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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.2025.1520573</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Marine Science</subject>
<subj-group>
<subject>Brief Research Report</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>New findings into the genetic population structure of two commercially valuable and threatened sharks, <italic>Mustelus mustelus</italic> (Linnaeus, 1758) and <italic>M. punctulatus</italic> (Risso, 1827), allow refining management strategy in the Central Mediterranean Sea</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name>
<surname>Barbato</surname>
<given-names>Matteo</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="aff" rid="aff3">
<sup>3</sup>
</xref>
<xref ref-type="author-notes" rid="fn001">
<sup>*</sup>
</xref>
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<contrib contrib-type="author">
<name>
<surname>Bonanomi</surname>
<given-names>Sara</given-names>
</name>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
<xref ref-type="aff" rid="aff4">
<sup>4</sup>
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<name>
<surname>Borme</surname>
<given-names>Diego</given-names>
</name>
<xref ref-type="aff" rid="aff5">
<sup>5</sup>
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<name>
<surname>&#x106;etkovi&#x107;</surname>
<given-names>Ilija</given-names>
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<xref ref-type="aff" rid="aff6">
<sup>6</sup>
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<contrib contrib-type="author">
<name>
<surname>Colloca</surname>
<given-names>Francesco</given-names>
</name>
<xref ref-type="aff" rid="aff7">
<sup>7</sup>
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<contrib contrib-type="author">
<name>
<surname>Di Lorenzo</surname>
<given-names>Manfredi</given-names>
</name>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
<xref ref-type="aff" rid="aff8">
<sup>8</sup>
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<contrib contrib-type="author">
<name>
<surname>Marino</surname>
<given-names>Ilaria A. M.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
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<contrib contrib-type="author">
<name>
<surname>Mazzoldi</surname>
<given-names>Carlotta</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
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<sup>3</sup>
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<contrib contrib-type="author">
<name>
<surname>Pe&#x161;i&#x107;</surname>
<given-names>Ana</given-names>
</name>
<xref ref-type="aff" rid="aff6">
<sup>6</sup>
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<contrib contrib-type="author">
<name>
<surname>Sala</surname>
<given-names>Antonello</given-names>
</name>
<xref ref-type="aff" rid="aff4">
<sup>4</sup>
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<contrib contrib-type="author">
<name>
<surname>Zane</surname>
<given-names>Lorenzo</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="aff" rid="aff3">
<sup>3</sup>
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<contrib contrib-type="author">
<name>
<surname>Mezzavilla</surname>
<given-names>Massimo</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
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<aff id="aff1">
<sup>1</sup>
<institution>Department of Biology, University of Padova</institution>, <addr-line>Padova</addr-line>, <country>Italy</country>
</aff>
<aff id="aff2">
<sup>2</sup>
<institution>National Inter-University Consortium for Marine Sciences (CoNISMa)</institution>, <addr-line>Rome</addr-line>, <country>Italy</country>
</aff>
<aff id="aff3">
<sup>3</sup>
<institution>National Biodiversity Future Center (NBFC)</institution>, <addr-line>Palermo</addr-line>, <country>Italy</country>
</aff>
<aff id="aff4">
<sup>4</sup>
<institution>Italian National Research Council (CNR), Institute for Marine Biological Resources and Biotechnologies (IRBIM)</institution>, <addr-line>Ancona</addr-line>, <country>Italy</country>
</aff>
<aff id="aff5">
<sup>5</sup>
<institution>National Institute of Oceanography and Applied Geophysics (OGS)</institution>, <addr-line>Trieste</addr-line>, <country>Italy</country>
</aff>
<aff id="aff6">
<sup>6</sup>
<institution>Institute of Marine Biology, University of Montenegro</institution>, <addr-line>Kotor</addr-line>, <country>Montenegro</country>
</aff>
<aff id="aff7">
<sup>7</sup>
<institution>Department of Integrative Marine Ecology, Stazione Zoologica Anton Dohrn</institution>, <addr-line>Rome</addr-line>, <country>Italy</country>
</aff>
<aff id="aff8">
<sup>8</sup>
<institution>Department of Integrative Marine Ecology, Sicily Marine Centre, Stazione Zoologica Anton Dohrn</institution>, <addr-line>Palermo</addr-line>, <country>Italy</country>
</aff>
<author-notes>
<fn fn-type="edited-by">
<p>Edited by: Brendan Shea, Beneath the Waves, Inc., United States</p>
</fn>
<fn fn-type="edited-by">
<p>Reviewed by: Edgardo Diaz-Ferguson, Estaci&#xf3;n Cient&#xed;fica Coiba AIP, Panama</p>
<p>Lisa M. Crawford, Stony Brook University, United States</p>
<p>Jo&#xe3;o Pedro Barreiros, University of the Azores, Portugal</p>
</fn>
<fn fn-type="corresp" id="fn001">
<p>*Correspondence: Matteo Barbato, <email xlink:href="mailto:matte.barbato@gmail.com">matte.barbato@gmail.com</email>
</p>
</fn>
</author-notes>
<pub-date pub-type="epub">
<day>07</day>
<month>02</month>
<year>2025</year>
</pub-date>
<pub-date pub-type="collection">
<year>2025</year>
</pub-date>
<volume>12</volume>
<elocation-id>1520573</elocation-id>
<history>
<date date-type="received">
<day>31</day>
<month>10</month>
<year>2024</year>
</date>
<date date-type="accepted">
<day>13</day>
<month>01</month>
<year>2025</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#xa9; 2025 Barbato, Bonanomi, Borme, &#x106;etkovi&#x107;, Colloca, Di Lorenzo, Marino, Mazzoldi, Pe&#x161;i&#x107;, Sala, Zane and Mezzavilla</copyright-statement>
<copyright-year>2025</copyright-year>
