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ORIGINAL RESEARCH article

Front. Microbiol., 03 December 2020 | https://doi.org/10.3389/fmicb.2020.601864

Episodic Decrease in Temperature Increases mcy Gene Transcription and Cellular Microcystin in Continuous Cultures of Microcystis aeruginosa PCC 7806

  • 1Department of Microbiology, The University of Tennessee, Knoxville, Knoxville, TN, United States
  • 2Department of Biological Sciences, Virginia Polytechnic Institute and State University, Blacksburg, VA, United States
  • 3Department of Chemistry, State University of New York College of Environmental Science and Forestry, Syracuse, NY, United States
  • 4Water Quality Engineering, Technical University of Berlin, Berlin, Germany
  • 5Civil and Environmental Engineering, Northeastern University, Boston, MA, United States

Microcystins produced during harmful cyanobacterial blooms are a public health concern. Although patterns are emerging, the environmental cues that stimulate production of microcystin remain confusing, hindering our ability to predict fluctuations in bloom toxicity. In earlier work, growth at cool temperatures relative to optimum (18°C vs. 26°C) was confirmed to increase microcystin quota in batch cultures of Microcystis aeruginosa NIES-843. Here, we tested this response in M. aeruginosa PCC 7806 using continuous cultures to examine temporal dynamics and using RNA-sequencing to investigate the physiological nature of the response. A temperature reduction from 26 to 19°C increased microcystin quota ∼2-fold, from an average of ∼464 ag μm–3 cell volume to ∼891 ag μm–3 over a 7–9 d period. Reverting the temperature to 26°C returned the cellular microcystin quota to ∼489 ag μm–3. Long periods (31–42 d) at 19°C did not increase or decrease microcystin quota beyond that observed at 7–9 d. Nitrogen concentration had little effect on the overall response. RNA sequencing indicated that the decrease in temperature to 19°C induced a classic cold-stress response in M. aeruginosa PCC 7806, but this operated on a different timescale than the increased microcystin production. Microcystin quota showed a strong 48- to 72-h time-lag correlation to mcy gene expression, but no correlation to concurrent mcy expression. This work confirms an effect of temperature on microcystin quota and extends our understanding of the physiological nature of the response.

Introduction

Cyanobacterial blooms plague fresh waters across the globe. A recent study confirmed that bloom frequency and duration have increased over the past three decades, a pattern long suspected (Ho et al., 2019). Trends in population, urbanization, land use, and temperature due to climate change all but ensure continued eutrophication of freshwater resources (Pachauri et al., 2014; Shukla et al., 2019; Jenny et al., 2020). Blooms degrade ecosystem services of the lakes they occupy, and the noxious effects of blooms are well recorded (Watson et al., 2016; Huisman et al., 2018). Additionally, the cyanotoxins frequently produced during blooms constitute a potential and growing public health concern (Carmichael and Boyer, 2016).

Of the toxins produced by bloom-forming cyanobacteria, microcystins are the most commonly detected (Loftin et al., 2016; Mantzouki et al., 2018). These compounds act as potent liver toxins in vertebrates (MacKintosh et al., 1990). While the physiological function of microcystin continues to be debated (Omidi et al., 2018), there is growing evidence that microcystin plays a role in moderating damage from oxidative stress by protecting key proteins involved in photosynthesis and carbon fixation (Zilliges et al., 2011; Wei et al., 2016). This picture is complicated by reports that microcystins can interfere with the ability of Microcystis to cope with externally induced oxidative stress (Schuurmans et al., 2018). These seemingly inconsistent results suggest a complexity in the function of microcystin that is yet to be fully revealed (Barchewitz et al., 2019).

In a similar vein, the environmental cues that stimulate and constrain the production of microcystin remain puzzling (Wilhelm et al., 2020), although general trends are emerging. For example, it is now accepted that higher nitrogen availability leads to greater microcystin production (Gobler et al., 2016). Nevertheless, even this trend can be at odds with lab studies investigating the influence of nitrogen availability on microcystin quota (Ginn et al., 2010; Pimentel and Giani, 2014; Peng et al., 2018). Again, these seemingly inconsistent results point to a combination of variability between strains and a complex regulation of microcystin biosynthesis. Ultimately, our ignorance regarding the function and regulation of microcystin hinders our ability to predict trends and fluctuations in bloom toxicity.

Previously we demonstrated that seasonally relevant cool temperatures increased cellular microcystin content in batch cultures of Microcystis aeruginosa NIES-843 (Peng et al., 2018). This cool-temperature phenotype is consistent with and may help explain field observations in which blooms are more toxic in early spring and less toxic in midsummer (Kardinaal and Visser, 2005). In the lab, this response to cool temperature could serve as a controllable phenotype to investigate the eco-physiological function of microcystin. Yet, key questions involving how this phenotype manifests in other strains and the temporal dynamic and physiologic nature of the response remain unanswered. In this work, we demonstrate, using continuous cultures, that an episodic decrease in temperature increases microcystin production in M. aeruginosa PCC 7806 and that this production reverts to previous rates with a return of temperature. Using RNA sequencing, we show that cellular microcystin is time-lag (48 h) correlated to mcy expression and that this expression appears to be partitioned from a generalized cold-stress response. Additionally, we show that nitrogen concentration and temperature affect cell size. Together, this work confirms the effect of reduced temperature on microcystin quota and extends our understanding of the physiological nature of this response.

Materials and Methods

Strains and Culture Conditions

Non-axenic cultures of Microcystis aeruginosa strain PCC 7806 were grown in medium modified from original CT (Watanabe and Ichimura, 1977). Final nitrogen (N) concentrations were either 81, 161, or 323 μM as a mix of Ca(NO3)2 and KNO3 which contributed N at a molar ratio of 1.37:1. Total phosphorus (P) was supplied at 16.3 μM by K2HPO4. Resulting N:P ratios were ∼5, 10, and 20 for respective N concentrations. Other components of CT were unchanged. The final pH was adjusted to 8.2 using 0.6 mL of 1 M NaOH. Our isolate of PCC 7806 was obtained from the Pasteur Culture Collection over a decade ago. The strain was re-verified before the start of the experiment via PCR/Sanger sequencing using cyanobacteria-specific 27F/809R primers (Jungblut et al., 2005).

Chemostats (described below) were kept in illuminated incubators (VWR model 2015-2). Experimental temperature was set to either 19 or 26°C and was measured every 30 min using a Hobo Tidbit TempLogger (OnSet Computer Corporation) that was suspended in a volume of water equal to the culture volume (1 L). Continuous light at a photosynthetic fluence rate of 50 μmol photons m–2 s–1 was supplied by fluorescent bulbs (GE Ecolux 32W).

Chemostat System and Construction

Chemostats were constructed using standard 2 L glass media bottles (VWR) as growth vessels. Vessels were sealed with GL45 Diba Omnifit T-series solvent caps (Cole-Parmer) with 4 ports to separately accommodate feed, weir, aeration, and sampling tubes. Rigid 1/8 in OD PTFE tubing extending through the GL45 cap ports provided airtight extensions to which flexible tubing could be securely connected. Masterflex L/S 14 silicon tubing was used for all other plumbing lines. To aerate the vessel, air filtered through a 0.22-μm nylon syringe filter was supplied by a standard aquarium pump (Topfin Air-500) at a flow rate of 0.5 L min–1. In addition, this airflow generated the pressurized headspace necessary to expel excess media through the weir tube to the waste vessel. The adjustable-height weir tube was set to maintain vessel volume at 1 L leaving a headspace of 1 L. Standard 2 or 5 L media bottles using 2-port GL45 caps accommodating a feed tube and a filtered air vent were used for culture medium reservoirs. Individual, single-channel, ultra-low-flow peristaltic pumps (Traceable Products #3384) supplied continuous flow of fresh media. Constant stirring with a magnetic stir bar was used to prevent cell sedimentation. Dilution rate (D) was maintained at 0.25 d–1 for all experiments reported here. Three independent chemostat vessels were used in this study.

Sample Collection

Samples were collected from luer-lock sampling ports to measure microcystin content, cell concentration/size, and for RNA extraction. Samples (50 mL) for microcystin quantification were collected on 47-mm glass filters (Advantec MFS GF75, 0.3 μm retention) via vacuum filtration, flash-frozen in liquid nitrogen, and stored at −80°C until processing. Samples for RNA (30 mL) were collected on 47-mm diameter polycarbonate filters (Whatman Nucleopore, 1.0 μm pore-size) via vacuum filtration, flash-frozen in liquid nitrogen, and stored at −80°C until extraction.

Predicting Mean Cell Diameter and Determining Culture Biovolume

Cell concentration was determined via flow cytometry using a Guava easyCyteHT (Millipore) flow cytometer gating on red fluorescence (a proxy for chlorophyll a) and forward scatter (a proxy for size). Mean cell diameter was predicted by a linear regression equation using forward scatter as the explanatory variable. To produce this regression equation, we measured both the forward scatter and the actual mean cell diameter from concurrent samples across a broad range of conditions. Mean cell diameter was measured with a FlowCam 8000 (Yokogawa Fluid Imaging Technologies) using a 20x objective and a FOV50 flowcell. A minimum of ∼5,000 cells was measured per sample using auto-imaging mode. The binary image particle property “area-based diameter” was used as cell diameter (Spaulding, 2014). Mean cell volume was calculated from predicted mean diameter assuming spherical cells. Culture biovolume was calculated as the product of mean cell volume and cell concentration of the culture.

Ion Chromatography

Two mL of culture were collected and filtered through a 0.22-μm pore-size SFCA syringe filter (Thermo Scientific). The filtrate was stored at 4°C until analysis. Each sample was analyzed for NO3 by ion chromatography using a Dionex ICS2100 Ion Chromatography System (Thermo Scientific) following Standard Methods 4110B with chemical suppression (American Public and Health Association, 2017).

