global nitrogen regulator NtcA. The pattern of the ntcA expression along the culture is similar to that of CYN accumulation. Our data suggest that CYN production in A. ovalisporum seems to be controlled both by the expression of genesaoa and ntcA, this last one suggesting the influence of available nitrogen; however, other regulation mechanisms of CYN synthesis cannot be discarded.

Received 27 February 2016; accepted 24 April 2016; published 27 April 2016

1. Introduction

Aphanizomenon ovalisporum is one of the toxic bloom-forming cyanobacteria in freshwater systems. It shows a potential invasive character, due to its high adaptability to different environmental factors [1] - [3] . It seems to be worldwide distributed, having been detected amongst other regions in Australia, Europe, Middle East and United States [4] . In the last decades, the presence of A. ovalisporum has become an important health hazard, because all strains found, with only one exception in Israel [5] , produce the toxic alkaloid cylindrospermopsin (CYN).

Various cyanobacteria species have been identified as CYN producers. The gene clusters (cyr genes) involved in CYN synthesis have been completely described in Cylindrospermopsis raciborskii AWT205 [6] and CS-505 [7] , Aphanizomenon sp. 10E6 [8] , Aphanizomenon sp. 22D11 [8] , Oscillatoria sp. PCC6506 [9] and Raphidiopsiscurvata CHAB1150 [10] . In the case of A. ovalisporum [11] , only a partial description of the genes has been reported (aoa genes). All cyr and aoa clusters characterized are highly similar with respect to nucleotide sequences; however, they show several rearrangements in gene order and different flanking regions that might be involved in the expression of cyr/aoa genes. Such is the case of hyp/hup sequences founded in C. raciborskii AWT205 [6] [12] , which could have NtcA binding sites, as they have been drecribed in Nostoc sp. PCC 73102 [13] . Bioinformatic analyses identified putative NtcA binding sites within the cyr gene cluster of C. raciborskii CS-505 and in Raphidiopsisbrookii [12] [14] . This fact and the high N content in the CYN molecule suggest the influence of N metabolism in the synthesis of the toxin. In general, nutrients seem to modulate CYN production, since nitrogen depletion [15] [16] , phosphate and sulphate starvations cause significant changes in the toxin production [17] .

The model of the CYN biosynthesis pathway [6] [18] includes the activity of an amidinotransferase (AMDT) in the first step, encoded by the aoaA/cyrA gene. The synthesis proceeds by the action of an enzyme complex constituted by a non-ribosomal peptide synthetase (NRPS)-polyketide synthase (PKS), codified by the aoaB/ cyrB gene, and further by a PKS encoded by the aoaC/cyrC gene. Other PKS activities and tailoring genes are necessary to complete the synthesis, including the sulfotransferase codified by the cyrJ gene, which was proposed as a genetic marker to detect CYN-producing strains [5] .

In A. ovalisporum, Shalev-Malul and coworkers [16] identified two transcriptional start points in the aoaA and aoaC genes, suggesting two modes of regulation of gene expression, one constitutive and the other alternative in response to environmental conditions, such as light intensity and nitrogen depletion [16] , or inorganic phosphate (Pi) deprivation [19] . Moreover, a transcription factor, AbrB-like protein, has been proposed to regulate CYN synthesis, its binding region being located between aoaA and aoaC [16] .

However, in C. raciborskii CS-505, transcriptomic analyses of four cyr genes (cyrB, cyrI, cyrJ and cyrK) under different nitrogen sources have shown almost no variation in gene expression, indicating only a constitutive expression [12] . But, different regulation points for individual genes have been observed.

Although diverse studies on CYN accumulation under different environmental conditions have been carried out, limited work has been focused in the relationship between gene expression and toxin production. In addition, the lack of standardization in experimental conditions makes it difficult to draw general conclusions on the possible gene regulation of CYN synthesis. The current work have the significant purpose to obtain further insights into the regulation of CYN production in A. ovalisporum we have performed BG11 batch cultures under optimal conditions, and analyzed the CYN content and the expression of the aoaA-C cyrJ and ntcA genes over 9 days. Additionally, NtcA putative binding sites inside the aoa cluster were searched, in order to link toxin production to nitrogen regulation.