<copyright-holder>Barbato, Bonanomi, Borme, &#x106;etkovi&#x107;, Colloca, Di Lorenzo, Marino, Mazzoldi, Pe&#x161;i&#x107;, Sala, Zane and Mezzavilla</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>Elasmobranch species are the direct or accidental catch of fisheries and can have a commercial importance. In the Mediterranean Sea, a long-term period of overfishing brought several demersal elasmobranchs to be depleted and threatened by extinction, due to vulnerability related to their life history traits. In such exploited species, information on genetic diversity and connectivity is lacking and should be collected to identify management units. In this study, we focused on two threatened smooth-hound species, <italic>Mustelus Mustelus</italic> (Linnaeus, 1758) and <italic>M. punctulatus</italic> (Risso, 1827), whose abundance and distribution showed a decline at the Mediterranean regional level in the last century. Thanks to an opportunistic yet extensive sampling, we obtained the largest subregional collection of specimens for genetic analysis so far. In total, 86 and 214 specimens of <italic>M. mustelus</italic> and <italic>M. punctulatus</italic> were collected between 2016 and 2020 in the Adriatic Sea and the Strait of Sicily. We assessed the population genetic structure typing 17 microsatellites and sequencing part of the mitochondrial control region in both species. We observed a substantial nuclear and mitochondrial genetic structure when accounting for the geographical sampling area for both species. Our results indicate the presence of at least two genetic stocks for each of the two species: one in the Strait of Sicily and the other in the Adriatic Sea. This study provides valuable data that should be integrated into a broader approach to define management units, improving the development of an effective management strategy for these threatened species in the Central Mediterranean Sea.</p>
</abstract>
<kwd-group>
<kwd>Triakidae</kwd>
<kwd>connectivity</kwd>
<kwd>elasmobranch</kwd>
<kwd>conservation</kwd>
<kwd>management</kwd>
</kwd-group>
<contract-sponsor id="cn001">Ministero dell&#x2019;Istruzione, dell&#x2019;Universit&#xe0; e della Ricerca<named-content content-type="fundref-id">10.13039/501100003407</named-content>
</contract-sponsor>
<counts>
<fig-count count="3"/>
<table-count count="1"/>
<equation-count count="0"/>
<ref-count count="77"/>
<page-count count="11"/>
<word-count count="4906"/>
</counts>
<custom-meta-wrap>
<custom-meta>
<meta-name>section-in-acceptance</meta-name>
<meta-value>Discoveries</meta-value>
</custom-meta>
</custom-meta-wrap>
</article-meta>
</front>
<body>
<sec id="s1" sec-type="intro">
<label>1</label>
<title>Introduction</title>
<p>The decline of elasmobranchs worsened during the late 20th and early 21st centuries, due to extensive global overexploitation of their populations (<xref ref-type="bibr" rid="B26">Dulvy et&#xa0;al., 2021</xref>). Their life history traits, including the slow growth rate and low fecundity, compared to other marine species, make elasmobranchs vulnerable to overfishing (<xref ref-type="bibr" rid="B27">Dulvy et&#xa0;al., 2017</xref>). Non-random space use (i.e., site fidelity and philopatry) and reproductive aggregations further contribute to their vulnerability (<xref ref-type="bibr" rid="B38">Hueter et&#xa0;al., 2005</xref>; <xref ref-type="bibr" rid="B14">Chapman et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B37">Hirschfeld et&#xa0;al., 2021</xref>). The conservation status of many elasmobranch species highlights the need for a scientific-tailored management plan (<xref ref-type="bibr" rid="B26">Dulvy et&#xa0;al., 2021</xref>). The concept of stock is a fundamental pillar in fishery management defined as an intraspecific group of randomly mating individuals with temporal or spatial integrity (<xref ref-type="bibr" rid="B40">Ihssen et&#xa0;al., 1981</xref>). The identification of genetic stock is a key step that could help delineate the geographic boundaries of populations characterized by consistent genetic distinctiveness (i.e., genetic structure) where divergence in allele frequencies is found at both nuclear and mitochondrial loci (<xref ref-type="bibr" rid="B58">Moritz, 1994</xref>). Ultimately, the combination of all ecological and biological traits (e.g., phenotype, movement, and genetics) leads to the definition of a management unit at different temporal organization (<xref ref-type="bibr" rid="B1">Abaunza et&#xa0;al., 2008</xref>; <xref ref-type="bibr" rid="B10">Cadrin et&#xa0;al., 2014</xref>).</p>
<p>Among evolutionary process, gene flow and genetic drift are two opposite forces that determine the genetic structure of a population and the genetic connectivity between adjacent populations. When gene flow occurs, the migratory movement and the successful mating of one or more individuals may contribute to the gene pool of a recipient population (<xref ref-type="bibr" rid="B10">Cadrin et&#xa0;al., 2014</xref>). Unlike species with larval stage, elasmobranchs are characterized by an active dispersal that occurs at the late juvenile/adult stage. Migrants may join an adjacent population without contribution to gene flow if successful mating relies on behavioral knowledge to engage with foreign reproductive aggregation (<xref ref-type="bibr" rid="B59">Ovenden, 2013</xref>). In elasmobranch species, genetic connectivity is influenced by maximum depth of occurrence, maximum body size, habitat, and species-specific dispersal potential (<xref ref-type="bibr" rid="B37">Hirschfeld et&#xa0;al., 2021</xref>).</p>
<p>In the Mediterranean Sea, elasmobranch species are overfished, and their decline was reported (<xref ref-type="bibr" rid="B31">Ferretti et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B4">Barausse et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B76">Walls and Dulvy, 2021</xref>). The common smooth-hound (<italic>Mustelus mustelus</italic>), hereafter <italic>Mm</italic>, and the black-spotted smooth-hound (<italic>M. punctulatus</italic>), hereafter <italic>Mp</italic>, are among the most important landed shark species in the Mediterranean Sea, as bycatch and being seasonally targeted by small-scale fishery, operating in the Northern Adriatic Sea and in the Strait of Sicily, two of the few Mediterranean areas where these species still show viable populations (<xref ref-type="bibr" rid="B4">Barausse et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B18">Colloca et&#xa0;al., 2017</xref>, <xref ref-type="bibr" rid="B17">Colloca et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B11">Carpentieri et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B21">Di Lorenzo et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B50">Maioli et&#xa0;al., 2023</xref>). Indeed, both species suffered a steep decline in the last century, with a strong contraction of their occurrence and abundance (<xref ref-type="bibr" rid="B18">Colloca et&#xa0;al., 2017</xref>), and they are classified in the International Union for Conservation of Nature (IUCN) red list as endangered (<italic>Mm</italic>) and vulnerable (<italic>Mp</italic>) at the global level (<xref ref-type="bibr" rid="B41">Jabado et&#xa0;al., 2021a</xref>; <xref ref-type="bibr" rid="B42">2021b</xref>), as vulnerable at the Mediterranean level (<xref ref-type="bibr" rid="B30">Farrell and Dulvy, 2016</xref>; <xref ref-type="bibr" rid="B25">Dulvy et&#xa0;al., 2016</xref>), and endangered by the Italian IUCN (<xref ref-type="bibr" rid="B67">Rondinini et&#xa0;al., 2022</xref>). These two benthic species are found in coastal habitats and shelf area, and they both feed on crustaceans, with only adults preying large crustaceans, cephalopods, and small teleosts (<xref ref-type="bibr" rid="B22">Di Lorenzo et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B32">Finotto et&#xa0;al., 2023</xref>). Their morphology is similar, except for the presence of black dots in <italic>Mp</italic> and for a species-specific mouth shape (<xref ref-type="bibr" rid="B53">Marino et&#xa0;al., 2018</xref>). They also differ in the maximum size and the size at sexual maturity, with <italic>Mm</italic> being larger and maturing at a greater size than <italic>Mp</italic> (<xref ref-type="bibr" rid="B66">Riginella et&#xa0;al., 2020</xref>; <xref ref-type="bibr" rid="B8">Boscolo Palo et&#xa0;al., 2022</xref>). The seasonal movement of <italic>Mm</italic> was highlighted in the Northern-Central Adriatic Sea (<xref ref-type="bibr" rid="B51">Manfredi et&#xa0;al., 2010</xref>; Bonanomi et&#xa0;al., 2018; <xref ref-type="bibr" rid="B5">Barbato et&#xa0;al., 2021</xref>) and a strong site fidelity was described for both species in the Strait of Sicily (<xref ref-type="bibr" rid="B8">Boscolo Palo et&#xa0;al., 2022</xref>). Hybridization between these two species was detected only in a single clutch (<xref ref-type="bibr" rid="B55">Marino et&#xa0;al., 2015b</xref>).</p>
