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  <front>
    <journal-meta>
      <journal-id journal-id-type="publisher-id">119</journal-id>
      <journal-id journal-id-type="index">urn:lsid:arphahub.com:pub:164696f9-9de4-57df-b939-8dd7e23d8d8f</journal-id>
      <journal-title-group>
        <journal-title xml:lang="en">Aquatic Invasions</journal-title>
        <abbrev-journal-title xml:lang="en">AquaInv</abbrev-journal-title>
      </journal-title-group>
      <issn pub-type="ppub">1798-6540</issn>
      <issn pub-type="epub">1818-5487</issn>
      <publisher>
        <publisher-name>Regional Euro-Asian Biological Invasions Centre</publisher-name>
      </publisher>
    </journal-meta>
    <article-meta>
      <article-id pub-id-type="doi">10.3391/ai.2025.20.4.172098</article-id>
      <article-id pub-id-type="publisher-id">172098</article-id>
      <article-categories>
        <subj-group subj-group-type="heading">
          <subject>Research Article</subject>
        </subj-group>
        <subj-group subj-group-type="biological_taxon">
          <subject>Animalia</subject>
          <subject>Ascidiacea</subject>
        </subj-group>
        <subj-group subj-group-type="scientific_subject">
          <subject>Biological Invasions</subject>
          <subject>Conservation Biology</subject>
        </subj-group>
        <subj-group subj-group-type="geographical_area">
          <subject>Atlantic Ocean Islands</subject>
        </subj-group>
      </article-categories>
      <title-group>
        <article-title>﻿Emergence of an invasive ascidian in Canary Islands (Eastern Atlantic): Tracking the arrival and spread of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic></article-title>
      </title-group>
      <contrib-group content-type="authors">
        <contrib contrib-type="author" corresp="yes">
          <name name-style="western">
            <surname>Turon</surname>
            <given-names>Xavier</given-names>
          </name>
          <email xlink:type="simple">xturon@ceab.csic.es</email>
          <uri content-type="orcid">https://orcid.org/0000-0002-9229-5541</uri>
          <xref ref-type="aff" rid="A1">1</xref>
        </contrib>
        <contrib contrib-type="author" corresp="no">
          <name name-style="western">
            <surname>Martín-Solà</surname>
            <given-names>Marc</given-names>
          </name>
          <uri content-type="orcid">https://orcid.org/0009-0002-5089-1772</uri>
          <xref ref-type="aff" rid="A2">2</xref>
          <xref ref-type="aff" rid="A3">3</xref>
        </contrib>
        <contrib contrib-type="author" corresp="no">
          <name name-style="western">
            <surname>Moro-Abad</surname>
            <given-names>Leopoldo</given-names>
          </name>
          <uri content-type="orcid">https://orcid.org/0000-0003-0528-3989</uri>
          <xref ref-type="aff" rid="A4">4</xref>
        </contrib>
        <contrib contrib-type="author" corresp="yes">
          <name name-style="western">
            <surname>Hernández</surname>
            <given-names>José Carlos</given-names>
          </name>
          <email xlink:type="simple">jocarher@ull.edu.es</email>
          <uri content-type="orcid">https://orcid.org/0000-0002-1539-1783</uri>
          <xref ref-type="aff" rid="A2">2</xref>
        </contrib>
      </contrib-group>
      <aff id="A1">
        <label>1</label>
        <addr-line content-type="verbatim">Department of Marine Ecology, Centre for Advanced Studies of Blanes (CEAB, CSIC), Blanes (Girona), Spain</addr-line>
        <institution>Centre for Advanced Studies of Blanes</institution>
        <addr-line content-type="city">Girona</addr-line>
        <country>Spain</country>
      </aff>
      <aff id="A2">
        <label>2</label>
        <addr-line content-type="verbatim">Marine Community Ecology and Conservation, Departamento Biología Animal, Edafología y Geología, Facultad de Ciencias (Biología), Universidad de La Laguna, Tenerife, Canary Islands, Spain</addr-line>
        <institution>Universidad de La Laguna</institution>
        <addr-line content-type="city">Tenerife</addr-line>
        <country>Spain</country>
      </aff>
      <aff id="A3">
        <label>3</label>
        <addr-line content-type="verbatim">Gestión y Planeamiento Territorial y Medioambiental, S.A. Santa Cruz de Tenerife, Spain</addr-line>
        <institution>Gestión y Planeamiento Territorial y Medioambiental</institution>
        <addr-line content-type="city">Tenerife</addr-line>
        <country>Spain</country>
      </aff>
      <aff id="A4">
        <label>4</label>
        <addr-line content-type="verbatim">Servicio de Biodiversidad, Gobierno de Canarias, Santa Cruz de Tenerife, Spain</addr-line>
        <institution>Servicio de Biodiversidad, Gobierno de Canarias</institution>
        <addr-line content-type="city">Santa Cruz de Tenerife</addr-line>
        <country>Spain</country>
      </aff>
      <author-notes>
        <fn fn-type="corresp">
          <p>Corresponding authors: Xavier Turon (<ext-link xlink:href="mailto:xturon@ceab.csic.es" ext-link-type="uri" xlink:type="simple">xturon@ceab.csic.es</ext-link>); José Carlos Hernández (<ext-link xlink:href="mailto:jocarher@ull.edu.es" ext-link-type="uri" xlink:type="simple">jocarher@ull.edu.es</ext-link>)</p>
        </fn>
        <fn fn-type="edited-by">
          <p>Academic editor: Noa Shenkar</p>
        </fn>
      </author-notes>
      <pub-date pub-type="collection">
        <year>2025</year>
      </pub-date>
      <pub-date pub-type="epub">
        <day>12</day>
        <month>11</month>
        <year>2025</year>
      </pub-date>
      <volume>20</volume>
      <issue>4</issue>
      <fpage>411</fpage>
      <lpage>425</lpage>
      <uri content-type="arpha" xlink:href="http://openbiodiv.net/5B73EA2F-5D7A-504F-B442-4A7225A8C013">5B73EA2F-5D7A-504F-B442-4A7225A8C013</uri>
      <uri content-type="zenodo_dep_id" xlink:href="https://zenodo.org/record/17607219">17607219</uri>
      <history>
        <date date-type="received">
          <day>10</day>
          <month>06</month>
          <year>2025</year>
        </date>
        <date date-type="accepted">
          <day>19</day>
          <month>08</month>
          <year>2025</year>
        </date>
      </history>
      <permissions>
        <copyright-statement>Xavier Turon, Marc Martín-Solà, Leopoldo Moro-Abad, José Carlos Hernández</copyright-statement>
        <license license-type="creative-commons-attribution" xlink:href="http://creativecommons.org/licenses/by/4.0/" xlink:type="simple">
          <license-p>This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.</license-p>
        </license>
      </permissions>
      <abstract>
        <label>﻿Abstract</label>