2. Materials and Methods

2.1. Culture Conditions

Aphanizomenon ovalisporum UAM-MAO strain [20] was used throughout the work.

Three independent experiments were performed with batch cultures in BG11 [21] , at 30˚C, under continuous white light (60 µmole photons m−2∙s−1) and bubbling with air passed through a 0.22-μm-pore-size filter. Culture samples were harvested every 24 h during 9 consecutive days. All plots were analyzed in triplicate. Cell observations were done with an Olympus BH-2 microscope at 400x magnification equipped with a Leica DC300F digital system.

2.2. Growth Parameters

Growth was followed both by biomass (optical density at 750 nm, O.D.750 nm) and Chlorophyll a (Chla) content. Chla was extracted in 90% of methanol, and quantified as described by Marker et al. [22] .

2.3. RNA Extraction and qPCR

RNA purification was performed using the RNeasy Mini Kit from Qiagen, following manufacturer instructions. Cells were collected from 5 mL of culture by filtration through 0.2 µm Nylon filters. The filters were washed twice with 50 mL of Milli-Q water, and frozen rapidly for RNA extraction. RNA samples were treated with DNAse to remove DNA, and DNA absence was evaluated by standard PCR reaction.

RNA quantification was performed by using a Nanodrop® ND-1000 spectrophotometer. RNA integrity and quality was determined by utilizing the Bioanalyzer 2100 (Agilent Technology, USA).

RNA samples were transcribed to cDNA utilizing randomprimers p(dN)9 and the high capacity RNA to cDNA Kit (Applied Biosystems).

Based on the genome of A. ovalisporum [11] PCR primers were designed to amplify three aoa genes. The sequence of cyrJ primers was designed from that of Aphanizomenon10E6 [8] . The ntcA primers were devised from Nostoc PCC7120 sequences [23] . The 16S rRNA gene was used as a reference, using primers designed from A. ovalisporum UAM289 [2] (Table 1). The right sequence of the expected amplicons was confirmed by sequencing previously to initiate the qPCR assays. Besides, similar amplification efficiency for target and the reference genes was ratified by carrying serial dilutions.

Real-time PCR was performed in 10 μL volume, including 5 μL Master Mix (SYBR Green, TOYOBO, Japan) and 0.25 μL of each primer (final concentration, 250 nM). The amplification reactions were performed in a AB7.900HTFast Real Time cycler (Applied Biosystems), under the following conditions: one cycle at 50˚C for 2 min, one cycle at 95˚C for 10 min, followed by 40 cycles of 95˚C for 15 s, 60˚C for 60 s, and 72˚C for 30 s. Each reaction was run in triplicate. The expression of 16S rRNA was stable under those specific conditions.

Gene expression data from the qPCR amplification were evaluated using the Ct values, and the 16S rRNAgene was used as a control to normalize the expression levels of target genes. Relative transcription was calculated using the 2-ΔΔCt method, where ΔΔCt = (Cttarget ? Ct16S) time x ? (Cttarget ? Ct16S)time 0, according to the handbook of Fast Real Time cycler-Applied Biosystems.

2.4. CYN Content Determination

CYN content was determined as previously described [20] . CYN standard was provided by Abraxis®.

2.5. Sequence Analysis and Data Representation

Putative NtcA binding domains in the aoa cluster (11.35 Kb) described by Shalev-Alon et al. [11] were searched

Table 1. qPCR primer sequences.

using the CLC sequence viewer® (version 6.8.2). All data analyses were performed using GraphPad Prism® 5.

