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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>
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<publisher-name>Frontiers Media S.A.</publisher-name>
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<article-meta>
<article-id pub-id-type="doi">10.3389/fmars.2025.1500646</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Marine Science</subject>
<subj-group>
<subject>Brief Research Report</subject>
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</subj-group>
</article-categories>
<title-group>
<article-title>Effect of ocean acidification on the oxygen consumption of the sea urchins <italic>Paracentrotus lividus</italic> (Lamarck, 1816) and <italic>Arbacia lixula</italic> (Linnaeus, 1758) living in CO<sub>2</sub> natural gradients</article-title>
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<contrib contrib-type="author" equal-contrib="yes" corresp="yes">
<name>
<surname>Fern&#xe1;ndez-Vilert</surname>
<given-names>Robert</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>*</sup>
</xref>
<xref ref-type="author-notes" rid="fn003">
<sup>&#x2020;</sup>
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<surname>Arranz</surname>
<given-names>Vanessa</given-names>
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<sup>1</sup>
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<sup>2</sup>
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<sup>*</sup>
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<sup>&#x2020;</sup>
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<name>
<surname>Mart&#xed;n-Huete</surname>
<given-names>Marta</given-names>
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<sup>1</sup>
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<contrib contrib-type="author">
<name>
<surname>Hern&#xe1;ndez</surname>
<given-names>Jos&#xe9; Carlos</given-names>
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<sup>3</sup>
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<contrib contrib-type="author">
<name>
<surname>Gonz&#xe1;lez-Delgado</surname>
<given-names>Sara</given-names>
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<sup>1</sup>
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<contrib contrib-type="author">
<name>
<surname>P&#xe9;rez-Portela</surname>
<given-names>Roc&#xed;o</given-names>
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<sup>1</sup>
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<sup>2</sup>
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<aff id="aff1">
<sup>1</sup>
<institution>Dept. de Biologia Evolutiva, Ecologia i Ci&#xe8;ncies Ambientals, Universitat de Barcelona</institution>, <addr-line>Barcelona</addr-line>, <country>Spain</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>Institut de Recerca de la Biodiversitat (IRBio), Universitat de Barcelona</institution>, <addr-line>Barcelona</addr-line>, <country>Spain</country>
</aff>
<aff id="aff3">
<sup>3</sup>
<institution>Dept. Biolog&#xed;a Animal, Edafolog&#xed;a y Geolog&#xed;a, Universidad de La Laguna</institution>, <addr-line>Santa Cruz de Tenerife</addr-line>, <country>Spain</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>Edited by: Caitlin Blain, The University of Auckland, New Zealand</p>
</fn>
<fn fn-type="edited-by">
<p>Reviewed by: Nathalie Oulhen, Brown University, United States</p>
<p>Federica Costantini, University of Bologna, Italy</p>
<p>Ian Dixon-Anderson, University of Otago, New Zealand</p>
</fn>
<fn fn-type="corresp" id="fn001">
<p>*Correspondence: Robert Fern&#xe1;ndez-Vilert, <email xlink:href="mailto:r.fvilert@gmail.com">r.fvilert@gmail.com</email>; Vanessa Arranz, <email xlink:href="mailto:v.arranz@ub.edu">v.arranz@ub.edu</email>
</p>
</fn>
<fn fn-type="equal" id="fn003">
<p>&#x2020;These authors have contributed equally to this work and share first authorship</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>04</day>
<month>02</month>
<year>2025</year>
</pub-date>
<pub-date pub-type="collection">
<year>2025</year>
</pub-date>
<volume>12</volume>
<elocation-id>1500646</elocation-id>
<history>
<date date-type="received">
<day>23</day>
<month>09</month>
<year>2024</year>
</date>
<date date-type="accepted">
<day>17</day>
<month>01</month>
<year>2025</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2025 Fern&#xe1;ndez-Vilert, Arranz, Mart&#xed;n-Huete, Hern&#xe1;ndez, Gonz&#xe1;lez-Delgado and P&#xe9;rez-Portela</copyright-statement>
<copyright-year>2025</copyright-year>
<copyright-holder>Fern&#xe1;ndez-Vilert, Arranz, Mart&#xed;n-Huete, Hern&#xe1;ndez, Gonz&#xe1;lez-Delgado and P&#xe9;rez-Portela</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>Ocean acidification (OA) stands out as one of the main threats to marine ecosystems. OA leads to a reduction in the availability of carbonate ions, which are essential for marine calcifiers such as echinoderms. We aim to understand the physiological responses of two sea urchin species, <italic>Paracentrotus lividus</italic> and <italic>Arbacia lixula</italic> to low pH conditions and determine whether their responses result from phenotypic plasticity or local adaptation. The study is divided into two parts: plasticity response over time, measuring respiration rates of individuals from the Mediterranean Sea exposed to low pH over seven days, and adaptation and plasticity under changing pH, analyzing individuals inhabiting a pH gradient in a natural CO<sub>2</sub> vent system located in La Palma Island, Spain. Over the seven days of low pH exposure, distinct patterns in respiration rates were revealed, with both species demonstrating potential for acclimatization. Notably, <italic>P. lividus</italic> and <italic>A. lixula</italic> displayed unsynchronized acidosis/alkalosis cycles, suggesting different physiological mechanisms. Additionally, environmental history seemed to influence adaptive capacity, as specimens from fluctuating pH environments exhibited respiration rates similar to those from stable environments with heightened phenotypic plasticity. Overall, our results suggest that both species possess the capacity for metabolic plasticity, which may enhance their resilience to future OA scenarios but likely involve energetic costs. Moreover, CO<sub>2</sub> vent systems may serve as OA refugia, facilitating long-term survival. Understanding the plastic responses versus adaptations is crucial for predicting the effects of OA on species distribution and abundance of marine organisms in response to ongoing climate change.</p>
