Original Research ARTICLE
De novo assembly of Aureococcus anophagefferens transcriptomes reveals diverse responses to the low nutrient and low light conditions present during blooms
- 1Department of Earth and Environmental Sciences and the Lamont-Doherty Earth Observatory, Columbia University, Palisades, NY, USA
- 2School of Marine and Atmospheric Sciences, Stony Brook University, Southampton, NY, USA
Transcriptome profiling was performed on the harmful algal bloom-forming pelagophyte Aureococcus anophagefferens strain CCMP 1850 to assess responses to common stressors for dense phytoplankton blooms: low inorganic nitrogen concentrations, low inorganic phosphorus concentrations, low light levels, and a replete control. The de novo assemblies of pooled reads from all treatments reconstructed ~54,000 transcripts using Trinity, and ~31,000 transcripts using ABySS. Comparison to the strain CCMP 1984 genome showed that the majority of the gene models were present in both de novo assemblies and that roughly 95% of contigs from both assemblies mapped to the genome, with Trinity capturing slightly more genome content. Sequence reads were mapped back to the de novo assemblies as well as the gene models and differential expression was analyzed using a Bayesian approach called Analysis of Sequence Counts (ASC). On average, 93% of significantly upregulated transcripts recovered by genome mapping were present in the significantly upregulated pool from both de novo assembly methods. Transcripts related to the transport and metabolism of nitrogen were upregulated in the low nitrogen treatment, transcripts encoding enzymes that hydrolyze organic phosphorus or relieve arsenic toxicity were upregulated in the low phosphorus treatment, and transcripts for enzymes that catabolize organic compounds, restructure lipid membranes, or are involved in sulfolipid biosynthesis were upregulated in the low light treatment. A comparison of this transcriptome to the nutrient regulated transcriptional response of CCMP 1984 identified conserved responses between these two strains. These analyses reveal the transcriptional underpinnings of physiological shifts that could contribute to the ecological success of this species in situ: organic matter processing, metal detoxification, lipid restructuring, and photosynthetic apparatus turnover.
In 1985 coastal embayments around Long Island, New York were disrupted by dense phytoplankton blooms that colored the water a murky brown (Gobler et al., 2005; Gobler and Sunda, 2012). Researchers identified the causative organism of these “brown tide” blooms as the pelagophyte phytoplankton Aureococcus anophagefferens. In the years since the first A. anophagefferens bloom, these brown tides have recurred annually and now extend down the eastern seaboard as far as Virginia (Kana et al., 2004; Gobler et al., 2005; Boneillo and Mulholland, 2013). In recent years, blooms of A. anophagefferens have also been detected off the coast of South Africa (Gobler et al., 2005) and in China (Zhang et al., 2012). Brown tides do not pose a direct threat to human health, however they do have damaging ecosystem effects. Brown tides have also been linked to the collapse of fisheries due to A. anophagefferens' toxicity to shellfish and the elevated cell densities during blooms can attenuate light and destroy seagrass beds (Gobler et al., 2005).
Brown tides occur in waters in which the concentration of organic carbon and organic nitrogen are high relative to inorganic nutrients and heightened cell densities attenuate light in the water column (Anderson et al., 2002; Sunda et al., 2006; Heisler et al., 2008; Gobler et al., 2011). These observations have been corroborated with laboratory studies that show A. anophagefferens can grow using organic compounds as a sole nutrient source (Berg et al., 2008; Wurch et al., 2011b) and can survive prolonged periods in the dark (Popels and Hutchins, 2002). Sequencing and analysis of the CCMP 1984 genome revealed the presence of a number of genes that were hypothesized to contribute to A. anophagefferens success in bloom conditions. For example, relative to other co-occurring phytoplankton, the A. anophagefferens genome contains more light harvesting complex proteins as well as numerous genes implicated in the import and breakdown of diverse organic compounds including dissolved organic nitrogen (DON) and dissolved organic phosphorus (DOP) (Gobler et al., 2011). Low resolution (Serial Analysis of Gene Expression) transcriptional studies and targeted approaches focused on nitrogen suggest that A. anophagefferens strain CCMP 1984 upregulates genes related to the utilization of a diverse array of DON and DOP sources in low inorganic nutrient concentrations (Berg et al., 2008; Wurch et al., 2011b). Despite these advances, the physiological mechanisms that facilitate growth in the low nitrogen (N), low phosphorus (P), and low light conditions found during blooms are still poorly understood. Further, it remains unclear if these capabilities are shared across strains or if they contribute to strain-level niche differentiation in the environment. Strain differentiation is of particular interest in A. anophagefferens as some strains are acutely toxic to bivalves and copepods, while others are not (Harke et al., 2011).
High throughput transcriptome sequencing can be used to reveal the system-wide response of an organism to experimentally controlled perturbations, with or without a genome (Grabherr et al., 2011). Here, the transcripts from cultures of the toxic A. anophagefferens strain, CCMP 1850, grown under low N, low P, low light, and replete nutrient and light levels were sequenced as part of the Marine Microbial Eukaryote Transcriptome Sequencing Project (MMETSP) (Keeling et al., 2014). Although it is common to map reads to a genome for expression analysis, this can arguably obscure strain heterogeneity. Additionally, the majority of eukaryotic phytoplankton, including the hundreds of genera analyzed through the MMETSP, do not have sequenced genomes. Herein sequenced reads were examined with three different methods: two de novo sequence assembly pipelines using the Trinity program and the ABySS program, and one pipeline in which reads were examined by mapping directly to the A. anophagefferens CCMP 1984 gene models. In each of the three methods, transcriptomes were also analyzed for significant differential expression between treatments and control using a stringent empirical Bayes method called Analysis of Sequence Counts (ASC) (Wu et al., 2010). ASC is optimized for use without sequenced replicates and has been shown to perform similarly, but conservatively, when compared to other differential expression analyses using a sample dataset with and without sequenced replicates (Wu et al., 2010).
Materials and Methods
Experiments were performed with A. anophagefferens strain CCMP 1850 (isolated from Great South Bay, Long Island, New York, USA, May, 1998) maintained on modified GSe medium (60 μM NH4, 5 μM PO4) (Doblin et al., 1999) made from 0.2 μm filtered seawater collected from the coastal Atlantic Ocean (final salinity 32). The culture used was not axenic, but was uni-algal and uni-eukaryotic. As a precautionary measure, an antibiotic and antimycotic solution (final concentrations = 100 IU mL−1 penicillin, 100 μg mL−1 streptomycin, and 0.25 μg mL−1 amphotericin B; Mediatech, Inc.) was added to the culture medium immediately before inoculation of cells at a 0.5% concentration (final volume). Experiments were conducted at 21°C on a 14:10 light:dark cycle illuminated by a bank of fluorescent lights at an intensity of 100 μE m−2 s−1, unless otherwise noted.
Culture conditions included low P (1 μM PO4), low N (30 μM NH4), low light (20 μE m−2 s−1), and a culture with replete amounts of N, P, (60 μM NH4, 5 μM PO4) and light (100 μE m−2 s−1) to serve as a control. Triplicate cultures were inoculated with 3.5 × 105 cells mL−1 and monitored for cell densities, in vivo chlorophyll a fluorescence, photosynthetic efficiency (Fv/Fm), alkaline phosphatase activity (APA), and dissolved nutrient concentrations. Measurements were made at the same time each day to avoid diel changes in gene expression and cell physiology. The control was harvested during exponential phase growth and the treatments were harvested at the onset of stationary phase to assure limitation by either light, N or P. This approach allows for the identification of N, P, and light effects independently, but common stress responses across all treatments cannot be distinguished from growth rate effects. A similar sampling scheme has been used for previous gene expression studies (e.g., Dyhrman et al., 2006; Wurch et al., 2011b; Dyhrman et al., 2012; Bender et al., 2014).
Lugol's iodine preserved cells were enumerated using a Beckman Coulter Multisizer™ 3 Coulter Counter® with a 50 μm aperture (Harke et al., 2011). Nutrient samples were filtered through 0.2 μm polycarbonate filters, and stored frozen. Nitrate was analyzed by reducing the nitrate to nitrite using spongy cadmium as per Jones (1984). Ammonium and phosphate were analyzed using techniques modified from Parsons and colleagues (1984). These nutrient analyses provided 100 ± 10% recovery of standard reference material (SPEX CertiPrep™) for nitrate, ammonium, and phosphate. Bulk APA was measured for each replicate experimental sample on a Turner Designs TD-700 fluorometer (EM filter of 410–600 nm and EX filter of 300–400 nm) using 4-Methylumbelliferone phosphate (250 μ M concentration) as the substrate (Hoppe, 1983). Maximum quantum efficiency of photosystem II (PSII) was estimated from in vivo (Fv) and DCMU (3,4-dichlorophenyl-1,1-dimethylurea)-enhanced in vivo fluorescence (Fm) of each replicate experimental sample on a Turner Designs TD-700 fluorometer (EM filter of >665 nm and EX filter of 340–500 nm). All readings were blank corrected using GSe media. DCMU blocks electron transfer between PSII and PSI and yields maximal fluorescence.
At the time of harvest, aliquots of each replicate in each treatment were centrifuged for 10 minutes at 1300 × g at 21°C. The supernatant was decanted and resulting cell pellet was resuspended with 1 mL of remaining media and placed into a 2 mL microcentrifuge tube. The concentrated sample was centrifuged again for 10 min at 1300 × g at 21°C and immediately flash frozen in liquid nitrogen and stored at −80°C. The entire harvest process took <30 min per experimental flask, and was similar to other studies with Aureococcus (Wurch et al., 2011a,b, 2014). Total RNA was extracted with a MO BIO UltraClean™ Plant RNA Isolation Kit according to the manufacturer's instructions. A second DNase step was conducted to remove any residual genomic DNA remaining on the spin filters using an Ambion Turbo DNA-free™ kit according to the manufacturer's instructions. Cell pellets for each replicate were extracted individually through separate columns and pooled. Sequencing of biological replicates was not available through the MMETSP; in order to account for biological variability in transcriptional response, extracts from triplicate cultures of each treatment and the control were pooled prior to sequencing at the National Center for Genome Resources (NCGR, Santa Fe, NM).
