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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. Mar. Sci.</journal-id>
<journal-title>Frontiers in Marine Science</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. Mar. Sci.</abbrev-journal-title>
<issn pub-type="epub">2296-7745</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/fmars.2023.1259783</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Marine Science</subject>
<subj-group>
<subject>Original Research</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Coastal upwelling systems as dynamic mosaics of bacterioplankton functional specialization</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Delgadillo-Nu&#xf1;o</surname>
<given-names>Erick</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
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<role content-type="https://credit.niso.org/contributor-roles/writing-original-draft/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Teira</surname>
<given-names>Eva</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/241193"/>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Pontiller</surname>
<given-names>Benjamin</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Lundin</surname>
<given-names>Daniel</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Joglar</surname>
<given-names>Vanessa</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<role content-type="https://credit.niso.org/contributor-roles/formal-analysis/"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-original-draft/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Pedr&#xf3;s-Ali&#xf3;</surname>
<given-names>Carlos</given-names>
</name>
<xref ref-type="aff" rid="aff4">
<sup>4</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/167948"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Fern&#xe1;ndez</surname>
<given-names>Emilio</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/174218"/>
<role content-type="https://credit.niso.org/contributor-roles/writing-review-editing/"/>
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</contrib>
<contrib contrib-type="author">
<name>
<surname>Pinhassi</surname>
<given-names>Jarone</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<uri xlink:href="https://loop.frontiersin.org/people/81141"/>
<role content-type="https://credit.niso.org/contributor-roles/conceptualization/"/>
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</contrib>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Mart&#xed;nez-Garc&#xed;a</surname>
<given-names>Sandra</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>*</sup>
</xref>
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</contrib-group>
<aff id="aff1">
<sup>1</sup>
<institution>Departamento de Ecolox&#xed;a e Biolox&#xed;a Animal, Centro de Investigaci&#xf3;n Mari&#xf1;a da Universidade de Vigo (CIM-UVigo)</institution>, <addr-line>Vigo</addr-line>,&#xa0;<country>Spain</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>Centre for Ecology and Evolution in Microbial Model Systems, Linnaeus University</institution>, <addr-line>Kalmar</addr-line>,&#xa0;<country>Sweden</country>
</aff>
<aff id="aff3">
<sup>3</sup>
<institution>GEOMAR Helmholtz Centre for Ocean Research Kiel</institution>, <addr-line>Kiel</addr-line>,&#xa0;<country>Germany</country>
</aff>
<aff id="aff4">
<sup>4</sup>
<institution>Centro Nacional de Biotecnolog&#xed;a (CNB-CSIC)</institution>, <addr-line>Madrid</addr-line>,&#xa0;<country>Spain</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>Edited by: Jin Zhou, Tsinghua University, China</p>
</fn>
<fn fn-type="edited-by">
<p>Reviewed by: Daniel Jonathan Sher, University of Haifa, Israel</p>
<p>Fabiano Thompson, Federal University of Rio de Janeiro, Brazil</p>
</fn>
<fn fn-type="corresp" id="fn001">
<p>*Correspondence: Sandra Mart&#xed;nez-Garc&#xed;a, <email xlink:href="mailto:sandra@uvigo.gal">sandra@uvigo.gal</email>
</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>04</day>
<month>01</month>
<year>2024</year>
</pub-date>
<pub-date pub-type="ecorrected">
<day>18</day>
<month>06</month>
<year>2026</year>
</pub-date>
<pub-date pub-type="collection">
<year>2023</year>
</pub-date>
<volume>10</volume>
<elocation-id>1259783</elocation-id>
<history>
<date date-type="received">
<day>26</day>
<month>07</month>
<year>2023</year>
</date>
<date date-type="accepted">
<day>27</day>
<month>11</month>
<year>2023</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2024 Delgadillo-Nu&#xf1;o, Teira, Pontiller, Lundin, Joglar, Pedr&#xf3;s-Ali&#xf3;, Fern&#xe1;ndez, Pinhassi and Mart&#xed;nez-Garc&#xed;a.</copyright-statement>
<copyright-year>2024</copyright-year>
<copyright-holder>Delgadillo-Nu&#xf1;o, Teira, Pontiller, Lundin, Joglar, Pedr&#xf3;s-Ali&#xf3;, Fern&#xe1;ndez, Pinhassi and Mart&#xed;nez-Garc&#xed;a</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/">
<p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p>
</license>
</permissions>
<abstract>
<p>Coastal upwelling areas are extraordinarily productive environments where prokaryotic communities, the principal remineralizers of dissolved organic matter (DOM), rapidly respond to phytoplankton bloom and decay dynamics. Nevertheless, the extent of variability of key microbial functions in such dynamic waters remains largely unconstrained. Our metatranscriptomics analyses of 162 marker genes encoding ecologically relevant prokaryotic functions showed distinct spatial-temporal patterns in the NW Iberian Peninsula upwelling area. Short-term (daily) changes in specific bacterial functions associated with changes in biotic and abiotic factors were superimposed on seasonal variability. Taxonomic and functional specialization of prokaryotic communities, based mostly on different resource acquisition strategies, was observed. Our results uncovered the potential influence of prokaryotic functioning on phytoplankton bloom composition and development (e.g., <italic>Cellvibrionales</italic> and <italic>Flavobacteriales</italic> increased relative gene expression related to vitamin B12 and siderophore metabolisms during <italic>Chaetoceros</italic> and <italic>Dinophyceae</italic> summer blooms). Notably, bacterial adjustments to C- or N-limitation and DMSP availability during summer phytoplankton blooms and different spatial-temporal patterns of variability in the expression of genes with different phosphate affinity indicated a complex role of resource availability in structuring bacterial communities in this upwelling system. Also, a crucial role of <italic>Cellvibrionales</italic> in the degradation of DOM (carbohydrate metabolism, TCA cycle, proteorhodopsin, ammonium, and phosphate uptake genes) during the summer phytoplankton bloom was found. Overall, this dataset revealed an intertwined mosaic of microbial interactions and nutrient utilization patterns along a spatial-temporal gradient that needs to be considered if we aim to understand the biogeochemical processes in some of the most productive ecosystems in the world&#xb4;s oceans.</p>
</abstract>
<kwd-group>
<kwd>bacterioplankton</kwd>
<kwd>upwelling systems</kwd>
<kwd>phytoplankton bloom</kwd>
<kwd>metatranscriptomics</kwd>
<kwd>metabarcoding</kwd>
</kwd-group>
<contract-num rid="cn001">CTM2014-59031-P, CTM2017-83362-R, PID2019-110011RB-C33, PRE2018-085871</contract-num>
<contract-sponsor id="cn001">Ministerio de Econom&#xed;a y Competitividad<named-content content-type="fundref-id">10.13039/501100003329</named-content>
</contract-sponsor>
<counts>
<fig-count count="6"/>
<table-count count="0"/>
<equation-count count="0"/>
<ref-count count="97"/>
<page-count count="17"/>
<word-count count="8227"/>
</counts>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-in-acceptance</meta-name>
<meta-value>Aquatic Microbiology</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="s1" sec-type="intro">
<title>Introduction</title>
<p>Coastal upwelling areas are complex and dynamic environments where winds displace surface water off the coast, allowing nutrient-rich deep water to reach the surface and driving remarkable productivity at all trophic levels (ultimately sustaining major portions of global fisheries) (<xref ref-type="bibr" rid="B41">K&#xe4;mpf and Chapman, 2016</xref>; <xref ref-type="bibr" rid="B83">Stock et&#xa0;al., 2017</xref>) [see K&#xe4;mpf, J. and Chapman, P 2016 and references therein]. Bacterioplankton is a crucial component of the ocean biome that has long been recognized for its principal role in regulating the biogeochemical cycling of carbon (<xref ref-type="bibr" rid="B74">Rivkin and Legendre, 2001</xref>), but also the remineralization and utilization of elements like N and P that are vital for ocean productivity (<xref ref-type="bibr" rid="B15">Caron, 1994</xref>). Moreover, recent findings emphasize the role of bacteria and their interactions with phytoplankton in providing vitamins and growth factors necessary for organisms throughout the food web (<xref ref-type="bibr" rid="B80">Shilova et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B5">Amin et&#xa0;al., 2015</xref>). Still, the specific adjustments in bacterial metabolism that regulate such processes in upwelling areas, and the taxa involved, remain largely unexplored.</p>
<p>The usage of &#x2018;meta-omics&#x2019; techniques has allowed the scientific community to gain comprehensive understanding on the succession of specific prokaryotic taxa and their metabolisms operating during the evolution of phytoplanton blooms. Thus, a recent study based on mesocosm experiments carried out in summer in the NW Iberian Peninsula upwelling system, showed important daily changes in the transcription of glycoside hydrolases, peptidases, and transporters, supporting the hypothesis that resource partitioning is affected by temporal changes in the availability of dissolved organic matter (DOM) (<xref ref-type="bibr" rid="B69">Pontiller et&#xa0;al., 2022</xref>). Similarly, recurrent patterns at the functional level, particularly regarding substrate-induced responses, have been observed throughout bacterioplankton succession during phytoplankton blooms in the southern North Sea (<xref ref-type="bibr" rid="B85">Teeling et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B86">Teeling et&#xa0;al., 2016</xref>) and in the Monterey upwelling system (<xref ref-type="bibr" rid="B59">Nowinski and Moran, 2021</xref>). Although geographically distant, there are interesting similarities in the involvement of bacterial taxa in these studies, with pronounced contributions of <italic>Flavobacteriaceae</italic> (<italic>Bacteroidota</italic>; recognized for their polymer degrading capacities) along with <italic>Alphaproteobacteria</italic> (e.g. <italic>Roseobacter</italic>) and <italic>Gammaproteobacteria</italic> (e.g. <italic>Alteromonadales</italic> and <italic>Cellvibrionales</italic>) that differ in preference for different quantity and quality of resources. Nevertheless, and surprisingly, little is known about the temporal shifts in the functional profiles of different bacteria associated with changes in nutrient availability, hydrodynamic conditions, or phytoplankton community composition and activity along the coast to offshore spatial gradient in upwelling systems.</p>
<p>The environmental conditions for life in upwelling areas vary substantially along both spatial and temporal dimensions (<xref ref-type="bibr" rid="B41">K&#xe4;mpf and Chapman, 2016</xref>). A key axis in the spatial structuring of upwelling ecosystems is the transition from the coastal zone, where the upwelling occurs, to offshore areas, where surface waters are displaced over time. This axis is strongly influenced by different coastal features like interactions between winds and the coastal topography (<xref ref-type="bibr" rid="B26">Figueiras et&#xa0;al., 2002</xref>), potential riverine inputs (<xref ref-type="bibr" rid="B89">Teixeira et&#xa0;al., 2018</xref>), and tidal forcing (<xref ref-type="bibr" rid="B82">Souto et&#xa0;al., 2001</xref>), generating spatial heterogeneity at various scales. In this regard, <xref ref-type="bibr" rid="B79">Satinsky et&#xa0;al. (2017)</xref> suggested that changes in microbial element cycling along the coastal system of the Amazon River Plume are largely associated with shifts in specific metabolisms. Accordingly, important spatial and temporal variability in the structure and function of microbial communities in large and heterogeneous upwelling areas can be expected (<xref ref-type="bibr" rid="B94">Zdanowski and Figueiras, 1997</xref>; <xref ref-type="bibr" rid="B7">Ar&#xed;stegui et&#xa0;al., 2009</xref>; <xref ref-type="bibr" rid="B19">Cury et&#xa0;al., 2011</xref>; <xref ref-type="bibr" rid="B10">Bertrand and Allen, 2012</xref>; <xref ref-type="bibr" rid="B37">Joglar et&#xa0;al., 2021a</xref>).</p>