        <p>This study documents the first occurrence and rapid expansion of the solitary ascidian <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> in natural marine habitats of Tenerife (Canary Islands). Native to the Indo-Pacific, <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> had previously been introduced to the Caribbean, Brazil, and Cape Verde. It was first observed in Tenerife in 2020, though retrospective records through citizen science tools date its presence back to 2018. A total of 74 sightings along the island’s coasts were reported between 2018 and 2024, when it reached densities of ca. 2 individuals/aggregates per square metre in the initial introduction area. Thus, the species is undergoing a clear proliferation and a spatial expansion. Morphological and genetic analyses confirmed the identity of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> and its phylogenetic placement, closely related to other <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part></tp:taxon-name></italic> and related genera such as <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Asterocarpa">Asterocarpa</tp:taxon-name-part></tp:taxon-name></italic>. This species shows concerning invasive characteristics, such as a fast expansion, abundance in natural habitats, and aggregative behaviour, suggesting potential threats to native biota. Due to its limited natural dispersal capacity, the introduction of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> to Tenerife is attributed to anthropogenic vectors, particularly oil platforms arriving at major Canary Island ports. The proximity of the initial records to port areas supports this hypothesis. Given the potential species’ ecological risks, the authors recommend close monitoring, manual removal where feasible, and strengthened involvement of citizen science. This case highlights the vulnerability of oceanic islands to marine biological invasions and the importance of ports and marinas as critical entry points, underscoring the need for proactive surveillance and early intervention strategies.</p>
      </abstract>
      <kwd-group>
        <label>Key words:</label>
        <kwd>Biological invasion</kwd>
        <kwd>citizen science</kwd>
        <kwd>DNA barcoding</kwd>
        <kwd>taxonomy</kwd>
        <kwd>tunicate</kwd>
      </kwd-group>
      <funding-group>
        <award-group>
          <funding-source>
            <named-content content-type="funder_name">Ministerio de Ciencia, Innovación y Universidades</named-content>
            <named-content content-type="funder_identifier">100014440</named-content>
            <named-content content-type="funder_ror">https://ror.org/05r0vyz12</named-content>
            <named-content content-type="funder_doi">http://doi.org/10.13039/100014440</named-content>
          </funding-source>
        </award-group>
      </funding-group>
    </article-meta>
    <notes>
      <sec sec-type="Citation" id="SECID0E6G">
        <title>Citation</title>
        <p>Turon X, Martín-Solà M, Moro-Abad L, Hernández JC (2025) Emergence of an invasive ascidian in Canary Islands (Eastern Atlantic): Tracking the arrival and spread of <italic>Cnemidocarpa irene</italic>. Aquatic Invasions 20(4): 411–425. <ext-link xlink:href="10.3391/ai.2025.20.4.172098" ext-link-type="doi" xlink:type="simple">https://doi.org/10.3391/ai.2025.20.4.172098</ext-link></p>
      </sec>
    </notes>
  </front>
  <body>
    <sec sec-type="﻿Introduction" id="SECID0EVH">
      <title>﻿Introduction</title>
      <p>Non-indigenous species (<abbrev xlink:title="Non-indigenous species" id="ABBRID0E2H">NIS</abbrev>) are a major cause of ecological change in marine communities and one of the main threats to global biodiversity (<xref ref-type="bibr" rid="B13">Dukes and Mooney 1999</xref>; <xref ref-type="bibr" rid="B3">Bax et al. 2003</xref>; <xref ref-type="bibr" rid="B29">McGeoch et al. 2010</xref>). Assessing the initial stages of any introduction is key to allow prompt management and to ascertain the introduction dynamics and forecast potential spread. However, this information is lacking for most known introductions and subsequent invasions in the marine environment.</p>
      <p>Oceanic islands in particular are well known models for biogeography and ecology studies. They are particularly sensitive to invasions by non-native species due to their high degree of endemism (<xref ref-type="bibr" rid="B51">Sax and Gaines 2008</xref>). While terrestrial introductions in insular systems have been extensively studied as models in invasion science (e.g., <xref ref-type="bibr" rid="B53">Simberloff 1995</xref>; <xref ref-type="bibr" rid="B25">Lenzner et al. 2020</xref>), much less is known on the effects of marine invasions on islands, with Pacific archipelagos being the most studied so far (e.g., <xref ref-type="bibr" rid="B41">Paulay et al. 2002</xref>; <xref ref-type="bibr" rid="B18">Inglis et al. 2006</xref>; <xref ref-type="bibr" rid="B7">Carlton and Eldredge 2015</xref>).</p>
      <p>The Macaronesian region in the eastern Atlantic (including Azores, Madeira, Canary Islands and Cabo Verde archipelagos) has been the subject of some studies of marine <abbrev xlink:title="Non-indigenous species" id="ABBRID0EIBAC">NIS</abbrev> (e.g., <xref ref-type="bibr" rid="B6">Canning-Clode et al. 2013</xref>; <xref ref-type="bibr" rid="B11">Chainho et al. 2015</xref>; <xref ref-type="bibr" rid="B40">Pajuelo et al. 2016</xref>). In a recent review of Macaronesian marine non-native species (<xref ref-type="bibr" rid="B10">Castro et al. 2022</xref>), the Canary Islands have been signalled as a hotspot for introductions compared to nearby archipelagos, and this is attributable to the intense shipping activity, touristic pressure involving a dense network of marinas, oil drill settings, and aquaculture activities, among others. Over 110 marine <abbrev xlink:title="Non-indigenous species" id="ABBRID0E3BAC">NIS</abbrev> have been reported in the Canary Islands (<ext-link xlink:href="https://www.biodiversidadcanarias.es/exos" ext-link-type="uri" xlink:type="simple">https://www.biodiversidadcanarias.es/exos</ext-link>, accessed 21 December 2024).</p>
      <p>Among marine invasive organisms, ascidians are an important group that includes species of major concern (<xref ref-type="bibr" rid="B22">Lambert 2001</xref>, <xref ref-type="bibr" rid="B23">2007</xref>), some of which have worldwide colonisation ranges (<xref ref-type="bibr" rid="B23">Lambert 2007</xref>; <xref ref-type="bibr" rid="B59">Zhan et al. 2015</xref>). They are sessile marine filter feeders with some characteristics suitable for successful colonisation: rapid growth rate and short time to maturity (<xref ref-type="bibr" rid="B45">Rius et al. 2009</xref>; <xref ref-type="bibr" rid="B43">Pineda et al. 2013</xref>; <xref ref-type="bibr" rid="B8">Casso et al. 2018</xref>), physical and chemical defences (<xref ref-type="bibr" rid="B55">Stoecker 1980</xref>; <xref ref-type="bibr" rid="B28">López-Legentil et al. 2006</xref>), and the production of a large number of short-lived non-feeding planktonic larvae (<xref ref-type="bibr" rid="B22">Lambert 2001</xref>). In the Canary Islands, the presence of nearly 50 new ascidians has been recorded over the past 10 years (<ext-link xlink:href="https://www.biodiversidadcanarias.es/exos" ext-link-type="uri" xlink:type="simple">https://www.biodiversidadcanarias.es/exos</ext-link>; Martín-Solà et al. 2022).</p>