Microcystin Extraction and Quantification

Particulate microcystins were quantified via coupled liquid chromatography/mass spectrometry using methods detailed in Boyer (2007, 2020). Glass fiber filters were extracted in 5 mL of 50% methanol containing 1% acetic acid using ultrasound sonication (three 20-s pulses separated by 20-s rests). Samples were clarified by centrifugation at 14,000 × g for 10 min at 4°C. The supernatants were filtered through 0.45 μm pore-size nylon syringe filters (Corning, CLS431225) and stored at −20°C until analysis. Reverse-phase HPLC using a Waters 2695 Separations Module coupled to a Waters ZQ4000 mass spectrometer (m/z 500–1250 amu) and a 2996 photodiode array detector (210–400 nm wavelength) was used to screen for molecular ions of 22 common microcystin congeners (RR, dRR, mRR, H4YR, hYR, YR, LR, mLR, zLR. dLR, meLR, AR, FR, WR, LA, dLA, mLA, LL, LY, LW, LF, WR). Separation conditions used an ACE 5 C18, 150 × 3.0 mm column and a 30–70% aqueous acetonitrile gradient containing 0.1% formic acid at a flow rate of 0.3 mL min–1. Concentration of individual congeners was quantified using the peak area of the extracted ion relative to standards of microcystin-LR or microcystin-RR (Enzo Life Sciences). This allows quantification of congeners where standards are not available. Detection of congeners was validated by co-occurring presence of the diagnostic UV signature from the ADDA group. Matrix spike experiments indicated that matrix inhibition was less than 1% so individual samples were not corrected for matrix suppression. Individual method detection limits were calculated from sample volumes and from specific instrument detection limits of the day samples were run (Boyer, 2020). The method detection limit for all samples was equal to or less than 0.32 μg L–1 (microcystin-LR equivalents). Total microcystin concentrations are reported as the sum of all congeners.

RNA Extraction, RNA Sequencing, and Gene Expression Analysis

RNA was extracted using the acid phenol/bead beating protocol described in Martin and Wilhelm (2020). Genomic DNA was digested using Turbo DNA-free kit (Ambion) following the method described in Martin and Wilhelm (2017). Samples were considered DNA-free if no bands were visible in an agarose gel after 30 cycles of PCR amplification using standard 27F/1522R primers targeting the 16S rRNA gene. Ribosomal RNA was depleted using the Ribominus Transcriptome Isolation Kit for yeast/bacteria (Invitrogen). Total RNA was quantified and checked for quality using an Agilent 2100 Bioanalyzer.

Libraries (cDNA) were prepared at The University of Tennessee Knoxville Genomics Core using the Illumina TruSeq Stranded mRNA Sample Preparation Kit following manufacturer instructions for the LT/LS protocol by adding the depleted RNA to the Fragment/Prime/Finish step of the protocol. Four multiplexed libraries, at a final cDNA concentration of 4 pM with 2% PhiX spiked-in, were sequenced per run on the Illumina MiSeq platform using Version 3 flowcells, generating 75-bp paired-end reads.

Residual ribosomal reads were removed in silico using the SortMeRNA algorithm on default settings (Kopylova et al., 2012). RNA-seq analysis was performed using CLC Genomics Workbench (v. 10.1.1). Reads were trimmed for quality using default parameters and mapped against annotated regions of the reference genome M. aeruginosa PCC 7806SL (GenBank accession NZ_CPO20771.1, version annotated January 28, 2020) (Zhao et al., 2018). Default parameters for mismatch, insertion, and deletion costs and custom settings of 0.8 for length fraction and 0.95 for similarity fraction were used. Expression values were calculated as transcripts per million (TPM) (Wagner et al., 2012) using only reads that mapped as pairs. Paired reads were counted as a single mapped fragment; reads mapped as broken pairs were ignored. Weighted gene correlation network analysis (WGCNA) (Zhang and Horvath, 2005) was performed as implemented in the R package WCGNA (Langfelder and Horvath, 2008). Genes with an average expression > 2 counts per million were included in this analysis. Expression values were normalized via TMM using edgeR (Robinson et al., 2010). A soft-thresholding power of 12 was used, generating a “signed” network with a minimum module size of 30 genes. We used OmicsBox (Götz et al., 2008) to assign Gene Ontology (GO) terms (Ashburner et al., 2000; Gene Ontology Consortium, 2019) to 3,150 of the 4,834 CDS in the PCC 7806SL genome and to conduct enrichment analysis of GO terms associated with genes assigned to WGCNA modules. Sequence libraries are publicly available and can be found in the NCBI Sequence Read Archive under Project Accession # PRJNA650205.

Calculation of Microcystin Production Rates

Particulate microcystin production rates were calculated using the following formula:

d M C d t = P B - MC D

where MC is microcystin concentration (μg L–1), P is biovolume-based production rate (μg mm–3 d–1), B is biovolume concentration (mm3 L–1), and D is chemostat dilution rate (d–1). Mean production rate for a given temperature period was calculated as the mean of daily production rates for that period.

Statistical Analysis

Statistical calculations were conducted in GraphPad Prism (v. 8.4.2). For repeated-measures (RM) ANOVA, assumption of sphericity was tested in the R statistical environment (v. 3.4.0); the Greenhouse–Geisser correction was applied when sphericity was not met (Greenhouse and Geisser, 1959). Post hoc multiple comparisons were adjusted with Tukey’s HSD. A significance level of p = 0.05 was used in all analyses.

Results

To examine the effects of a temperature change on cellular microcystin concentration, we grew M. aeruginosa PCC 7806 in continuous cultures at a standard lab temperature of 26°C. Over an experimental period of 21 days, steady-state cultures were first sampled daily for 5 days at 26°C temperatures to establish a baseline. Vessel temperature was then decreased to 19°C and cultures sampled for 9 days. Subsequently, the temperature was returned to 26°C and cultures sampled over an 8-day period during recovery (we note day 16 was missed).

Nitrogen and Temperature Treatments Induce Cell Size Change

We observed notable shifts in cell size in response to nitrogen concentration and temperature. These cell size differences were sufficient to influence normalization of microcystin measurements and complicated comparisons of per cell quota. A necessary first step, then, was to address the issue of dynamic cell size. To resolve this, we measured cell diameter across all treatment conditions and related those diameters to mean forward scatter (Supplementary Figure S1). Mean forward scatter described ∼96% of the variation in measured mean cell diameter (R2 = 0.96) and the slope was significantly non-zero (p < 0.0001). Cell diameter increased with decreasing N concentration, resulting in large differences in estimated mean cell volume. For example, the mean cell diameter at steady-state in nitrate concentration of 81 μM was ∼4.33 μm (S.D. 1.01 μm), while for cells growing in 323 μM it was ∼3.45 μm (S.D. 1.05 μm) (Mann–Whitney p < 0.0001), representing a 2-fold difference in volume (Figure 1). While the size relationship to nitrogen concentration was consistent, it fluctuated over the course of continuous cultures and was affected strongly by changes in temperature (Figure 2). Given the observed changes in cell size, microcystin measurements were normalized to mean cell volume rather than being reported as a per cell quota. Normalizing this way allows comparison of results between tested conditions.

FIGURE 1
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Figure 1. Violin plot of cell diameter in cultures of M. aeruginosa PCC 7806 grown in different concentrations of nitrate. Black horizontal bars represent mean diameter. Each measured cell is represented by a plotted point. Width of plot is proportional to frequency of cells at a given diameter. n = 4,890 (81 μM); n = 5,213 (323 μM). p-value from Mann–Whitney test.

FIGURE 2
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Figure 2. Dynamics of cell concentration, cell volume, and cellular microcystin concentration in continuous cultures of M. aeruginosa PCC 7806. Blue shading represents the time period when temperature was set to 19°C. (A) Cell concentration and cell volume. Solid lines represent cell concentration on the left y-axis. Dashed lines represent cell volume on the right y-axis. (B) Cellular microcystin concentration.

Chemostat theory predicts that at steady state, concentration of the limiting substrate is relatively constant over a range of dilution rates and is independent of the substrate concentration in the inflowing medium (Herbert et al., 1956). To investigate the effects of nitrogen availability on microcystin production, we empirically tested a range of inflowing nitrate concentrations and selected concentrations that on the higher end (323 μM N) resulted in an excess of nitrate as measured by ion chromatography (and indicating limitation by another nutrient, likely phosphorus), and that on the lower end (81 μM N) clearly resulted in nitrogen-limitation. The third concentration (161 μM N) was selected to be intermediate of these two. The three inflowing nitrate concentrations influenced cellular physiology as evidenced by differences in steady-state cell size (Figure 1) and in chlorophyll a fluorescence of individual cells as measured by flow cytometry (Supplementary Figure S2).

A Temperature Drop Increased Cellular Microcystin Concentration and Cell Size

Actual mean temperatures during the experimental periods were 26.4°C (SD = 0.05°C), 19.4°C (SD = 0.16°C), and 25.9°C (SD = 0.07°C) for the baseline, cold stress, and recovery periods, respectively. A trace of the actual temperature measurements is shown in Supplementary Figure S3. Chemostat vessels equilibrated to within ∼0.3°C of the targeted temperature within ∼6 h of temperature adjustment.

The dynamics of PCC 7806 cultures are illustrated in Figure 2. Steady-state (baseline) cell concentration at 26°C was ∼2.3-, 5.3-, and 8.6 × 106 cells mL–1 in 81 μM, 161 μM, and 323 μM N, respectively. After the temperature was decreased to 19°C, growth rates slowed to less than the dilution rate and cell concentration began to decline as cells were washed out of the chemostats (Figure 2A). In 81 and 161 μM N, cell concentration reached a minimum after 7 days at 19°C, dropping to ∼1.1 × 106 mL–1 (48% of baseline) and ∼2.3 × 106 mL–1 (43% of baseline), respectively. In 323 μM N, cell concentration reached a minimum after 6 days dropping to ∼5.3 × 106 mL–1 (62% of baseline). Cell concentration then stabilized and increased slowly to ∼50, 48, and 71% of baseline by the end of the cold stress period for 81, 161, and 323 μM N, respectively. Cell concentrations increased sharply after temperature was returned to 26°C, rebounding to an average of ∼67, 107, and 83% of baseline, respectively. Cell concentration remained relatively constant across the final days of the experiment.