3. Results

3.1. Culture Growth

A. ovalisporum UAM-MAO was grown in BG11 batch cultures, under conditions previously considered optimal for this strain, temperature 30˚C [24] and light (60 µmol photons m−2∙s−1) [2] . The growth was checked during nine days both by the Chla content and the biomass (O.D.750) (Figure 1). The growth pattern after each parameter was different. Thus, the increment of chlorophyll was practically exponential from the start of the culture, and reached its late exponential phase around the sixth day. However, the biomass exhibited a lag phase, followed by an exponential phase; and late exponential phase was reached at the ninth day. Therefore, only the biomass showed a typical bacterial growth curve. No remarkable morphological changes, neither heterocyst formation, was observed in the filaments along the experiment.

3.2. CYN Production

CYN production was followed by quantifying both internal and external toxin per biomass unit; the pattern of both fractions being very different. However, the internal and total CYN content had the same tendency, showing three well differentiated phases (Figure 2): an increment from the beginning to the 4th day of the experiment, a

Figure 1. Growth of Aphanizomenon ovalisporum UAM-MAO expressed by biomass (O.D.750 nm) and Chlorophyll a.

Figure 2. Cylindrospermopsin accumulation in A. ovalisporum UAM- MAO batch cultures. Intra-, extracellular and total CYN concentration (μg/mL) per biomass (O.D.750).

decrease in the following three days, and a new increment during the two last days. It is important to notice that the main contribution to total CYN content throughout the experiment was provided by the intracellular fraction being between 60% to 100%.

3.3. Gene Expression Analysis

The kinetics of aoaA-C gene expression was studied in parallel with that of CYN accumulation. The expression of the 3 genes showed a similar tendency along the experimental time period (Figures 3(a)-(c)): an increment between days 2 - 3, a lagduring days 4 - 5, and a further slow recovery in days 6 - 9, reaching the maximum levels during the last two days. The expression of aoaA was the earliestdetected, and the highest relative expression corresponded to aoaB and aoaC.

The kinetics of gene cyrJ expression was also compared with that of CYN accumulation. In C. raciborskii, cyrJ encodes a putative sulfotransferase involved in the lasts steps of the CYN biosynthesis pathway. Since the sequence of the homologous gene in A. ovalisporumis unknown, the sequence of Aphanizomenon 10E6 was used to design the primers for the expression analysis of cyrJ. The fluctuations of this genetranscript exhibited the same pattern of those of aoa genes, reaching the maximum levels on days 3, 8 and 9 (Figure 3(d)).

To study the possible influence of nitrogen metabolism in CYN formation, the expression of the ntcA gene was analyzed. The pattern of ntcA mRNA levels showed a similar trend to that of aoaA-C and cyrJ genes (Figure 4), the highest ntcA expression level being attained between the days 8 - 10.

By comparing the data of Figure 2 and Figure 3, it is apparent that the kinetics of CYN production correlated with that of the relative expression of the genes involved in the CYN synthesis, aoaA-C and CyrJ, as well as with that of ntcA: the maximum toxin content between days 4 - 9 fitted with the highest gene expression.

Figure 3. Expression of genes involved in CYN synthesis along a batch culture of A. ovalisporum. Relative expression values (normalized by 16S rRNA), RQ, are given. (a) aoaA, (b) aoaB, (c) aoaC and (d) cyrJ genes.

Figure 4. Expression of the ntcA gene along a batch culture of A. ovalisporum. Relative expression values (normalized by 16S rRNA), RQ, are given.

3.4. NtcA-Binding Regions

NtcA binding sequences, both canonical and non-canonical types, were searched along the aoa cluster (11.35 Kb) described for A. ovalisporum by [11] . In our search it was also taken into account other putative NtcAbinding motifs, as described by [25] . Three sequences were found inside the aoa coding regions (Figure 5): two were located inside the coding region of the aoaC gene, as GTA(N7) TACN23TAN3T and GT(N10)ACN23TAN3T sequences; and the third one within the aoaA coding region, as GT(N10)ACN20TAN3T. The three sequences agree with those described −10 consensus-like box with the form TAN3T, separated by 20 - 24 nt from the putative NtcA binding site upstream (Figure 5).