      <p>Invasive ascidians are commonly found on artificial substrates (<xref ref-type="bibr" rid="B58">Tyrrell and Byers 2007</xref>) which makes them one of the main fouling groups in marinas, aquaculture facilities and other human-built structures (<xref ref-type="bibr" rid="B1">Airoldi et al. 2015</xref>). There are, however, some cases of ascidian invasions of natural benthic communities, where they can aggressively overgrow epibenthic communities and cover large areas of the seafloor. Some prominent instances are <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Didemnum">Didemnum</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="vexillum">vexillum</tp:taxon-name-part></tp:taxon-name></italic> in the NE American coast (<xref ref-type="bibr" rid="B5">Bullard et al. 2007</xref>; <xref ref-type="bibr" rid="B19">Kaplan et al. 2018</xref>), <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Pyura">Pyura</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="praeputialis">praeputialis</tp:taxon-name-part></tp:taxon-name></italic> in Chile (<xref ref-type="bibr" rid="B9">Castilla et al. 2004</xref>), or <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Distaplia">Distaplia</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="stylifera">stylifera</tp:taxon-name-part></tp:taxon-name></italic> in Baja California (<xref ref-type="bibr" rid="B38">Moreno-Dávila et al. 2023</xref>).</p>
      <p>We describe here the recent arrival and expansion of a solitary ascidian previously unreported in the Canary Islands. This species is identified as <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> (Hartmeyer, 1906), an Indo-Pacific species that has been first introduced in the Caribbean, from where it expanded its range to Brazil and Cape Verde islands. The species can thrive in natural habitats and therefore poses a worrisome threat to native biota, warranting urgent monitoring.</p>
    </sec>
    <sec sec-type="methods" id="SECID0E3FAC">
      <title>﻿Methods</title>
      <sec sec-type="﻿Abundance and distribution" id="SECID0EAGAC">
        <title>﻿Abundance and distribution</title>
        <p>The species was first documented during biodiversity assessments at shallow rocky reefs of Boca Cangrejo (coordinates: <named-content content-type="dwc:verbatimCoordinates"><named-content content-type="geo-json" specific-use="{&quot;type&quot;:&quot;Point&quot;,&quot;coordinates&quot;:[-16.314799,28.406016]}" id="NCID0EJGAC">28.406016 -16.314799</named-content></named-content>, NE Tenerife Island, Fig. <xref ref-type="fig" rid="F1">1</xref>) in August 2020. This locality is a natural environment, hotspot for diving and recreational activities, located 11 Km south of the island’s main port hub in the capital, Santa Cruz. No individuals had been observed in July of the same year at Boca Cangrejo. A follow-up was performed at this locality during 2020–2021 to monitor its initial spread. A further tally was done at the end of 2024. All assessments were made by deploying 3 to 5 transects (10 × 2 metres) between 2 and 5 m of depth and counting the number of individuals or aggregates found.</p>
        <fig id="F1" position="float" orientation="portrait">
          <object-id content-type="doi">10.3391/ai.2025.20.4.172098.figure1</object-id>
          <object-id content-type="arpha">01A4763B-C3BF-560C-8E54-1119399F6C4E</object-id>
          <label>Figure 1.</label>
          <caption>
            <p>Map of Tenerife (Canary Islands) with the total number of observations. The findings of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> in the different areas (2018–2024) recorded in RedPROMAR are coloured according to the period of initial observations: red (2018–2019), orange (2020–2022), and green (2023–2024). Sourced from <ext-link xlink:href="https://redpromar.org/home" ext-link-type="uri" xlink:type="simple">https://redpromar.org/home</ext-link> (accessed January 2025). Arrow points at the location of Boca Cangrejo, the initial point of detection, and where the abundance transects were performed. Circles mark the position of the main ports and marinas in the island. The bigger, colored one indicates the main commercial port of Santa Cruz. The other ports indicated (starting from Santa Cruz in a clockwise direction) are Radazul, Candelaria, Güímar, Granadilla, San Miguel, Las Galletas (southernmost port), Los Cristianos, Puerto Colón, Los Gigantes, and Garachico.</p>
          </caption>
          <graphic xlink:href="aquaticinvasions-20-411_article-172098__-g001.jpg" position="float" orientation="portrait" xlink:type="simple" id="oo_1463706.jpg">
            <uri content-type="original_file">https://binary.pensoft.net/fig/1463706</uri>
          </graphic>
        </fig>
        <p>In addition, and in the framework of the citizen science platform RedPROMAR (<ext-link xlink:href="https://redpromar.org" ext-link-type="uri" xlink:type="simple">https://redpromar.org</ext-link>), observations of the species have been recorded in recent years at various locations on the island of Tenerife (Fig. <xref ref-type="fig" rid="F1">1</xref>). REDPROMAR is a network set up by the Canary Islands Government for the monitoring and surveillance of marine life in the Archipelago. Anyone can register and upload sightings, which must be accompanied by a precise location, date, and a picture of the organism. Sightings are validated by a team of specialists in various taxonomic groups.</p>
      </sec>
      <sec sec-type="﻿Taxonomic observation" id="SECID0E1HAC">
        <title>﻿Taxonomic observation</title>
        <p>All specimens examined were sampled at Boca Cangrejo, seven collected in January 2021 and eight in October 2021. Half the specimens were preserved in alcohol for genetic analyses, and the other half in formalin for morphological examination. The latter were dissected and examined under a stereomicroscope, and the cuticular lining of the siphons was excised to examine the siphonal spines with a light microscope.</p>
      </sec>
      <sec sec-type="﻿Genetic analyses" id="SECID0E6HAC">
        <title>﻿Genetic analyses</title>
        <p>A small piece (ca. 5–9 mm<sup>2</sup>) of the muscular mantle tissue of six individuals was extracted with REDExtract-N-Amp Tissue kit (Sigma-Aldrich), following manufacturer’s recommendations. A fragment of ca. 590 bp of the cytochrome oxidase I (<abbrev xlink:title="cytochrome oxidase I" id="ABBRID0EHIAC">COI</abbrev>) mitochondrial gene was amplified with the ascidian-specific primers Tun_forward 5’ TCGACTAATCATAAAGATATTAG 3’, and Tun_reverse2, 5’ AACTTGTATTTAAATTACGATC 3’ (<xref ref-type="bibr" rid="B54">Stefaniak et al. 2009</xref>). PCR amplification was done in 20 µL total reaction volume with 10 µL of REDExtract-N-Amp PCR reaction mix (Sigma-Aldrich), 0.8 µL (10 mM) of each primer, 6.4 µL of ultra-pure water (Sigma-Aldrich) and 2 µL of DNA at a concentration of ca. 5 ng/µL. PCR followed an initial denaturation at 94 °C for 5 min, 35 cycles of a denaturation step at 94 °C for 1 min, an annealing step at 50 °C for 1 min, an elongation step at 72 °C for 1 min, and a final elongation step at 72 °C for 7 min. The amplified DNA was purified with Exo-SAP. Sequencing was carried out (both strands) at Macrogen facilities (Netherlands). The resulting sequences were assembled, edited and aligned in BioEdit v.7.2.6 (<xref ref-type="bibr" rid="B16">Hall 1999</xref>). The final alignment length was 584 bp.</p>