Cell size increased at the onset of cold stress (Figure 2A). Cells in 81 and 161 μM N showed similar trends, increasing to ∼181 and 215% of their respective baseline volumes after 6 days at 19°C. Volumes declined gradually until the temperature returned to 26°C, after which they declined sharply back to baseline volume. Cells in 323 μM N reached peak volume of ∼162% of baseline after 2 days at 19°C, then gradually declined to baseline volumes.

Microcystin content per biovolume showed similar trends among nitrogen concentrations (Figure 2B). While variable across the baseline period, it increased markedly after about 2 days at 19°C, reached a peak ∼7–9 days after onset of cold stress, then declined sharply after temperature was returned to 26°C. On the last day of baseline, mean microcystin content across nitrogen concentrations was 464 ag μm–3 (range: 328–574 ag μm–3). It increased to ∼891 ag μm–3 by the last day of cold stress (range: 819–929 ag μm–3), and returned to ∼489 ag μm–3 by the final day of recovery (range: 342–668 ag μm–3). Means between periods differed (RM-ANOVA p = 0.011); baseline and recovery differed from cold stress (Tukey’s p = 0.015, p = 0.018), but not from each other (Supplementary Figure S4).

Two congeners of microcystin were detected: microcystin-LR and [D-Asp3]-microcystin-LR. This is consistent with previous reports (Tonk et al., 2009; Yeung et al., 2016). The congener profile varied in response to nitrogen concentration and temperature and is illustrated in Supplementary Figure S5.

To statistically test the temporal pattern of microcystin, we determined the slope of the regression line of cellular microcystin content vs. time for each nitrogen concentration in each treatment period (Supplementary Figure S6). Within a treatment period, slopes between nitrogen concentrations were similar (Supplementary Figure S6A; baseline p = 0.39, cold stress p = 0.18, recovery p = 0.29). Mean slopes differed between periods (RM-ANOVA p = 0.0004); baseline and recovery differed from cold stress (Tukey’s p = 0.016, p = 0.010) but not from each other (Supplementary Figure S6B). Mean slope during baseline was −26.5 ag μm–3 d–1 but was not different from zero (one sample t-test p = 0.13). Mean slope increased to 64.8 ag μm–3 d–1 during cold stress, and declined to −50.9 ag μm–3 d–1 across recovery.

If microcystin production is constitutive, it is conceivable that the increasing cellular microcystin content observed during the 19°C period could be due to constitutive production coupled with the reduced growth rate observed during this period. To examine this possibility, we calculated mean microcystin production rates during each of the experimental periods. Across N concentrations, microcystin production (normalized to culture biovolume) averaged 0.11 μg per cubic mm cell biovolume per day (μg mm–3 d–1) during baseline (range: 0.08–0.14 μg mm–3 d–1). It increased ∼73% to 0.19 μg mm–3 d–1 during the period of cold stress (range: 0.17–0.20 μg mm–3 d–1), and returned to 0.11 μg mm–3 d–1 in recovery (range: 0.08–0.15 μg mm–3 d–1). These means produced a significant RM-ANOVA (p = 0.036), with no significant p-value between baseline and cold stress (Tukey’s p = 0.136), and a significant p-value between cold stress and recovery (Tukey’s p = 0.0549) (Supplementary Figure S7).

To examine the long-term effects of cool temperature on cellular microcystin concentration, we maintained cultures at 19°C for up to 42 days in two chemostats (81 and 161 μM N). Across nitrate concentrations, the long-term mean microcystin concentration at 19°C was 802 ag μm–3 for days 31–42, and was not different than the mean of 850 ag μm–3 from days 7–9 (p = 0.84) (Supplementary Figure S8).

To test reproducibility, we repeated in biological triplicate the core study described above, but with nitrate concentration set at 161 μM in all chemostats. The temporal patterns in cell concentration, cell size, and cellular microcystin concentration were reproducible (Supplementary Figure S9).

Decrease in Temperature Induces a General Stress Response

To examine temporal responses in gene expression, we sequenced RNA from 12 samples from a single chemostat over the 21-day experiment. RNA samples were collected from cultures grown in 81 μM N. Sequenced samples were distributed across each of the three experimental periods (Supplementary Figure S10). Sequencing produced a total of ∼131.6 M raw reads, or ∼11 M reads per sample. Collectively, ∼10.1 M reads remained (∼7.7% of total) after in silico reduction of rRNA. After trimming for quality, an average of ∼700k reads (or ∼350k cDNA fragments) per sample mapped to the PCC 7806SL reference genome, representing an effective sequencing depth of ∼10.2 fold. Mapping statistics per sample are summarized in Supplementary Table S1.

We used weighted gene correlation network analysis (WGCNA) to analyze patterns of gene expression. In the context WGCNA, a module is a group of genes whose expression is highly correlated among samples, while eigengenes represent the typical expression profile of genes in a given module (Zhang and Horvath, 2005; Langfelder and Horvath, 2008). In PCC 7806, WGCNA identified three modules whose expression responded to changes in treatment temperature (Figure 3; a list of all genes in each of these three modules is provided in Supplementary Table S2). Module 1 (673 genes) and module 3 (379 genes) comprise genes that were upregulated during cold stress. Expression of genes in module 1 was immediately and sharply induced by cool temperature with peak expression occurring within 24 h of the decrease to 19°C. Expression declined through the remaining period of cold stress, then dropped rapidly upon return to 26°C. Module 3 exhibited an immediate but more gradual increase in expression and reached a peak midway through the 19°C period, then dropped rapidly upon return to 26°C. Module 2 (441 genes) comprised genes that were downregulated during cold stress. In this module, expression dropped sharply within 24 h of the decrease to 19°C and remained constant until return to 26°C, whereupon expression rapidly returned to baseline levels.

FIGURE 3
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Figure 3. Standardized expression profiles of eigengenes from WGCNA modules. Blue shading represents time period when temperature was set to 19°C. Module 1 represents 673 genes that were quickly and sharply upregulated during cold stress. Module 2 represents 441 genes that were downregulated during cold stress. Module 3 represents 379 genes that were upregulated during cold stress but on a timescale distinctly different from that of module 1.

To gain insight into genes whose transcription responds to temperature changes, we conducted enrichment analysis of Gene Ontology (GO) terms associated with genes in modules 1 and 3 collectively (those upregulated) and in module 2 (those downregulated). GO terms enriched (FDR p < 0.05) in combined modules 1 and 3 are listed in Table 1; only the most specific terms are listed. No GO terms were enriched in module 2. The complete list of enriched GO terms, including parent terms, is provided in Supplementary Table S3.

TABLE 1
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Table 1. Enriched gene ontology terms derived from genes in combined Modules 1 and 3.

The most striking transcriptional response was an upregulation of almost all genes responsible for ribosomal biogenesis upon decrease in temperature. Genes encoding 52 of 54 ribosomal proteins were upregulated. Genes for ribosomal proteins S7 and S12, which are adjacent in the genome, were the only genes failing to respond to cool temperature. Ten of 23 over-enriched GO terms were directly related to translation.

Cyanobacteria acclimate to cooler temperature by decreasing saturation of fatty acids in glycerolipid membranes (Murata and Wada, 1995; Los et al., 1997). Expression of all primary acyl-lipid desaturases in PCC 7806 were induced by decrease to 19°C, as would be predicted. Genes induced by a decrease in temperature included those responding to oxidative stress (super oxide dismutase sodB, peroxiredoxin ahpC, thioredoxin and thioredoxin reductase trxAB), photosystem II core (psbA) and repair proteins (ftsH2), and those that respond to more general stress conditions (rpoAB, groEL, groES, hspA, and clpB) (Drath et al., 2008; Sinetova and Los, 2016). Additional genes upregulated by cool temperature included those involved in transcriptional (nusG) and post-transcriptional regulation (homologs of rbp1 and rbp2) and in re-initiation of translation (hflX) (Suzuki et al., 2001; Tan et al., 2011; Zhang et al., 2015). Collectively, the gene expression patterns suggest that reduction of temperature to 19°C induces a typical cold-stress response.

Cellular Microcystin Is Time-Lag Correlated With Expression of mcy Genes

The mcy gene cluster encodes enzymes that synthesize microcystin (Tillett et al., 2000). In this study, transcripts were detected for all 10 mcy genes. The most highly transcribed across all samples was mcyJ with a mean of ∼300 TPM; mcyC had the lowest transcription with a mean of ∼57 TPM. Except for mcyC, the expression of all mcy genes was induced by a decrease in temperature to 19°C; all were more highly expressed during cold stress than in baseline or recovery. mcyA grouped in module 1 (those up regulated most rapidly); all others, except mcyC, grouped in to module 3 (those increasing more gradually). Figure 4 illustrates the expression of mcyD overlaid with the time trace of microcystin content. Expression increased at the onset of cold stress, reached a peak after 5 days at 19°C, started a gradual decline through the remainder of cold stress, then dropped more sharply after the temperature returned to 26°C. Mean expression during cold stress was ∼174 TPM, representing a ∼47% increase over the mean of baseline/recovery (∼119 TPM).

FIGURE 4
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Figure 4. Time trace of mcyD expression and normalized cellular microcystin content. Blue shading represents time period when temperature was set to 19°C.

mcy gene expression and concurrent microcystin content were not correlated. However, as illustrated in Figure 4, it appears that microcystin content follows a pattern similar to that of mcyD expression, albeit with a notable time lag. Time-lag correlation analysis (Schmitt et al., 2004) demonstrates that microcystin content is highly correlated to mcy gene expression at a 48-h delay. Using the mcyD example, correlation increased from r = 0.32 (p = 0.314) at 0-h time lag to r = 0.87 (p = 0.0004) at 48-h time lag, and extended to r = 0.86 (p = 0.002) at 72 h (Figure 5). All mcy genes except mcyCF were significantly correlated to cellular microcystin concentration at both 48- and 72-h time lags (range of significant correlation, r = 0.66–0.88). mcyD was the most highly correlated at 48-h while mcyE was the most highly correlated at 72-h. Time-lag correlations of all mcy genes are listed in Supplementary Table S4.