<p>Short-term variability in wind regimes superimposed on seasonality induces patchiness in the prevalence of upwelling and downwelling events (typically 2-5 days (<xref ref-type="bibr" rid="B68">Pisareva et&#xa0;al., 2019</xref>)), particularly in the coastal zone (<xref ref-type="bibr" rid="B11">Blanton et&#xa0;al., 1984</xref>). Measurements of microbial bulk abundance and activity (e.g., production, respiration, enzymatic activities) show that such short-term temporal dynamics are associated with phytoplankton blooms and affect microbial community biomass, activity, and composition (<xref ref-type="bibr" rid="B82">Souto et&#xa0;al., 2001</xref>). The spatial and temporal scales of variability of phytoplankton growth and microbial food web functioning in upwelling systems are, therefore, inherently complex (<xref ref-type="bibr" rid="B42">Kerkhof et&#xa0;al., 1999</xref>; <xref ref-type="bibr" rid="B8">Barbosa et&#xa0;al., 2001</xref>; <xref ref-type="bibr" rid="B9">Bergen et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B92">Wear et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B34">Hern&#xe1;ndez-Ruiz et&#xa0;al., 2018</xref>), and constraining this complexity remains an important challenge.</p>
<p>The coastal area of the NW Iberian Peninsula is a highly dynamic and productive ecosystem, characterized by a light&#x2013;limited winter and a nutrient&#x2013;limited summer period, and by diatom and dinoflagellate blooms during spring and autumn, respectively (<xref ref-type="bibr" rid="B27">Figueiras and R&#xed;os, 1993</xref>). On top of these seasonal patterns, this region is affected by the intermittent upwelling of cold and inorganic nutrient-rich Eastern North Atlantic Central Water (<xref ref-type="bibr" rid="B58">Nogueira et&#xa0;al., 1997</xref>). Although upwelling-favorable northerly winds prevail from March to September and downwelling-favorable southerly winds the rest of the year, out-of-season upwelling or downwelling events have been frequently recorded. During downwelling periods, surface, nutrient-poor seawater moves from the ocean to the coast. The extensive knowledge of the physical, chemical, and biological oceanography in the area provides a solid background against which to assess aspects of the microbial ecology (<xref ref-type="bibr" rid="B82">Souto et&#xa0;al., 2001</xref>; <xref ref-type="bibr" rid="B26">Figueiras et&#xa0;al., 2002</xref>; <xref ref-type="bibr" rid="B88">Teira et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B89">Teixeira et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B37">Joglar et&#xa0;al., 2021a</xref>). Thus, we approached this ecosystem with the objective of refining our understanding of microbial and biogeochemical processes in upwelling areas. In the current work we aimed to capture the range of variability in frequencies and amplitudes of key microbial functions. Our comparative metatranscriptome analysis comprised a collection of 162 genes previously used as informative markers for nutrient (e.g., C, N, P, S, Fe) fluxes and microbial metabolism (e.g., response to stimuli and stress, phototrophy, and synthesis of vitamins) (<xref ref-type="bibr" rid="B78">Satinsky et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B75">Robidart et&#xa0;al., 2019</xref>) and covered different oceanographic and biological settings. We hypothesized that short-term oceanographic features as wells as differences in upwelling intensity between coastal and offshore areas will have distinct effects on the diverse set of key microbial functions studied.</p>
</sec>
<sec id="s2">
<title>Methods</title>
<sec id="s2_1">
<title>Study site and sampling</title>
<p>Three 10-day cruises were conducted on board B/O Ram&#xf3;n Margalef in February (winter), April (spring), and August (summer) 2016 to cover a wide range of hydrographic and ecological conditions. Samples were taken at two locations in the eastern Atlantic Ocean, in the upwelling system near the R&#xed;a de Vigo: the Coastal station (88 m depth, 42.14&#xb0; N, 8.95&#xb0; W, sampled between 8:00 and 8:20 am) and the Offshore station (260 m depth, 42.10&#xb0; N, 9.60&#xb0; W, sample between 6:30 and 6:45pm) (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1A</bold>
</xref>). It is important to note that the different time of sampling may have biased the metatranscriptome comparisons between both sampling stations, as it has been previously shown that prokaryotic transcriptomes from natural samples may exhibit diel periodicity, particularly those of <italic>Cyanobacteria</italic> in open ocean waters (<xref ref-type="bibr" rid="B62">Ottesen et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B63">Ottesen et&#xa0;al., 2014</xref>).</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>
<bold>(A)</bold> Map showing bathymetry and sampling locations (coastal and offshore) in NW Iberian Peninsula. <bold>(B)</bold> Temporal evolution of salinity, temperature, chlorophyll a, bacterial abundance, nitrate (NO<sub>3</sub>
<sup>-</sup>), ammonium (NH&#x2084;&#x207a;), phosphate (PO&#x2084;&#xb3;&#x207b;), N:P ratio (calculated as the sum of NO<sub>3</sub>
<sup>-</sup>, NO<sub>2</sub>
<sup>-</sup> and NH&#x2084;&#x207a;divided by PO&#x2084;&#xb3;&#x207b;), and silicate (SiO<sub>2</sub>) at surface (5m) during winter (blue), spring (red) and summer (green) at surface (5m) at days 1, 3, 5 and 7 at the offshore and coastal stations.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-10-1259783-g001.tif"/>
</fig>
<p>Detailed information on the experimental setup and specific methods below are given in <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Material</bold>
</xref>.</p>
</sec>
<sec id="s2_2">
<title>Hydrographic survey</title>
<p>Vertical profiles of temperature (&#xb0;C), salinity, turbidity (NTU), total chlorophyll fluorescence, and photosynthetically active radiation (PAR) were obtained using a Seabird CTD rosette. Inorganic-nutrient determinations of collected water were done with a Bran + Luebbe segmented flow analyzer (<xref ref-type="bibr" rid="B32">Hansen and Grasshoff, 1983</xref>).</p>
</sec>
<sec id="s2_3">
<title>Chlorophyll <italic>a</italic> and prokaryotic abundance</title>
<p>Chlorophyll a (Chl-<italic>a</italic>) concentration was measured by the non-acidification technique as a phytoplankton biomass proxy (<xref ref-type="bibr" rid="B93">Welschmeyer, 1994</xref>). Fluorescence was determined with a TD-700 Turner Designs fluorometer (absorption coefficient as 87.7 at 663 nm) (<xref ref-type="bibr" rid="B51">Lorenzen and Newton Downs, 1986</xref>). Prokaryotic abundance in seawater samples was calculated as described by <xref ref-type="bibr" rid="B29">Gasol and Del Giorgio (2000)</xref> using a Becton Dickinson FACSCalibur flow cytometer (488 nm light produced by argon&#x2010;ion laser).</p>
</sec>
<sec id="s2_4">
<title>Microbial community composition</title>
<p>Community composition was assessed from 24 samples by sequencing the 16S rRNA gene for prokaryotes and the 18S rRNA gene for eukaryotes (0.22 - 3&#xb5;m size-fraction and &gt; 3&#xb5;m size-fraction, respectively). DNA was amplified using the universal primers 515F and 926R for prokaryotes (<xref ref-type="bibr" rid="B65">Parada et&#xa0;al., 2016</xref>) and TAReuk454FWD1 and TAReukREV3 for eukaryotes (<xref ref-type="bibr" rid="B50">Logares et&#xa0;al., 2014</xref>). Amplified regions were sequenced in an Illumina Miseq platform. The sequencing depth for amplicon 16S and 18S was 10,000 reads per sample The sequences obtained were analyzed with the software DADA2 for amplicon sequence variants (ASVs) (<xref ref-type="bibr" rid="B14">Callahan et&#xa0;al., 2016</xref>) using the SILVA reference database (v138.1) for taxonomic assignment of 16S (<xref ref-type="bibr" rid="B72">Quast et&#xa0;al., 2013</xref>), and the databases PR2 (<xref ref-type="bibr" rid="B31">Guillou et&#xa0;al., 2012</xref>) and the marine protist from the BioMarKs project (<xref ref-type="bibr" rid="B54">Massana et&#xa0;al., 2015</xref>) for taxonomic assignment of 18S ASVs.</p>
</sec>
<sec id="s2_5">
<title>Metatranscriptomic analyses: prokaryotic community gene expression</title>
<p>RNA samples (&lt; 3&#xb5;m size-fraction) were taken during the experimental period at the surface in the coastal and oceanic stations (a total of 24 samples). Sampling for gene expression analyses was carried out on days 1, 3, 5, and 7 of each cruise. mRNA samples were extracted and sequenced using Illumina Miseq sequencing technology at the Science for Life Laboratory in Stockholm (SciLifeLab; <ext-link ext-link-type="uri" xlink:href="http://www.scilifelab.se">www.scilifelab.se</ext-link>). The sequencing depth was 70,000 sequences. Illumina HiSeq 2500 raw paired-end reads (2x125bp) were quality checked with FastQC and MultiQC (<xref ref-type="bibr" rid="B24">Ewels et&#xa0;al., 2016</xref>), primer sequences were removed with cutadapt (<xref ref-type="bibr" rid="B52">Marcel, 2011</xref>), reads were trimmed with Sickle (<xref ref-type="bibr" rid="B40">Joshi and Fass, 2011</xref>) and filtered with ERNE (<xref ref-type="bibr" rid="B21">Del Fabbro et&#xa0;al., 2013</xref>) against a &#x201c;contamination reference&#x201d; database to filter reads designated as artifacts. Subsequently, forward and reverse reads were merged with PEAR (<xref ref-type="bibr" rid="B95">Zhang et&#xa0;al., 2014</xref>). All Merged reads were aligned with DIAMOND (<xref ref-type="bibr" rid="B12">Buchfink et&#xa0;al., 2014</xref>) against the NCBI RefSeq protein database (<xref ref-type="bibr" rid="B60">O&#x2019;Leary et&#xa0;al., 2016</xref>). Afterward, all the sequences were compared to the 162 protein families (Pfams and TIGRfams) by running MEGAN (<xref ref-type="bibr" rid="B35">Huson et&#xa0;al., 2016</xref>) to annotate taxonomy and all possible transcripts to select marker genes relevant to a variety of ecological processes. The 162 genes found out of the 198 target protein profiles were grouped into nine categories and 44 subcategories (<xref ref-type="supplementary-material" rid="SM1">
<bold>Table S1</bold>
</xref>). To make comparisons between samples, considering that the transcripts have different lengths, and the libraries differ in size, we used a Transcript Per Million (TPM) normalization.</p>
</sec>
<sec id="s2_6">
<title>Statistical analyses</title>
<p>Non-parametric Mann-Whitney U Test analyses were performed to compare the salinity, nutrient concentrations, bacterial abundance and chlorophyll a concentration during the different seasons at both stations. T-tests analyses were performed to compare the contribution of each taxonomical group to the 16S dataset and to the metatranscriptome. To test the null hypothesis that data came from a normally distributed population, a Kolmogorov-Smirnov &amp; Lillierors test was used.</p>
<p>Analysis of Non-parametric MultiDimensional Scaling (nMDS) and PERmutational Multivariate ANalysis Of VAriance (PERMANOVA) were used to test the grouping of metatranscriptomes by seasons and stations. ReDundancy Analyses (RDA) were applied to show the variability in the metatranscriptomes that is explained by environmental data and by the composition of phytoplankton and bacteria communities and PERMANOVA was used to test the significance of explanatory variables.</p>
<p>A Benjamini-Hochberg correction was applied to the Spearman rank correlation analyses.</p>
</sec>
</sec>
<sec id="s3" sec-type="results">
<title>Results</title>
<sec id="s3_1">
<title>Physicochemical and biological conditions</title>
<p>The results of the hydrographic surveys showed that downwelling conditions prevailed during winter and spring (<xref ref-type="fig" rid="f1">
<bold>Figures&#xa0;1B</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S1</bold>
</xref>&#x2013;<xref ref-type="supplementary-material" rid="SM1">
<bold>S2</bold>
</xref>). During this period, the important vertical mixing and reduced light availability prevented phytoplankton blooms and relatively high concentrations of inorganic nutrients were measured in surface waters (NO<sub>3</sub>
<sup>-</sup>, NO<sub>2</sub>
<sup>-</sup>and SiO<sub>2</sub> concentrations and the N:P ratio during winter and spring at both stations were significantly higher than those measured in summer, Mann-Whitney U Test, p-value &lt; 0.05; <xref ref-type="supplementary-material" rid="SM1">