4. Discussion

The final aim of the present work was to contribute to the understanding of the regulation of CYN production in A. ovalisporum. We first analyzed the relationship between the CYN content and the expression of four genes considered to be involved in CYN synthesis, aoaA-C [11] [18] and cyrJ; and second, we explored if nitrogen metabolism could be related to the control of the CYN production, by comparing the toxin content and the expression of the nitrogen metabolism control gene ntcA, and searching for NtcA-binding sequences in the aoa cluster.

The experiments were carried out with batch cultures of the strain of A. ovalisporum UAM-MAO [26] , grown with nitrate as N source and under other conditions described by other authors as optima for A. ovalisporum. The conditions used seemed appropriate, as indicated by the maximum growth rate attained, 0.24 day-1, similar to the value range previously reported, 0.2 - 0.36 day−1 [2] [27] . The calculation of the growth rate was based on biomass increase, which under our conditions proved to be a more reliable criterion than chlorophyll. In effect, chlorophylla variation along the culture did not permit to trace the expected growth pattern of a bacteria culture throughout the time of the experiment (Figure 1).

All analytical and gene expression measurements were carried out every 24 h along 9 days, just until late exponential phase of growth, to avoid nutrient depletion and the effects of possible inhibitory growth factors. To determine CYN production, both intra and extracellular contents of the toxin were quantified. Intracellular CYN was the main toxin fraction throughout the growth, representing 62.6% to 100% of the total toxin value (Figure 2). The greater cell CYN content is in accordance with previous studies with cultures of A. ovalisporum [2] [28] and with other data from our laboratory, obtained with another A. ovalisporum strain (VAC+) and one of C. raciborskii (VCC+) (data not shown), and disagrees with the general idea that in environmental samples CYN appears mainly dissolved in the surrounding medium [29] [30] . Nevertheless, an extracellular location, higher than 40%, could be expected under extreme environmental conditions, during the stationary phase of cyanobacteria

Figure 5. Putative NtcA boxes within the aoa cluster. Putative NtcA binding sites are represented in bold face and highlighted in grey. Regulatory conserved―10 box sequences (TAN3T) are in bold face and enclosed in light grey rectangles. Location of putative NtcA sequences is marked by a thick black line within the cluster.

growth [31] , and after cell lysis. The existence of CYN+ strains from different species, A. ovalisporum included, in which the extracellular CYN was the major toxin fraction cannot be discarded.

The kinetics pattern of total CYN production correlates with that of aoaA-C and cyrJ (Figure 3) transcript accumulation, suggesting a control of CYN synthesis by those genes, at least under the conditions used. The fluctuations of both CYN and transcript levels were conspicuous at the early (days 3-4) and late exponential (days 8 - 9) phase. But in all instances, appreciable quantities of CYN and transcripts were observed, indicating a constitutive gene activity. This could justify a constitutive production of CYN in A. ovalisporum, as previously suggested [2] [17] [28] . Two transcriptional start points were described for aoaA and aoaC genes in A. ovalisporum, and differential expression levels of those genes were reported under diverse environmental conditions, suggesting the presence of two alternative promoters [16] . The distinct activity of each promoter might account for the fluctuations of both gene transcripts and CYN content.