<p>Genetic structure differences were identified in other benthic Mediterranean elasmobranch species, linked to habitat fragmentation, heterogeneity, and the presence of oceanographic currents (<xref ref-type="bibr" rid="B36">Gubili et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B12">Catalano et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B20">Di Crescenzo et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B57">Melis et&#xa0;al., 2023</xref>). Consequently, a similar hypothesis can be formulated for both <italic>Mustelus</italic> species. To date, a differentiated genetic structure was described between Mediterranean subregions for nuclear DNA (nDNA) only in <italic>M. mustelus</italic> but not for mitochondrial DNA (mtDNA) (<xref ref-type="bibr" rid="B39">Hull et&#xa0;al., 2019</xref>).</p>
<p>An opportunistic yet extensive sampling of tissues for genetics, representing the first subregional effort, enabled this research on <italic>M. mustelus</italic> and <italic>M. punctulatus</italic>. This study aimed to 1) evaluate nuclear and mitochondrial diversity of the two species and 2) assess their genetic structure in two Mediterranean subareas, the Adriatic Sea, and the Strait of Sicily. To this end, we used 17 microsatellite loci&#x2014;the largest panel of nuclear markers applied to these species&#x2014;and partial sequencing of the control region (CR), a widely used mitochondrial marker. Microsatellites are highly polymorphic nDNA loci with repeated motifs [1&#x2013;6 base pairs (bp)], typically located in non-coding regions unaffected by selection. Their co-dominant inheritance provides detailed insights into heterozygosity and genetic structure (<xref ref-type="bibr" rid="B24">Dudgeon et&#xa0;al., 2012</xref>). The CR, an mtDNA marker, is uniparentally inherited and has variable non-coding regions, less constrained by selection than protein-coding mtDNA genes, enabling analyses of haplotype and nucleotide diversity while complementing population differentiation studies (<xref ref-type="bibr" rid="B62">Phillips et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B63">Portnoy and Heist, 2012</xref>)</p>
</sec>
<sec id="s2" sec-type="materials|methods">
<label>2</label>
<title>Materials and methods</title>
<sec id="s2_1">
<label>2.1</label>
<title>Sample collection and DNA extraction</title>
<p>During scientific surveys on fishing vessels operating various fishing gears from 2016 to 2020, muscle tissue samples were opportunistically collected from 300 individuals (86 <italic>Mm</italic> and 214 <italic>Mp</italic>), representing populations from the Strait of Sicily (SIC; GSA 16) and the Adriatic Sea (ADRI; GSA 17 and 18). Within ADRI, samples were taken from the Italian Northern-Central coasts (N-ADRI; GSA 17) and the Montenegrin coasts (S-ADRI; GSA 18), with S-ADRI samples collected exclusively in 2020 (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1</bold>
</xref>; <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figures S1</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>S2</bold>
</xref>). Sampled individuals were identified using the latest diagnostic morphological features from <xref ref-type="bibr" rid="B53">Marino et&#xa0;al. (2018)</xref> such as black spot presence, distance of the nostrils and mouth shape, and, when possible, dermal denticle observation under stereoscopes. Total length (TL; in centimeters), sex, and haul coordinates were recorded for individuals: <italic>Mm</italic> ranged from 40-&#xa0;cm to 150-cm TL (24 females and 14 males) and <italic>Mp</italic> from 30-cm to 120-cm TL (58 females and 68 males) in N-ADRI. In SIC, <italic>Mm</italic> ranged from 30-&#xa0;cm to 150-cm TL (21 females and 17 males) and <italic>Mp</italic> from 30-&#xa0;cm to 90-cm TL (30 females and 21 males). In S-ADRI, only female <italic>Mp</italic> were sampled, ranging from 92-cm to 138-cm TL (<xref ref-type="fig" rid="f1">
<bold>Figure&#xa0;1</bold>
</xref>); only three <italic>Mm</italic> were sampled in S-ADRI and were not included in the analyses. From each individual, a muscle sample was collected and stored in pure grade ethanol at 4 degree Celsius (&#xb0;C) for further analyses.</p>
<fig id="f1" position="float">
<label>Figure&#xa0;1</label>
<caption>
<p>
<bold>(A)</bold> Red points indicate cumulatively all sampling coordinate points in the North-Central Adriatic Sea (GSA17), defined as N-ADRI, the Southern Adriatic Sea (GSA18), defined as S-ADRI, and the Strait of Sicily (GSA16), defined as SIC, in the Mediterranean Sea (<xref ref-type="bibr" rid="B34">Google Maps, 2023</xref>); <bold>(B)</bold> length frequency distribution of the sampled <italic>M. mustelus</italic> (Mm) and <italic>M. punctulatus</italic> (Mp) females (red) and males (green) from each sampling locations (red circles in the map A). Plots were created by 'ggplot2' R package (<xref ref-type="bibr" rid="B77">Wickham, 2016</xref>).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-12-1520573-g001.tif"/>
</fig>
<p>Genomic DNA was extracted from 30-mg to 40-mg tissue samples by salting-out protocol (<xref ref-type="bibr" rid="B61">Patwary et&#xa0;al., 1994</xref>), and the extract quality was checked by 1% agarose gel in TBE buffer (1&#xd7;) electrophoresis, with GelRed stain (0.025 &#x3bc;L/mL; Biotium). Extracted DNA was conserved at &#x2212;20&#xb0;C.</p>
</sec>
<sec id="s2_2">
<label>2.2</label>
<title>Nuclear DNA amplification</title>
<p>A total number of 19 loci were used (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S1.1</bold>