<bold>Table S2</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S3</bold>
</xref>). At the coastal station, a persistent surface halocline associated with rain and terrestrial runoff was observed during winter and spring (during winter and spring surface salinity was significantly lower than during summer, Mann-Whitney U Test, p-value &lt; 0.05) (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figures S1</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S3</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>Table S2</bold>
</xref>). By contrast, during summer, the upwelling brought deep, salty, and nutrient-rich water to the surface. In summer, a massive phytoplankton bloom was observed at the coast and spread to the offshore station: at the surface significantly higher Chl<italic>-a</italic> concentrations accompanied by significantly higher bacterial abundance were measured compared to spring and winter (Mann-Whitney U Test, p-value &lt; 0.05) (see satellite images, <xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S4</bold>
</xref>). The observed very low nutrients concentrations during summer in surface waters at the coastal station are probably due to the massive consumption of nutrients by the phytoplankton bloom (<xref ref-type="fig" rid="f1">
<bold>Figures&#xa0;1B</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S1</bold>
</xref>&#x2013;<xref ref-type="supplementary-material" rid="SM1">
<bold>S3</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>Table S2</bold>
</xref>). At the coastal station, pronounced changes in Chl<italic>-a</italic> concentration were observed at the end of the winter cruise (<xref ref-type="fig" rid="f1">
<bold>Figures&#xa0;1B</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S1</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S5</bold>
</xref>) and even more so, at the end of the summer cruise (likely due to the rapid wind relaxation that interrupted the upwelling and disrupted the bloom (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S1</bold>
</xref>), see Joglar et&#xa0;al., 2020 (<xref ref-type="bibr" rid="B39">Joglar et&#xa0;al., 2020</xref>). Collectively, there was more daily variation in physicochemical and biological oceanographic conditions (e.g. salinity, nutrients, chlorophyll a and bacterial biomass) in the coastal compared to the offshore and in summer compared to winter (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figures S1</bold>
</xref>&#x2013;<xref ref-type="supplementary-material" rid="SM1">
<bold>S3</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S5</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>Table S2</bold>
</xref>). An interesting exception to this was temperature, which registered a similar large daily variation in the offshore and coastal stations in summer due to the intense upwelling of cold water that precisely promoted the changes in the rest of variables.</p>
<p>The eukaryotic community at both stations was dominated by dinoflagellates and diatoms (<italic>Dinophyceae</italic>, <italic>Thalassiosira</italic>, and <italic>Chaetoceros</italic>, particularly in summer) (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S6A</bold>
</xref>) (<xref ref-type="bibr" rid="B39">Joglar et&#xa0;al., 2020</xref>). Among the bacteria, <italic>Pelagibacterales</italic> and <italic>Synechococcales</italic> showed higher relative proportions at the offshore station, particularly in winter, while other <italic>Alphaproteobacteria</italic> and <italic>Flavobacteria</italic> reached higher relative abundances in spring and summer on the coast. At both stations, <italic>Oceanospirillales</italic> were relatively more abundant in winter, whereas <italic>Cellvibrionales</italic> increased in summer (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S6B</bold>
</xref>) (<xref ref-type="bibr" rid="B39">Joglar et&#xa0;al., 2020</xref>).</p>
</sec>
<sec id="s3_2">
<title>Relationships between metatranscriptomes and environment variables</title>
<p>Our metatranscriptomics analysis showed a dominance by <italic>Alphaproteobacteria</italic> (mainly <italic>Pelagibacterales</italic> and <italic>Rhodobacterales</italic>), <italic>Gammaproteobacteria</italic> (including <italic>Alteromonadales</italic> and <italic>Cellvibrionales</italic>), and <italic>Bacteroidota</italic> (mainly <italic>Flavobacteriales</italic>) in both stations and in the three sampled seasons (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2A</bold>
</xref>). The taxonomic distribution of transcripts for functional genes was similar in winter and spring, except for higher levels of <italic>Cyanobacteria</italic> at the offshore station in winter. During the summer phytoplankton bloom at the coastal station there was an important increase in the relative transcription levels of <italic>Cellvibrionales</italic> (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2A</bold>
</xref>). A relatively higher representation in the metatranscriptomics than in the DNA-based 16S rRNA gene amplicon data was observed for both <italic>Pelagibacterales</italic> (offshore station) and Other <italic>Gammaproteobacteria</italic> and <italic>Cellvibrionales</italic> (coastal station) during the three different seasons (t-test, p-value &lt; 0.05) (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S7</bold>
</xref>).</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>
<bold>(A)</bold> Contribution of the major taxonomic groups to the bacterial metatranscriptome at surface (5m) during winter (WIN), spring (SPG) and summer (SUM) at the coastal and offshore stations. The mean of four replicates (days 1, 3, 5 and 7) per station and season is shown. Redundancy analysis (RDA) of bacterioplankton metatranscriptome data constrained by: <bold>(B)</bold> environmental variables, <bold>(C)</bold> relative abundances of main eukaryotic groups (18S), and <bold>(D)</bold> prokaryotic groups (16S). The metatranscriptome data was clr-transformed to calculate Euclidean distances and to perform the RDA. A PERMANOVA analysis (p-values provided in each plot) was conducted to determine the significance of the analysis. Black arrows indicate the variables that significantly constrain each model. The percentages representing variability are displayed on the axes. Circles: coast, triangles: offshore. Winter: blue, spring: red and, summer: green.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-10-1259783-g002.tif"/>
</fig>
<p>Analysis of Non-parametric MultiDimensional Scaling (nMDS) and PERmutational Multivariate ANalysis Of VAriance (PERMANOVA) of bacterioplankton metatranscriptomes revealed a grouping of samples based on seasons and sampling stations (PERMANOVA, p-value &lt; 0.05) (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S8</bold>
</xref>). Redundancy Analysis (RDA) showed that functional profiles of winter and spring bacterial communities from both stations were significantly (PERMANOVA, p-value &lt; 0.001) associated with high concentrations of specific nutrients (NO<sub>3</sub>
<sup>-</sup> and SiO<sub>2</sub>) and with fairly high relative abundances (estimated from DNA-based 16S rRNA gene amplicon data presented in <xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S6</bold>
</xref>) of the eukaryotic phytoplankton <italic>Ciliophora</italic>, <italic>Cryptophyceae</italic>, and <italic>Dictyophiceae</italic> (PERMANOVA, p-value &lt; 0.005) and the bacteria <italic>Oceanospirillales</italic>, <italic>Pelagibacterales</italic>, and <italic>Alphaproteobacteria</italic> (PERMANOVA, p-value &lt; 0.001) (<xref ref-type="fig" rid="f2">
<bold>Figures&#xa0;2B&#x2013;D</bold>
</xref>). During the summer bloom, the bacterial functional profiles showed higher variability and
appeared to be linked to increased bacterial abundance, Chl-<italic>a</italic> concentration, PO<sup>3</sup>, and NH<sub>4</sub>
<sup>+</sup> concentration (PERMANOVA, p-value &lt; 0.001) as well as with <italic>Chaetoceros</italic>, <italic>Dinophyceae</italic>, and Fungi at both stations (PERMANOVA, p-value &lt; 0.005) (<xref ref-type="fig" rid="f2">
<bold>Figures&#xa0;2B&#x2013;D</bold>
</xref>). At the offshore station, bacterial functioning during summer was associated with high relative abundances of <italic>Amylibacter</italic>, <italic>Flavobacteriales</italic>, and <italic>Rhodobacterales</italic> (PERMANOVA, p-value &lt; 0.001), while at the coastal station, it was associated with higher numbers of <italic>Cellvibrionales</italic> (PERMANOVA, p&lt;0.001) (<xref ref-type="fig" rid="f2">
<bold>Figures&#xa0;2B&#x2013;D</bold>
</xref>).</p>
</sec>
<sec id="s3_3">
<title>Spatial-temporal variability in expression of ecological marker genes</title>
<p>We next assessed the microbial functions related to nutrient fluxes (C, N, P, S, and Fe) and to vitamin synthesis, response to stress and stimuli, and phototrophy in this upwelling system. Different seasonal (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S9</bold>
</xref>&#x2013;<xref ref-type="supplementary-material" rid="SM1">
<bold>S17</bold>
</xref>), daily (<xref ref-type="fig" rid="f4">
<bold>Figures&#xa0;4</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S18</bold>
</xref>&#x2013;<xref ref-type="supplementary-material" rid="SM1">
<bold>S23</bold>
</xref>) and spatial patterns were observed in the different functions studied.</p>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p>Relative transcript abundance (TPM) of selected key biological process: carbohydrate metabolism, TCA cycle, amino acid metabolism, ammonium uptake, phosphate metabolism, DMSP assimilation, siderophore metabolism, iron storage, vitamins, motility, photosynthesis, and proteorhodopsin. Color bars represent the relative contribution of main taxonomic groups to transcription at the costal and offshore station during winter (WIN), spring (SPG), and summer (SUM). The mean of four replicates (days 1, 3, 5 and 7) is shown. Note that different number of genes are included in each category (see supplementary material) and that different scales are used on the y-axis.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-10-1259783-g003.tif"/>
</fig>
<fig id="f4" position="float">
<label>Figure&#xa0;4</label>
<caption>
<p>Daily variability of selected genes at the costal and offshore stations during winter (WIN), spring (SPG), and summer (SUM). Relative transcript abundance (TPM) of selected key biological process is provided. Color bars represent the relative contribution of main taxonomic groups to transcription. The value for each sampling day (days 1, 3, 5 and 7) is shown. Note that different scales are used on the y-axis.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-10-1259783-g004.tif"/>
</fig>
<sec id="s3_3_1">
<title>Carbon, nitrogen and phosphorous metabolisms</title>
<p>In the carbon metabolism category, high relative transcription of carbohydrate metabolism and TCA cycle genes, particularly by <italic>Cellvibrionales</italic> and some <italic>Alphaproteobacteria</italic>, was observed in both stations as the seasons progressed, with higher values in summer during the phytoplankton bloom (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S9</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S18</bold>
</xref>). Isocitrate dehydrogenase (<italic>icd</italic>) and succinate dehydrogenase (<italic>sdhA</italic>) were the TCA cycle genes with highest relative transcription (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figures S9</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S18</bold>
</xref>). While <italic>icd</italic>, (which produces 2-oxoglutarate, also a precursor in amino acid metabolism, see below) was mainly transcribed by <italic>Gammaproteobacteria</italic> (<italic>Cellvibrionales</italic>), <italic>sdhA</italic> was transcribed by several taxa, including <italic>Bacteroidetes</italic> (<italic>Flavobacteriales</italic>) and <italic>Gammaproteobacteria</italic> at the coast and <italic>Alphaproteobacteria</italic> (<italic>Pelagibacterales</italic>) at the offshore (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figures S9</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S18</bold>
</xref>).</p>
<p>In the nitrogen metabolism category, ammonium uptake and amino acid metabolism were the subcategories with the highest proportion of transcripts, while urea utilization and nitrogen fixation remained low (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S10</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S18</bold>