RNA Library Preparation and Sequencing
Samples were quantified using Invitrogen Qubit Q32855 and RNA quality was assessed using the Agilent 2100 Bioanalyzer. The Illumina TruSeq RNA Sample Preparation Kit was used to generate libraries using ~2 μg of RNA. Sequencing of 50 base pair paired-end reads from each library was performed on an Illumina HiSeq 2000 at the NCGR. Over 2 Gbp of sequence was generated per library. Sequence data is available on the Community Cyberinfrastructure for Advanced Microbial Ecology Research and Analysis (CAMERA) server (http://camera.calit2.net/) with the identification numbers MMETSP0914, MMETSP0915, MMETSP0916, and MMETSP0917.
Assembly and Annotation
Reads were analyzed with three different approaches: mapping reads to the A. anophagefferens CCMP 1984 gene models, and two de novo assembly pipelines, one utilizing the Trinity de novo assembly suite (Grabherr et al., 2011) and the other performed by the NCGR as part of the MMETSP (Keeling et al., 2014) utilizing the ABySS assembler (Birol et al., 2009).
For the ABySS method, the assembly and quantifications provided by NCGR were carried out as follows. Sequences were trimmed using SGA Preprocess at Q15 with the swinging average setting (Simpson and Durbin, 2012). Following trimming, reads shorter than 25 nucleotides were discarded, all treatments were merged and then assembled using ABySS and 20 runs with k-mer sizes ranging from k = 26 to k = 50 (Simpson et al., 2009). Contigs from all runs were merged and then clustered at 98% sequence identity using CD-Hit (Li and Godzik, 2006). Clustered contigs were then assembled into longer sequences using CAP3 (Huang, 1999) and the paired-end scaffolding feature of ABySS (Simpson et al., 2009). GapCloser from the SOAP de novo assembly software was used to close gaps created during scaffolding (Li et al., 2008). Finally, scaffolds were clustered with CD-Hit a second time at 98% identity and sequences less than 150 base pairs were removed (Li and Godzik, 2006).
Prior to commencing the Trinity method, raw reads were trimmed using Trimmomatic with paired-end parameters, sliding window of 6 through 20, and a minimum accepted length of 25 base pairs (Lohse et al., 2012), then reads from all 4 treatments were merged and assembled using the paired end settings of the Trinity software package (Grabherr et al., 2011). Geneious was used to predict open reading frames (ORFs) greater than 100 base pairs with the options to exclude interior sequences and potential outside start/stop codons (www.geneious.com). Clustering of the Trinity assembly was performed using the CD-Hit program (Fu et al., 2012). The resulting sequences were filtered to remove contigs less than 200 base pairs in length.
Transcripts identified by mapping (see below) to the genome were annotated by retrieving annotations from the CCMP 1984 genome (Gobler et al., 2011). Coding sequences in the ABySS assembly were identified using ESTScan (Iseli et al., 1999; Lottaz et al., 2003). Hits against the UniProtKB and Swiss-Prot databases were determined using BLASTp (Altschul et al., 1990). Identified coding sequences were further characterized with Pfam-A, TIGRFAM, and SUPERFAMILY databases using HMMER3 (Haft et al., 2001; Gough et al., 2001; Zhang and Wood, 2003; Bateman, 2004). Trinity assembly contigs were then annotated by aligning against the ABySS assembly contigs; all contigs generated from the Trinity pipeline were additionally compared against the non-redundant protein database on NCBI using BLASTx from the BLAST+ software with an e-value cutoff of 1 × 10−5 (Camacho et al., 2009). Trinity method contigs were further annotated by identifying biochemical pathways using the Kyoto Encyclopedia of Genes and Genomes database using the partial genome single-directional best hit method (Kanehisa, 2006). The annotations of the transcripts presented herein are putative, as the functions of these transcripts have not been experimentally verified in A. anophagefferens CCMP 1850.
In the de novo pipelines, counts for each contig quantified by first using Bowtie 2 run with the “–sensitive” parameters in “–end-to-end” mode in order to align trimmed reads to the final contigs produced by the ABySS or Trinity assemblies. These Bowtie 2 settings were chosen because previous studies have shown that increasing the sensitivity does not yield a dramatic increase in the percentage of reads aligned but does greatly increase computation time (Langmead and Salzberg, 2012) and because Bowtie 2 alignments have been shown to be less sensitive to altered parameters than similar alignment programs (Lindner and Friedel, 2012). The HTSeq Count program was then used to obtain counts (www.huber.embl.de/users/anders/HTSeq/).
For the genome mapping method, TopHat with parameters of 15 threads and an expected inner distance between mate pairs of 100 bp (Roberts et al., 2012) was used to map raw reads from each treatment and the control to the CCMP 1984 genome (genome.jgi.doe.gov/Auran1/Auran1.home.html, Gobler et al., 2011) with 2 mismatches allowed. Following genome mapping, transcript abundance was quantified using HTSeq Count. The de novo assemblies from Trinity and ABySS were compared against one another and the CCMP 1984 gene models and the full genome scaffolds by performing reciprocal BLASTn searches with e-value cutoffs of 1 × 10−5 (Camacho et al., 2009).
For all three pipelines, significant differential expression patterns in the low N, low P, and low light treatments vs. the replete condition control were assigned using a method called ASC (Wu et al., 2010). ASC is an empirical Bayes method that estimates the prior distribution by modeling biological variability using the data itself, rather than imposing a negative binomial distribution. ASC has been shown to perform similarly, but conservatively, relative to other differential expression analyses implemented on data sets with and without replicates (Wu et al., 2010). ASC has been successfully utilized in a number of studies for which sequenced replicates were not available (Alexander et al., 2012; Dyhrman et al., 2012; Thomas et al., 2012; Konotchick et al., 2013). In each condition relative to the control, genes upregulated or downregulated with a fold change greater than or equal to 2 and a posterior probability greater than 0.95 were deemed significantly differentially regulated, which are parameters used in previous studies of this type (Dyhrman et al., 2012).
In the low N treatment, several of the expected A. anophagefferens transcriptional responses identified in previous studies (Berg et al., 2008; Wurch et al., 2011b) were not found among the significant transcripts. We compiled a list of significantly upregulated, biologically important low N response genes previously identified in A. anophagefferens CCMP 1984 (Berg et al., 2008; Wurch et al., 2011b), as well as other phytoplankton including diatoms (Allen et al., 2011; Bender et al., 2014) and the coccolithophore Emiliania huxleyi (Dyhrman et al., 2006). This list included ammonium, amino acids, nitrite, and urea transporters, a xanthine/uracil/vitamin C permease, and the enzymes formamidase, urease, nitrate reductase, and arginase. All transcripts with these functional annotations were selected from within the assembled CCMP 1850 transcriptome and expression patterns across all treatments were examined by plotting the average variance from the normalized count (reads or tags per million; TPM). This expression pattern was compared against the mean variance in TPM from all ASC-identified significantly upregulated low N transcripts in each treatment.
Differential Growth Among Treatments
The replete cultures were harvested during the exponential phase of growth on day 9 (Figure 1). The low nutrient cultures were harvested in early stationary phase; this corresponded to day 9 in low N and day 12 in low P. The cultures grown in low light maintained a steady low growth rate and were harvested on day 9 (Figure 1). At the time of harvest, control cultures were growing at significantly higher rates (0.49 d−1) than those of the treatments, which ranged from 0.01 to 0.09 d−1 (p < 0.001). The longer lag time in replete and low P cultures relative to low N is likely due to the initial excess of ammonium hindering growth, which has been seen in similar studies (Wurch et al., 2014). In the low N and low P cultures, the reduced growth rates were consistent with reduced concentrations of N or P, respectively (Table 1). Inorganic phosphate concentrations in the low P treatment at the time of harvest were 1.34 ± 0.23 μM and were significantly lower than the other treatments (>3 μM; p < 0.001). Nitrate levels were below the detection limit in the low N treatment but were >9 μM in the replete, low P and low light treatments. Ammonium levels in the low N treatment were also significantly lower (1.76 ± 0.28 μM) than the other three treatments (13–38 μM; p < 0.001). Photosynthetic efficiency of photosystem II (Fv/Fm) at the time of harvest was significantly higher in the control (0.58 ± 0.02; p < 0.05) than all other treatments (Table 1). The APA was measured during stationary phase and just prior to harvesting (days 10 and 11) in the low P cultures, and on days 6 and 7 during exponential phase in the replete condition cultures (Figure 1). The average activity in the triplicate cultures over the 2 days prior to harvesting was 4.0 nmol P L−1 h−1 in the low P treatment and 2.1 nmol P L−1 h−1 in the replete cultures.
Figure 1. Cell growth in each treatment. Error bars represent standard deviation of triplicate cultures. Arrows indicate time of harvest.
Table 1. Nutrient concentrations in the culture media and cellular photosynthetic efficiency (Fv/Fm) at the time of harvest.