</abstract>
<kwd-group>
<kwd>echinoderms</kwd>
<kwd>aquatic respirometry</kwd>
<kwd>metabolism</kwd>
<kwd>climate change</kwd>
<kwd>CO2 vent</kwd>
</kwd-group>
<counts>
<fig-count count="3"/>
<table-count count="0"/>
<equation-count count="1"/>
<ref-count count="66"/>
<page-count count="9"/>
<word-count count="4444"/>
</counts>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-in-acceptance</meta-name>
<meta-value>Global Change and the Future Ocean</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="s1" sec-type="intro">
<title>Introduction</title>
<p>The anthropogenic rise in atmospheric CO<sub>2</sub> leads to its absorption by the oceans resulting in the decreasing of seawater pH, known as ocean acidification (OA). Under current emissions, a drop in oceanic pH by 0.4 units is projected by the end of the 21st century compared to the current values (<xref ref-type="bibr" rid="B3">Allan et&#xa0;al., 2021</xref>). OA severely threatens marine ecosystems (<xref ref-type="bibr" rid="B21">Dupont and P&#xf6;rtner, 2013</xref>), due to the reduction in the availability of carbonate ions, which affects marine calcifiers who use these minerals to synthesize carbonate biostructures. This vulnerability encompasses a broad range of taxa, including echinoderms (<xref ref-type="bibr" rid="B12">Byrne and Hern&#xe1;ndez, 2020</xref>). The consequences of vulnerable systems are disruptions to food webs, alteration of biodiversity on marine invertebrates, and impacts on the overall health of the oceans (<xref ref-type="bibr" rid="B55">Stumpp et&#xa0;al., 2013</xref>).</p>
<p>The sea urchins <italic>Paracentrotus lividus</italic> (Lamarck, 1816) and <italic>Arbacia lixula</italic> (Linnaeus, 1758) are calcifying species and key components in benthic communities of the Mediterranean Sea and northeast Atlantic due to their role in algae population regulation (<xref ref-type="bibr" rid="B49">Palac&#x131;&#x301;n et&#xa0;al., 1998</xref>). Within the Mediterranean, the combined grazing action at high densities promotes the formation of barren ground areas (<xref ref-type="bibr" rid="B8">Bonaviri et al., 2011</xref>; <xref ref-type="bibr" rid="B1">Agnetta et al., 2015</xref>), making changes in their abundance a concern for coastal conservation (<xref ref-type="bibr" rid="B64">Verg&#xe9;s et&#xa0;al., 2014</xref>). Studying their adaptability to overcome OA is essential to predict potential impacts on shallow Atlantic-Mediterranean waters.</p>
<p>Seawater pH affects the metabolism of the organisms by altering biochemical pathways (<xref ref-type="bibr" rid="B20">Dupont et&#xa0;al., 2010</xref>). External rising CO<sub>2</sub> concentration can diffuse into body tissues causing hypercapnia and acidosis (a decreased internal pH) (<xref ref-type="bibr" rid="B18">Collard et&#xa0;al., 2013</xref>) which disrupt physiological processes such as calcification, nutrition, and metabolism (<xref ref-type="bibr" rid="B44">Melzner et al., 2009</xref>; <xref ref-type="bibr" rid="B11">Byrne and Fitzer, 2019</xref>; <xref ref-type="bibr" rid="B51">P&#xf6;rtner, 2008</xref>). Understanding metabolic responses is necessary for assessing the species survival, health, and fitness under environmental challenges (<xref ref-type="bibr" rid="B9">Brown et&#xa0;al., 2004</xref>; <xref ref-type="bibr" rid="B13">Calosi et&#xa0;al., 2013</xref>). Stabilized metabolic rates can occur via adaptation (selecting genotypes), or acclimatization (phenotypic plasticity) (<xref ref-type="bibr" rid="B47">Norin and Metcalfe, 2019</xref>). However, physiological plasticity and adaptation to low pH in marine organisms remain poorly understood (<xref ref-type="bibr" rid="B13">Calosi et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B19">Di Giglio et&#xa0;al., 2020</xref>). Both <italic>P. lividus</italic> and <italic>A. lixula</italic> have a likely efficient pH compensation system, essential for survival in acidified&#xa0;areas. However, <italic>P. lividus</italic> is less effective in regulating extracellular acid-base balance than <italic>A. lixula</italic> (<xref ref-type="bibr" rid="B13">Calosi et&#xa0;al., 2013</xref>). Nevertheless, this buffering ability may involve an energy reallocation (<xref ref-type="bibr" rid="B15">Catarino et&#xa0;al., 2012</xref>), making it essential to study these hidden physiological responses for predicting their long-term viability and ecosystem dynamics.</p>
<p>Much of our knowledge of OA effects mainly comes from short to medium-term laboratory experiments (e.g. <xref ref-type="bibr" rid="B56">Stumpp et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B54">Spicer et&#xa0;al., 2011</xref>; <xref ref-type="bibr" rid="B66">Wood et&#xa0;al., 2008</xref>), but long-term exposure often reveals more complex responses. Long-term studies on tropical sea urchins, particularly those in the <italic>Echinometra</italic> genus, showed varied OA responses, depending on life stage and environmental context (<xref ref-type="bibr" rid="B62">Uthicke et&#xa0;al., 2020</xref>, <xref ref-type="bibr" rid="B63">2021</xref>; <xref ref-type="bibr" rid="B38">Karelitz et&#xa0;al., 2019</xref>). Moreover, studies on natural CO<sub>2</sub> emission points, also known as CO<sub>2</sub> vents, such as those at Ischia, Papua New Guinea and Canary Island, show that some populations of sea