</xref>), starting from previously tested microsatellites (<xref ref-type="bibr" rid="B7">Boomer and Stow, 2010</xref>; <xref ref-type="bibr" rid="B13">Chabot and Nigenda, 2011</xref>; <xref ref-type="bibr" rid="B33">Giresi et&#xa0;al., 2012</xref>; <xref ref-type="bibr" rid="B54">Marino et&#xa0;al., 2015a</xref>; <xref ref-type="bibr" rid="B49">Maduna et&#xa0;al., 2017</xref>). Among these, four loci were amplified in only one of the two species, according to previous successful amplification and testing (<xref ref-type="bibr" rid="B54">Marino et&#xa0;al., 2015a</xref>; <xref ref-type="bibr" rid="B49">Maduna et&#xa0;al., 2017</xref>), namely, Mmu9 and Gg22 in <italic>Mm</italic> and MaND5 and Mh29 in <italic>Mp</italic>. Thus, for each species, 17 microsatellites for each species were included throughout the analysis. The microsatellites were divided into three groups and amplified by a Multiplex PCR kit (QIAGEN) according to the published amplification profiles (<xref ref-type="bibr" rid="B54">Marino et&#xa0;al., 2015a</xref>; <xref ref-type="bibr" rid="B39">Hull et&#xa0;al., 2019</xref>). For each microsatellite, fluorophores were chosen according to length to avoid overlapping (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S1.1</bold>
</xref>). A separate single locus PCR was carried out for the Mmu11 locus, and PCR products were assembled before sending to the genotyping service (see <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Materials</bold>
</xref> for Mmu11 amplification profile). This was necessary only in Mmu11 because the allelic peaks did not match when comparing single and multiplex amplifications. After checking the successful amplification by electrophoresis in 1.8% agarose gel, PCR products were sent to the BMR Genomics (Padua, Italy) for genotyping service where an ABI Prism 3100 Genetic Analyzer and LIZ500 as size standard were used. Scoring to examine the allelic profiles was performed for each sample by the software PEAK SCANNER v1.0 (Applied Biosystems). The binning was done by FLEXIBIN (<xref ref-type="bibr" rid="B3">Amos et&#xa0;al., 2007</xref>).</p>
</sec>
<sec id="s2_3">
<label>2.3</label>
<title>Mitochondrial DNA amplification</title>
<p>For the CR amplification, the primer pair MaCYB/MaDLP was used (<xref ref-type="bibr" rid="B39">Hull et&#xa0;al., 2019</xref>), following the protocols reported therein. After confirming the amplification by electrophoresis, amplicons were purified by EuroSAP - PCR Enzymatic Clean-up (Euroclone, Italy) and then sent for Sanger sequencing at the Eurofins Genomics (Colone, Germany). All sequences were manually checked for quality by FinchTV (Geospiza Inc.) and then trimmed, edited, and forward primer&#x2013;removed. All sequences were visualized in Mega 6 (<xref ref-type="bibr" rid="B74">Tamura et&#xa0;al., 2013</xref>) and aligned by Muscle algorithm (<xref ref-type="bibr" rid="B28">Edgar, 2004</xref>) with default parameters.</p>
<p>The sequenced fragment encompassed the last part of cytochrome b, two Transfer Ribonucleic Acid (tRNA), and the first part of the CR (orientation 5&#x2032;-3&#x2032;) when compared to the full mitochondrial genome of <italic>Mm</italic>, available on GenBank (accession number MH559351.1) by Blastn (<xref ref-type="bibr" rid="B2">Altschul et&#xa0;al., 1990</xref>) and Clustal Muscle alignment (<xref ref-type="bibr" rid="B28">Edgar, 2004</xref>). The initial sequenced fragment was composed of 713 bp and the first 230 bp encompassed the cytochrome b and tRNAs. The remaining 483 bp included the beginning of the CR region, which started at base position 15638 of the <italic>Mm</italic> complete genome (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figure S3</bold>
</xref>). All the downstream analyses were performed considering only the CR fragment (483 bp).</p>
</sec>
<sec id="s2_4">
<label>2.4</label>
<title>Genetic diversity</title>
<p>Microsatellite genotypes were first checked for null alleles using MicroChecker v2.2.3 (<xref ref-type="bibr" rid="B75">Van Oosterhout et&#xa0;al., 2004</xref>), and their presence was evaluated on the estimation of genetic structure by FreeNA (<xref ref-type="bibr" rid="B15">Chapuis and Estoup, 2007</xref>). GENEPOP ON THE WEB v4.2 (<xref ref-type="bibr" rid="B65">Raymond and Rousset, 1995</xref>; <xref ref-type="bibr" rid="B68">Rousset, 2008</xref>) was used for testing linkage disequilibrium (LD) and deviations from Hardy&#x2013;Weinberg equilibrium (HWE). For statistical significance of multiple tests, Benjamini&#x2013;Hochberg correction (B-H; <xref ref-type="bibr" rid="B6">Benjamini and Hochberg, 1995</xref>) was applied with the function <italic>p.adjust</italic> on RStudio 1.3.1093-1 (<xref ref-type="bibr" rid="B70">RStudio Team, 2020</xref>). Bayesian structure analysis by STRUCTURE (<xref ref-type="bibr" rid="B64">Pritchard et&#xa0;al., 2000</xref>) was run to obtain the most reliable species identification for each specimen, assuming an admixture ancestry model with independent allelic frequencies and without a prior on sample origin (see <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Materials</bold>
</xref> for more details). Using the species identification based on STRUCTURE, for each species, the nDNA genetic diversity was calculated using the R package DiveRsity (<xref ref-type="bibr" rid="B45">Keenan et&#xa0;al., 2013</xref>), as the number of alleles observed per locus per population sample (A), the allelic richness (A<sub>R</sub>), the observed and expected heterozygosity (H<sub>O</sub> and H<sub>E</sub>), and the inbreeding coefficient (F<sub>IS</sub>). For the mtDNA, the CR diversity was calculated by DnaSP (<xref ref-type="bibr" rid="B69">Rozas et&#xa0;al., 2017</xref>) on the basis of the same species identification. Total number of haplotypes (H), haplotype diversity (h), and nucleotide diversity (&#x3c0;) were obtained. The haplotype network was created using TCS (<xref ref-type="bibr" rid="B16">Clement et&#xa0;al., 2000</xref>) and edited with PopART (<xref ref-type="bibr" rid="B47">Leigh and Bryant, 2015</xref>). To avoid that population structure was influenced by family structure, Colony v2.0.6.7 (<xref ref-type="bibr" rid="B44">Jones and Wang, 2010</xref>) was used for each species in separate runs selecting for female and male polygamy with inbreeding and cloning, by full-likelihood method at 95% and no prior. Only one sample for each full-sibling pair was kept for further analysis (see <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Materials</bold>
</xref>).</p>
</sec>
<sec id="s2_5">
<label>2.5</label>
<title>Population differentiation</title>
<p>To assess the level of genetic structure among the sampling sites in the two species, a Bayesian clustering analysis by STRUCTURE was performed with correlated allelic frequencies together with the abovementioned settings and software to account for uneven sample size.</p>