RNA Sequencing and de novo Assembly
Illumina sequencing of the replete sample library yielded 22,291,148 paired reads, low N yielded 23,413,795 paired reads, low P yielded 27,635,028 paired reads, and low light yielded 22,259,313 paired reads. After trimming, the replete library had 21,013,910 paired reads, low N had 20,712,739 paired reads, low P had 25,555,090 paired reads, and low light had 20,840,187 paired reads. Greater than 90% of trimmed reads mapped to the CCMP 1984 genome or de novo assemblies in all cases (Table 2). The Trinity assembly yielded 53,886 contigs (N50 = 2148) while the ABySS assembly yielded 31,473 (N50 = 1393) (Table 3). In the Trinity and ABySS assemblies, 85 and 74% of contigs respectively contained ORFs greater than 100 base pairs. Each de novo assembly was assessed by comparing the assemblies against one another and against the CCMP 1984 gene models and genome (Gobler et al., 2011). Roughly 98.2% (30,933 out of 31,473) of the ABySS contigs were present in the Trinity assembly, while 85.5% of the Trinity contigs (46,055 out of 53,866) were present in the ABySS assembly (Table 3). BLAST alignments of the de novo assemblies against the CCMP 1984 gene models resulted in 8221 out of 11,501 gene models recovered by the Trinity assembly and 7543 out of 11,501 gene models recovered by the ABySS assembly (Table 3). There were 7275 shared gene models between the de novo assemblies, with 946 gene models represented solely in the Trinity assembly, and 267 gene models represented solely in the ABySS assembly. However, over 95% of both Trinity and ABySS contigs aligned successfully to the full A. anophagefferens CCMP 1984 genome scaffolds. This is a metric that has previously been used to assess the efficacy and relative performance of de novo assembly pipelines (Grabherr et al., 2011). The high percentage of contigs aligned to the genome scaffolds relative to gene models recovered is likely due to the presence of multiple isoforms, as multiple isoforms were observed aligning to each gene model. Additionally, the difference could in part be affected by genes missed during modeling as was case with the VTC4 polyphosphate polymerase, discussed below.
Table 2. The percentage of trimmed reads that mapped to the CCMP 1984 gene models and the two CCMP 1850 de novo assemblies.
Table 3. Trinity and ABySS de novo assembly statistics and comparisons between the CCMP 1984 gene model sequences and the assembled contigs from CCMP 1850.
Clustering the Trinity assembly at 98, 95, and 90% sequence identity reduced the number of contigs to 49,047, 42,508, and 37,314, respectively. Clustering the Trinity assembly at 90% sequence identity did not appreciably decrease the percentage of successfully mapped sequences when compared with the ABySS-generated transcripts: 98% or 30,858 out 31,473 ABySS transcripts mapped to the 37,314 Trinity 90% clusters. The number of gene models represented in the Trinity 90% clusters was also similar to the unclustered Trinity assembly: 8149 out of 11,501 models. Roughly 52% of the total contigs in the clustered Trinity assembly remained unannotated after the annotation steps. Clustering at 90% created a more manageable dataset; this technique has been implemented in past studies as a way to remove redundant sequences (Suzek et al., 2007) and to remove biases caused by abundant sequences (Holm and Sander, 1998).
Identifying Differentially Expressed Transcripts
ASC was used to determine significant differential expression in the treatments relative to the replete condition control using the 90% clustered Trinity assembly (Wu et al., 2010). The low P condition elicited the strongest overall response, with more transcripts (1205) significantly upregulated than the other treatments and the largest fold changes (Figure 2; Table 4). The transcriptomic response to low N was the weakest overall, relative to the other treatments (Figure 2; Table 4). The Trinity and ABySS methods yielded similar numbers of differentially upregulated transcripts (Table 4). Although the genome mapping method recovered fewer significantly differentially regulated transcripts, this disparity is due to the difference in the number of gene models (11,501) vs. the number of contigs generated by the two de novo assemblies (>30,000). The percentage of differentially expressed transcripts relative to the total were comparable across all methods, with ~2.5% of all gene models or contigs significantly upregulated.
Figure 2. Pairwise comparison of transcriptional responses across 37,314 contigs generated by a 90% clustering of the Trinity assembly in each treatment relative to the replete control. Transcriptome-side gene expression patterns are shown in low N (A), low P (B), and low light (C). Transcripts were normalized to total library size in tags per million (TPM). Gray points represent transcripts that were not significantly differentially regulated. Significance (colored points) was determined with ASC using a fold change greater than or equal to 2 and a posterior probability greater than 0.95 (Wu et al., 2010). The average significant fold change and maximum fold change value of up and downregulated transcripts is noted.
Table 4. Significantly differentially upregulated transcripts from the mapping and assembly pipelines.
A careful examination of transcripts significantly upregulated under each condition was performed to identify biochemical pathways utilized by A. anophagefferens during the low N, P, and light conditions that prevail during brown tides. Significantly downregulated transcripts were not focused on as these largely represented genes indicative of the stationary phase of growth; as such, they were generally less informative of specific responses to the low nutrient or low light conditions tested. In all treatments, the Trinity and ABySS assemblies captured an average of 93% of the ASC-identified significantly differentially regulated gene models as determined by the genome mapping method (Table 4). Between 76 and 89% of significant Trinity contigs were homologous to ABySS contigs (Table 4). Furthermore, the functional annotations of the vast majority of significantly differentially expressed transcripts discussed in detail herein are present in the ASC significant sets across both de novo methods and the genome mapping method. The single exception to this is the transcript encoding the VTC4 polyphosphate polymerase. This contig aligns to the full A. anophagefferens genome but is not present in the published gene models, therefore this transcript was not detected by the genome mapping method. Overall, these results indicate that the biological interpretation presented here would be similar regardless of the assembly or mapping method utilized in downstream analyses. Additionally, these results show that de novo assemblies can enable the detection of important genes that are not included in the modeled gene set, as was the case for the VTC4 polyphosphate polymerase. In order to highlight the efficacy of de novo assembly methods in light of the constraints of the MMETSP, namely that the majority of datasets are generated from organisms without sequenced genomes, downstream analyses were performed on differential expression results from the Trinity de novo assembly, clustered at 90% sequence identity.
Treatment Specific Responses
The A. anophagefferens CCMP 1850 response to low N conditions was characterized by significantly upregulated transcripts encoding nitrate transporters, nitrate reductases and peptidases (Table 5). In addition to the transcripts that passed the stringent ASC significance cutoff, modeling of expression of N metabolism genes known to respond significantly to N limitation in A. anophagefferens CCMP 1984 (Berg et al., 2008; Wurch et al., 2011b) or other phytoplankton (Dyhrman et al., 2006; Allen et al., 2011; Bender et al., 2014) revealed that these transcripts mirror expression patterns in the significantly upregulated N-responsive set, with higher expression in the low N treatment relative to replete, low P and low light (Table 5; Figure 3).
Figure 3. Expression patterns of key nitrogen metabolism transcripts. The black hashed line denotes the mean variance in expression across treatments of transcripts significantly upregulated in the low N treatment. Significance was determined with ASC using a fold change greater than or equal to 2 and a posterior probability greater than 0.95 (Wu et al., 2010). The blue line denotes the average variance in expression of transcripts from this study with functional annotations previously determined to be significantly upregulated during low N conditions in A. anophagefferens CCMP 1984 (Berg et al., 2008; Wurch et al., 2011b) (See Table 5). The green line denotes the variance in expression of transcripts from this study with functional annotations identified as upregulated during low N conditions in diatoms or coccolithophores (Dyhrman et al., 2006, 2012; Allen et al., 2011; Bender et al., 2014) (See Table 5).
The response to the low P treatment featured the significant upregulation of transcripts responsible for phosphate transport and the hydrolysis of DOP including several phosphatases and a 5′-nucleotidase (Figure 4; Table 6), concurrent with an increase in alkaline phosphatase activity. Transcripts for components of a PHO-like (Toh-e et al., 1981) P regulatory signaling cascade were found to be upregulated under low P (Figure 4; Table 6), as was a vacuolar transport chaperone 4 (VTC4) with homology to a eukaryotic polyphosphate polymerase (Hothorn et al., 2009) (Figure 4; Table 6). Transcripts encoding components of an arsenite detoxification pathway including an arsenite transporting ATPase and a glutathione S-transferase were also significantly upregulated (Figure 4; Table 6). An arsenate reductase was identified in the transcriptome, but was not significantly upregulated in the low P treatment relative to the replete control.
Figure 4. Schematic cell model illustrating the potential role of the transcripts highlighted in this study. Localization of the proteins depicted is for clarity and is not meant to represent actual protein localization in the cell. Proteins with black dashed lines represent transcripts that were detected in transcriptomes but were not significantly differentially expressed relative to the control. AAP, Amino acid permease; ACP, Acid phosphatase; ALP, Alkaline phosphatase; AMT, Ammonia transporter; APR, Adenosine-5′-phosphosulfate reductase, ARG, arginase; ArsA, Arsenite trasnlocating ATPase; ArsB, Arsenite efflux protein; ArsC, Arsenate reductase; DUR, Urea transporter; FDS, Formamidase; FGS, Ferredoxin-dependent glutamate synthase; GPX, Glutathione peroxidase; GST, Glutathione S Transferase; HIP, Histidine phosphatase; LHC, Light harvesting complex; LPL, Lysophospholipase; NAR, Nitrite transporter; NIA, Nitrate reductase; NII, Nitrite reductase; NRT, Nitrate transporter; NTD, 5′-Nucleotidase; P4-85, PHO pathway; PEP, Peptidase; PEPyr, Phosphoenolpyruvate; PPL, Patatin-like phospholipase; PTA, Phosphate transporter; SQD, SQD1 (sulfolipid biosynthesis gene); STP, Serine/threonine phosphatase; SUP, Sulfate permease; SUR, Sulfate reductase; UDPG, UDP-glucose; URE, Urease; VTC, Vacuolar transport chaperone (VTC4); XUV, Xanthine/uracil/Vitamin C permease.
