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. 2024 Jul 23;9(7):e0070923.
doi: 10.1128/msystems.00709-23. Epub 2024 Jun 10.

Microbial diversity, genomics, and phage-host interactions of cyanobacterial harmful algal blooms

Affiliations

Microbial diversity, genomics, and phage-host interactions of cyanobacterial harmful algal blooms

Lauren E Krausfeldt et al. mSystems. .

Abstract

The occurrence of cyanobacterial harmful algal blooms (cyanoHABs) is related to their physical and chemical environment. However, less is known about their associated microbial interactions and processes. In this study, cyanoHABs were analyzed as a microbial ecosystem, using 1 year of 16S rRNA sequencing and 70 metagenomes collected during the bloom season from Lake Okeechobee (Florida, USA). Biogeographical patterns observed in microbial community composition and function reflected ecological zones distinct in their physical and chemical parameters that resulted in bloom "hotspots" near major lake inflows. Changes in relative abundances of taxa within multiple phyla followed increasing bloom severity. Functional pathways that correlated with increasing bloom severity encoded organic nitrogen and phosphorus utilization, storage of nutrients, exchange of genetic material, phage defense, and protection against oxidative stress, suggesting that microbial interactions may promote cyanoHAB resilience. Cyanobacterial communities were highly diverse, with picocyanobacteria ubiquitous and oftentimes most abundant, especially in the absence of blooms. The identification of novel bloom-forming cyanobacteria and genomic comparisons indicated a functionally diverse cyanobacterial community with differences in its capability to store nitrogen using cyanophycin and to defend against phage using CRISPR and restriction-modification systems. Considering blooms in the context of a microbial ecosystem and their interactions in nature, physiologies and interactions supporting the proliferation and stability of cyanoHABs are proposed, including a role for phage infection of picocyanobacteria. This study displayed the power of "-omics" to reveal important biological processes that could support the effective management and prediction of cyanoHABs.

Importance: Cyanobacterial harmful algal blooms pose a significant threat to aquatic ecosystems and human health. Although physical and chemical conditions in aquatic systems that facilitate bloom development are well studied, there are fundamental gaps in the biological understanding of the microbial ecosystem that makes a cyanobacterial bloom. High-throughput sequencing was used to determine the drivers of cyanobacteria blooms in nature. Multiple functions and interactions important to consider in cyanobacterial bloom ecology were identified. The microbial biodiversity of blooms revealed microbial functions, genomic characteristics, and interactions between cyanobacterial populations that could be involved in bloom stability and more coherently define cyanobacteria blooms. Our results highlight the importance of considering cyanobacterial blooms as a microbial ecosystem to predict, prevent, and mitigate them.

Keywords: Lake Okeechobee; blooms; cyanobacteria; metagenomics; microbial biodiversity; microbial interactions.

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Conflict of interest statement

The authors declare no conflict of interest.

Figures

Fig 1
Fig 1
A map of Lake Okeechobee showing ecological zones and the sites sampled in this study. The color of the points corresponds to the ecological zone they represented in this study: dark blue closed circles = pelagic zone, light blue closed squares = nearshore zone, and green closed triangles = lake inflow. The shading on the map represents the boundaries of ecological zones that have been previously described: light blue = pelagic, orange = nearshore, and green = littoral zone. No samples from this study were collected from the littoral zone. The top left shows the relative position of the lake in Florida (USA) and sampling sites S79 and S80. Map of Lake Okeechobee adapted from reference and modified in Adobe Illustrator (39). Inset created using MapMaker by National Geographic (40) and modified in Adobe Illustrator (39).
Fig 2
Fig 2
Microbial community dynamics and environmental conditions in Lake O. (a) Non-metric multidimensional scaling (NMDS) analysis (2D stress: 0.17) depicting ecological zones as biogeographical patterns in microbial composition using Bray–Curtis similarities after square root transformation of relative abundances of ASVs from all samples collected from March 2019 to February 2020 from Lake O. Biological environmental stepwise (BEST) (41) analysis was used to determine the environmental variables that significantly correlated (Pearson R2 = 0.511, P = 0.001) to the patterns in microbial composition between samples. (b) NMDS (2D stress: 0.16) analysis depicting ecological zones as biogeographical patterns in functional composition from April 2019 to September 2019. Bray–Curtis similarities were generated for this analysis after square root transformation of copies per million (CPM) bioprocesses defined by Gene Ontology (GO) (43). BEST (41) analysis was used to determine the environmental variables that significantly correlated. (c) A comparison of the physical and chemical factors that corresponded to sample collection for microbial community analyses that differed between ecological zones. Black line represents the average. Pairwise comparisons were performed using the Kruskal–Wallis test and corrected for multiple comparisons using Dunn’s test (*P ≤ 0.05, **P ≤ 0.01, ***P ≤ 0.001, and ****P ≤ 0.0001). (d) Chlorophyll a concentration over time in ecological zones. Black line represents the average. Pairwise comparisons of ecological zones were performed using the Kruskal–Wallis test and corrected for multiple comparisons using Dunn’s test (****P ≤ 0.0001). TP = total phosphorus, TN = total nitrogen, SD = Secchi depth.
Fig 3
Fig 3
Microbial community composition and functional potential in Lake O. (a) The relative abundance of the top 10 phyla averaged for each month from March 2019 to February 2020 in each ecological zone. The remaining phyla in lower abundances are not shown. (b) The topmost abundant functional pathways shown as the log-transformed CPM of bioprocesses defined by Gene Ontology (43) across ecological zones.
Fig 4
Fig 4
Microbial community composition and functional potential associated with blooms. (a) The families identified in the 16S rRNA data collected from March 2019 to February 2020 that significantly correlated (Pearson R2 > 0.3 or <−0.3, P value <0.05) to chl-a concentration. (b) Pathways identified in metagenomes generated from samples collected from April 2019 to September 2019 classified by Gene Ontology bioprocesses that positively correlated with chl-a concentrations (Pearson R2, P < 0.05); a CPM of >3 in all samples; encoded processes for nutrient utilization, phage defense, and stress response; and supported microbial interactions.
Fig 5
Fig 5
Spatiotemporal trends in the relative abundances of cyanobacteria from samples capturing cyanobacterial bloom season (April–September 2019). MAGs are ordered based on phylogenetic placement using maximum likelihood phylogeny. Taxonomic classification associated with each MAG was determined from GTDB-Tk (46), and different colored circles represent different families of cyanobacteria. Chlorophyll a and cyanobacterial cell concentrations (cells/mL) for each sample are shown in the bottom panel. Any value below the green lines represents little to no bloom conditions. Any value above the green lines indicates the threshold for moderate blooms, and the red line and above indicate the threshold for severe bloom conditions (44).
Fig 6
Fig 6
The functional potential of the cyanobacterial community in Lake O. The proportion of protein coding genes in functional pathways relative to the total number of protein coding genes in each cyanobacterial MAG. MAGs are ordered based on phylogenetic placement using maximum likelihood phylogeny, and the colors represent the family to which they belong.
Fig 7
Fig 7
Phage defense systems and phage–cyanobacterial dynamics in Lake O. (a) The distribution and number of phage defense systems in the cyanobacteria of Lake O. (b) Co-occurrence networks based on correlative relationships between cyanophage and cyanobacteria using relative abundances of each genome. Red and blue edges connecting nodes represent positive (Pearson R2 > 0.3) and negative (Pearson R2 < −0.3) correlations, respectively. The nodes connected by thicker lines represent the MCL clusters determined. Photosynthesis genes found in a specific cyanophage are indicated: psbA encodes a core protein in photosystem II; hli = high-light inducible genes.

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