        <p>In order to place the new sequences in a phylogenetic context, we compiled a dataset of <tp:taxon-name><tp:taxon-name-part taxon-name-part-type="family">Styelidae</tp:taxon-name-part></tp:taxon-name><abbrev xlink:title="cytochrome oxidase I" id="ABBRID0E1IAC">COI</abbrev> sequences available in GenBank. We obtained sequences of all genera available with enough coverage (90% or above) of the sequenced region. We included representative species of these genera and, whenever possible, two sequences per species for a better clade sorting. We also downloaded all sequences from the genus <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part></tp:taxon-name></italic> and, in the case of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="verrucosa">verrucosa</tp:taxon-name-part></tp:taxon-name></italic>, we obtained representatives of the two clades (spA and spB) recognized by <xref ref-type="bibr" rid="B50">Ruiz et al. (2020)</xref>. Three unpublished sequences of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part></tp:taxon-name></italic> in GenBank, two identified as <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="areolata">areolata</tp:taxon-name-part></tp:taxon-name></italic> (a synonym of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic>, see Discussion) with accession numbers <ext-link ext-link-type="gen" xlink:href="KX138515" xlink:type="simple">KX138515</ext-link> and <ext-link ext-link-type="gen" xlink:href="KX138514" xlink:type="simple">KX138514</ext-link>, and a <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part></tp:taxon-name></italic> sp. (<ext-link ext-link-type="gen" xlink:href="KX650767" xlink:type="simple">KX650767</ext-link>), were not included in the final dataset. The three of them were &gt; 90% similar, but blast searches of these sequences showed a low similarity with any other ascidian. The best hits were ca. 78% similarity with a <tp:taxon-name><tp:taxon-name-part taxon-name-part-type="family">Pyuridae</tp:taxon-name-part></tp:taxon-name> (<italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Microcosmus">Microcosmus</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="squamiger">squamiger</tp:taxon-name-part></tp:taxon-name></italic>) and with a <tp:taxon-name><tp:taxon-name-part taxon-name-part-type="family">Styelidae</tp:taxon-name-part></tp:taxon-name> (<italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Botrylloides">Botrylloides</tp:taxon-name-part></tp:taxon-name></italic> sp.). Similarities with all other <tp:taxon-name><tp:taxon-name-part taxon-name-part-type="family">Styelidae</tp:taxon-name-part></tp:taxon-name> sequences in the dataset had a mean of 72.8%. As there is no publication and we could not verify their identity, we considered these divergent sequences as being misidentified.</p>
        <p>The aligned sequences were trimmed to a common length (536 bp) and checked with the modelTest function of the R package <italic>phangorn</italic> (<xref ref-type="bibr" rid="B52">Schliep 2011</xref>) to select the best-fit evolutionary model of nucleotide substitution based on the Akaike Information Criterion (<abbrev xlink:title="Akaike Information Criterion" id="ABBRID0EQMAC">AIC</abbrev>). This model was then selected in a maximum likelihood tree search in Mega X (<xref ref-type="bibr" rid="B21">Kumar et al. 2018</xref>) with default options and 100 bootstrap replicates. A sequence of the pyurid <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Halocynthia">Halocynthia</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="papillosa">papillosa</tp:taxon-name-part></tp:taxon-name></italic> was used as an outgroup. A fasta file with the alignment is provided as Suppl. material <xref ref-type="supplementary-material" rid="S1">1</xref>.</p>
      </sec>
    </sec>
    <sec sec-type="﻿Results" id="SECID0EHNAC">
      <title>﻿Results</title>
      <sec sec-type="﻿Abundance and distribution" id="SECID0ELNAC">
        <title>﻿Abundance and distribution</title>
        <p><italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> is a solitary species of the family <tp:taxon-name><tp:taxon-name-part taxon-name-part-type="family">Styelidae</tp:taxon-name-part></tp:taxon-name>. However, it is most often present in nature forming aggregates of 2–10 individuals. For simplicity, we will hereafter use “aggregates” as the abundance unit (albeit occasionally what we counted were single individuals). In the monitored point at Punta Cangrejo, the abundance of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> increased in little more than one year since first detection (August 2020) to values over 1 aggregate per square meter. Four years after arrival, it reached densities of 1.9 aggregates*m<sup>-2</sup> in December of 2024 (Fig. <xref ref-type="fig" rid="F2">2</xref>).</p>
        <fig id="F2" position="float" orientation="portrait">
          <object-id content-type="doi">10.3391/ai.2025.20.4.172098.figure2</object-id>
          <object-id content-type="arpha">80A43273-9D82-5043-B209-C26ECA787F7D</object-id>
          <label>Figure 2.</label>
          <caption>
            <p><italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> abundance trend at Boca Cangrejo site for 2020–2024. Photo credit: Antonio de la Rosa.</p>
          </caption>
          <graphic xlink:href="aquaticinvasions-20-411_article-172098__-g002.jpg" position="float" orientation="portrait" xlink:type="simple" id="oo_1463707.jpg">
            <uri content-type="original_file">https://binary.pensoft.net/fig/1463707</uri>
          </graphic>
        </fig>
        <p>After identification of the species in 2021, we could in retrospect identify some observations previously registered at the RedPROMAR citizen science platform (RedPROMAR 2025), but as yet unassigned. The identification was based on pictures of individuals matching the general appearance of the species and in which the siphons are open and their typical aspect (see below) could be ascertained. This pushed back <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic>’s arrival in Tenerife to 2018 (Fig. <xref ref-type="fig" rid="F1">1</xref>). Since that year, in the Canary Islands, this species has only been observed on Tenerife. The first records in the platform (2018–2019) were located in the northeastern part of the island. Subsequently (2020–2022), additional sightings were recorded at other locations along the eastern coast. In recent years (2023–2024), sightings have also been reported along the southern and western coasts. In total, 74 sightings have been documented on the RedPROMAR platform during this period (Fig. <xref ref-type="fig" rid="F1">1</xref>).</p>