CYN production, as well as the activity of aoaA-C and cyrJ genes, might be modulated by nitrogen metabolism, since the expression pattern of the N-master regulator gene ntcA (Figure 4) is similar to those of CYN content and the level aoa/cyr transcripts. Three potential NtcA targets with −10 like box consensus sequence TGT- N9/10-ACA, suggested by Ramasubramanian et al. [32] were located inside the coding region of aoaA and aoaC genes (Figure 5). Similarly to those described in C. raciborskii CS-505 and R. brookii D9 by Stuken et al. [14] . The putative NtcA sequences are non-canonical, but that is not necessarily an impediment to recognize NtcA, since some other sequences have been suggested for NtcA recognition [25] [33] , which differ from the NtcA sequence GTAN8TAC reported as the optimal for NtcA binding. As far as we know, only one canonical intragenic NtcA box has been described in cyanobacteria [34] , moreover 1762 intragenic NtcA binding region have been found in the Anabaena PCC7120 genome, presenting the abundance of NtcA targets and function in cyanobacteria [35] . The modulation of CYN synthesis by nitrogen metabolism seems logical, considering the alkaloid nature of the toxin and, therefore the high demand for nitrogen availability. Nitrogen metabolism participation might not be restricted to NtcA; it could well be that a metabolite from nitrogen anabolism or catabolism is also involved in CYN synthesis, either in the aoa gene expression or/and in posttranscriptional steps. At any rate, further molecular experiments are needed to confirm or discard our suggestions on the modulation of CYN synthesis by either or both NtcA and a nitrogen metabolite.

5. Conclusion

Here we report the pattern of four toxin genes expression during the Aphanizomenon ovalisporum cells growth, in the presence of nitrogen; besides, the dynamics of CYN accumulation was determined in the same assay. The data have showed parallel fluctuations on toxin content and gene expression, suggesting a control of the CYN production by the regulation of gene expression. However, appreciable quantities of CYN and transcripts have been detected, indicating a constitutive gene activity. Moreover, the expression of ntcA gene detected, as well as the identification of putative NtcA binding sites, in the aoa cluster, might reveal the influence of N metabolism in the A. ovalisporum CYN production.

Acknowledgements

Ángel Barón Sola was a recipient of a predoctoral contract from the Comunidad Autónoma de Madrid, Spain. We would like to thank: Dr. Lee Robertson, from the Museo Nacional de Ciencias Naturales for improving English language; and Silvia Vázquez and Ricardo Ramos from the Parque Científico de Madrid for helping us with qRT-PCR data.

NOTES

*Corresponding author.

Cite this paper
Barón-Sola, Á. , Campo, F. and Sanz-Alférez, S. (2016) Dynamics of Cylindrospermopsin Production and Toxin Gene Expression in Aphanizomenon ovalisporum. Advances in Microbiology, 6, 381-390. doi: 10.4236/aim.2016.65037.
References
[1]   Mehnert, G., Leunert, F., Cires, S., Joehnk, K.D., Ruecker, J., Nixdorf, B. and Wiedner, C. (2010) Competitiveness of Invasive and Native Cyanobacteria from Temperate Freshwaters under Various Light and Temperature Conditions. Journal of Plankton Research, 32, 1009-1021.
http://dx.doi.org/10.1093/plankt/fbq033

[2]   Cires, S., Woermer, L., Timon, J., Wiedner, C. and Quesada, A. (2011) Cylindrospermopsin Production and Release by the Potentially Invasive Cyanobacterium Aphanizomenon ovalisporum under Temperature and Light Gradients. Harmful Algae, 10, 668-675.
http://dx.doi.org/10.1016/j.hal.2011.05.002

[3]   Sukenik, A., Hadas, O., Kaplan, A. and Quesada, A. (2012) Invasion of Nostocales (Cyanobacteria) to Subtropical and Temperate Freshwater Lakes—Physiological, Regional, and Global Driving Forces. Frontiers in Microbiology, 3.
http://dx.doi.org/10.3389/fmicb.2012.00086

[4]   Rzymski, P. and Poniedzialek, B. (2014) In Search of Environmental Role of Cylindrospermopsin: A Review on Global Distribution and Ecology of Its Producers. Water Research, 66, 320-337.
http://dx.doi.org/10.1016/j.watres.2014.08.029