FIGURE 5
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Figure 5. Time-lag effect on correlation between mcyD expression and normalized cellular microcystin content. Red dots represent time-lag periods with high correlation and significant p-value.

Potential Reference Genes for Use in Experiments With Changing Temperature

The study design allowed us to identify genes whose expression was stable across changing temperatures and thus might potentially serve as reference (housekeeping) genes for use in experiments that include changes in temperature. Genes with an average expression across all time points of >250 TPM and a coefficient of variation < 10% are listed in Supplementary Table S5.

Discussion

A clear understanding of the environmental cues that govern microcystin production is necessary to enable predictions of bloom toxicity. In addition, a grasp of the mechanisms through which microcystin production is regulated opens the way for agent-based models to predict production at the cellular level by integrating the effects of these cues. With this long-term goal in mind, our objective here was to extend our understanding of how changes in the fundamental parameter of temperature affect the production of microcystin and the resulting quota. The influence of temperature on toxin production in cyanobacteria has been examined frequently [see Supplementary Table S1 in Peng et al. (2018) for a summary of these reports]. In many of those studies, efforts focused on the effects of a change in temperature to one above the optimum for growth, or to one above in situ conditions, primarily due to interest in the effects of climate change. The focus of this work is on episodic drops in temperature, defined here as a short-term decrease in temperature to one distinctly below that needed for optimum growth, but which is within the range of temperatures that are still relevant to bloom conditions. In earlier work, we demonstrated in batch culture that a seasonally relevant lower temperature increased cellular microcystin content in M. aeruginosa NIES-843 (Peng et al., 2018). The current work is a follow-up of that study meant to confirm this response in another strain of M. aeruginosa, and to describe both the physiologic and temporal nature of the response to this change in temperature.

We investigated M. aeruginosa PCC 7806 because it, along with NIES-843, are the most commonly used lab strains in Microcystis research (Harke et al., 2016). We note that these cyanobacteria were originally isolated from disparate geographic locations and have notably different genome sizes (Meyer et al., 2017), and thus represent dissimilar strains. Our observations confirm, in a second strain, an effect of below-optimal temperature on microcystin quota. RNA sequencing identified physiological responses associated with an increase in toxin production, while WGCNA and time-lag analysis revealed metabolic processes operating at different timescales and directly demonstrated a temporal disconnect between mcy transcript abundance and cellular toxin content. We frame these observations within the ecology of Microcystis and the potential for multiple environmental factors to influence cellular growth and toxin production (Wilhelm et al., 2020).

Temperature Effect on Cellular Microcystin Concentration

Like NIES-843, PCC 7806 increased microcystin quota when grown at 19°C relative to 26°C, demonstrating that this response to cool temperature is not unique to a single strain. Differences in experimental methods prevent direct comparisons between the two strains, but relative comparisons demonstrate that the response in each strain was similar. In batch cultures of NIES-843, average microcystin quota was ∼2.1 fold higher at 18°C than at 26°C (Peng et al., 2018). In continuous cultures of PCC 7806, cellular microcystin concentration increased ∼1.9 fold at 19°C relative to 26°C.

Under the conditions tested here, nitrate concentration did not meaningfully alter the increase in cellular microcystin content due to cool temperature. This is similar to the earlier findings in batch cultures of NIES-843. It is interesting to note that the cold-induced increase in microcystin content fully manifested itself within ∼8–9 days at 19°C. Long periods at 19°C (31–42 days) did not significantly alter microcystin concentration from that observed after 9 days. This suggests that higher microcystin content is maintained at this temperature and is not a short-term shock response.

Lastly, calculations demonstrated that microcystin production had to increase at 19°C and decrease upon return to 26°C to account for the observed cellular microcystin concentrations. This observation is at odds with the general trends outlined in Long et al. (2001), which indicated that microcystin quota can be predicted from growth rate in nitrogen-limited chemostats.

Calculations of production were based on measurements of particulate (intra-cellular) microcystin. As a result, these production estimates do not account for dissolved microcystin released due to cell death. However, an increase in cell death rates, e.g., in response to a decrease in temperature, results in an increase in the unaccounted-for-loss of microcystin from the chemostat, which necessitates a production rate higher than our calculation. We therefore feel our estimates of production are conservative.

Transcriptional Response of Microcystis to Decrease in Temperature

It has been said that “blooms like it hot” (Paerl and Huisman, 2008). That said, we expected that a 7°C decrease would induce a “cold-stress” response leading to a characteristic transcriptional profile. To test this, we compared the expression profile of PCC 7806 to other cyanobacteria in the literature (Synechocystis and Synechococcus), as studies of Microcystis are limited. In PCC 7806, the most extensive changes were increased ribosomal biogenesis and an upregulation of genes encoding ribosomal proteins. This pattern has been observed in both Synechococcus PCC 7942 (Billis et al., 2014) and Synechocystis PCC 6803 (Suzuki et al., 2001; Billis et al., 2014; Sinetova and Los, 2016). This response seems counterintuitive when compared to changes observed in model heterotrophic bacteria. For example, in Escherichia coli, ribosomal biosynthesis typically increases with change in conditions that stimulate rapid growth, rather than with conditions that slow growth as observed here (Vadia and Levin, 2015). The increase in translational machinery due to cold-stress has been interpreted as a compensatory response necessary to maintain adequate protein synthesis in the cell as the rate of synthesis per unit ribosome deceases at low temperature (Suzuki et al., 2001). Low temperature directly inhibits synthesis of proteins involved in photodamage repair of photosystem II (PSII) (Kanervo et al., 1997; Allakhverdiev and Murata, 2004). Thus, it has been suggested that this compensatory response is important in cyanobacteria as a way to maintain repair of PSII during periods of low temperature (Suzuki et al., 2001). Reports of this pattern in eukaryotic phytoplankton suggest that it could be a more general phenomenon of photosynthetic organisms (Rhee and Gotham, 1981).

A well-documented transcriptional response to cold stress is an upregulation of genes involved in desaturation of fatty acids in membrane lipids. A decrease in saturation is necessary to maintain membrane fluidity at lower temperatures (Murata and Wada, 1995). Synechocystis PCC 6803 increased transcription of all desaturase genes within 60 min of a 12°C downshift in temperature (Los et al., 1997). Likewise, in thermotolerant Synechococcus PCC 7002, growth at 30°C produced a prominent upregulation of desaturases relative to growth at 38°C (Ludwig and Bryant, 2012). Within 24 h of temperature decrease, transcription of all desaturases in PCC 7806 was sharply increased, consistent with well-described cold-stress responses.

Finally, expression of additional genes, including chaperone proteins commonly associated with heat shock (groES, groEL, hspA), sigma factors (rpoA), and PSII core and repair proteins (psbA, ftsH), were increased by cool temperature in a pattern similar to those in Synechococcus and Synechocystis (Inaba et al., 2003; Billis et al., 2014; Sinetova and Los, 2016).

Rocca et al. (2015) pointed out that transcriptional studies often assume a positive relationship between transcript abundance and rates of the corresponding process, a relationship that is not always valid. In a study relevant here, in a strain of marine Synechococcus responding to cold stress, the transcriptional patterns outlined above were largely confirmed at the point of protein abundance, suggesting a generally conserved and bona fide response in these cyanobacteria (Varkey et al., 2016).

In a recent study, Antosiak et al. (2020) used Raphidiopsis (Cylindrospermopsis) raciborskii to examine expression of a subset of genes thought to be associated with the acquired chill-light tolerance response. Though the timing of transcriptional change varied, there was a high degree of correspondence between Raphidiopsis and PCC 7806 in genes upregulated by cool temperature. Among these were desA, ftsH, hflX, nusG, and rbp1. This correspondence between distantly related species suggests a conserved response across cyanobacteria. In contrast to Raphidiopsis (Antosiak et al., 2020) and Synechocystis PCC6803 (Li et al., 2012), the ccr2 homolog (cyanobacterial cold resistance) in PCC 7806 did not exhibit notable changes in expression due to decrease in temperature; nor did ccr1 (Yin et al., 2007). Ccr2 is a thylakoid-associated protein (Li et al., 2012) and microcystin is known to preferentially localize near thylakoids in PCC 7806 (Young et al., 2005). As neither Raphidiopsis nor Synechocystis produce microcystin, it would be interesting to determine if ccr2 responds differently in non-toxic strains of Microcystis.

In PCC 7806, the expression profile of a group of genes was especially notable. These genes included the sigma factor rpoB, the protease clpB, the heat shock protein hspA, superoxide dismutase sodB, the peroxiredoxin ahpC, and thioredoxin and thioredoxin reductase trxAB, respectively. These genes play a part in maintaining redox balance in the cell and their transcription is known to increase during oxidative stress (Billis et al., 2014; Sinetova and Los, 2016). Consequently, their upregulation in PCC 7806 at 19°C suggests that Microcystis experienced oxidative stress in this condition. However, our interpretation on this point was complicated by the fact that transcriptional response within the complement of peroxiredoxins was incomplete. Notably, none of the four peroxiredoxins of the PrxQ-subclass showed increased expression, indicating that this group of putative peroxidases likely responds to oxidative stress stimuli not triggered by a reduction in temperature.

The similarity of gene expression profiles between PCC 7806 and other model cyanobacteria demonstrated that a decrease in temperature induced a classic cold-stress response in PCC 7806. While perhaps obvious, this conclusion remains important as it confirms the physiological status of the cell, places the response of microcystin quota into context, and demonstrated that experimental methods were robust enough to detect predicted responses.