</xref>). There were pronounced seasonal changes in the relative expression of ammonium transporter (<italic>amt</italic>) genes (increasing from winter to summer, when low ammonium concentrations were measured during the phytoplankton bloom in the coast) and different taxa contributed to the transcription of <italic>amt-1 (</italic>mainly <italic>Cellvibrionales</italic>) and <italic>amt-2</italic> (<italic>Pelagibacterales</italic> and <italic>Rhizobiales)</italic> (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figures S10</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S18</bold>
</xref>). The dominant genes in amino acid metabolism were also involved in nitrogen assimilation, such as the <italic>glnA</italic> gene, also importantly transcribed by <italic>Cellvibrionales</italic> and encoding glutamine synthetase that is the key enzyme that catalyzes the incorporation of ammonium or amino groups from amino acids into glutamine, and the global nitrogen-metabolism regulatory protein P-II (<italic>glnB</italic>) that modulates the expression of both glutamine synthetase and ammonium transporter genes (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figures S10</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S18</bold>
</xref>).</p>
<p>The phosphorus metabolism category was dominated by the expression of genes for phosphate metabolism, with higher relative values in spring and summer than in winter, especially at the coast (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S11</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S18</bold>
</xref>). <italic>Pelagibacterales</italic> and <italic>Rhodobacterales</italic> (offshore and coastal station, respectively) and <italic>Gammaproteobacteria</italic> (particularly <italic>Cellvibrionales</italic> in summer at the coast) were the main groups accounting for this expression (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S11</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S18</bold>
</xref>). Thus, phosphate import ATP-binding protein (<italic>pstB</italic>) was mainly transcribed by <italic>Pelagibacterales</italic> at the offshore station and by <italic>Rhodobacterales</italic> and <italic>Cellvibrionales</italic> at the coast and the transcription (mainly by <italic>Cellvibrionales</italic>) of the high affinity phosphate transporter <italic>pstS</italic> relatively increased in the coast in summer, while the low-affinity phosphate transporter (<italic>pit</italic>), which peaked in spring at the coast, was mainly transcribed by <italic>Gammaproteobacteria</italic> at both stations (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figures S11</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S18</bold>
</xref>).</p>
<p>Several of the C, N and P metabolism genes at both stations showed important daily changes in relative transcription levels over the course of the 7-day cruises (particularly during summer at both stations, <xref ref-type="supplementary-material" rid="SM1">
<bold>Figures S21</bold>
</xref>&#x2013;<xref ref-type="supplementary-material" rid="SM1">
<bold>S23</bold>
</xref>) coinciding with short-term oceanographic variability (<xref ref-type="fig" rid="f5">
<bold>Figures&#xa0;5</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S5</bold>
</xref>). As an example, individual phosphate acquisition genes showed different dynamics during the last part of the summer cruise at the coastal station (i.e., <italic>pstB</italic> increased while <italic>pstS</italic> decreased) and during winter and spring at the coastal station (i.e., <italic>pit</italic>, <italic>pstB</italic>, <italic>pstS</italic>) (<xref ref-type="fig" rid="f4">
<bold>Figures&#xa0;4</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S21</bold>
</xref>), coinciding with changes in phosphate availability in the field (<xref ref-type="fig" rid="f1">
<bold>Figures&#xa0;1</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S5</bold>
</xref>). Interestingly, daily changes (calculated as the ratio of the daily value divided by the mean value during the four days of the specific season and station) in PO<sub>4</sub>&#xb3;<sup>-</sup>concentration observed in the field were inversely correlated with the day-to-day changes in <italic>amt1, amt2, glnA, glnB, zwf, icd, pstS</italic>, and <italic>cobG</italic> (p &lt; 0.05) (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5</bold>
</xref>). It is important to note here that daily changes in the N/P ratio were mostly driven by changes in NO<sub>3</sub>
<sup>-</sup> concentrations and not in PO<sub>4</sub>
<sup>-3</sup> availability (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1B</bold>
</xref>). On the other hand, daily changes in bacterial biomass were inversely correlated with the day-to-day changes in <italic>icd, zwf, glnB</italic> and <italic>amt2</italic> and directly correlated with those in <italic>sdhA, pit, dmdA1</italic> and <italic>fbpA</italic> (p &lt; 0.05) (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5</bold>
</xref>). Finally, daily changes in temperature were directly correlated with the day-to-day changes in <italic>icd</italic>, <italic>zwf</italic>, <italic>amt1</italic>, <italic>amt2</italic>, <italic>glnA</italic>, <italic>glnB</italic> and <italic>pstS</italic> and inversely correlated with those in <italic>pit</italic> (p &lt; 0.05) (<xref ref-type="fig" rid="f5">
<bold>Figure&#xa0;5</bold>
</xref>).</p>
<fig id="f5" position="float">
<label>Figure&#xa0;5</label>
<caption>
<p>
<bold>(A)</bold> Daily variability (estimated as the ratio of the daily value of each variable divided by the mean value of that variable during the four days of the specific season and station) of phosphate (PO&#x2084;&#xb3;&#x207b;) and of <italic>pstB</italic> transcripts measured at the costal and offshore stations during winter (WIN), spring (SPG), and summer (SUM). The color and the vertical position of the bubble (y-axis) represent the value of the ratio <bold>(B)</bold> Correlation between values presented in panel <bold>(A)</bold>, Spearman coefficient and p-value of the correlation are provided. <bold>(C)</bold> Spearman rank correlation analysis between daily variability of the different environmental variables and that of selected genes. A Benjamini-Hochberg method was used to adjust the p-values. Dots indicate p &lt; 0.05. NP stands for N:P ratio.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-10-1259783-g005.tif"/>
</fig>
</sec>
<sec id="s3_3_2">
<title>Sulfur, iron and vitamin metabolisms</title>
<p>Dimethylsulfoniopropionate (DMSP) assimilation, especially <italic>Pelagibacterales dmdA1</italic> and <italic>dmdA2</italic> transcription, was the category with the highest relative expression levels of all categories studied (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3</bold>
</xref>, <xref ref-type="fig" rid="f4">
<bold>4</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S12</bold>
</xref>). A large peak in DMSP assimilation was observed in summer at the offshore station coinciding with a relative increase in the contribution of <italic>Dinophyceae</italic> to the eukaryotic community (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S6</bold>
</xref>). Large short-term changes were observed in the transcription of DMSP assimilation genes during the final phase of the summer cruise at both the coastal and offshore stations (<xref ref-type="fig" rid="f4">
<bold>Figures&#xa0;4</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S19</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S22</bold>
</xref>). Relative expression of genes for sulfite and sulfate assimilation also reached fairly high levels, accounted for by <italic>Pelagibacterales</italic> and <italic>Gammaproteobacteria</italic> for sulfite (e.g., adenylsulfate reductase genes <italic>aprAB</italic>) and by a variety of taxa for sulfate (e.g., <italic>cysN</italic>) (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S12</bold>
</xref>). <italic>Synechococcales</italic> and <italic>Cellvibrionales</italic> increased their relative contribution to <italic>cysN</italic> transcription in winter at the offshore station and during the summer bloom at the coastal station, respectively (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S12</bold>
</xref>).</p>
<p>Iron metabolism genes were transcribed by various taxa, including <italic>Cellvibrionales</italic>, <italic>Flavobacteriales</italic>, and <italic>Synechococcales</italic> (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3</bold>
</xref>, <xref ref-type="fig" rid="f4">
<bold>4</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S13</bold>
</xref>). The relative transcription of iron storage genes increased at the offshore station during winter and spring. In contrast, pronounced relative increases in siderophore transport (e.g., <italic>exbB</italic> by <italic>Cellvibrionales</italic>), and ferric uptake were observed at the coast during summer and spring, respectively (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3</bold>
</xref>, <xref ref-type="fig" rid="f4">
<bold>4</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S13</bold>
</xref>). The expression of ferric ion uptake genes (e.g., <italic>fbpA</italic>) was mainly associated with <italic>Pelagibacterales</italic>, while iron storage genes (e.g., <italic>ftnA</italic>) were mostly associated with <italic>Synechococcales</italic> (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3</bold>
</xref>, <xref ref-type="fig" rid="f4">
<bold>4</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S13</bold>
</xref>). Interestingly, day-to-day changes in expression of iron uptake (i.e., <italic>fbpAB</italic>) and storage (<italic>ftnA</italic>) genes during the summer bloom at the coastal station showed opposite patterns (<xref ref-type="fig" rid="f4">
<bold>Figures&#xa0;4</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S19</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S22</bold>
</xref>).</p>
<p>Vitamin synthesis marker genes selected were on one hand, <italic>thiL</italic> and <italic>thiC</italic> as marker genes of B1 synthesis metabolism and, on the other hand, <italic>cbiX</italic> (as marker gene of the anaerobic pathway) and, <italic>cobG</italic>, <italic>cobN</italic> and <italic>cobT</italic> (as marker genes of the aerobic pathway) for B12 synthesis metabolism. Vitamin synthesis genes generally showed higher relative expression levels in summer at the offshore station and during spring and summer at the coastal station (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>). Vitamin synthesis genes were mainly related to <italic>Alphaproteobacteria</italic> (mostly <italic>Pelagibacterales</italic> at the offshore station), <italic>Gammaproteobacteria</italic> (particularly <italic>Cellvibrionales</italic> at the coastal station<italic>)</italic> and <italic>Synechococcales</italic> and <italic>Flavobacteriales</italic> at the offshore and at the coastal station, respectively (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>). Specific genes related to vitamin synthesis presented different spatial-temporal patterns and were transcribed by different taxonomic groups (<xref ref-type="fig" rid="f4">
<bold>Figures&#xa0;4</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S14</bold>
</xref>). Still, there were marked spatial-temporal patterns for different vitamins and bacterial taxa. For example, vitamin B1 gene <italic>thiL</italic> and B12 gene <italic>cobG</italic> were mainly transcribed by <italic>Cellvibrionales</italic> and <italic>Flavobacteria</italic>, with increased relative transcription in summer, particularly at the coastal station (<xref ref-type="fig" rid="f4">
<bold>Figures&#xa0;4</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S14</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S19</bold>
</xref>). <italic>Pelagibacterales</italic> instead dominated the transcription of vitamin B12 gene <italic>cobT</italic>, particularly at the offshore station during summer (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figures S14</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S19</bold>
</xref>). By contrast, vitamin B12 gene <italic>cbiX</italic> was transcribed by multiple taxa with no clear patterns (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figures S14</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S19</bold>