[5]   Ballot, A., Ramm, J., Rundberget, T., Kaplan-Levy, R.N., Hadas, O., Sukenik, A. and Wiedner, C. (2011) Occurrence of Non-Cylindrospermopsin-Producing Aphanizomenon ovalisporum and Anabaena bergii in Lake Kinneret (Israel). Journal of Plankton Research, 33, 1736-1746.
http://dx.doi.org/10.1093/plankt/fbr071

[6]   Mihali, T.K., Kellmann, R., Muenchhoff, J., Barrow, K.D. and Neilan, B.A. (2008) Characterization of the Gene Cluster Responsible for Cylindrospermopsin Biosynthesis. Applied Environmental Microbiology, 74, 716-722.
http://dx.doi.org/10.1128/AEM.01988-07

[7]   Stucken, K., John, U., Cembella, A., Murillo, A.A., Soto-Liebe, K., Fuentes-Valdes, J.J., Friedel, M., Plominsky, A.M., Vasquez, M. and Gloeckner, G. (2010) The Smallest Known Genomes of Multicellular and Toxic Cyanobacteria: Comparison, Minimal Gene Sets for Linked Traits and the Evolutionary Implications. Plos One, 5, e9235.
http://dx.doi.org/10.1371/journal.pone.0009235

[8]   Stuken, A. and Jakobsen, K.S. (2010) The Cylindrospermopsin Gene Cluster of Aphanizomenon sp. Strain 10E6: Organization and Recombination. Microbiology, 156, 2438-2451.
http://dx.doi.org/10.1099/mic.0.036988-0

[9]   Mazmouz, R., Chapuis-Hugon, F., Mann, S., Pichon, V., Mejean, A. and Ploux, O. (2010) Biosynthesis of Cylindrospermopsin and 7-Epicylindrospermopsin in Oscillatoria sp. Strain PCC 6506: Identification of the cyr Gene Cluster and Toxin Analysis. Applied Environmental Microbiology, 76, 4943-4949.
http://dx.doi.org/10.1128/AEM.00717-10

[10]   Jiang, Y., Xiao, P., Yu, G., Sano, T., Pan, Q. and Li, R. (2012) Molecular Basis and Phylogenetic Implications of Deoxycylindrospermopsin Biosynthesis in the Cyanobacterium Raphidiopsis curvata. Applied Environmental Microbiology, 78, 2256-2263.
http://dx.doi.org/10.1128/AEM.07321-11

[11]   Shalev-Alon, G., Sukenik, A., Livnah, O., Schwarz, R. and Kaplan, A. (2002) A Novel Gene Encoding Amidinotransferase in the Cylindrospermopsin Producing Cyanobacterium Aphanizomenon ovalisporum. FEMS Microbiology Letters, 209, 87-91.
http://dx.doi.org/10.1111/j.1574-6968.2002.tb11114.x

[12]   Stucken, K. (2010) Physiogenomics of Cylindrospermopsis raciborskii and Raphidiopsis brookii (Cyanobacteria) with Emphasis on Evolution, Nitrogen Control and Toxin Biosynthesis. Ph.D. Thesis.

[13]   Hansel, A., Axelsson, R., Lindberg, P., Troshina, O.Y., Wunschiers, R. and Lindblad, P. (2001) Cloning and Characterisation of a hyp Gene Cluster in the Filamentous Cyanobacterium Nostoc sp. Strain PCC 73102. FEMS Microbiology Letters, 201, 59-64.
http://dx.doi.org/10.1111/j.1574-6968.2001.tb10733.x

[14]   Stucken, K., John, U., Cembella, A., Soto-Liebe, K. and Vasquez, M. (2014) Impact of Nitrogen Sources on Gene Expression and Toxin Production in the Diazotroph Cylindrospermopsis raciborskii CS-505 and Non-Diazotroph Raphidiopsis brookii D9. Toxins, 6, 1896-1915.
http://dx.doi.org/10.3390/toxins6061896