Cold-Stress Response Is Partitioned Between Short- and Long-Term Time Scales

In continuous cultures of PCC 7806, a decrease in temperature induced mcy gene expression, microcystin production and microcystin cellular concentration. Concomitantly, this decrease in temperature also induced a classic cold-stress response that appears to operate on a timescale different from that of microcystin production. The question then arises as to whether these responses are one in the same? In bacteria, transcriptional response to stress typically occurs with amazing speed: in E. coli, for example, responses to cell envelope damage can be detected in as little as 3 min (Ades et al., 1999), while robust responses to induced oxidative stress occur within 10 min (Jozefczuk et al., 2010). In Synechocystis PCC 6803, exposure to a reduced temperature induces detectable changes in gene expression within 20 min (Los et al., 1997). In this study, the expression of genes in module 1 increased sharply within 24 h of temperature decrease, which was the time resolution of our experiment. In contrast, mcy gene expression, along with other genes in module 3, increased over a period of about 5 days while microcystin concentration increased over a period of 7 days. As a stress response, mcy expression and microcystin production seem to operate over an unusually protracted period. Given the distinct timescales over which genes in module 1 and 3 seem to function, it is possible these genes responded to different manifestations of the same stress stimuli and belong to different regulatory groups. Taken together, our data hint at a partitioning of the cold-stress response in Microcystis between short-term and long-term regulatory networks.

The fact that cellular microcystin concentration increases slowly over a period of days is puzzling. It may be that microcystin biosynthesis is finely calibrated to the damage it presumably mitigates, and that this injury, which can be caused by cool temperature, accumulates incrementally over days. Consistent with these findings, the timescale over which microcystin quotas change in this experiment is similar to that shown in continuous cultures responding to changes in light (Utkilen and Gjølme, 1992). Collectively, these studies support the concept of long-term stress responses and regulatory networks. Unfortunately few studies designed to capture the long-term dynamic response to cold-stress in cyanobacteria are available for comparison. Moreover, the many studies comparing batch cultures grown at different yet constant temperatures do not capture the dynamic nature of the response; they instead observe physiology acclimated to specific temperatures. Additional work investigating various timescales will be needed to clarify and confirm this conjecture.

Change in Cell Size

The increase in cell size that occurred during lower temperature is consistent with indications of a generalized stress response. We base this conclusion tentatively on studies demonstrating that cell size in M. aeruginosa is generally inversely related to growth rate (Long et al., 2001; Yeung et al., 2016) and increases under either general stress conditions (Krüger and Eloff, 1981) or during growth at cooler temperatures (Chen et al., 2011). Our results are consistent with these findings and hint at a more general relationship between cell size and stress in M. aeruginosa. An exception to this trend comes from Yin et al. (2016). These authors found that cell size in M. aeruginosa increased with increasing temperature. It is possible that strain variation (they do not report the specific isolate they used) or specific experimental conditions (they grew strains under 12:12 day:night cycles and in batch culture) may exert enough influence to alter what might be a general trend.

The inverse relationship between cell size and nitrogen concentration was surprising, as it seems to contradict the surface area to volume principle that permits greater nutrient flux per unit cell volume in smaller cells (Grover, 1989; Chisholm, 1992). While data are somewhat scarce, other cyanobacteria seem to follow the surface area to volume concept under some observed nutrient gradients. For example, in Synechococcus and Anabaena flos-aquae, cell size was notably reduced in iron-limited cultures (Gorham et al., 1964; Sherman and Sherman, 1983) and similar observations have been made with natural communities in the Pacific Ocean (Eldridge et al., 2004; Hare et al., 2005). Nevertheless, if a phenomenon exists whereby stress induces an increase in cell size in Microcystis, it is possible that the inverse relationship between cell size and nitrogen concentration is a result of N-limited stress superseding any advantages gained by more efficient nutrient flux due to smaller cells.

The precise mechanism regulating cell size in bacteria is still debated (Harris and Theriot, 2018). Intriguingly, our preliminary observations in M. aeruginosa seem in agreement with the relative rates model proposed by Harris and Theriot (2016) in which cell size is governed by the relative increase in cell envelope biomaterial vs. increase in cell volume. These authors further posited that increase in surface area material is likely regulated by peptidoglycan synthesis. In our case, expression of glmS, the enzyme responsible for the first committed step in peptidoglycan synthesis (Barreteau et al., 2008), dropped sharply when the temperature decreased to 19°C, generally rose slowly through the remainder of cool period, then increased quickly when the temperature returned to 26°C. Based on the relative rates model, this pattern could, in principle, explain the increase in cell size during cold stress and a decrease when warm temperature returns. Likewise, it is possible that other stressors exert their influence and increase cell size by suppressing cell envelope synthesis. While cell size is known to influence key physiological processes in phytoplankton, this subject is outside the purview of this study. We report on it here only because it affects normalization methods, it is consistent with other reports of stress response, and it may provide information useful to other researchers.

Proposed Mechanism for Microcystin Response to Cold Stress

The mechanism responsible for increased synthesis of microcystin during cold stress is uncertain. In a widely cited paper, Zilliges et al. (2011) hypothesized that microcystin mitigates the effects of oxidative stress on Calvin cycle proteins. Building upon this hypothesis, we suggest a provisional mechanism for the stimulation of production of microcystin during cool temperatures. Conceptually, the mechanism would be activated in the following way. A downshift in temperature is known to suppress photodamage repair of PSII (Allakhverdiev and Murata, 2004; Murata et al., 2007), leaving the reaction center in a decreased state of repair after a period of lower temperatures. Compounding this strain, under constant light, a decrease in temperature increases PSII excitation pressure and offsets cellular redox balance via the enzyme-mediated transport chain (Maxwell et al., 1995). In combination, these factors trigger an oxidative stress response, of which an increase in microcystin production is part.

The proposed mechanism is compatible with results by Kaebernick et al. (2000) in which PCC 7806 exposed to high light intensity increased transcription of mcyBD, but did not increase detectable cellular microcystin content. The group later demonstrated that high light intensity and oxidative stress stimulated binding of microcystin to photosynthetic proteins, thus linking microcystin to an oxidative stress response and at least partially explaining the apparent disconnect between expression of mcy and quota (Zilliges et al., 2011; Meissner et al., 2013). Excitation pressure in PSII increases with light intensity if temperature is constant and increases at constant light if temperature is decreased (Maxwell et al., 1995). Consequently the two methods should, in principal, lead to an equivalent or similar modulation of excitation pressure (Maxwell et al., 1995). In this way, the observed responses to cold stress vs. high light may be one in the same.

We see an increase in mcy expression with a concomitant increase in cellular microcystin content over time. But this increase in content occurs only after a small, short-term decline 24–48 h after the downshift in temperature. This temporary decline is consistent with the concept that induction of oxidative stress stimulates microcystin binding to proteins, thus hiding that portion of the cellular pool of microcystin from standard detection methods (Meissner et al., 2013). Moreover, the timescale over which it occurs coincides with that demonstrated in Schuurmans et al. (2018). These authors hypothesized that the short-term decline was due to binding of microcystin to proteins upon induction of severe oxidative stress via application of hydrogen peroxide.

Time-Lag Correlation of Microcystin and mcy Expression

Several studies have examined the relationship between mcy expression and microcystin quota, and found either no or (at best) a weak correlation (Kaebernick et al., 2000; Tonk et al., 2005; Sevilla et al., 2008; Peng et al., 2018). This might be explained in part by the fact that environmental stimuli that induce mcy transcription can also stimulate the binding of microcystin to cellular proteins, thus hiding this portion of microcystin from detection (Meissner et al., 2013). Our results provide an additional potential explanation.

Under the conditions tested, we also saw no correlation between mcy expression and concurrent microcystin concentration, but instead observed a very strong 48 h time-lag correlation of microcystin content to mcy expression. The reason for such a long time lag between gene expression and the manifestation of that expression is unclear. The relationship could be an artifact of experimental conditions such as strain specificity, continuous irradiance, dilution rate, or experimental duration. But the fact that mcy expression was highly time-lagged correlated to microcystin concentration over a 21-day period across conditions of both increasing and decreasing microcystin production is intriguing and has potentially exciting implications. If this observation can be confirmed in other strains, other experimental designs, and in field conditions, it opens a future possibility of forecasting fluctuations in bloom toxicity with a 48- to 72-h lead-time.

Conclusion

In this work, we demonstrated that cellular microcystin concentration increases when M. aeruginosa PCC 7806 is subjected to temperatures below those optimal for growth, confirming this phenotype in a separate disparate strain. Gene expression profiles demonstrated that the drop in temperature induced a cold-stress response in Microcystis but suggested that the increase in microcystin production may be regulated through separate transcriptional networks and on a different timescale. This simple method of manipulating microcystin production in the laboratory should prove valuable in exploring the eco-physiological function of microcystin. This response to cool temperature has potential to partially explain the observation that natural blooms are frequently found to be more toxic during late spring when water temperature is cooler and less toxic in mid-summer as water temperatures rise. Similarly, the work suggests that episodic climactic events that can cause significant reduction in surface temperature might influence toxin production by in situ populations. We show that under the conditions tested, microcystin concentration is highly time-lag correlated to mcy gene expression. If confirmed under field conditions, this raises the possibility of estimating fluctuations in bloom toxicity with a 48-h lead-time by monitoring gene expression.

Data Availability Statement

The datasets presented in this study can be found in online repositories. The names of the repository/repositories and accession number(s) can be found in the article/Supplementary Material.

Author Contributions

RM, SW, FH, and AP conceived and designed the research. RM and GS performed the experiments. DD, BW, and GB performed the microcystin analysis. RM, MM, and EG analyzed the data. RM and SW wrote the draft manuscript. All the authors contributed to and reviewed the final version of the manuscript.

Conflict of Interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Funding

This work was supported by grants from the National Oceanographic and Atmospheric Administration (NA18NOS4780175) to SW, FH, and AP. This is NOAA contribution # 970. This work was also supported by a grant from the National Science Foundation (IOS-1451528 to SW), and funding from the NIEHS (1P01ES028939–01) and NSF (OCE-1840715) to SW through the Great Lakes Center for Fresh Waters and Human Health at Bowling Green State University.

Acknowledgments

The authors thank Gary LeCleir, George Bullerjahn, and Mike McKay for thoughts and comments on this project and Xiaocun Sun and Andrew Steen for advice on statistical analysis.