<p>For both nDNA and mtDNA, genetic differentiation, pairwise F<sub>ST</sub>, and &#x3a6;<sub>ST</sub> respectively, was determined by ARLEQUIN (<xref ref-type="bibr" rid="B29">Excoffier and Lischer, 2010</xref>) with 10<sup>4</sup> permutations across sampling sites. Only for the <italic>Mp</italic>, the comparisons were performed between the ADRI and SIC (pooling together N-ADRI and S-ADRI), and among N-ADRI, S-ADRI, and SIC. When appropriate, B-H correction for multiple comparisons was performed with experiment-wide significance at p-values &lt; 0.01. To assess whether unbalanced sample size in <italic>Mp</italic> may have affected the genetic differentiation, a random subsampling was performed, taking 50 random individuals from N-ADRI (N = 37) and S-ADRI (N = 13) while also balancing the sex ratio; the metrics of genetic differentiation were computed as described above.</p>
<p>The discriminant analysis of principal components (DAPC) (<xref ref-type="bibr" rid="B43">Jombart et&#xa0;al., 2010</xref>) was used to investigate population genetic structure. By summarizing between-group variation and ignoring within-group variation, DAPC effectively identified genetic structure within the samples. This multivariate approach assigned individuals to distinct groups and assessed inter-population differentiation without relying on specific population genetics models (e.g., HWE and LD).</p>
</sec>
</sec>
<sec id="s3" sec-type="results">
<label>3</label>
<title>Results</title>
<sec id="s3_1">
<label>3.1</label>
<title>Genetic diversity</title>
<sec id="s3_1_1">
<label>3.1.1</label>
<title>Nuclear DNA</title>
<p>DNA of satisfactory quality was obtained from the 300 available tissue samples, and it was used to confirm the morphological identification using STRUCTURE. The optimal K was equal to 2 and cluster analysis allowed identifying 86 <italic>Mm</italic> and 214 <italic>Mp</italic>. Overall, four samples were discarded because of too many missing loci (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figure S4</bold>
</xref>). Using F<sub>ST</sub>, the genetic divergence between the two species was 0.63 (p-value &lt; 0.001). The presence of null alleles did not affect the estimates of genetic structure (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S2</bold>
</xref>), and no significant deviation from HWE (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S3</bold>
</xref>) and LD (data not shown) was detected across sampling sites. Thus, all loci were kept for further analyses. In <italic>Mm</italic>, a low genetic diversity emerged at both locations, with A<sub>R</sub> around 3.5 and Ho between 0.33 and 0.36, whereas <italic>Mp</italic> samples showed even smaller values, with A<sub>R</sub> between 2.14 and 2.33 and with Ho between 0.22 and 0.26. F<sub>IS</sub> turned out to be positive across locations (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S4</bold>
</xref>).</p>
</sec>
<sec id="s3_1_2">
<label>3.1.2</label>
<title>Mitochondrial DNA</title>
<p>The mtDNA CR of 83 samples of <italic>Mm</italic> and 207 samples of <italic>Mp</italic> was successfully sequenced, whereas 10 samples were not kept for further analyses (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S5</bold>
</xref>). Among the excluded samples, seven <italic>Mp</italic> (N = 3 from the N-ADRI, 1 from the S-ADRI, and 3 from the SIC) and three <italic>Mm</italic> from SIC had poor sequencing quality or failed amplification. One specimen was identified to be an introgressed hybrid and discarded. In detail, the individual (sample #S301) had a CR haplotype belonging to <italic>Mp</italic>, but it was identified as a sexually mature male of 135&#xa0;cm of TL <italic>Mm</italic> based on morphology, and this species identification was confirmed by STRUCTURE. In this sample, only one of the two <italic>Mm</italic> species-specific microsatellites (Mmu9) was successfully amplified. Even though the sample was excluded from further analysis, being out of the scope of this study, its haplotype was accounted for in the haplotype occurrence.</p>
<p>In <italic>Mm</italic>, a moderate variation was found, with four haplotypes and three or two segregating sites, respectively, in N-ADRI and SIC. In <italic>Mp</italic>, the haplotype number ranged from 3 to 5 and the segregating sites between 2 and 5 (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S5</bold>
</xref>). In <italic>Mm</italic>, the haplotype N3 was the most frequent, present in 63% of individuals, followed by N4. Haplotype N2 and N10 were only found in the SIC and the N-ADRI, respectively (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S6</bold>
</xref>). <italic>Mp</italic> has 83% of individuals with haplotype N1, and N7 was the second most frequent haplotype. <italic>Mp</italic> presented three unique haplotypes in the N-ADRI (N11, N12, and N13), one in the S-ADRI (N9), and two in the SIC (N6 and N8) (<xref ref-type="fig" rid="f2">
<bold>Figure&#xa0;2</bold>
</xref>, <xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Table S7</bold>
</xref>).</p>
<fig id="f2" position="float">
<label>Figure&#xa0;2</label>
<caption>
<p>Haplotype network of the sequenced control region fragment of <italic>M. mustelus</italic> <bold>(A)</bold> and <italic>M. punctulatus</italic> <bold>(B)</bold>. The size of the circles represents the number of samples belonging to a unique haplotype.</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-12-1520573-g002.tif"/>
</fig>
</sec>
</sec>
<sec id="s3_2">
<label>3.2</label>
<title>Population differentiation</title>
<sec id="s3_2_1">
<label>3.2.1</label>
<title>Microsatellites</title>
<p>Without using prior information of sample origin, the cluster analysis in STRUCTURE did not evidence the presence of structure between the ADRI and the SIC (<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Figure S5</bold>
</xref>) for both species, with STRUCTURESELECTOR metrics indicating that the optimal K was equal to 1. From ARLEQUIN analysis, however, microsatellite-derived F<sub>ST</sub> showed a statistically significant differentiation between the population samples from N-ADRI and SIC in <italic>Mm</italic> (F<sub>ST</sub> = 0.02, p-value = 0.005) and between ADRI and SIC in <italic>Mp</italic> (F<sub>ST</sub> = 0.03, p-value = 0.003); for this latter species, genetic differences did not emerge between N-ADRI and S-ADRI samples (F<sub>ST</sub> = 0.002, p-value = 0.23), whereas divergence was found between S-ADRI and the SIC (F<sub>ST</sub> = 0.02, p-value &lt; 0.001). The result of significant genetic differentiation between ADRI and SIC in <italic>Mp</italic> was further investigated, possibly biased by the unbalanced sample size of the two population samples (N = 163 and 51, respectively). To this end, the analysis was repeated, randomly subsampling 50 ADRI individuals from the genetically homogeneous N-ADRI and S-ADRI population samples (see Materials and Methods) and comparing them with the 51 SIC individuals, confirming our finding (F<sub>ST</sub> = 0.03, p-value &lt; 0.001) (<xref ref-type="table" rid="T1">
<bold>Table&#xa0;1</bold>
</xref>).</p>
<table-wrap id="T1" position="float">
<label>Table&#xa0;1</label>
<caption>