</xref>). Highest daily variability in the relative transcription of genes related to vitamins was observed during winter at the offshore station (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S22</bold>
</xref>).</p>
</sec>
<sec id="s3_3_3">
<title>Motility, phototrophy and response to stress</title>
<p>Transcription of stress response genes was distributed among <italic>Pelagibacterales</italic> (offshore) and <italic>Cellvibrionales</italic> (coast) and increased at the coastal station in summer and at the offshore station in spring (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figures S15</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S20</bold>
</xref>). The expression of stimuli-related genes (e.g., motility genes like <italic>fliC</italic>) was mostly associated with <italic>Cellvibrionales</italic>, <italic>Alphaproteobacteria</italic>, and <italic>Verrucomicrobia</italic>. (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figures S16</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S20</bold>
</xref>). Highest daily variability in the relative transcription of genes related to response to stress and stimuli were observed during summer at both stations (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S22</bold>
</xref>).</p>
<p>In the phototrophy category, the relative transcription of our selected photosynthesis genes (up to ~5500 TPM; <xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>) was dominated by <italic>Synechococcales</italic> and was generally higher at the offshore station where it peaked in winter (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S17</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S20</bold>
</xref>). This included genes for light harvesting antenna (e.g., <italic>cpcAB</italic> for phycocyanin), the photosystems (<italic>psa</italic> and <italic>psb</italic>) and carbon fixation (rubisco subunits). In contrast to the variability in photosynthesis genes, the proteorhodopsin (<italic>prd</italic>) gene expression was relatively stable and high (~4000) across all samples (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>). The <italic>prd</italic> expression was generally dominated by <italic>Pelagibacterales</italic> with fair contributions also by other taxa - especially <italic>Cellvibrionales</italic> at the coastal station in summer (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>S17</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S20</bold>
</xref>). Bacteriochlorophyll gene (<italic>puf</italic>) expression was below 5 TPM (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figures S17</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S20</bold>
</xref>). Highest daily variability in the relative transcription of genes related to phototrophy was observed during winter at the offshore station (<xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S23</bold>
</xref>).</p>
</sec>
</sec>
<sec id="s3_4">
<title>Relationships between bacterial functioning and phytoplankton community composition</title>
<p>Since eukaryotic phytoplankton are key components of upwelling ecosystems &#x2013; potentially shaping the conditions for bacterial activities &#x2013; we carried out Spearman rank correlation analyses (applying a Benjamini-Hochberg correction) between the relative abundance of the major eukaryotic taxa in the 18S rRNA gene amplicon data and the relative transcription levels of the studied prokaryotic functional categories (<xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6A</bold>
</xref>) and environmental variables (<xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6B</bold>
</xref>). Notably, bacterial biomass, temperature, and salinity displayed significantly positive correlations (p-value &lt; 0.05 marked with asterisks in <xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6</bold>
</xref>) with categories related to bacterial uptake and utilization of resources (e.g., metabolism of carbohydrates, amino acids, phosphate and sulfate, and ammonium uptake) while the opposite pattern was observed for nutrients concentration (p-value &lt; 0.05 <xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6B</bold>
</xref>). Significant positive correlations were also found between the categories related to bacterial uptake and utilization of resources and the relative abundances of <italic>Stramenopiles</italic> (particularly <italic>Chaetoceros</italic>), <italic>Dinophyceae</italic>, marine stramenopiles (MAST), and Fungi (p-value &lt; 0.05) (<xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6A</bold>
</xref>). A positive relationship was found between the transcription of DMSP assimilation genes by the prokaryotic community and the abundance of <italic>Dinophyceae</italic> (p-value = 0.052) and marine alveolate (MALV) (p-value &lt; 0.05) (<xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6A</bold>
</xref>). In contrast, other metabolic traits, such as sulfite assimilation, iron storage, and photosynthesis genes, showed a significantly positive correlation (p-value &lt; 0.05) with <italic>Chlorophyta</italic> (particularly <italic>Ostreococcus</italic> and <italic>Micromonas</italic>) and <italic>Cryptophyceae</italic> (<xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6A</bold>
</xref>) and with low chlorophyll <italic>a</italic> values (p-value &lt; 0.05) (<xref ref-type="fig" rid="f6">
<bold>Figure&#xa0;6B</bold>
</xref>).</p>
<fig id="f6" position="float">
<label>Figure&#xa0;6</label>
<caption>
<p>Spearman rank correlation analysis between transcription of selected prokaryotic gene subcategories and <bold>(A)</bold> the relative abundance of the major eukaryotic taxa (18S) and; <bold>(B)</bold> environmental variables. The metatranscriptome data was clr-transformed before the analysis and a Benjamini-Hochberg method was used to adjust the p-values. Dots indicate p &lt; 0.05.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-10-1259783-g006.tif"/>
</fig>
</sec>
</sec>
<sec id="s4" sec-type="discussion">
<title>Discussion</title>
<sec id="s4_1">
<title>Coastal upwelling systems: dynamic grids of bacterioplankton functional specialization</title>
<p>Our analyses provided novel information about the potential mechanisms governing microbial interactions, nutrient utilization, and energy and matter fluxes in a representative upwelling system. We reason that it is essential to identify and characterize the large diversity of microbial processes and patterns for two important reasons. First, it partly results from two-way interactions with the inherently diverse distribution patterns of phytoplankton and bacteria within the microbial communities. Second, because of the complex interdependency between different physicochemical conditions and the myriad of ecological processes driven by different microbes in the ocean. Thus, focusing on the transcriptional investment by any one taxon in any particular metabolic pathway or a specific season of choice, would unavoidably have resulted in underestimating the magnitude of dynamics and distribution patterns characteristic of coastal upwelling systems. In the following we will discuss these findings with the intention to understand potential linkages between physicochemical and biotic processes.</p>
</sec>
<sec id="s4_2">
<title>Resource availability as a powerful driver in structuring microbial functioning</title>
<p>The present work is, to our knowledge, the first studying high resolution spatial and temporal changes in bacterial functioning by means of metatranscriptomics in an upwelling system. The coastal area of the NW Iberian Peninsula is a highly dynamic ecosystem, affected by the intermittent upwelling of cold and inorganic nutrient-rich water that promotes phytoplankton and bacterial growth (<xref ref-type="bibr" rid="B27">Figueiras and R&#xed;os, 1993</xref>; <xref ref-type="bibr" rid="B58">Nogueira et&#xa0;al., 1997</xref>; <xref ref-type="bibr" rid="B3">&#xc1;lvarez-Salgado et&#xa0;al., 2002</xref>). Our dataset suggests that the coast to offshore gradient and the temporal changes in environmental and biological conditions promoted by the upwelling are key drivers of the observed pronounced taxonomic and functional bacterial diversification in this system. Several examples extracted from our results may be given.</p>
<p>The present dataset exemplifies some specific functional mechanisms behind the important role of nitrogen (N) and phosphorus (P) in structuring the functioning of microbial communities previously suggested to exist in this ecosystem (<xref ref-type="bibr" rid="B53">Mart&#xed;nez-Garc&#xed;a et&#xa0;al., 2010</xref>; <xref ref-type="bibr" rid="B87">Teira et&#xa0;al., 2016</xref>). Regarding nitrogen, the observed high expression of the <italic>amt</italic>, <italic>glnAB</italic>, and <italic>icd</italic> genes by <italic>Gammaproteobacteria</italic> (particularly <italic>Cellvibrionales</italic>) during summer at the coastal station was remarkable. The enzymes encoded by these genes are linked in the process of nitrogen assimilation from ammonium in that <italic>amt</italic> encodes an ammonium transporter, <italic>glnAB</italic> encode glutamine synthase that synthesizes glutamine from ammonium and glutamate (glutamine can next be used for amino acid synthesis<italic>)</italic>, and <italic>icd</italic> encodes the TCA cycle enzyme isocitrate dihydrogenase that produces 2-oxoglutarate, which is the precursor of glutamate. This may suggest that the competitive ability of <italic>Cellvibrionales</italic> during the phytoplankton bloom in part lies in their ability to gear their metabolism towards utilizing N from ammonium as a means to utilize the C that they process. This is in line with the emerging view that the dialogue between the metabolic N and C cycles is largely mediated at the intercept between the TCA-cycle and the synthesis of amino acids (<xref ref-type="bibr" rid="B28">Forchhammer et&#xa0;al., 2022</xref>). At the offshore station, on the other hand, <italic>Pelagibacterales</italic> showed a relatively higher transcription of ammonium transporters compared to other taxa, suggesting this group is more capable of assimilating ammonium at the low concentrations typically found in oceanic areas. We think analysis of adjustments of central metabolism between biosynthetic as compared to energy-yielding pathways (such as respiration) has a large potential to inform on how marine bacteria meet challenges in elemental stoichiometry of their resources (as imposed through e.g. C- or N-limitation). Especially if advances are made in characterizing gene systems like amino acid transporters and extracellular proteases involved in the utilization of dissolved organic nitrogen.</p>
<p>The high expression of the gene that encodes the transport system for orthophosphate (<italic>pstB</italic>) during summer, when phosphate concentration was low, is coherent with the suggested role of the Pst system (<italic>pstABCS</italic>) in inorganic phosphate (Pi) uptake only under Pi-limiting conditions (<xref ref-type="bibr" rid="B33">Harke and Gobler, 2013</xref>; <xref ref-type="bibr" rid="B36">Jimenez-Infante et&#xa0;al., 2017</xref>). On the other hand, the transcription of the <italic>pit</italic> gene, a low-affinity phosphate membrane transporter typically expressed under high phosphorus concentrations and post-bloom conditions (<xref ref-type="bibr" rid="B2">Alonso-S&#xe1;ez et&#xa0;al., 2020</xref>), peaked at the coast in spring, coinciding with the highest ammonium and phosphate concentrations registered. Note here that, even though the phosphate concentration was similar in winter and spring at the coastal site, dissolved inorganic N, particularly ammonium, was considerably higher in spring, suggesting that higher expression of the pit gene in spring than in winter might be related to the higher ammonium to phosphate ratio. Overall, the different spatial-temporal patterns of variability observed in genes with different phosphate affinity in this upwelling system, regardless of the relatively limited variability in phosphate ambient concentration, reinforces the hypothesis of a complex role of phosphate in structuring bacterial functioning (<xref ref-type="bibr" rid="B33">Harke and Gobler, 2013</xref>; <xref ref-type="bibr" rid="B78">Satinsky et&#xa0;al., 2014</xref>).</p>