Supplementary Material

The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fmicb.2020.601864/full#supplementary-material

References

Ades, S. E., Connolly, L. E., Alba, B. M., and Gross, C. A. (1999). The Escherichia coli sigma E-dependent extracytoplasmic stress response is controlled by the regulated proteolysis of an anti-sigma factor. Genes Dev. 13, 2449–2461. doi: 10.1101/gad.13.18.2449

PubMed Abstract | CrossRef Full Text | Google Scholar

Allakhverdiev, S. I., and Murata, N. (2004). Environmental stress inhibits the synthesis de novo of proteins involved in the photodamage-repair cycle of photosystem II in Synechocystis sp. PCC 6803. Biochim. Biophys. Acta 1657, 23–32. doi: 10.1016/j.bbabio.2004.03.003

PubMed Abstract | CrossRef Full Text | Google Scholar

American Public and Health Association (2017). “4110 Determination of anions by ion chromatography,” in Standard Methods for the Examination of Water and Wastewater, 23rd Edn, eds A. Eaton, R. Baird, and E. Rice (Washington, DC: American Public Health Association).

Google Scholar

Antosiak, A., Tokodi, N., Maziarz, R., Kokociński, M., Brzozowska, A., Strzałka, W., et al. (2020). Different gene expression response of Polish and Australian Raphidiopsis raciborskii strains to the chill/light stress. Appl.Sci. 10:5437. doi: 10.3390/app10165437

CrossRef Full Text | Google Scholar

Ashburner, M., Ball, C. A., Blake, J. A., Botstein, D., Butler, H., Cherry, J. M., et al. (2000). Gene ontology: tool for the unification of biology. Nat. Genet. 25, 25–29. doi: 10.1038/75556

PubMed Abstract | CrossRef Full Text | Google Scholar

Barchewitz, T., Guljamow, A., Meissner, S., Timm, S., Henneberg, M., Baumann, O., et al. (2019). Non-canonical localization of RubisCO under high-light conditions in the toxic cyanobacterium Microcystis aeruginosa PCC7806. Environ. Microbiol. 21, 4836–4851. doi: 10.1111/1462-2920.14837

PubMed Abstract | CrossRef Full Text | Google Scholar

Barreteau, H., Kovac, A., Boniface, A., Sova, M., Gobec, S., and Blanot, D. (2008). Cytoplasmic steps of peptidoglycan biosynthesis. FEMS Microbiol. Rev. 32, 168–207. doi: 10.1111/j.1574-6976.2008.00104.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Billis, K., Billini, M., Tripp, H. J., Kyrpides, N. C., and Mavromatis, K. (2014). Comparative transcriptomics between Synechococcus PCC 7942 and Synechocystis PCC 6803 provide insights into mechanisms of stress acclimation. PLoS ONE 9:e109738. doi: 10.1371/journal.pone.0109738

PubMed Abstract | CrossRef Full Text | Google Scholar

Boyer, G. L. (2007). The occurrence of cyanobacterial toxins in New York lakes: lessons from the MERHAB-lower Great Lakes program. Lake Reserv. Manag. 23, 153–160. doi: 10.1080/07438140709353918

CrossRef Full Text | Google Scholar

Boyer, G. L. (2020). LCMS-SOP determination of microcystins in water samples by high performance liquid chromatography (HPLC) with single quadrupole mass spectrometry (MS) [Online]. protocols.io. Available Online at: https://dx.doi.org/10.17504/protocols.io.bck2iuye (Accessed July 7 2020).

Google Scholar

Carmichael, W. W., and Boyer, G. L. (2016). Health impacts from cyanobacteria harmful algae blooms: implications for the North American Great Lakes. Harmful Algae 54, 194–212. doi: 10.1016/j.hal.2016.02.002

PubMed Abstract | CrossRef Full Text | Google Scholar

Chen, M., Li, J., Dai, X., Sun, Y., and Chen, F. (2011). Effect of phosphorus and temperature on chlorophyll a contents and cell sizes of Scenedesmus obliquus and Microcystis aeruginosa. Limnology 12, 187–192. doi: 10.1007/s10201-010-0336-y

CrossRef Full Text | Google Scholar

Chisholm, S. W. (1992). “Phytoplankton Size,” in Primary Productivity and Biogeochemical Cycles in the Sea, eds P. G. Falkowski, A. D. Woodhead, and K. Vivirito (Boston, MA: Springer), 213–237. doi: 10.1007/978-1-4899-0762-2_12

CrossRef Full Text | Google Scholar

Drath, M., Kloft, N., Batschauer, A., Marin, K., Novak, J., and Forchhammer, K. (2008). Ammonia triggers photodamage of photosystem II in the cyanobacterium Synechocystis sp. strain PCC 6803. Plant Physiol. 147, 206–215. doi: 10.1104/pp.108.117218

PubMed Abstract | CrossRef Full Text | Google Scholar

Eldridge, M. L., Trick, C. G., Alm, M. B., DiTullio, G. R., Rue, E. L., Bruland, K. W., et al. (2004). Phytoplankton community response to a manipulation of bioavailable iron in HNLC waters of the subtropical pacific ocean. Aquat. Microb. Ecol. 35, 79–91. doi: 10.3354/ame035079

CrossRef Full Text | Google Scholar

Gene Ontology Consortium (2019). The gene ontology resource: 20 years and still GOing strong. Nucleic Acids Res. 47, D330–D338. doi: 10.1093/nar/gky1055

PubMed Abstract | CrossRef Full Text | Google Scholar

Ginn, H. P., Pearson, L. A., and Neilan, B. A. (2010). NtcA from Microcystis aeruginosa PCC 7806 is autoregulatory and binds to the microcystin promoter. Appl. Environ. Microbiol. 76, 4362–4368. doi: 10.1128/aem.01862-09

PubMed Abstract | CrossRef Full Text | Google Scholar

Gobler, C. J., Burkholder, J. M., Davis, T. W., Harke, M. J., Johengen, T., Stow, C. A., et al. (2016). The dual role of nitrogen supply in controlling the growth and toxicity of cyanobacterial blooms. Harmful Algae 54, 87–97. doi: 10.1016/j.hal.2016.01.010

PubMed Abstract | CrossRef Full Text | Google Scholar

Gorham, P., McLachlan, J., Hammer, U., and Kim, W. (1964). Isolation and culture of toxic strains of Anabaena flos-aquae (Lyngb.). SIL Proc. 15, 796–804. doi: 10.1080/03680770.1962.11895606

CrossRef Full Text | Google Scholar

Götz, S., García-Gómez, J. M., Terol, J., Williams, T. D., Nagaraj, S. H., Nueda, M. J., et al. (2008). High-throughput functional annotation and data mining with the Blast2GO suite. Nucleic Acids Res. 36, 3420–3435. doi: 10.1093/nar/gkn176

PubMed Abstract | CrossRef Full Text | Google Scholar

Greenhouse, S. W., and Geisser, S. (1959). On methods in the analysis of profile data. Psychometrika 24, 95–112. doi: 10.1007/BF02289823

CrossRef Full Text | Google Scholar

Grover, J. P. (1989). Influence of cell shape and size on algal competitive ability. J. Phycol. 25, 402–405. doi: 10.1111/j.1529-8817.1989.tb00138.x

CrossRef Full Text | Google Scholar

Hare, C. E., DiTullio, G. R., Trick, C. G., Wilhelm, S. W., Bruland, K. W., Rue, E. L., et al. (2005). Phytoplankton community structure changes following simulated upwelled iron inputs in the peru upwelling region. Aquat. Microb. Ecol. 38, 269–282. doi: 10.3354/ame038269

CrossRef Full Text | Google Scholar

Harke, M. J., Steffen, M. M., Gobler, C. J., Otten, T. G., Wilhelm, S. W., Wood, S. A., et al. (2016). A review of the global ecology, genomics, and biogeography of the commonly toxic cyanobacterium. Microcystis spp. Harmful Algae 54, 4–20. doi: 10.1016/j.hal.2015.12.00

CrossRef Full Text | Google Scholar

Harris, L. K., and Theriot, J. A. (2016). Relative rates of surface and volume synthesis set bacterial cell size. Cell 165, 1479–1492. doi: 10.1016/j.cell.2016.05.045

PubMed Abstract | CrossRef Full Text | Google Scholar

Harris, L. K., and Theriot, J. A. (2018). Surface area to volume ratio: a natural variable for bacterial morphogenesis. Trends Microbiol. 26, 815–832. doi: 10.1016/j.tim.2018.04.008

PubMed Abstract | CrossRef Full Text | Google Scholar

Herbert, D., Elsworth, R., and Telling, R. (1956). The continuous culture of bacteria; a theoretical and experimental study. Microbiology 14, 601–622. doi: 10.1099/00221287-14-3-601

PubMed Abstract | CrossRef Full Text | Google Scholar

Ho, J. C., Michalak, A. M., and Pahlevan, N. (2019). Widespread global increase in intense lake phytoplankton blooms since the 1980s. Nature 574, 667–670. doi: 10.1038/s41586-019-1648-7

PubMed Abstract | CrossRef Full Text | Google Scholar

Huisman, J., Codd, G. A., Paerl, H. W., Ibelings, B. W., Verspagen, J. M. H., and Visser, P. M. (2018). Cyanobacterial blooms. Nat. Rev. Microbiol. 16, 471–483. doi: 10.1038/s41579-018-0040-1

PubMed Abstract | CrossRef Full Text | Google Scholar

Inaba, M., Suzuki, I., Szalontai, B., Kanesaki, Y., Los, D. A., Hayashi, H., et al. (2003). Gene-engineered rigidification of membrane lipids enhances the cold inducibility of gene expression in Synechocystis. J. Biol. Chem. 278, 12191–12198. doi: 10.1074/jbc.M212204200

PubMed Abstract | CrossRef Full Text | Google Scholar

Jenny, J.-P., Anneville, O., Arnaud, F., Baulaz, Y., Bouffard, D., Domaizon, I., et al. (2020). Scientists’ warning to humanity: rapid degradation of the world’s large lakes. J. Great Lakes Res. 46, 686–702. doi: 10.1016/j.jglr.2020.05.006