urchins exhibit adaptations to high CO<sub>2</sub> environments, with adults demonstrating resilience (<xref ref-type="bibr" rid="B24">Foo et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B19">Di Giglio et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B61">Uthicke et&#xa0;al., 2016</xref>, <xref ref-type="bibr" rid="B60">2019</xref>; <xref ref-type="bibr" rid="B28">Gonz&#xe1;lez-Delgado et&#xa0;al., 2024</xref>). In this sense, marine CO<sub>2</sub> vents, which create natural pH gradients, offer valuable scenarios to study the long-term effects of OA on marine ecosystems (<xref ref-type="bibr" rid="B27">Gonz&#xe1;lez-Delgado and Hern&#xe1;ndez, 2018</xref>; <xref ref-type="bibr" rid="B29">Gonz&#xe1;lez-Delgado et&#xa0;al., 2023</xref>), allowing scientists to investigate the biological responses of organisms, as well as their adaptive potential and resilience (<xref ref-type="bibr" rid="B35">Hofmann et&#xa0;al., 2014</xref>).</p>
<p>The Canary Islands, situated in the northeastern Atlantic Ocean, are home to the only subtropical marine CO<sub>2</sub> vent under investigation (<xref ref-type="bibr" rid="B32">Hern&#xe1;ndez et&#xa0;al., 2024</xref>). La Palma Island presents a continuous degassing of CO<sub>2</sub> in the south, in Fuencaliente (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1</bold>
</xref>) (<xref ref-type="bibr" rid="B14">Carracedo et al., 2001</xref>; <xref ref-type="bibr" rid="B48">Padr&#xf3;n et al., 2015</xref>). The features of the natural CO<sub>2</sub> vent include a pH gradient that decreases from 8.1 at open sea (150m from the vent center) to less than 7.4 at the source during low tide (<xref ref-type="bibr" rid="B26">Gonz&#xe1;lez-Delgado et&#xa0;al., 2021</xref>), allowing us to test the effect of decreasing pH on marine organisms in a situation analogous to future oceans.</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>
<bold>(A, B)</bold> Sampling sites at La Palma (Canary Islands, north-eastern Atlantic Ocean). Ambient sampling sites: El Muelle del Faro (A1), and La Bajita (A2) with pH ~8.1. Vent sampling sites: Playa del Faro (V1), and Las Cabras (V2) with pH ~7.5-7.8. Green dots are the sampling sites for <italic>Paracentrotus lividus</italic>, and purple dots are the sampling sites for <italic>Arbacia lixula</italic>. The maps used are distributed in the public domain (<ext-link ext-link-type="uri" xlink:href="https://www.grafcan.es/">https://www.grafcan.es/</ext-link>, last accessed: 30 January 2024).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-12-1500646-g001.tif"/>
</fig>
<p>This study investigates how the metabolic rates vary in two calcifying echinoderms, the sea urchins <italic>P. lividus</italic> and <italic>A. lixula</italic>, under different pH conditions during experiments in a laboratory and along a naturally acidified area. The main goal is to better understand their physiological responses to OA conditions predicted for the near future and whether those responses are a result of large phenotypic plasticity or local adaptation to long-term exposure to low pH. Specifically, we measured metabolic responses by analyzing respiration rates (VO<sub>2</sub> consumption) of organisms under experimental pH changes to assess their innate plasticity to pH shifts. Additionally, we compared organisms from natural CO<sub>2</sub> vent systems (pH ~7.5) and ambient sites (pH ~8.1) to identify potential adaptive differences between them. We expected organisms from more stable environments to be more affected by environmental changes, while those accustomed to greater environmental variability may respond more effectively, having adapted to wider fluctuations in abiotic factors (<xref ref-type="bibr" rid="B4">Asnicar et&#xa0;al., 2021</xref>). It is critical to have a clear understanding of when plastic responses occur instead of genetic adaptations and vice versa, as this knowledge is essential for predicting how OA affects the distribution and abundance of species and thus predicting the responses of marine organisms to ongoing climate change.</p>
</sec>
<sec id="s2" sec-type="materials|methods">
<title>Materials and methods</title>
<p>Our study is divided into two different parts. For investigating the plasticity response over time experiments were performed with individuals collected from ambient sites at pH 8.1 to measure their plasticity responses to low pH conditions over seven&#x2013;days. Adaptation and plasticity under changing pH was analyzed using individuals living along a pH gradient from a natural CO<sub>2</sub> vent system. Each part of the study was performed in a different laboratory and locality due to infrastructure and field requirements.</p>
<sec id="s2_1">
<title>Plasticity response over time</title>
<p>To measure metabolic responses to experimental changes of pH, we collected individuals by freediving at 0.5&#x2013;5 m depth at Cala Sant Francesc in Blanes (NW Mediterranean) (see <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S1</bold>
</xref>). All specimens collected were adults with volumes between 16.72&#x2013;38.6 mL in <italic>P. lividus</italic> and 8.55&#x2013;27.76 mL in <italic>A. lixula</italic>. Twelve individuals of <italic>P. lividus</italic> were collected in February 2024, six specimens were used for control conditions (individuals maintained at the same collection chemical parameters) and six specimens for experimental conditions (individuals collected and exposed to low pH)(<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S2</bold>
</xref> for chemical parameters). <italic>For A.lixula</italic> six specimens were collected in December 2023 for control conditions and six in May 2024 for experimental conditions (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S3</bold>