      </sec>
      <sec sec-type="﻿Morphological description" id="SECID0EAAAE">
        <title>﻿Morphological description</title>
        <p>The synonymy of the species is complicated (see Discussion), and detailed morphological descriptions are necessary to verify the taxonomic status of any new finding. Thus, we aim here to provide a comprehensive account of the external and internal morphology of the specimens collected.</p>
        <p>The individuals measure up to 5 cm in maximal dimension. The tunic is reddish to orange in live specimens (turning brown in fixative) (Fig. <xref ref-type="fig" rid="F3">3A–E</xref>). The siphons are distinctive, with the inner surface covered by a velum extending almost to the siphon rim. This gives the inner siphons a marbled appearance, predominantly whitish, yellowish or greenish in tone. In some specimens, the inner surface of the siphons is darker, brown to reddish, featuring yellow-green patches (Fig. <xref ref-type="fig" rid="F3">3F</xref>). Scale-like spines (20 µm in width) are present in the upper inner tunic of the siphons, but they are few and hard to observe. The tunic surface ranges from near-smooth to rough with tubercles of several sizes. The ascidians are covered by other epibionts, mainly algae species. However, when individuals are found in areas with sea urchins they are cleaner than otherwise, likely due to the effect of sea urchin grazing upon epibionts. The ascidians are fixed ventrally and posteriorly, and the intersiphonal distance is ca. half the total tunic length. It is not uncommon to see individuals on the carapace of sponge crabs (<italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Dromia">Dromia</tp:taxon-name-part></tp:taxon-name></italic> spp., Fig. <xref ref-type="fig" rid="F3">3E</xref>).</p>
        <fig id="F3" position="float" orientation="portrait">
          <object-id content-type="doi">10.3391/ai.2025.20.4.172098.figure3</object-id>
          <object-id content-type="arpha">C620358D-C204-528E-9910-4A464CB1EFBB</object-id>
          <label>Figure 3.</label>
          <caption>
            <p><italic>In situ</italic> images of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic>. <bold>A–C</bold> underwater pictures of the species, note variable cover by epibionts (the colonial ascidian <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Symplegma">Symplegma</tp:taxon-name-part></tp:taxon-name></italic> sp in A); <bold>D</bold> an aggregation of individuals; <bold>E</bold> individual hitchhiking a sponge crab (<italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Dromia">Dromia</tp:taxon-name-part></tp:taxon-name></italic> sp.); <bold>F</bold> detail of the oral siphon of another individual. Photo Credit: <bold>A–E</bold> Marc Martín-Solà; <bold>F</bold> Leopoldo Moro-Abad.</p>
          </caption>
          <graphic xlink:href="aquaticinvasions-20-411_article-172098__-g003.jpg" position="float" orientation="portrait" xlink:type="simple" id="oo_1463708.jpg">
            <uri content-type="original_file">https://binary.pensoft.net/fig/1463708</uri>
          </graphic>
        </fig>
        <p>The tunic is consistent but not coriaceous, it has an inner whitish layer and the mantle is easily separated from it. The mantle is dark-brown, weakly muscular, and allows the gonads to be seen from outside (Fig. <xref ref-type="fig" rid="F4">4A, B</xref>).</p>
        <fig id="F4" position="float" orientation="portrait">
          <object-id content-type="doi">10.3391/ai.2025.20.4.172098.figure4</object-id>
          <object-id content-type="arpha">424BB661-6A42-5C04-832E-9B7AEEA946B5</object-id>
          <label>Figure 4.</label>
          <caption>
            <p>Anatomical details of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic>. <bold>A, B</bold> right and left view of the mantle of an individual; <bold>C</bold> dissected mantle of another specimen, branchial sac retired; <bold>D</bold> section of the stomach showing internal ridges; <bold>E, F</bold> images of the apertures of the neural gland of two individuals; <bold>G</bold> detail of the branchial mesh between folds; <bold>H</bold> enlarged view of the atrial siphon (as) zone, showing the distal end of four gonads on the right body side and two on the left (asterisks), anus (a), and esophagus (e). Arrowheads point to filiform tentacles at the base of the atrial velum; <bold>I</bold> detail of the distal end of one gonad, showing sperm ducts (arrowheads) joining a common duct that runs along the length of the gonad (asterisks). Male and female papillae are shown. Photo credit: Xavier Turon. Scale bars: 1 cm (<bold>A–C</bold>); 5 mm (<bold>D</bold>); 1 mm (<bold>E–G</bold>); 5 mm (<bold>H</bold>); 1 mm (<bold>I</bold>).</p>
          </caption>
          <graphic xlink:href="aquaticinvasions-20-411_article-172098__-g004.jpg" position="float" orientation="portrait" xlink:type="simple" id="oo_1463709.jpg">
            <uri content-type="original_file">https://binary.pensoft.net/fig/1463709</uri>
          </graphic>
        </fig>
        <p>The oral siphon is lined by a variable number (20–30) of simple tentacles (Fig. <xref ref-type="fig" rid="F4">4C</xref>) arising from a short membrane with a denticulate margin. The pericoronal area is narrow, and the aperture of the neural gland is U-shaped with horns more or less rolled (Fig. <xref ref-type="fig" rid="F4">4E, F</xref>). The branchial sac has four folds on each side that are well separated and do not overlap. The dorsal lamina is simple and low. The branchial formula varies among individuals, but for a 4.5 cm specimen at the posterior part of the branchial sac it was:</p>
        <p>Right: Dorsal lamina-5-(14)-7-(18)-5-(13)-5-(14)-5-Endostyle</p>
        <p>Left: Dorsal lamina-7-(12)-5-(14)-5-(13)-5-(14)-5-Endostyle</p>
        <p>There are up to 7–10 stigmata in a branchial mesh (Fig. <xref ref-type="fig" rid="F4">4G</xref>), and parastigmatic vessels are sometimes present, particularly near the dorsal lamina.</p>
        <p>The digestive system forms a closed loop, with the ascending and descending branches of the gut close together (Fig. <xref ref-type="fig" rid="F4">4C</xref>). The secondary loop is wide open. The digestive system does not reach the posterior end of the body, leaving a free space. The stomach is sac-like with a smooth outer surface, although internally there are up to 20 laminar plications (Fig. <xref ref-type="fig" rid="F4">4D</xref>). The anus is multi-lobed and opens near the atrial siphon (Fig. <xref ref-type="fig" rid="F4">4H</xref>). In this same area open the gonoducts, and a ring of filiform tentacles is present at the basis of the atrial velum (Fig. <xref ref-type="fig" rid="F4">4H</xref>).</p>