<p>Our results support the idea of a taxonomic diversification in iron (Fe) provision strategies in this upwelling system. Thus, while <italic>Cellvibrionales</italic> and <italic>Flavobacteriales</italic> are suggested to mostly use siderophore-associated Fe, <italic>Pelagibacterales</italic> probably use ferric ions and <italic>Synechococcales</italic> accumulate Fe as ferritin in this ecosystem (<xref ref-type="bibr" rid="B1">Ahlgren et&#xa0;al., 2020</xref>). On the other hand, a widespread genetic capacity for the uptake and utilization of sulfate in surface waters off NW Iberian Peninsula can be deduced from our data, as opposed to previous knowledge limiting sulfate use during phytoplankton blooms to a few bacterial groups (<xref ref-type="bibr" rid="B97">Zhou et&#xa0;al., 2020</xref>). Interestingly, our results also highlight a probable dominant role of <italic>Pelagibacterales</italic> in sulfite assimilation in the system, extending to upwelling areas previous findings in offshore epipelagic layers (<xref ref-type="bibr" rid="B57">Needham et&#xa0;al., 2017</xref>). The present dataset suggests for the first time the relevant role of organic sulfur (S) compounds as sources of reduced S for marine prokaryotes in this upwelling system, confirming previous studies in other areas (<xref ref-type="bibr" rid="B43">Kiene et&#xa0;al., 2000</xref>; <xref ref-type="bibr" rid="B55">Moran et&#xa0;al., 2003</xref>). Interestingly, the high relative abundance of <italic>dmdA</italic> transcripts at the offshore station during the summer upwelling period coincided with a dominance of the phytoplankton community by <italic>Dinophyceae</italic>. Dinoflagellates are known to have high dimethylsulfoniopropionate (DMSP) production rates (<xref ref-type="bibr" rid="B96">Zhao et&#xa0;al., 2021</xref>), and previous work has suggested that their DMSP-producing ability could affect the structure of their associated bacterial community (<xref ref-type="bibr" rid="B47">Lin et&#xa0;al., 2021</xref>). In this regard, the observed dominant role of <italic>Pelagibacterales</italic> in the transcription of DMSP utilization genes expands the work by <xref ref-type="bibr" rid="B90">Varaljay et&#xa0;al. (2012)</xref> in the North Pacific subtropical gyre to this upwelling system. Furthermore, DMSP has been previously reported to have a photoprotective function (<xref ref-type="bibr" rid="B6">Archer et&#xa0;al., 2009</xref>), which may be related to the high radiation levels and the strong thermal stratification registered in the offshore station during summer.</p>
<p>Finally, the present dataset suggests that different strategies for using light as a source of energy by bacteria occur in this upwelling system. Thus, the relative transcription of photosynthesis related genes by <italic>Synechococcales</italic> was more important in the offshore station during winter, where the abundance of this group was relatively higher (<xref ref-type="bibr" rid="B39">Joglar et&#xa0;al., 2020</xref>). It is important to note here that, as explained in the <italic>Methods</italic> section, the coastal and offshore stations were sampled at different time points in the daily cycle. Thus, the high relative transcription of photosynthesis-related genes by <italic>Synechococcales</italic> during winter in the offshore station may be not only related to the broad differences in physicochemical and biological conditions (higher relative abundance of <italic>Synechococcales</italic> during winter in the offshore station, see <xref ref-type="supplementary-material" rid="SM1">
<bold>Figure S6</bold>
</xref>) but also partly to an increase in the investment in light capture due to the sampling time. In this regard, previous studies have shown that prokaryotic transcriptomes from natural samples may exhibit diel periodicity, particularly those of <italic>Cyanobacteria</italic> in open ocean waters (<xref ref-type="bibr" rid="B62">Ottesen et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B63">Ottesen et&#xa0;al., 2014</xref>). Interestingly, the data on the transcription of the <italic>prd</italic> gene suggest that photrophy mediated though proteorhodopsin was relevant and widespread among different taxa, including <italic>Pelagibacterales</italic>, in accordance with the results by <xref ref-type="bibr" rid="B61">Olson et&#xa0;al. (2018)</xref> in oligotrophic waters and <italic>Gammaproteobacteria</italic> during the coastal phytoplankton bloom.</p>
</sec>
<sec id="s4_3">
<title>Short-term dynamics in microbial functioning</title>
<p>Previous studies have shown recurring daily patterns in the functioning of heterotrophic bacteria from relatively stable oligotrophic environments (<xref ref-type="bibr" rid="B63">Ottesen et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B56">Muratore et&#xa0;al., 2022</xref>). It is also well known that the metabolism of naturally occurring bacteria experience inter- and intra-seasonal changes associated to phytoplankton blooms (<xref ref-type="bibr" rid="B85">Teeling et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B86">Teeling et&#xa0;al., 2016</xref>). However, this is to our knowledge the first time that systematic changes in specific microbial functions (identified from gene expression analyses) associated to short-term oceanographic variability are shown. Our results evidence important short-term dynamics in bacterioplankton functioning superimposed on seasonal variability that coincided with changes in hydrography, nutrient availability and biotic variables in this system. Interestingly, this day-to-day changes in transcripts for specific functions related to nutrient fluxes and response to stimuli were even more pronounced when daily variability in oceanographic conditions (e.g. temperature, phytoplankton biomass, resource availability) was highest, that is: close to the coast during summer.</p>
<p>In summer, a wind relaxation event interrupted the ongoing upwelling, which modified the vertical density gradient at the coastal station, altered the hydrographic conditions and nutrient availability, and disrupted the phytoplankton bloom (see (<xref ref-type="bibr" rid="B8">Barbosa et&#xa0;al., 2001</xref>) and (<xref ref-type="bibr" rid="B38">Joglar et&#xa0;al., 2021b</xref>)). Concomitantly, a sharp decrease in the transcription of functions related with bacterial utilization of resources derived from the phytoplankton bloom was observed, including amino acid metabolism (<italic>glnAB</italic>), TCA cycle (<italic>icd</italic>), and ammonium uptake (<italic>amt</italic>). This suggests that bacteria quickly responded to the changes in resource supply and potentially also in the C/N ratio of resources, as previously suggested by others (see review by <xref ref-type="bibr" rid="B28">Forchhammer et&#xa0;al. (2022)</xref>). Also, the relative importance of high-affinity phosphate uptake genes (e.g., <italic>pstS</italic> and <italic>pstB</italic>, which are considered an indicator of microbial P limitation and that varies seasonally in relation to P availability (<xref ref-type="bibr" rid="B23">Dyhrman et&#xa0;al., 2007</xref>)) decreased quickly after bloom disruption (on day 5), this probably due to the cease of the competition with phytoplankton. In contrast, the transcription of low-affinity phosphate uptake gene <italic>pit</italic> followed the opposite pattern and relatively increased at the end of the summer sampling at the coast when phosphorus availability increased. Similarly, bacteria shifted from a strategy based on iron storage to an increase in the relative importance of iron uptake (as suggested by the high relative transcription of <italic>ftnA</italic> and <italic>fbpAB</italic>, respectively) when the phytoplankton bloom was interrupted. Interestingly, the important short-term changes observed in the transcription of DMSP assimilation genes coincided with day-to-day peaks in the relative abundance of dinoflagellates during the final phase of the summer cruise at both stations. Overall, these results suggested a close coupling between the physicochemical conditions and the bacterial and algal component of microbial communities from this upwelling system.</p>
</sec>
<sec id="s4_4">
<title>Unraveling functional interactions between bacteria and coastal phytoplankton</title>
<p>Overall, our results demonstrate that specific functional processes of the prokaryotic community identified from gene expression analyses) are associated with different phytoplankton groups in the upwelling system off the NW Iberian Peninsula. The presence of different phytoplankton and bacterioplankton populations during periods with different environmental conditions has been suggested in previous studies both in the area (<xref ref-type="bibr" rid="B39">Joglar et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B17">Costas-Selas et&#xa0;al., 2023</xref>) and in other marine ecosystems (<xref ref-type="bibr" rid="B67">Pinhassi et&#xa0;al., 2004</xref>; <xref ref-type="bibr" rid="B57">Needham et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B13">Bunse et&#xa0;al., 2019</xref>). Recent work in the NW Iberian Peninsula suggests a key role of biotic interactions as structuring factors of the eukaryotic community, mostly driven by positive associations between phytoplankton and bacteria (<xref ref-type="bibr" rid="B17">Costas-Selas et&#xa0;al., 2023</xref>). These findings may suggest some coevolution between the algae and the associated bacterial community that extends beyond the ability to transform phytoplankton-derived macromolecules by bacteria. The present dataset unravel the specific metabolic processes and bacterial and phytoplankton taxa that may be behind these associations through space and time. It is important to note here again that the interactions between phytoplankton and bacteria may change throughout the light cycle as it is known to affect the functioning of photosynthetic organisms (<xref ref-type="bibr" rid="B62">Ottesen et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B63">Ottesen et&#xa0;al., 2014</xref>). Therefore, the sampling at different times in both stations might influence to some extent the results discussed below.</p>
<p>Two interesting examples of possible phytoplankton-bacteria linkages observed during the productive season were associated to the bacterial transcription of genes related to the metabolism of DMSP (see above) and to the synthesis of B-vitamins. The observed increase in the relative abundance of transcripts of vitamin-related genes during summer is likely related to the high phytoplankton and bacterial requirements characteristic of blooming populations (<xref ref-type="bibr" rid="B18">Croft et&#xa0;al., 2005</xref>; <xref ref-type="bibr" rid="B45">Koch, 2012</xref>; <xref ref-type="bibr" rid="B77">Sa&#xf1;udo-Wilhelmy et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B46">Koch and Trimborn, 2019</xref>). Interestingly, genes belonging to the aerobic pathway of B12 synthesis (e.g. <italic>cobG</italic> and <italic>cobT</italic>), which is mostly associated with phytoplankton blooms (<xref ref-type="bibr" rid="B97">Zhou et&#xa0;al., 2020</xref>), increased during summer, while transcription of <italic>cbiX</italic>, which belongs to the anaerobic pathway of B12 synthesis that has been previously suggested to be independent of phytoplankton activity (<xref ref-type="bibr" rid="B30">Grossman, 2016</xref>), did not follow a clear seasonal pattern. The relative increase in <italic>thiL</italic> and <italic>cobG</italic> transcription by <italic>Cellvibrionales</italic> and <italic>Flavobacteria</italic> during summer suggests that these groups provided B1 and B12 vitamins to blooming eukaryotic phytoplankton. Interestingly, this hypothesis is also supported by microcosms experiments stimulating phytoplankton growth and including B1 and B12 vitamins additions carried out in summer in the NW Iberian Peninsula upwelling system that showed relatively important contributions of <italic>Cellvibrionales</italic> and <italic>Flavobacteria</italic> to the transcription of genes related to vitamin metabolism (<xref ref-type="bibr" rid="B37">Joglar et&#xa0;al., 2021a</xref>).</p>