</xref> for chemical parameters). The individuals maintained at the collected parameters (control condition) were used to control the housing effect. All experiments were conducted at the University of Barcelona. Seawater pH at the sampling point was measured with the multiparametric sensor AAQ-RINKO by JFE Advantech Co., Ltd. Experiments were conducted separately for both species, following the same protocol.</p>
<p>Once in the laboratory, animals were acclimatized in a 25L settling tank. After 48 hours, they were transferred to experimental tanks (125L), containing individual 10L tanks for each replicate. Then, they were exposed to either control or experimental low-pH conditions for seven days as explained above. Oxygen consumption (VO<sub>2</sub> consumption) of each specimen was measured before placing it in the experimental tank (Day 0) and after 24h (Day 1), 48h (Day 2), 72h (Day 3), and 168h (Day 7) of the experiment. Animals were allowed to feed over the rocks placed at the bottom of the tank throughout the experiments. However, before each VO<sub>2</sub> measurement of the corresponding days, animals were starved for 12h to ensure a similar physiological status for all of them (<xref ref-type="bibr" rid="B30">Grosjean, 1998</xref>; <xref ref-type="bibr" rid="B53">Shpigel et&#xa0;al., 2004</xref>). Values of pH were achieved using a pH-controlling setup (Milwaukee PRO Digital controller) connected to a pH electrode which regulated pH by bubbling CO<sub>2</sub> gas into the seawater to maintain or reach the desired pH 7.5. Dissolved oxygen (DO) levels were maintained by the simultaneously bubbling air. Alkalinity was also checked using a SERA KH test to keep it constant at 11&#x2013;14 dKH by adding Reef Carbonate (4,000 meq/L) from Seachem when necessary. Temperature was experimentally maintained at the temperature of the collection day (16&#xb0;C&#xb1;1&#xb0;C) using a cooler (HAILEA HS28A).</p>
<p>Respiration rate (VO<sub>2</sub>; mg/kg/h) was independently measured per specimen using an intermittent-flow respirometry system (Q-box mini-AQUA aquatic respirometer, Qubit Systems) with the Logger Pro 3.16.1 software from Vernier Software Technology. A respirometer chamber was placed in a 20L aquarium equipped with a pH-controlling setup connected to a pH electrode to control the desired pH and a cooler to maintain a constant temperature. The total volume of the respirometry setup was 465ml. Once introduced into the chamber, the specimens were allowed 5 minutes to acclimate as performed by <xref ref-type="bibr" rid="B16">Christensen et&#xa0;al. (2011)</xref>. The decreasing DO levels were measured with three cycles of oxygen consumption consisting of a 5-minute flush phase, 7-minute rest phase, and 10-minutes of closed circulation. A run without specimen (blank run) was performed before each condition to control the background VO<sub>2</sub> consumption from microorganisms. Each specimen was weighed (g), and the height (mm) and the width (mm) were measured to calculate its volume (mL) using the <xref ref-type="bibr" rid="B23">Elliott et&#xa0;al. (2012)</xref> formula:</p>
<disp-formula id="eq.">
<label>.</label>
<mml:math display="block" id="M1">
<mml:mrow>
<mml:mfrac>
<mml:mn>4</mml:mn>
<mml:mn>3</mml:mn>
</mml:mfrac>
<mml:mi>&#x3c0;</mml:mi>
<mml:mo>&#xd7;</mml:mo>
<mml:msup>
<mml:mrow>
<mml:mo>(</mml:mo>
<mml:mfrac>
<mml:mn>1</mml:mn>
<mml:mn>2</mml:mn>
</mml:mfrac>
<mml:mi>D</mml:mi>
<mml:mi>i</mml:mi>
<mml:mi>a</mml:mi>
<mml:mi>m</mml:mi>
<mml:mi>e</mml:mi>
<mml:mi>t</mml:mi>
<mml:mi>e</mml:mi>
<mml:mi>r</mml:mi>
<mml:mo>)</mml:mo>
</mml:mrow>
<mml:mn>2</mml:mn>
</mml:msup>
<mml:mo>&#xd7;</mml:mo>
<mml:mfrac>
<mml:mn>1</mml:mn>
<mml:mn>2</mml:mn>
</mml:mfrac>
<mml:mi>H</mml:mi>
<mml:mi>e</mml:mi>
<mml:mi>i</mml:mi>
<mml:mi>g</mml:mi>
<mml:mi>h</mml:mi>
<mml:mi>t</mml:mi>
</mml:mrow>
</mml:math>
</disp-formula>
<p>The respiration rate for each specimen was calculated with the difference between final VO<sub>2</sub> and background VO<sub>2</sub> (blank run).</p>
</sec>
<sec id="s2_2">
<title>Adaptation and rapid response under natural pH gradients</title>
<p>To determine potential differences in metabolic rates for individuals that naturally live under different pH values, we collected adult individuals of both species in La Palma (Canary Islands, Spain) in four different places in January 2024 (see <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S1</bold>
</xref>). We sampled at two &#x201c;Ambient&#x201d; sites (pH 8.1) at Muelle del Faro (A1) for <italic>P. lividus</italic> and La Bajita (A2) for both species, and two CO<sub>2</sub> &#x201c;Vent&#x201d; sites at Playa del Faro (V1) for both species with a pH fluctuation between 8.01&#x2013;7.4, and Las Cabras (V2) for <italic>A. lixula</italic>, with a pH fluctuation of 8.0&#x2013;7.7 (See <xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S1</bold>
</xref>) (<xref ref-type="bibr" rid="B26">Gonz&#xe1;lez-Delgado et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B33">Hern&#xe1;ndez et&#xa0;al., 2016</xref>). Specimens were collected following the same criteria applied before. There were some differences in the sampling scheme and experimental design between species due to their different abundances at the sampling points. The analyses were conducted at the Observatorio Marino de Cambio Clim&#xe1;tico (OMACC) in Fuencaliente, La Palma Island.</p>
<p>The experiments were conducted using freshly collected seawater from the sampling points keeping the variables salinity and temperature constant (see <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Tables S2</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S3</bold>
</xref>). The temperature, salinity, and pH were measured at each sampling point using a multiparametric sensor (AAQ-RINKO by JFE Advantech Co., Ltd.) and specimens were acclimatized at the same seawater parameters as the collection site. Unfortunately, due to infrastructure limitations, experiments at the OMACC had to be limited to a 24-hour acclimatization. After acclimatization in the settling tank (25L), the specimens were transferred to an experimental tank (125L), with individual tanks (10L) inside for each replicate. Following a 24-hour exposure period to the conditions described below, the VO<sub>2</sub> consumption was measured for each specimen after 12h of starvation and following the same protocol previously detailed.</p>