<p>Pairwise F<sub>ST</sub> and &#x3a6;<sub>ST</sub> values were calculated, respectively according to microsatellite on nuclear DNA and to controlo region (CR) on mitochondrial DNA comparing the sampling origins (N-ADRI, Northern-Central Adriatic Sea; S-ADRI, Southern Adriatic Sea; SIC, Strait of Sicily); B-H correction was applied only for <italic>M. punctulatus</italic> when comparing multiple sampling sites, marked by the asterisk, and statistical significance was set at p-values &lt; 0.01, reported in bold when significant.</p>
</caption>
<table frame="hsides">
<thead>
<tr>
<th valign="middle" rowspan="2" colspan="2" align="center"/>
<th valign="middle" align="center">
<italic>M. mustelus</italic>
</th>
<th valign="middle" colspan="4" align="center">
<italic>M. punctulatus</italic>
</th>
</tr>
<tr>
<th valign="middle" align="center">N-ADRI-SIC</th>
<th valign="middle" align="center">ADRI/SIC</th>
<th valign="middle" align="center">N-ADRI/S-ADRI</th>
<th valign="middle" align="center">N-ADRI/SIC</th>
<th valign="middle" align="center">S-ADRI/SIC</th>
</tr>
</thead>
<tbody>
<tr>
<td valign="middle" rowspan="3" align="left">
<bold>nDNA</bold>
</td>
<td valign="middle" align="center">
<bold>F<sub>ST</sub>
</bold>
</td>
<td valign="middle" align="center">
<bold>0.02</bold>
</td>
<td valign="middle" align="center">
<bold>0.03</bold>
</td>
<td valign="middle" align="center">0.002</td>
<td valign="middle" align="center">
<bold>0.03</bold>
</td>
<td valign="middle" align="center">
<bold>0.02</bold>
</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>p-value</bold>
</td>
<td valign="middle" align="center">
<bold>0.005</bold>
</td>
<td valign="middle" align="center">
<bold>0.003</bold>
</td>
<td valign="middle" align="center">0.23*</td>
<td valign="middle" align="center">
<bold>&lt;0.001*</bold>
</td>
<td valign="middle" align="center">
<bold>&lt;0.001*</bold>
</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>Sample size</bold>
</td>
<td valign="middle" align="center">48:38</td>
<td valign="middle" align="center">163:51</td>
<td valign="middle" align="center">126:37</td>
<td valign="middle" align="center">126:51</td>
<td valign="middle" align="center">37:51</td>
</tr>
<tr>
<td valign="middle" rowspan="3" align="left">
<bold>CR</bold>
</td>
<td valign="middle" align="center">
<italic>&#x3a6;</italic>
<bold>
<sub>ST</sub>
</bold>
</td>
<td valign="middle" align="center">
<bold>0.12</bold>
</td>
<td valign="middle" align="center">
<bold>0.086</bold>
</td>
<td valign="middle" align="center">0.03</td>
<td valign="middle" align="center">
<bold>0.09</bold>
</td>
<td valign="middle" align="center">0.06</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>p-value</bold>
</td>
<td valign="middle" align="center">
<bold>0.001</bold>
</td>
<td valign="middle" align="center">
<bold>&lt;0.001</bold>
</td>
<td valign="middle" align="center">0.026*</td>
<td valign="middle" align="center">
<bold>&lt;0.001*</bold>
</td>
<td valign="middle" align="center">0.026*</td>
</tr>
<tr>
<td valign="middle" align="center">
<bold>Sample size</bold>
</td>
<td valign="middle" align="center">48:35</td>
<td valign="middle" align="center">160:48</td>
<td valign="middle" align="center">123:36</td>
<td valign="middle" align="center">123:48</td>
<td valign="middle" align="center">36:48</td>
</tr>
</tbody>
</table>
<table-wrap-foot>
<fn>
<p>B-H correction was applied only for M. punctulatus when comparing multiple sampling sites, marked by the asterisk. Statistical significance was set at p-values &lt; 0.01, reported in bold when significant. N refers to the sample size.</p>
</fn>
</table-wrap-foot>
</table-wrap>
<p>DAPC analyses revealed a clear distinction for <italic>Mm</italic> among the two sampling sites (N-ADRI) and SIC, with a reasonable power to reassign individuals from the two locations using our microsatellites data, albeit with a slight overlap between the two regions (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3A, B</bold>
</xref>). On the other hand, DAPC analyses on <italic>Mp</italic> revealed no distinction between N-ADRI and S-ADRI, but a significant level of correct re-assignment for SIC versus N-ADRI, with still an overlap between the two clusters (<xref ref-type="fig" rid="f3">
<bold>Figures&#xa0;3C, D</bold>
</xref>).</p>
<fig id="f3" position="float">
<label>Figure&#xa0;3</label>
<caption>
<p>DAPC analysis accounting for the sampling origin for <italic>M. mustelus</italic> <bold>(A, B)</bold> and <italic>M. punctulatus</italic> <bold>(C, D)</bold>. For the two studied species, the principal component diagram <bold>(A, C)</bold> and the bar plot of the percentage of reassignment <bold>(B, D)</bold> are shown. The average percentage of correct reassignment for <italic>M. mustelus </italic>is 0.9, which indicates a high degree of discrimination between SIC and ADRI clusters. On the other hand, we have an average reassignment around 0.68 for <italic>M. punctulatus</italic>. This value is due to the low level of discrimination between N-ADRI and S-ADRI (e.g., samples from Montenegro) clusters. Population codes: ADRI (Adriatic Sea); N-ADRI (North Adriatic Sea); S-ADRI (South Adriatic Sea, Montenegro coast); SIC (Strait of Sicily).</p>
</caption>
<graphic mimetype="image" mime-subtype="tiff" xlink:href="fmars-12-1520573-g003.tif"/>
</fig>
</sec>
<sec id="s3_2_2">
<label>3.2.2</label>
<title>Control region</title>
<p>CR-derived &#x3a6;<sub>ST</sub> values showed significant differentiation in both species sampled in the ADRI and the SIC (&#x3a6;<sub>ST</sub> = 0.12, p-value = 0.001, in <italic>Mm</italic>; and &#x3a6;<sub>ST</sub> = 0.086, p-value &lt; 0.001 in <italic>Mp</italic>). When accounting for uneven sample size in <italic>Mp</italic>, randomly subsampled sequences from N-ADRI and S-ADRI confirmed the differences with SIC (&#x3a6;<sub>ST</sub> = 0.07, p-value &lt; 0.001). After B-H correction, significant genetic divergence emerged only in <italic>Mp</italic> between the N-ADRI and the SIC (&#x3a6;<sub>ST</sub> = 0.09, p-value &lt; 0.001), whereas no statistical significance was observed between the N-ADRI and S-ADRI (&#x3a6;<sub>ST</sub> = 0.03, p-value = 0.026) and between the S-ADRI and the SIC (&#x3a6;<sub>ST</sub> = 0.06, p-value = 0.026) (<xref ref-type="table" rid="T1">
<bold>Table&#xa0;1</bold>
</xref>).</p>
</sec>
</sec>
</sec>
<sec id="s4" sec-type="discussion">
<label>4</label>
<title>Discussion</title>
<sec id="s4_1">
<label>4.1</label>
<title>Genetic diversity</title>