CrossRef Full Text | Google Scholar

Jozefczuk, S., Klie, S., Catchpole, G., Szymanski, J., Cuadros-Inostroza, A., Steinhauser, D., et al. (2010). Metabolomic and transcriptomic stress response of Escherichia coli. Mol. Syst. Biol. 6:364. doi: 10.1038/msb.2010.18

PubMed Abstract | CrossRef Full Text | Google Scholar

Jungblut, A. D., Hawes, I., Mountfort, D., Hitzfeld, B., Dietrich, D. R., Burns, B. P., et al. (2005). Diversity within cyanobacterial mat communities in variable salinity meltwater ponds of McMurdo Ice Shelf. Antarct. Environ. Microbiol. 7, 519–529. doi: 10.1111/j.1462-2920.2005.00717.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Kaebernick, M., Neilan, B. A., Borner, T., and Dittmann, E. (2000). Light and the transcriptional response of the microcystin biosynthesis gene cluster. Appl. Environ. Microbiol. 66, 3387–3392. doi: 10.1128/aem.66.8.3387-3392.2000

PubMed Abstract | CrossRef Full Text | Google Scholar

Kanervo, E., Tasaka, Y., Murata, N., and Aro, E.-M. (1997). Membrane lipid unsaturation modulates processing of the photosystem II reaction-center protein D1 at low temperatures. Plant Physiol. 114, 841–849. doi: 10.1104/pp.114.3.841

PubMed Abstract | CrossRef Full Text | Google Scholar

Kardinaal, W. E. A., and Visser, P. M. (2005). “Dynamics of cyanobacterial toxins,” in Harmful Cyanobacteria Aquatic Ecology Series, eds J. Huisman, H. C. P. Matthijs, and P. M. Visser (Dordrecht: Springer), 41–64. doi: 10.1007/1-4020-3022-3_3

CrossRef Full Text | Google Scholar

Kopylova, E., Noé, L., and Touzet, H. (2012). SortMeRNA: fast and accurate filtering of ribosomal RNAs in metatranscriptomic data. Bioinformatics 28, 3211–3217. doi: 10.1093/bioinformatics/bts611

PubMed Abstract | CrossRef Full Text | Google Scholar

Krüger, G., and Eloff, J. (1981). The effect of physico-chemical factors on growth relevant to the mass culture of axenic Microcystis,” in The Water Environment, ed. W.W. Carmichael. Boston, MA: Springer, 193–222. doi: 10.1007/978-1-4613-3267-1_15

CrossRef Full Text | Google Scholar

Langfelder, P., and Horvath, S. (2008). WGCNA: an R package for weighted correlation network analysis. BMC Bioinformatics 9:559. doi: 10.1186/1471-2105-9-559

PubMed Abstract | CrossRef Full Text | Google Scholar

Li, W., Gao, H., Yin, C., and Xu, X. (2012). Identification of a novel thylakoid protein gene involved in cold acclimation in cyanobacteria. Microbiology 158, 2440–2449. doi: 10.1099/mic.0.060038-0

PubMed Abstract | CrossRef Full Text | Google Scholar

Loftin, K. A., Graham, J. L., Hilborn, E. D., Lehmann, S. C., Meyer, M. T., Dietze, J. E., et al. (2016). Cyanotoxins in inland lakes of the United States: occurrence and potential recreational health risks in the EPA national lakes Assessment 2007. Harmful Algae 56, 77–90. doi: 10.1016/j.hal.2016.04.001

PubMed Abstract | CrossRef Full Text | Google Scholar

Long, B. M., Jones, G. J., and Orr, P. T. (2001). Cellular microcystin content in N-limited Microcystis aeruginosa can be predicted from growth rate. Appl. Environ. Microbiol. 67, 278–283. doi: 10.1128/aem.67.1.278-283.2001

PubMed Abstract | CrossRef Full Text | Google Scholar

Los, D. A., Ray, M. K., and Murata, N. (1997). Differences in the control of the temperature-dependent expression of four genes for desaturases in Synechocystis sp. PCC 6803. Mol. Microbiol. 25, 1167–1175. doi: 10.1046/j.1365-2958.1997.5641912.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Ludwig, M., and Bryant, D. A. (2012). Synechococcus sp. strain PCC 7002 transcriptome: acclimation to temperature, salinity, oxidative stress, and mixotrophic growth conditions. Front. Microbiol. 3:354. doi: 10.3389/fmicb.2012.00354

PubMed Abstract | CrossRef Full Text | Google Scholar

MacKintosh, C., Beattie, K. A., Klumpp, S., Cohen, P., and Codd, G. A. (1990). Cyanobacterial microcystin-LR is a potent and specific inhibitor of protein phosphatases 1 and 2A from both mammals and higher plants. FEBS Lett. 264, 187–192. doi: 10.1016/0014-5793(90)80245-E

CrossRef Full Text | Google Scholar

Mantzouki, E., Lurling, M., Fastner, J., de Senerpont Domis, L., Wilk-Wozniak, E., Koreiviene, J., et al. (2018). Temperature effects explain continental scale distribution of cyanobacterial toxins. Toxins 10:156. doi: 10.3390/toxins10040156

PubMed Abstract | CrossRef Full Text | Google Scholar

Martin, R. M., and Wilhelm, S. W. (2017). Hot-phenol RNA Extraction [Online]. Berkeley: protocol.io. doi: 10.17504/protocols.io.g89bzz6 (accessed July 8, 2020).

CrossRef Full Text | Google Scholar

Martin, R. M., and Wilhelm, S. W. (2020). Phenol-based RNA Extraction From Polycarbonate Filters [Online]. Berkeley: protocol.io. doi: 10.17504/protocols.io.bivuke6w (accessed July 27, 2020).

CrossRef Full Text | Google Scholar

Maxwell, D. P., Falk, S., and Huner, N. P. (1995). Photosystem II excitation pressure and development of resistance to photoinhibition I. Light-harvesting complex II abundance and zeaxanthin content in Chlorella vulgaris. Plant Physiol. 107, 687–694. doi: 10.1104/pp.107.3.687

PubMed Abstract | CrossRef Full Text | Google Scholar

Meissner, S., Fastner, J., and Dittmann, E. (2013). Microcystin production revisited: conjugate formation makes a major contribution. Environ. Microbiol. 15, 1810–1820. doi: 10.1111/1462-2920.12072

PubMed Abstract | CrossRef Full Text | Google Scholar

Meyer, K. A., Davis, T. W., Watson, S. B., Denef, V. J., Berry, M. A., and Dick, G. J. (2017). Genome sequences of lower great lakes Microcystis sp. reveal strain-specific genes that are present and expressed in western Lake Erie blooms. PLoS ONE 12:e0183859. doi: 10.1371/journal.pone.0183859

PubMed Abstract | CrossRef Full Text | Google Scholar

Murata, N., Takahashi, S., Nishiyama, Y., and Allakhverdiev, S. I. (2007). Photoinhibition of photosystem II under environmental stress. Biochim. Biophys. Acta 1767, 414–421. doi: 10.1016/j.bbabio.2006.11.019

PubMed Abstract | CrossRef Full Text | Google Scholar

Murata, N., and Wada, H. (1995). Acyl-lipid desaturases and their importance in the tolerance and acclimatization to cold of cyanobacteria. Biochem. J. 308:1. doi: 10.1042/bj3080001

PubMed Abstract | CrossRef Full Text | Google Scholar

Omidi, A., Esterhuizen-Londt, M., and Pflugmacher, S. (2018). Still challenging: the ecological function of the cyanobacterial toxin microcystin–what we know so far. Toxin Rev. 37, 87–105. doi: 10.1080/15569543.2017.1326059

CrossRef Full Text | Google Scholar

Pachauri, R. K., Allen, M. R., Barros, V. R., Broome, J., Cramer, W., Christ, R., et al. (2014). Climate change 2014: synthesis report. Contribution of Working Groups I, II and III to the fifth assessment report of the Intergovernmental Panel on Climate Change. Geneva: IPCC.

Google Scholar

Paerl, H. W., and Huisman, J. (2008). Blooms like it hot. Science 320, 57–58. doi: 10.1126/science.1155398

PubMed Abstract | CrossRef Full Text | Google Scholar

Peng, G., Martin, R., Dearth, S., Sun, X., Boyer, G. L., Campagna, S., et al. (2018). Seasonally-relevant cool temperatures interact with N chemistry to increase microcystins produced in lab cultures of Microcystis aeruginosa NIES-843. Environ. Sci. Technol. 52, 4127–4136. doi: 10.1021/acs.est.7b06532

PubMed Abstract | CrossRef Full Text | Google Scholar

Pimentel, J. S., and Giani, A. (2014). Microcystin production and regulation under nutrient stress conditions in toxic Microcystis strains. Appl. Environ. Microbiol. 80, 5836–5843. doi: 10.1128/AEM.01009-14

PubMed Abstract | CrossRef Full Text | Google Scholar

Rhee, G. Y., and Gotham, I. J. (1981). The effect of environmental factors on phytoplankton growth: temperature and the interactions of temperature with nutrient limitation. Limnol. Oceanogr. 26, 635–648. doi: 10.4319/lo.1981.26.4.0635

CrossRef Full Text | Google Scholar

Robinson, M. D., McCarthy, D. J., and Smyth, G. K. (2010). edgeR: a Bioconductor package for differential expression analysis of digital gene expression data. Bioinformatics 26, 139–140. doi: 10.1093/bioinformatics/btp616

PubMed Abstract | CrossRef Full Text | Google Scholar

Rocca, J. D., Hall, E. K., Lennon, J. T., Evans, S. E., Waldrop, M. P., Cotner, J. B., et al. (2015). Relationships between protein-encoding gene abundance and corresponding process are commonly assumed yet rarely observed. ISME J. 9, 1693–1699. doi: 10.1038/ismej.2014.252

PubMed Abstract | CrossRef Full Text | Google Scholar

Schmitt, W. A., Raab, R. M., and Stephanopoulos, G. (2004). Elucidation of gene interaction networks through time-lagged correlation analysis of transcriptional data. Genome Res. 14, 1654–1663. doi: 10.1101/gr.2439804

PubMed Abstract | CrossRef Full Text | Google Scholar

Schuurmans, J. M., Brinkmann, B. W., Makower, A. K., Dittmann, E., Huisman, J., and Matthijs, H. C. (2018). Microcystin interferes with defense against high oxidative stress in harmful cyanobacteria. Harmful Algae 78, 47–55. doi: 10.1016/j.hal.2018.07.008

PubMed Abstract | CrossRef Full Text | Google Scholar

Sevilla, E., Martin-Luna, B., Vela, L., Bes, M. T., Fillat, M. F., and Peleato, M. L. (2008). Iron availability affects mcyD expression and microcystin-LR synthesis in Microcystis aeruginosa PCC7806. Environ. Microbiol. 10, 2476–2483. doi: 10.1111/j.1462-2920.2008.01663.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Sherman, D. M., and Sherman, L. A. (1983). Effect of iron deficiency and iron restoration on ultrastructure of Anacystis nidulans. J. Bacteriol. 156, 393–401. doi: 10.1128/jb.156.1.393-401.1983

PubMed Abstract | CrossRef Full Text | Google Scholar

Shukla, P., Skeg, J., Buendia, E. C., Masson-Delmotte, V., Pörtner, H.-O., Roberts, D., et al. (2019). Climate Change and Land: an IPCC special report on climate change, desertification, land degradation, sustainable land management, food security, and greenhouse gas fluxes in terrestrial ecosystems. Geneva: IPCC.