<p>To investigate if metabolic rates vary due to local adaptation to pH, we tested individuals from the sampling sites under their natural conditions, hereafter basal conditions. For <italic>P. lividus</italic> (N=24), we collected eight samples from each of the three locations: Ambient 1 (A1A, pH = 8.1), Ambient 2 (A2A, pH = 8.1), and Vent 1 (V1V, pH = 7.5). For <italic>A. lixula</italic> (N=24), we took eight samples from three locations as well: Ambient 2 (A2A, pH = 8.1), Vent 1 (V1V, pH = 7.5), and Vent 2 (V2V, pH = 7.8). <italic>A. lixula</italic> was not present in the Ambient 1 site, thus we collected only ambient specimens from La Bajita (A2). Therefore, achieving equivalent sampling points for both species was not feasible, although the design was maintained as initially planned.</p>
<p>Finally, to determine whether specimens which are geographically closely related but living under different pH conditions do display different immediate responses to pH changes, we experimentally varied pH values in the laboratory, hereafter experimental conditions. In <italic>P. lividus</italic>, eight specimens from the Vent 1 were exposed to ambient pH (V1A: pH=8.1), and eight specimens from Ambient 2 were exposed to low pH (A2V: pH=7.5). In <italic>A. lixula</italic>, eight specimens from Ambient 2 were exposed to low pH (A2V: pH= 7.5). The abundance of individuals of <italic>A. lixula</italic> in both vent sites was low, which prevented us from conducting the exposure of specimens from the vent to ambient pH.</p>
</sec>
<sec id="s2_3">
<title>Statistical analysis</title>
<p>For the plasticity response over time experiments, we fitted mixed-effects models (<xref ref-type="bibr" rid="B31">Harrison et&#xa0;al., 2018</xref>) to evaluate the interaction between TREAT (Control <italic>vs</italic> pH 7.5) and DAY (Day 0, Day 1, Day 2, Day 3 and Day 7) on VO<sub>2</sub> consumption, incorporating random effects for individuals, thereby accounting for repeated measures. The analyses were conducted in RStudio version 4.2.2 (2022-10-31; <xref ref-type="bibr" rid="B52">R Core Team, 2022</xref>) and using <italic>lme4 package</italic> (<xref ref-type="bibr" rid="B6">Bates et&#xa0;al., 2015</xref>). Different distributions (Normal and Gamma) and log transformations were tested. Models were selected based on the lowest AIC and convergence (<xref ref-type="bibr" rid="B2">Akaike, 1998</xref>). To further explore the interaction effects, <italic>post-hoc</italic> and pairwise comparisons were performed using <italic>emmeans</italic> package (<xref ref-type="bibr" rid="B42">Lenth, 2024</xref>). To illustrate the results, box plots were created using the <italic>ggplot2</italic> package (<xref ref-type="bibr" rid="B65">Wickham, 2016</xref>). The normality of the residuals of the models was tested with the Shapiro-Wilk test.</p>
<p>For investigating the adaptation and rapid response under natural pH gradients, we compared the VO<sub>2</sub> consumption among individuals in their basal and experimental conditions. We normalized the VO<sub>2</sub> values of <italic>A. lixula</italic> using a log transformation whereas the transformation was not needed for <italic>P. lividus</italic> data. Initially, normality of the residuals was checked using the Shapiro-Wilk test, while the homogeneity of variances was evaluated for the variables &#x2018;meanVO<sub>2</sub>&#x2019; (dependent variable) and &#x2018;pH&#x2019; (independent variable) using the Levene test through <italic>rstatix</italic> package (<xref ref-type="bibr" rid="B39">Kassambara, 2023</xref>). An analysis of variance (ANOVA) was performed in RStudio followed by the <italic>post-hoc</italic> Tukey test through the function TukeyHSD (<xref ref-type="bibr" rid="B52">R Core Team, 2022</xref>) to determine differences between the respiration rates from vent and ambient specimens and at different pH conditions. Boxplots were created for data visualization using the <italic>ggplot2</italic> package.</p>
</sec>
</sec>
<sec id="s3" sec-type="results">
<title>Results</title>
<sec id="s3_1">
<title>Plasticity response over time</title>
<p>The VO<sub>2</sub> consumption of both species was log-transformed to normalize the data for subsequent analyses. A linear mixed model was then employed for <italic>P. lividus</italic>, as its residuals were normally distributed, whereas a generalized mixed model with gamma distribution was applied for <italic>A. lixula</italic>, to account for its non-normal distribution. The best model in both species followed the formula: VO<sub>2</sub>~DAY*TREAT+(1|IND). The Shapiro-Wilk test confirmed the normal distribution of residuals for both species after applying the respective models (<italic>P. lividus</italic>, p = 0.053; <italic>A. lixula</italic>, p = 0.07).</p>
<p>We assessed mean VO<sub>2</sub> across days under control conditions for each species to account for potential housing effects, we assessed mean VO<sub>2</sub> across days under control conditions for each species. In <italic>P. lividus</italic>, the VO<sub>2</sub> consumption under control conditions ranged from 7.70 to 24.65 mg/kg/h over the seven days, showing minor variations in respiration rates over time (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S4</bold>
</xref>). Although comparisons among some days were significantly different (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Tables S5</bold>