<p>A low genetic diversity emerged in this study, particularly evident in the nDNA of <italic>Mp</italic> with an expected heterozygosity of about 0.25 and only about two alleles expected per locus. For <italic>Mm</italic>, the genetic diversity was slightly higher, with about 35% expected heterozygotes and 3.5 alleles per locus, and, to a small extent, greater than what previously found in <italic>Mm</italic> with only nine microsatellites (<xref ref-type="bibr" rid="B39">Hull et&#xa0;al., 2019</xref>). The low nuclear diversity found in our study is in line with the one found in other benthic elasmobranchs in the Mediterranean populations such as the <italic>Galeus melastomus</italic> in the southern Adriatic Sea and in Sicily (A<sub>R</sub> = 2.7&#x2013;2.8 and H<sub>E</sub> = 0.36&#x2013;0.4; <xref ref-type="bibr" rid="B20">Di Crescenzo et&#xa0;al., 2022</xref>) and the <italic>Raja asterias</italic> in the northern Adriatic Sea (A<sub>R</sub> = 3.35 and H<sub>E</sub> = 0.56; <xref ref-type="bibr" rid="B12">Catalano et&#xa0;al., 2022</xref>). On the other hand, a higher nuclear diversity (A<sub>R</sub> = 5.2&#x2013;6.5, H<sub>E</sub> = 0.56&#x2013;0.76) was reported in the northern Adriatic Sea for other benthic elasmobranch species, such as the <italic>Schyliorhinus canicula</italic> (<xref ref-type="bibr" rid="B36">Gubili et&#xa0;al., 2014</xref>), the <italic>R. clavata</italic> (<xref ref-type="bibr" rid="B57">Melis et&#xa0;al., 2023</xref>), and the epibenthic <italic>Squalus acanthias</italic> (<xref ref-type="bibr" rid="B35">Gra&#x10d;an et&#xa0;al., 2020</xref>). The mtDNA diversity found in our study mirrors the pattern observed with nDNA, showing a very low variability in <italic>Mp</italic> (h = 0.16&#x2013;0.31 and &#x3c0; = 0.0003&#x2013;0.001) and higher values in <italic>Mm</italic> (h = 0.52&#x2013;0.54 and &#x3c0; = 0.001); in <italic>Mm</italic>, despite the shorter sequenced fragment in our study, CR showed similar diversity values to those previously found (<xref ref-type="bibr" rid="B39">Hull et&#xa0;al., 2019</xref>). CR diversity, however, is known to vary between closely related species and within the same species (<xref ref-type="bibr" rid="B73">Subramanian and Lambert, 2011</xref>). Accordingly, several studies in other elasmobranch species reported very different patterns with a moderate to high CR genetic diversity in some species [reviewed by <xref ref-type="bibr" rid="B39">Hull et&#xa0;al. (2019)</xref>; h = 0.78&#x2013;0.99 and &#x3c0; = 0.004&#x2013;0.35], including <italic>S. canicula</italic> from the Adriatic Sea (h = 0.71 and &#x3c0; = 0.003; <xref ref-type="bibr" rid="B36">Gubili et&#xa0;al., 2014</xref>).</p>
<p>For the aforementioned benthic elasmobranch species, whose genetic diversity was investigated in many Mediterranean subareas (<xref ref-type="bibr" rid="B36">Gubili et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B12">Catalano et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B20">Di Crescenzo et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B57">Melis et&#xa0;al., 2023</xref>), including the two smooth-hound species of the present study, their steep decline found support in literature (<xref ref-type="bibr" rid="B18">Colloca et&#xa0;al., 2017</xref>; <xref ref-type="bibr" rid="B31">Ferretti et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B26">Dulvy et&#xa0;al., 2021</xref>). This calls for further research to deepen the understanding of fishery-induced effect of the genetic diversity of over-exploited elasmobranch species (<xref ref-type="bibr" rid="B23">Domingues et&#xa0;al., 2018</xref>)</p>
</sec>
<sec id="s4_2">
<label>4.2</label>
<title>Population differentiation</title>
<p>The evidence of genetic structure found in our study for <italic>Mm</italic> confirms and extends what was previously known at the global level for this species (<xref ref-type="bibr" rid="B39">Hull et&#xa0;al., 2019</xref>). In fact, although, as expected, our extended microsatellite panel confirms the existence of genetic differentiation between the Adriatic Sea and the Strait of Sicily, our study adds new support for the occurrence of a genetic structure between these two Mediterranean areas that, thanks to our higher sample size, were detected, for the first time, using also mtDNA. In <italic>Mm</italic>, the occurrence of one high-frequency shared haplotype in SIC and ADRI could be due to a recent common ancestor, whereas the other shared haplotypes could be the result of recent immigration. However, the existence of the unique haplotype (N10) points out to the occurrence of some level of isolation reflecting either localized adaptation or bottlenecks in N-ADRI. In <italic>Mp</italic>, although one prevailing ancestral haplotype was found, multiple unique haplotypes were detected in both N-ADRI, S-ADRI, and SIC, highlighting a higher degree of isolation and genetic drift. Through sequencing a longer CR fragment, focused research could discern whether mtDNA divergence could also result from a sex-biased dispersal (<xref ref-type="bibr" rid="B37">Hirschfeld et&#xa0;al., 2021</xref>; <xref ref-type="bibr" rid="B62">Phillips et&#xa0;al., 2021</xref>). However, the haplotype network and the value of <italic>&#x3a6;</italic>
<bold>
<sub>ST</sub>
</bold> and F<sub>ST</sub> could potentially be explained by alternative hypothesis such as female-mediate gene flow, incomplete lineage sorting, or strong population genetic declines, as also discussed at global level in <xref ref-type="bibr" rid="B39">Hull et&#xa0;al. (2019)</xref>. This result of genetic differentiation is in line with what reported for this species at the global scale, <italic>Mm</italic> displayed a significant level of isolation shaped by the effect of oceanic currents or other biogeographical barriers, despite the capability to undertake rare and long migrations (<xref ref-type="bibr" rid="B52">Mann and Bullen, 2009</xref>; <xref ref-type="bibr" rid="B19">da Silva et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B48">Maduna et&#xa0;al., 2016</xref>). In South African water, the combination of tagging and genetic methods in <italic>Mm</italic> contributed to find a contrasted dynamic between a strong site fidelity in a relatively short period and a significant gene flow at evolutionary scale (<xref ref-type="bibr" rid="B46">Klein et&#xa0;al., 2022</xref>).</p>
<p>With regard to <italic>Mp</italic>, our study provided the first evidence for a significant structure between SIC and ADRI, with a pattern that mirrors the <italic>Mm</italic> structure. It is worth noting that seasonal and permanent currents occur in this area; in particular, the ADRI circulation consisted in wind-driven currents, one from south to north along the eastern coast and another one from north to the south in the western coast, and three seasonal gyres (<xref ref-type="bibr" rid="B71">Russo and Artegiani, 1996</xref>). The ADRI hydrodynamics did not appear to influence the genetic differentiation between N-ADRI and S-ADRI in <italic>Mp</italic> while being responsible for the genetic structure of many marine species with larval dispersal (<xref ref-type="bibr" rid="B60">Papetti et&#xa0;al., 2013</xref>; <xref ref-type="bibr" rid="B56">Mati&#x107;-Skoko et&#xa0;al., 2018</xref>). Similarly, other populations of <italic>Mustelus</italic> species appeared to be genetically structured, including the gummy shark (<italic>M. antarcticus</italic>) in Australian waters despite a wide movement range (238&#x2013;900 km) (<xref ref-type="bibr" rid="B9">Braccini et&#xa0;al., 2017</xref>) and the brown smooth-hound (<italic>M. henlei</italic>) in the Gulf of California (<xref ref-type="bibr" rid="B72">Sandoval-Castillo and Beheregaray, 2015</xref>). Our analyses of re-assignment using DAPC further supported the concept of two distinct and yet slightly connected populations, highlighting the presence of a semi-permeable barrier between the Adriatic Sea and the Mediterranean Sea.</p>