In A. anophagefferens, low light conditions resulted in the upregulation of genes involved in a variety of lipid modification and recycling reactions. Light stress uniquely resulted in the significant upregulation of transcripts encoding two different phospholipase-like enzymes: several identified as lysophospholipases and the other a patatin-like phospholipase (Figure 4; Table 7). A set of transcripts involved in the structure and activity of peroxisomes, including peroxidases/catalases, glutathione peroxidase, and an integral membrane protein of peroxisomes (MPV17) were also significantly upregulated in the low light treatment (Figure 4; Table 7). Finally, transcripts from the pathway for sulfolipid biosynthesis were detected in the low light treatment. A transcript encoding the sulfolipid biosynthesis protein SQD1 was significantly upregulated (Figure 4; Table 7). An accessory protein to the sulfolipid biosynthesis process, ferredoxin-dependent glutamate synthase (FdGOGAT) and a sulfate transporter were also detected in the low light transcriptome, but were not significantly upregulated relative to the replete treatment. A complete list of the patterns of abundance and differential expression statistics generated by ASC for each transcript are provided in the supplemental data (Data Sheet 1).
Patterns in Overlapping Responses
Response patterns are defined by identifying the overlap in significantly differentially regulated transcripts under the low nutrient and low light treatments (Figure 5). The overlap between significant transcripts from low N and low P conditions represents differential expression indicative of nutrient stress. The general response transcripts are defined here as those that are either upregulated or downregulated under all three treatments relative to the control (Figure 5). However, many of these general response transcripts could be jointly upregulated because they are responding to the switch to stationary phase and the cessation of exponential growth, rather than being a shared response to nutrient or light stress.
Figure 5. Broad categories of significant transcriptional responses. Diagrams illustrate the patterns of significantly differentially regulated genes across the treatments. Sections without overlap represent unique responses to each treatment. Overlapping sections are indicative of nutrient stress response transcripts [overlap between low nitrogen (N) and low phosphorus (P)], and shared low light and low N or P responses. The generally responsive category describes significantly up or downregulated transcripts shared across three treatments.
There were relatively very few transcripts upregulated in all three treatments or shared across two treatments, as compared to significantly downregulated transcripts overlapping between treatments (Figure 5). Two of the six shared upregulated transcripts encode for putative WLM domains and the other four transcripts share homology to an ADP-ribosylation factor. The majority of the 2166 shared downregulated transcripts encode protein kinases, DNA polymerase subunits, and proteins involved in signal transduction (such as calmodulin), falling into KEGG pathways like DNA replication, ribosome biogenesis, and purine and pyrimidine metabolism (Figure 6). During nutrient stress (low N and low P), the most numerous categories of KEGG classified downregulated transcripts include metabolic pathways, biosynthesis of secondary metabolites, purine synthesis and cell cycle regulation proteins (Figure 6). The most numerous general response downregulated transcripts in these KEGG categories were involved with signal transduction, protein phosphorylation, and transcripts involved in transcription or translation (Figure 6). The downregulation of the transcripts in these categories could also point to decreases in growth rate that accompany the onset of stationary phase when treatment cultures were harvested.
Figure 6. Percentage of transcripts in the top 20 KEGG annotations for significantly downregulated transcripts in the general response and nutrient stress categories. The only shared KEGG annotation between these two categories was calmodulin.
Transcripts involved with photosynthetic processes were dynamically expressed across all treatments. There were different transcripts identified as encoding photosystem I and II proteins upregulated under all three treatments. In addition to these photosystem-encoding transcripts, a large number of significantly responsive transcripts in all treatments were identified as encoding light harvesting complex (LHC) proteins. CCMP 1984 genome analysis identified 62 LHC proteins, which fell into 16 distinct groups based on phylogenetic similarity to LHCs from other phytoplankton (Gobler et al., 2011). Significantly upregulated LHC contigs spanned 15 of the 16 LHC groups during low P and 10 groups during low light, while significantly downregulated contigs during low N spanned 7 groups (Figure 7). The downregulation of LHC transcripts is supported by the noted decrease in photosynthetic efficiency at the time of culture harvest in the low N sample (Table 1).
Figure 7. Expression patterns of light harvesting complex (LHC) transcripts between treatments. The notation on the x-axis refers to the phylogenetic groups of different LHC genes identified in the A. anophagefferens CCMP 1984 genome (Gobler et al., 2011). Filled circles indicate LHC groups with significantly differentially expressed contigs in the LHC group. Open circles indicate a lack of significant differentially expressed contigs in the LHC group. Error bars denote standard deviation.
Comparison to A. anophagefferens CCMP 1984
In the low N treatment, transcripts for nitrate transporters and peptidase were found to be significantly upregulated in both strains (Berg et al., 2008; Wurch et al., 2011b) (Table 5). Nitrite reductase was not observed to be significantly upregulated in low N in previous work on CCMP 1984, but was significantly upregulated in this study of CCMP 1850 (Table 5). The other significant N-responsive transcripts identified in CCMP 1984 included transporters of urea, ammonia, amino acids, nitrate, and xanthine/uracil/vitamin C, and formamidase (Berg et al., 2008; Wurch et al., 2011b) (Table 5). All of these genes were highly expressed in the low N treatment and followed an expression pattern similar to that of significantly upregulated N transcripts (Figure 3). Examination of low P transcripts in CCMP 1984 (Wurch et al., 2011b) identified considerable overlap with the CCMP 1850 low P transcriptome, including the upregulation of a 5′-nucleotidase, alkaline phosphatase, arsenite translocating ATPase, inorganic phosphate transporter, and a VTC4 polyphosphate polymerase (Table 6).
Full genome sequencing for eukaryotic phytoplankton is rare and with the recent exception of E. huxleyi (Read et al., 2013), genomes are only available for single isolates within a species (Palenik et al., 2007), and often only for a single species within the genus or even functional group (Armbrust et al., 2004; Gobler et al., 2011). The de novo assembly of high throughput transcript reads is an increasingly used and powerful alternative for the examination of strain differences, gene discovery, and expression analysis (Moustafa et al., 2010; Thompson et al., 2011; Dyhrman et al., 2012; Keeling et al., 2014). Here, high throughput sequencing was used to examine the toxic A. anophagefferens strain CCMP 1850 transcriptome, and how it was modulated under the low N, low P, and low light conditions that this alga may experience in an ecosystem setting during harmful algal blooms.
Comparison of the two de novo assemblies of strain CCMP 1850 to the CCMP 1984 genome found >95% of the assembled transcripts successfully aligned to the full CCMP 1984 genome scaffolds. Another indication of strain similarity was further observed, in that the majority of CCMP 1984 gene models were present in the two de novo assemblies with the Trinity pipeline performing somewhat better. Variability in gene model recovery could be related to sequence heterogeneity or variability in gene content between strains. It could also be that these genes are not expressed, or not expressed highly enough under the conditions used to build the assembly for them to be detected. A specific key difference between the genome strain CCMP 1984 and CCMP 1850 is the noted toxicity of the latter (Harke et al., 2011). No clear pathways for toxin production were detected by this study, most likely because the mechanism of toxicity of this alga is unclear (Gobler et al., 2005) and, hence, the genes responsible for mediating toxicity are likely novel. Little is known about the regulation of toxin production, but it is also possible that the transcripts for toxin production are not present in this assembly. Future conditional gene expression studies in toxic strains of A. anophagefferens would help elucidate pathways for toxin production.
The conditions used for the transcriptome assembly presented here provide an opportunity to examine differential responses in CCMP 1850 to the low inorganic nutrient and low light conditions that may prevail during blooms. Sequencing of biological replicates was not available as part of the MMETSP. To address this, samples in this study were pooled from triplicate cultures and then analyzed with a conservative statistical tool developed and optimized for analyzing non-replicated RNA-seq data. ASC is a Bayesian method which computes the posterior probability associated with different fold changes (Wu et al., 2010). ASC detects differentially expressed genes over a wide range of read counts and performs accurately but conservatively when compared to other methods on data with and without replicates (Wu et al., 2010). In short, while false discovery is low, the trade-off is that ASC generally recovers fewer significant genes compared to other bioinformatics methods applied with replicates (Wu et al., 2010). Hence, this approach may not detect some responses that are biologically relevant. This tool has been successfully implemented to study differential expression patterns in a number of peer-reviewed studies (Alexander et al., 2012; Dyhrman et al., 2012; Thomas et al., 2012; Konotchick et al., 2013).
Functional annotation of significantly expressed transcripts showed that pathways recovered were similar regardless of whether transcriptomes were assembled with de novo or genome mapping pipelines. An important exception to this is the VTC4 polyphosphate polymerase that was not among the CCMP 1984 gene models, but was present in the genome scaffolds. The detection of a significant and biologically important transcript within de novo assemblies that would not have been readily detected using genome mapping underscores the benefit of using these methods to facilitate gene discovery. In each transcriptome, roughly half of the significant transcripts remained unannotated after the annotation step; these transcripts could represent important conditional responses and future studies could focus on the determination of their function. While the functions of the discussed genes have not been experimentally validated, overall the results presented here underscore both the robust nature of de novo assemblies and the detection of consistent significant responses using ASC without replicates and with or without a genome. As such, other researchers performing similar analyses on MMETSP data may be able to confidently recover genes and assess differential responses regardless of the assembly method, the presence of a sequenced genome, or replicates.
Low N Responses in A. anophagefferens CCMP 1850
The low N treatment was characterized by the significant upregulation of transcripts with known roles in N metabolism including a nitrate transporter, nitrite reductase and a peptidase. This underscores that increased transport of inorganic N and utilization of DON sources are central responses to the low N conditions in which blooms occur. These responses emphasize the importance of DON metabolism in this species, which has been well-documented in other studies (Berg et al., 2008; Gobler et al., 2011; Wurch et al., 2011b).