[15]   Saker, M.L. and Neilan, B.A. (2001) Varied Diazotrophies, Morphologies, and Toxicities of Genetically Similar Isolates of Cylindrospermopsis raciborskii (Nostocales, Cyanophyceae) from Northern Australia. Applied Environmental Microbiology, 67, 1839-1845.
http://dx.doi.org/10.1128/AEM.67.4.1839-1845.2001

[16]   Shalev-Malul, G., Lieman-Hurwitz, J., Viner-Mozzini, Y., Sukenik, A., Gaathon, A., Lebendiker, M. and Kaplan, A. (2008) An AbrB-Like Protein Might Be Involved in the Regulation of Cylindrospermopsin Production by Aphanizomenon ovalisporum. Environmental Microbiology, 10, 988-999.
http://dx.doi.org/10.1111/j.1462-2920.2007.01519.x

[17]   Bacsi, I., Vasas, G., Suranyi, G., Hamvas, M., Mathe, C., Toth, E., Grigorszy, I., Gaspar, A., Toth, S. and Borbely, G. (2006) Alteration of Cylindrospermopsin Production in Sulfate- or Phosphate-Starved Cyanobacterium Aphanizomenon ovalisporum. FEMS Microbiology Letters, 259, 303-310.
http://dx.doi.org/10.1111/j.1574-6968.2006.00282.x

[18]   Kellmann, R., Mills, T. and Neilan, B.A. (2006) Functional Modeling and Phylogenetic Distribution of Putative Cylindrospermopsin Biosynthesis Enzymes. Journal of Molecular Evolution, 62, 267-280.
http://dx.doi.org/10.1007/s00239-005-0030-6

[19]   Bar-Yosef, Y., Sukenik, A., Hadas, O., Viner-Mozzini, Y. and Kaplan, A. (2010) Enslavement in the Water Body by Toxic Aphanizomenon ovalisporum, Inducing Alkaline Phosphatase in Phytoplanktons. Current Biology, 20, 1557- 1561.
http://dx.doi.org/10.1016/j.cub.2010.07.032

[20]   Baron-Sola, A., Ouahid, Y. and del Campo, F.F. (2012) Detection of Potentially Producing Cylindrospermopsin and Microcystin Strains in Mixed Populations of Cyanobacteria by Simultaneous Amplification of Cylindrospermopsin and Microcystin Gene Regions. Ecotoxicology and Environmental Safety, 75, 102-108.
http://dx.doi.org/10.1016/j.ecoenv.2011.08.022

[21]   Rippka, R., Deruelles, J., Waterbury, J.B., Herdman, M. and Stanier, R.Y. (1979) Generic Assignments, Strain Histories and Properties of Pure Cultures of Cyanobacteria. Microbiology, 111, 1-61.
http://dx.doi.org/10.1099/00221287-111-1-1

[22]   Marker, A.F., Nush, E.A., Rai, H. and Riemann, B. (1980) The Measurement of Photosynthetic Pigments in Freshwaters and Standardization of Methods: Conclusions and Recommendations. Archives fur Hydrobiologie, 14, 91-106.

[23]   Kaneko, T., Nakamura, Y., Wolk, C.P., Kuritz, T., Sasamoto, S., Watanabe, A., Iriguchi, M., Ishikawa, A., Kawashima, K. and Kimura, T. (2001) Complete Genomic Sequence of the Filamentous Nitrogen-Fixing Cyanobacterium Anabaena sp. Strain PCC 7120. DNA Research, 8, 205-213.
http://dx.doi.org/10.1093/dnares/8.5.205

[24]   Hadas, O., Pinkas, R., Malinsky-Rushansky, N., Shalev-Alon, G., Delphine, E., Berner, T., Sukenik, A. and Kaplan, A. (2002) Physiological Variables Determined under Laboratory Conditions May Explain the Bloom of Aphanizomenon ovalisporum in Lake Kinneret. European Journal of Phycology, 37, 259-267.
http://dx.doi.org/10.1017/S0967026202003645