        <p>The gonads are elongated and tubular, in variable numbers. We have found generally four (sometimes three) on the right side, but often some of them are bifurcated (one gonad divides distally in two branches) or two gonads are fused distally (e.g., Fig. <xref ref-type="fig" rid="F4">4C</xref>). On the left side there are generally two (sometimes three) gonads, anterior to the digestive loop. The gonads have the male follicles in the lower (mantle-wise) part, while the upper (branchial-wise) portion contains the oocytes. In all cases the gonads were ripe (samples examined were from January and October). The sperm ducts from the male follicles surround the oocyte mass and join in the upper part of the gonad into a common sperm duct that runs the length of the gonad until the distal male papilla situated just above the female opening (Fig. <xref ref-type="fig" rid="F4">4I</xref>).</p>
        <p>There are a few endocarps interspersed with the gonads on the right side of the body, but they are more frequent both inside the gut loop and following the outer margin of the intestine curve (Fig. <xref ref-type="fig" rid="F4">4C</xref>).</p>
      </sec>
      <sec sec-type="﻿Genetic analyses" id="SECID0EYFAE">
        <title>﻿Genetic analyses</title>
        <p>We obtained 4 different haplotypes from the 6 individuals sequenced (H1, H2, H3: one individual each; H4: three individuals). The sequences have been deposited in GenBank (accession numbers: <ext-link ext-link-type="gen" xlink:href="PV849603" xlink:type="simple">PV849603</ext-link> to <ext-link ext-link-type="gen" xlink:href="PV849606" xlink:type="simple">PV849606</ext-link>). Sequence identities between them ranged from 0.917 to 0.984, being H2 the most divergent with respect to the other three haplotypes. They were added to a database of 48 sequences of <tp:taxon-name><tp:taxon-name-part taxon-name-part-type="family">Styelidae</tp:taxon-name-part></tp:taxon-name> encompassing 14 genera (Suppl. material <xref ref-type="supplementary-material" rid="S1">1</xref>). The modelTest function revealed that the best-fit model of nucleotide selection for this dataset was the General Time Reversible model with a gamma distributed rate variation among sites and a proportion of invariable sites (GTR+G+I). This model was input in the ML algorithm of Mega and the corresponding phylogenetic tree obtained is depicted in Fig. <xref ref-type="fig" rid="F5">5</xref> (G parameter = 0.731, I parameter = 43.76%).</p>
        <fig id="F5" position="float" orientation="portrait">
          <object-id content-type="doi">10.3391/ai.2025.20.4.172098.figure5</object-id>
          <object-id content-type="arpha">379310B0-A7A7-5810-9891-AB537FA2DC8E</object-id>
          <label>Figure 5.</label>
          <caption>
            <p>Maximum likelihood tree of the <tp:taxon-name><tp:taxon-name-part taxon-name-part-type="family">Styelidae</tp:taxon-name-part></tp:taxon-name> dataset. For each branch, GenBank accession number and species name (as in Suppl. material <xref ref-type="supplementary-material" rid="S1">1</xref>) is provided. Numbers in main branches indicate bootstrap support values (when &gt; 50%). For <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="verrucosa">verrucosa</tp:taxon-name-part></tp:taxon-name></italic>, the two clades (spA and spB) identified by <xref ref-type="bibr" rid="B50">Ruiz et al. (2020)</xref> are indicated. The same was done for the two clades of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Styela">Styela</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="plicata">plicata</tp:taxon-name-part></tp:taxon-name></italic> named Group1 and Group2 in <xref ref-type="bibr" rid="B42">Pineda et al. (2011)</xref>. Sequences obtained in this study are indicated in red.</p>
          </caption>
          <graphic xlink:href="aquaticinvasions-20-411_article-172098__-g005.jpg" position="float" orientation="portrait" xlink:type="simple" id="oo_1463710.jpg">
            <uri content-type="original_file">https://binary.pensoft.net/fig/1463710</uri>
          </graphic>
        </fig>
        <p>It can be seen that the four haplotypes obtained formed a monophyletic clade with high bootstrap support. In turn, this clade joins the one formed by 4 sequences of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="verrucosa">verrucosa</tp:taxon-name-part></tp:taxon-name></italic> and 2 of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Asterocarpa">Asterocarpa</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="humilis">humilis</tp:taxon-name-part></tp:taxon-name></italic> (each species forming a separate clade). The sister clade to this group includes the five <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Styela">Styela</tp:taxon-name-part></tp:taxon-name></italic> species in the dataset. It is noteworthy that the only other <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part></tp:taxon-name></italic> sequence included, <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="finmarkiensis">finmarkiensis</tp:taxon-name-part></tp:taxon-name></italic>, was rather divergent from the ones in the <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part></tp:taxon-name></italic> + <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Asterocarpa">Asterocarpa</tp:taxon-name-part></tp:taxon-name></italic> clade, forming part of an unresolved polytomy.</p>
      </sec>
    </sec>
    <sec sec-type="﻿Discussion" id="SECID0EIKAE">
      <title>﻿Discussion</title>
      <p>The specimens studied match previous descriptions of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic>, in particular the detailed ones of <xref ref-type="bibr" rid="B31">Monniot (1983</xref>, as <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="areolata">areolata</tp:taxon-name-part></tp:taxon-name></italic>), <xref ref-type="bibr" rid="B39">Nishikawa (1991)</xref>, <xref ref-type="bibr" rid="B47">Rocha et al. (2012)</xref>, and <xref ref-type="bibr" rid="B35">Monniot (2018)</xref>. It should be noted that the synonymy of the species is complicated, as discussed by <xref ref-type="bibr" rid="B32">Monniot and Monniot (1984)</xref> and <xref ref-type="bibr" rid="B39">Nishikawa (1991)</xref>. <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> is a species found from shallow waters to deep sea (<xref ref-type="bibr" rid="B36">Monniot 2021</xref>), and is a cause of concern for its invasive potential (<xref ref-type="bibr" rid="B27">Locke 2009</xref>; <xref ref-type="bibr" rid="B35">Monniot 2018</xref>). Punta Cangrejo, the locality of the first sightings and where the highest densities of the species have been found, is located a few kilometres south of the main port of Santa Cruz, in an area with predominantly southward currents. Thus, it is likely that the species first entered the island via the commercial hub of its capital.</p>