Although the stringency of ASC limited the number of statistically significant responses with known roles in N metabolism detected in CCMP 1850, N-related transcriptional responses have been studied in some detail for other phytoplankton including diatoms and coccolithophores (Dyhrman et al., 2006; Allen et al., 2011; Bender et al., 2014). The homologs of N-responsive genes (e.g. nitrate transporter, urea transporter etc.) from other phytoplankton were present in the CCMP 1850 transcriptome, and their expression patterns closely paralleled those of the significant CCMP 1850 N-responsive transcripts. It is likely that these transcripts, which encode for arginase, nitrate reductase, and urease, among others, are biologically responding to the low exogenous inorganic N supply given their expression characteristics, even though the stringency of ASC prevented their inclusion among the pool of genes identified as significantly differentially expressed. Ultimately, given the patterns observed here, it is likely that the aforementioned transcripts are in fact important N responders and thus implicated in enabling A. anophagefferens success under the low N conditions that occur during blooms. In phytoplankton certain low N responses appear to be conserved. These include upregulation of nitrate transporters, which was observed in E. huxleyi and several diatoms (Dyhrman et al., 2006; Allen et al., 2011; Bender et al., 2014). Conversely, urea uptake and utilization pathways have more varied patterns of expression in response to low N, with upregulation of urea cycle transcripts observed in diatoms and A. anophagefferens, but not E. huxleyi (Dyhrman et al., 2006; Allen et al., 2011; Bender et al., 2014). The variability in expression of these pathways has implications for the influence of urea on niche segregation over other nutrients like nitrate in phytoplankton.
The observed downregulation of LHC-encoding transcripts in the low N treatment and the concurrent upregulation of protein recycling enzymes like peptidases hint at a mechanism of N sparing with the concomitant loss of photosynthetic efficiency. This is consistent with a marked decrease in chlorophyll a concentration and the observed decline in photosynthetic efficiency without a decrease in cell concentration at the time of harvesting the low N treatment. In other phytoplankton, environmental cues such as changes in light level and nutrient availability have been noted to alter the composition of LHC proteins (Grossman et al., 1993). Additionally, a transcriptional investigation of E. huxleyi noted a downregulation of LHC transcripts in response to low N (Dyhrman et al., 2006). Consistent with N-sparing through a reduction in N-rich proteins, transcripts encoding protein-degrading enzymes were significantly upregulated and could serve to recycle N in order to increase the pool of available N during times when exogenous concentrations are low.
Low P Responses in A. anophagefferens CCMP 1850
Transcriptional patterns in the low P treatment reflect the importance of phosphate transport, organic P utilization, P homeostasis, and the detoxification of arsenate. With the upregulation of a phosphate transporter and several transcripts encoding enzymes like 5′-nucleotidase and alkaline phosphatase, A. anophagefferens CCMP 1850 likely increases phosphate uptake and the hydrolysis of DOP under low P conditions. Notably, alkaline phosphatase activity was heightened in the low P treatment concurrent with the significant upregulation of the alkaline phosphatase transcript. These low P responses have also been detected in other phytoplankton including coccolithophores and diatoms at the transcriptional level (Dyhrman et al., 2006, 2012), and in many other physiological studies (Gonzalez-Gil et al., 1998; Dyhrman and Palenik, 1999; Chung et al., 2003; Dyhrman, 2005; Dyhrman and Ruttenberg, 2006) highlighting the conserved nature of this response. As with the patterns described above for DON, DOP likely plays a critical role in fueling the growth of this species during blooms.
Although these responses are typically conserved among eukaryotic algae, relatively little is known about the molecular-level signaling cascade that regulates these genes. In Chlamydomonas the P stress response is thought to be regulated in part by the induction of the transcription factor PSR1 that controls expression of phosphate transporters and phosphatases (Wykoff et al., 1999; Moseley et al., 2006). Although a possible homolog of Chlamydomonas PSR1 was detected in the CCMP 1850 transcriptome, it was not upregulated in response to low P. In yeast, there is a well-characterized cyclin-dependent PHO pathway (Lenburg and O'Shea, 1996), and the significant upregulation of a yeast PHO81 homolog in A. anophagefferens CCMP 1850 suggests that a yeast-like mechanism may be used to sense and respond to low P in A. anophagefferens. In Aureococcus, the relationship between P deprivation and bloom dynamics is increasingly recognized as important (Wurch et al., 2014) and the P sensor response system in this species warrants further study.
Potential P recycling and sparing strategies in A. anophagefferens CCMP 1850 are evident by the upregulation of an acid phosphatase and a polyphosphate polymerase. In higher plants, acid phosphatases are upregulated under low P (Veljanovski et al., 2006) where they act to circumvent the P-requiring steps of glycolysis by preferentially hydrolyzing phosphoenolpyruvate (PEP) (Lefebvre et al., 1990). Breakdown of PEP leads to a “glycolytic bypass” whereby carbon metabolism is able to progress while bypassing some P-requiring steps (Lefebvre et al., 1990). The presence of a glycolytic bypass has been hypothesized for diatoms (Dyhrman et al., 2012) and A. anophagefferens CCMP 1984 (Wurch et al., 2011a). It is also possible that the acid phosphatase is localized to an intracellular vacuole where it may be involved in polyphosphate cycling (Veljanovski et al., 2006). The modulation of polyphosphate pools is increasingly recognized as an important aspect of P homeostasis in low P conditions (Dyhrman et al., 2006, 2012; Martin and Van Mooy, 2013; Martin et al., 2014). The upregulation of the VTC4 polyphosphate polymerase (Hothorn et al., 2009), suggests that although luxury stores of polyphosphate may be mobilized during P stress, there may also be polyphosphate biosynthesis. This is consistent with observations of increased polyphosphate to total particulate phosphate ratios in phytoplankton from the low P Sargasso Sea (Martin et al., 2014). During low P conditions cells could experience a temporary excess of inorganic phosphate that could preemptively repress continued phosphate uptake. The upregulation of a polyphosphate polymerase during P stress conditions could enable the creation of a sink of readily accessible P while also circumventing repression of P scavenging (Ogawa et al., 2000). On the whole, the role of polyphosphate metabolism in P homeostasis is relatively unexplored in marine phytoplankton, and the presence of this response in A. anophagefferens, as well as coccolithophores and diatoms (Dyhrman et al., 2006, 2012) hints that induction of polyphosphate polymerases is an important and conserved P stress response.
In the low P transcriptome, an inorganic phosphate transporter was significantly upregulated; such transporters cannot typically discriminate between phosphate and arsenate and their upregulation could lead to an increase in intracellular arsenate (Budd and Craig, 1981; Silver and Phung, 2005). During low P conditions A. anophagefferens may mitigate arsenic toxicity by enzymatically reducing arsenate to arsenite and then pumping arsenite out of the cell. Eukaryotes have also been shown to employ an alternate method for arsenate reduction via a glutathione S-transferase (Zakharyan et al., 2005). This enzyme was significantly upregulated in the low P treatment, and it is possible that this represents a primary mode for arsenate reduction in A. anophagefferens. The resulting arsenite may be removed from the cell via an arsenite translocating ATPase, which was upregulated in the low P treatment. Some eukaryotic proteins with homology to arsenite translocating ATPases are implicated in gas vesicle formation and carbon starvation responses rather than arsenate detoxification (Castillo and Saier, 2010), but it is common for these pathways to be induced during low P in cyanobacteria (Cervantes et al., 1994; Rahman and Hassler, 2014). No transcripts encoding proteins in metal detoxification pathways were upregulated in the low P treatments of T. pseudonana (Dyhrman et al., 2012) or E. huxleyi (Dyhrman et al., 2006). This indicates that a highly responsive arsenic detoxification pathway could be a uniquely important physiological strategy for A. anophagefferens to bloom in coastal systems with high metal concentrations. Consistent with this idea, the greater abundance of metalloenzymes in A. anophagefferens compared to other phytoplankton has previously been interpreted as a sign of genomic adaptation to high metal concentrations in coastal environments (Gobler et al., 2011).
The uptake of arsenate could be amplified in coastal environments where arsenate concentrations are relatively high (Sanders, 1985) and ratios of As:P could be increased during the low inorganic P conditions that accompany brown tide blooms (Wurch et al., 2014). In the surface waters of oxidizing marine systems, arsenate is the most abundant inorganic arsenic compound (Sanders and Windom, 1980). In marine systems, microbial activities have been shown to modulate arsenic geochemistry and it has been noted that arsenite is the dominant species in systems with low P (Cutter and Cutter, 2006), suggestive of microbial detoxification. In A. anophagefferens, arsenate uptake, detoxification through arsenite efflux, and its potential role in altering coastal geochemistry have yet to be studied. Given the low and sometimes growth limiting inorganic P concentrations that have been observed during brown tide bloom events (Gobler et al., 2004; Wurch et al., 2014), the role of arsenic in A. anophagefferens eco-physiology is an important area of future research.
Low Light Response in A. anophagefferens CCMP 1850
In A. anophagefferens, growth under low light conditions resulted in the upregulation of transcripts related to lipid metabolism and cycling, the breakdown of organic molecules, and restructuring of the photosynthetic apparatus. The upregulated transcripts encoding lipid-specific enzymes like lysophospholipases have not been characterized in eukaryotic phytoplankton, but in bacteria they are cell membrane localized and are the first step in lipid scavenging for membrane incorporation (Pride et al., 2013). Patatin-like phospholipases are widely distributed in prokaryotes and eukaryotes and are implicated in an array of functions including triacylglyceride metabolism, lipid membrane recycling, and membrane trafficking (Wilson, 2006).