</xref>), the overall pattern remained stable, indicating no major housing effect. For <italic>A. lixula</italic>, there was no evidence of housing effect, as VO<sub>2</sub> consumption range of 8.00 to 18.13 mg/kg/h and showed no significant differences among days under control conditions (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Tables S4</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S5</bold>
</xref>).</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>Plasticity responses over time. Means of VO<sub>2</sub> consumption from all the specimens on different experimental conditions of pH in <italic>Paracentrotus lividus</italic> <bold>(A)</bold> and <italic>Arbacia lixula</italic> <bold>(B)</bold>. For control conditions the pH was 8.1 and for experiment conditions the pH was 7.5 in both species. The pH during the Day 0 was 8.1 in both species and conditions. The numbers above the bars indicate the significance of pairwise comparisons (padj&lt;0.05) among days in experimental conditions. Asterisks below pH treatment of each day indicate (padj&lt;0.05) between control and experimental conditions.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-12-1500646-g002.tif"/>
</fig>
<p>In <italic>P. lividus</italic>, VO<sub>2</sub> consumption during the experimental condition was consistent on Day 0, Day 2, and Day 7 (11.00&#x2013;31.90 mg/kg/h) but spiked on Day 1 and Day 3 (98.50&#x2013; 79.80 mg/kg/h). In <italic>A. lixula</italic> the VO<sub>2</sub> consumption was stable on Day 0, Day 2, and Day 7 (42.60&#x2013;57.20 mg/kg/h), but dropped significantly on Day 1, and Day 3 (17.40&#x2013;16.31 mg/kg/h) (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Material Tables S4</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S5</bold>
</xref>). Interestingly, for each species the VO<sub>2</sub> consumption before low pH exposure (Day 0) and the last day of experiment at low pH 7.5 (Day 7) showed similar values. However, only <italic>A. lixula</italic> showed no significant difference among those values (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S5</bold>
</xref>).</p>
</sec>
<sec id="s3_2">
<title>Adaptation and rapid response under natural pH gradients</title>
<p>The Shapiro-Wilk test confirmed normal distribution of the residuals for both, <italic>P. lividus</italic> (p = 0.68), and <italic>A. lixula</italic> (p = 0.73). The Levene test proved homogeneity of variances for both, <italic>P. lividus</italic> (p = 0.29), and <italic>A. lixula</italic> (p = 0.13).</p>
<p>The ANOVA analysis indicated significant differences among the measured respiration rates in both species (<italic>P. lividus</italic>: F= 20.94, p &lt;0.05; <italic>A. lixula</italic>: F= 25.17, p &lt; 0.05) across all conditions, indicating differences in the VO<sub>2</sub> consumption after the 24 hours of the experiment. Pairwise comparisons (Tukey tests) found no significant differences in basal VO<sub>2</sub> consumption between specimens from the Vent and Ambient sites in both species (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Tables S6</bold>
</xref>&#x2013;<xref ref-type="supplementary-material" rid="SM1">
<bold>8</bold>
</xref>). Basal conditions in <italic>P. lividus</italic>, both ambient (A1 the closest to the Vent site and A2 the furthest to the Vent site) and the Vent showed a similar VO<sub>2</sub> consumption (29.00 mg/kg/h). Moreover, in <italic>A. lixula</italic>, both Vents and the Ambient ranged from 27.50 to 53.20 mg/kg/h. Significant differences were found between the experimental and the basal conditions in both species (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Tables S6</bold>
</xref>&#x2013;<xref ref-type="supplementary-material" rid="SM1">
<bold>8</bold>
</xref>). <italic>P. lividus</italic> from ambient sites exposed to pH 7.5 showed a mean VO<sub>2</sub> consumption (A2V = 150.90 mg/kg/h) twice as high as the individuals from the Vent exposed to ambient pH (V1A = 74.20 mg/kg/h) (<xref ref-type="fig" rid="f3">
<bold>Figure&#xa0;3</bold>
</xref>). <italic>A. lixula</italic> from the Ambient exposed to pH 7.5 (A2V = 276.41 mg/kg/h) increased 10 times the VO<sub>2</sub> consumption compared to the basal levels (27.50&#x2013;53.20 mg/kg/h).</p>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p>Adaptation and rapid responses to pH changes. Means of VO<sub>2</sub> consumption from all the specimens on different experimental conditions of pH in <italic>Paracentrotus lividus</italic> <bold>(A)</bold> and <italic>Arbacia lixula</italic> <bold>(B)</bold>. The exposure to each condition lasted 24 hours in both species. The numbers above the bars indicate the significance of pairwise comparisons (padj&lt;0.05) among days in experimental conditions.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-12-1500646-g003.tif"/>
</fig>
</sec>
</sec>
<sec id="s4" sec-type="discussion">
<title>Discussion</title>
<p>Echinoderms, as marine calcifiers, are among the most sensitive organisms to future OA conditions (<xref ref-type="bibr" rid="B12">Byrne and Hern&#xe1;ndez, 2020</xref>; <xref ref-type="bibr" rid="B11">Byrne and Fitzer, 2019</xref>). Studies that combine laboratory experiments and OA natural analogues are useful for assessing the stress response and long-term effects of OA (<xref ref-type="bibr" rid="B32">Hern&#xe1;ndez et&#xa0;al., 2024</xref>). In the present study, we combined the study of short, medium, and long-term metabolic responses to OA conditions in two keystone species of sea urchins.</p>