      <p>Although detailed morphological examination is essential for the reliable identification of ascidian species, it is not feasible for all sightings, particularly those reported through citizen science platforms that rely primarily on photographs. Therefore, diagnostic characters based on external features are desirable. In <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic>, aside from overall shape and coloration, the inner siphonal pattern can serve as a useful diagnostic trait, as the marbled appearance and coloration of the siphons are distinctive. Many <tp:taxon-name><tp:taxon-name-part taxon-name-part-type="family">Styelidae</tp:taxon-name-part></tp:taxon-name> and <tp:taxon-name><tp:taxon-name-part taxon-name-part-type="family">Pyuridae</tp:taxon-name-part></tp:taxon-name>, groups that include similarly sized solitary ascidians, exhibit a marked pattern of longitudinal bands in the siphons. A potential source of confusion is <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Pyura">Pyura</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="herdmani">herdmani</tp:taxon-name-part></tp:taxon-name></italic>, which has similarly marbled inner siphonal linings, occurs in NW Africa, and has recently been introduced to Europe (<xref ref-type="bibr" rid="B46">Rius et al. 2024</xref>). However, individuals of this species are much larger (up to 30 cm) than those of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic>. For this and other solitary ascidian species, it is strongly recommended that citizen science practitioners obtain underwater pictures of individuals with their siphons wide open to capture the characteristic colour patterns.</p>
      <p><italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> was described from Japan (<xref ref-type="bibr" rid="B17">Hartmeyer 1906</xref>) and is common in the Indo-West Pacific region (<xref ref-type="bibr" rid="B20">Kott 1985</xref>, as <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="areolata">areolata</tp:taxon-name-part></tp:taxon-name></italic>, <xref ref-type="bibr" rid="B44">Rho and Park 1998</xref>; <xref ref-type="bibr" rid="B37">Monniot and Monniot 2003</xref>; <xref ref-type="bibr" rid="B27">Locke 2009</xref>; <xref ref-type="bibr" rid="B24">Lambert et al. 2021</xref>), but in the western Atlantic it had only been reported for the Caribbean (<xref ref-type="bibr" rid="B31">Monniot 1983</xref>, as <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="areolata">areolata</tp:taxon-name-part></tp:taxon-name></italic>; <xref ref-type="bibr" rid="B32">Monniot and Monniot 1984</xref>, as <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="valborg">valborg</tp:taxon-name-part></tp:taxon-name></italic>). <xref ref-type="bibr" rid="B31">Monniot (1983)</xref> indicated that it had likely been introduced in the Caribbean, and the species has been recently reported as introduced to Brazilian waters (<xref ref-type="bibr" rid="B47">Rocha et al. 2012</xref>, <xref ref-type="bibr" rid="B48">2024</xref>; <xref ref-type="bibr" rid="B12">Dias et al. 2013</xref>; <xref ref-type="bibr" rid="B15">Granthom-Costa et al. 2025</xref>).</p>
      <p>In the eastern Atlantic it was first reported in Cape Verde in 1990 by <xref ref-type="bibr" rid="B33">Monniot and Monniot (1994)</xref>, albeit these authors noted also that the species <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="maroccana">maroccana</tp:taxon-name-part></tp:taxon-name></italic> may be instead <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic>, in which case there would also be a report in Morocco, pushing back in time the presence of the species in the eastern Atlantic. The type specimen being lost, this fact remains unverifiable (<xref ref-type="bibr" rid="B33">Monniot and Monniot 1994</xref>).</p>
      <p>The genetic results show that the sequences obtained formed a robust clade, which in turn groups with that of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="verrucosa">verrucosa</tp:taxon-name-part></tp:taxon-name></italic> and <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Asterocarpa">Asterocarpa</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="humilis">humilis</tp:taxon-name-part></tp:taxon-name></italic>. The latter was initially placed in the genus <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part></tp:taxon-name></italic>, until the new genus <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Asterocarpa">Asterocarpa</tp:taxon-name-part></tp:taxon-name></italic> was described (<xref ref-type="bibr" rid="B4">Brewin 1946</xref>). Both genera are closely related (<xref ref-type="bibr" rid="B20">Kott 1985</xref>), and are distinguished on the basis of a different gonad arrangement, albeit this separation is not accepted by some authors (<xref ref-type="bibr" rid="B34">Monniot et al. 2001</xref>). Our genetic results did not support the establishment of a separate <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Asterocarpa">Asterocarpa</tp:taxon-name-part></tp:taxon-name></italic> genus. The closest clade to the <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part></tp:taxon-name></italic> + <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Asterocarpa">Asterocarpa</tp:taxon-name-part></tp:taxon-name></italic> one comprises the species of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Styela">Styela</tp:taxon-name-part></tp:taxon-name></italic>, a genus closely related to <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part></tp:taxon-name></italic> also on morphological grounds (<xref ref-type="bibr" rid="B20">Kott 1985</xref>). On the other hand, the nature of the rather divergent sequence of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="finmarkiensis">finmarkiensis</tp:taxon-name-part></tp:taxon-name></italic> surely deserves more studies with taxonomically verified material and more sequences. Albeit <abbrev xlink:title="cytochrome oxidase I" id="ABBRID0EKVAE">COI</abbrev> lacks resolution to establish a reliable phylogeny, the results obtained with this dataset confirm the placement of our sequences in the genus <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">Cnemidocarpa</tp:taxon-name-part></tp:taxon-name></italic> and agree in some aspects (such as the polyphyly of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Polyandrocarpa">Polyandrocarpa</tp:taxon-name-part></tp:taxon-name></italic> and <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Polycarpa">Polycarpa</tp:taxon-name-part></tp:taxon-name></italic>) with more detailed phylogenomic analyses (<xref ref-type="bibr" rid="B2">Alié et al. 2018</xref>).</p>