Peroxisome activity could be another important lipid-related, low light response to organic matter processing. Transcripts identified as encoding integral peroxisome membrane components, peroxidase/catalase and glutathione peroxidase were significantly upregulated in the low light treatment. Antioxidant enzymes have been shown to respond to stress conditions in other phytoplankton (Pinto et al., 2003). There are many different specific functions of peroxisomes, however many contain antioxidant enzymes and are implicated in the oxidation of long chain fatty acids (Stabenau et al., 1989). Whether exogenous lipids were being catabolized as an energy source or recycled back into membranes to avoid the high energetic cost of fatty acid biosynthesis is unknown. Uptake and metabolism of long chain fatty acids is rare in bacteria (Pride et al., 2013), largely uncharacterized in phytoplankton, and has been previously overlooked as a mechanism that could allow A. anophagefferens to thrive under the low light conditions that are pervasive during dense brown tides.
The oxidation of organic molecules could help to explain the ability of A. anophagefferens to survive in conditions generally unfavorable for phototrophic growth. During experimental prolonged dark incubation, the cellular chlorophyll a content of A. anophagefferens did not decline, despite slight decreases in total cellular carbohydrates, proteins, and lipids (Popels et al., 2007). The pattern of utilization of cellular reserves appears to be conserved across eukaryotic phytoplankton, starting preferentially with the breakdown of starch, followed by proteolytic recycling of peptides, and ultimately the utilization of lipids (Handa, 1969; Griffiths, 1973; Dehning and Tilzer, 1989). The low light transcriptional responses identified here support the occurrence of these processes in A. anophagefferens during low light conditions.
The significant expression of transcripts involved in sulfolipid biosynthesis was a unique response to low light treatment. Despite their wide occurrence, sulfolipids are not essential for growth in autotrophs and their biosynthesis and substitution for phospholipids has been shown to serve mainly as a P stress response (Van Mooy et al., 2009; Martin et al., 2011; Wurch et al., 2011a). In A. anophagefferens, the concurrent upregulation of transcripts for sulfolipid biosynthesis and transcripts encoding photosystem proteins like LHCs could reflect an attempt to increase plastid membrane surface area to maximize photosynthetic yield during low light levels. This is corroborated by the expression of lipid recycling enzymes in the low P and low light treatments.
It is well-established that in low light photosynthetic cells increase pigment concentration and plastid membrane production (Archer et al., 1997). In the environment, dense brown tide blooms are accompanied by attenuated light conditions. Thus, low light could result in an altered P demand depending on how much phospholipid is recycled, replaced with sulfolipids, or newly synthesized as membrane area increases to accommodate more pigments. If there is an increase in phospholipid biosynthesis associated with low light, then A. anophagefferens blooms could experience enhanced P demand and subsequent P stress under the low light levels that accompany elevated cell densities. Consistent with this hypothesis, recent fieldwork has identified P stress responses in high density populations of A. anophagefferens (Wurch et al., 2014) and former work has found P limitation of A. anophagefferens net growth rates during blooms (Gobler et al., 2004). It has been established in ecosystem (Van Mooy et al., 2009) and laboratory studies (Martin et al., 2011; Wurch et al., 2011a; Dyhrman et al., 2012) that phytoplankton (including A. anophagefferens CCMP 1984) switch phospholipids for sulfolipids as a P conservation strategy. The results of this study indicate that the expression of sulfolipid biosynthesis genes might not be specific enough to assess P stress from light stress in field populations. Instead, the lipid composition of phytoplankton cells might be more diagnostic, as cells compensating for low P concentrations would have a higher ratio of sulfolipid to phospholipid relative to cells in replete conditions, whereas cells in low light would more likely have similar ratios but higher overall amounts of both lipids.
Overlapping Transcriptional Responses
There were few transcripts that were jointly upregulated across all treatments. This could indicate that during stress conditions the transcriptional response of A. anophagefferens is uniquely tailored to the environment. The lack of overlap also illustrates the potential to use significant condition-responsive transcripts as biomarkers of environmental conditions in the field. In contrast to the low number of general stress and nutrient stress transcripts that were upregulated, these overlap categories had high number of transcripts downregulated relative to the control. Based on their KEGG identification, a high number these transcripts could be related to cell division or growth processes and are likely indicative of the stationary phase that these treatments were entering at the time of harvest.
During nutrient stress, a high proportion of genes for the synthesis of secondary metabolites were downregulated. It has been noted that at the height of brown tide blooms, A. anophagefferens is only minimally subjected to grazing (Gobler et al., 2005; Sunda et al., 2006). The production of secondary metabolites could be an important facet of grazer deterrence and the genome of A. anophagefferens has been shown to contain significantly more genes involved in the biosynthesis of these metabolites than other phytoplankton (Gobler et al., 2011). It is possible that slowed production of secondary metabolites when nutrient supplies diminish may leave this species more vulnerable to predation pressure that may contribute to the demise of brown tides.
Strain Responses to Low N and Low P
Previous low-resolution global transcriptional studies of A. anophagefferens CCMP 1984 (Wurch et al., 2011b) and targeted work on a suite of N metabolism genes (Berg et al., 2008) enabled the assessment of potential strain heterogeneity in response to low N and low P for this species. However, these comparisons carry several caveats. Subtle differences in the time of cell harvest and the growth conditions could impact the observed signals dramatically. Further, the CCMP 1984 Long-SAGE study by Wurch et al. (2011b) only examined the most abundant transcripts with NlaIII restriction sites. Despite these caveats there was overlap of significant nutrient responsive genes between the strains.
In both strains, the low P response was characterized by significantly upregulating transcripts for phosphate transport, DOP hydrolysis, the modulation of intracellular polyphosphate, and the detoxification of arsenic. Notably, the regulation of the phosphate transporter has been shown to be tightly regulated by P in CCMP 1984, and is expressed in field populations (Wurch et al., 2014). Its joint presence in both strains suggests both the consistency of the strain responses, and its potential utility as a biomarker of P stress in field populations.
There was also considerable strain overlap in response to low N. Shared significant functional responses included increased nitrate transport and peptidase activity (Berg et al., 2008; Wurch et al., 2011b), which again emphasizes the importance of DON metabolism in this species. By querying the CCMP 1850 transcripts for genes with known N regulation patterns in other algae and CCMP 1984, a number of putatively N-responsive transcripts were identified that followed an N-responsive pattern but were not detected as significant with our conservative application of ASC. These transcripts, putatively N-regulated in both strains, were found to encode a suite of transporters and enzymes for the transport and metabolism of DON, such as a xanthine/uracil/vitamin C permease, a formamidase, and an amino acid transporter among others. The xanthine/uracil/vitaminC permease is tightly regulated by N in CCMP 1984 and expressed in field populations (Wurch et al., 2014). More detailed expression work in CCMP 1850 may confirm its utility as a biomarker of N stress, although with the data herein, the nitrate transporter may be a better candidate given its significant response in both strains (Berg et al., 2008; Wurch et al., 2011b). Overall, the overlapping responses to nutrient deficiency reinforce the importance of traits that are critical to this HAB-forming organism's ecological success: the ability to utilize or recycle a wide range of N and P forms, especially DON and DOP.
Assembly of 50 bp reads generated from high throughput sequence data from A. anophagefferens CCMP 1850 and differential expression analysis using ASC (Wu et al., 2010) revealed that genome mapping and de novo assembly pipelines can yield similar results, thus highlighting the efficacy of these approaches for the analysis of future MMETSP datasets. These findings underscore the utility of transcriptome profiling for gene discovery, examining strain differences and differential expression analysis, even in the absence of a sequenced genome. Taken in whole, the transcriptional responses to the test conditions in CCMP 1850 and the presence of similar responses in strain CCMP 1984 underscore that the ability to utilize and recycle organic compounds is a critical, niche-defining stress response in A. anophagefferens. Previous studies have assessed the range of strain level variation within a single phytoplankton species by examining the metabolic potential encoded in the genome (Read et al., 2013). The results presented here underscore that strain differentiation can also be considered at the transcriptional level, as differentiation has the potential to be conditional and dynamic, rather than inherent and static. Future comparison of transcriptional responses across conditions and between strains of A. anophagefferens will be a useful tool in the exploration of the eco-physiology of this organism.
Conflict of Interest Statement
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.
This research was funded by NOAA Grant #NA09NOA4780206 through the ECOHAB Program. Funding was also provided by the Woods Hole Oceanographic Institution Coastal Ocean Institute and in part by the Gordon and Betty Moore Foundation through Grant #2637 to the National Center for Genome Resources. The samples referenced in this study (MMETSP0914, MMETSP0915, MMETSP0916, and MMETSP0917) were sequenced, assembled and annotated with the ABySS pipeline at the National Center for Genome Resources. The authors acknowledge the work of Dr. Dianna Berry who developed and implemented the metholodogies for extracting RNA from cultures for this project. The authors also acknowledge the Mason cluster of the National Center for Genome Analysis Support, and Carrie Ganote, Sheean Haley and Harriet Alexander for valuable input and bioinformatics assistance. The authors also acknowledge the reviewers, whose comments and suggestions strengthened the manuscript. CJG and MJH efforts were supported by NOAA award #NA10NOS4780140. KRF is funded under a National Science Foundation Graduate Research Fellowship.