<p>The ability of sea urchins such as <italic>P. lividus</italic> and <italic>A. lixula</italic> to cope with pH fluctuations stems from their coelomic fluid&#x2019;s buffering capacity (<xref ref-type="bibr" rid="B13">Calosi et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B19">Di Giglio et&#xa0;al., 2020</xref>). Moreover, other physiological processes such as osmoregulation, and excretion, are also interrelated for maintaining metabolic activities (<xref ref-type="bibr" rid="B15">Catarino et&#xa0;al., 2012</xref>). After seven days of experiments at acidified conditions (pH=7.5), respiration rates of both species reached similar VO<sub>2</sub> levels to Day 0 (pH=8.1) before the low pH exposure, indicating a potential recovery of the basal respiration rates. However, <italic>A. lixula</italic> showed significant differences when compared to the respiration rates found in the controls, possibly related to the sampling season. The specimens for the control conditions were collected at the end of December of 2023 while the specimens used for the experimental conditions were collected at the beginning of May of 2024. Although similar seawater temperature (16&#xb0;C &#xb1; 1&#xb0;C), other internal physiological (such as reproductive season) and external ecological (such as food supply) processes might be influencing the respiration rate of collected specimens (<xref ref-type="bibr" rid="B10">Burton et&#xa0;al., 2011</xref>).</p>
<p>During the seven days of low pH exposure, VO<sub>2</sub> consumption alternate between increases and decreases in both species, following opposite patterns. In <italic>P. lividus</italic>, elevated respiration rates may be explained through metabolic upregulation to compensate for tissue acidosis (<xref ref-type="bibr" rid="B56">Stumpp et&#xa0;al., 2012</xref>). This finding aligns with <xref ref-type="bibr" rid="B13">Calosi et&#xa0;al. (2013)</xref>, who reported that <italic>P. lividus</italic> adjusts to low pH by accumulating bicarbonates, a buffering mechanism likely requiring increased metabolic activity. In contrast, <italic>A. lixula</italic> exhibited an initial decrease in VO<sub>2</sub> consumption, likely due to its non-bicarbonate buffering mechanisms requiring less metabolic adjustment (<xref ref-type="bibr" rid="B13">Calosi et&#xa0;al., 2013</xref>). These distinct physiological responses underline the species-specific strategies for coping with low pH.</p>
<p>Both species show potential for adaptation and/or long-term acclimatization in physiological responses since the basal respiration rates showed no differences between populations from the ambient sites (pH=8.1) and the CO<sub>2</sub> vent sites (pH=7.5 and 7.8) at La Palma. <xref ref-type="bibr" rid="B45">Migliaccio et&#xa0;al. (2019)</xref> also found a lack of differences in <italic>P. lividus</italic> respiration rates between specimens from a CO<sub>2</sub> vent and ambient sites, suggesting physiological mechanisms to survive under OA. Acclimatization to OA over time is not rare in sea urchins since several studies have already found no differences in respiration rates between pH treatments in the long-term, for instance, <italic>P. lividus</italic> (<xref ref-type="bibr" rid="B15">Catarino et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B17">Cohen-Rengifo et&#xa0;al., 2019</xref>), <italic>Echinometra</italic> sp (<xref ref-type="bibr" rid="B4">Asnicar et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B46">Moulin et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B62">Uthicke et&#xa0;al., 2020</xref>, <xref ref-type="bibr" rid="B63">2021</xref>), <italic>Hemicentrotus pulcherrimus</italic> (<xref ref-type="bibr" rid="B41">Kurihara et&#xa0;al., 2013</xref>), <italic>Strongylocentrotus droebachiensis</italic> (<xref ref-type="bibr" rid="B56">Stumpp et&#xa0;al., 2012</xref>), and <italic>Sterechinus neumayeri</italic> (<xref ref-type="bibr" rid="B57">Suckling et&#xa0;al., 2015</xref>). However, studies such as <xref ref-type="bibr" rid="B36">Holtmann (2013)</xref> and <xref ref-type="bibr" rid="B43">Mar&#x10d;eta et&#xa0;al. (2020)</xref>, indicate that maintaining coelomic fluid pH may involve metabolic trade-offs impacting growth, reproduction and immune functions. In this study, the sex of the individuals was not recorded to avoid sacrificing them. <xref ref-type="bibr" rid="B43">Mar&#x10d;eta et&#xa0;al. (2020)</xref> found that females exposed to acidified conditions showed reduced gonad quality and impaired oocyte development. These findings suggests that sex-specific differences could exist in the responses of <italic>P. lividus</italic> and <italic>A. lixula</italic> to OA, with females potentially being more sensitive due to the energetic demands of reproduction. While maintaining acid-base homeostasis is energetically demanding and can reduce the energy available for other essential processes (<xref ref-type="bibr" rid="B15">Catarino et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B18">Collard et&#xa0;al., 2013</xref>) it may not fully explain the shifts in energy budgets observed in OA environments. Indeed, other cofounding factors could contribute to a shift in energy budgets and VO<sub>2</sub> consumption rates, such as biomineralization (<xref ref-type="bibr" rid="B40">Kurihara et&#xa0;al., 2012</xref>). These trade-offs further highlight the metabolic challenges associated with ocean acidification (<xref ref-type="bibr" rid="B22">Dupont and Thorndyke, 2012</xref>; <xref ref-type="bibr" rid="B56">Stumpp et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B34">Hernroth et&#xa0;al., 2011</xref>).</p>
<p>To assess the phenotypic plasticity, individuals from ambient sites in La Palma of both species were placed under short-term exposure to low pH conditions (pH=7.5). VO<sub>2</sub> consumption increased significantly, especially in <italic>A. lixula</italic>, indicating a stress response to the sudden change. Interestingly, <italic>P. lividus</italic> showed a higher increase in VO<sub>2</sub> consumption when ambient individuals were exposed to low pH conditions (A-V) compared to vent specimens exposed to ambient pH conditions (V-A). This might be related to the natural exposure to fluctuating pH of individuals living at vent sites, ranging from pH=8.1 to pH=7.4 during tides (<xref ref-type="bibr" rid="B26">Gonz&#xe1;lez-Delgado et&#xa0;al., 2021</xref>) while organisms from ambient sites live under constant pH values (pH=8.1). Differences in food consumption at varying pH levels