      <p>Given the reduced natural dispersal abilities of the short-lived larval stage of ascidians (<xref ref-type="bibr" rid="B56">Svane and Young 1989</xref>; <xref ref-type="bibr" rid="B22">Lambert 2001</xref>), the arrival of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> to the Canary Islands is attributable to anthropogenic transport. There are several potential mechanisms, from plastic trash rafting to oil platforms that can move entire benthic and fouling communities. However, oil platforms have been recently highlighted to be one of the most important introduction vectors in the Canary Islands to explain the massive exotic fish species arrivals of the last two decades, which has coincided in time with an increase of oil platform arrivals (<xref ref-type="bibr" rid="B40">Pajuelo et al. 2016</xref>; <xref ref-type="bibr" rid="B14">Falcón et al. 2023</xref>) to Santa Cruz in Tenerife and Las Palmas in Gran Canaria, the main harbours of these islands. The exotic communities mainly come from tropical regions of the eastern Atlantic and the Gulf of Guinea. However, Canary Islands also receive platforms from western tropical Atlantic regions such as Brazil, the Caribbean. Finally, a few rigs have been transported from the Indo-Pacific region. These movements imply that large ports, particularly those receiving oil platforms, are hotspots for non-indigenous species and, at the same time, priority areas for the early detection and management prior to the spread of potential marine biological invasions (<xref ref-type="bibr" rid="B26">Lehtiniemi et al. 2015</xref>; <xref ref-type="bibr" rid="B49">Romeo et al. 2015</xref>; <xref ref-type="bibr" rid="B57">Tempesti et al. 2020</xref>). The presence of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> was traced back to 2018, and in the shallow natural environment. These initial records and the majority of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> sightings reported on the RedPROMAR platform were concentrated in the northeastern part of the island (RedPROMAR 2025), near the port area of Santa Cruz de Tenerife, the main maritime hub of the island. After the identification of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic>, its presence has also been noted in harbours of the island (Martín-Solà, <italic>pers obs</italic>), where it had likely been previously overlooked, so an initial date of introduction in harbours cannot be determined at present.</p>
      <p>As the introduction is recent, it is not possible to ascertain its effects on local communities. While aggregates formed by <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> may provide substrate for other species, they can also compete for food and space with the native biota and have detrimental effects, especially if they reach high abundances as the increasing trend observed suggests. Given the current extent of <italic><tp:taxon-name><tp:taxon-name-part taxon-name-part-type="genus" reg="Cnemidocarpa">C.</tp:taxon-name-part> <tp:taxon-name-part taxon-name-part-type="species" reg="irene">irene</tp:taxon-name-part></tp:taxon-name></italic> proliferation in Tenerife, eradication of the species is no longer a realistic goal; it may have been feasible only at the onset of its introduction (likely in 2018 or shortly before). At present, mitigation measures such as manual removal are only practical when newly colonizing individuals are detected early upon arrival at a locality. To be able to identify these early stages of introduction, a close monitoring is necessary, particularly in and near harbours and marinas. The help of local citizens and diving clubs can prove invaluable in this respect. This case highlights the vulnerability of oceanic islands to marine biological invasions, underscoring the need for proactive surveillance and early intervention strategies.</p>
    </sec>
    <sec sec-type="﻿Funding" id="SECID0ELZAE">
      <title>﻿Funding</title>
      <p>This research was partially financed by project BlueDNA (PID2023-146307OB), funded by the Spanish Ministry of Science, Innovation, and Universities (MICIU/AEI/<ext-link xlink:type="simple" ext-link-type="doi" xlink:href="10.13039/501100011033)">10.13039/501100011033)</ext-link> and by ERDF/EU.</p>
    </sec>
    <sec sec-type="﻿Authors contribution" id="SECID0EWZAE">
      <title>﻿Authors contribution</title>
      <p>All authors, study conceptualization and design; LMA, JCH, MMS, data collection; LMA, MMS, underwater photographs; JCH, LMA, MMS, time series analyses; XT, morphology and genetic analyses, original draft; JCH, XT, funding; All authors, draft review and editing. We also acknowledge the contributions of two anonymous reviewers.</p>
    </sec>
  </body>
  <back>
    <ack>
      <title>﻿Acknowledgments</title>
      <p>The authors acknowledge the collaboration of all anonymous citizens that participated in the RedPROMAR initiative. We are also grateful to the comments by two anonymous reviewers that improved our manuscript.</p>
    </ack>
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        <mixed-citation xlink:type="simple"><person-group><name name-style="western"><surname>Zhan</surname><given-names>A</given-names></name><name name-style="western"><surname>Briski</surname><given-names>E</given-names></name><name name-style="western"><surname>Bock</surname><given-names>DG</given-names></name><name name-style="western"><surname>Ghabooli</surname><given-names>S</given-names></name><name name-style="western"><surname>MacIsaac</surname><given-names>HJ</given-names></name></person-group> (<year>2015</year>) <article-title>Ascidians as models for studying invasion success.</article-title><source>Marine Biology</source><volume>162</volume>: <fpage>2449</fpage>–<lpage>2470</lpage>. <ext-link xlink:href="10.1007/s00227-015-2734-5" ext-link-type="doi" xlink:type="simple">https://doi.org/10.1007/s00227-015-2734-5</ext-link></mixed-citation>
      </ref>
    </ref-list>
    <sec sec-type="supplementary-material">
      <title>Supplementary materials</title>
      <supplementary-material id="S1" position="float" orientation="portrait" xlink:type="simple">
        <object-id content-type="arpha">6AF4E34F-EDA9-5D90-9012-FD6B84F17AEC</object-id>
        <label>Supplementary material 1</label>
        <caption>
          <p>Alignment of the sequences used in the phylogeny reconstruction</p>
        </caption>
        <statement content-type="dataType">
          <label>Data type</label>
          <p>fas</p>
        </statement>
        <statement content-type="notes">
          <label>Explanation note</label>
          <p>GenBank accession numbers are indicated.</p>
        </statement>
        <media xlink:href="aquaticinvasions-20-411_article-172098__-s001.fas" mimetype="unknown" mime-subtype="unknown" position="float" orientation="portrait" xlink:type="simple" id="oo_1463711.fas">
          <uri content-type="original_file">https://binary.pensoft.net/file/1463711</uri>
        </media>
        <permissions>
          <license xlink:type="simple">
            <license-p>This dataset is made available under the Open Database License (http://opendatacommons.org/licenses/odbl/1.0/). The Open Database License (ODbL) is a license agreement intended to allow users to freely share, modify, and use this Dataset while maintaining this same freedom for others, provided that the original source and author(s) are credited.</license-p>
          </license>
        </permissions>
        <attrib specific-use="authors">Xavier Turon, Marc Martín-Solà, Leopoldo Moro-Abad, José Carlos Hernández</attrib>
      </supplementary-material>
    </sec>
  </back>
</article>