The Supplementary Material for this article can be found online at: http://www.frontiersin.org/journal/10.3389/fmicb.2014.00375/abstract
Alexander, H., Jenkins, B. D., Rynearson, T. A., Saito, M. A., Mercier, M. L., and Dyhrman, S. T. (2012). Identifying reference genes with stable expression from high throughput sequence data. Front. Microbiol. 3:385. doi: 10.3389/fmicb.2012.00385
Allen, A. E., Dupont, C. L., Oborník, M., Horák, A., Nunes-Nesi, A., McCrow, J. P., et al. (2011). Evolution and metabolic significance of the urea cycle in photosynthetic diatoms. Nature 473, 203–207. doi: 10.1038/nature10074
Archer, S. D., McDonald, K. A., and Jackman, A. P. (1997). Effect of light irradiance on the production of sulfolipids from Anabaena 7120 in a fed-batch photobioreactor. Appl. Biochem. Biotechnol. 67, 139–152.
Armbrust, E. V., Berges, J. A., Bowler, C., Green, B. R., Martinez, D., Putnam, N. H., et al. (2004). The genome of the diatom Thalassiosira pseudonana: ecology, evolution, and metabolism. Science 306, 79–86. doi: 10.1126/science.1101156
Bender, S. J., Durkin, C. A., Berthiaume, C. T., Morales, R. L., and Armbrust, E. V. (2014). Transcriptional responses of three model diatoms to nitrate limitation of growth. Front.Mar. Sci. 1:3 doi: 10.3389/fmars.2014.00003
Berg, G. M., Shrager, J., Glöckner, G., Arrigo, K. R., and Grossman, A. R. (2008). Understanding nitrogen limitation in Aureococcus anophagefferens (Pelagophyceae) through cDNA and qRT-PCR analysis. J. Phycol. 44, 1235–1249. doi: 10.1111/j.1529-8817.2008.00571.x
Birol, I., Jackman, S. D., Nielsen, C. B., Qian, J. Q., Varhol, R., and Stazyk, G., et al. (2009). De novo transcriptome assembly with ABySS. Bioinformatics 25, 2872–2877. doi: 10.1093/bioinformatics/btp367
Boneillo, G. E., and Mulholland, M. R. (2013). Interannual variability influences brown tide (Aureococcus anophagefferens) blooms in coastal embayments. Estuaries Coasts 37, 1–17. doi: 10.1007/s12237-013-9683-3
Chung, C., Hwang, S. L., Chang, J., Chung, C., Hwang, S. L., and Chang, J. (2003). Identification of a high-affinity phosphate transporter gene in a Prasinophyte alga, Tetraselmis chui, and its expression under nutrient limitation (2003). Appl. Environ. Microbiol. 69, 754–759. doi: 10.1128/AEM.69.2.754-759.2003
Doblin, M. A., Blackburn, S. I., and Hallegraeff, G. M. (1999). Growth and biomass stimulation of the toxic dinoflagellate Gymnodinium catenatum (Graham) by dissolved organic substances. J. Exp. Mar. Biol. Ecol. 236, 33–47.
Dyhrman, S. T., Haley, S. T., Birkeland, S. R., Wurch, L. L., Cipriano, M. J., and McArthur, A. G. (2006). Long serial analysis of gene expression for gene discovery and transcriptome profiling in the widespread marine coccolithophore Emiliania huxleyi. Appl. Env. Microbiol. 72, 252–260. doi: 10.1128/AEM.72.1.252-260.2006
Dyhrman, S. T., Jenkins, B. D., Rynearson, T. A., Saito, M. A., Mercier, M. L., Alexander, H., et al. (2012). The transcriptome and proteome of the diatom Thalassiosira pseudonana reveal a diverse phosphorus stress response. PLoS ONE 7:e33768. doi: 10.1371/journal.pone.0033768
Dyhrman, S. T., and Palenik, B. (1999). Phosphate stress in cultures and field populations of the dinoflagellate Prorocentrum minimum detected by a single-cell alkaline phosphatase assay. Appl. Env. Microbiol. 65, 3205–3212.
Dyhrman, S. T., and Ruttenberg, K. C. (2006). Presence and regulation of alkaline phosphatase activity in eukaryotic phytoplankton from the coastal ocean: Implications for dissolved organic phosphorus remineralization. Limnol. Oceangr. 51, 1381–1390. doi: 10.4319/lo.2006.51.3.1381
Gobler, C. J., Berry, D. L., Dyhrman, S. T., Wilhelm, S. W., Salamov, A., Lobanov, A. V., et al. (2011). Niche of harmful alga Aureococcus anophagefferens revealed through ecogenomics. Proc. Natl. Acad. Sci. U.S.A. 108, 4352–4357. doi: 10.1073/pnas.1016106108
Gobler, C. J., Boneillo, G. E., Debenham, C., and Caron, D. A. (2004). Nutrient limitation, organic matter cycling, and plankton dynamics during an Aureococcus anophagefferens bloom. Aquatic Microbial Ecol. 35, 31–43. doi: 10.3354/ame035031
Gobler, C. J., Lonsdale, D. J., and Boyer, G. L. (2005). A review of the causes, effects, and potential management of harmful brown tide blooms caused by Aureococcus anophagefferens (Hargraves et sieburth). Estuaries 28, 726–749. doi: 10.1007/BF02732911
Gobler, C. J., and Sunda, W. G. (2012). Ecosystem disruptive algal blooms of the brown tide species, Aureococcus anophagefferens and Aureoumbra lagunensis. Harmful Algae 14, 36–45. doi: 10.1016/j.hal.2011.10.013
Gonzalez-Gil, S., Keafer, B. A., Jovine, R. V. M., Aguilera, A., Lu, S., and Anderson, D. M. (1998). Detection and quantification of alkaline phosphatase in single cells of phosphorus-starved marine phytoplankton. Mar. Ecol. Prog. Ser. 164, 21–35.
Gough, J., Karplus, K., Hughey, R., and Chothia, C. (2001). Assignment of homology to genome sequences using a library of hidden Markov models that represent all proteins of known structure. J. Mol. Biol. 313, 903–919. doi: 10.1006/jmbi.2001.5080
Grabherr, M. G., Haas, B. J., Yassour, M., Levin, J. Z., Thompson, D. A., Amit, I., et al. (2011). Full-length transcriptome assembly from RNA-Seq data without a reference genome. Nat. Biotechnol. 29, 644–652. doi: 10.1038/nbt.1883
Haft, D. H., Loftus, B. J., Richardson, D. L., Yang, F., Eisen, J. A., Paulsen, I. T., et al. (2001). TIGRFAMs: a protein family resource for the functional identification of proteins. Nucleic Acids Res. 29, 41–43. doi: 10.1093/nar/29.1.41
Harke, M. J., Gobler, C. J., and Shumway, S. E. (2011). Suspension feeding by the Atlantic slipper limpet (Crepidula fornicata) and the northern quahog (Mercenaria mercenaria) in the presence of cultured and wild populations of the harmful brown tide alga, Aureococcus anophagefferens. Harmful Algae 10, 503–511. doi: 10.1016/j.hal.2011.03.005
Heisler, J., Glibert, P. M., Burkholder, J. M., Anderson, D. M., Cochlan, W., Dennison, W. C., et al. (2008). Eutrophication and harmful algal blooms: a scientific consensus. Harmful Algae 8, 3–13. doi: 10.1016/j.hal.2008.08.006
Hothorn, M., Neumann, H., Lenherr, E. D., Wehner, M., Rybin, V., and Hassa, P. O., et al. (2009). Catalytic core of a membrane-associated eukaryotic polyphosphate polymerase. Science 324, 513–516. doi: 10.1126/science.1168120
Iseli, C., Jongeneel, C. V., and Bucher, P. (1999). ESTScan: a program for detecting, evaluating, and reconstructing potential coding regions in EST sequences. Proc. Int. Conf. Intell. Syst. Mol. Biol. 99, 138–148.
Kana, T. M., Lomas, M. W., MacIntyre, H. L., Cornwell, J. C., and Gobler, C. J. (2004). Stimulation of the brown tide organism, Aureococcus anophagefferens, by selective nutrient additions to in situ mesocosms. Harmful Algae 3, 377–388. doi: 10.1016/j.hal.2004.06.008
Keeling, P. J., Burki, F., Wilcox, H. M., Allam, V., Allen, E. E., Amaral-Zettler, L. A., et al. (2014). The marine microbial eukaryote transcriptome sequencing project (MMETSP): illuminating the functional diversity of eukaryotic life in the oceans through transcriptome sequencing. PLoS Biol. 12:e1001889. doi: 10.1371/journal.pbio.1001889
Konotchick, T., Dupont, C. L., Valas, R. E., Badger, J. H., and Allen, A. E. (2013). Transcriptomic analysis of metabolic function in the giant kelp, Macrocystis pyrifera, across depth and season. New Phytol. 198, 398–407. doi: 10.1111/nph.12160
Lefebvre, D. D., Duff, S. M., Fife, C. A., Julien-Inalsingh, C., and Plaxton, W. C. (1990). Response to phosphate deprivation in Brassica nigra suspension cells : enhancement of intracellular, cell surface, and secreted phosphatase activities compared to increases in pi-absorption rate. Plant Physiol. 93, 504–511.