Google Scholar

Sinetova, M., and Los, D. (2016). Systemic analysis of stress transcriptomics of Synechocystis reveals common stress genes and their universal triggers. Mol. Biosyst. 12, 3254–3258. doi: 10.1039/C6MB00551A

PubMed Abstract | CrossRef Full Text | Google Scholar

Spaulding, B. (2014). FlowCam Manual. Maine, USA.: Fluid Imaging Technologies.

Google Scholar

Suzuki, I., Kanesaki, Y., Mikami, K., Kanehisa, M., and Murata, N. (2001). Cold-regulated genes under control of the cold sensor Hik33 in Synechocystis. Mol. Microbiol. 40, 235–244. doi: 10.1046/j.1365-2958.2001.02379.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Tan, X., Zhu, T., Shen, S., Yin, C., Gao, H., and Xu, X. (2011). Role of rbp1 in the acquired chill-light tolerance of cyanobacteria. J. Bacteriol. 193, 2675–2683. doi: 10.1128/jb.01454-10

PubMed Abstract | CrossRef Full Text | Google Scholar

Tillett, D., Dittmann, E., Erhard, M., von Dohren, H., Borner, T., and Neilan, B. A. (2000). Structural organization of microcystin biosynthesis in Microcystis aeruginosa PCC7806: an integrated peptide-polyketide synthetase system. Chem. Biol. 7, 753–764. doi: 10.1016/s1074-5521(00)00021-1

CrossRef Full Text | Google Scholar

Tonk, L., Visser, P. M., Christiansen, G., Dittmann, E., Snelder, E. O., Wiedner, C., et al. (2005). The microcystin composition of the cyanobacterium Planktothrix agardhii changes toward a more toxic variant with increasing light intensity. Appl. Environ. Microbiol. 71, 5177–5181. doi: 10.1128/AEM.71.9.5177-5181.2005

PubMed Abstract | CrossRef Full Text | Google Scholar

Tonk, L., Welker, M., Huisman, J., and Visser, P. M. (2009). Production of cyanopeptolins, anabaenopeptins, and microcystins by the harmful cyanobacteria Anabaena 90 and Microcystis PCC 7806. Harmful Algae 8, 219–224. doi: 10.1016/j.hal.2008.05.005

CrossRef Full Text | Google Scholar

Utkilen, H., and Gjølme, N. (1992). Toxin production by Microcystis aeruginosa as a function of light in continuous cultures and its ecological significance. Appl. Environ. Microbiol. 58, 1321–1325. doi: 10.1128/aem.58.4.1321-1325.1992

PubMed Abstract | CrossRef Full Text | Google Scholar

Vadia, S., and Levin, P. A. (2015). Growth rate and cell size: a re-examination of the growth law. Curr. Opin. Microbiol. 24, 96–103. doi: 10.1016/j.mib.2015.01.011

PubMed Abstract | CrossRef Full Text | Google Scholar

Varkey, D., Mazard, S., Ostrowski, M., Tetu, S. G., Haynes, P., and Paulsen, I. T. (2016). Effects of low temperature on tropical and temperate isolates of marine Synechococcus. ISME J. 10, 1252–1263. doi: 10.1038/ismej.2015.179

PubMed Abstract | CrossRef Full Text | Google Scholar

Wagner, G. P., Kin, K., and Lynch, V. J. (2012). Measurement of mRNA abundance using RNA-seq data: RPKM measure is inconsistent among samples. Theory Biosci. 131, 281–285. doi: 10.1007/s12064-012-0162-3

PubMed Abstract | CrossRef Full Text | Google Scholar

Watanabe, M. M., and Ichimura, T. (1977). Fresh and salt-water forms of Spirulina platensis in axenic cultures. Bull. Jap. Soc. Phycol. 25, 371–377.

Google Scholar

Watson, S. B., Miller, C., Arhonditsis, G., Boyer, G. L., Carmichael, W., Charlton, M. N., et al. (2016). The re-eutrophication of Lake Erie: harmful algal blooms and hypoxia. Harmful Algae 56, 44–66. doi: 10.1016/j.hal.2016.04.010

PubMed Abstract | CrossRef Full Text | Google Scholar

Wei, N., Hu, L., Song, L., and Gan, N. (2016). Microcystin-bound protein patterns in different cultures of Microcystis aeruginosa and field samples. Toxins (Basel) 8:293. doi: 10.3390/toxins8100293

PubMed Abstract | CrossRef Full Text | Google Scholar

Wilhelm, S. W., Bullerjahn, G. S., and McKay, R. M. L. (2020). The complicated and confusing ecology of Microcystis blooms. mBio 11:20. doi: 10.1128/mBio.00529-20

PubMed Abstract | CrossRef Full Text | Google Scholar

Yeung, A. C., D’Agostino, P. M., Poljak, A., McDonald, J., Bligh, M. W., Waite, T. D., et al. (2016). Physiological and proteomic responses of continuous cultures of Microcystis aeruginosa PCC7806 to changes in iron bioavailability and growth rate. Appl. Environ. Microbiol. 82, 5918–5929. doi: 10.1128/AEM.01207-16

PubMed Abstract | CrossRef Full Text | Google Scholar

Yin, C., Li, W., Du, Y., Kong, R., and Xu, X. (2007). Identification of a gene, ccr-1 (sll1242), required for chill-light tolerance and growth at 15 °C in Synechocystis sp. PCC 6803. Microbiology 153, 1261–1267. doi: 10.1099/mic.0.2006/005074-0

PubMed Abstract | CrossRef Full Text | Google Scholar

Yin, Y., Zhang, Y., Wang, M., and Shi, K. (2016). Effects of temperature on the optical properties of Microcystis aeruginosa and Scenedesmus obliquus. J. Freshwater Ecol. 31, 361–375. doi: 10.1080/02705060.2016.1151467

CrossRef Full Text | Google Scholar

Young, F. M., Thomson, C., Metcalf, J. S., Lucocq, J. M., and Codd, G. A. (2005). Immunogold localisation of microcystins in cryosectioned cells of Microcystis. J. Struct. Biol. 151, 208–214. doi: 10.1016/j.jsb.2005.05.007

PubMed Abstract | CrossRef Full Text | Google Scholar

Zhang, B., and Horvath, S. (2005). A general framework for weighted gene co-expression network analysis. Stat. Appl. Genet. Mol. Biol. 4:17. doi: 10.2202/1544-6115.1128

PubMed Abstract | CrossRef Full Text | Google Scholar

Zhang, Y., Mandava, C. S., Cao, W., Li, X., Zhang, D., Li, N., et al. (2015). HflX is a ribosome-splitting factor rescuing stalled ribosomes under stress conditions. Nat. Struct. Mol. Biol. 22, 906–913. doi: 10.1038/nsmb.3103

PubMed Abstract | CrossRef Full Text | Google Scholar

Zhao, L., Song, Y., Li, L., Gan, N., Brand, J. J., and Song, L. (2018). The highly heterogeneous methylated genomes and diverse restriction-modification systems of bloom-forming Microcystis. Harmful Algae 75, 87–93. doi: 10.1016/j.hal.2018.04.005

PubMed Abstract | CrossRef Full Text | Google Scholar

Zilliges, Y., Kehr, J. C., Meissner, S., Ishida, K., Mikkat, S., Hagemann, M., et al. (2011). The cyanobacterial hepatotoxin microcystin binds to proteins and increases the fitness of Microcystis under oxidative stress conditions. PLoS ONE 6:e17615. doi: 10.1371/journal.pone.0017615

PubMed Abstract | CrossRef Full Text | Google Scholar

Keywords: microcystin, temperature, cyanotoxins, cyanobacteria, episodic events

Citation: Martin RM, Moniruzzaman M, Stark GF, Gann ER, Derminio DS, Wei B, Hellweger FL, Pinto A, Boyer GL and Wilhelm SW (2020) Episodic Decrease in Temperature Increases mcy Gene Transcription and Cellular Microcystin in Continuous Cultures of Microcystis aeruginosa PCC 7806. Front. Microbiol. 11:601864. doi: 10.3389/fmicb.2020.601864

Received: 09 September 2020; Accepted: 12 November 2020;
Published: 03 December 2020.

Edited by:

Thomas E. Hanson, University of Delaware, United States

Reviewed by:

Leda Giannuzzi, Consejo Nacional de Investigaciones Científicas y Técnicas (CONICET), Argentina
Huansheng Cao, Arizona State University, United States
Dariusz Dziga, Jagiellonian University, Poland

Copyright © 2020 Martin, Moniruzzaman, Stark, Gann, Derminio, Wei, Hellweger, Pinto, Boyer and Wilhelm. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Steven W. Wilhelm, wilhelm@utk.edu