<p>Despite being opportunistic, our sampling represents the first coordinated subregional effort, yielding the largest genetic dataset for these exploited species. Combining microsatellite genotyping with CR sequencing, we detected genetic diversity and a statistically significant population structure between the Adriatic Sea and the Strait of Sicily, confirming two distinct genetic stocks for <italic>Mm</italic> (SIC) and <italic>Mp</italic> (ADRI) for the first time. Our results were in line with previous analyses on Mediterranean and benthic elasmobranch species that showed significant genetic structuring between Mediterranean areas (<xref ref-type="bibr" rid="B36">Gubili et&#xa0;al., 2014</xref>; <xref ref-type="bibr" rid="B12">Catalano et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B20">Di Crescenzo et&#xa0;al., 2022</xref>; <xref ref-type="bibr" rid="B57">Melis et&#xa0;al., 2023</xref>). The diversity of habitats present between ADRI and SIC, encompassed by deep water and the presence of the Strait of Otranto, seemed to act as an only semi-permeable dispersal barrier for many populations of elasmobranch species, highlighting the importance of identifying genetic stock. Behaviors like philopatry and sex-biased dispersal may play a role in shaping the genetic structure and contribute to the connectivity in elasmobranch (<xref ref-type="bibr" rid="B14">Chapman et&#xa0;al., 2015</xref>; <xref ref-type="bibr" rid="B62">Phillips et&#xa0;al., 2021</xref>), but, due to the opportunistic sampling, this study was not able to address this goal and needs to be further investigated. Considering the stock definition (<xref ref-type="bibr" rid="B40">Ihssen et&#xa0;al., 1981</xref>), fishery management of these two stocks could be improved tailoring stock specific strategies that consider different growth rate, reproduction and nursery areas, and harvesting dynamic (<xref ref-type="bibr" rid="B10">Cadrin et&#xa0;al., 2014</xref>). The commercial relevance and the conservation issues of <italic>Mm</italic> and <italic>Mp</italic> in the two Mediterranean populations require the delineation of management units. Albeit a holistic approach is needed, our study provides solid evidence in relation to the genetic stocks of these exploited and threatened shark species.</p>
</sec>
</sec>
</body>
<back>
<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 in the article/<xref ref-type="supplementary-material" rid="SM1">
<bold>Supplementary Material</bold>
</xref>. The datasets generated during and/or analysed during the current study are available in the Figshare repository: <uri xlink:href="https://doi.org/10.6084/m9.figshare.22652257">https://doi.org/10.6084/m9.figshare.22652257</uri>.</p>
</sec>
<sec id="s6" sec-type="ethics-statement">
<title>Ethics statement</title>
<p>Samples from the Adriatic Sea were collected from dead specimens caught during professional fishing activity and, therefore, no approval from the local ethics committee was necessary. In the strait of Sicily, all procedures carried out were approved by the international authorities (EU/DG Mare, FAO/GFCM). All specimens and methods were caught and performed in accordance with the relevant guidelines and regulations. In the cases the animal was alive when it arrived on the vessel during the scientific survey (MEDITS-DCF, EU Reg. 199/2008), it was suppressed in compliance with the recommendation of Decree Law n. 26 of 4 March 2014. All efforts were made to minimize suffering. The study was conducted in accordance with the local legislation and institutional requirements.</p>
</sec>
<sec id="s7" sec-type="author-contributions">
<title>Author contributions</title>
<p>MB: Writing &#x2013; original draft, Writing &#x2013; review &amp; editing, Conceptualization, Data curation, Formal analysis, Investigation, Methodology. SB: Funding acquisition, Writing &#x2013; review &amp; editing. DB: Investigation, Writing &#x2013; review &amp; editing. IC: Investigation, Writing &#x2013; review &amp; editing. FC: Investigation, Writing &#x2013; review &amp; editing. MD: Investigation, Writing &#x2013; review &amp; editing. IM: Conceptualization, Data curation, Investigation, Methodology, Writing &#x2013; review &amp; editing. CM: Conceptualization, Funding acquisition, Writing &#x2013; review &amp; editing. AP: Investigation, Writing &#x2013; review &amp; editing. AS: Funding acquisition, Writing &#x2013; review &amp; editing. LZ: Conceptualization, Methodology, Project administration, Supervision, Writing &#x2013; review &amp; editing. MM: Conceptualization, Investigation, Methodology, Supervision, Validation, Writing &#x2013; review &amp; editing.</p>
</sec>
<sec id="s8" 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. We would like to acknowledge that this study was funded by the monitoring programme &#x201c;BYCATCH 2016-2017&#x201d; and &#x201c;Task 5.1a PLNRDA 2018-2020&#x201d; in compliance with the Regulations (EC) 812/2004 and from the &#x201c;<italic>Piano di Lavoro Nazionale Raccolta Dati Alieutici 2018-2020</italic>&#x201d; in compliance with EU Data Collection Framework and the scientific survey programme (MEDITS-DCF, EU Reg. 199/2008). Additional funding to LZ was provided by the National Biodiversity Future Center (NBFC, funded under the European Union Next-GenerationEU (National Recovery and Resilience Plan (PNRR), Mission 4 Component 2 Investment 1.4 - D.D. 3175 18/12/2021, CN_00000033), which also funded IAM salary. This study was also funded by the Italian Ministry of Education, Universities and Research (MIUR) within the scientific research program of national interest &#x201c;Preserving coastal marine ecosystem functions and services under climate change pressure and overfishing&#x201d; to LZ (PRIN 2020 Prot. 2020J3W3WC). Open Access funding provided by Universit&#xe0; degli Studi di Padova | University of Padua, Open Science Committee.</p>
</sec>
<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="ai-statement">
<title>Generative AI statement</title>
<p>The author(s) declare that no Generative AI was used in the creation of this manuscript.</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.2025.1520573/full#supplementary-material">https://www.frontiersin.org/articles/10.3389/fmars.2025.1520573/full#supplementary-material</ext-link>
</p>
<supplementary-material xlink:href="DataSheet1.docx" id="SM1" mimetype="application/vnd.openxmlformats-officedocument.wordprocessingml.document"/>
</sec>
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