Lohse, M., Bolger, A. M., Nagel, A., Fernie, A. R., Lunn, J. E., Stitt, M., et al. (2012). RobiNA: a user-friendly, integrated software solution for RNA-Seq-based transcriptomics. Nucleic Acids Res. 40, W622–W627. doi: 10.1093/nar/gks540
Martin, P., Dyhrman, S. T., Lomas, M. W., Poulton, N. J., and Van Mooy, B. A. S. (2014). Accumulation and enhanced cycling of polyphosphate by Sargasso Sea plankton in response to low phosphorus. Proc. Natl. Acad. Sci. U.S.A. 111, 8089–8094. doi: 10.1073/pnas.1321719111
Martin, P., and Van Mooy, B. A. S. (2013). Fluorometric quantification of polyphosphate in environmental plankton samples: extraction protocols, matrix effects, and nucleic acid interference. Appl. Environ. Microbiol. 79, 273–281. doi: 10.1128/AEM.02592-12
Martin, P., Van Mooy, B. A. S., Heithoff, A., and Dyhrman, S. T. (2011). Phosphorus supply drives rapid turnover of membrane phospholipids in the diatom Thalassiosira pseudonana. ISME J. 5, 1057–1060. doi: 10.1038/ismej.2010.192
Moseley, J. L., Chang, C., and Arthur, G. (2006). Genome-based approaches to understanding phosphorus deprivation responses and PSR1 control in Chlamydomonas reinhardtii. Eukaryot. Cell. 5, 26–44. doi: 10.1128/EC.5.1.26-44.2006
Moustafa, A., Evans, A. N., Kulis, D. M., Hackett, J. D., Erdner, D. L., Anderson, D. M., et al. (2010). Transcriptome profiling of a toxic dinoflagellate reveals a gene-rich protist and a potential impact on gene expression due to bacterial presence. PLoS ONE 5:e9688. doi: 10.1371/journal.pone.0009688
Ogawa, N., DeRisi, J., and Brown, P. O. (2000). New components of a system for phosphate accumulation and polyphosphate metabolism in Saccharomyces cerevisiae revealed by genomic expression analysis. Mol. Biol. Cell. 11, 4309–4321. doi: 10.1091/mbc.11.12.4309
Palenik, B., Grimwood, J., Aerts, A., Rouzé, P., Salamov, A., Putnam, N., et al. (2007). The tiny eukaryote Ostreococcus provides genomic insights into the paradox of plankton speciation. Proc. Natl. Acad. Sci. USA. 104, 7705–7710. doi: 10.1073/pnas.0611046104
Pinto, E., Sigaud-Kutner, T. C. S., Leitao, M. A. S., Okamoto, O. K., Morse, D., and Colepicolo, P. (2003). Heavy metal-induced oxidative stress in algae. J. Phycol. 39, 1008–1018. doi: 10.1111/j.0022-3646.2003.02-193.x
Popels, L. C., and Hutchins, D. A. (2002). Factors affecting dark survival of the brown tide alga Aureococcus anophagefferens (Pelagophyceae). J. Phycol. 38, 738–744. doi: 10.1046/j.1529-8817.2002.01115.x
Popels, L. C., MacIntyre, H. L., Warner, M. E., Zhang, Y., and Hutchins, D. A. (2007). Physiological responses during dark survival and recovery in Aureococcus anophagefferens (Pelagophyceae). J. Phycol. 43, 32–42. doi: 10.1111/j.1529-8817.2006.00303.x
Pride, A. C., Herrera, C. M., Guan, Z., Giles, D. K., and Trent, M. S. (2013). The outer surface lipoprotein VolA mediates utilization of exogenous lipids by Vibrio cholerae. MBio 4, e00305–e00313. doi: 10.1128/mBio.00305-13
Read, B. A., Kegel, J., Klute, M. J., Kuo, A., Lefebvre, S. C., Maumus, F., et al. (2013). Pan genome of the phytoplankton Emiliania huxleyi underpins its global distribution. Nature 499, 209–213. doi: 10.1038/nature12221
Roberts, A., Goff, L., Pertea, G., Kim, D., Kelley, D. R., Pimentel, H., et al. (2012). Differential gene and transcript expression analysis of RNA-seq experiments with TopHat and Cufflinks. Nat. Protoc. 7, 562–578. doi: 10.1038/nprot.2012.016
Silver, S., and Phung, L. T. (2005). Minireview: genes and enzymes involved in bacterial oxidation and reduction of inorganic arsenic. Appl. Env. Microbiol. 71, 599–608. doi: 10.1128/AEM.71.2.599-608.2005
Simpson, J. T., Wong, K., Jackman, S. D., Schein, J. E., Jones, S. J. M., and Birol, I. (2009). ABySS: a parallel assembler for short read sequence data. Genome Res. 19, 1117–1123. doi: 10.1101/gr.089532.108
Stabenau, H., Winkler, U., and Säftel, W. (1989). Compartmentation of peroxisomal enzymes in algae of the group of prasinophyceae: occurrence of possible microbodies without catalase. Plant Physiol. 90, 754–759.
Sunda, W. G., Granéli, E., and Gobler, C. J. (2006). Positive feedback and the development and persistence of ecosystem disruptive algal blooms. J. Phycol. 42, 963–974. doi: 10.1111/j.1529-8817.2006.00261.x
Suzek, B. E., Huang, H., McGarvey, P., Mazumder, R., and Wu, C. H. (2007). UniRef: comprehensive and non-redundant UniProt reference clusters. Bioinformatics 23, 1282–1288. doi: 10.1093/bioinformatics/btm098
Thomas, M. F., Abdul-Wajid, S., Panduro, M., Babiarz, J. E., Rajaram, M., Woodruff, P., et al. (2012). Eri1 regulates microRNA homeostasis and mouse lymphocyte development and antiviral function. Blood 120, 130–142. doi: 10.1182/blood-2011-11-394072
Thompson, A. W., Huang, K., Saito, M. A., and Chisholm, S. W. (2011). Transcriptome response of high- and low-light-adapted Prochlorococcus strains to changing iron availability. ISME J. 5, 1580–1594. doi: 10.1038/ismej.2011.49
Toh-e, A., Inouye, S., and Oshima, Y. (1981). Structure and function of the PHO82-pho4 locus controlling the synthesis of repressible acid phosphatase of Saccharomyces cerevisiae. J. Bacteriol. 145, 221–232.
Van Mooy, B. A. S., Fredricks, H. F., Pedler, B. E., Dyhrman, S. T., Karl, D. M., Koblížek, M., et al. (2009). Phytoplankton in the ocean use non-phosphorus lipids in response to phosphorus scarcity. Nature 457, 69–72. doi: 10.1038/nature07659
Veljanovski, V., Vanderbeld, B., Knowles, V. L., Snedden, W. A., and Plaxton, W. C. (2006). Biochemical and molecular characterization of AtPAP26, a vacuolar purple acid phosphatase up-regulated in phosphate-deprived Arabidopsis suspension cells and seedlings. Plant Physiol. 142, 1282–1293. doi: 10.1104/pp.106.087171
Wu, Z., Jenkins, B. D., Rynearson, T. A., Dyhrman, S. T., Saito, M. A., Mercier, M., et al. (2010). Empirical bayes analysis of sequencing-based transcriptional profiling without replicates. BMC Bioinformatics 11:564. doi: 10.1186/1471-2105-11-564
Wurch, L. L., Bertrand, E. M., Saito, M. A., Van Mooy, B. A. S., and Dyhrman, S. T. (2011a). Proteome changes driven by phosphorus deficiency and recovery in the brown tide-forming alga Aureococcus anophagefferens. PLoS ONE 6:e28949. doi: 10.1371/journal.pone.0028949
Wurch, L. L., Haley, S. T., Orchard, E. D., Gobler, C. J., and Dyhrman, S. T. (2011b). Nutrient-regulated transcriptional responses in the brown tide-forming alga Aureococcus anophagefferens. Environ. Microbiol. 13, 468–481. doi: 10.1111/j.1462-2920.2010.02351.x
Wurch, L. L., Gobler, C. J., and Dyhrman, S. T. (2014). Expression of a xanthine and phosphate transporter in cultures and field populations of the harmful alga Aureococcus anophagefferens: tracking nutritional deficiency during brown tides. Environ. Microbiol. doi: 10.1111/1462-2920.12374. [Epub ahead of print].
Wykoff, D. D., Grossman, A. R., Weeks, D. P., Usuda, H., and Shimogawara, K. (1999). Psr1, a nuclear localized protein that regulates phosphorus metabolism in Chlamydomonas. Proc. Natl. Acad. Sci. U.S.A. 96, 15336–15341.
Zakharyan, R. A., Tsaprailis, G., Chowdhury, U. K., Hernandez, A., and Aposhian, H. V. (2005). Interactions of sodium selenite, glutathione, arsenic species, and omega class human glutathione transferase. Chem. Res. Toxicol. 18, 1287–1295. doi: 10.1021/tx0500530
Zhang, Q. C., Qiu, L. M., Yu, R. C., Kong, F. Z., Wang, Y. F., Yan, T., et al. (2012). Emergence of brown tides caused by Aureococcus anophagefferens Hargraves et Sieburth in China. Harmful Algae 19, 117–124. doi: 10.1016/j.hal.2012.06.007
Keywords: Aureococcus anophagefferens, phytoplankton, harmful algal bloom, eco-physiology, transcriptome, de novo assembly, gene expression
Citation: Frischkorn KR, Harke MJ, Gobler CJ and Dyhrman ST (2014) De novo assembly of Aureococcus anophagefferens transcriptomes reveals diverse responses to the low nutrient and low light conditions present during blooms. Front. Microbiol. 5:375. doi: 10.3389/fmicb.2014.00375
Received: 04 March 2014; Accepted: 03 July 2014;
Published online: 24 July 2014.
Edited by:Anton F. Post, MBL, USA
Reviewed by:Tom O. Delmont, Marine Biological Laboratory, USA
Lisa Campbell, Texas A&M Univeresity, USA
Chris Dupont, J. Craig Venter Institute, USA
Copyright © 2014 Frischkorn, Harke, Gobler and Dyhrman. 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) or licensor 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: Sonya T. Dyhrman, Department of Earth and Environmental Sciences and Lamont-Doherty Earth Observatory, Columbia University, 61 Route 9W, Palisades, NY 10964, USA e-mail: firstname.lastname@example.org