<p>Finally, our results suggest strong functional linkages between bacteria and phytoplankton during non-blooming winter conditions. In this regard, the association between transcripts related to bacterial metabolic traits such as sulfite assimilation, iron uptake and storage, and photosynthesis, and <italic>Clorophyta</italic> and <italic>Cryptophyceae</italic> may reflect the close association between these phytoplankton groups and bacteria from the orders <italic>Pelagibacterales</italic> and <italic>Synechococcales</italic>, which played prominent roles in the relative transcription of genes associated with these metabolic functions. The close connection between these phytoplankton groups and <italic>Synechococcus</italic> sp., also described by <xref ref-type="bibr" rid="B17">Costas-Selas et&#xa0;al. (2023)</xref> in the same study area, were hypothesized to be linked with B12 provision. Our results point to an additional interaction mechanism between these groups, which could be related to the high capacity of <italic>Synechococcus</italic> to store Fe. As <italic>Clorophyta</italic> and <italic>Cryptophyceae</italic> may have mixotrophic behavior (<xref ref-type="bibr" rid="B84">Stoecker et&#xa0;al., 2017</xref>), predation on <italic>Synechococcus</italic> might be a source of Fe for them. A previous experimental study observed a sharp decrease in genes related to Fe uptake in a mixotrophic <italic>Haptophyta</italic> fed with bacteria, suggesting that bacterivory may provide Fe to the algae (<xref ref-type="bibr" rid="B49">Liu et&#xa0;al., 2015</xref>).</p>
<p>The close correlation between <italic>Chlorophyta</italic> (particularly <italic>Ostreococcus</italic> and <italic>Micromonas</italic>), <italic>Cryptophyceae</italic>, and <italic>Pelagibacterales</italic> suggests a link mediated by the sulfur metabolites, given the strong correlation between these phytoplankton groups and the relative abundance of sulfite assimilation genes. In this regard, a recent study suggests that adenylylsulfate reductase genes (<italic>aprAB</italic>) in <italic>Pelagibacterales</italic> clades could be related to taurine metabolism, oxidizing the sulfite derived from the conversion of taurine into acetyl-CoA (<xref ref-type="bibr" rid="B20">De Corte et al., 2021</xref>; <xref ref-type="bibr" rid="B76">Ruiz-Perez et&#xa0;al., 2021</xref>), a result consistent with the demonstrated ability of <italic>Ostreococcus</italic> and <italic>Micromonas</italic> to produce high quantities of taurine (<xref ref-type="bibr" rid="B22">Durham et&#xa0;al., 2019</xref>).</p>
</sec>
<sec id="s4_5">
<title>
<italic>Cellvibronales</italic>: an unexpected key player in upwelling systems</title>
<p>Knowledge of the ecophysiology and ecology of <italic>Cellvibrionales</italic> is still scarce, but they appear to reach highest relative abundances in surface waters and coastal areas (<xref ref-type="bibr" rid="B16">Ch&#xe9;nard et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B64">Pajares et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B73">Reji et&#xa0;al., 2020</xref>). Although <italic>Cellvibrionales</italic> is not the most abundant bacterial group in this system, it appears to play a relevant and unexpected role during the summer phytoplankton bloom formation and development.</p>
<p>First, our field data suggest a prominent role of <italic>Cellvibrionales</italic> in degradation of phytoplankton-derived organic matter. Thus, during the <italic>Dinophyceae</italic> and <italic>Chaetoceros</italic> summer bloom, <italic>Flavobacteriales</italic> and <italic>Cellvibrionales</italic> dominated the relative expression of genes related to resource utilization and remineralization. It is well known that the primary role of <italic>Flavobacteriales</italic> in the degradation of polymeric organic matter (<xref ref-type="bibr" rid="B85">Teeling et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B25">Fern&#xe1;ndez-G&#xf3;mez et&#xa0;al., 2013</xref>) is especially important during diatom blooms in upwelling ecosystems (<xref ref-type="bibr" rid="B44">Klindworth et&#xa0;al., 2014</xref>). However, the high transcription by <italic>Cellvibrionales</italic> of carbohydrate and TCA cycle-related genes as well as ammonium utilization and amino acid synthesis genes during the phytoplankton bloom presented here is remarkable. This behavior may be related to efficient energy production (<xref ref-type="bibr" rid="B91">Wang et&#xa0;al., 2022</xref>) and to adjustments to C or N-limitation by this group when resources are available during summer phytoplankton blooms (see above). Thus, the increase in the transcription of C metabolism-related genes by <italic>Cellvibrionales</italic> is consistent with recent findings in concurrent mesocosms experiments (performed in the same sampling area during the present study) (<xref ref-type="bibr" rid="B69">Pontiller et&#xa0;al., 2022</xref>) and in other regions (<xref ref-type="bibr" rid="B71">Poretsky et&#xa0;al., 2010</xref>; <xref ref-type="bibr" rid="B48">Liu et&#xa0;al., 2020</xref>), suggesting a quick response of <italic>Cellvibrionales</italic> to phytoplankton-derived organic matter. In surface waters of coastal systems like the NW Iberian Peninsula, the Gullmar Fjord and the German Bight, <italic>Cellvibrionales</italic> have been shown to importantly invest energy in the expression of different polymer degrading enzyme systems including for example laminarases that allow bacteria to decompose the algal storage glucan laminarin (<xref ref-type="bibr" rid="B85">Teeling et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B70">Pontiller et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B69">Pontiller et&#xa0;al., 2022</xref>) emphasizing their significant role in the turnover of phytoplankton-derived organic matter in these systems. Similarly, the relatively abundant <italic>Cellvibrionales</italic> transcription of motility-related genes during the summer bloom is in accordance with their description as a copiotroph group, known to quickly respond to the increase of DOM surrounding the microenvironment of phytoplankton cells in productive environments (<xref ref-type="bibr" rid="B81">Smriga et&#xa0;al., 2016</xref>). In addition, the high transcription of the proteorhodopsin gene (i.e. <italic>prd</italic>) by <italic>Cellvibrionales</italic> during summer may indicate that this group uses proton pumps as a supplemental energy source to uptake recently released complex carbon compounds during phytoplankton blooms (<xref ref-type="bibr" rid="B66">Pinhassi et&#xa0;al., 2016</xref>).</p>
<p>Our data suggest that the association between blooming phytoplankton and <italic>Cellvibrionales</italic> may be more complex than just the ability to transform phytoplankton derived macromolecules. We found higher levels of expression of genes for vitamins B1 and B12 synthesis by these bacteria associated with phytoplankton groups dominant during the blooms (i.e., <italic>Chaetoceros</italic> and <italic>Dinophyceae</italic>). This finding suggests that <italic>Cellvibrionales</italic> have an important role as suppliers of micronutrients needed for phytoplankton growth and bloom development. Similarly, the increase in the expression of siderophore-uptake related genes by <italic>Cellvibrionales</italic> associated with bloom-forming phytoplankton may indicate that these bacteria compete with <italic>Chaetoceros</italic> and <italic>Dinophyceae</italic> algae for organically-bound iron during the bloom season (<xref ref-type="bibr" rid="B4">Amin et&#xa0;al., 2009</xref>). Therefore, our data suggest that <italic>Cellvibrionalles</italic> develop a mutualistic relationship with blooming phytoplankton by producing growth-promoting compounds like vitamin B12 and facilitating phytoplankton functioning. They also show, as explained above, that <italic>Cellvibrionalles</italic> seem to act as competitors of blooming phytoplankton for iron provision in this productive upwelling system.</p>
<p>In conclusion, the present work highlights the mosaic of microbial processes governing energy and matter transformations in this representative upwelling system. Uncovering the linkages between bacterial activity and spatial-temporal variability in environmental conditions represents a relevant goal for microbial oceanography The systematic patterns that emerge from this work are encouraging in the context of future modeling attempts aiming to predict biogeochemical processes in such highly productive ecosystems.</p>
</sec>
</sec>
<sec id="s5" sec-type="data-availability">
<title>Data availability statement</title>
<p>The datasets presented in this study can be found in online repositories. The names of the repository/repositories and accession number(s) can be found below: <ext-link ext-link-type="uri" xlink:href="https://www.ebi.ac.uk/ena">https://www.ebi.ac.uk/ena</ext-link>, PRJEB36188 (16S rRNA gene); PRJEB36099 (18S rRNA gene) and; PRJEB36728 (ERS5513557-ERS5513582) (metatranscriptome sequences).</p>
</sec>
<sec id="s6" sec-type="author-contributions">
<title>Author contributions</title>
<p>ED-N: Formal analysis, Writing &#x2013; original draft. ET: Writing &#x2013; original draft, Conceptualization, Funding acquisition, Writing &#x2013; review &amp; editing. BP: Writing &#x2013; original draft, Writing &#x2013; review &amp; editing, Formal analysis. DL: Formal analysis, Writing &#x2013; original draft. VJ: Formal analysis, Writing &#x2013; original draft. CP-A: Writing &#x2013; review &amp; editing. EF: Writing &#x2013; review &amp; editing, Conceptualization, Funding acquisition, Writing &#x2013; original draft. JP: Conceptualization, Writing &#x2013; original draft, Writing &#x2013; review &amp; editing, Formal analysis. SM-G: Conceptualization, Formal analysis, Writing &#x2013; original draft, Writing &#x2013; review &amp; editing.</p>
</sec>
</body>
<back>
<sec id="s7" sec-type="funding-information">
<title>Funding</title>
<p>The author(s) declare financial support was received for the research, authorship, and/or publication of this article. This research was supported by the Spanish Ministry of Science and Innovation through the ENVISION (CTM2014-59031-P) INTERES (CTM2017-83362-R), TRAITS (PID2019-110011RB-C33) and BIOTOX (PID2021-125643OB-C21) projects.</p>
</sec>
<ack>
<title>Acknowledgments</title>
<p>The authors would like to acknowledge support from Science for Life Laboratory, the National Genomics Infrastructure, NGI, and Uppmax (compute project SNIC 2017/7-419 and storage project SNIC 2020/16- 76) for assisting in massive parallel sequencing and computational infrastructure. We also thank the crew of B/O Ram&#xf3;n Margalef for their hospitality and professionalism during cruises and all the people involved in the project ENVISION for helping with sampling and analytical work. Erick Delgadillo acknowledges a predoctoral FPI fellowship (PRE2018-085871) from the Spanish Ministry of Economy and Competitiveness.</p>
</ack>
<sec id="s9" sec-type="COI-statement">
<title>Conflict of interest</title>
<p>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.</p>
<p>The author(s) declared that they were an editorial board member of Frontiers, at the time of submission. This had no impact on the peer review process and the final decision.</p>
</sec>
<sec id="s10" sec-type="correction-statement">
<title>Correction note</title>
<p>A correction has been made to this article. Details can be found at: <ext-link xlink:href="https://doi.org/10.3389/fmars.2026.1886620" ext-link-type="uri">10.3389/fmars.2026.1886620</ext-link>.</p>
</sec>
<sec id="s11" sec-type="disclaimer">
<title>Publisher&#x2019;s note</title>
<p>All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.</p>
</sec>
<sec id="s12" sec-type="supplementary-material">
<title>Supplementary material</title>
<p>The Supplementary Material for this article can be found online at: <ext-link ext-link-type="uri" xlink:href="https://www.frontiersin.org/articles/10.3389/fmars.2023.1259783/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fmars.2023.1259783/full#supplementary-material</ext-link>
</p>
<supplementary-material xlink:href="Table1.docx" id="ST1" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document">
<label>Supplementary Table&#xa0;1</label>
<caption>
<p>List of the 162 genes found out of the 198 target protein profiles grouped into nine categories and 44 subcategories.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="Table2.docx" id="ST2" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document">
<label>Supplementary Table&#xa0;2</label>
<caption>
<p>Average and standard deviation of the different oceanographic parameters measured at the offshore and coastal stations during winter, spring and summer.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF1" mimetype="application/zip">
<label>Supplementary Figure&#xa0;1</label>
<caption>