[25]   Herrero, A., Muro-Pastor, A.M. and Flores, E. (2001) Nitrogen Control in Cyanobacteria. Journal of Bacteriology, 183, 411-425.
http://dx.doi.org/10.1128/JB.183.2.411-425.2001

[26]   Baron-Sola, A., Gutierrez-Villanueva, M.A., Del Campo, F.F. and Sanz-Alferez, S. (2013) Characterization of Aphanizomenon ovalisporum Amidinotransferase Involved in Cylindrospermopsin Synthesis. Microbiology Open, 2, 447- 458.
http://dx.doi.org/10.1002/mbo3.78

[27]   Pollingher, U., Hadas, O., Yacobi, Y.Z., Zohary, T. and Berman, T. (1998) Aphanizomenon ovalisporum (Forti) in Lake Kinneret, Israel. Journal of Plankton Research, 20, 1321-1339.
http://dx.doi.org/10.1093/plankt/20.7.1321

[28]   Preussel, K., Wessel, G., Fastner, J. and Chorus, I. (2009) Response of Cylindrospermopsin Production and Release in Aphanizomenon flos-aquae (Cyanobacteria) to Varying Light and Temperature Conditions. Harmful Algae, 8, 645-650.
http://dx.doi.org/10.1016/j.hal.2008.10.009

[29]   Chiswell, R.K., Shaw, G.R., Eaglesham, G., Smith, M.J., Norris, R.L., Seawright, A.A. and Moore, M.R. (1999) Stability of Cylindrospermopsin, the Toxin from the Cyanobacterium, Cylindrospermopsis raciborskii: Effect of pH, Temperature, and Sunlight on Decomposition. Environmental Toxicology, 14, 155-161.
http://dx.doi.org/10.1002/(SICI)1522-7278(199902)14:1<155::AID-TOX20>3.0.CO;2-Z

[30]   Ruecker, J., Stueken, A., Nixdorf, B., Fastner, J., Chorus, I. and Wiedner, C. (2007) Concentrations of Particulate and Dissolved Cylindrospermopsin in 21 Aphanizomenon-Dominated Temperate Lakes. Toxicon, 50, 800-809.
http://dx.doi.org/10.1016/j.toxicon.2007.06.019

[31]   Hawkins, P.R., Putt, E., Falconer, I. and Humpage, A. (2001) Phenotypical Variation in a Toxic Strain of the Phytoplankter, Cylindrospermopsis raciborskii (Nostocales, Cyanophyceae) during Batch Culture. Environmental Toxicology, 16, 460-467.
http://dx.doi.org/10.1002/tox.10005

[32]   Ramasubramanian, T.S., Wei, T.F. and Golden, J.W. (1994) Two Anabaena sp. Strain PCC7120 DNA-Binding Factors Interact with Vegetative Cell-Specific and Heterocyst-Specific Genes. Journal of Bacteriology, 176, 1214-1223.

[33]   Camargo, S., Valladares, A., Flores, E. and Herrero, A. (2012) Transcription Activation by NtcA in the Absence of Consensus NtcA-Binding Sites in an Anabaena Heterocyst Differentiation Gene Promoter. Journal of Bacteriology, 194, 2939-2948.
http://dx.doi.org/10.1128/JB.05994-11

[34]   Khudyakov, I. and Wolk, C.P. (1996) Evidence That the hanA Gene Coding for HU Protein Is Essential for Heterocyst Differentiation in, and Cyanophage A-4(L) Sensitivity of Anabaena sp. Strain PCC 7120. Journal of Bacteriology, 178, 3572-3577.

[35]   Picossi, S., Flores, E. and Herrero, A. (2014) ChIP Analysis Unravels an Exceptionally Wide Distribution of DNA Binding Sites for the NtcA Transcription Factor in a Heterocyst-Forming Cyanobacterium. BMC Genomics, 15, 22.
http://dx.doi.org/10.1186/1471-2164-15-22

 
 
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