41 research outputs found

    Two Strains of Crocosphaera watsonii with Highly Conserved Genomes are Distinguished by Strain-Specific Features

    Get PDF
    Unicellular nitrogen-fixing cyanobacteria are important components of marine phytoplankton. Although non-nitrogen-fixing marine phytoplankton generally exhibit high gene sequence and genomic diversity, gene sequences of natural populations and isolated strains of Crocosphaera watsonii, one of the two most abundant open ocean unicellular cyanobacteria groups, have been shown to be 98–100% identical. The low sequence diversity in Crocosphaera is a dramatic contrast to sympatric species of Prochlorococcus and Synechococcus, and raises the question of how genome differences can explain observed phenotypic diversity among Crocosphaera strains. Here we show, through whole genome comparisons of two phenotypically different strains, that there are strain-specific sequences in each genome, and numerous genome rearrangements, despite exceptionally low sequence diversity in shared genomic regions. Some of the strain-specific sequences encode functions that explain observed phenotypic differences, such as exopolysaccharide biosynthesis. The pattern of strain-specific sequences distributed throughout the genomes, along with rearrangements in shared sequences is evidence of significant genetic mobility that may be attributed to the hundreds of transposase genes found in both strains. Furthermore, such genetic mobility appears to be the main mechanism of strain divergence in Crocosphaera which do not accumulate DNA microheterogeneity over the vast majority of their genomes. The strain-specific sequences found in this study provide tools for future physiological studies, as well as genetic markers to help determine the relative abundance of phenotypes in natural populations

    Seasonal Expression of the Picocyanobacterial Phosphonate Transporter Gene phnD in the Sargasso Sea

    Get PDF
    In phosphorus-limited marine environments, picocyanobacteria (Synechococcus and Prochlorococcus spp.) can hydrolyze naturally occurring phosphonates as a P source. Utilization of 2-aminoethylphosphonate (2-AEP) is dependent on expression of the phn genes, encoding functions required for uptake, and C–P bond cleavage. Prior work has indicated that expression of picocyanobacterial phnD, encoding the phosphonate binding protein of the phosphonate ABC transporter, is a proxy for the assimilation of phosphonates in natural assemblages of Synechococcus spp. and Prochlorococcus spp (Ilikchyan et al., 2009). In this study, we expand this work to assess seasonal phnD expression in the Sargasso Sea. By RT-PCR, our data confirm that phnD expression is constitutive for the Prochlorococcus spp. detected, but in Synechococcus spp. phnD transcription follows patterns of phosphorus availability in the mixed layer. Specifically, our data suggest that phnD is repressed in the spring when P is bioavailable following deep winter mixing. In the fall, phnD expression follows a depth-dependent pattern reflecting depleted P at the surface following summertime drawdown, and elevated P at depth

    Calculation of Splicing Potential from the Alternative Splicing Mutation Database

    Get PDF
    © 2008 Bechtel et al; licensee BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution Licens

    Phosphonates Utilization in Marine and Freshwater Picocyanobacteria

    No full text
    A PCR-based assay is described, designed to detect expression of the phosphonate assimilation gene phnD from picocyanobacteria. The phnD gene encodes the phosphonate binding protein of the ABC-type phosphonate transporter, present in many of the picocyanobacterial genome sequences. Detection of phnD expression can indicate a capacity of picoplankton to utilize phosphonates, a refractory form of phosphorus that can represent 25% of the high molecular weight dissolved organic phosphorus pool in marine systems. Primer sets were designed to specifically amplify phnD sequences from marine and freshwater Synechococcus spp., Prochlorococcus spp. and environmental samples from the ocean and Laurentian Great Lakes. Marine strain Synechococcus WH8102 and some freshwater Synechococcus strains are able to grow on phosphonates as a sole P source; particularly, freshwater Synechococcus ARC-21 is able to utilize synthetic phosphonate herbicide (glyphosate). Quantitative RT-PCR from cultured marine Synechococcus sp. strain WH8102 and freshwater Synechococcus sp. ARC-21 demonstrated induction of phnD expression in P-deficient media, suggesting that phn genes are regulated coordinately with genes under phoRB control. However, pho box was not found in the putative promoters of phosphonate utilization genes in picocyanobacteria. Last, RT-PCR of environmental RNA samples from the Sargasso Sea, Pacific Ocean, and the Baltic Sea detected phnD expression from the endemic picocyanobacterial population. Synechococcus spp. phnD expression yielded a depth-dependent pattern following gradients of P bioavailability, and addition of phosphate to natural sample resulted in deactivation of Synechococcus phnD expression. By contrast, the Prochlorococcus spp. primers revealed that in all samples tested, phnD expression was constitutive. In overall, this study demonstrated the significance of phosphonates as a phosphorus source in the DOP pool for picocyanobacteria in P-depleted environments. The method described herein will allow future studies aimed at understanding the utilization of naturally-occurring phosphonates in the ocean as well as monitoring the acquisition of synthetic phosphonate herbicides (e.g. glyphosate) by picocyanobacteria in fresh waters

    Phosphonates Utilization in Marine and Freshwater Picocyanobacteria

    No full text
    A PCR-based assay is described, designed to detect expression of the phosphonate assimilation gene phnD from picocyanobacteria. The phnD gene encodes the phosphonate binding protein of the ABC-type phosphonate transporter, present in many of the picocyanobacterial genome sequences. Detection of phnD expression can indicate a capacity of picoplankton to utilize phosphonates, a refractory form of phosphorus that can represent 25% of the high molecular weight dissolved organic phosphorus pool in marine systems. Primer sets were designed to specifically amplify phnD sequences from marine and freshwater Synechococcus spp., Prochlorococcus spp. and environmental samples from the ocean and Laurentian Great Lakes. Marine strain Synechococcus WH8102 and some freshwater Synechococcus strains are able to grow on phosphonates as a sole P source; particularly, freshwater Synechococcus ARC-21 is able to utilize synthetic phosphonate herbicide (glyphosate). Quantitative RT-PCR from cultured marine Synechococcus sp. strain WH8102 and freshwater Synechococcus sp. ARC-21 demonstrated induction of phnD expression in P-deficient media, suggesting that phn genes are regulated coordinately with genes under phoRB control. However, pho box was not found in the putative promoters of phosphonate utilization genes in picocyanobacteria. Last, RT-PCR of environmental RNA samples from the Sargasso Sea, Pacific Ocean, and the Baltic Sea detected phnD expression from the endemic picocyanobacterial population. Synechococcus spp. phnD expression yielded a depth-dependent pattern following gradients of P bioavailability, and addition of phosphate to natural sample resulted in deactivation of Synechococcus phnD expression. By contrast, the Prochlorococcus spp. primers revealed that in all samples tested, phnD expression was constitutive. In overall, this study demonstrated the significance of phosphonates as a phosphorus source in the DOP pool for picocyanobacteria in P-depleted environments. The method described herein will allow future studies aimed at understanding the utilization of naturally-occurring phosphonates in the ocean as well as monitoring the acquisition of synthetic phosphonate herbicides (e.g. glyphosate) by picocyanobacteria in fresh waters
    corecore