may have influenced the observed VO<sub>2</sub> patterns, as sea urchins might adjust feeding to cope with acidification stress, aligning with other studies (e.g., <xref ref-type="bibr" rid="B20">Dupont et&#xa0;al., 2010</xref>). However, food consumption was not directly measured in this study. Populations exposed to high environmental variability may develop tolerance to environmental stressors (<xref ref-type="bibr" rid="B4">Asnicar et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B58">Teixid&#xf3; et&#xa0;al., 2020</xref>) as well as maternal anticipatory effects (<xref ref-type="bibr" rid="B50">Palombo et&#xa0;al., 2023</xref>; <xref ref-type="bibr" rid="B38">Karelitz et&#xa0;al., 2019</xref>; <xref ref-type="bibr" rid="B59">Thor and Dupont, 2015</xref>). Studies have shown that echinoderms exhibit reduced sensitivity to OA when exposed to a highly variable environmental history (<xref ref-type="bibr" rid="B5">Asnicar et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B37">Kapsenberg and Cyronak, 2019</xref>) indicating higher phenotypic plasticity in specimens from more fluctuating environments, such as the CO<sub>2</sub> vent sites studied here. In those lines, high pH variability areas have been proposed as OA refugia, offering adaptive advantages for marine organisms (<xref ref-type="bibr" rid="B7">Bednar&#x161;ek et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B25">Garc&#xed;a et&#xa0;al., 2018</xref>; <xref ref-type="bibr" rid="B37">Kapsenberg and Cyronak, 2019</xref>). Thus, CO<sub>2</sub> vent systems in particular, may serve as significant OA refugia to consider.</p>
<p>While <italic>P. lividus</italic> and <italic>A. lixula</italic> may acclimate their respiration rates to low pH over time, understanding their long-term physiological responses is key to predicting viability and ecosystem dynamics. This study suggests that adult sea urchins of both species can potentially acclimate to low pH conditions over the long-term, supporting previous findings (<xref ref-type="bibr" rid="B13">Calosi et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B18">Collard et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B19">Di Giglio et&#xa0;al., 2020</xref>; and <xref ref-type="bibr" rid="B45">Migliaccio et&#xa0;al., 2019</xref>). Incorporating sex identification and measuring feeding rates could reveal sex-specific differences and clarify dietary roles in metabolic homeostasis. Future research combining physiological data with population genomics and transcriptomics could uncover adaptive mechanisms and their inheritance.</p>
</sec>
</body>
<back>
<sec id="s5" sec-type="data-availability">
<title>Data availability statement</title>
<p>The original contributions presented in the study are included in the article/supplementary material. Further inquiries can be directed to the corresponding authors.</p>
</sec>
<sec id="s6" sec-type="author-contributions">
<title>Author contributions</title>
<p>RF: Conceptualization, Data curation, Formal analysis, Investigation, Methodology, Writing &#x2013; original draft, Writing &#x2013; review &amp; editing, Visualization. VA: Conceptualization, Formal analysis, Investigation, Methodology, Writing &#x2013; original draft, Writing &#x2013; review &amp; editing, Data curation, Funding acquisition, Visualization. MM: Data curation, Formal analysis, Methodology, Writing &#x2013; review &amp; editing, Investigation, Visualization. JH: Conceptualization, Methodology, Resources, Supervision, Writing &#x2013; review &amp; editing, Funding acquisition. SG: Writing &#x2013; review &amp; editing, Investigation, Methodology. RP: Conceptualization, Funding acquisition, Methodology, Project administration, Resources, Supervision, Validation, Visualization, Writing &#x2013; review &amp; editing.</p>
</sec>
<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 funded by the Spanish Government projects ACIDOMIC (CNS2022-135968 funded by MCIN/AEO/10.13039/501100011033 and, by the European Union NextGeneration EU/PRTR), ENVIOME (PID2021-128094NB-I00/MCIN/AEI/10.13039/501100011033/and FEDER una manera de hacer Europa), and ADAPTIVE (PGC2018-100735-B-I00/MCIU/AEI/FEDER, UE), and a &#x201c;Ram&#xf3;n y Cajal&#x201d; contract to RP (RYC2018-025070-I), the project &#x201c;DIVERGEN- Ayudas Fundaci&#xf3;n BBVA a Proyectos Investigaci&#xf3;n Cient&#xed;fica 2021&#x201d;, and the Marie Sklodowska-Curie grant (agreement No 101105400 funded by the European Union&#x2019;s Horizon Europe research and innovation program to VA). This paper is a contribution of the Consolidated Research Team: 2021 SGR 01271 Marine Biodiversity and Evolution (MBE).</p>
</sec>
<ack>
<title>Acknowledgments</title>
<p>Thanks to the Observatorio Marino de Cambio Clim&#xe1;tico (OMACC) from La Palma for letting us use their facilities at the Fuencaliente Lighthouse to carry out these experiments; to the QUIMA group of IOCAG, (ULPGC, Spain) for providing us with the chemical data of the sampling sites (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S2</bold>
</xref>); to Dr. Quesada, from the Museum of Natural Science of Barcelona, for assisting us with the statistical analysis of our data; to the four reviewers for their valuable comments and suggestions, which have greatly improved the quality of this manuscript and its clarity. Also, thanks to Nancy and Adam for their help and support during our field trips to Fuencaliente, La Palma Island.</p>
</ack>
<sec id="s8" 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="s9" 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="s10" 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.2025.1500646/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fmars.2025.1500646/full#supplementary-material</ext-link>
</p>
<supplementary-material xlink:href="Table1.docx" id="SM1" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document"/>
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