<p>Vertical distribution over time of temperature (&#xb0;C; panels 1-6), photosynthetically active radiation (&#xb5;mol photons m<sup>2</sup> s<sup>-1</sup>; 7-12), Chl a derived from calibrated CTD fluorescence sensor (&#xb5;g L<sup>-1</sup>; 13-18), salinity (PSU; 19-24) and turbidity (NTU; 25-30) in winter, spring and summer cruises at the offshore and coastal stations.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF2" mimetype="application/zip">
<label>Supplementary Figure&#xa0;2</label>
<caption>
<p>Vertical distribution over time of ammonium (NH<sub>4</sub>
<sup>+</sup> &#xb5;mol L&#xb9;; panels 1-6), nitrite (NO<sub>2</sub>
<sup>-</sup> &#xb5;mol L&#xb9;; 7-12), nitrate (NO<sub>3</sub>
<sup>-</sup> &#xb5;mol L&#xb9;; 13-18), silicate (SiO<sub>2</sub> &#xb5;mol L&#xb9;; 19-24) and phosphate (PO<sub>4</sub>
<sup>3-</sup> &#xb5;mol L&#xb9;; 25-30) in winter, spring and summer cruises at the offshore and coastal stations.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF3" mimetype="application/zip">
<label>Supplementary Figure&#xa0;3</label>
<caption>
<p>Box plots of salinity, temperature, chlorophyll a, bacterial abundance, nitrate (NO<sub>3</sub>
<sup>-</sup>), ammonium (NH<sub>4</sub>
<sup>+</sup>), phosphate (PO<sub>4</sub>
<sup>3-</sup>), N:P ratio, and silicate (SiO<sub>2</sub>) at surface (5m) during winter (WIN), spring (SPG) and summer (SUM). Horizontal line in the box represents the median value. The whiskers above and below the box represent the range of the data (maximum and minimum) within 1.5 times the interquartile range (IQR). Points outside the whiskers are outliers.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF4" mimetype="application/zip">
<label>Supplementary Figure&#xa0;4</label>
<caption>
<p>Chlorophyll-a composite from Aqua-MODIS Composite satellite images during the cruise periods, showing the chlorophyll-a filaments extending form the coast to the ocean during the upwelling in summer. During summer offshore chlorophyll-a is very low due to nutrient-limitation associated to thermal stratification.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF5" mimetype="application/zip">
<label>Supplementary Figure&#xa0;5</label>
<caption>
<p>Daily variability (estimated as the ratio of the daily value of each variable divided by the mean value of that variable during the four days of the specific season and station) of the different oceanographic variables measured at the costal and offshore stations during winter (WIN), spring (SPG), and summer (SUM). The color and the vertical position of the bubble (y-axis) represent the value of the ratio.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF6" mimetype="application/zip">
<label>Supplementary Figure&#xa0;6</label>
<caption>
<p>Temporal evolution of the relative abundances of major taxonomic groups of: <bold>(A)</bold> prokaryotes (16S) and <bold>(B)</bold> eukaryotes (18S) at surface (5m) in the coastal and offshore stations during winter, spring and summer. Data for each sampling day (days 1, 3, 5 and 7) is shown.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF7" mimetype="application/zip">
<label>Supplementary Figure&#xa0;7</label>
<caption>
<p>Relative abundance of major prokaryotic groups (16S) (x-axis) and relative contribution of each group to the metatranscriptome (y-axis) in the offshore and coastal stations during winter, spring and summer. For each taxonomic group, the value in the y and x-axis were significantly different (t-test, p&lt;0.05) in all cases except for: <italic>Oceanospirillales</italic>, <italic>Pelagibacterales</italic>, <italic>Rhodobacterales</italic> and Other <italic>Alphaproteobacteria</italic> in the offshore station in winter; <italic>Cellvibrionales</italic>, <italic>Rhizobiales</italic> and Other <italic>Alphaproteobacteria</italic> in the offshore station in spring; <italic>Cellvibrionales</italic> and <italic>Verrucomicrobia</italic> in the offshore station in summer; <italic>Oceanospirillales</italic>, <italic>Pelagibacterales</italic>, <italic>Prochlorococcus</italic> and Other <italic>Alphaproteobacteria</italic> in the coastal station in winter; <italic>Cellvibrionales</italic>, <italic>Oceanospirillales</italic>, <italic>Synechoccales</italic> and <italic>Verrucomicrobia</italic> in the coastal station in spring and; <italic>Oceanospirillales</italic>, <italic>Synechoccales</italic>, <italic>Prochlorococcu</italic>s and <italic>Verrucomicrobia</italic> in the coastal station in summer (t-test, p&gt;0.05).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF8" mimetype="application/zip">
<label>Supplementary Figure&#xa0;8</label>
<caption>
<p>Analysis of Non-parametric MultiDimensional Scaling (nMDS) of clr-transformed bacterioplankton metatranscriptomes. PERmutational Multivariate ANalysis Of VAriance (PERMANOVA, p &lt; 0.01) was used to differentiate between groups. Circles: coast, triangles: offshore. Winter: blue, spring: red and, summer: green.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF9" mimetype="application/zip">
<label>Supplementary Figure&#xa0;9</label>
<caption>
<p>Relative transcript abundance (TPM) of carbon metabolism-related genes. Color bars represent the relative contribution of main taxonomic groups to the transcription of each gene at the costal and offshore station during winter (WIN), spring (SPG), and summer (SUM).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF10" mimetype="application/zip">
<label>Supplementary Figure&#xa0;10</label>
<caption>
<p>Relative transcript abundance (TPM) of nitrogen metabolism-related genes. Color bars represent the relative contribution of main taxonomic groups to the transcription of each gene at the costal and offshore station during winter (WIN), spring (SPG), and summer (SUM).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF11" mimetype="application/zip">
<label>Supplementary Figure&#xa0;11</label>
<caption>
<p>Relative transcript abundance (TPM) of phosphorus metabolism-related genes. Color bars represent the relative contribution of main taxonomic groups to the transcription of each gene at the costal and offshore station during winter (WIN), spring (SPG), and summer (SUM).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF12" mimetype="application/zip">
<label>Supplementary Figure&#xa0;12</label>
<caption>
<p>Relative transcript abundance (TPM) of sulfur metabolism-related genes. Color bars represent the relative contribution of main taxonomic groups to the transcription of each gene at the costal and offshore station during winter (WIN), spring (SPG), and summer (SUM).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF13" mimetype="application/zip">
<label>Supplementary Figure&#xa0;13</label>
<caption>
<p>Relative transcript abundance (TPM) of iron metabolism-related genes. Color bars represent the relative contribution of main taxonomic groups to the transcription of each gene at the costal and offshore station during winter (WIN), spring (SPG), and summer (SUM).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF14" mimetype="application/zip">
<label>Supplementary Figure&#xa0;14</label>
<caption>
<p>Relative transcript abundance (TPM) of vitamin-related genes. Color bars represent the relative contribution of main taxonomic groups to the transcription of each gene at the costal and offshore station during winter (WIN), spring (SPG), and summer (SUM).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF15" mimetype="application/zip">
<label>Supplementary Figure&#xa0;15</label>
<caption>
<p>Relative transcript abundance (TPM) of response to stress-related genes. Color bars represent the relative contribution of main taxonomic groups to the transcription of each gene at the costal and offshore station during winter (WIN), spring (SPG), and summer (SUM).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF16" mimetype="application/zip">
<label>Supplementary Figure&#xa0;16</label>
<caption>
<p>Relative transcript abundance (TPM) of response to stimuli-related genes. Color bars represent the relative contribution of main taxonomic groups to the transcription of each gene at the costal and offshore station during winter (WIN), spring (SPG), and summer (SUM).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF17" mimetype="application/zip">
<label>Supplementary Figure&#xa0;17</label>
<caption>
<p>Relative transcript abundance (TPM) of phototrophy-related genes. Color bars represent the relative contribution of main taxonomic groups to the transcription of each gene at the costal and offshore station during winter (WIN), spring (SPG), and summer (SUM).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF18" mimetype="application/zip">
<label>Supplementary Figure&#xa0;18</label>
<caption>
<p>Daily variability of carbon-, nitrogen- and phosphorus-related genes at the costal and offshore stations during winter (WIN), spring (SPG), and summer (SUM). Relative transcript abundance (TPM) of selected key biological process is provided. Color bars represent the relative contribution of main taxonomic groups to transcription. The value for each sampling day (days 1, 3, 5 and 7) is shown. Note that different scales are used on the y-axis.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF19" mimetype="application/zip">
<label>Supplementary Figure&#xa0;19</label>
<caption>
<p>Daily variability of sulfur-, iron- and vitamins-related genes at the costal and offshore stations during winter (WIN), spring (SPG), and summer (SUM). Relative transcript abundance (TPM) of selected key biological process is provided. Color bars represent the relative contribution of main taxonomic groups to transcription. The value for each sampling day (days 1, 3, 5 and 7) is shown. Note that different scales are used on the y-axis.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF20" mimetype="application/zip">
<label>Supplementary Figure&#xa0;20</label>
<caption>
<p>Daily variability of response to stimuli-, response to stress- and phototrophy-related genes at the costal and offshore stations during winter (WIN), spring (SPG), and summer (SUM). Relative transcript abundance (TPM) of selected key biological process is provided. Color bars represent the relative contribution of main taxonomic groups to transcription. The value for each sampling day (days 1, 3, 5 and 7) is shown. Note that different scales are used on the y-axis.</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF21" mimetype="application/zip">
<label>Supplementary Figure&#xa0;21</label>
<caption>
<p>Daily variability (estimated as the daily TPMs of each gene divided by the mean value of the TPMs of that gene during the four days of the specific season and station) of selected genes in the carbon, nitrogen and phosphorus metabolism categories at the offshore and costal stations during winter (WIN), spring (SPG), and summer (SUM). The color and the vertical position of the bubble (y-axis) represent the value of the ratio. The size of the bubble represents the daily relative abundance (TPM) of each gene over the days of sampling (days 1, 3, 5, and 7; x-axis).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF22" mimetype="application/zip">
<label>Supplementary Figure&#xa0;22</label>
<caption>
<p>Daily variability (estimated as the daily TPMs of each gene divided by the mean value of the TPMs of that gene during the four days of the specific season and station) of selected genes in the sulfur, iron and vitamins metabolism categories at the offshore and costal stations during winter (WIN), spring (SPG), and summer (SUM). The color and the vertical position of the bubble (y-axis) represent the value of the ratio. The size of the bubble represents the daily relative abundance (TPM) of each gene over the days of sampling (days 1, 3, 5, and 7; x-axis).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet1.zip" id="SF23" mimetype="application/zip">
<label>Supplementary Figure&#xa0;23</label>
<caption>
<p>Daily variability (estimated as the daily TPMs of each gene divided by the mean value of the TPMs of that gene during the four days of the specific season and station) of selected genes in the response to stimuli, response to stress, and phototrophy categories at the offshore and costal stations during winter (WIN), spring (SPG), and summer (SUM). The color and the vertical position of the bubble (y-axis) represent the value of the ratio. The size of the bubble represents the daily relative abundance (TPM) of each gene over the days of sampling (days 1, 3, 5, and 7; x-axis).</p>
</caption>
</supplementary-material>
<supplementary-material xlink:href="DataSheet2.docx" id="SM1" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document"/>
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